Microorganism	Tax ID	Plastic	Ref	Enzyme	Enzyme ID	Database Enzyne Name	Gene	GenbankID	Sequence	Year	Evidence	Plastic used	Manufacturer	Analitical grade	Thermophilic conditions	Isolation sample type	Isolation environment	Isolation location	Degradation extrapolated from enzyme	Enzyme ID in paper	DOI
Ralstonia pickettii	329	PHB	Yukawa, H., Uchida, Y., Kohama, K., & Kurusu, Y. (1994). Monitoring of polymer biodegradabilities in the environment by a DNA probe method. In Studies in Polymer Science (Vol. 12, pp. 65-76). Elsevier.	PHB depolymerase	00001	00001 | PHB depolymerase | Ralstonia pickettii | PHB PHA	Yes	BAA04986.1	MKHPYGYRWHWLYALVVTLMTALATFSAHAAVTAGPGAWSSQQTWAADTVNGGNLTGYFYWPASQPTTPNGKRALVLVLHGCLQTASGDVIDNANGAGFNWKTIAEQYGAVVLAPNATGNVYSNHCWDYANTSPSRTSGHVGVLLDLVNRFVTNSQYAIDPNQVYVAGLSSGGGMTMVLGCIAPDIFAGIGINAGPPPAITRWKIGVVPSGYTATTAANNCKAWAGSNASSFNTQIAGAVWGTSDYTVAQAYGPMDTAAFRQIYGGTFTQGAQVSISGGGTNTPYTDSNGKLRTHEISVSGMAHAWPAGTGGDNNNYVDATHINYPAFVMDYWVKNNLRAGSGPVQSAGTPTGLTVTGTTTTSVSLSWNAVTNATSYNVYRNGSKVGSSTSTTYTDTGLIAGTTYSYTVTEIDPTAGESAQSSAVSAKTQSSFACTATTASNYAHVQAGRAHDSGGIAYANGSNQSMGLDNVFYTNTLAQTAAGYYVIGNCP	1994.0						Soil	Soil	Japan	Yes		
Ralstonia pickettii	329	PHA	Yukawa, H., Uchida, Y., Kohama, K., & Kurusu, Y. (1994). Monitoring of polymer biodegradabilities in the environment by a DNA probe method. In Studies in Polymer Science (Vol. 12, pp. 65-76). Elsevier.	PHB depolymerase	00001	00001 | PHB depolymerase | Ralstonia pickettii | PHB PHA	Yes	BAA04986.1	MKHPYGYRWHWLYALVVTLMTALATFSAHAAVTAGPGAWSSQQTWAADTVNGGNLTGYFYWPASQPTTPNGKRALVLVLHGCLQTASGDVIDNANGAGFNWKTIAEQYGAVVLAPNATGNVYSNHCWDYANTSPSRTSGHVGVLLDLVNRFVTNSQYAIDPNQVYVAGLSSGGGMTMVLGCIAPDIFAGIGINAGPPPAITRWKIGVVPSGYTATTAANNCKAWAGSNASSFNTQIAGAVWGTSDYTVAQAYGPMDTAAFRQIYGGTFTQGAQVSISGGGTNTPYTDSNGKLRTHEISVSGMAHAWPAGTGGDNNNYVDATHINYPAFVMDYWVKNNLRAGSGPVQSAGTPTGLTVTGTTTTSVSLSWNAVTNATSYNVYRNGSKVGSSTSTTYTDTGLIAGTTYSYTVTEIDPTAGESAQSSAVSAKTQSSFACTATTASNYAHVQAGRAHDSGGIAYANGSNQSMGLDNVFYTNTLAQTAAGYYVIGNCP	1994.0						Soil	Soil	Japan	Yes		
Pseudomonas fluorescens	294	PHO	Schirmer, A., & Jendrossek, D. (1994). Molecular characterization of the extracellular poly (3-hydroxyoctanoic acid)[P (3HO)] depolymerase gene of Pseudomonas fluorescens GK13 and of its gene product. Journal of bacteriology, 176(22), 7065-7073.	PHA depolymerase	00002	00002 | PHA depolymerase | Pseudomonas fluorescens | PHO PHA	Yes	AAA64538.1	MPLRTLLCGLLLAVCLGQHALAASRCSERPRTLLRPAEVSCSYQSTWLDSGLVGQRKIIYQTPLGTPPAGGWPVVLIYQGSFFPLNDFSYHSNLPFGGYYEGKLVQNLLDHGYAVIAPSAPADLFWQTNIPGLAQAYELSTDYDFLGNVLAAIASGHFGPLNAQRQYATGISSGGYNTSRMAVSFPGKFRALAVQSGSYATCSGPLCVVPDQLPADHPPTLFLHGFVDAVVPWWSMDLYYDRLLHQGIETARYTEPLGGHEWFAASPGKVLAWFNAHP	1994.0	Clear zone;Spectrophotometry	 P(3HO) was isolated from P. oleovorans grown in minimal medium with sodium octanoate (0.75%, wtlvol) as the carbon source		Yes	No				Yes		
Pseudomonas fluorescens	294	PHA	Schirmer, A., & Jendrossek, D. (1994). Molecular characterization of the extracellular poly (3-hydroxyoctanoic acid)[P (3HO)] depolymerase gene of Pseudomonas fluorescens GK13 and of its gene product. Journal of bacteriology, 176(22), 7065-7073.	PHA depolymerase	00002	00002 | PHA depolymerase | Pseudomonas fluorescens | PHO PHA	Yes	AAA64538.1	MPLRTLLCGLLLAVCLGQHALAASRCSERPRTLLRPAEVSCSYQSTWLDSGLVGQRKIIYQTPLGTPPAGGWPVVLIYQGSFFPLNDFSYHSNLPFGGYYEGKLVQNLLDHGYAVIAPSAPADLFWQTNIPGLAQAYELSTDYDFLGNVLAAIASGHFGPLNAQRQYATGISSGGYNTSRMAVSFPGKFRALAVQSGSYATCSGPLCVVPDQLPADHPPTLFLHGFVDAVVPWWSMDLYYDRLLHQGIETARYTEPLGGHEWFAASPGKVLAWFNAHP	1994.0	Clear zone;Spectrophotometry	 P(3HO) was isolated from P. oleovorans grown in minimal medium with sodium octanoate (0.75%, wtlvol) as the carbon source		Yes	No				Yes		
Paucimonas lemoignei	29443	PHB	Jendrossek, D. I. E. T. E. R., Frisse, A. N. D. R. E. A., Behrends, A. S. T. R. I. D., Andermann, M. E. I. K. E., Kratzin, H. D., Stanislawski, T. H. O. M. A. S., & Schlegel, H. G. (1995). Biochemical and molecular characterization of the Pseudomonas lemoignei polyhydroxyalkanoate depolymerase system. Journal of Bacteriology, 177(3), 596-607.	PHB depolymerase A	00003	00003 | PHB depolymerase-A | Paucimonas lemoignei | PHB PHA	Yes	AAA65705.1	MRNTLKAAFKLGVISAALLAPFATQAATAGPGAWSSQQTWAADSVNGGNLTGFYYWPATQPVHANGKRALVLVLHGCAQTASGDVINNGDNGYNWKAAADQYGAVILAPNATGNVSSQHCWDYSRTSHSRSTGHEYVLLDLINRFKNDPQYEIDPNQVYVTGLSSGGGETIVLGCIAPDVFAGWASNAGPTPGTTTLQIGAVPSGYTATNAKNNCLSLAGSNSSYFSTQIAGVVWGTSDFTVAPGYNPLMMDAMRQIYGGTFTKQASTSVATGGTNTTYKDSSGRVRTHELSVSGMSHAWPAGTGGQNTNYVTSQYVNYPLFVMDYFFTNNSRAGSGGGTTTTTAGGTTTTTAAGTTTTAATTTTTASSTTTTVAATCYTSSNYAHVTAGRAHNSSGYALANGSNQNMGLNNTFYTSTLKQTSPGYYVIGTCP	1995.0	Clear zone	The homopolyester PHB was isolated from sodium gluconate-grown cells of A. eutrophus H16 (51), by the sodium hypochlorite method as described previously (26, 36).		Yes	No	Culture collection	Culture collection		No		
Paucimonas lemoignei	29443	PHA	Jendrossek, D. I. E. T. E. R., Frisse, A. N. D. R. E. A., Behrends, A. S. T. R. I. D., Andermann, M. E. I. K. E., Kratzin, H. D., Stanislawski, T. H. O. M. A. S., & Schlegel, H. G. (1995). Biochemical and molecular characterization of the Pseudomonas lemoignei polyhydroxyalkanoate depolymerase system. Journal of Bacteriology, 177(3), 596-607.	PHB depolymerase A	00003	00003 | PHB depolymerase-A | Paucimonas lemoignei | PHB PHA	Yes	AAA65705.1	MRNTLKAAFKLGVISAALLAPFATQAATAGPGAWSSQQTWAADSVNGGNLTGFYYWPATQPVHANGKRALVLVLHGCAQTASGDVINNGDNGYNWKAAADQYGAVILAPNATGNVSSQHCWDYSRTSHSRSTGHEYVLLDLINRFKNDPQYEIDPNQVYVTGLSSGGGETIVLGCIAPDVFAGWASNAGPTPGTTTLQIGAVPSGYTATNAKNNCLSLAGSNSSYFSTQIAGVVWGTSDFTVAPGYNPLMMDAMRQIYGGTFTKQASTSVATGGTNTTYKDSSGRVRTHELSVSGMSHAWPAGTGGQNTNYVTSQYVNYPLFVMDYFFTNNSRAGSGGGTTTTTAGGTTTTTAAGTTTTAATTTTTASSTTTTVAATCYTSSNYAHVTAGRAHNSSGYALANGSNQNMGLNNTFYTSTLKQTSPGYYVIGTCP	1995.0	Clear zone	The homopolyester PHB was isolated from sodium gluconate-grown cells of A. eutrophus H16 (51), by the sodium hypochlorite method as described previously (26, 36).		Yes	No	Culture collection	Culture collection		No		
Paucimonas lemoignei	29443	PHB	Jendrossek, D. I. E. T. E. R., Frisse, A. N. D. R. E. A., Behrends, A. S. T. R. I. D., Andermann, M. E. I. K. E., Kratzin, H. D., Stanislawski, T. H. O. M. A. S., & Schlegel, H. G. (1995). Biochemical and molecular characterization of the Pseudomonas lemoignei polyhydroxyalkanoate depolymerase system. Journal of Bacteriology, 177(3), 596-607.	PHB-depolymerase	00004	00004 | PHB depolymerase | Paucimonas lemoignei | PHB PHA	Yes	WP_132258119.1	MLAKQIKKANSRSTLLRKSLLFAAPIILAVSSSSVYALTQVSNFGTNPGNLQMFKHVPSGMPANAPLVVALHGCTQTAAAYEASGWSALGNTHKFYVVYPQQQSGNNSNKCFNWFEPGDITRGQGEALSIKQMVDNMKANHSIDPSRVYVTGLSAGAFMTTVMAATYPDVFAGAAPIAGGPYKCATSMTSAFTCMSPGVDKTPAAWGDLARGGYSGYNGPKPKISIWHGSSDYTVAPANQNETVEQFTNYHGIDQTPDVSDTVGGFPHKVYKSANGTPLVETYTITGMGHGTPVDPGTGANQCGTAGAYILDVNVCSSYYIGQFFGIIGGGGTTTTTTSGNVTTTTAATTTTTTATQGYTQTTSATVTNHYVAGRINVTQYNVLGARYGYVTTIPLYYCPSLSGWTDKANCSPI	1995.0	Clear zone	The homopolyester PHB was isolated from sodium gluconate-grown cells of A. eutrophus H16 (51), by the sodium hypochlorite method as described previously (26, 36).		Yes	No	Culture collection	Culture collection		No		
Paucimonas lemoignei	29443	PHA	Jendrossek, D. I. E. T. E. R., Frisse, A. N. D. R. E. A., Behrends, A. S. T. R. I. D., Andermann, M. E. I. K. E., Kratzin, H. D., Stanislawski, T. H. O. M. A. S., & Schlegel, H. G. (1995). Biochemical and molecular characterization of the Pseudomonas lemoignei polyhydroxyalkanoate depolymerase system. Journal of Bacteriology, 177(3), 596-607.	PHB-depolymerase	00004	00004 | PHB depolymerase | Paucimonas lemoignei | PHB PHA	Yes	WP_132258119.1	MLAKQIKKANSRSTLLRKSLLFAAPIILAVSSSSVYALTQVSNFGTNPGNLQMFKHVPSGMPANAPLVVALHGCTQTAAAYEASGWSALGNTHKFYVVYPQQQSGNNSNKCFNWFEPGDITRGQGEALSIKQMVDNMKANHSIDPSRVYVTGLSAGAFMTTVMAATYPDVFAGAAPIAGGPYKCATSMTSAFTCMSPGVDKTPAAWGDLARGGYSGYNGPKPKISIWHGSSDYTVAPANQNETVEQFTNYHGIDQTPDVSDTVGGFPHKVYKSANGTPLVETYTITGMGHGTPVDPGTGANQCGTAGAYILDVNVCSSYYIGQFFGIIGGGGTTTTTTSGNVTTTTAATTTTTTATQGYTQTTSATVTNHYVAGRINVTQYNVLGARYGYVTTIPLYYCPSLSGWTDKANCSPI	1995.0	Clear zone	The homopolyester PHB was isolated from sodium gluconate-grown cells of A. eutrophus H16 (51), by the sodium hypochlorite method as described previously (26, 36).		Yes	No	Culture collection	Culture collection		No		
Paucimonas lemoignei	29443	PHB	Jendrossek, D. I. E. T. E. R., Frisse, A. N. D. R. E. A., Behrends, A. S. T. R. I. D., Andermann, M. E. I. K. E., Kratzin, H. D., Stanislawski, T. H. O. M. A. S., & Schlegel, H. G. (1995). Biochemical and molecular characterization of the Pseudomonas lemoignei polyhydroxyalkanoate depolymerase system. Journal of Bacteriology, 177(3), 596-607.	PHA depolymerase B	00005	00005 | PHA depolymerase B | Paucimonas lemoignei | PHB PHA	Yes	AAB17150.1	MMSSQTTQSSKFSLFLKRGLLLAAAPLLAMSASSALAATQVTGFGSNPGNLLMYKHVPSSMPANAPLVIAMHGCTQSASAYEATGWTQLANTYKFYVVYPEQQSSNNQNKCFNWFEPGDIARGQGEALSIKQMVDKMKADHSIDTNRVYVTGLSAGGYMVNVMLATYPDVFAGGAPFSGGPYNCATSMTNAFTCMSPGVDKTPAAWGDLARGGYSGYTGRKPIVSIWHGDADYTVKQSNQVEEVEQWTNYHGIDQTADVSDTVAGFPHKVYKDASGNALVETYTITGMGHGTPVDPGTGSLQCGTAGAYILDVNICSSYYVAKFWGLIGGSGTTTTTSAGTTTTTSAGTTTTKASTTTTKVSTTTTASTTTTTAGACYNSSNYAHVTAGRAHDTGGYAYTNGSNQKMGLNNTFYTSKLRKTGTNYYVIDTTCP	1995.0	Clear zone	The homopolyester PHB was isolated from sodium gluconate-grown cells of A. eutrophus H16 (51), by the sodium hypochlorite method as described previously (26, 36).		Yes	No	Culture collection	Culture collection		No		
Paucimonas lemoignei	29443	PHA	Jendrossek, D. I. E. T. E. R., Frisse, A. N. D. R. E. A., Behrends, A. S. T. R. I. D., Andermann, M. E. I. K. E., Kratzin, H. D., Stanislawski, T. H. O. M. A. S., & Schlegel, H. G. (1995). Biochemical and molecular characterization of the Pseudomonas lemoignei polyhydroxyalkanoate depolymerase system. Journal of Bacteriology, 177(3), 596-607.	PHA depolymerase B	00005	00005 | PHA depolymerase B | Paucimonas lemoignei | PHB PHA	Yes	AAB17150.1	MMSSQTTQSSKFSLFLKRGLLLAAAPLLAMSASSALAATQVTGFGSNPGNLLMYKHVPSSMPANAPLVIAMHGCTQSASAYEATGWTQLANTYKFYVVYPEQQSSNNQNKCFNWFEPGDIARGQGEALSIKQMVDKMKADHSIDTNRVYVTGLSAGGYMVNVMLATYPDVFAGGAPFSGGPYNCATSMTNAFTCMSPGVDKTPAAWGDLARGGYSGYTGRKPIVSIWHGDADYTVKQSNQVEEVEQWTNYHGIDQTADVSDTVAGFPHKVYKDASGNALVETYTITGMGHGTPVDPGTGSLQCGTAGAYILDVNICSSYYVAKFWGLIGGSGTTTTTSAGTTTTTSAGTTTTKASTTTTKVSTTTTASTTTTTAGACYNSSNYAHVTAGRAHDTGGYAYTNGSNQKMGLNNTFYTSKLRKTGTNYYVIDTTCP	1995.0	Clear zone	The homopolyester PHB was isolated from sodium gluconate-grown cells of A. eutrophus H16 (51), by the sodium hypochlorite method as described previously (26, 36).		Yes	No	Culture collection	Culture collection		No		
Paucimonas lemoignei	29443	PHB	Jendrossek, D. I. E. T. E. R., Frisse, A. N. D. R. E. A., Behrends, A. S. T. R. I. D., Andermann, M. E. I. K. E., Kratzin, H. D., Stanislawski, T. H. O. M. A. S., & Schlegel, H. G. (1995). Biochemical and molecular characterization of the Pseudomonas lemoignei polyhydroxyalkanoate depolymerase system. Journal of Bacteriology, 177(3), 596-607.	PHB depolymerase	00006	00006 | PHB depolymerase | Paucimonas lemoignei | PHB PHA	Yes	WP_132257894.1	MQLKKSLRVTIAVLLGAGVSASAFALTPGSGTWVKESATYGTPNLQDAYLYVPKNPAPQVLGGKRALMLSLHGCGQTASTSVIDKRFNWEETAEKYGMVVVAPTVPTGTSSTRAASGCWDWFGTAHNRTTRDVVPLIKLIDAVKARTNLDIDPNQIYVSGLSAGAGETHVLGCSFPDYFAGVAPNASPSLGSAAGDISVPPKRTPQQVADMCRAINGNQFNAHLDTQIFATVYGDKDYLVLPAHNEVNRDGMKIAYDATVSAGTASVDGGGTASLFKDSRGRLRISSMVVAGMSHAWPSGPGAAPYIAWVDSTRVNYPAYVTQFFFENNLRVNKWKITCSVNVPNASSATVSASATAAAGATVASYRVALQGKTAINDNAAGSGTSLNKSYNLGNGIYAGTVTAVDSKGVESEACQLSSFQVGQLDPLYPPSDIQATGISSSSIKLNWSAVSSATAYDVRRNGGAPVRVTATQYTDTGLAPDTSYSYTVTSVNDNMTSGQSGQIIGKTQPVTYTEKVTATVTGHYSAGRINVNQYLQLGAKYGYNASLTLYKCEGVWTNSSSCGPLQ	1995.0	Clear zone	The homopolyester PHB was isolated from sodium gluconate-grown cells of A. eutrophus H16 (51), by the sodium hypochlorite method as described previously (26, 36).		Yes	No	Culture collection	Culture collection		No		
Paucimonas lemoignei	29443	PHA	Jendrossek, D. I. E. T. E. R., Frisse, A. N. D. R. E. A., Behrends, A. S. T. R. I. D., Andermann, M. E. I. K. E., Kratzin, H. D., Stanislawski, T. H. O. M. A. S., & Schlegel, H. G. (1995). Biochemical and molecular characterization of the Pseudomonas lemoignei polyhydroxyalkanoate depolymerase system. Journal of Bacteriology, 177(3), 596-607.	PHB depolymerase	00006	00006 | PHB depolymerase | Paucimonas lemoignei | PHB PHA	Yes	WP_132257894.1	MQLKKSLRVTIAVLLGAGVSASAFALTPGSGTWVKESATYGTPNLQDAYLYVPKNPAPQVLGGKRALMLSLHGCGQTASTSVIDKRFNWEETAEKYGMVVVAPTVPTGTSSTRAASGCWDWFGTAHNRTTRDVVPLIKLIDAVKARTNLDIDPNQIYVSGLSAGAGETHVLGCSFPDYFAGVAPNASPSLGSAAGDISVPPKRTPQQVADMCRAINGNQFNAHLDTQIFATVYGDKDYLVLPAHNEVNRDGMKIAYDATVSAGTASVDGGGTASLFKDSRGRLRISSMVVAGMSHAWPSGPGAAPYIAWVDSTRVNYPAYVTQFFFENNLRVNKWKITCSVNVPNASSATVSASATAAAGATVASYRVALQGKTAINDNAAGSGTSLNKSYNLGNGIYAGTVTAVDSKGVESEACQLSSFQVGQLDPLYPPSDIQATGISSSSIKLNWSAVSSATAYDVRRNGGAPVRVTATQYTDTGLAPDTSYSYTVTSVNDNMTSGQSGQIIGKTQPVTYTEKVTATVTGHYSAGRINVNQYLQLGAKYGYNASLTLYKCEGVWTNSSSCGPLQ	1995.0	Clear zone	The homopolyester PHB was isolated from sodium gluconate-grown cells of A. eutrophus H16 (51), by the sodium hypochlorite method as described previously (26, 36).		Yes	No	Culture collection	Culture collection		No		
Paucimonas lemoignei	29443	PHB	Jendrossek, D. I. E. T. E. R., Frisse, A. N. D. R. E. A., Behrends, A. S. T. R. I. D., Andermann, M. E. I. K. E., Kratzin, H. D., Stanislawski, T. H. O. M. A. S., & Schlegel, H. G. (1995). Biochemical and molecular characterization of the Pseudomonas lemoignei polyhydroxyalkanoate depolymerase system. Journal of Bacteriology, 177(3), 596-607.	PHB depolymerase	00007	00007 | PHB depolymerase | Paucimonas lemoignei | PHB PHA	Yes	WP_132256575.1	MNKYLKNLCFAAATVTLMASAPSAFALSEVTGFGTNPGALKMFKHVPTSMPTNAPLIVAMHGCTQSASAYEGSGWSALANNYKFYVVYPEQQSGNNSNKCFNWFESGDIARGQGEALSIKQMVDKMKADYSIDANRVYVTGLSAGAFMTAVMAATYPDVFAGAAPIAGGPYKCATSMIDAFSCMSPGTDKTPAAWGDLARGGYSGYNGRKPKISVWQGSSDTTVKPMNMDELMQQWTNYHGIDQTADVSETVKGFPHKVYKDASGNALVETWSITGMAHGTPVDPGTGAEQCGTSGSYILDVNICSSYHIAQFFGLTGAGTTTTTTVGSTSTTTGYTSTSSAPVTTTTSVASTTTTTVAAGACYNASNYAHVTAGRAVNSMGYAKAKGSNQNMGLYNTFTTSKLREAPAGYFTIDSTCP	1995.0	Clear zone	The homopolyester PHB was isolated from sodium gluconate-grown cells of A. eutrophus H16 (51), by the sodium hypochlorite method as described previously (26, 36).		Yes	No	Culture collection	Culture collection		No		
Paucimonas lemoignei	29443	PHA	Jendrossek, D. I. E. T. E. R., Frisse, A. N. D. R. E. A., Behrends, A. S. T. R. I. D., Andermann, M. E. I. K. E., Kratzin, H. D., Stanislawski, T. H. O. M. A. S., & Schlegel, H. G. (1995). Biochemical and molecular characterization of the Pseudomonas lemoignei polyhydroxyalkanoate depolymerase system. Journal of Bacteriology, 177(3), 596-607.	PHB depolymerase	00007	00007 | PHB depolymerase | Paucimonas lemoignei | PHB PHA	Yes	WP_132256575.1	MNKYLKNLCFAAATVTLMASAPSAFALSEVTGFGTNPGALKMFKHVPTSMPTNAPLIVAMHGCTQSASAYEGSGWSALANNYKFYVVYPEQQSGNNSNKCFNWFESGDIARGQGEALSIKQMVDKMKADYSIDANRVYVTGLSAGAFMTAVMAATYPDVFAGAAPIAGGPYKCATSMIDAFSCMSPGTDKTPAAWGDLARGGYSGYNGRKPKISVWQGSSDTTVKPMNMDELMQQWTNYHGIDQTADVSETVKGFPHKVYKDASGNALVETWSITGMAHGTPVDPGTGAEQCGTSGSYILDVNICSSYHIAQFFGLTGAGTTTTTTVGSTSTTTGYTSTSSAPVTTTTSVASTTTTTVAAGACYNASNYAHVTAGRAVNSMGYAKAKGSNQNMGLYNTFTTSKLREAPAGYFTIDSTCP	1995.0	Clear zone	The homopolyester PHB was isolated from sodium gluconate-grown cells of A. eutrophus H16 (51), by the sodium hypochlorite method as described previously (26, 36).		Yes	No	Culture collection	Culture collection		No		
Fusarium verticillioides	117187	PCL	Murphy, C. A., Cameron, J. A., Huang, S. J., & Vinopal, R. T. (1996). Fusarium polycaprolactone depolymerase is cutinase. Appl. Environ. Microbiol., 62(2), 456-460.	Cutinase	00008	00008 | Cutinase | Fusarium verticillioides | PCL	Yes	Q96UT0.1	MKFFALTTLLAATASALPTSHPVQELEARQLGGGTTRNDLTNGNSASCADVIFIYARGSTETGNLGTLGPSIASKLESAFGRDGVWIQGVGGAYRATLGDNSLPRGTSSAAIREMLGLFQQANTKCPDATLIAGGYSQGAALGAASVEDLDSAIRDKIAGTVLFGYTKNLQNHGRIPNFPADRTKVFCNTGDLVCTGSLIIAAPHLTYGPDARGPAPEFLIEKVRAVRGSA	1996.0	Clear zone	PCL with a molecular weight of approximately 10,000 was used.	Cellomer Associates		No	Culture collection	Culture collection		No		
Fusarium verticillioides	117187	PCL	Murphy, C. A., Cameron, J. A., Huang, S. J., & Vinopal, R. T. (1996). Fusarium polycaprolactone depolymerase is cutinase. Appl. Environ. Microbiol., 62(2), 456-460.	Cutinase	00009	00009 | Cutinase | Fusarium verticillioides | PCL	Yes	Q96US9.1	MKFFALTTLLAATDSALPTSHPVQELEARQLGGGTTRNDLTNGNSASCADVIFIYARGSTETGNLGTLGPSIASKLESAFGRDGVWIQGVGGAYRATLGDNSLPRGTSSAAIREMLGLFQQPNTKCPDATLIAGGYSQGAALAAASVEDLDSAIRDKIAGTVLFGYTKNLQNHGRIPNFPADRTKVFCNTGDLVCTGSLIIAAPHLTYGPDARGPAPEFLIEKVRAVRGSA	1996.0	Clear zone;Spectrophotometry	PCL (Cellomer Associates, Inc., Webster, N.Y.) with a molecular weight of approximately 10,000 was used.	Cellomer Associates	Yes	No	Culture collection	Culture collection		No		
Pseudomonas sp.	306	PVA	SHIMAO, M., TAMOGAMI, T., NISHI, K., & HARAYAMA, S. (1996). Cloning and characterization of the gene encoding pyrroloquinoline quinone-dependent poly (vinyl alcohol) dehydrogenase of Pseudomonas sp. strain VM15C. Bioscience, biotechnology, and biochemistry, 60(7), 1056-1062.	PVA dehydrogenase	00010	00010 | PVA dehydrogenase | Pseudomonas sp. | PVA	Yes	BAA09321.1	MQQNIERNQVSMTTSRFVWGAVMALVALGSASAAELNLPDGAALYRARCGTCHDNPQDRTPARDVIARNSPAFIMAAMNGVMAPMAAGLSEAEKQAIALHLGARPAGGSQEINPHAIWGPPSASMPLDGPKCKGKIPPIDLSTPDQWNGWGAGITNARFQPNPGLTAADVPRLKVKWAFNYPGSKNGQATVVGDRLFVTSMSGAVYALNAKTGCVYWRHDAAAATRSSVHVVQLPAGAPAQYAIFFSDWTKAAVALDAQTGKQLWKTTIDDQPGVQMTGSPTYHEGKLFVPISSGNEAFATNDQWECCKFRGALVALDALSGKVLWKTYTTQKEPAPFRLNKLGKQMWGPAGGSIWSAPTIDPKRGLVYVATSNSYTEVHHEGSDAVMAMEIETGKVRWINQVTKDDNYIIGCPRAANCPEKVGPDFALGNSPILHTLQDGRQYIVVGQKSGAVYAMDPDNDGELIWMRRVSPGSELGGVEFGMAADAENVYVGISDVITRKGGKPGVYALRIRDGADVWAFPAPRTPCRWNNIFCHPAVSQAVTAMPGVVFAGSMDGHFRAFSTSDGKVLWEFNTAAAPYKTVAGKQADGGVMDGAGPTIAGGMVYVHSGYAGRSTQNAGDLRGREGNVLIAFSVDGK	1996.0	Spectrophotometry	PVA500 and PVA1500	Wako Pure Chemical	Yes	No				Yes		
Comamonas acidovorans	80866	PHB	Kasuya, K. I., Inoue, Y., Tanaka, T., Akehata, T., Iwata, T., Fukui, T., & Doi, Y. (1997). Biochemical and molecular characterization of the polyhydroxybutyrate depolymerase of Comamonas acidovorans YM1609, isolated from freshwater. Appl. Environ. Microbiol., 63(12), 4844-4852.	PHB-depolymerase	00011	00011 | PHB depolymerase | Comamonas acidovorans | PHB PHA	Yes	BAA19791.1	MAFNFIRAAAAGAAMALCGVGSVHAAVNLPALKIDKTQTTVSGLSSGGFMAVQLHVAYSATFAKGAGVVAGGPFYCAEGSIVNATGRCMASPAGIPTSTLVSTTNTWASQGVIDPVANLQNSKVYLFSGTLDSVVKTGVMDALRTYYNSFVPAANVVYKKDIAAEHAMVTDDYGNACSTKGAPYISDCNFDLAGAMLQHLYGTLNARNNATLPTGNYIEFNQSEFITNHGMATTGWAYVPQACQAGGTATCKLHVVLHGCKQNIGDVQQQYVRNTGYNRWADTNNIVMLYPQTSTAATNSCWDWWGYDSANYSKKSGPQMAAIKAMVDRVSSGTGGTTPPDPVALPAPTGVSTSGATASSMAIGWAAVMGAASYNVYRNANKVNALPVTATSYTDTGLAASTTYSWTVRAADANGAEGATSAAASGTTLAASGGGTATCTTASNYAHTLAGRAYAAGGYTYALGSNQNMGLWNVFVTNTLKQTSTNYYVIGTCP	1997.0	Spectrophotometry;HPLC	P(3HB) was produced by Ralstonia eutropha			No	Freshwater	River/Lake	Japan	No		
Comamonas acidovorans	80866	PHA	Kasuya, K. I., Inoue, Y., Tanaka, T., Akehata, T., Iwata, T., Fukui, T., & Doi, Y. (1997). Biochemical and molecular characterization of the polyhydroxybutyrate depolymerase of Comamonas acidovorans YM1609, isolated from freshwater. Appl. Environ. Microbiol., 63(12), 4844-4852.	PHB-depolymerase	00011	00011 | PHB depolymerase | Comamonas acidovorans | PHB PHA	Yes	BAA19791.1	MAFNFIRAAAAGAAMALCGVGSVHAAVNLPALKIDKTQTTVSGLSSGGFMAVQLHVAYSATFAKGAGVVAGGPFYCAEGSIVNATGRCMASPAGIPTSTLVSTTNTWASQGVIDPVANLQNSKVYLFSGTLDSVVKTGVMDALRTYYNSFVPAANVVYKKDIAAEHAMVTDDYGNACSTKGAPYISDCNFDLAGAMLQHLYGTLNARNNATLPTGNYIEFNQSEFITNHGMATTGWAYVPQACQAGGTATCKLHVVLHGCKQNIGDVQQQYVRNTGYNRWADTNNIVMLYPQTSTAATNSCWDWWGYDSANYSKKSGPQMAAIKAMVDRVSSGTGGTTPPDPVALPAPTGVSTSGATASSMAIGWAAVMGAASYNVYRNANKVNALPVTATSYTDTGLAASTTYSWTVRAADANGAEGATSAAASGTTLAASGGGTATCTTASNYAHTLAGRAYAAGGYTYALGSNQNMGLWNVFVTNTLKQTSTNYYVIGTCP	1997.0	Spectrophotometry;HPLC	P(3HB) was produced by Ralstonia eutropha			No	Freshwater	River/Lake	Japan	No		
Alcaligenes faecalis	511	PHB	Kita, K., Mashiba, S. I., Nagita, M., Ishimaru, K., Okamoto, K., Yanase, H., & Kato, N. (1997). Cloning of poly (3-hydroxybutyrate) depolymerase from a marine bacterium, Alcaligenes faecalis AE122, and characterization of its gene product. Biochimica et Biophysica Acta (BBA)-Gene Structure and Expression, 1352(1), 113-122.	PHB-depolymerase	00012	00012 | PHB depolymerase | Alcaligenes faecalis | PHB PHA	Yes	AAB40611.1	MTSRPMRSLVIAFLTLVAAAAPALAGAGAWQNNLSLGGFNKVHLYTPDGDSPVGNGKALLIVLHGCTQSIDAYKTANLEVAAEEYGMVVAVPDAMNKAGFSCWSYWQGTKSRSAGDYKNLINLANTLSGDAARGIDPNQVYIAGLSSGASFANTTACLAPDVFAGVGVSAGPSVGTSSSGAIGTCEQADVESRCRDLGGGYQSAFDTQVASIAHGDADTTVDTCYNRQNAEGMAGLYGVSEVAGSTVINADGGSAEEFLWQDGRVSMLWFHGLDHSWSGGQGASGSYVSGASINYARYLGGFFAEHNARIDRNRVPTLAQVDVTASADRIQVSGQASDEDGTVSSVAIVIEGVNGGGATLAAAIDNNGYFQATSDPLADGLYTVAVTAADDDGGESEPAIRTVRVGPEPPASAPVLSDIAVSVDGQCATVSGQVVDENQDLAGVTVTFASGVRAAGIDGVRYSARACDLPGGAQNATVSAEDEGGLSSGDQIDFVIDAGQTATLDQHISAGRLDYTNYADCYLEYGADAFKLTEATVSGQCQWQDDDASCAGPVQACSGAGGGGDPQPQPGDECQTQSTYNYYHKVAGRAYSTGNYYAPDYFAQGSDEPMAGSTWGLTALYSEDGGNVWRLGECP	1997.0	GC	PHB	Sigma Aldrich	Yes	No	Seawater	Soil	Japan	No		
Alcaligenes faecalis	511	PHA	Kita, K., Mashiba, S. I., Nagita, M., Ishimaru, K., Okamoto, K., Yanase, H., & Kato, N. (1997). Cloning of poly (3-hydroxybutyrate) depolymerase from a marine bacterium, Alcaligenes faecalis AE122, and characterization of its gene product. Biochimica et Biophysica Acta (BBA)-Gene Structure and Expression, 1352(1), 113-122.	PHB-depolymerase	00012	00012 | PHB depolymerase | Alcaligenes faecalis | PHB PHA	Yes	AAB40611.1	MTSRPMRSLVIAFLTLVAAAAPALAGAGAWQNNLSLGGFNKVHLYTPDGDSPVGNGKALLIVLHGCTQSIDAYKTANLEVAAEEYGMVVAVPDAMNKAGFSCWSYWQGTKSRSAGDYKNLINLANTLSGDAARGIDPNQVYIAGLSSGASFANTTACLAPDVFAGVGVSAGPSVGTSSSGAIGTCEQADVESRCRDLGGGYQSAFDTQVASIAHGDADTTVDTCYNRQNAEGMAGLYGVSEVAGSTVINADGGSAEEFLWQDGRVSMLWFHGLDHSWSGGQGASGSYVSGASINYARYLGGFFAEHNARIDRNRVPTLAQVDVTASADRIQVSGQASDEDGTVSSVAIVIEGVNGGGATLAAAIDNNGYFQATSDPLADGLYTVAVTAADDDGGESEPAIRTVRVGPEPPASAPVLSDIAVSVDGQCATVSGQVVDENQDLAGVTVTFASGVRAAGIDGVRYSARACDLPGGAQNATVSAEDEGGLSSGDQIDFVIDAGQTATLDQHISAGRLDYTNYADCYLEYGADAFKLTEATVSGQCQWQDDDASCAGPVQACSGAGGGGDPQPQPGDECQTQSTYNYYHKVAGRAYSTGNYYAPDYFAQGSDEPMAGSTWGLTALYSEDGGNVWRLGECP	1997.0	GC	PHB	Sigma Aldrich	Yes	No	Seawater	Soil	Japan	No		
Comamonas acidovorans	80866	PU	Nomura, N., Shigeno-Akutsu, Y., Nakajima-Kambe, T., & Nakahara, T. (1998). Cloning and sequence analysis of a polyurethane esterase of Comamonas acidovorans TB-35. Journal of fermentation and bioengineering, 86(4), 339-345.	PU-esterase 	00013	00013 | PU esterase  | Comamonas acidovorans | PU	Yes	BAA76305.1	MNSRSLTKAIRFPTILALAGFSVLGACGGSDNDSSSNNQGAPAVAITVAGQVQAVDRLGMRRYFGIPFAAPPVGNLRWMPPAPPQSWAAPLAKTQSNAPCMQTGATDPLRLPNGTEDCLYLDVHAPATGEGPFPVMVWIHGGAFSIGGTITYADPSPLVSKGVIVVNIAYRMGAMGFLGHPSLRAADGTVGNYGIMDQQAALRWVQDNIAAFGGDKSNVTIFGESAGGFSVMTHLASPLSKGLFAKAIVQSGGYGFDRQLTQAQLEAQSTSIVNSALAAAGVSCPTVDAACLRGLSAELVNNQLATAFTTANWSPVPSVDGKVLPKSIKATFVAGENNKVPLVNGSNQDEWSYFVASRELVAGPLTAAQYPSYLQTSLGLPPSLATVYPLTDYGTNTAQQPSLAATAAGTDMHFSCPALNLSKRVLSQATPIFMYEFRDRTAIPSIGRNTISFNQGAGHTYELQYLFNLRDLETAEHRDLQASMARYWTNFARTSNPNNGDPVATSWPAFTGPTKVLGLDVASAGGIRELATFETDHKCNTAWTSLTF	1998.0	GC	The polyester polyurethane (PUR) usedin this study was synthesized by the condensation of poly(diethylene glycol adipate) (DEGA) and 2,4-tolylene diisocyanate under anhydrous conditions as described previously (6, 7). 		Yes	No				No		
Acidovorax sp.	1872122	PHB	Kobayashi, T., Sugiyama, A., Kawase, Y., Saito, T., Mergaert, J., & Swings, J. (1999). Biochemical and genetic characterization of an extracellular poly (3-hydroxybutyrate) depolymerase from Acidovorax sp. strain TP4. Journal of environmental polymer degradation, 7(1), 9-18.	PHB depolymerase	00014	00014 | PHB depolymerase | Acidovorax sp. | PHB PPL PHA	Yes	BAA35137.1	MAFNFIRAAAAGAAIALCGVASVHAAVNLPALKIDKTQTTVSGLSSGGFMAVQLHVAYSATFAKGVGVVAGGPFYCAEGSVVNATGRCMASPTGIPTSTLVNTTNTWAGQGVIDPVANLQNSKVYLFSGTLDSVVKTGVMDALRTYYNSFVPAANVVYKKDIASEHAMVTDDYGNGCSTKGAPYISDCNFDLAGAMLQHLYGTLNARNNATLPSGNFIEFNQSEFISNHGMATTGWAYVPQACQAGGTATCKLHVVLHGCKQNVNDVQQQYVRNTGYNRWADSNNIVMLYPQTSLAATNSCWDWWGYDSANYSKKSGPQMAAIKAMVDRVGSGGTTNPPVDLPAPTGVKPSGATASSMAIGWNAVSGGPSYNVYRNGNKTNALPVTATNFTDTGLAASTTYSWTVRAADGNGAEGAVSAAASGTTLAASGGGTGTCTTASNYAHTMAGRAYVYGGYTFALGSNQSMGLWNIFVNKTLKQTSPNYYVIGTCP	1999.0	Clear zone;Spectrophotometry	 Purified PHB granules for enzyme assays of PHB depolymerase were prepared as described by Smibert and Krieg			No			Japan	No		
Acidovorax sp.	1872122	PPL	Kobayashi, T., Sugiyama, A., Kawase, Y., Saito, T., Mergaert, J., & Swings, J. (1999). Biochemical and genetic characterization of an extracellular poly (3-hydroxybutyrate) depolymerase from Acidovorax sp. strain TP4. Journal of environmental polymer degradation, 7(1), 9-18.	PHB depolymerase	00014	00014 | PHB depolymerase | Acidovorax sp. | PHB PPL PHA	Yes	BAA35137.1	MAFNFIRAAAAGAAIALCGVASVHAAVNLPALKIDKTQTTVSGLSSGGFMAVQLHVAYSATFAKGVGVVAGGPFYCAEGSVVNATGRCMASPTGIPTSTLVNTTNTWAGQGVIDPVANLQNSKVYLFSGTLDSVVKTGVMDALRTYYNSFVPAANVVYKKDIASEHAMVTDDYGNGCSTKGAPYISDCNFDLAGAMLQHLYGTLNARNNATLPSGNFIEFNQSEFISNHGMATTGWAYVPQACQAGGTATCKLHVVLHGCKQNVNDVQQQYVRNTGYNRWADSNNIVMLYPQTSLAATNSCWDWWGYDSANYSKKSGPQMAAIKAMVDRVGSGGTTNPPVDLPAPTGVKPSGATASSMAIGWNAVSGGPSYNVYRNGNKTNALPVTATNFTDTGLAASTTYSWTVRAADGNGAEGAVSAAASGTTLAASGGGTGTCTTASNYAHTMAGRAYVYGGYTFALGSNQSMGLWNIFVNKTLKQTSPNYYVIGTCP	1999.0	Clear zone;Spectrophotometry	PPL (Lot No. EXP235-D; Mn = 119,000)	Tokuyama		No			Japan	No		
Acidovorax sp.	1872122	PHA	Kobayashi, T., Sugiyama, A., Kawase, Y., Saito, T., Mergaert, J., & Swings, J. (1999). Biochemical and genetic characterization of an extracellular poly (3-hydroxybutyrate) depolymerase from Acidovorax sp. strain TP4. Journal of environmental polymer degradation, 7(1), 9-18.	PHB depolymerase	00014	00014 | PHB depolymerase | Acidovorax sp. | PHB PPL PHA	Yes	BAA35137.1	MAFNFIRAAAAGAAIALCGVASVHAAVNLPALKIDKTQTTVSGLSSGGFMAVQLHVAYSATFAKGVGVVAGGPFYCAEGSVVNATGRCMASPTGIPTSTLVNTTNTWAGQGVIDPVANLQNSKVYLFSGTLDSVVKTGVMDALRTYYNSFVPAANVVYKKDIASEHAMVTDDYGNGCSTKGAPYISDCNFDLAGAMLQHLYGTLNARNNATLPSGNFIEFNQSEFISNHGMATTGWAYVPQACQAGGTATCKLHVVLHGCKQNVNDVQQQYVRNTGYNRWADSNNIVMLYPQTSLAATNSCWDWWGYDSANYSKKSGPQMAAIKAMVDRVGSGGTTNPPVDLPAPTGVKPSGATASSMAIGWNAVSGGPSYNVYRNGNKTNALPVTATNFTDTGLAASTTYSWTVRAADGNGAEGAVSAAASGTTLAASGGGTGTCTTASNYAHTMAGRAYVYGGYTFALGSNQSMGLWNIFVNKTLKQTSPNYYVIGTCP	1999.0	Clear zone;Spectrophotometry	PPL (Lot No. EXP235-D; Mn = 119,000)	Tokuyama		No			Japan	No		
Comamonas acidovorans	80866	P3HP	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00015	00015 | PHB depolymerase | Comamonas acidovorans | P3HP P4HB PEA PES PHB PHA	Yes	BAA19791.1	MAFNFIRAAAAGAAMALCGVGSVHAAVNLPALKIDKTQTTVSGLSSGGFMAVQLHVAYSATFAKGAGVVAGGPFYCAEGSIVNATGRCMASPAGIPTSTLVSTTNTWASQGVIDPVANLQNSKVYLFSGTLDSVVKTGVMDALRTYYNSFVPAANVVYKKDIAAEHAMVTDDYGNACSTKGAPYISDCNFDLAGAMLQHLYGTLNARNNATLPTGNYIEFNQSEFITNHGMATTGWAYVPQACQAGGTATCKLHVVLHGCKQNIGDVQQQYVRNTGYNRWADTNNIVMLYPQTSTAATNSCWDWWGYDSANYSKKSGPQMAAIKAMVDRVSSGTGGTTPPDPVALPAPTGVSTSGATASSMAIGWAAVMGAASYNVYRNANKVNALPVTATSYTDTGLAASTTYSWTVRAADANGAEGATSAAASGTTLAASGGGTATCTTASNYAHTLAGRAYAAGGYTYALGSNQNMGLWNVFVTNTLKQTSTNYYVIGTCP	1999.0	Weight loss	4HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.		Yes	No				Yes		
Comamonas acidovorans	80866	P4HB	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00015	00015 | PHB depolymerase | Comamonas acidovorans | P3HP P4HB PEA PES PHB PHA	Yes	BAA19791.1	MAFNFIRAAAAGAAMALCGVGSVHAAVNLPALKIDKTQTTVSGLSSGGFMAVQLHVAYSATFAKGAGVVAGGPFYCAEGSIVNATGRCMASPAGIPTSTLVSTTNTWASQGVIDPVANLQNSKVYLFSGTLDSVVKTGVMDALRTYYNSFVPAANVVYKKDIAAEHAMVTDDYGNACSTKGAPYISDCNFDLAGAMLQHLYGTLNARNNATLPTGNYIEFNQSEFITNHGMATTGWAYVPQACQAGGTATCKLHVVLHGCKQNIGDVQQQYVRNTGYNRWADTNNIVMLYPQTSTAATNSCWDWWGYDSANYSKKSGPQMAAIKAMVDRVSSGTGGTTPPDPVALPAPTGVSTSGATASSMAIGWAAVMGAASYNVYRNANKVNALPVTATSYTDTGLAASTTYSWTVRAADANGAEGATSAAASGTTLAASGGGTATCTTASNYAHTLAGRAYAAGGYTYALGSNQNMGLWNVFVTNTLKQTSTNYYVIGTCP	1999.0	Weight loss	5HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.		Yes	No				Yes		
Comamonas acidovorans	80866	PEA	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00015	00015 | PHB depolymerase | Comamonas acidovorans | P3HP P4HB PEA PES PHB PHA	Yes	BAA19791.1	MAFNFIRAAAAGAAMALCGVGSVHAAVNLPALKIDKTQTTVSGLSSGGFMAVQLHVAYSATFAKGAGVVAGGPFYCAEGSIVNATGRCMASPAGIPTSTLVSTTNTWASQGVIDPVANLQNSKVYLFSGTLDSVVKTGVMDALRTYYNSFVPAANVVYKKDIAAEHAMVTDDYGNACSTKGAPYISDCNFDLAGAMLQHLYGTLNARNNATLPTGNYIEFNQSEFITNHGMATTGWAYVPQACQAGGTATCKLHVVLHGCKQNIGDVQQQYVRNTGYNRWADTNNIVMLYPQTSTAATNSCWDWWGYDSANYSKKSGPQMAAIKAMVDRVSSGTGGTTPPDPVALPAPTGVSTSGATASSMAIGWAAVMGAASYNVYRNANKVNALPVTATSYTDTGLAASTTYSWTVRAADANGAEGATSAAASGTTLAASGGGTATCTTASNYAHTLAGRAYAAGGYTYALGSNQNMGLWNVFVTNTLKQTSTNYYVIGTCP	1999.0	Weight loss	7HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Showa Denko		No				Yes		
Comamonas acidovorans	80866	PES	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00015	00015 | PHB depolymerase | Comamonas acidovorans | P3HP P4HB PEA PES PHB PHA	Yes	BAA19791.1	MAFNFIRAAAAGAAMALCGVGSVHAAVNLPALKIDKTQTTVSGLSSGGFMAVQLHVAYSATFAKGAGVVAGGPFYCAEGSIVNATGRCMASPAGIPTSTLVSTTNTWASQGVIDPVANLQNSKVYLFSGTLDSVVKTGVMDALRTYYNSFVPAANVVYKKDIAAEHAMVTDDYGNACSTKGAPYISDCNFDLAGAMLQHLYGTLNARNNATLPTGNYIEFNQSEFITNHGMATTGWAYVPQACQAGGTATCKLHVVLHGCKQNIGDVQQQYVRNTGYNRWADTNNIVMLYPQTSTAATNSCWDWWGYDSANYSKKSGPQMAAIKAMVDRVSSGTGGTTPPDPVALPAPTGVSTSGATASSMAIGWAAVMGAASYNVYRNANKVNALPVTATSYTDTGLAASTTYSWTVRAADANGAEGATSAAASGTTLAASGGGTATCTTASNYAHTLAGRAYAAGGYTYALGSNQNMGLWNVFVTNTLKQTSTNYYVIGTCP	1999.0	Weight loss	6HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Showa Denko		No				Yes		
Comamonas acidovorans	80866	PHB	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00015	00015 | PHB depolymerase | Comamonas acidovorans | P3HP P4HB PEA PES PHB PHA	Yes	BAA19791.1	MAFNFIRAAAAGAAMALCGVGSVHAAVNLPALKIDKTQTTVSGLSSGGFMAVQLHVAYSATFAKGAGVVAGGPFYCAEGSIVNATGRCMASPAGIPTSTLVSTTNTWASQGVIDPVANLQNSKVYLFSGTLDSVVKTGVMDALRTYYNSFVPAANVVYKKDIAAEHAMVTDDYGNACSTKGAPYISDCNFDLAGAMLQHLYGTLNARNNATLPTGNYIEFNQSEFITNHGMATTGWAYVPQACQAGGTATCKLHVVLHGCKQNIGDVQQQYVRNTGYNRWADTNNIVMLYPQTSTAATNSCWDWWGYDSANYSKKSGPQMAAIKAMVDRVSSGTGGTTPPDPVALPAPTGVSTSGATASSMAIGWAAVMGAASYNVYRNANKVNALPVTATSYTDTGLAASTTYSWTVRAADANGAEGATSAAASGTTLAASGGGTATCTTASNYAHTLAGRAYAAGGYTYALGSNQNMGLWNVFVTNTLKQTSTNYYVIGTCP	1999.0	Weight loss	3HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Polysciences		No				Yes		
Comamonas acidovorans	80866	PHA	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00015	00015 | PHB depolymerase | Comamonas acidovorans | P3HP P4HB PEA PES PHB PHA	Yes	BAA19791.1	MAFNFIRAAAAGAAMALCGVGSVHAAVNLPALKIDKTQTTVSGLSSGGFMAVQLHVAYSATFAKGAGVVAGGPFYCAEGSIVNATGRCMASPAGIPTSTLVSTTNTWASQGVIDPVANLQNSKVYLFSGTLDSVVKTGVMDALRTYYNSFVPAANVVYKKDIAAEHAMVTDDYGNACSTKGAPYISDCNFDLAGAMLQHLYGTLNARNNATLPTGNYIEFNQSEFITNHGMATTGWAYVPQACQAGGTATCKLHVVLHGCKQNIGDVQQQYVRNTGYNRWADTNNIVMLYPQTSTAATNSCWDWWGYDSANYSKKSGPQMAAIKAMVDRVSSGTGGTTPPDPVALPAPTGVSTSGATASSMAIGWAAVMGAASYNVYRNANKVNALPVTATSYTDTGLAASTTYSWTVRAADANGAEGATSAAASGTTLAASGGGTATCTTASNYAHTLAGRAYAAGGYTYALGSNQNMGLWNVFVTNTLKQTSTNYYVIGTCP	1999.0	Weight loss	3HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Polysciences		No				Yes		
Pseudomonas chlororaphis	587753	PU	Howard, G. T., Ruiz, C., & Hilliard, N. P. (1999). Growth of Pseudomonas chlororaphis on apolyester–polyurethane and the purification andcharacterization of a polyurethanase–esterase enzyme. International biodeterioration & biodegradation, 43(1-2), 7-12.	Polyurethane esterase A	00016	00016 | Polyurethane esterase A | Pseudomonas chlororaphis | PU	Yes		MGVFDYKNFTASDSKALFSDALAITLYSYHNIDNGFAEGYQHNGFGLGLPATLVTALIGSGNSQGVIPGIPWNPDSEKAALDALHQAGWSTISAQQLGYDGKVDGRGTFFGEKAGYGTAQVEILGKYDAQGHLESIGIAFRGTSGPRESVISDTIGDVINDLLAALGPKDYAKNYAGEAFGKLLGDVAAFAQANGLSGKDVLVSGHSLGGLGVNSLADLSSERWSGFYKDSNYIAYASPTQSASDKVLNIGYENDPVFRALDGSTFNLSSLGVHDAHQDSATNNIVNFNDHYASTLWNVLPSSILNIPTWLSHLPTGYGDGLSRVLESKFYDFTSKDSTIVVANLSDPARASTWVQDLNRNAETHKGSTFIIGSDGNDLIQGGSGNDYLEGRAGNDTFRDSGGYNIILGGQGSNTLDLQQSVKNYSFASDGAGTLYLRDANGGISMTRDIGAIQSKEPGFLWGLFKDDVIHQVTDQGLKAGGQLTQYASSVRGDAGDNVLKAHAGGDWLFGLDGNDHLIGGQGNDVFVGGAGNDLMEAGGGNNTFLFTGHFGQDRILGYQGGDKLVFMGVSGVLPDQDYRAHASSSGNDTVLTFGQDSVTLVGVSLEHLNGSGIVLA	1999.0	Clear zone	Impranil DLN		No	No	Culture collection	Culture collection		No		
Comamonas testosteroni	285	PHB	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00017	00017 | PHB depolymerase | Comamonas testosteroni | PHB PHA	Yes	BAA22882.1	MRVQSWRSGVAALALWGGVNLAAGAAVPLGQYNIATDQISVSGLSSGGFMANQLGNAYSASFMGVGIFAAGPYMCAGLNNYTACMYNASISSAQLNAMQSSIDSYSSAASIDAKSRIAAQKIYIFTGTSDYTVGPNLTDALQTQYLNNGVPQGNIAYVKRSGAAHVLPTDFDSSGNNACSSSASPYISNCGYDGAKAALTHFYGALNPRNDAPATGNYIEFNQASYTNANPGMASTGWLYVPQSCASGTQCRLHVVLHGCQQSTDKIGDKFVRNTGFSRWADTNNIIVLYPQTQVDNNNRSTSKSGSLANPNACWDWIGWYGNNFAQKSGVQMTAIKAMIDRIASGAGSGTGGGNGGGTPTQPALAAPTGLGASAATSTSMQLDWAPVTSAAGYNVYRNGNKANALTVYATSYVDAALNPATSYSWTVRAVDGNGAESADSAAVSASTLTGSNPAGTCTTASNYAHVQANRAYQQGGYAYANGSGQNMGLWNVFYTTTLKQTGSNYYVIGTCP	1999.0	Weight loss	18HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Polysciences		No				Yes		
Comamonas testosteroni	285	PHA	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00017	00017 | PHB depolymerase | Comamonas testosteroni | PHB PHA	Yes	BAA22882.1	MRVQSWRSGVAALALWGGVNLAAGAAVPLGQYNIATDQISVSGLSSGGFMANQLGNAYSASFMGVGIFAAGPYMCAGLNNYTACMYNASISSAQLNAMQSSIDSYSSAASIDAKSRIAAQKIYIFTGTSDYTVGPNLTDALQTQYLNNGVPQGNIAYVKRSGAAHVLPTDFDSSGNNACSSSASPYISNCGYDGAKAALTHFYGALNPRNDAPATGNYIEFNQASYTNANPGMASTGWLYVPQSCASGTQCRLHVVLHGCQQSTDKIGDKFVRNTGFSRWADTNNIIVLYPQTQVDNNNRSTSKSGSLANPNACWDWIGWYGNNFAQKSGVQMTAIKAMIDRIASGAGSGTGGGNGGGTPTQPALAAPTGLGASAATSTSMQLDWAPVTSAAGYNVYRNGNKANALTVYATSYVDAALNPATSYSWTVRAVDGNGAESADSAAVSASTLTGSNPAGTCTTASNYAHVQANRAYQQGGYAYANGSGQNMGLWNVFYTTTLKQTGSNYYVIGTCP	1999.0	Weight loss	18HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Polysciences		No				Yes		
Stutzerimonas stutzeri	316	P3HP	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00018	00018 | PHB depolymerase | Pseudomonas stutzeri | P3HP P4HB PEA PES PHB PHA	Yes	BAA32541.1	MTKQSLPQGMADQRLCRFFTAALCSLLMLLLWPTTVTAGQTFSYTSPQQAYSGSRERSYKVYVPTGLSTPAPMVMALHGCRQTNDDVLNDWGLKAAADRYGFILVAPFITSYDGLRNENCWGFWFEQHIHQGGGEVADLHRIAQQVEANFVIDANRRFITGLSSGGAMALVAAVAYNEYWAAAAPAAGLPYRETASSVSLSGQCPGSATFRSVSQVAADMRSEVNDAYPIPLMILQNRNDCTVLQTAANNMRDAHLQVFGSASRNTPATTKASDTGCSPYHQNDYGCRHIAYTQDGTTATRSLVETVIYDGPLATPNPQDTNHGHYWIGGAQGNNGKWSLQVGPSYPDIIWDFFSRHSRDGSQPQGHPVIVLQGDNPLSVPLGSTFNDPGASASDAEDGSLPVSADCSAVNPSVVGSYSCLYSATDSDGNRSTLTRTVEVYDPNAPVETCQVVSASPSAHIGAGRAYAGGTSNLRAYAKDDGVDIGGSFDTWSNVPLYEGEPGRWYAQRPAACGGSGQAFTCQEWNASNLSHVMAGRAYYGYYTVGGNQYLGSLSGLSTWVRETAQGHFQAGRCSN	1999.0	Weight loss	9HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.		Yes	No				Yes		
Stutzerimonas stutzeri	316	P4HB	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00018	00018 | PHB depolymerase | Pseudomonas stutzeri | P3HP P4HB PEA PES PHB PHA	Yes	BAA32541.1	MTKQSLPQGMADQRLCRFFTAALCSLLMLLLWPTTVTAGQTFSYTSPQQAYSGSRERSYKVYVPTGLSTPAPMVMALHGCRQTNDDVLNDWGLKAAADRYGFILVAPFITSYDGLRNENCWGFWFEQHIHQGGGEVADLHRIAQQVEANFVIDANRRFITGLSSGGAMALVAAVAYNEYWAAAAPAAGLPYRETASSVSLSGQCPGSATFRSVSQVAADMRSEVNDAYPIPLMILQNRNDCTVLQTAANNMRDAHLQVFGSASRNTPATTKASDTGCSPYHQNDYGCRHIAYTQDGTTATRSLVETVIYDGPLATPNPQDTNHGHYWIGGAQGNNGKWSLQVGPSYPDIIWDFFSRHSRDGSQPQGHPVIVLQGDNPLSVPLGSTFNDPGASASDAEDGSLPVSADCSAVNPSVVGSYSCLYSATDSDGNRSTLTRTVEVYDPNAPVETCQVVSASPSAHIGAGRAYAGGTSNLRAYAKDDGVDIGGSFDTWSNVPLYEGEPGRWYAQRPAACGGSGQAFTCQEWNASNLSHVMAGRAYYGYYTVGGNQYLGSLSGLSTWVRETAQGHFQAGRCSN	1999.0	Weight loss	10HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.		Yes	No				Yes		
Stutzerimonas stutzeri	316	PEA	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00018	00018 | PHB depolymerase | Pseudomonas stutzeri | P3HP P4HB PEA PES PHB PHA	Yes	BAA32541.1	MTKQSLPQGMADQRLCRFFTAALCSLLMLLLWPTTVTAGQTFSYTSPQQAYSGSRERSYKVYVPTGLSTPAPMVMALHGCRQTNDDVLNDWGLKAAADRYGFILVAPFITSYDGLRNENCWGFWFEQHIHQGGGEVADLHRIAQQVEANFVIDANRRFITGLSSGGAMALVAAVAYNEYWAAAAPAAGLPYRETASSVSLSGQCPGSATFRSVSQVAADMRSEVNDAYPIPLMILQNRNDCTVLQTAANNMRDAHLQVFGSASRNTPATTKASDTGCSPYHQNDYGCRHIAYTQDGTTATRSLVETVIYDGPLATPNPQDTNHGHYWIGGAQGNNGKWSLQVGPSYPDIIWDFFSRHSRDGSQPQGHPVIVLQGDNPLSVPLGSTFNDPGASASDAEDGSLPVSADCSAVNPSVVGSYSCLYSATDSDGNRSTLTRTVEVYDPNAPVETCQVVSASPSAHIGAGRAYAGGTSNLRAYAKDDGVDIGGSFDTWSNVPLYEGEPGRWYAQRPAACGGSGQAFTCQEWNASNLSHVMAGRAYYGYYTVGGNQYLGSLSGLSTWVRETAQGHFQAGRCSN	1999.0	Weight loss	12HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Showa Denko		No				Yes		
Stutzerimonas stutzeri	316	PES	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00018	00018 | PHB depolymerase | Pseudomonas stutzeri | P3HP P4HB PEA PES PHB PHA	Yes	BAA32541.1	MTKQSLPQGMADQRLCRFFTAALCSLLMLLLWPTTVTAGQTFSYTSPQQAYSGSRERSYKVYVPTGLSTPAPMVMALHGCRQTNDDVLNDWGLKAAADRYGFILVAPFITSYDGLRNENCWGFWFEQHIHQGGGEVADLHRIAQQVEANFVIDANRRFITGLSSGGAMALVAAVAYNEYWAAAAPAAGLPYRETASSVSLSGQCPGSATFRSVSQVAADMRSEVNDAYPIPLMILQNRNDCTVLQTAANNMRDAHLQVFGSASRNTPATTKASDTGCSPYHQNDYGCRHIAYTQDGTTATRSLVETVIYDGPLATPNPQDTNHGHYWIGGAQGNNGKWSLQVGPSYPDIIWDFFSRHSRDGSQPQGHPVIVLQGDNPLSVPLGSTFNDPGASASDAEDGSLPVSADCSAVNPSVVGSYSCLYSATDSDGNRSTLTRTVEVYDPNAPVETCQVVSASPSAHIGAGRAYAGGTSNLRAYAKDDGVDIGGSFDTWSNVPLYEGEPGRWYAQRPAACGGSGQAFTCQEWNASNLSHVMAGRAYYGYYTVGGNQYLGSLSGLSTWVRETAQGHFQAGRCSN	1999.0	Weight loss	11HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Showa Denko		No				Yes		
Stutzerimonas stutzeri	316	PHB	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00018	00018 | PHB depolymerase | Pseudomonas stutzeri | P3HP P4HB PEA PES PHB PHA	Yes	BAA32541.1	MTKQSLPQGMADQRLCRFFTAALCSLLMLLLWPTTVTAGQTFSYTSPQQAYSGSRERSYKVYVPTGLSTPAPMVMALHGCRQTNDDVLNDWGLKAAADRYGFILVAPFITSYDGLRNENCWGFWFEQHIHQGGGEVADLHRIAQQVEANFVIDANRRFITGLSSGGAMALVAAVAYNEYWAAAAPAAGLPYRETASSVSLSGQCPGSATFRSVSQVAADMRSEVNDAYPIPLMILQNRNDCTVLQTAANNMRDAHLQVFGSASRNTPATTKASDTGCSPYHQNDYGCRHIAYTQDGTTATRSLVETVIYDGPLATPNPQDTNHGHYWIGGAQGNNGKWSLQVGPSYPDIIWDFFSRHSRDGSQPQGHPVIVLQGDNPLSVPLGSTFNDPGASASDAEDGSLPVSADCSAVNPSVVGSYSCLYSATDSDGNRSTLTRTVEVYDPNAPVETCQVVSASPSAHIGAGRAYAGGTSNLRAYAKDDGVDIGGSFDTWSNVPLYEGEPGRWYAQRPAACGGSGQAFTCQEWNASNLSHVMAGRAYYGYYTVGGNQYLGSLSGLSTWVRETAQGHFQAGRCSN	1999.0	Weight loss	8HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Polysciences		No				Yes		
Stutzerimonas stutzeri	316	PHB	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00018	00018 | PHB depolymerase | Pseudomonas stutzeri | P3HP P4HB PEA PES PHB PHA	Yes	BAA32541.1	MTKQSLPQGMADQRLCRFFTAALCSLLMLLLWPTTVTAGQTFSYTSPQQAYSGSRERSYKVYVPTGLSTPAPMVMALHGCRQTNDDVLNDWGLKAAADRYGFILVAPFITSYDGLRNENCWGFWFEQHIHQGGGEVADLHRIAQQVEANFVIDANRRFITGLSSGGAMALVAAVAYNEYWAAAAPAAGLPYRETASSVSLSGQCPGSATFRSVSQVAADMRSEVNDAYPIPLMILQNRNDCTVLQTAANNMRDAHLQVFGSASRNTPATTKASDTGCSPYHQNDYGCRHIAYTQDGTTATRSLVETVIYDGPLATPNPQDTNHGHYWIGGAQGNNGKWSLQVGPSYPDIIWDFFSRHSRDGSQPQGHPVIVLQGDNPLSVPLGSTFNDPGASASDAEDGSLPVSADCSAVNPSVVGSYSCLYSATDSDGNRSTLTRTVEVYDPNAPVETCQVVSASPSAHIGAGRAYAGGTSNLRAYAKDDGVDIGGSFDTWSNVPLYEGEPGRWYAQRPAACGGSGQAFTCQEWNASNLSHVMAGRAYYGYYTVGGNQYLGSLSGLSTWVRETAQGHFQAGRCSN	1999.0	Weight loss	8HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Polysciences		No				Yes		
Ralstonia pickettii	329	P3HP	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00019	00019 | PHB depolymerase | Ralstonia pickettii | P3HP P4HB PEA PES PHB PHA	Yes	AAA21974.1	MVRRLWRRIAGWLAACVAILCAFPLHAATAGPGAWSSQQTWAADSVNGGNLTGYFYWPASQPTTPNGKRALVLVLHGCVQTASGDVIDNANGAGFNWKSVADQYGAVILAPNATGNVYSNHCWDYANASPSRTAGHVGVLLDLVNRFVTNSQYAIDPNQVYVAGLSSGGGMTMVLGCIAPDIFAGIGINAGPPPGTTTAQIGYVPSGFTATTAANKCNAWAGSNAGKFSTQIAGAVWGTSDYTVAQAYGPMDAAAMRLVYGGNFTQGSQVSISGGGTNTPYTDSNGKVRTHEISVSGMAHAWPAGTGGDNTNYVDATHINYPVFVMDYWVKNNLRAGSGTGQAGSAPTGLAVTATTSTSVSLSWNAVANASSYGVYRNGSKVGSATATAYTDSGLIAGTTYSYTVTAVDPTAGESQPSAAVSATTKSAFTCTATTASNYAHVQAGRAHDSGGIAYANGSNQSMGLDNLFYTSTLAQTAAGYYIVGNCP	1999.0	Weight loss	14HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.		Yes	No				Yes		
Ralstonia pickettii	329	P4HB	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00019	00019 | PHB depolymerase | Ralstonia pickettii | P3HP P4HB PEA PES PHB PHA	Yes	AAA21974.1	MVRRLWRRIAGWLAACVAILCAFPLHAATAGPGAWSSQQTWAADSVNGGNLTGYFYWPASQPTTPNGKRALVLVLHGCVQTASGDVIDNANGAGFNWKSVADQYGAVILAPNATGNVYSNHCWDYANASPSRTAGHVGVLLDLVNRFVTNSQYAIDPNQVYVAGLSSGGGMTMVLGCIAPDIFAGIGINAGPPPGTTTAQIGYVPSGFTATTAANKCNAWAGSNAGKFSTQIAGAVWGTSDYTVAQAYGPMDAAAMRLVYGGNFTQGSQVSISGGGTNTPYTDSNGKVRTHEISVSGMAHAWPAGTGGDNTNYVDATHINYPVFVMDYWVKNNLRAGSGTGQAGSAPTGLAVTATTSTSVSLSWNAVANASSYGVYRNGSKVGSATATAYTDSGLIAGTTYSYTVTAVDPTAGESQPSAAVSATTKSAFTCTATTASNYAHVQAGRAHDSGGIAYANGSNQSMGLDNLFYTSTLAQTAAGYYIVGNCP	1999.0	Weight loss	15HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.		Yes	No				Yes		
Ralstonia pickettii	329	PEA	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00019	00019 | PHB depolymerase | Ralstonia pickettii | P3HP P4HB PEA PES PHB PHA	Yes	AAA21974.1	MVRRLWRRIAGWLAACVAILCAFPLHAATAGPGAWSSQQTWAADSVNGGNLTGYFYWPASQPTTPNGKRALVLVLHGCVQTASGDVIDNANGAGFNWKSVADQYGAVILAPNATGNVYSNHCWDYANASPSRTAGHVGVLLDLVNRFVTNSQYAIDPNQVYVAGLSSGGGMTMVLGCIAPDIFAGIGINAGPPPGTTTAQIGYVPSGFTATTAANKCNAWAGSNAGKFSTQIAGAVWGTSDYTVAQAYGPMDAAAMRLVYGGNFTQGSQVSISGGGTNTPYTDSNGKVRTHEISVSGMAHAWPAGTGGDNTNYVDATHINYPVFVMDYWVKNNLRAGSGTGQAGSAPTGLAVTATTSTSVSLSWNAVANASSYGVYRNGSKVGSATATAYTDSGLIAGTTYSYTVTAVDPTAGESQPSAAVSATTKSAFTCTATTASNYAHVQAGRAHDSGGIAYANGSNQSMGLDNLFYTSTLAQTAAGYYIVGNCP	1999.0	Weight loss	17HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Showa Denko		No				Yes		
Ralstonia pickettii	329	PES	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00019	00019 | PHB depolymerase | Ralstonia pickettii | P3HP P4HB PEA PES PHB PHA	Yes	AAA21974.1	MVRRLWRRIAGWLAACVAILCAFPLHAATAGPGAWSSQQTWAADSVNGGNLTGYFYWPASQPTTPNGKRALVLVLHGCVQTASGDVIDNANGAGFNWKSVADQYGAVILAPNATGNVYSNHCWDYANASPSRTAGHVGVLLDLVNRFVTNSQYAIDPNQVYVAGLSSGGGMTMVLGCIAPDIFAGIGINAGPPPGTTTAQIGYVPSGFTATTAANKCNAWAGSNAGKFSTQIAGAVWGTSDYTVAQAYGPMDAAAMRLVYGGNFTQGSQVSISGGGTNTPYTDSNGKVRTHEISVSGMAHAWPAGTGGDNTNYVDATHINYPVFVMDYWVKNNLRAGSGTGQAGSAPTGLAVTATTSTSVSLSWNAVANASSYGVYRNGSKVGSATATAYTDSGLIAGTTYSYTVTAVDPTAGESQPSAAVSATTKSAFTCTATTASNYAHVQAGRAHDSGGIAYANGSNQSMGLDNLFYTSTLAQTAAGYYIVGNCP	1999.0	Weight loss	16HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Showa Denko		No				Yes		
Ralstonia pickettii	329	PHB	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00019	00019 | PHB depolymerase | Ralstonia pickettii | P3HP P4HB PEA PES PHB PHA	Yes	AAA21974.1	MVRRLWRRIAGWLAACVAILCAFPLHAATAGPGAWSSQQTWAADSVNGGNLTGYFYWPASQPTTPNGKRALVLVLHGCVQTASGDVIDNANGAGFNWKSVADQYGAVILAPNATGNVYSNHCWDYANASPSRTAGHVGVLLDLVNRFVTNSQYAIDPNQVYVAGLSSGGGMTMVLGCIAPDIFAGIGINAGPPPGTTTAQIGYVPSGFTATTAANKCNAWAGSNAGKFSTQIAGAVWGTSDYTVAQAYGPMDAAAMRLVYGGNFTQGSQVSISGGGTNTPYTDSNGKVRTHEISVSGMAHAWPAGTGGDNTNYVDATHINYPVFVMDYWVKNNLRAGSGTGQAGSAPTGLAVTATTSTSVSLSWNAVANASSYGVYRNGSKVGSATATAYTDSGLIAGTTYSYTVTAVDPTAGESQPSAAVSATTKSAFTCTATTASNYAHVQAGRAHDSGGIAYANGSNQSMGLDNLFYTSTLAQTAAGYYIVGNCP	1999.0	Weight loss	13HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Polysciences		No				Yes		
Ralstonia pickettii	329	PHA	Kasuya, K. I., Ohura, T., Masuda, K., & Doi, Y. (1999). Substrate and binding specificities of bacterial polyhydroxybutyrate depolymerases. International journal of biological macromolecules, 24(4), 329-336.	PHB depolymerase	00019	00019 | PHB depolymerase | Ralstonia pickettii | P3HP P4HB PEA PES PHB PHA	Yes	AAA21974.1	MVRRLWRRIAGWLAACVAILCAFPLHAATAGPGAWSSQQTWAADSVNGGNLTGYFYWPASQPTTPNGKRALVLVLHGCVQTASGDVIDNANGAGFNWKSVADQYGAVILAPNATGNVYSNHCWDYANASPSRTAGHVGVLLDLVNRFVTNSQYAIDPNQVYVAGLSSGGGMTMVLGCIAPDIFAGIGINAGPPPGTTTAQIGYVPSGFTATTAANKCNAWAGSNAGKFSTQIAGAVWGTSDYTVAQAYGPMDAAAMRLVYGGNFTQGSQVSISGGGTNTPYTDSNGKVRTHEISVSGMAHAWPAGTGGDNTNYVDATHINYPVFVMDYWVKNNLRAGSGTGQAGSAPTGLAVTATTSTSVSLSWNAVANASSYGVYRNGSKVGSATATAYTDSGLIAGTTYSYTVTAVDPTAGESQPSAAVSATTKSAFTCTATTASNYAHVQAGRAHDSGGIAYANGSNQSMGLDNLFYTSTLAQTAAGYYIVGNCP	1999.0	Weight loss	13HB) was purchased from Polyscience Inc. Poly(3-hydroxypentanoate) ((P(3HV)) was produced by a recombinant Ralstonia eutropha from pentanoic acid [28]. Poly(3-hydroxyoctanoate) ((P(3HO)) was produced by Pseudomonas oleo6orans ATCC 29347 from octanoic acid [29]. Poly(4-hydroxybutyrate) ((P(4HB)) was produced by C. acido6orans IFO 13582 from 1,4-butanediol [30]. Poly(3-hydroxypropionate) ((P(3HP)), poly(5-hydroxypentanoate) (P(5HV)), and poly(6-hydroxyhexanoate) (P(6HH) were prepared at 60°C by ring-opening polymerizations of b-propiolactone, d-valelolactone, and o-caprolactone in the presence of poly(methylaluminoxane) catalyst, respectively [31]. Poly(2-hydroxypropionate) (P(2HP)) was purchased from Shimadzu Inc. Poly(ethylene adipate) (PEA), poly(ethylene succinate) (PESU), poly(butylene adipate) (PBA), and poly(- butylene succinate) (PBSU) were kind gifts of Showa High Polymer Inc.	Polysciences		No				Yes		
Pseudomonas chlororaphis	587753	PU	Stern, R. V., & Howard, G. T. (2000). The polyester polyurethanase gene (pueA) from Pseudomonas chlororaphis encodes a lipase. FEMS Microbiology Letters, 185(2), 163-168.	Polyurethane esterase A	00021	00021 | Polyurethane esterase A | Pseudomonas chlororaphis | PU	Yes	AAD22743.1	MGVFDYKNFTASDSKALFSDALAITLYSYHNIDNGFAEGYQHNGFGLGLPATLVTALIGSGNSQGVIPGIPWNPDSEKAALDALHQAGWSTISAQQLGYDGKVDGRGTFFGEKAGYGTAQVEILGKYDAQGHLESIGIAFRGTSGPRESVISDTIGDVINDLLAALGPKDYAKNYAGEAFGKLLGDVAAFAQANGLSGKDVLVSGHSLGGLGVNSLADLSSERWSGFYKDSNYIAYASPTQSASDKVLNIGYENDPVFRALDGSTFNLSSLGVHDAHQDSATNNIVNFNDHYASTLWNVLPSSILNIPTWLSHLPTGYGDGLSRVLESKFYDFTSKDSTIVVANLSDPARASTWVQDLNRNAETHKGSTFIIGSDGNDLIQGGSGNDYLEGRAGNDTFRDSGGYNIILGGQGSNTLDLQQSVKNYSFASDGAGTLYLRDANGGISMTRDIGAIQSKEPGFLWGLFKDDVIHQVTDQGLKAGGQLTQYASSVRGDAGDNVLKAHAGGDWLFGLDGNDHLIGGQGNDVFVGGAGNDLMEAGGGNNTFLFTGHFGQDRILGYQGGDKLVFMGVSGVLPDQDYRAHASSSGNDTVLTFGQDSVTLVGVSLEHLNGSGIVLA	2000.0	Clear zone	Impranil DLN		No	No	Culture collection	Culture collection		Yes		
Pseudomonas sp.	306	O-PVA	Shimao, M., Tamogami, T., Kishida, S., & Harayama, S. (2000). The gene pvaB encodes oxidized polyvinyl alcohol hydrolase of Pseudomonas sp. strain VM15C and forms an operon with the polyvinyl alcohol dehydrogenase gene pvaA. Microbiology, 146(3), 649-657.	Oxidized PVA hydrolase 	00022	00022 | Oxidized PVA hydrolase | Pseudomonas sp. | O-PVA	Yes	BAA94192.1	MNQSLGVLRLTRGVIALALASVASGCSSTGADRTAATPAAANPAATEPVKWECPAGYEVKEGLNVDFPHKGMKRAFIVYPAKNVSGPAPVWVPMTGSVESTNDNLTVARSGANSILADHGYTVIAPVRACANQDPNIRGERCNGPGSNGWNWNPWFEGRAADPSGEHWKNDEGPDSSFFVAMVQCVGTKYKLDARRLFLGGISSGGTMTNRALLFRSNFWAGGLPISGEWYVTSDDGTPLSFDDARAAVAAAPTKIHQGRVGPYPLPAKVGPLIVMTVWGGEKDLWNCTRPDGSRFLCADYRPSTQAGSNFFSAQPDVVHVACSSTHGHMWPQLNTQEFNRWALDTLASHPKGSDPRSFKLTQPPEGYTCHVGPFTGLY	2000.0	Spectrophotometry	PQQ and PVAs with degrees of polymerization of 500 (PVA500) and 1500 (PVA1500) have been described previously (Shimao et al., 1996).		No	No				Yes		
Pseudomonas sp.	306	PVA	Shimao, M., Tamogami, T., Kishida, S., & Harayama, S. (2000). The gene pvaB encodes oxidized polyvinyl alcohol hydrolase of Pseudomonas sp. strain VM15C and forms an operon with the polyvinyl alcohol dehydrogenase gene pvaA. Microbiology, 146(3), 649-657.	PVA dehydrogenase	00022	00022 | Oxidized PVA hydrolase | Pseudomonas sp. | O-PVA	Yes	BAA94193.1	MQQNIERNQVSMTTSRFVWGAVMALVALGSASAAELNLPDGAALYRARCGTCHDNPQDRTPARDVIARNSPAFIMAAMNGVMAPMAAGLSEAEKQAIALHLGARPAGGSQEINPHAIWGPPSASMPLDGPKCKGKIPPIDLSTPDQWNGWGAGITNARFQPNPGLTAADVPRLKVKWAFNYPGSKNGQATVVGDRLFVTSMSGAVYALNAKTGCVYWRHDAAAATRSSVHVVQLPAGAPAQYAIFFSDWTKAAVALDAQTGKQLWKTTIDDQPGVQMTGSPTYHEGKLFVPISSGNEAFATNDQWECCKFRGALVALDALSGKVLWKTYTTQKEPAPFRLNKLGKQMWGPAGGSIWSAPTIDPKRGLVYVATSNSYTEVHHEGSDAVMAMEIETGKVRWINQVTKDDNYIIGCPRAANCPEKVGPDFALGNSPILHTLQDGRQYIVVGQKSGAVYAMDPDNDGELIWMRRVSPGSELGGVEFGMAADAENVYVGISDVITRKGGKPGVYALRIRDGADVWAFPAPRTPCRWNNIFCHPAVSQAVTAMPGVVFAGSMDGHFRAFSTSDGKVLWEFNTAAAPYKTVAGKQADGGVMDGAGPTIAGGMVYVHSGYAGRSTQNAGDLRGREGNVLIAFSVDGK	2000.0	Viscosimeter	PQQ and PVAs with degrees of polymerization of 500 (PVA500) and 1500 (PVA1500) have been described previously (Shimao et al., 1996).		No	No				Yes		
Pseudomonas chlororaphis	587753	PU	Howard, G. T., Crother, B., & Vicknair, J. (2001). Cloning, nucleotide sequencing and characterization of a polyurethanase gene (pueB) from Pseudomonas chlororaphis. International biodeterioration & biodegradation, 47(3), 141-149.	Polyurethanase	00023	00023 | Polyurethanase | Pseudomonas chlororaphis | PU	Yes	AAF01331.1	MSMSIFDYKTALGGDGKALYSEAITLALYASTPTGEALPGTAWRPISVSQLGYQGNVSAQGTISGEQAIVSDAQSRCWANTTRPGSCCPSASSFRGTRQPQGRYQRLAGGLRVGLLPTTTSRLAFDNLLGKVAAFAAAQGLSGSDVLVTGHSLGGLGGQPRGGHEQRSLGRLLPGRQLLGFASPTQSANSSQVLNIGYETTRCSAPWTALISTALSLGTHWQAPGVATNNIVSFTDHYSSFLGEVDSPEHPQSAVLVGPQCGGLRRGLNRLINSDFYDLTSRDSTVVISNLSEGKRDQVWVKDLNLYAEKHTGSTFIIGTQSNDLLHGGKGNDYLDGGAGDDRFRDDGGYNIIHGGQGHNVLELQQPLKNFSIANDGDGTLYIRDAYGGISMTRDVGALVSHETGSWWQLFGKDVSHSVTADGLQNGNQWTAYNHSLNGDAYGNALVASVDGDWLFGHGGDDLLSSDKANVTFVGGTGNDVMHSSGGGGNTFLFSGNFGFDLIHGYQNTDKLVFMGVPGVDAHYDYSQHLSQNGNDTLVQVFGEFLRVNPWWGSAWTSLSGSGLVFA	2001.0	Clear zone	Impranil	Bayer 	No	No				Yes		
Acidovorax delafieldii	47920	PBS	Uchida, H., Shigeno-Akutsu, Y., Nomura, N., Nakahara, T., & Nakajima-Kambe, T. (2002). Cloning and sequence analysis of poly (tetramethylene succinate) depolymerase from Acidovorax delafieldii strain BS-3. Journal of bioscience and bioengineering, 93(2), 245-247.	PBS depolymerase	00024	00024 | PBS depolymerase | Acidovorax delafieldii | PBS	Yes	BAB86909.1	MHLPRSRWDIPFKEETTMTHHFSVRALLAAGALLASAAVSAQTNPYERGPAPTTSSLEASRGPFSYQSFTVSRPSGYRAGTVYYPTNAGGPVGAIAIVPGFTARQSSINWWGPRLASHGFVVITIDTNSTLDQPDSRSRQQMAALSQVATLSRTSSSPIYNKVDTSRLGVMGWSMGGGGSLISARNNPSIKAAAPQAPWSASKNFSSLTVPTLIIACENDTIAPVNQHADTFYDSMSRNPREFLEINNGSHSCANSGNSNQALLGKKGVAWMKRFMDNDRRYTSFACSNPNSYNVSDFRVAACN	2002.0	Clear zone	PBS (Bionolle #1020). The number average molecular weight of PBS is approximately 60,000. 	Showa Denko		No				No		
Caldimonas manganoxidans	196015	PHB	Takeda, M., Kamagata, Y., Ghiorse, W. C., Hanada, S., & Koizumi, J. I. (2002). Caldimonas manganoxidans gen. nov., sp. nov., a poly (3-hydroxybutyrate)-degrading, manganese-oxidizing thermophile. International journal of systematic and evolutionary microbiology, 52(3), 895-900.	PHB depolymerase	00025	00025 | PHB depolymerase | Caldimonas manganoxidans | PHB PHA	Yes	BAA92354.1	MKTRMLVGWAAAAVLAAGPAWAVQSLPRLNIDKSQISVSGLSSGGFMANQLGVAHSSTFMGVGVFAAGPYMCAGHYNYTACMYNATISDGQLSTMQSSINHWSGSQIDDKAGIAKQKIYLFVGTSDSTIGPNPMDALRKQYANNAVPTGNDEYIKRSGAAHVFPTDFDAAGNNSCGSTSSPYIANCGYDGAKAVLTRIYGTLNPRNDTPPASNYIEFSQASFTNNPGMAATGWVYVPSDCAAGAQCRLHVALHGCQQSYAQIGDKFIKNTGYTRWADTNRIVVLFPQTKVDNTSRSTAASGLLPNPNACWDWIGWYGSDFAQKGGSQISAIKAMVDHLASGAPTSTLPAPTGVSTSGATDTSMVISWASVQGAAGYHVYRNGAKQTTTPVTGTSYTDTGLTPATTYQWTVTAVDGQGAESVPSAAASGTTTGAAPPPATCYTASNYAHTTACRAYAAWGYAYAKGSNQNMGLWNIYVITTLKQTGPNHYVIGTCP	2002.0					Yes		Hot spring		No		
Caldimonas manganoxidans	196015	PHA	Takeda, M., Kamagata, Y., Ghiorse, W. C., Hanada, S., & Koizumi, J. I. (2002). Caldimonas manganoxidans gen. nov., sp. nov., a poly (3-hydroxybutyrate)-degrading, manganese-oxidizing thermophile. International journal of systematic and evolutionary microbiology, 52(3), 895-900.	PHB depolymerase	00025	00025 | PHB depolymerase | Caldimonas manganoxidans | PHB PHA	Yes	BAA92354.1	MKTRMLVGWAAAAVLAAGPAWAVQSLPRLNIDKSQISVSGLSSGGFMANQLGVAHSSTFMGVGVFAAGPYMCAGHYNYTACMYNATISDGQLSTMQSSINHWSGSQIDDKAGIAKQKIYLFVGTSDSTIGPNPMDALRKQYANNAVPTGNDEYIKRSGAAHVFPTDFDAAGNNSCGSTSSPYIANCGYDGAKAVLTRIYGTLNPRNDTPPASNYIEFSQASFTNNPGMAATGWVYVPSDCAAGAQCRLHVALHGCQQSYAQIGDKFIKNTGYTRWADTNRIVVLFPQTKVDNTSRSTAASGLLPNPNACWDWIGWYGSDFAQKGGSQISAIKAMVDHLASGAPTSTLPAPTGVSTSGATDTSMVISWASVQGAAGYHVYRNGAKQTTTPVTGTSYTDTGLTPATTYQWTVTAVDGQGAESVPSAAASGTTTGAAPPPATCYTASNYAHTTACRAYAAWGYAYAKGSNQNMGLWNIYVITTLKQTGPNHYVIGTCP	2002.0					Yes		Hot spring		No		
Marinobacter sp.	50741	PHB	Kasuya, K. I., Takano, T., Tezuka, Y., Hsieh, W. C., Mitomo, H., & Doi, Y. (2003). Cloning, expression and characterization of a poly (3-hydroxybutyrate) depolymerase from Marinobacter sp. NK-1. International journal of biological macromolecules, 33(4-5), 221-226.	PHB depolymerase	00026	00026 | PHB depolymerase | Marinobacter sp. | PHB PHA	Yes	BAC15574.1	MQHLLSGWIRRIALPVLTLSTLIILPSLPAHAGQTDSYTLPQQAYNQSRARDYKVYVPDGLTSPAPMVMALHGCKQTNNDVLNDWGLKAAADRYGFILVAPYITSYDGLRNQNCWGFWFDHHRHEGAGEVEDLHQIALAVEGNYSIDPQRRFITGLSSGGAMTAVAAITHNEYWAAAASASGLPYGEDSSSVSLTGQCPGNATFHSVSRVVSDMQAELNDPYPIPMMVLQNKNDCTVLKKAADNIRDAHLKVFGEAGFDTPSGADAGTVNCSPYYQNDYNCTHTRYTQDGTTGTRSVVETVYLDGPLSTPNTQDTDHGHYWVSGKDGNNGKWAIRVGPSYPDIIWNFFAAHDRDGPDPEGYPVITLIGDNPMSVAIGTAFTDPGATAEDAEDGSLTVSADCSDVDTASVGTYACTYSATDSDTNETTVTRSVEVYDPKAPVETCQQATASPSGHISAGRAYAGGTSNLRAYANGDDADIGASFDSWSSVVLYEGEPGQWFSQEPSACSGVPDDGNDNGDPVACQDWNASNLSHSMAGRAYYSAGYYTTGGDDSLGPIPGTYTWVKETSAGVFEAGQCP	2003.0	Spectrophotometry	The P(3HB) granules were a gift from Monsanto (St. Louis, MO).							Yes		
Marinobacter sp.	50741	PHA	Kasuya, K. I., Takano, T., Tezuka, Y., Hsieh, W. C., Mitomo, H., & Doi, Y. (2003). Cloning, expression and characterization of a poly (3-hydroxybutyrate) depolymerase from Marinobacter sp. NK-1. International journal of biological macromolecules, 33(4-5), 221-226.	PHB depolymerase	00026	00026 | PHB depolymerase | Marinobacter sp. | PHB PHA	Yes	BAC15574.1	MQHLLSGWIRRIALPVLTLSTLIILPSLPAHAGQTDSYTLPQQAYNQSRARDYKVYVPDGLTSPAPMVMALHGCKQTNNDVLNDWGLKAAADRYGFILVAPYITSYDGLRNQNCWGFWFDHHRHEGAGEVEDLHQIALAVEGNYSIDPQRRFITGLSSGGAMTAVAAITHNEYWAAAASASGLPYGEDSSSVSLTGQCPGNATFHSVSRVVSDMQAELNDPYPIPMMVLQNKNDCTVLKKAADNIRDAHLKVFGEAGFDTPSGADAGTVNCSPYYQNDYNCTHTRYTQDGTTGTRSVVETVYLDGPLSTPNTQDTDHGHYWVSGKDGNNGKWAIRVGPSYPDIIWNFFAAHDRDGPDPEGYPVITLIGDNPMSVAIGTAFTDPGATAEDAEDGSLTVSADCSDVDTASVGTYACTYSATDSDTNETTVTRSVEVYDPKAPVETCQQATASPSGHISAGRAYAGGTSNLRAYANGDDADIGASFDSWSSVVLYEGEPGQWFSQEPSACSGVPDDGNDNGDPVACQDWNASNLSHSMAGRAYYSAGYYTTGGDDSLGPIPGTYTWVKETSAGVFEAGQCP	2003.0	Spectrophotometry	The P(3HB) granules were a gift from Monsanto (St. Louis, MO).							Yes		
Paenibacillus amylolyticus	1451	PLA	Akutsu-Shigeno, Y., Teeraphatpornchai, T., Teamtisong, K., Nomura, N., Uchiyama, H., Nakahara, T., & Nakajima-Kambe, T. (2003). Cloning and sequencing of a poly (DL-lactic acid) depolymerase gene from Paenibacillus amylolyticus strain TB-13 and its functional expression in Escherichia coli. Appl. Environ. Microbiol., 69(5), 2498-2504.	PLA depolymerase	00027	00027 | PLA depolymerase | Paenibacillus amylolyticus | PLA	Yes	BAC67195.1	MRKLKLLLMVCMSMVFIFTLPGMGQSLKASAATERTPIVFVHGLTGSDSNFALIERYLRGEGWSSDELFAIDLPSKAGNQLLNSAAISRFVDDVLRQTGHSKVHIVAHSMGGANSLYYILNRGGIDKVDKLITLGGANRLTTSRAPDGIRVTSIYSTSDTIVSPALSRLDGANNISVNLVTHIGLLYNSRVNALIKAALIE	2003.0	Spectrophotometry;TOC;Clear zone	PLA samples with weight-average molecular weights of 0.5x104  (PLA05), 1.0x104 (PLA10), 1.5x 104 (PLA15), and 2.0x104 (PLA20) were used.	Wako Pure Chemical		No				Yes		
Azospirillum brasilense	192	PHB	Kadouri, D., Jurkevitch, E., & Okon, Y. (2003). Poly β-hydroxybutyrate depolymerase (PhaZ) in Azospirillum brasilense and characterization of a phaZ mutant. Archives of microbiology, 180(5), 309-318.	PHB depolymerase	00028	00028 | PHB depolymerase | Azospirillum brasilense | PHB PHA	Yes	AAQ05770.1	MSVLHGMFGFLSPEGPSSPSDGVGSLEQVAEREAHQGPGPGDAPMLVARGDHMTTPAQPSPFHRVLGHRLLGGPFDRRGATVLSDDAARGPDPGILDHVRPGGRVACVAEPESVGRQPAAVRQAAQRMAVRTPAMLAPRSGRAGGDGTVLMFGGTVDEAGHSDQGWWLRTKPKPNLAHRTVRGNPQRWPARGNSSIAGYDESRVHRRLGTLCGTRSPLLQAGGAGGSILPLVPVRHCLYAVRQIGAIGHGKGNSAAEFGLKTTVVDGETVAITERIALRKPFCNLLHFAKPEGTPAQPRVLLVAPMSGHHATLLRGTVAALLADHDVFVTDWIDARLVPLACGRFDLDDYIDTVVTELIRFLGPQTHVIAVCQPAVPVLAAVSLMAAGDEAVQPRSMTLMGGPIDPMANPTVPVKLAATHPLSWFERNVITTVPAYYPGGFRQVYPGFIQLSGFMSMNLDRHIGEHVGLFRHLVRGDGDSAVQHRRFYDEYLSVMDLSAEFYLQTIETVFHKHSLANGTMESRGRKVEPAAIRRTAVMTVEGELDDISAPGQTESAHRLCASLPDDMRARHFQKGVGHYGIFNGRRWRESIMPAVREFIRKHD	2003.0	GC	A high carbon-to-nitrogen (C:N) ratio medium (Burdman et al. 1999; Okon et al. 1977) was used to induce accumulation of PHB in A. Brasilense.		Yes	No				No		
Azospirillum brasilense	192	PHA	Kadouri, D., Jurkevitch, E., & Okon, Y. (2003). Poly β-hydroxybutyrate depolymerase (PhaZ) in Azospirillum brasilense and characterization of a phaZ mutant. Archives of microbiology, 180(5), 309-318.	PHB depolymerase	00028	00028 | PHB depolymerase | Azospirillum brasilense | PHB PHA	Yes	AAQ05770.1	MSVLHGMFGFLSPEGPSSPSDGVGSLEQVAEREAHQGPGPGDAPMLVARGDHMTTPAQPSPFHRVLGHRLLGGPFDRRGATVLSDDAARGPDPGILDHVRPGGRVACVAEPESVGRQPAAVRQAAQRMAVRTPAMLAPRSGRAGGDGTVLMFGGTVDEAGHSDQGWWLRTKPKPNLAHRTVRGNPQRWPARGNSSIAGYDESRVHRRLGTLCGTRSPLLQAGGAGGSILPLVPVRHCLYAVRQIGAIGHGKGNSAAEFGLKTTVVDGETVAITERIALRKPFCNLLHFAKPEGTPAQPRVLLVAPMSGHHATLLRGTVAALLADHDVFVTDWIDARLVPLACGRFDLDDYIDTVVTELIRFLGPQTHVIAVCQPAVPVLAAVSLMAAGDEAVQPRSMTLMGGPIDPMANPTVPVKLAATHPLSWFERNVITTVPAYYPGGFRQVYPGFIQLSGFMSMNLDRHIGEHVGLFRHLVRGDGDSAVQHRRFYDEYLSVMDLSAEFYLQTIETVFHKHSLANGTMESRGRKVEPAAIRRTAVMTVEGELDDISAPGQTESAHRLCASLPDDMRARHFQKGVGHYGIFNGRRWRESIMPAVREFIRKHD	2003.0	GC	A high carbon-to-nitrogen (C:N) ratio medium (Burdman et al. 1999; Okon et al. 1977) was used to induce accumulation of PHB in A. Brasilense.		Yes	No				No		
Schlegelella thermodepolymerans	215580	P(3HB-co-3MP)	Elbanna, K., Lütke-Eversloh, T., Jendrossek, D., Luftmann, H., & Steinbüchel, A. (2004). Studies on the biodegradability of polythioester copolymers and homopolymers by polyhydroxyalkanoate (PHA)-degrading bacteria and PHA depolymerases. Archives of microbiology, 182(2-3), 212-225.	PHA depolymerase	00029	00029 | PHA depolymerase | Schlegelella thermodepolymerans | P(3HB-co-3MP) PHA	Yes		MRSIRLKRLIAAVALGGAAAATQAASPLPRLNVDKTQISVSGLSAGGFMANQLGYAYSGTFMGVGIFAGGPYMCAGHSNYTSCMYNATITSSMRSAMQASIDNWSGAHIDPKAHVANQRVFLFVGNSDTTVGPNPMDAVHAQYQHNGVRRTARVRGRNSTAHVFPTDFDATGNNACNSTASPYIANCGYDGAKAVLSRIYGTLQPRNDAPAGANYIEFDQTAFTNNPGMASTGWVYVPANCAAGAQCRLHVALHGCQQSTGHIGDRFVKNTGYTRWADTNNIIVLFPQAKTDNTPRNTAASGMLPNPNACWDWVGWYGSNFAQKTGTQAAAIKAMVDHVASARPRLRLPAPTGVQTSGATSSSMVISWAAVQGAAGYNVYRDGTKVNATAVSGTSYTDNGLSPGTTYQWTVRAVNAQGPRPAVGPATGTTTGTAAVCFTSSNYAHVSAGRAYVSMGYTYANASHQNMGLWNVFVTTTLKQTGPNYYVIGTCP	2004.0	GC;NMR;FTIR;MS;MALDI-TOF	Poly(3HB) and poly(3HB-co-3MP) were isolated from R. eutropha H16 (DSM428).		Yes	No				No		
Schlegelella thermodepolymerans	215580	PHA	Elbanna, K., Lütke-Eversloh, T., Jendrossek, D., Luftmann, H., & Steinbüchel, A. (2004). Studies on the biodegradability of polythioester copolymers and homopolymers by polyhydroxyalkanoate (PHA)-degrading bacteria and PHA depolymerases. Archives of microbiology, 182(2-3), 212-225.	PHA depolymerase	00029	00029 | PHA depolymerase | Schlegelella thermodepolymerans | P(3HB-co-3MP) PHA	Yes		MRSIRLKRLIAAVALGGAAAATQAASPLPRLNVDKTQISVSGLSAGGFMANQLGYAYSGTFMGVGIFAGGPYMCAGHSNYTSCMYNATITSSMRSAMQASIDNWSGAHIDPKAHVANQRVFLFVGNSDTTVGPNPMDAVHAQYQHNGVRRTARVRGRNSTAHVFPTDFDATGNNACNSTASPYIANCGYDGAKAVLSRIYGTLQPRNDAPAGANYIEFDQTAFTNNPGMASTGWVYVPANCAAGAQCRLHVALHGCQQSTGHIGDRFVKNTGYTRWADTNNIIVLFPQAKTDNTPRNTAASGMLPNPNACWDWVGWYGSNFAQKTGTQAAAIKAMVDHVASARPRLRLPAPTGVQTSGATSSSMVISWAAVQGAAGYNVYRDGTKVNATAVSGTSYTDNGLSPGTTYQWTVRAVNAQGPRPAVGPATGTTTGTAAVCFTSSNYAHVSAGRAYVSMGYTYANASHQNMGLWNVFVTTTLKQTGPNYYVIGTCP	2004.0	GC;NMR;FTIR;MS;MALDI-TOF	Poly(3HB) and poly(3HB-co-3MP) were isolated from R. eutropha H16 (DSM428).		Yes	No				No		
Schlegelella sp.	2838790	PHB	Romen, F., Reinhardt, S., & Jendrossek, D. (2004). Thermotolerant poly (3-hydroxybutyrate)-degrading bacteria from hot compost and characterization of the PHB depolymerase of Schlegelella sp. KB1a. Archives of microbiology, 182(2-3), 157-164.	PHB depolymerase	00030	00030 | PHB depolymerase | Schlegelella sp. | PHB PHA	Yes	AAT09963.1	MRSIRLKRLIAAVALGGAAAATQAASPLPRLNVDKTQISVSGLSAGGFMANQLGYAYSGTFMGVGIFAGGPYMCAGHSNYTSCMYNATITSSMRSAMQASIDNWSGAHIDPKAHVANQRVFLFVGNSDTTVGPNPMDAVHAQYQHNGVRRTARVRGRNSTAHVFPTDFDATGNNACNSTASPYIANCGYDGAKAVLSRIYGTLQPRNDAPAGANYIEFDQTAFTNNPGMASTGWVYVPANCAAGAQCRLHVALHGCQQSTGHIGDRFVKNTGYTRWADTNNIIVLFPQAKTDNTPRNTAASGMLPNPNACWDWVGWYGSNFAQKTGTQAAAIKAMVDHVASARPRLRLPAPTGVQTSGATSSSMVISWAAVQGAAGYNVYRDGTKVNATAVSGTSYTDNGLSPGTTYQWTVRAVNAQGPRPAVGPATGTTTGTAAVCFTSSNYAHVSAGRAYVSMGYTYANASHQNMGLWNVFVTTTLKQTGPNYYVIGTCP	2004.0	Clear zone;Spectrophotometry	PHB and poly(3-hydroxyvalerate) (PHV) were isolated from gluconate-grown or valerate-grown cells of Ralstonia eutropha H16 (DSMZ428) or Chromobacterium violaceum (DSMZ30191), respectively, by sodium hypochlorite digestion and subsequent solvent extraction with acetone/diethylether as described elsewhere (Jendrossek et al. 1993b). 		Yes	Yes	Compost	Compost	Germany	No		
Schlegelella sp.	2838790	PHA	Romen, F., Reinhardt, S., & Jendrossek, D. (2004). Thermotolerant poly (3-hydroxybutyrate)-degrading bacteria from hot compost and characterization of the PHB depolymerase of Schlegelella sp. KB1a. Archives of microbiology, 182(2-3), 157-164.	PHB depolymerase	00030	00030 | PHB depolymerase | Schlegelella sp. | PHB PHA	Yes	AAT09963.1	MRSIRLKRLIAAVALGGAAAATQAASPLPRLNVDKTQISVSGLSAGGFMANQLGYAYSGTFMGVGIFAGGPYMCAGHSNYTSCMYNATITSSMRSAMQASIDNWSGAHIDPKAHVANQRVFLFVGNSDTTVGPNPMDAVHAQYQHNGVRRTARVRGRNSTAHVFPTDFDATGNNACNSTASPYIANCGYDGAKAVLSRIYGTLQPRNDAPAGANYIEFDQTAFTNNPGMASTGWVYVPANCAAGAQCRLHVALHGCQQSTGHIGDRFVKNTGYTRWADTNNIIVLFPQAKTDNTPRNTAASGMLPNPNACWDWVGWYGSNFAQKTGTQAAAIKAMVDHVASARPRLRLPAPTGVQTSGATSSSMVISWAAVQGAAGYNVYRDGTKVNATAVSGTSYTDNGLSPGTTYQWTVRAVNAQGPRPAVGPATGTTTGTAAVCFTSSNYAHVSAGRAYVSMGYTYANASHQNMGLWNVFVTTTLKQTGPNYYVIGTCP	2004.0	Clear zone;Spectrophotometry	PHB and poly(3-hydroxyvalerate) (PHV) were isolated from gluconate-grown or valerate-grown cells of Ralstonia eutropha H16 (DSMZ428) or Chromobacterium violaceum (DSMZ30191), respectively, by sodium hypochlorite digestion and subsequent solvent extraction with acetone/diethylether as described elsewhere (Jendrossek et al. 1993b). 		Yes	Yes	Compost	Compost	Germany	No		
Schlegelella sp.	2838790	PHB	Romen, F., Reinhardt, S., & Jendrossek, D. (2004). Thermotolerant poly (3-hydroxybutyrate)-degrading bacteria from hot compost and characterization of the PHB depolymerase of Schlegelella sp. KB1a. Archives of microbiology, 182(2-3), 157-164.	PHB depolymerase	00031	00031 | PHB depolymerase | Schlegelella sp. | PHB PHA	Yes	AAT09963.1	MRSIRLKRLIAAVALGGAAAATQAASPLPRLNVDKTQISVSGLSAGGFMANQLGYAYSGTFMGVGIFAGGPYMCAGHSNYTSCMYNATITSSMRSAMQASIDNWSGAHIDPKAHVANQRVFLFVGNSDTTVGPNPMDAVHAQYQHNGVRRTARVRGRNSTAHVFPTDFDATGNNACNSTASPYIANCGYDGAKAVLSRIYGTLQPRNDAPAGANYIEFDQTAFTNNPGMASTGWVYVPANCAAGAQCRLHVALHGCQQSTGHIGDRFVKNTGYTRWADTNNIIVLFPQAKTDNTPRNTAASGMLPNPNACWDWVGWYGSNFAQKTGTQAAAIKAMVDHVASARPRLRLPAPTGVQTSGATSSSMVISWAAVQGAAGYNVYRDGTKVNATAVSGTSYTDNGLSPGTTYQWTVRAVNAQGPRPAVGPATGTTTGTAAVCFTSSNYAHVSAGRAYVSMGYTYANASHQNMGLWNVFVTTTLKQTGPNYYVIGTCP	2004.0	Clear zone;Spectrophotometry	PHB and poly(3-hydroxyvalerate) (PHV) were isolated from gluconate-grown or valerate-grown cells of Ralstonia eutropha H16 (DSMZ428) or Chromobacterium violaceum (DSMZ30191), respectively, by sodium hypochlorite digestion and subsequent solvent extraction with acetone/diethylether as described elsewhere (Jendrossek et al. 1993b). 		Yes	Yes	Compost	Compost	Germany	No		
Schlegelella sp.	2838790	PHA	Romen, F., Reinhardt, S., & Jendrossek, D. (2004). Thermotolerant poly (3-hydroxybutyrate)-degrading bacteria from hot compost and characterization of the PHB depolymerase of Schlegelella sp. KB1a. Archives of microbiology, 182(2-3), 157-164.	PHB depolymerase	00031	00031 | PHB depolymerase | Schlegelella sp. | PHB PHA	Yes	AAT09963.1	MRSIRLKRLIAAVALGGAAAATQAASPLPRLNVDKTQISVSGLSAGGFMANQLGYAYSGTFMGVGIFAGGPYMCAGHSNYTSCMYNATITSSMRSAMQASIDNWSGAHIDPKAHVANQRVFLFVGNSDTTVGPNPMDAVHAQYQHNGVRRTARVRGRNSTAHVFPTDFDATGNNACNSTASPYIANCGYDGAKAVLSRIYGTLQPRNDAPAGANYIEFDQTAFTNNPGMASTGWVYVPANCAAGAQCRLHVALHGCQQSTGHIGDRFVKNTGYTRWADTNNIIVLFPQAKTDNTPRNTAASGMLPNPNACWDWVGWYGSNFAQKTGTQAAAIKAMVDHVASARPRLRLPAPTGVQTSGATSSSMVISWAAVQGAAGYNVYRDGTKVNATAVSGTSYTDNGLSPGTTYQWTVRAVNAQGPRPAVGPATGTTTGTAAVCFTSSNYAHVSAGRAYVSMGYTYANASHQNMGLWNVFVTTTLKQTGPNYYVIGTCP	2004.0	Clear zone;Spectrophotometry	PHB and poly(3-hydroxyvalerate) (PHV) were isolated from gluconate-grown or valerate-grown cells of Ralstonia eutropha H16 (DSMZ428) or Chromobacterium violaceum (DSMZ30191), respectively, by sodium hypochlorite digestion and subsequent solvent extraction with acetone/diethylether as described elsewhere (Jendrossek et al. 1993b). 		Yes	Yes	Compost	Compost	Germany	No		
Sphingomonas macrogoltabidus	33050	PEG	Ohta, T., Tani, A., Kimbara, K., & Kawai, F. (2005). A novel nicotinoprotein aldehyde dehydrogenase involved in polyethylene glycol degradation. Applied microbiology and biotechnology, 68(5), 639-646.	PEG dehydrogenase	00032	00032 | PEG dehydrogenase | Sphingomonas macrogoltabidus | PEG	Yes	BAF98451.1	MCLVTLYRCTPIWVRNRGMHKFDFVVVGAGSAGCTVASRLSENGKYQVALLEAGGSHNNPLISIPFNFAFTVPKGPHNWSFETVPQEGLNGRRGYQPRGKVLGGSSSINAMVYIRGAKEDYEHWAALGNEGWSYEEVLPFFKKAQNRVKGANEYHAQGGPLTVSPPRSPNPLNDMFIKAGMDCQLPYNEDFNGETQEGIGCYELTQDRGKRCSAALAYVTPAEKRKNLTIFKQAFVEKVLVENGQATGVMVKLNGNLQLIKARREVILSCGAFQSPQLLLLSGIGAKDKLDPHKIKVVHELPGVGENLYDHVDFCLMYQSDSEHVLGKNARSVFRVAWNQFKYFAGRRGILTTNFNESGAFYFTNPDERSPDIQLHFAFTLVDQHGLKRHGRGGFGCHVCVLRPKSHGNLTLADANPATPPLIDPAFLKDERDVATLLAGVKRAQQILQAPAFDEIRGKPVYATASNNDDELIEDIRNRADTIYHPVGTCKMGPDSDPMAVVDSSLRVRGIRNLRVIDASIMPSIVSGNTNAPTIMIGEKGAQMILDEAESYT	2005.0	Spectrophotometry	PEG-aldehydes were prepared from PEGs by a reaction with the recombinant PEGDH			No				Yes		
Sphingomonas sp.	28214	O-PVA	Klomklang, W., Tani, A., Kimbara, K., Mamoto, R., Ueda, T., Shimao, M., & Kawai, F. (2005). Biochemical and molecular characterization of a periplasmic hydrolase for oxidized polyvinyl alcohol from Sphingomonas sp. strain 113P3. Microbiology, 151(4), 1255-1262.	PVA hydrolase	00033	00033 | PVA hydrolase | Sphingomonas sp. | PVA O-PVA	Yes	BAD95542.3	MFKPVVKSRSSRSFCYLAGCLAMVAATLSSTAQAKSEWACPEGFTPKAGLNTDFPSDGKKRAFVVVPPKDSAGGAPVWVPMVGTVEATNWNLNVPRSGNNAKLAEHGYMVISPVRQCAEQDPNLGAGACNGVGKDGWTWNPWNDGRAPDASGDKYKTDAGDDVRFLEAMVRCVGTKWKLDRKRLFLGGISAGGTMTNRALLFDSEFWAGGMPISGEWYSTKDDGSTVPFQETRKMVAAAPAKIWQGRVGPYPLPSKLDPMVVITVWGGEKDLWDCGPPLGLCSDYRPTTQASSNYFSSISNVVHVACSATHGHMWPQVNTDAFNLWALNTMASHPKGSSPKDFKLTAPPEGYSCKIGRFTDHYK	2005.0		PVA 117 [number-average molar mass (‘average molecular weight’, Mn) 75 000]. Oxidized PVA was prepared as described previously (Shimao et al., 2000)	Wako Pure Chemical Industries		No				Yes		
Sphingomonas sp.	28214	PVA	Klomklang, W., Tani, A., Kimbara, K., Mamoto, R., Ueda, T., Shimao, M., & Kawai, F. (2005). Biochemical and molecular characterization of a periplasmic hydrolase for oxidized polyvinyl alcohol from Sphingomonas sp. strain 113P3. Microbiology, 151(4), 1255-1262.	PVA hydrolase	00033	00033 | PVA hydrolase | Sphingomonas sp. | PVA O-PVA	Yes	BAD95543.3	MGSHAWGGAVFSAATLIAFGSVVHASGTVAETAPQSGHAVPADQLDGETLYKARCAACHDNAEGRTPSREVLSKNPASFILASMRTGAMVPMAEGLTLEEMTAIARAVGKADAKTDDGIDLRRIWGNSVEGTPLDAPQCSSAPTPVDLGAANQWNGWSTEKDNGRFQRKPALDVADIPKLKLKWAFQYPGSKNGQATVIGDRLFTTSTSGAVYALNAKTGCVYWRHAAEGATRTSPVIAALPEGAPAKTALFFSDFTKAAVALDAETGKQLWKTVVDDQPALQMTGSITYWDGKIYVPISSGTEAFAQIPTWECCKFRGALVALDAATGKILWKRYTTEQEPRPFKLNKAGRQMWGPSGGAIWVTPTVDEARRLIYVGTSNSYTDVPYDNSDSVMAIDADTGAVRWTVQLLADDNYIDGCWQKGKEHANCPNPLGPDFSIGAAPIYRKMADGKEFLLVGQKSGMIYALDPANKGAKIWERQLSLGSALGGIEFGTAADDGKVYAGVSDIASQAKDRGKPGLWALDIRTGEVAWNFLNAPDTKCRWNNWWCHGAFSQAISVIPGAIFAGSYDGHFRAFDTATGKIIWDVDTGTKAVTTLSGAKAFGGVMDGAGPTIAGGMVYVHSGYAGRSSESGGRDLRGTDGNILMAFSVDGK	2005.0		PVA 117 [number-average molar mass (‘average molecular weight’, Mn) 75 000]. Oxidized PVA was prepared as described previously (Shimao et al., 2000)	Wako Pure Chemical Industries		No				Yes		
Streptomyces sp.	1931	PEG	Ohta, T., Tani, A., Kimbara, K., & Kawai, F. (2005). A novel nicotinoprotein aldehyde dehydrogenase involved in polyethylene glycol degradation. Applied microbiology and biotechnology, 68(5), 639-646.	PEG aldehyde dehydrogenase	00035	00035 | PEG aldehyde dehydrogenase | Streptomyces sp. | PEG	Yes	BAF98449.1	MKEYPNLYIGGQWVSPHSDNMSTVINPSTEEVCAKIASGDKADVDAPVRAAREAFDSFWQSSRESRVKLLRDVVAGIQSRADEFAEAINQEMGAPLWWAQQAQVPAGIAHFATAADVLEKFKFVEAKGTTHLRREAIGVCGMITPWNWPLNQVACKIAAALAVGCTVVLKPAEQTPLDSILLAEVIDAAGAPPGVFNLVTGSGSVVGSALSDHPEVDMVSFTGSTRAGAMVAKAAADSIKRVSQELGGKSVNLVLPDADLQESVVRAVRSLMSNAGQTCSAGSRLLVPADRQEEAIAIAKQTAESIPVALSADADAPAIGPISTQRQYEQVKKLIGVGIDEGATLVTGGVESPSGATKGFFVKPTIFANVNNAMAIAQEEIFGPVLVIIAYEDVDQAVQIANDSPYGLSGYVQGPHEQAVEVASSIRTGQVFINNAHADFNAPFGGFKQSGNGREWGEVGFDEFLEY	2005.0	Spectrophotometry	PEG-aldehydes were prepared from PEGs by a reaction with the recombinant PEGDH			No				Yes		
Pseudomonas alcaligenes	43263	PCL	Kim, H. C., Kim, S. Y., & Rhee, Y. H. (2005). Molecular characterization of extracellular medium-chain-length poly (3-hydroxyalkanoate) depolymerase genes from Pseudomonas alcaligenes strains. The Journal of Microbiology, 43(3), 285-294.	MCL PHA depolymerase	00036	00036 | MCL PHA depolymerase | Pseudomonas alcaligenes | PCL PHA PHBV PHPV	Yes	AAQ72538.1	MLAPRSLLFCLLLFALPNAFADSRCSERAKTLLLPAKVSCSYKTTWIDSGLIGARQVIYQAPLGTPPAGGWPVVLIYQGSFFPLNNFTYYSNQPFGGYYEGKLVRALLDSGYAVIAPSAPADLFWQTNIPGLAQAYELTTDYDFLGNVFDAIASGHFGPLNSQRKYATGISSGGYNTSRMAVSFPGQFKALAIQSGSYATCSGPLCVVPDQLPADHXPTYFLHGFVDLTVPWWSMDLYYDRLLQQGIETARYTEPLGGHEWFAASPGKVLAWFNAHP	2005.0	Spectrophotometry	Polycaprolactone (PCL; number average molecular weight, 80,000) was purchased from the Aldrich Chemical (USA).	Sigma Aldrich	Yes	No	Water	Marine	South Korea	No		
Pseudomonas alcaligenes	43263	PHA	Kim, H. C., Kim, S. Y., & Rhee, Y. H. (2005). Molecular characterization of extracellular medium-chain-length poly (3-hydroxyalkanoate) depolymerase genes from Pseudomonas alcaligenes strains. The Journal of Microbiology, 43(3), 285-294.	MCL PHA depolymerase	00036	00036 | MCL PHA depolymerase | Pseudomonas alcaligenes | PCL PHA PHBV PHPV	Yes	AAQ72538.1	MLAPRSLLFCLLLFALPNAFADSRCSERAKTLLLPAKVSCSYKTTWIDSGLIGARQVIYQAPLGTPPAGGWPVVLIYQGSFFPLNNFTYYSNQPFGGYYEGKLVRALLDSGYAVIAPSAPADLFWQTNIPGLAQAYELTTDYDFLGNVFDAIASGHFGPLNSQRKYATGISSGGYNTSRMAVSFPGQFKALAIQSGSYATCSGPLCVVPDQLPADHXPTYFLHGFVDLTVPWWSMDLYYDRLLQQGIETARYTEPLGGHEWFAASPGKVLAWFNAHP	2005.0	Clear zone	MCL-PHAs were produced by culturing P.oleovorans ATCC 29347 in a mineral salt medium containing carboxylic acids with corresponding chemical structures as described elsewhere (Lageveen et al., 1988). Synthesized PHAs were isolated and purified from lyophilized cells by extraction with hot chloroform using a Soxhlet apparatus as previously described (Kim et al., 2000c).		Yes	No	Seawater	Marine		No		
Pseudomonas alcaligenes	43263	PHBV	Kim, H. C., Kim, S. Y., & Rhee, Y. H. (2005). Molecular characterization of extracellular medium-chain-length poly (3-hydroxyalkanoate) depolymerase genes from Pseudomonas alcaligenes strains. The Journal of Microbiology, 43(3), 285-294.	MCL PHA depolymerase	00036	00036 | MCL PHA depolymerase | Pseudomonas alcaligenes | PCL PHA PHBV PHPV	Yes	AAQ72538.1	MLAPRSLLFCLLLFALPNAFADSRCSERAKTLLLPAKVSCSYKTTWIDSGLIGARQVIYQAPLGTPPAGGWPVVLIYQGSFFPLNNFTYYSNQPFGGYYEGKLVRALLDSGYAVIAPSAPADLFWQTNIPGLAQAYELTTDYDFLGNVFDAIASGHFGPLNSQRKYATGISSGGYNTSRMAVSFPGQFKALAIQSGSYATCSGPLCVVPDQLPADHXPTYFLHGFVDLTVPWWSMDLYYDRLLQQGIETARYTEPLGGHEWFAASPGKVLAWFNAHP	2005.0	Spectrophotometry	 Poly(3-hydroxybutyrate-co-3-hydroxyvalerate) (PHBV) copolyesters were synthesized by a threonine-overproducing mutant of Alcaligenes sp. SH-69 (Choi et al., 2003)		Yes	No	Water	Marine	South Korea	No		
Pseudomonas alcaligenes	43263	PHPV	Kim, H. C., Kim, S. Y., & Rhee, Y. H. (2005). Molecular characterization of extracellular medium-chain-length poly (3-hydroxyalkanoate) depolymerase genes from Pseudomonas alcaligenes strains. The Journal of Microbiology, 43(3), 285-294.	MCL PHA depolymerase	00036	00036 | MCL PHA depolymerase | Pseudomonas alcaligenes | PCL PHA PHBV PHPV	Yes	AAQ72538.1	MLAPRSLLFCLLLFALPNAFADSRCSERAKTLLLPAKVSCSYKTTWIDSGLIGARQVIYQAPLGTPPAGGWPVVLIYQGSFFPLNNFTYYSNQPFGGYYEGKLVRALLDSGYAVIAPSAPADLFWQTNIPGLAQAYELTTDYDFLGNVFDAIASGHFGPLNSQRKYATGISSGGYNTSRMAVSFPGQFKALAIQSGSYATCSGPLCVVPDQLPADHXPTYFLHGFVDLTVPWWSMDLYYDRLLQQGIETARYTEPLGGHEWFAASPGKVLAWFNAHP	2005.0	Spectrophotometry	 Poly(3-hydroxybutyrate-co-3-hydroxyvalerate) (PHBV) copolyesters were synthesized by a threonine-overproducing mutant of Alcaligenes sp. SH-69 (Choi et al., 2003)		Yes	No	Water	Marine	South Korea	No		
Cryptococcus sp.	2046349	PBS	Masaki, K., Kamini, N. R., Ikeda, H., & Iefuji, H. (2005). Cutinase-like enzyme from the yeast Cryptococcus sp. strain S-2 hydrolyzes polylactic acid and other biodegradable plastics. Appl. Environ. Microbiol., 71(11), 7548-7550.	Cutinase	00037	00037 | Cutinase | Cryptococcus sp. | PBS PCL PHB PLA PHA	Yes	BAC67242.1	MLVSALALAVLSAASLGRAAPTPESAEAHELEARATSSACPQYVLINTRGTGEPQGQSAGFRTMNSQITAALSGGTIYNTVYTADFSQNSAAGTADIIRRINSGLAANPNVCYILQGYSQGAAATVVALQQLGTSGAAFAVKGVFLIGNPDHKSGLTCNVDSNGGTTTRNVNGLSVAYQGSVPSGWVSKTLDVCAYGDGVCDTAHGFGINAQHLSYPSDQGVQTMGYKFAVNKLGGSA	2005.0	Spectrophotometry	PBS Bionolle; no. 1001; Showa Highpolymer Co., Ltd., Tokyo, Japan	Showa Denko		No				Yes		
Cryptococcus sp.	2046349	PCL	Masaki, K., Kamini, N. R., Ikeda, H., & Iefuji, H. (2005). Cutinase-like enzyme from the yeast Cryptococcus sp. strain S-2 hydrolyzes polylactic acid and other biodegradable plastics. Appl. Environ. Microbiol., 71(11), 7548-7550.	Cutinase	00037	00037 | Cutinase | Cryptococcus sp. | PBS PCL PHB PLA PHA	Yes	BAC67242.1	MLVSALALAVLSAASLGRAAPTPESAEAHELEARATSSACPQYVLINTRGTGEPQGQSAGFRTMNSQITAALSGGTIYNTVYTADFSQNSAAGTADIIRRINSGLAANPNVCYILQGYSQGAAATVVALQQLGTSGAAFAVKGVFLIGNPDHKSGLTCNVDSNGGTTTRNVNGLSVAYQGSVPSGWVSKTLDVCAYGDGVCDTAHGFGINAQHLSYPSDQGVQTMGYKFAVNKLGGSA	2005.0	Spectrophotometry	PCL Mol wt, 1.0  104 ; Wako Pure Chemical Industries, Ltd., Osaka, Japan	Wako Pure Chemical		No				Yes		
Cryptococcus sp.	2046349	PHB	Masaki, K., Kamini, N. R., Ikeda, H., & Iefuji, H. (2005). Cutinase-like enzyme from the yeast Cryptococcus sp. strain S-2 hydrolyzes polylactic acid and other biodegradable plastics. Appl. Environ. Microbiol., 71(11), 7548-7550.	Cutinase	00037	00037 | Cutinase | Cryptococcus sp. | PBS PCL PHB PLA PHA	Yes	BAC67242.1	MLVSALALAVLSAASLGRAAPTPESAEAHELEARATSSACPQYVLINTRGTGEPQGQSAGFRTMNSQITAALSGGTIYNTVYTADFSQNSAAGTADIIRRINSGLAANPNVCYILQGYSQGAAATVVALQQLGTSGAAFAVKGVFLIGNPDHKSGLTCNVDSNGGTTTRNVNGLSVAYQGSVPSGWVSKTLDVCAYGDGVCDTAHGFGINAQHLSYPSDQGVQTMGYKFAVNKLGGSA	2005.0	Spectrophotometry				No				Yes		
Cryptococcus sp.	2046349	PLA	Masaki, K., Kamini, N. R., Ikeda, H., & Iefuji, H. (2005). Cutinase-like enzyme from the yeast Cryptococcus sp. strain S-2 hydrolyzes polylactic acid and other biodegradable plastics. Appl. Environ. Microbiol., 71(11), 7548-7550.	Cutinase	00037	00037 | Cutinase | Cryptococcus sp. | PBS PCL PHB PLA PHA	Yes	BAC67242.1	MLVSALALAVLSAASLGRAAPTPESAEAHELEARATSSACPQYVLINTRGTGEPQGQSAGFRTMNSQITAALSGGTIYNTVYTADFSQNSAAGTADIIRRINSGLAANPNVCYILQGYSQGAAATVVALQQLGTSGAAFAVKGVFLIGNPDHKSGLTCNVDSNGGTTTRNVNGLSVAYQGSVPSGWVSKTLDVCAYGDGVCDTAHGFGINAQHLSYPSDQGVQTMGYKFAVNKLGGSA	2005.0	Spectrophotometry	PLA LACEA; HT-100; mol wt, 1.4  105 ; Mitsui Chemicals, Inc., Tokyo, Japan	Mitsubishi Gas Chemical		No				Yes		
Cryptococcus sp.	2046349	PHA	Masaki, K., Kamini, N. R., Ikeda, H., & Iefuji, H. (2005). Cutinase-like enzyme from the yeast Cryptococcus sp. strain S-2 hydrolyzes polylactic acid and other biodegradable plastics. Appl. Environ. Microbiol., 71(11), 7548-7550.	Cutinase	00037	00037 | Cutinase | Cryptococcus sp. | PBS PCL PHB PLA PHA	Yes	BAC67242.1	MLVSALALAVLSAASLGRAAPTPESAEAHELEARATSSACPQYVLINTRGTGEPQGQSAGFRTMNSQITAALSGGTIYNTVYTADFSQNSAAGTADIIRRINSGLAANPNVCYILQGYSQGAAATVVALQQLGTSGAAFAVKGVFLIGNPDHKSGLTCNVDSNGGTTTRNVNGLSVAYQGSVPSGWVSKTLDVCAYGDGVCDTAHGFGINAQHLSYPSDQGVQTMGYKFAVNKLGGSA	2005.0	Spectrophotometry	PLA LACEA; HT-100; mol wt, 1.4  105 ; Mitsui Chemicals, Inc., Tokyo, Japan	Mitsubishi Gas Chemical		No				Yes		
Priestia megaterium	1404	PHB	Takaku, H., Kimoto, A., Kodaira, S., Nashimoto, M., & Takagi, M. (2006). Isolation of a Gram-positive poly (3-hydroxybutyrate)(PHB)-degrading bacterium from compost, and cloning and characterization of a gene encoding PHB depolymerase of Bacillus megaterium N-18-25-9. FEMS microbiology letters, 264(2), 152-159.	PHB depolymerase	00039	00039 | PHB depolymerase | Bacillus megaterium | PHB PHA	Yes	BAF35850.1	MKRLFIAGMIFMLFFSLGAVSSSAAGSFTSKTYNGRTYKLYVPSSYQGGAALPLVVMLHGCTQDPDQFAAGTQMNALAETEKFLVLYPEQPSSANSNKCWNWFDTAHQSRGSGEPALIAGMVNQIKSSYSIDADQVFVGGLSAGAAMSVIMGATYPDIFAAISVGAGLEYKAATSVTGAYTAMSSGGPNPIQQGDLAYSAMGEHKRVVPVILFHGTADYTVAPINAHQILSQWAQTNDRASDGLDNNNIDDTADQTLPGTVSGGRSYTQYIYKDTAGKTVMEKYMIEGMGHAWPGGSTSGSYTDPKGPNATTLSWNFFKSHPKNSDAPNPGDISPPVTAASPAGGTYGSSVSVTLSTNEPATTYYTLDGSTPTVNSLKYSEPISINSSKTIKFFSVDAAGNQEGVKTEVYQISGTSEKSSVFSSLAAEDGFIGNLSADGMSSSIHKIGDKGMYNTDTYRTILSFDTSSLPDDAIITDVSLKIYRKSSTGNISSLKGDIKTGVFGTSSALEQIDYQASPSISAAFQMSVPSLDNGYTTIQLPSSLLGYMNRNGKTQFRLSSSGSADFLSDVVEIYGGDNPAYAPTLTVSYK	2006.0	Clear zone	The PHB granules were purchased from Sigma-Aldrich (Steinheim, Germany).	Sigma Aldrich	Yes	Yes	Compost	Compost	Japan	No		
Priestia megaterium	1404	PHA	Takaku, H., Kimoto, A., Kodaira, S., Nashimoto, M., & Takagi, M. (2006). Isolation of a Gram-positive poly (3-hydroxybutyrate)(PHB)-degrading bacterium from compost, and cloning and characterization of a gene encoding PHB depolymerase of Bacillus megaterium N-18-25-9. FEMS microbiology letters, 264(2), 152-159.	PHB depolymerase	00039	00039 | PHB depolymerase | Bacillus megaterium | PHB PHA	Yes	BAF35850.1	MKRLFIAGMIFMLFFSLGAVSSSAAGSFTSKTYNGRTYKLYVPSSYQGGAALPLVVMLHGCTQDPDQFAAGTQMNALAETEKFLVLYPEQPSSANSNKCWNWFDTAHQSRGSGEPALIAGMVNQIKSSYSIDADQVFVGGLSAGAAMSVIMGATYPDIFAAISVGAGLEYKAATSVTGAYTAMSSGGPNPIQQGDLAYSAMGEHKRVVPVILFHGTADYTVAPINAHQILSQWAQTNDRASDGLDNNNIDDTADQTLPGTVSGGRSYTQYIYKDTAGKTVMEKYMIEGMGHAWPGGSTSGSYTDPKGPNATTLSWNFFKSHPKNSDAPNPGDISPPVTAASPAGGTYGSSVSVTLSTNEPATTYYTLDGSTPTVNSLKYSEPISINSSKTIKFFSVDAAGNQEGVKTEVYQISGTSEKSSVFSSLAAEDGFIGNLSADGMSSSIHKIGDKGMYNTDTYRTILSFDTSSLPDDAIITDVSLKIYRKSSTGNISSLKGDIKTGVFGTSSALEQIDYQASPSISAAFQMSVPSLDNGYTTIQLPSSLLGYMNRNGKTQFRLSSSGSADFLSDVVEIYGGDNPAYAPTLTVSYK	2006.0	Clear zone	The PHB granules were purchased from Sigma-Aldrich (Steinheim, Germany).	Sigma Aldrich	Yes	Yes	Compost	Compost	Japan	No		
Pseudomonas chlororaphis	587753	PU	Howard, G. T., Mackie, R. I., Cann, I. K. O., Ohene‐Adjei, S., Aboudehen, K. S., Duos, B. G., & Childers, G. W. (2007). Effect of insertional mutations in the pueA and pueB genes encoding two polyurethanases in Pseudomonas chlororaphis contained within a gene cluster. Journal of applied microbiology, 103(6), 2074-2083.	Polyurethanase	00041	00041 | Polyurethanase | Pseudomonas chlororaphis | PU	Yes	ABM54447.1	MGVFDYKNFTASDSKALFSDALAITLYSYHNIDNGFAEGYQHNGFGLGLPATLVTALIGSGNSQGVIPGIPWNPDSEKAALDALHQAGWSTISAQQLGYDGKVDGRGTFFGEKAGYGTAQVEILGKYDAQGHLESIGIAFRGTSGPRESVISDTIGDVINDLLAALGPKDYAKNYAGEAFGKLLGDVAAFAQANGLSGKDLVSGHSLGGLGVNSLADLSSERWSGFYKDSNYIAYASPTQSASDKVLNIGYENDPVFRALDGSTFNLSSLGVHDAHQDSATNNIVNFNDHYASTLWNVLPSSILNIPTWLSHLPTGYGDGLSRVLESKFYDFTSKDSTIVVANLSDPARASTWVQDLNRNAETHKGSTFIIGSDGNDLIQGGSGNDYLEGRAGNDTFRDSGGYNIILGGQGSNTLDLQQSVKNYSFASDGAGTLYLRDANGGISMTRDIGAIQSKEPGFLWGLFKDDVIHQVTDQGLKAGGQLTQYASSVRGDAGDNVLKAHAGGDWLFGLDGNDHLIGGQGNDVFVGGAGNDLMEAGGGNNTFLFTGHFGQDRILGYQGGDKLVFMGVSGVLPDQDYRAHASSSGNDTVLTFGQDSVTLVGVSLEHLNGSGIVLA	2007.0	Clear zone	Impranil	Bayer 	No	No		Culture collection		No		
Agromyces sp. 	51513	Nylon	Yasuhira, K., Uedo, Y., Takeo, M., Kato, D. I., & Negoro, S. (2007). Genetic organization of nylon-oligomer-degrading enzymes from alkalophilic bacterium, Agromyces sp. KY5R. Journal of bioscience and bioengineering, 104(6), 521-524.	Nylon hydrolase	00042	00042 | Nylon Oligomer Degrading Enzyme | Agromyces sp. | Nylon	Yes	BAE97629.1	MLRFDFPGVSIGAAHYEEGPTGATVIHIPAGARTAVDARGGAVGLSGGYDFNHAICLAGGAGYGLEAGAGVSGALLERLEYRTGFAELQLVSSAVIYDFSARSTAVYPDKALGRAALEFAVPGEFPQGRAGAGMSASAGKVDWDRTEITGQGAAFRRLGDVRILAVVVPNPVGVIVDRAGTVVRGNYDAQTGVRRHPVFDYQEAFAEQVPPVTEAGNTTISAIVTNVRMSPVELNQFAKQVHSSMHRGIQPFHTDMDGDTLFAVTTDEIDLPTTPGSSRGRLSVNATALGAIASEVMWDAVLEAGK	2007.0	Spectrophotometry				No	Sludge	Sewage/Sludge	Japan	No		
Agromyces sp. 	51513	Nylon	Yasuhira, K., Uedo, Y., Takeo, M., Kato, D. I., & Negoro, S. (2007). Genetic organization of nylon-oligomer-degrading enzymes from alkalophilic bacterium, Agromyces sp. KY5R. Journal of bioscience and bioengineering, 104(6), 521-524.	Nylon hydrolase	00043	00043 | Nylon Oligomer Degrading Enzyme | Agromyces sp. | Nylon	Yes	BAE97621.1	MNARSTGQHPARYPGAAAGEPTLDSWQEAPHNRWAFARLGELLPTAAVSRRDPATPAEPVVRLDALATRLPDLEQRLEETCTDAFLVLRGSEVLAEYYRAGFAPDDRHLLMSVSKSLCGTVVGALIDEGRIDPAQPVTEYVPELAGSVYDGPSVLQVLDMQISIDYNEDYVDPASEVQTHDRSAGWRTRRDGDPADTYEFLTTLRGDGGTGEFQYCSANTDVLAWIVERVTGLRYVEALSTYLWANVDADRDATITVDQTGFGFANGGVSCTARDLARVGRMMLDGGVAPGGRVVSQGWVESVLAGGSREAMTDEGFTSAFPEGSYTRQWWCTGNERGNVSGIGIHGQNLWLDPRTDSVIVKLSSWPDPDTRHWHGLQSGILLDVSRALDAV	2007.0	Spectrophotometry				No	Sludge	Sewage/Sludge	Japan	No		
Agromyces sp. 	51513	Nylon	Yasuhira, K., Uedo, Y., Takeo, M., Kato, D. I., & Negoro, S. (2007). Genetic organization of nylon-oligomer-degrading enzymes from alkalophilic bacterium, Agromyces sp. KY5R. Journal of bioscience and bioengineering, 104(6), 521-524.	Nylon hydrolase	00044	00044 | Nylon Oligomer Degrading Enzyme | Agromyces sp. | Nylon	Yes	BAE97630.1	MNARSTGQHPARYPGAAAGEPTLDSWQEAPHNRWAFARLGELLPTAAVSRRDPATPAEPVVRLDALATRLPDLEQRLEETCTDAFLVLRGTEVVAEYYRAGFAPDDRHLLMSVSKSLCGTVVGALVDEGRIDPAQPVTEYVPELAGSVYDGPSVLQVLDMQISIDYNEDYVDPASEVQTHGRSAGWRTRRHGDPADTYEFLTTLRGDGSTGEFQYCSANTDVLAWIVERVTGLRYVEALSTYLWAKLDADRDATITVDTTGFGFAHGGVSCTARDLARVGRMMLDGGVAPGGRVVSEDWVRRVLAGGSHEAMTDKGFTNTFPDGSYTRQWWCTGNERGNVSGIGIHGQNLWLDPLTDSVIVKLSSWPDPDTEHWHRLQNGILLDVSRALDAV	2007.0	Spectrophotometry				No	Sludge	Sewage/Sludge	Japan	No		
Pseudomonas chlororaphis	587753	PU	Howard, G. T., Mackie, R. I., Cann, I. K. O., Ohene‐Adjei, S., Aboudehen, K. S., Duos, B. G., & Childers, G. W. (2007). Effect of insertional mutations in the pueA and pueB genes encoding two polyurethanases in Pseudomonas chlororaphis contained within a gene cluster. Journal of applied microbiology, 103(6), 2074-2083.	Polyurethanase	00046	00046 | Polyurethanase | Pseudomonas chlororaphis | PU	Yes	ABM54446.1	MSMSIFDYKTALGGDGKALYSEAITLALYASTPTGEALPGTAWRPISVSQLGYQGNVSAQGTISGEQAIVSDAQSRCWANTTRPGSCCPSASSFRGTRQPQGRYQRLAGGLRVGLLPTTTSRLAFDNLLGKVAAFAAAQGLSGSDVLVTGHSLGGLGGQPRGGHEQRSLGRLLPGRQLLGFASPTQSANSSQVLNIGYETTRCSAPWTALISTALSLGTHWQAPGVATNNIVSFTDHYSSFLGEVDSPEHPQSAVLVGPQCGGLRRGLNRLINSDFYDLTSRDSTVVISNLSEGKRDQVWVKDLNLYAEKHTGSTFIIGTQSNDLLHGGKGNDYLDGGAGDDRFRDDGGYNIIHGGQGHNVLELQQPLKNFSIANDGDGTLYIRDAYGGISMTRDVGALVSHETGSWWQLFGKDVSHSVTADGLQNGNQWTAYNHSLNGDAYGNALVASVDGDWLFGHGGDDLLSSDKANVTFVGGTGNDVMHSSGGGGNTFLFSGNFGFDLIHGYQNTDKLVFMGVPGVDAHYDYSQHLSQNGNDTLVQVFGEFLRVNPWWGSAWTSLSGSGLVFA	2007.0	Clear zone	Impranil	Bayer 	No	No		Culture collection		No		
Uncultured bacterium	77133	PLA	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00047	00047 | PLA depolymerase | Uncultured bacterium | PLA PBS PBSA PCL PES PHB PHA	Yes	BAF57213.1	MEMVKGVHLAIAALLFLCVLPGNADASEKQFDLVLVHGLTNKHRWSDSFLRALVNEWGSGNVYVIYTNQSMQVSKRTIDGKTITFIGKNDFSAGDDSVKDQAEIMAEKIEVLKRDHGLSPQFYIIAHSMGGLVSRQYIYDHPNTVAGLVTLGTPHHGSPLASDFDWLGFFIGAEAAMDNLRPEWVEDFNRRFPVENAPLYNGGKIYTIRGDSDGKIWEWGAMGELYVGWHILHKKHGTDSDGLVPHASAVIEGAVHLADFPNYHHLDLVTREEVAKKAAEVLR	2008.0	Clear zone;Spectrophotometry	Poly(DL-lactic acid) with weight-average molecular weights of 0.5×104 (PLA0005) and 2.0×104 (PLA0020) and poly(caprolactone) (PCL) were purchased from Wako Pure Chemical Industries (Tokyo, Japan).	Wako Pure Chemical	Yes	No				Yes		
Uncultured bacterium	77133	PBS	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00047	00047 | PLA depolymerase | Uncultured bacterium | PLA PBS PBSA PCL PES PHB PHA	Yes	BAF57212.1	METVKGVHLAIAALLFLCVLPGNADASEKQFDLVLVHGLTNKHRWSDSFLRALVNEWGSGNVYVIYTNQSMQVSKRTIDGKTITFIGKNDFSAGDDSVKDQAEIMAEKIEVLKRDHGLSPQFYIIAHSMGGLVSRQYIYDHPNTVAGLVTLGTPHHGSPLASDFDWLGFFIGAEAAMDNLRPEWVEDFNRRFPVENAPLYNGGKIYTIRGDSDGKIWEWGAMGELYVGWHILHKKHGTDSDGLVPHASAVIEGAVHLADFPNYHHLDLVTREEVAKKAAEVLR	2008.0	Spectrophotometry	PBS (BIONOLLE 1001™; PBS1001; weight-average molecular weight, 2.6×105 ) and PBSA (BIONOLLE emulsion EM-301™ were purchased from Showa Highpolymer (Tokyo, Japan).	Showa Denko		No				Yes		
Uncultured bacterium	77133	PBSA	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00047	00047 | PLA depolymerase | Uncultured bacterium | PLA PBS PBSA PCL PES PHB PHA	Yes	BAF57212.1	METVKGVHLAIAALLFLCVLPGNADASEKQFDLVLVHGLTNKHRWSDSFLRALVNEWGSGNVYVIYTNQSMQVSKRTIDGKTITFIGKNDFSAGDDSVKDQAEIMAEKIEVLKRDHGLSPQFYIIAHSMGGLVSRQYIYDHPNTVAGLVTLGTPHHGSPLASDFDWLGFFIGAEAAMDNLRPEWVEDFNRRFPVENAPLYNGGKIYTIRGDSDGKIWEWGAMGELYVGWHILHKKHGTDSDGLVPHASAVIEGAVHLADFPNYHHLDLVTREEVAKKAAEVLR	2008.0	Spectrophotometry	PBS (BIONOLLE 1001™; PBS1001; weight-average molecular weight, 2.6×105 ) and PBSA (BIONOLLE emulsion EM-301™ were purchased from Showa Highpolymer (Tokyo, Japan).	Showa Denko		No				Yes		
Uncultured bacterium	77133	PCL	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00047	00047 | PLA depolymerase | Uncultured bacterium | PLA PBS PBSA PCL PES PHB PHA	Yes	BAF57212.1	METVKGVHLAIAALLFLCVLPGNADASEKQFDLVLVHGLTNKHRWSDSFLRALVNEWGSGNVYVIYTNQSMQVSKRTIDGKTITFIGKNDFSAGDDSVKDQAEIMAEKIEVLKRDHGLSPQFYIIAHSMGGLVSRQYIYDHPNTVAGLVTLGTPHHGSPLASDFDWLGFFIGAEAAMDNLRPEWVEDFNRRFPVENAPLYNGGKIYTIRGDSDGKIWEWGAMGELYVGWHILHKKHGTDSDGLVPHASAVIEGAVHLADFPNYHHLDLVTREEVAKKAAEVLR	2008.0	Spectrophotometry	Poly(DL-lactic acid) with weight-average molecular weights of 0.5×104 (PLA0005) and 2.0×104 (PLA0020) and poly(caprolactone) (PCL) were purchased from Wako Pure Chemical Industries (Tokyo, Japan).	Wako Pure Chemical	Yes	No				Yes		
Uncultured bacterium	77133	PES	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00047	00047 | PLA depolymerase | Uncultured bacterium | PLA PBS PBSA PCL PES PHB PHA	Yes	BAF57212.1	METVKGVHLAIAALLFLCVLPGNADASEKQFDLVLVHGLTNKHRWSDSFLRALVNEWGSGNVYVIYTNQSMQVSKRTIDGKTITFIGKNDFSAGDDSVKDQAEIMAEKIEVLKRDHGLSPQFYIIAHSMGGLVSRQYIYDHPNTVAGLVTLGTPHHGSPLASDFDWLGFFIGAEAAMDNLRPEWVEDFNRRFPVENAPLYNGGKIYTIRGDSDGKIWEWGAMGELYVGWHILHKKHGTDSDGLVPHASAVIEGAVHLADFPNYHHLDLVTREEVAKKAAEVLR	2008.0	Spectrophotometry	Poly(ethylene succinate) (PES) was provided by Nippon Shokubai.	Nippon Shokubai		No				Yes		
Uncultured bacterium	77133	PHB	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00047	00047 | PLA depolymerase | Uncultured bacterium | PLA PBS PBSA PCL PES PHB PHA	Yes	BAF57212.1	METVKGVHLAIAALLFLCVLPGNADASEKQFDLVLVHGLTNKHRWSDSFLRALVNEWGSGNVYVIYTNQSMQVSKRTIDGKTITFIGKNDFSAGDDSVKDQAEIMAEKIEVLKRDHGLSPQFYIIAHSMGGLVSRQYIYDHPNTVAGLVTLGTPHHGSPLASDFDWLGFFIGAEAAMDNLRPEWVEDFNRRFPVENAPLYNGGKIYTIRGDSDGKIWEWGAMGELYVGWHILHKKHGTDSDGLVPHASAVIEGAVHLADFPNYHHLDLVTREEVAKKAAEVLR	2008.0	Spectrophotometry	 Poly (3-hydroxybutyric acid) (PHB) was purchased from Sigma-Aldrich Chemical (St. Louis, MO, USA).	Sigma Aldrich	Yes	No				Yes		
Uncultured bacterium	77133	PHA	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00047	00047 | PLA depolymerase | Uncultured bacterium | PLA PBS PBSA PCL PES PHB PHA	Yes	BAF57212.1	METVKGVHLAIAALLFLCVLPGNADASEKQFDLVLVHGLTNKHRWSDSFLRALVNEWGSGNVYVIYTNQSMQVSKRTIDGKTITFIGKNDFSAGDDSVKDQAEIMAEKIEVLKRDHGLSPQFYIIAHSMGGLVSRQYIYDHPNTVAGLVTLGTPHHGSPLASDFDWLGFFIGAEAAMDNLRPEWVEDFNRRFPVENAPLYNGGKIYTIRGDSDGKIWEWGAMGELYVGWHILHKKHGTDSDGLVPHASAVIEGAVHLADFPNYHHLDLVTREEVAKKAAEVLR	2008.0	Spectrophotometry	 Poly (3-hydroxybutyric acid) (PHB) was purchased from Sigma-Aldrich Chemical (St. Louis, MO, USA).	Sigma Aldrich	Yes	No				Yes		
Uncultured bacterium	77133	PBS	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00048	00048 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PLA PHA	Yes	BAF57214.1	MHESVHAESLWLTMDDGAEVYVRVWEPAARAAADSSDDAPAPPAAAGGPRAVLQLAHGMTEHSGRYDDFARFLAGRGFAVVGNDHRGHGHTGERADSMGYLADQDGFERLVDDLRAVHEWACRRWPGAPRFLMGHSMGSFLVRRYIQRYGDTVAGVIIMGTAGNPGLPGKIGRRLARLEMRRRGPRHPSMLLTSLVFGGYNKKIRSPKTAFDWLSRDAEAVKAYVADPWCGFVPSAGFYFDLLTGLLLIHDEREIARIPKDLPMLFLSGDADPVTGYGKGVERVIAQYERHGLRRMTSILYKDARHELLNELNKEEVYGDILKWLENTQAGILRNLSK	2008.0	Spectrophotometry	PBS (BIONOLLE 1001™; PBS1001; weight-average molecular weight, 2.6×105 ) and PBSA (BIONOLLE emulsion EM-301™ were purchased from Showa Highpolymer (Tokyo, Japan).	Showa Denko		No				Yes		
Uncultured bacterium	77133	PBSA	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00048	00048 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PLA PHA	Yes	BAF57214.1	MHESVHAESLWLTMDDGAEVYVRVWEPAARAAADSSDDAPAPPAAAGGPRAVLQLAHGMTEHSGRYDDFARFLAGRGFAVVGNDHRGHGHTGERADSMGYLADQDGFERLVDDLRAVHEWACRRWPGAPRFLMGHSMGSFLVRRYIQRYGDTVAGVIIMGTAGNPGLPGKIGRRLARLEMRRRGPRHPSMLLTSLVFGGYNKKIRSPKTAFDWLSRDAEAVKAYVADPWCGFVPSAGFYFDLLTGLLLIHDEREIARIPKDLPMLFLSGDADPVTGYGKGVERVIAQYERHGLRRMTSILYKDARHELLNELNKEEVYGDILKWLENTQAGILRNLSK	2008.0	Spectrophotometry	PBS (BIONOLLE 1001™; PBS1001; weight-average molecular weight, 2.6×105 ) and PBSA (BIONOLLE emulsion EM-301™ were purchased from Showa Highpolymer (Tokyo, Japan).	Showa Denko		No				Yes		
Uncultured bacterium	77133	PCL	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00048	00048 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PLA PHA	Yes	BAF57214.1	MHESVHAESLWLTMDDGAEVYVRVWEPAARAAADSSDDAPAPPAAAGGPRAVLQLAHGMTEHSGRYDDFARFLAGRGFAVVGNDHRGHGHTGERADSMGYLADQDGFERLVDDLRAVHEWACRRWPGAPRFLMGHSMGSFLVRRYIQRYGDTVAGVIIMGTAGNPGLPGKIGRRLARLEMRRRGPRHPSMLLTSLVFGGYNKKIRSPKTAFDWLSRDAEAVKAYVADPWCGFVPSAGFYFDLLTGLLLIHDEREIARIPKDLPMLFLSGDADPVTGYGKGVERVIAQYERHGLRRMTSILYKDARHELLNELNKEEVYGDILKWLENTQAGILRNLSK	2008.0	Spectrophotometry	Poly(DL-lactic acid) with weight-average molecular weights of 0.5×104 (PLA0005) and 2.0×104 (PLA0020) and poly(caprolactone) (PCL) were purchased from Wako Pure Chemical Industries (Tokyo, Japan).	Wako Pure Chemical	Yes	No				Yes		
Uncultured bacterium	77133	PES	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00048	00048 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PLA PHA	Yes	BAF57214.1	MHESVHAESLWLTMDDGAEVYVRVWEPAARAAADSSDDAPAPPAAAGGPRAVLQLAHGMTEHSGRYDDFARFLAGRGFAVVGNDHRGHGHTGERADSMGYLADQDGFERLVDDLRAVHEWACRRWPGAPRFLMGHSMGSFLVRRYIQRYGDTVAGVIIMGTAGNPGLPGKIGRRLARLEMRRRGPRHPSMLLTSLVFGGYNKKIRSPKTAFDWLSRDAEAVKAYVADPWCGFVPSAGFYFDLLTGLLLIHDEREIARIPKDLPMLFLSGDADPVTGYGKGVERVIAQYERHGLRRMTSILYKDARHELLNELNKEEVYGDILKWLENTQAGILRNLSK	2008.0	Spectrophotometry	Poly(ethylene succinate) (PES) was provided by Nippon Shokubai.	Nippon Shokubai		No				Yes		
Uncultured bacterium	77133	PLA	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00048	00048 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PLA PHA	Yes	BAF57214.1	MHESVHAESLWLTMDDGAEVYVRVWEPAARAAADSSDDAPAPPAAAGGPRAVLQLAHGMTEHSGRYDDFARFLAGRGFAVVGNDHRGHGHTGERADSMGYLADQDGFERLVDDLRAVHEWACRRWPGAPRFLMGHSMGSFLVRRYIQRYGDTVAGVIIMGTAGNPGLPGKIGRRLARLEMRRRGPRHPSMLLTSLVFGGYNKKIRSPKTAFDWLSRDAEAVKAYVADPWCGFVPSAGFYFDLLTGLLLIHDEREIARIPKDLPMLFLSGDADPVTGYGKGVERVIAQYERHGLRRMTSILYKDARHELLNELNKEEVYGDILKWLENTQAGILRNLSK	2008.0	Clear zone;Spectrophotometry	Poly(DL-lactic acid) with weight-average molecular weights of 0.5×104 (PLA0005) and 2.0×104 (PLA0020) and poly(caprolactone) (PCL) were purchased from Wako Pure Chemical Industries (Tokyo, Japan).	Wako Pure Chemical	Yes	No				Yes		
Uncultured bacterium	77133	PHA	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00048	00048 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PLA PHA	Yes	BAF57214.1	MHESVHAESLWLTMDDGAEVYVRVWEPAARAAADSSDDAPAPPAAAGGPRAVLQLAHGMTEHSGRYDDFARFLAGRGFAVVGNDHRGHGHTGERADSMGYLADQDGFERLVDDLRAVHEWACRRWPGAPRFLMGHSMGSFLVRRYIQRYGDTVAGVIIMGTAGNPGLPGKIGRRLARLEMRRRGPRHPSMLLTSLVFGGYNKKIRSPKTAFDWLSRDAEAVKAYVADPWCGFVPSAGFYFDLLTGLLLIHDEREIARIPKDLPMLFLSGDADPVTGYGKGVERVIAQYERHGLRRMTSILYKDARHELLNELNKEEVYGDILKWLENTQAGILRNLSK	2008.0	Clear zone;Spectrophotometry	Poly(DL-lactic acid) with weight-average molecular weights of 0.5×104 (PLA0005) and 2.0×104 (PLA0020) and poly(caprolactone) (PCL) were purchased from Wako Pure Chemical Industries (Tokyo, Japan).	Wako Pure Chemical	Yes	No				Yes		
Uncultured bacterium	77133	PBS	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00049	00049 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PHB PLA PHA	Yes	BAF57210.1	MLLKKRWLIFISFLLAFTLLIPTAASASEKHYKPNIALEPIENSEGNEHPIILVHGLGGFGRDELGGIIKMWGGIHDIEKKLREKGYKVYTAAVGPVSSNRDRAIELYYQIKGGTVDYGEAHAKKYGHDRYGRTYPGFYPEWGEINPKTGKPNKVHLIGHSMGGQTIRTLAQLLYEGDPEEHKTGGNDISPLLSGEKQPWLHSVLSISSPHDGSTATYLVNDVIPIIQELVIGAAIFAGNIDQNLYDFKLDHWGIKKRPGESFHSYVQRVRNSPGWKTKDTANWDLKPEGAYELNRWVKAQPDVYYFSVSNTQSRRSLLTGYYVPDLFMNPFLHPTAYYIGSKTFRKSNFVLDKTWWENDGLVSVKAMKGPNIGSNDVIVEYNGTPRKGVWNHLGTMRQFDHLDIIGWGVRDVTSWYEDVARFLYSLPDDY	2008.0	Spectrophotometry	PBS (BIONOLLE 1001™; PBS1001; weight-average molecular weight, 2.6×105 ) and PBSA (BIONOLLE emulsion EM-301™ were purchased from Showa Highpolymer (Tokyo, Japan).	Showa Denko		Yes				Yes		
Uncultured bacterium	77133	PBSA	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00049	00049 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PHB PLA PHA	Yes	BAF57210.1	MLLKKRWLIFISFLLAFTLLIPTAASASEKHYKPNIALEPIENSEGNEHPIILVHGLGGFGRDELGGIIKMWGGIHDIEKKLREKGYKVYTAAVGPVSSNRDRAIELYYQIKGGTVDYGEAHAKKYGHDRYGRTYPGFYPEWGEINPKTGKPNKVHLIGHSMGGQTIRTLAQLLYEGDPEEHKTGGNDISPLLSGEKQPWLHSVLSISSPHDGSTATYLVNDVIPIIQELVIGAAIFAGNIDQNLYDFKLDHWGIKKRPGESFHSYVQRVRNSPGWKTKDTANWDLKPEGAYELNRWVKAQPDVYYFSVSNTQSRRSLLTGYYVPDLFMNPFLHPTAYYIGSKTFRKSNFVLDKTWWENDGLVSVKAMKGPNIGSNDVIVEYNGTPRKGVWNHLGTMRQFDHLDIIGWGVRDVTSWYEDVARFLYSLPDDY	2008.0	Spectrophotometry	PBS (BIONOLLE 1001™; PBS1001; weight-average molecular weight, 2.6×105 ) and PBSA (BIONOLLE emulsion EM-301™ were purchased from Showa Highpolymer (Tokyo, Japan).	Showa Denko		Yes				Yes		
Uncultured bacterium	77133	PCL	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00049	00049 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PHB PLA PHA	Yes	BAF57210.1	MLLKKRWLIFISFLLAFTLLIPTAASASEKHYKPNIALEPIENSEGNEHPIILVHGLGGFGRDELGGIIKMWGGIHDIEKKLREKGYKVYTAAVGPVSSNRDRAIELYYQIKGGTVDYGEAHAKKYGHDRYGRTYPGFYPEWGEINPKTGKPNKVHLIGHSMGGQTIRTLAQLLYEGDPEEHKTGGNDISPLLSGEKQPWLHSVLSISSPHDGSTATYLVNDVIPIIQELVIGAAIFAGNIDQNLYDFKLDHWGIKKRPGESFHSYVQRVRNSPGWKTKDTANWDLKPEGAYELNRWVKAQPDVYYFSVSNTQSRRSLLTGYYVPDLFMNPFLHPTAYYIGSKTFRKSNFVLDKTWWENDGLVSVKAMKGPNIGSNDVIVEYNGTPRKGVWNHLGTMRQFDHLDIIGWGVRDVTSWYEDVARFLYSLPDDY	2008.0	Spectrophotometry	Poly(DL-lactic acid) with weight-average molecular weights of 0.5×104 (PLA0005) and 2.0×104 (PLA0020) and poly(caprolactone) (PCL) were purchased from Wako Pure Chemical Industries (Tokyo, Japan).	Wako Pure Chemical	Yes	Yes				Yes		
Uncultured bacterium	77133	PES	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00049	00049 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PHB PLA PHA	Yes	BAF57210.1	MLLKKRWLIFISFLLAFTLLIPTAASASEKHYKPNIALEPIENSEGNEHPIILVHGLGGFGRDELGGIIKMWGGIHDIEKKLREKGYKVYTAAVGPVSSNRDRAIELYYQIKGGTVDYGEAHAKKYGHDRYGRTYPGFYPEWGEINPKTGKPNKVHLIGHSMGGQTIRTLAQLLYEGDPEEHKTGGNDISPLLSGEKQPWLHSVLSISSPHDGSTATYLVNDVIPIIQELVIGAAIFAGNIDQNLYDFKLDHWGIKKRPGESFHSYVQRVRNSPGWKTKDTANWDLKPEGAYELNRWVKAQPDVYYFSVSNTQSRRSLLTGYYVPDLFMNPFLHPTAYYIGSKTFRKSNFVLDKTWWENDGLVSVKAMKGPNIGSNDVIVEYNGTPRKGVWNHLGTMRQFDHLDIIGWGVRDVTSWYEDVARFLYSLPDDY	2008.0	Spectrophotometry	Poly(ethylene succinate) (PES) was provided by Nippon Shokubai.	Nippon Shokubai		Yes				Yes		
Uncultured bacterium	77133	PHB	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00049	00049 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PHB PLA PHA	Yes	BAF57210.1	MLLKKRWLIFISFLLAFTLLIPTAASASEKHYKPNIALEPIENSEGNEHPIILVHGLGGFGRDELGGIIKMWGGIHDIEKKLREKGYKVYTAAVGPVSSNRDRAIELYYQIKGGTVDYGEAHAKKYGHDRYGRTYPGFYPEWGEINPKTGKPNKVHLIGHSMGGQTIRTLAQLLYEGDPEEHKTGGNDISPLLSGEKQPWLHSVLSISSPHDGSTATYLVNDVIPIIQELVIGAAIFAGNIDQNLYDFKLDHWGIKKRPGESFHSYVQRVRNSPGWKTKDTANWDLKPEGAYELNRWVKAQPDVYYFSVSNTQSRRSLLTGYYVPDLFMNPFLHPTAYYIGSKTFRKSNFVLDKTWWENDGLVSVKAMKGPNIGSNDVIVEYNGTPRKGVWNHLGTMRQFDHLDIIGWGVRDVTSWYEDVARFLYSLPDDY	2008.0	Spectrophotometry	 Poly (3-hydroxybutyric acid) (PHB) was purchased from Sigma-Aldrich Chemical (St. Louis, MO, USA).	Sigma Aldrich	Yes	Yes				Yes		
Uncultured bacterium	77133	PLA	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00049	00049 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PHB PLA PHA	Yes	BAF57210.1	MLLKKRWLIFISFLLAFTLLIPTAASASEKHYKPNIALEPIENSEGNEHPIILVHGLGGFGRDELGGIIKMWGGIHDIEKKLREKGYKVYTAAVGPVSSNRDRAIELYYQIKGGTVDYGEAHAKKYGHDRYGRTYPGFYPEWGEINPKTGKPNKVHLIGHSMGGQTIRTLAQLLYEGDPEEHKTGGNDISPLLSGEKQPWLHSVLSISSPHDGSTATYLVNDVIPIIQELVIGAAIFAGNIDQNLYDFKLDHWGIKKRPGESFHSYVQRVRNSPGWKTKDTANWDLKPEGAYELNRWVKAQPDVYYFSVSNTQSRRSLLTGYYVPDLFMNPFLHPTAYYIGSKTFRKSNFVLDKTWWENDGLVSVKAMKGPNIGSNDVIVEYNGTPRKGVWNHLGTMRQFDHLDIIGWGVRDVTSWYEDVARFLYSLPDDY	2008.0	Clear zone;Spectrophotometry	Poly(DL-lactic acid) with weight-average molecular weights of 0.5×104 (PLA0005) and 2.0×104 (PLA0020) and poly(caprolactone) (PCL) were purchased from Wako Pure Chemical Industries (Tokyo, Japan).	Wako Pure Chemical	Yes	Yes				Yes		
Uncultured bacterium	77133	PHA	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00049	00049 | PLA depolymerase | Uncultured bacterium | PBS PBSA PCL PES PHB PLA PHA	Yes	BAF57210.1	MLLKKRWLIFISFLLAFTLLIPTAASASEKHYKPNIALEPIENSEGNEHPIILVHGLGGFGRDELGGIIKMWGGIHDIEKKLREKGYKVYTAAVGPVSSNRDRAIELYYQIKGGTVDYGEAHAKKYGHDRYGRTYPGFYPEWGEINPKTGKPNKVHLIGHSMGGQTIRTLAQLLYEGDPEEHKTGGNDISPLLSGEKQPWLHSVLSISSPHDGSTATYLVNDVIPIIQELVIGAAIFAGNIDQNLYDFKLDHWGIKKRPGESFHSYVQRVRNSPGWKTKDTANWDLKPEGAYELNRWVKAQPDVYYFSVSNTQSRRSLLTGYYVPDLFMNPFLHPTAYYIGSKTFRKSNFVLDKTWWENDGLVSVKAMKGPNIGSNDVIVEYNGTPRKGVWNHLGTMRQFDHLDIIGWGVRDVTSWYEDVARFLYSLPDDY	2008.0	Clear zone;Spectrophotometry	Poly(DL-lactic acid) with weight-average molecular weights of 0.5×104 (PLA0005) and 2.0×104 (PLA0020) and poly(caprolactone) (PCL) were purchased from Wako Pure Chemical Industries (Tokyo, Japan).	Wako Pure Chemical	Yes	Yes				Yes		
Uncultured bacterium	77133	PLA	Mayumi, D., Akutsu-Shigeno, Y., Uchiyama, H., Nomura, N., & Nakajima-Kambe, T. (2008). Identification and characterization of novel poly (DL-lactic acid) depolymerases from metagenome. Applied microbiology and biotechnology, 79(5), 743-750.	PLA depolymerase	00050	00050 | PLA depolymerase | Uncultured bacterium | PLA	Yes	BAF57211.1	SFLLAFTPFVPTATASASEKNYQPNINLEPIQNSEGNEYPIILVHGLGGFGRDELGGIIKMWGGIHDIEKKLREKGYKVYTAAVGPVSSNRDRAIELYYQIKGGTVDYGEAHAKKTGHSRYGRTYPGFYPEWGEINPKTGKPNKVHLIGHSMGGQTIRTLAQLLYEGDPEEQKISGNDISPLLSGEKQPWLHSVLSISSPHDGSTATYLVNDVIPIIQELVIGAAIFAGNIDQNLYDFKLDHWGIKKQPGESFHSYVQRVRNSPGWKTKDTANWDLKPEGAYELNRWVKAQPDVYYFSVSNTQSRRSLLTGHYVPDLFMNPFLHPTSYYIGSKTFRKSNFVLDKTWWENDGLVSVKAMKGPNIGSNDVIVEYDGTPRKGVWNHLGTMRQFDHLDIIGWGVRDVTGWYEDVARFLYSLPE	2008.0	Clear zone;Spectrophotometry	Poly(DL-lactic acid) with weight-average molecular weights of 0.5×104 (PLA0005) and 2.0×104 (PLA0020) and poly(caprolactone) (PCL) were purchased from Wako Pure Chemical Industries (Tokyo, Japan).	Wako Pure Chemical	Yes	No				Yes		
Pseudomonas aeruginosa	287	PBSA	Lee, S. H., & Kim, M. N. (2010). Isolation of bacteria degrading poly (butylene succinate-co-butylene adipate) and their lip A gene. International Biodeterioration & Biodegradation, 64(3), 184-190.	Lipase	00052	00052 | Lipase | Pseudomonas aeruginosa | PBSA	Yes		MNLVGHSQGGLTSRYVAAVAPDLVASVTTIGTPHRGSEFADFVQSVLAYDPTGLSSSVIAAFANVFGILTSSSNNTNQDALAALKTLTTSQAATYNQNYPSAGLGAPGSCQTGAPTETVGGNTHLLYSWAGTAIQPTISAFGVTGATDTSTIPLIDPANALDLSTLALFGTGTVMINRASGQNDGLVSKCSALYGKVLSTSYKWNHLDEINQLLGVRGANAEDPVAVIRTHANRLKLAGV	2010.0	CO2;Clear zone	PBSA was supplied in pellet shape from IRE Chemical Co. The number average molecular weight and weight average molecular weight of PBSAwas 60,000 gmol^-1  and 130,000 gmol^-1 respectively.	IRE Chemical		No	Soil	Soil	South Korea	No		
Diaphorobacter sp.	1934310	PHB	Zhang, T., Chaudhry, M. T., & Liu, Z. P. (2010). Genetic and biochemical characterization of poly 3-hydroxybutyrate depolymerase from Diaphorobacter sp. PCA039. World Journal of Microbiology and Biotechnology, 26(10), 1803-1811.	PHB depolymerase	00053	00053 | PHB depolymerase | Diaphorobacter sp. | PHB PHBV PHA	Yes	ACI48814.2	MPFHRFLLAAALASAGMAQAAAPLGQYNIDTGKISVSGLSSGGFMANQLGNAYSSTFMGVGVFAAGPYMCAGHNNYTACMYNASISASQQSAMQGSIDSYSANGTIDGKSGIAAQKIYIFTGTSDYTVGPNLTDALQTQYLNNGVPAGNITYVKRSGTAHVLPTDFDSTSNNACSSSTSPFISNCGYDGAGAVLSHFYGALNARNNAPAAANYIEFDQSAYTAGNPGMAANAWLYVPASCASGAQCKLHVVLHGCQQSTDKIGDKFVKNTGYSRWADTNQIILLFPQTRIDNTSRSTAKSGSLANPNACWDWIGWYGGNFAHKSGAQMAAIKAMVDRIASGAGSGDGGGTTPPNDPVLPAPTGLSLSGATATSMNLAWNAVAGASGYNVYRNGNKANALTVYATSYTDSALTASTTYSWAVRAVDANGAEGDASNAVSGTTLAPTQSPGTCTTASNYAHTQAGRAYQQGGYTYANGSGQSMGLWNVFVTTTLKQTATNYYVIGTCP	2010.0	Spectrophotometry	PHB(V) was a kind gift from TianAn Biologic Material Co., Ltd (Ningbo, China).	TianAn Biologic Material	Yes	No	Sludge	Sewage/Sludge	China	No		
Diaphorobacter sp.	1934310	PHBV	Zhang, T., Chaudhry, M. T., & Liu, Z. P. (2010). Genetic and biochemical characterization of poly 3-hydroxybutyrate depolymerase from Diaphorobacter sp. PCA039. World Journal of Microbiology and Biotechnology, 26(10), 1803-1811.	PHB depolymerase	00053	00053 | PHB depolymerase | Diaphorobacter sp. | PHB PHBV PHA	Yes	ACI48814.2	MPFHRFLLAAALASAGMAQAAAPLGQYNIDTGKISVSGLSSGGFMANQLGNAYSSTFMGVGVFAAGPYMCAGHNNYTACMYNASISASQQSAMQGSIDSYSANGTIDGKSGIAAQKIYIFTGTSDYTVGPNLTDALQTQYLNNGVPAGNITYVKRSGTAHVLPTDFDSTSNNACSSSTSPFISNCGYDGAGAVLSHFYGALNARNNAPAAANYIEFDQSAYTAGNPGMAANAWLYVPASCASGAQCKLHVVLHGCQQSTDKIGDKFVKNTGYSRWADTNQIILLFPQTRIDNTSRSTAKSGSLANPNACWDWIGWYGGNFAHKSGAQMAAIKAMVDRIASGAGSGDGGGTTPPNDPVLPAPTGLSLSGATATSMNLAWNAVAGASGYNVYRNGNKANALTVYATSYTDSALTASTTYSWAVRAVDANGAEGDASNAVSGTTLAPTQSPGTCTTASNYAHTQAGRAYQQGGYTYANGSGQSMGLWNVFVTTTLKQTATNYYVIGTCP	2010.0	Spectrophotometry	PHB(V) was a kind gift from TianAn Biologic Material Co., Ltd (Ningbo, China).	TianAn Biologic Material	Yes	No	Sludge	Sewage/Sludge	China	No		
Diaphorobacter sp.	1934310	PHA	Zhang, T., Chaudhry, M. T., & Liu, Z. P. (2010). Genetic and biochemical characterization of poly 3-hydroxybutyrate depolymerase from Diaphorobacter sp. PCA039. World Journal of Microbiology and Biotechnology, 26(10), 1803-1811.	PHB depolymerase	00053	00053 | PHB depolymerase | Diaphorobacter sp. | PHB PHBV PHA	Yes	ACI48814.2	MPFHRFLLAAALASAGMAQAAAPLGQYNIDTGKISVSGLSSGGFMANQLGNAYSSTFMGVGVFAAGPYMCAGHNNYTACMYNASISASQQSAMQGSIDSYSANGTIDGKSGIAAQKIYIFTGTSDYTVGPNLTDALQTQYLNNGVPAGNITYVKRSGTAHVLPTDFDSTSNNACSSSTSPFISNCGYDGAGAVLSHFYGALNARNNAPAAANYIEFDQSAYTAGNPGMAANAWLYVPASCASGAQCKLHVVLHGCQQSTDKIGDKFVKNTGYSRWADTNQIILLFPQTRIDNTSRSTAKSGSLANPNACWDWIGWYGGNFAHKSGAQMAAIKAMVDRIASGAGSGDGGGTTPPNDPVLPAPTGLSLSGATATSMNLAWNAVAGASGYNVYRNGNKANALTVYATSYTDSALTASTTYSWAVRAVDANGAEGDASNAVSGTTLAPTQSPGTCTTASNYAHTQAGRAYQQGGYTYANGSGQSMGLWNVFVTTTLKQTATNYYVIGTCP	2010.0	Spectrophotometry	PHB(V) was a kind gift from TianAn Biologic Material Co., Ltd (Ningbo, China).	TianAn Biologic Material	Yes	No	Sludge	Sewage/Sludge	China	No		
Thermobifida alba	53522	PCL	Hu, X., Thumarat, U., Zhang, X., Tang, M., & Kawai, F. (2010). Diversity of polyester-degrading bacteria in compost and molecular analysis of a thermoactive esterase from Thermobifida alba AHK119. Applied microbiology and biotechnology, 87(2), 771-779.	Esterase	00054	00054 | Esterase | Thermobifida alba | PCL	Yes	BAI99230.2	MSVTTPRREASLLSRAVAVAAAAAATVALAAPAQAANPYERGPNPTESMLEARSGPFSVSEERASRLGADGFGGGTIYYPRENNTYGAIAISPGYTGTQSSIAWLGERIASHGFVVIAIDTNTTLDQPDSRARQLNAALDYMLTDASSSVRNRIDASRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKSWRDITVPTLIIGADLDTIAPVSSHSEPFYNSIPSSTDKAYLELNNATHFAPNITNKTIGMYSVAWLKRFVDEDTRYTQFLCPGPRTGLLSDVDEYRSTCPF	2010.0	Clear zone	Apexa® (formerly Biomax® 4026 and 4027) is a thermostable polyethylene terephthalate copolymer that is synthesized with terephthalic acid and ethylene glycol and an undisclosed component to be compostable; the product was kindly supplied by Dupont (Tokyo, Japan).	Apexa		Yes	Film	Compost		No		
Thermobifida alba	53522	PCL	Hu, X., Thumarat, U., Zhang, X., Tang, M., & Kawai, F. (2010). Diversity of polyester-degrading bacteria in compost and molecular analysis of a thermoactive esterase from Thermobifida alba AHK119. Applied microbiology and biotechnology, 87(2), 771-779.	Esterase	00055	00055 | Esterase | Thermobifida alba | PCL	Yes	BAK48590.1	MSVTTPRRETSLLSRALRATAAAATAVVATVALAAPAQAANPYERGPNPTESMLEARSGPFSVSEERASRFGADGFGGGTIYYPRENNTYGAIAISPGYTGTQSSIAWLGERIASHGFVVIAIDTNTTLDQPDSRARQLNAALDYMLTDASSAVRNRIDASRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKSWRDITVPTLIIGAEYDTIASVTLHSKPFYNSIPSPTDKAYLELDGASHFAPNITNKTIGMYSVAWLKRFVDEDTRYTQFLCPGPRTGLLSDVEEYRSTCPF	2010.0	Clear zone	Apexa® (formerly Biomax® 4026 and 4027) is a thermostable polyethylene terephthalate copolymer that is synthesized with terephthalic acid and ethylene glycol and an undisclosed component to be compostable; the product was kindly supplied by Dupont (Tokyo, Japan).	Apexa		Yes	Film	Compost		No		
Burkholderia cepacia	292	PBSA	Lee, S. H., & Kim, M. N. (2010). Isolation of bacteria degrading poly (butylene succinate-co-butylene adipate) and their lip A gene. International Biodeterioration & Biodegradation, 64(3), 184-190.	Lipase	00056	00056 | Lipase | Burkholderia cepacia | PBSA	Yes		MVRSMRSRVVAAAVACAMSGAQFAGTTAVMTLATTHAATAATAATAATAATDDYAATRYPVVLVHGLTGTDKYAGVLEYWYGIQEDLQRHGATVYVANLSGFQSDDGPNGRGEQLLAYVKTVLAATGATKVNLIGHSQGGLTSRYVAAVAPDLVASVTTIGTPHRGSEFADFVQSVLAYDPTGLSSSVIATFFNVFGILTSSSNNTNQDALAALKTLTTSQAAAYNQNYPSAGLGAPGSCQTGAPTETVGGNTHLLYSWAGTAIQPTVSMFGVTGAKDVSTIPVIDPANALDLSTLALLGTGTVMINRGAGQNDGLVSKCSALYGQVLGTRYKWNHLDEINQLLGVRGAYAEDPVAVIRTHANRLKLAGV	2010.0	CO2;Clear zone	PBSA was supplied in pellet shape from IRE Chemical Co. The number average molecular weight and weight average molecular weight of PBSAwas 60,000 gmol^-1  and 130,000 gmol^-1 respectively.	IRE Chemical		No	Soil	Sewage/Sludge	South Korea	No		
Thermobifida fusca	2021	PET	Herrero Acero, E., Ribitsch, D., Steinkellner, G., Gruber, K., Greimel, K., Eiteljoerg, I., ... & Cavaco-Paulo, A. (2011). Enzymatic surface hydrolysis of PET: effect of structural diversity on kinetic properties of cutinases from Thermobifida. Macromolecules, 44(12), 4632-4640.	Cutinase	00057	00057 | Cutinase | Thermobifida fusca | PET	Yes	ADV92528.1	MANPYERGPNPTDALLEARSGPFSVSEENVSRLSASGFGGGTIYYPRENNTYGAVAISPGYTGTEASIAWLGERIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGSLRLASQRPDLKAAIPLTPWHLNKNWSSVRVPTLIIGADLDTIAPVLTHARPFYNSLPTSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2011.0	Spectrophotometry;HPLC;FTIR	All other chemicals were of analytical grade from SIGMA (Germany) except the model substrate bis(benzoyloxyethyl) terephthalate (3PET) which was synthetized in two steps as previously described.3	Sigma Aldrich	Yes	No				Yes		
Thermobifida cellulosilytica	144786	PET	Herrero Acero, E., Ribitsch, D., Steinkellner, G., Gruber, K., Greimel, K., Eiteljoerg, I., ... & Cavaco-Paulo, A. (2011). Enzymatic surface hydrolysis of PET: effect of structural diversity on kinetic properties of cutinases from Thermobifida. Macromolecules, 44(12), 4632-4640.	Cutinase	00058	00058 | Cutinase | Thermobifida cellulosilytica | PET	Yes	ADV92527.1	MANPYERGPNPTDALLEARSGPFSVSEERASRFGADGFGGGTIYYPRENNTYGAVASPGYTGTQASVAWLGERIASHGFVVITIDTNTTLDQPDSRARQLNAALDYMINDASSAVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVRVPTLIIGADLDTIAPVLTHARPFYNSLPTSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2011.0	Spectrophotometry;HPLC;FTIR	All other chemicals were of analytical grade from SIGMA (Germany) except the model substrate bis(benzoyloxyethyl) terephthalate (3PET) which was synthetized in two steps as previously described.3	Sigma Aldrich	Yes	No				Yes		
Thermobifida cellulosilytica	144786	PET	Herrero Acero, E., Ribitsch, D., Steinkellner, G., Gruber, K., Greimel, K., Eiteljoerg, I., ... & Cavaco-Paulo, A. (2011). Enzymatic surface hydrolysis of PET: effect of structural diversity on kinetic properties of cutinases from Thermobifida. Macromolecules, 44(12), 4632-4640.	Cutinase	00059	00059 | Cutinase | Thermobifida cellulosilytica | PET	Yes	ADV92526.1	MANPYERGPNPTDALLEASSGPFSVSEENVSRLSASGFGGGTIYYPRENNTYGAVAISPGYTGTEASIAWLGERIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVTVPTLIIGADLDTIAPVATHAKPFYNSLPSSISKAYLELDGATHFAPNPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2011.0	Spectrophotometry;HPLC;FTIR	All other chemicals were of analytical grade from SIGMA (Germany) except the model substrate bis(benzoyloxyethyl) terephthalate (3PET) which was synthetized in two steps as previously described.3	Sigma Aldrich	Yes	No				Yes		
Rhodospirillum rubrum	1085	PHB	Sznajder, A., & Jendrossek, D. (2011). Biochemical characterization of a new type of intracellular PHB depolymerase from Rhodospirillum rubrum with high hydrolytic activity on native PHB granules. Applied microbiology and biotechnology, 89(5), 1487-1495.	PHB depolymerase	00060	00060 | PHB depolymerase | Rhodospirillum rubrum | PHB PHA	Yes	ABC22769.1	MKNPFAHGSLPPIPLPDLTEATRLTRSGRLGEATALIGRLLGRGQPEATPPFEPSPLTPPTIDGEAIEITPRPGGAPRPQAPPAGRGAFLALTHRGPAGTRDYKLFVPPGSGDSSLPLILMLHGCTQDPDDFAAGTGMNKLAEEAGCLVAYPRQPASANPSKCWNWFNDENQHRGQGEAALLAELTRAIIGERRVDPARVYVAGLSAGGAAAAILAVTYPDLFAAVGVHSGLACGAARDMASAFAAMRQGGATVRPAPSAIPAIVFHGDRDTTVHPGNGDSLVSQFTADRSGLRETSQTGRAPGGHGYRRTLHSAADGTVLCEQWTIQGGGHAWSGGQPAGSFTDPRGPDASAEMLRFFLAQCHPGLGAKAPC	2011.0	Clear zone	nPHB granules were prepared from crude extracts (French press) of PHB-rich cells of R. eutropha H16 by two sodium phosphate-buffered glycerol density gradient centrifugation steps as described previously (Handrick et al. 2000).		Yes	No	Culture collection	Culture collection		No		
Rhodospirillum rubrum	1085	PHA	Sznajder, A., & Jendrossek, D. (2011). Biochemical characterization of a new type of intracellular PHB depolymerase from Rhodospirillum rubrum with high hydrolytic activity on native PHB granules. Applied microbiology and biotechnology, 89(5), 1487-1495.	PHB depolymerase	00060	00060 | PHB depolymerase | Rhodospirillum rubrum | PHB PHA	Yes	ABC22769.1	MKNPFAHGSLPPIPLPDLTEATRLTRSGRLGEATALIGRLLGRGQPEATPPFEPSPLTPPTIDGEAIEITPRPGGAPRPQAPPAGRGAFLALTHRGPAGTRDYKLFVPPGSGDSSLPLILMLHGCTQDPDDFAAGTGMNKLAEEAGCLVAYPRQPASANPSKCWNWFNDENQHRGQGEAALLAELTRAIIGERRVDPARVYVAGLSAGGAAAAILAVTYPDLFAAVGVHSGLACGAARDMASAFAAMRQGGATVRPAPSAIPAIVFHGDRDTTVHPGNGDSLVSQFTADRSGLRETSQTGRAPGGHGYRRTLHSAADGTVLCEQWTIQGGGHAWSGGQPAGSFTDPRGPDASAEMLRFFLAQCHPGLGAKAPC	2011.0	Clear zone	nPHB granules were prepared from crude extracts (French press) of PHB-rich cells of R. eutropha H16 by two sodium phosphate-buffered glycerol density gradient centrifugation steps as described previously (Handrick et al. 2000).		Yes	No	Culture collection	Culture collection		No		
Pseudomonas sp.	306	PE	Yoon, M., Jeon, H., & Kim, M. (2012). Biodegradation of polyethylene by a soil bacterium and AlkB cloned recombinant cell. J Bioremed Biodegrad, 3(4), 1-8.	Alkane hydroxylase	00061	00061 | Alkane hydroxylase | Pseudomonas sp. | PE	Yes		EHIRGHHVHVSTPEDASSSRFGQSLYAFLPHAYKHNFLNAWRLEAERLHRRGLPALHWRNELIWWYAISALLLLGFSLAFGWLGALFFLGQALMAFTLLEIVNYVEHY	2012.0	Clear zone;SEM	Instead of pre-oxidized polyethylene which has been used for the isolation of polyethylene-degrading strains in the previous studies, we used LMWPE which had been prepared by thermal degradation of a commercially available neat polyethylene under a strict nitrogen atmosphere. The weight average molecular weight (Mw) of LMWPE was in the range between 1,700 and 23,700 as shown in Table 1, which was far superior to 500, the maximum value reported to be penetrable through microbial membrane. Biodegradability of LMWPE with different Mw was assessed in the compost inoculated with the isolated strain after sterilization.			No	Soil	Soil	South Korea	No		
Bdellovibrio bacteriovorus	959	PHA	Martínez, V., de la Peña, F., García-Hidalgo, J., de la Mata, I., García, J. L., & Prieto, M. A. (2012). Identification and biochemical evidence of a medium-chain-length polyhydroxyalkanoate depolymerase in the Bdellovibrio bacteriovorus predatory hydrolytic arsenal. Appl. Environ. Microbiol., 78(17), 6017-6026.	MCL PHA depolymerase	00064	00064 | MCL PHA depolymerase | Bdellovibrio bacteriovorus | PHA	Yes		MKKLLAGVFGVVAMSLSAQAAKKASNCEVTGLVDRMTCPYLEKLVSGPHLTRHVKYSLPKGKTPKAGWPTVILYQGSLFPVEFSRSSLMIAGGYNEIRLIQTLLDSGFAVIAPPAIEGVAWMTNIVGIDYDTSEDFYFVEELLVAMGNGEFGKLNMDRLYATGISSGGYHSSRMAVAFPGVFKALAVHSASYADCGGPMCFVPAQVPENHPPTIFLHGRLDPVVPVRTMYPYHETLKNQGVETEMFVSPWARHEWLEEAPELITNWFINHK	2012.0	Clear zone;Spectrophotometry	All other products were of analytical quality or high-performance liquid chromatography (HPLC) grade.		Yes	No				Yes		
Pseudomonas mendocina	300	PHB	Wang, Y., Li, F., Wang, Z.-Y., Liu, D.-B. (2012). Purification and properties of an extracellular polyhydroxybutyrate depolymerase from Pseudomonas mendocina DSWY0601. Chem. Res. Chin. Univ. 28, 459–464.	PHB depolymerase	00066	00066 | PHB depolymerase | Pseudomonas mendocina | PHB PHA	Yes	AEZ06355.1	MTKQSLPQGMADQRLCRFFTAALCSLLMILLWPTTVTAGQTFSYTSPQQAYSGSRERSYKVYVPTGLSTPAPMVMALHGCRQTNDDVLNDWGLKAAADRYGFILVAPFITSYDGLRNENCWGFWFEQHIHQGGGEVADLHRIAQQVEANFVIDANRRFITGLSSGGAMSLVAAVAYNEYWAAAAPAAGLPYRETASSVSLSGQCPGSATFRSVSQVAADMRSEVNDAYPIPLMVLQNRNDCTVLQTAANNMRDAHLQVFGSASRNTPATTQASDTGCSPYHQNDYGCRHIAYTQDGTTATRSLVETVIYDGPLATPNPQDTNHGHYWIGGAQGNNGKWSLQVGPSYPDIIWDFFSRHSRDGSQPQGHPVIVLQGDNPLSVPLGSTFNDPGASASDAEDGSLPVSAECSAVNPSVVGSCSCLYSATDSDGNRSTLTRTVEVYDPNAPVETCQVVSASPSVHIGAGRAYAGGTSNLRAYAKDDGVDIGGSFDTWSNVPLYEGEPGRWYAQRPAACGGSGQAFTCQEWNASNLSHVMAGRAYYGYYTVGGNQYLGSLSGLSTWVRETAQGHFQAGRCSN	2012.0	Clear zone;SEM;Spectrophotometry;MS	PHB was provided by the Institute of Microbiology of the Chinese Academy of Science(Beijing, China). Unless otherwise stated, all the chemicals used were of analytical grade. 		Yes	No	Sludge	Sewage/Sludge	China	No		
Pseudomonas mendocina	300	PHA	Wang, Y., Li, F., Wang, Z.-Y., Liu, D.-B. (2012). Purification and properties of an extracellular polyhydroxybutyrate depolymerase from Pseudomonas mendocina DSWY0601. Chem. Res. Chin. Univ. 28, 459–464.	PHB depolymerase	00066	00066 | PHB depolymerase | Pseudomonas mendocina | PHB PHA	Yes	AEZ06355.1	MTKQSLPQGMADQRLCRFFTAALCSLLMILLWPTTVTAGQTFSYTSPQQAYSGSRERSYKVYVPTGLSTPAPMVMALHGCRQTNDDVLNDWGLKAAADRYGFILVAPFITSYDGLRNENCWGFWFEQHIHQGGGEVADLHRIAQQVEANFVIDANRRFITGLSSGGAMSLVAAVAYNEYWAAAAPAAGLPYRETASSVSLSGQCPGSATFRSVSQVAADMRSEVNDAYPIPLMVLQNRNDCTVLQTAANNMRDAHLQVFGSASRNTPATTQASDTGCSPYHQNDYGCRHIAYTQDGTTATRSLVETVIYDGPLATPNPQDTNHGHYWIGGAQGNNGKWSLQVGPSYPDIIWDFFSRHSRDGSQPQGHPVIVLQGDNPLSVPLGSTFNDPGASASDAEDGSLPVSAECSAVNPSVVGSCSCLYSATDSDGNRSTLTRTVEVYDPNAPVETCQVVSASPSVHIGAGRAYAGGTSNLRAYAKDDGVDIGGSFDTWSNVPLYEGEPGRWYAQRPAACGGSGQAFTCQEWNASNLSHVMAGRAYYGYYTVGGNQYLGSLSGLSTWVRETAQGHFQAGRCSN	2012.0	Clear zone;SEM;Spectrophotometry;MS	PHB was provided by the Institute of Microbiology of the Chinese Academy of Science(Beijing, China). Unless otherwise stated, all the chemicals used were of analytical grade. 		Yes	No	Sludge	Sewage/Sludge	China	No		
Streptomyces ascomycinicus	476551	PHB	García-Hidalgo, J., Hormigo, D., Arroyo, M., & de la Mata, I. (2013). Novel extracellular PHB depolymerase from Streptomyces ascomycinicus: PHB copolymers degradation in acidic conditions. PLoS One, 8(8), e71699.	PHB depolymerase	00067	00067 | PHB depolymerase | Streptomyces ascomycinicus | PHB PHA	Yes		MQPPPFRGILTPLFPLSSSPPVGSLSRPGRRGVLTRLVAVVALVLGAALLGPAPTAHAAAGLAKPGLTKADLTEVADFGTNPGRLNMYVYRPASLPAEPAVVFALHGCTQDAQGYADNSGLLSFADRYGFLLVFAETTSSNNANRCFNWFQSSDNRRGQGEAASIRQMAAHTVSAYGADPQRTYITGLSAGGAMTSVMLATYPDVFQAGAVVAGLPFGCATDVSSAYLCMNPGTDLTADQWARRVRDGYPSWSGPWPRVAIWHGDKDTTVAPRNADELRDQWTAVHGVSQTPDRTSVIGPNSTRHEEYLAADGSVAVEVNRVPGIGHGTPVDPGTGAQQCGSTGAAYFLDSICSSYWITQFFGLSGSASDPGSLPAPSGLAATGATDTTISLTWKPVDGATDYAVHRDGAQITTSATTSYTDTGLRAGTSHTYAVAARDADGKAGPLSGAVTAQTTGATAVCWTAGNYAHVQAGRATTSAGYTYAKGSGQNMGLYNTFVTTTLKESPTGYFTVANDTCP	2013.0	Spectrophotometry	All chemical reagents and polymers were purchased from Sigma-Aldrich.	Sigma Aldrich	Yes	No				Yes		
Streptomyces ascomycinicus	476551	PHA	García-Hidalgo, J., Hormigo, D., Arroyo, M., & de la Mata, I. (2013). Novel extracellular PHB depolymerase from Streptomyces ascomycinicus: PHB copolymers degradation in acidic conditions. PLoS One, 8(8), e71699.	PHB depolymerase	00067	00067 | PHB depolymerase | Streptomyces ascomycinicus | PHB PHA	Yes		MQPPPFRGILTPLFPLSSSPPVGSLSRPGRRGVLTRLVAVVALVLGAALLGPAPTAHAAAGLAKPGLTKADLTEVADFGTNPGRLNMYVYRPASLPAEPAVVFALHGCTQDAQGYADNSGLLSFADRYGFLLVFAETTSSNNANRCFNWFQSSDNRRGQGEAASIRQMAAHTVSAYGADPQRTYITGLSAGGAMTSVMLATYPDVFQAGAVVAGLPFGCATDVSSAYLCMNPGTDLTADQWARRVRDGYPSWSGPWPRVAIWHGDKDTTVAPRNADELRDQWTAVHGVSQTPDRTSVIGPNSTRHEEYLAADGSVAVEVNRVPGIGHGTPVDPGTGAQQCGSTGAAYFLDSICSSYWITQFFGLSGSASDPGSLPAPSGLAATGATDTTISLTWKPVDGATDYAVHRDGAQITTSATTSYTDTGLRAGTSHTYAVAARDADGKAGPLSGAVTAQTTGATAVCWTAGNYAHVQAGRATTSAGYTYAKGSGQNMGLYNTFVTTTLKESPTGYFTVANDTCP	2013.0	Spectrophotometry	All chemical reagents and polymers were purchased from Sigma-Aldrich.	Sigma Aldrich	Yes	No				Yes		
Pseudozyma antarctica	84753	PBS-Blend	Shinozaki, Y., Morita, T., Cao, X. H., Yoshida, S., Koitabashi, M., Watanabe, T., ... & Kitamoto, H. K. (2013). Biodegradable plastic-degrading enzyme from Pseudozyma antarctica: cloning, sequencing, and characterization. Applied microbiology and biotechnology, 97(7), 2951-2959.	Cutinase	00068	00068 | Cutinase | Pseudozyma antarctica | PBS-Blend PBSA-Blend	Yes		MSIDKYSPKTRGLINSRRHKMKQSTNNSASPSGLVVQHLDEKAHLRHQNRMDEATICLSLKSLDTEVGAHGLNVGVVSVGKVLGGDSESGADVANSVAVDADVERLGDPVGGDALGESSRDTSSAEGGLATVTIDVASEVGLVFGVADKNDTLDGVERRTSKLRKGIAGGSGTLGVALEEEARVGVAGQTGLDLGHDVGSTLGRVLVDTGWVDGVVFGATRNGGANAGVHGAEADRGTLRLAGTASVDDDVRRTASTLLERSSLHETSGGKDEGGKGRLELHLEIDRKGG	2013.0	SEM;NMR;TOC	PBS film Bionolle 1001G, MW 2.0-2.5x10^5, thickness 20um	Bayer 	No	No	Culture collection	Culture collection		No		
Pseudozyma antarctica	84753	PBSA-Blend	Shinozaki, Y., Morita, T., Cao, X. H., Yoshida, S., Koitabashi, M., Watanabe, T., ... & Kitamoto, H. K. (2013). Biodegradable plastic-degrading enzyme from Pseudozyma antarctica: cloning, sequencing, and characterization. Applied microbiology and biotechnology, 97(7), 2951-2959.	Cutinase	00068	00068 | Cutinase | Pseudozyma antarctica | PBS-Blend PBSA-Blend	Yes		MSIDKYSPKTRGLINSRRHKMKQSTNNSASPSGLVVQHLDEKAHLRHQNRMDEATICLSLKSLDTEVGAHGLNVGVVSVGKVLGGDSESGADVANSVAVDADVERLGDPVGGDALGESSRDTSSAEGGLATVTIDVASEVGLVFGVADKNDTLDGVERRTSKLRKGIAGGSGTLGVALEEEARVGVAGQTGLDLGHDVGSTLGRVLVDTGWVDGVVFGATRNGGANAGVHGAEADRGTLRLAGTASVDDDVRRTASTLLERSSLHETSGGKDEGGKGRLELHLEIDRKGG	2013.0	SEM;NMR;TOC	PBSA (Bionolle EM-301, MW 1.2-1.5x10^5;Bionolle #3020, MW 1.4x10^5;PBSA film Bionolle 3001G, MW 2.0-2.5x10^5, thickness 20um)	Bayer 	No	No	Culture collection	Culture collection		No		
Streptomyces thermoviolaceus	1952	PCL	Chua, T. K., Tseng, M., & Yang, M. K. (2013). Degradation of Poly (ε-caprolactone) by thermophilic Streptomyces thermoviolaceus subsp. thermoviolaceus 76T-2. AMB Express, 3(1), 8.	Chitinase	00069	00069 | Chitinase | Streptomyces thermoviolaceus | PCL	Yes		MTASTTRQRISARRLGLRRATLGVATAGLVAAMFTAASAQAATGPVAGSTHVSASAAGSDTIQANFVVSEAQFNQMFPNRNPFYTYQGLVDALSAFPGFANTGDDTTKKQEAAAFLANVNHETGGLQYVVEQNTANYPAYCDWSQPYGCPAGQDAYYGRGPIQLSWNFNYKAAGDAIGVDLLNNPWLVENDPAIAWKTGLWYWNTQSGPGTMTPHDAMVNHAGFGQTIRSINGSLECDGRNPAQVQSRVDAYQRFTSILGVAPGDNLYC	2013.0	Clear zone	PLC powder			No	Soil	Soil	Taiwan	No		
Paracoccus denitrificans	266	PHB	Lu, J., Takahashi, A., & Ueda, S. (2014). 3-Hydroxybutyrate oligomer hydrolase and 3-hydroxybutyrate dehydrogenase participate in intracellular polyhydroxybutyrate and polyhydroxyvalerate degradation in Paracoccus denitrificans. Appl. Environ. Microbiol., 80(3), 986-993.	3HB oligomer hydrolase	00070	00070 | 3HB oligomer hydrolase | Paracoccus denitrificans | PHB PHA	Yes		MAVQFFQAEDGARLAYRDEGEGLPVLALPGLTRTGRDFDYLAPHLPGVRLIRPDYRGRGDSDWTGSDSYTVPQEARDVLVLLDHLGVAQAAVLGTSRGGIIGMLLAATARERLLGLCLNDVGPVLQRSGLERIFDYVGRNPAAKNLEDLAQRLPAAMPGFANVPASRWLEEAARHYVETPSGLSVNYDPALREAFLAAFDGPEVDLWPLFDATQGLPLALIRGANSDLLSHETATEMQRRRPDMILAEARDRAHVPFLDEPESLAAIHAWLAAMR	2014.0	HPLC	3HB oligomer	Sigma Aldrich	Yes	No				Yes		
Paracoccus denitrificans	266	PHA	Lu, J., Takahashi, A., & Ueda, S. (2014). 3-Hydroxybutyrate oligomer hydrolase and 3-hydroxybutyrate dehydrogenase participate in intracellular polyhydroxybutyrate and polyhydroxyvalerate degradation in Paracoccus denitrificans. Appl. Environ. Microbiol., 80(3), 986-993.	3HB oligomer hydrolase	00070	00070 | 3HB oligomer hydrolase | Paracoccus denitrificans | PHB PHA	Yes		MAVQFFQAEDGARLAYRDEGEGLPVLALPGLTRTGRDFDYLAPHLPGVRLIRPDYRGRGDSDWTGSDSYTVPQEARDVLVLLDHLGVAQAAVLGTSRGGIIGMLLAATARERLLGLCLNDVGPVLQRSGLERIFDYVGRNPAAKNLEDLAQRLPAAMPGFANVPASRWLEEAARHYVETPSGLSVNYDPALREAFLAAFDGPEVDLWPLFDATQGLPLALIRGANSDLLSHETATEMQRRRPDMILAEARDRAHVPFLDEPESLAAIHAWLAAMR	2014.0	HPLC	3HB oligomer	Sigma Aldrich	Yes	No				Yes		
Paracoccus denitrificans	266	P3HV	Lu, J., Takahashi, A., & Ueda, S. (2014). 3-Hydroxybutyrate oligomer hydrolase and 3-hydroxybutyrate dehydrogenase participate in intracellular polyhydroxybutyrate and polyhydroxyvalerate degradation in Paracoccus denitrificans. Appl. Environ. Microbiol., 80(3), 986-993.	3HV dehydrogenase	00071	00071 | 3HV dehydrogenase | Paracoccus denitrificans | P3HV PHBV PHA	Yes		MFEKFLSGKTAVVTGSNSGIGLGIAHELARAGADLVLNSFTDMPEDHALAESLAAEHGVEVRYVQADMSKGADCRALIEKAGACDILVNNAGIQHVAPIPDFPGEKWDAIIAINLSSAFHTTAAALPLMRKAGWGRVINIASAHGLTASEYKSAYVAAKHGIVGLTKVTALETAKEPITCNAICPGYVLTPIVEKQIPDQMKTHNMSREDVIAKVMLQRQPSGQFATVEQMGGTAVFLCSPAAEQITGTTISVDGGWTAL	2014.0	HPLC	3HV oligomer	Sigma Aldrich	Yes	No	Culture collection	Culture collection		Yes		
Paracoccus denitrificans	266	PHBV	Lu, J., Takahashi, A., & Ueda, S. (2014). 3-Hydroxybutyrate oligomer hydrolase and 3-hydroxybutyrate dehydrogenase participate in intracellular polyhydroxybutyrate and polyhydroxyvalerate degradation in Paracoccus denitrificans. Appl. Environ. Microbiol., 80(3), 986-993.	3HV dehydrogenase	00071	00071 | 3HV dehydrogenase | Paracoccus denitrificans | P3HV PHBV PHA	Yes		MFEKFLSGKTAVVTGSNSGIGLGIAHELARAGADLVLNSFTDMPEDHALAESLAAEHGVEVRYVQADMSKGADCRALIEKAGACDILVNNAGIQHVAPIPDFPGEKWDAIIAINLSSAFHTTAAALPLMRKAGWGRVINIASAHGLTASEYKSAYVAAKHGIVGLTKVTALETAKEPITCNAICPGYVLTPIVEKQIPDQMKTHNMSREDVIAKVMLQRQPSGQFATVEQMGGTAVFLCSPAAEQITGTTISVDGGWTAL	2014.0	HPLC	3HV oligomer	Sigma Aldrich	Yes	No				Yes		
Paracoccus denitrificans	266	PHA	Lu, J., Takahashi, A., & Ueda, S. (2014). 3-Hydroxybutyrate oligomer hydrolase and 3-hydroxybutyrate dehydrogenase participate in intracellular polyhydroxybutyrate and polyhydroxyvalerate degradation in Paracoccus denitrificans. Appl. Environ. Microbiol., 80(3), 986-993.	3HV dehydrogenase	00071	00071 | 3HV dehydrogenase | Paracoccus denitrificans | P3HV PHBV PHA	Yes		MFEKFLSGKTAVVTGSNSGIGLGIAHELARAGADLVLNSFTDMPEDHALAESLAAEHGVEVRYVQADMSKGADCRALIEKAGACDILVNNAGIQHVAPIPDFPGEKWDAIIAINLSSAFHTTAAALPLMRKAGWGRVINIASAHGLTASEYKSAYVAAKHGIVGLTKVTALETAKEPITCNAICPGYVLTPIVEKQIPDQMKTHNMSREDVIAKVMLQRQPSGQFATVEQMGGTAVFLCSPAAEQITGTTISVDGGWTAL	2014.0	HPLC	3HV oligomer	Sigma Aldrich	Yes	No				Yes		
Bacillus thuringiensis	1428	PHB	Wang, Y. L., Lin, Y. T., Chen, C. L., Shaw, G. C., & Liaw, S. H. (2014). Crystallization and preliminary crystallographic analysis of poly (3-hydroxybutyrate) depolymerase from Bacillus thuringiensis. Acta Crystallographica Section F: Structural Biology Communications, 70(10), 1421-1423.	PHB depolymerase	00072	00072 | PHB depolymerase | Bacillus thuringiensis | PHB PHA	Yes	EAO52570.1	MGELVMIKPATMEFVSLSNGETIAYQEVGRRNTDILVLIHGNMTSSQHWDLVIEKLQDQYHIYALDLRGFGQSTYNQSIDSLQDFAEDVKLFIDELKLEKFSLMGWSMGGGVAMQFTANHPTFVEKLILVESVGMKGYPIFKKDTNGQPIVSSLVKTKEEIAQDPVQIAPVLDAIKNMNKLYYRTVWNLLIYTHNQPEPDRYEKYLDDMLTQRNFVDVNYALITFNISDEHNGVVGGSKQIHRIKAPTLVIQGDRDYVVPQVVGEELAKHLPNAELKVLEDCGHSPFIDCLDVFIKHVEDWLEQK	2014.0					No				Yes		
Bacillus thuringiensis	1428	PHA	Wang, Y. L., Lin, Y. T., Chen, C. L., Shaw, G. C., & Liaw, S. H. (2014). Crystallization and preliminary crystallographic analysis of poly (3-hydroxybutyrate) depolymerase from Bacillus thuringiensis. Acta Crystallographica Section F: Structural Biology Communications, 70(10), 1421-1423.	PHB depolymerase	00072	00072 | PHB depolymerase | Bacillus thuringiensis | PHB PHA	Yes	EAO52570.1	MGELVMIKPATMEFVSLSNGETIAYQEVGRRNTDILVLIHGNMTSSQHWDLVIEKLQDQYHIYALDLRGFGQSTYNQSIDSLQDFAEDVKLFIDELKLEKFSLMGWSMGGGVAMQFTANHPTFVEKLILVESVGMKGYPIFKKDTNGQPIVSSLVKTKEEIAQDPVQIAPVLDAIKNMNKLYYRTVWNLLIYTHNQPEPDRYEKYLDDMLTQRNFVDVNYALITFNISDEHNGVVGGSKQIHRIKAPTLVIQGDRDYVVPQVVGEELAKHLPNAELKVLEDCGHSPFIDCLDVFIKHVEDWLEQK	2014.0					No				Yes		
Thermobifida fusca	2021	PET	Roth, C., Wei, R., Oeser, T., Then, J., Föllner, C., Zimmermann, W., & Sträter, N. (2014). Structural and functional studies on a thermostable polyethylene terephthalate degrading hydrolase from Thermobifida fusca. Applied microbiology and biotechnology, 98(18), 7815-7823.	Cutinase	00073	00073 | Cutinase | Thermobifida fusca | PET	Yes		MRGVWRYMPVYYYKCMLIPLLTFTKISIISKPQESRISLIICRTMPTVATFLGLAISGAAMASGAALGAYNVDPNSISVSGLSSGGFMSAQLGVAYSDTFKVGFGVFAGGPYDCARGQSYTTCMYNQNPSITTPVANMKSWSGNKINPVSNLQSRKIYMWTGTADTTVGPNVMSQLKTQLANFASAANVSYITTSGAAHTFPTDFDAAGDNSCSSSVSPYISNCQCDGAGAVLQWMYGPLNARNPGTLSGSIVSFSQTGEYGASGMDTTGYLYVPRACQPGSSTVCKLHVALHGCKQSYSMIGSKFVSNTGYNMWADTNDIIILYPQAVADNTMHTIWTGMPLPNPNGCWDWVGWYGANADQVGGVQMAAIVNQVARVVSGYGAGSSSSTTAATPTTTTGSITTTTTTTATVTTTAVAPLYGQCGGIGWTGPTACATGVCTAYSPYYAQCLLIV	2014.0									Yes		
Saccharomonospora viridis	1852	PBAT	Kawai, F., Oda, M., Tamashiro, T., Waku, T., Tanaka, N., Yamamoto, M., ... & Tanokura, M. (2014). A novel Ca 2+-activated, thermostabilized polyesterase capable of hydrolyzing polyethylene terephthalate from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 98(24), 10053-10064.	Cutinase	00074	00074 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes	BAO42836.1	MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2014.0	Clear zone	Ecoflex® is an aliphatic-co-aromatic polyester consisting of terephthalic acid, 1,4-butane diol, adipate, and an unknown compound (Kleeberg et al. 2005).			No	Compost	Compost	Japan	Yes		
Saccharomonospora viridis	1852	PBS	Kawai, F., Oda, M., Tamashiro, T., Waku, T., Tanaka, N., Yamamoto, M., ... & Tanokura, M. (2014). A novel Ca 2+-activated, thermostabilized polyesterase capable of hydrolyzing polyethylene terephthalate from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 98(24), 10053-10064.	Cutinase	00074	00074 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes	BAO42836.1	MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2014.0	Clear zone	The poly(butylene succinate-co-adipate) (PBSA) (Bionolle™ #3001; weight-average MW=1.0×105 ), poly(butylene succinate) (PBS) (Bionolle™ #1020; weight-average MW=1.3× 105 ), and PBSA suspension (Bionolle™ EM-301; weightaverage MW=1.0×105 ) are products of Showa Denko K. K. (Tokyo, Japan)	Showa Denko		No	Compost	Compost	Japan	Yes		
Saccharomonospora viridis	1852	PBSA	Kawai, F., Oda, M., Tamashiro, T., Waku, T., Tanaka, N., Yamamoto, M., ... & Tanokura, M. (2014). A novel Ca 2+-activated, thermostabilized polyesterase capable of hydrolyzing polyethylene terephthalate from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 98(24), 10053-10064.	Cutinase	00074	00074 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes	BAO42836.1	MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2014.0	Clear zone	The poly(butylene succinate-co-adipate) (PBSA) (Bionolle™ #3001; weight-average MW=1.0×105 ), poly(butylene succinate) (PBS) (Bionolle™ #1020; weight-average MW=1.3× 105 ), and PBSA suspension (Bionolle™ EM-301; weightaverage MW=1.0×105 ) are products of Showa Denko K. K. (Tokyo, Japan)	Showa Denko		No	Compost	Compost	Japan	Yes		
Saccharomonospora viridis	1852	PCL	Kawai, F., Oda, M., Tamashiro, T., Waku, T., Tanaka, N., Yamamoto, M., ... & Tanokura, M. (2014). A novel Ca 2+-activated, thermostabilized polyesterase capable of hydrolyzing polyethylene terephthalate from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 98(24), 10053-10064.	Cutinase	00074	00074 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes	BAO42836.1	MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2014.0	Clear zone	poly(caprolactone) (PCL; average molecular weight (MW)=40,000) was purchased from Wako Pure Chemical Industries (Osaka, Japan)	Wako Pure Chemical		No	Compost	Compost	Japan	Yes		
Saccharomonospora viridis	1852	PET	Kawai, F., Oda, M., Tamashiro, T., Waku, T., Tanaka, N., Yamamoto, M., ... & Tanokura, M. (2014). A novel Ca 2+-activated, thermostabilized polyesterase capable of hydrolyzing polyethylene terephthalate from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 98(24), 10053-10064.	Cutinase	00074	00074 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes	BAO42836.1	MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2014.0	Clear zone	A 0.25-mm-thick film of amorphous PET (PET-GF) was obtained from Goodfellows Cambridge, Ltd. (Tokyo, Japan). 	Goodfellow Cambridge		No	Compost	Compost	Japan	Yes		
Saccharomonospora viridis	1852	PHB	Kawai, F., Oda, M., Tamashiro, T., Waku, T., Tanaka, N., Yamamoto, M., ... & Tanokura, M. (2014). A novel Ca 2+-activated, thermostabilized polyesterase capable of hydrolyzing polyethylene terephthalate from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 98(24), 10053-10064.	Cutinase	00074	00074 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes	BAO42836.1	MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2014.0	Clear zone	The PHB was kindly provided by the Mitsubishi Gas Chem. Co., Inc. (Tokyo, Japan).	Mitsubishi Gas Chemical		No	Compost	Compost	Japan	Yes		
Saccharomonospora viridis	1852	PLA	Kawai, F., Oda, M., Tamashiro, T., Waku, T., Tanaka, N., Yamamoto, M., ... & Tanokura, M. (2014). A novel Ca 2+-activated, thermostabilized polyesterase capable of hydrolyzing polyethylene terephthalate from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 98(24), 10053-10064.	Cutinase	00074	00074 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes	BAO42836.1	MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2014.0	Clear zone	The poly(L-lactic acid) (PLLA; weight-average MW=1.69×105 ) and PDLA (weight-average MW=1.63×105 ) were synthesized as previously described (Kawai et al. 2011)		Yes	No	Compost	Compost	Japan	Yes		
Saccharomonospora viridis	1852	PHA	Kawai, F., Oda, M., Tamashiro, T., Waku, T., Tanaka, N., Yamamoto, M., ... & Tanokura, M. (2014). A novel Ca 2+-activated, thermostabilized polyesterase capable of hydrolyzing polyethylene terephthalate from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 98(24), 10053-10064.	Cutinase	00074	00074 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes	BAO42836.1	MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2014.0	Clear zone	The poly(L-lactic acid) (PLLA; weight-average MW=1.69×105 ) and PDLA (weight-average MW=1.63×105 ) were synthesized as previously described (Kawai et al. 2011)		Yes	No	Compost	Compost	Japan	Yes		
Fusarium oxysporum	5507	PCL	Dimarogona, M., Nikolaivits, E., Kanelli, M., Christakopoulos, P., Sandgren, M., & Topakas, E. (2015). Structural and functional studies of a Fusarium oxysporum cutinase with polyethylene terephthalate modification potential. Biochimica et Biophysica Acta (BBA)-General Subjects, 1850(11), 2308-2317.	Cutinase	00075	00075 | Cutinase | Fusarium oxysporum | PCL PET	Yes	5AJH_A	MLPAGQDAAALEARQLGGSITRNDLANGNSGSCPGVIFIYARGSTESGNLGTLGPRVASKLEAKYGKNGVWIQGVGGAYRATLGDNALPRGTSSAAIREMLGHFSDANQKCPDAVLIAGGYSQGAALAAASVTDVDAGIREKIAGAVLFGYTKNLQNRGKIPSYPEDRTKVFCNTGDLVCTGSLIVAAPHLAYQSAASGAAPEFLIQKADAAGAAAAALEHHHHHH	2015.0	Weight loss	Polycaprolactone (PCL), was purchased from Sigma-Aldrich	Sigma Aldrich	No	No				Yes		
Fusarium oxysporum	5507	PET	Dimarogona, M., Nikolaivits, E., Kanelli, M., Christakopoulos, P., Sandgren, M., & Topakas, E. (2015). Structural and functional studies of a Fusarium oxysporum cutinase with polyethylene terephthalate modification potential. Biochimica et Biophysica Acta (BBA)-General Subjects, 1850(11), 2308-2317.	Cutinase	00075	00075 | Cutinase | Fusarium oxysporum | PCL PET	Yes	5AJH_A	MLPAGQDAAALEARQLGGSITRNDLANGNSGSCPGVIFIYARGSTESGNLGTLGPRVASKLEAKYGKNGVWIQGVGGAYRATLGDNALPRGTSSAAIREMLGHFSDANQKCPDAVLIAGGYSQGAALAAASVTDVDAGIREKIAGAVLFGYTKNLQNRGKIPSYPEDRTKVFCNTGDLVCTGSLIVAAPHLAYQSAASGAAPEFLIQKADAAGAAAAALEHHHHHH	2015.0	Spectrophotometry	Commercial PET woven fabric with tricot knit was kindly supplied by Colora S.A	Colora	No	No				Yes		
Saccharomonospora viridis	1852	PET	Miyakawa, T., Mizushima, H., Ohtsuka, J., Oda, M., Kawai, F., & Tanokura, M. (2015). Structural basis for the Ca 2+-enhanced thermostability and activity of PET-degrading cutinase-like enzyme from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 99(10), 4297-4307.	Cutinase	00076	00076 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes		MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2015.0									Yes		
Saccharomonospora viridis	1852	PHA	Miyakawa, T., Mizushima, H., Ohtsuka, J., Oda, M., Kawai, F., & Tanokura, M. (2015). Structural basis for the Ca 2+-enhanced thermostability and activity of PET-degrading cutinase-like enzyme from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 99(10), 4297-4307.	Cutinase	00076	00076 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes		MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2015.0									Yes		
Saccharomonospora viridis	1852	PBAT	Miyakawa, T., Mizushima, H., Ohtsuka, J., Oda, M., Kawai, F., & Tanokura, M. (2015). Structural basis for the Ca 2+-enhanced thermostability and activity of PET-degrading cutinase-like enzyme from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 99(10), 4297-4307.	Cutinase	00076	00076 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes		MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2015.0									Yes		
Saccharomonospora viridis	1852	PBS	Miyakawa, T., Mizushima, H., Ohtsuka, J., Oda, M., Kawai, F., & Tanokura, M. (2015). Structural basis for the Ca 2+-enhanced thermostability and activity of PET-degrading cutinase-like enzyme from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 99(10), 4297-4307.	Cutinase	00076	00076 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes		MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2015.0									Yes		
Saccharomonospora viridis	1852	PBSA	Miyakawa, T., Mizushima, H., Ohtsuka, J., Oda, M., Kawai, F., & Tanokura, M. (2015). Structural basis for the Ca 2+-enhanced thermostability and activity of PET-degrading cutinase-like enzyme from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 99(10), 4297-4307.	Cutinase	00076	00076 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes		MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2015.0									Yes		
Saccharomonospora viridis	1852	PCL	Miyakawa, T., Mizushima, H., Ohtsuka, J., Oda, M., Kawai, F., & Tanokura, M. (2015). Structural basis for the Ca 2+-enhanced thermostability and activity of PET-degrading cutinase-like enzyme from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 99(10), 4297-4307.	Cutinase	00076	00076 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes		MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2015.0									Yes		
Saccharomonospora viridis	1852	PHB	Miyakawa, T., Mizushima, H., Ohtsuka, J., Oda, M., Kawai, F., & Tanokura, M. (2015). Structural basis for the Ca 2+-enhanced thermostability and activity of PET-degrading cutinase-like enzyme from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 99(10), 4297-4307.	Cutinase	00076	00076 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes		MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2015.0									Yes		
Saccharomonospora viridis	1852	PLA	Miyakawa, T., Mizushima, H., Ohtsuka, J., Oda, M., Kawai, F., & Tanokura, M. (2015). Structural basis for the Ca 2+-enhanced thermostability and activity of PET-degrading cutinase-like enzyme from Saccharomonospora viridis AHK190. Applied microbiology and biotechnology, 99(10), 4297-4307.	Cutinase	00076	00076 | Cutinase | Saccharomonospora viridis | PBAT PBS PBSA PCL PET PHB PLA PHA	Yes		MRIRRQAGTGARASMARAIGVMTTALAVLVGAVGGVAGAEVSTAQDNPYERGPDPTEDSIEAIRGPFSVATERVSSFASGFGGGTIYYPRETDEGTFGAVAVAPGFTASQGSMSWYGERVASQGFIVFTIDTNTRLDQPGQRGRQLLAALDYLVERSDRKVRERLDPNRLAVMGHSMGGGGSLEATVMRPSLKASIPLTPWNLDKTWGQVQVPTFIIGAELDTIASVRTHAKPFYESLPSSLPKAYMELDGATHFAPNIPNTTIAKYVISWLKRFVDEDTRYSQFLCPNPTDRAIEEYRSTCPY	2015.0									Yes		
Clostridium botulinum	1491	PBAT	Perz, V., Baumschlager, A., Bleymaier, K., Zitzenbacher, S., Hromic, A., Steinkellner, G., ... & Küper, U. (2016). Hydrolysis of synthetic polyesters by Clostridium botulinum esterases. Biotechnology and bioengineering, 113(5), 1024-1034.	Esterase	00077	00077 | Esterase | Clostridium botulinum | PBAT	Yes	AKZ20828.1	MAEPKAQGTQKVESSTTKKEVKDAEETIKIPTLEDIDNLIDSAEEVKSEEDINKMPPLKFPVEFPEVNTRSIIGGNNYPIVLVHGFMGFGRDELLGYKYWGGVVDLQEKLNASGHETYTATVGPVSSNWDRACELYAYIVGGTVDYGEAHAKKFKHNRYGRTYPGIYKNISNENKIHLIGHSMGGQTIRTLTQLLSEGSEEEINCGQENISPLFEGGKHWIHSVSTISTPNDGTTLSDLMPAKDLISYTFGVLGTITGKNKLFSSIYDLKLDQWGLKKQNGESQRDYIERVLDSNIWNSTKDIATYDLSTEGAQELNTWVKAQPDVYYFSWTTQATKESILTGHSVAQIGPMNPIFYPTANLMGRYSRNQKDLPIIDKKWFPNDGVVNCISQDGPKLGSNDVIEQYNGGVKIGQWNAMPR	2016.0	HPLC	PBAT (poly(butylene adipate-co-butylene terephthalate) was kindly provided by BASF SE.	BASF		No		Culture collection		Yes		
Clostridium botulinum	1491	PBAT	Perz, V., Baumschlager, A., Bleymaier, K., Zitzenbacher, S., Hromic, A., Steinkellner, G., ... & Küper, U. (2016). Hydrolysis of synthetic polyesters by Clostridium botulinum esterases. Biotechnology and bioengineering, 113(5), 1024-1034.	Esterase	00078	00078 | Esterase | Clostridium botulinum | PBAT	Yes	AKZ20829.1	MAGNSDAMGVGNNYPIVMVHGCFGWGSNEGAGLYYWGGKESLTQKLTEKGYTVYSPSIGPVSSNWDRACELYTYIVGGTVDYGESHSKKYGHERYGRSYPGVYKQIGTKDSSGNVQKIHLIGHSMGGQTIRLLAQLLENGDPNELSFTTDGSINSLFTGGKSWVSSITSIATPHDGSQEAHIKCDIEPLTHQFVAAIAAIKGKNVNLDDLNYDFQLDQWGLKRKPGESRLAYNNRVIKSEIWKKTKDLSVWDLSPEGAREFNSYVKAQSDIDYFSIACVNTHEDKLTHFQVPNKKMNPVLVKSSIFMGMYTNNKSGEVPIDKSWWRNDGVVSVISAINPKVGSTDKIVDYSGTAVKGTWNYLGELDNTDHIEVCGMKYDRKGIEQMYFNVAEMLSKLPVEIINTDHMDIVGTFGNVKDWYMDYASFLSNLSR	2016.0	HPLC	PBAT (poly(butylene adipate-co-butylene terephthalate) was kindly provided by BASF SE.	BASF		No		Culture collection		Yes		
Clostridium hathewayi	154046	PBAT	Perz, V., Hromic, A., Baumschlager, A., Steinkellner, G., Pavkov-Keller, T., Gruber, K., ... & Sinkel, C. (2016). An esterase from anaerobic Clostridium hathewayi can hydrolyze aliphatic–aromatic polyesters. Environmental science & technology, 50(6), 2899-2907.	Esterase	00079	00079 | Esterase | Clostridium hathewayi | PBAT	Yes	EFC94627.1	MAKQFLYDNLPVVETKAGKLRGYQWEGTYIFKGIRYARANRFQLPEEVEPWEGVKEAASYGFVCPMLTRDHPQGELLVPHRYWPQDEDCLSLNIWSQSLDRSAKKPVMFWIHGGAFSMGSSIEQKAYNGENMSRYGDVVVVTVNHRLNILGYLDLSPYGERYAGSANAGQADLVAALKWVRDNIEAFGGDPDNVTIFGQSGGGMKVSGLMQTPEADGLFHRAMIMSGVAGDVLPYSTGDSRPLIQAMLKELGLAEQEAGRLETVPYYDLAAAYNRVSPAIARAGGYIGCTPRPDDFYKGEGPAVGFTDHAKTIPVMVGTVFGEFAMMPLPFNKETISEAELDEILDKRFQGHGKELKTVFAEAYPGKSPVDLLTLDTIFRGPTKEFVRSLAAAGGSVYSYLFALEFPYQNQKTA	2016.0	HPLC;SEM	Milled PBAT	BASF	Yes	No				No		
Pelosinus fermentans	365349	PBAT	Biundo, A., Hromic, A., Pavkov-Keller, T., Gruber, K., Quartinello, F., Haernvall, K., ... & Guebitz, G. M. (2016). Characterization of a poly (butylene adipate-co-terephthalate)-hydrolyzing lipase from Pelosinus fermentans. Applied microbiology and biotechnology, 100(4), 1753-1764.	Lipase	00080	00080 | Lipase | Pelosinus fermentans | PBAT	Yes	EIW29778.1	MDSVMQTKEMVMKSNVNSYPIVLVHGFMGWGRNEVLGLKYWGGITDYEQELSSYGYTAYTATVGPVSSNWDRACELYAYIKGGTVDYGHAHSTQKGHSRYGRTYPGLYPEWGNLTTEGKVNKIHLVAHSMGGQTVRTLVQLLKEGSEEERNTTPSQLSSLFAGGKSWVHSITTIASPHDGTTLADGINIFGDFAKNLVASLASFTGAGEKLIYDFKLDQWGLNRKSGESLTDYTNRVFNSAIWNSTNDLANWDLSTDGARVLNQWVKAQSDIYYFSYSTCATVPSILTSNELPHVIYMTPLLYPFGRFIGSYTRNEQGRVIIDNSWKPNDGVVNTISQNGPKIWSSDKIVNYNGVPQIGKWNSMPLLDTIDHMDACGIGTNALTLSWYKGLAEKLSQLTISN	2016.0	Spectrophotometry;MS	PBAT	BASF	Yes	No				Yes		
Pseudomonas protegens	380021	PU	Hung, C. S., Zingarelli, S., Nadeau, L. J., Biffinger, J. C., Drake, C. A., Crouch, A. L., ... & Crookes-Goodson, W. J. (2016). Carbon catabolite repression and Impranil polyurethane degradation in Pseudomonas protegens strain Pf-5. Appl. Environ. Microbiol., 82(20), 6080-6090.	Polyurethanase A	00081	00081 | Polyurethanase A | Pseudomonas protegens | PU	Yes	WP_011061486.1	MGVFDYKNFTASDSKALFSDALAITLYSYHNIDNGFAEGYQHNGFGLGLPATLVTALIGSGNSQGVIPGIPWNPDSEKAALDALHQAGWSTISAQQLGYDGKVDGRGTFFGEKAGYGTAQVEILGKYDAQGHLESIGIAFRGTSGPRESVISDTIGDVINDLLAALGPKDYAKNYAGEAFGKLLGDVAAFAQANGLSGKDVLVSGHSLGGLGVNSLADLSSERWSGFYKDSNYIAYASPTQSASDKVLNIGYENDPVFRVLDGSTFKLSSLGVHDAHQDSATNNIVNFNDHYASTLWNVLPFSILNIPTWLSHLPTGYGDGLTRVLESKFYDFTSKDSTIVVANLSDPARASTWVQDLNRNAETHKGSTFIIGSDGNDLIQGGSGNDYLEGRAGNDTFRDSGGYNIILGGQGSNTLDLQQSVKNYSFASDGAGTLYLRDANGGISMTRDIGAIQSKEPGFLWGLFKDDVIHQVTDQGLKAGGQLTQYASSVRGDAGDNVLKAHAGGDWLFGLDGNDHLIGGQGNDVFVGGAGNDLMEAGGGNNTFLFTGHFGQDRILGYQGGDKLVFMGVSGVLPDQDYRAHASSSGNDTVLTFGQDSVTLVGVSLEHLNGSGIVLA	2016.0	Clear zone;Spectrophotometry;NMR;HPLC	Impranil DLN (Impranil)	Bayer 	No	No				No		
Pseudomonas protegens	380021	PU	Hung, C. S., Zingarelli, S., Nadeau, L. J., Biffinger, J. C., Drake, C. A., Crouch, A. L., ... & Crookes-Goodson, W. J. (2016). Carbon catabolite repression and Impranil polyurethane degradation in Pseudomonas protegens strain Pf-5. Appl. Environ. Microbiol., 82(20), 6080-6090.	Polyurethanase B	00082	00082 | Polyurethanase B | Pseudomonas protegens | PU	Yes	WP_011061489.1	MSIFDYKTALGGDGKALYSEAITLALYASTPTGEALPGTAWRPISASQLGYQGNVSAQGTISGEQAIVSDAQVEVLGKYDASGQLLSIGISFRGTDSLKDGINDLQAAFVSGFADNYSRLAFDNLLGKVAAFAAAQGLSGSDVLVTGHSLGGLGVNSLAAMSSDHWGGFYQDASYVAFASPTQSANSSQVLNIGYENDPVFRALDGTHFNASSLGTHDKPQESATNNIVSFTDHYSSFLGKLIPQSILNPQSWSAHSAVDYAGGLNRLINSDFYDLTSRDSTVVISNLSEGKRDQVWVKDLNLYAEKHTGSTFIIGTQSNDLLHGGKGNDYLDGGAGDDRFRDDGGYNIIHGGQGHNVLELQQPLKNFSIANDGDGTLYIRDAYGGISMTRDVGALVSHETGSWWQLFGKDVSHSVTADGLQNGNQWTAYNHSLNGDAYGNALVASVDGDWLFGHGGDDLLSSDKANVTFVGGTGNDVMHSSGGGGNTFLFSGNFGFDLIHGYQNTDKLVFMGVPGVDAHYDYSQHLSQNGNDTLLSVGEFSVTLVGVGMDSLSGSGLVFA	2016.0	Clear zone;Spectrophotometry;NMR;HPLC	Impranil DLN (Impranil)	Bayer 	No	No				No		
Pseudideonella sakaiensis	1547922	PET	Yoshida, S., Hiraga, K., Takehana, T., Taniguchi, I., Yamaji, H., Maeda, Y., ... & Oda, K. (2016). A bacterium that degrades and assimilates poly (ethylene terephthalate). Science, 351(6278), 1196-1199.; Liu, C., Shi, C., Zhu, S., Wei, R., & Yin, C. C. (2019). Structural and functional characterization of polyethylene terephthalate hydrolase from Ideonella sakaiensis. Biochemical and biophysical research communications, 508(1), 289-294.; Seo, H., Kim, S., Son, H. F., Sagong, H. Y., Joo, S., & Kim, K. J. (2019). Production of extracellular PETase from Ideonella sakaiensis using sec-dependent signal peptides in E. coli. Biochemical and biophysical research communications, 508(1), 250-255.; 	PETase	00083	00083 | PETase | Ideonella sakaiensis | PET PEF	Yes	A0A0K8P6T7	MNFPRASRLMQAAVLGGLMAVSAAATAQTNPYARGPNPTAASLEASAGPFTVRSFTVSRPSGYGAGTVYYPTNAGGTVGAIAIVPGYTARQSSIKWWGPRLASHGFVVITIDTNSTLDQPSSRSSQQMAALRQVASLNGTSSSPIYGKVDTARMGVMGWSMGGGGSLISAANNPSLKAAAPQAPWDSSTNFSSVTVPTLIFACENDSIAPVNSSALPIYDSMSRNAKQFLEINGGSHSCANSGNSNQALIGKKGVAWMKRFMDNDTRYSTFACENPNSTRVSDFRTANCS	2016.0	SEM;Weight loss	PET film			No	Plastic debris	Plastic waste dumping site	Japan	No		
Pseudideonella sakaiensis	1547922	PET	Yoshida, S., Hiraga, K., Takehana, T., Taniguchi, I., Yamaji, H., Maeda, Y., ... & Oda, K. (2016). A bacterium that degrades and assimilates poly (ethylene terephthalate). Science, 351(6278), 1196-1199.; Liu, C., Shi, C., Zhu, S., Wei, R., & Yin, C. C. (2019). Structural and functional characterization of polyethylene terephthalate hydrolase from Ideonella sakaiensis. Biochemical and biophysical research communications, 508(1), 289-294.; Seo, H., Kim, S., Son, H. F., Sagong, H. Y., Joo, S., & Kim, K. J. (2019). Production of extracellular PETase from Ideonella sakaiensis using sec-dependent signal peptides in E. coli. Biochemical and biophysical research communications, 508(1), 250-255.; 	MHETase	00084	00084 | MHETase | Ideonella sakaiensis | PET	Yes	A0A0K8P8E7	MQTTVTTMLLASVALAACAGGGSTPLPLPQQQPPQQEPPPPPVPLASRAACEALKDGNGDMVWPNAATVVEVAAWRDAAPATASAAALPEHCEVSGAIAKRTGIDGYPYEIKFRLRMPAEWNGRFFMEGGSGTNGSLSAATGSIGGGQIASALSRNFATIATDGGHDNAVNDNPDALGTVAFGLDPQARLDMGYNSYDQVTQAGKAAVARFYGRAADKSYFIGCSEGGREGMMLSQRFPSHYDGIVAGAPGYQLPKAGISGAWTTQSLAPAAVGLDAQGVPLINKSFSDADLHLLSQAILGTCDALDGLADGIVDNYRACQAAFDPATAANPANGQALQCVGAKTADCLSPVQVTAIKRAMAGPVNSAGTPLYNRWAWDAGMSGLSGTTYNQGWRSWWLGSFNSSANNAQRVSGFSARSWLVDFATPPEPMPMTQVAARMMKFDFDIDPLKIWATSGQFTQSSMDWHGATSTDLAAFRDRGGKMILYHGMSDAAFSALDTADYYERLGAAMPGAAGFARLFLVPGMNHCSGGPGTDRFDMLTPLVAWVERGEAPDQISAWSGTPGYFGVAARTRPLCPYPQIARYKGSGDINTEANFACAAPP	2016.0	SEM;Weight loss	PET film			No	Plastic debris	Plastic waste dumping site	Japan	No		
Uncultured bacterium	77133	PBAT	Müller, C. A., Perz, V., Provasnek, C., Quartinello, F., Guebitz, G. M., & Berg, G. (2017). Discovery of polyesterases from moss-associated microorganisms. Appl. Environ. Microbiol., 83(4), e02641-16.	Carboxylesterase	00085	00085 | Carboxylesterase | Uncultured bacterium | PBAT	Yes	AOR05752.1	MASWQSKILNPVIRALVKRKLLKTHDAAGIRKAFGGVLPPPRGAQFSADVVGGMPGEWAKSGGAAAGTMLYLHGGGYVGGSTATHRPITAAFAIRGLDVFVPDYRLAPENAFPAAVDDGLAAYKGLLDAGIAPAKLTIAGDSAGGGLALAILLAAKAEGVTMPACAILLSPWTDLAVTGETVRTNLDRDPMLTDSVLKDNAAFYLNGADPKNPLASPLYGDLAGLPPLMITAGDTEVLLEDSTRFAARAREHGVAVSLKIWEGMPHVWQLFQRVLPEARAAIEEAARFAKAHFST	2017.0	Clear zone;HPLC	Milled PBAT, with a melting point of 125.3°C, a glass transition temperature of _x005	BASF	Yes	No				Yes		
Uncultured bacterium	77133	PBAT	Müller, C. A., Perz, V., Provasnek, C., Quartinello, F., Guebitz, G. M., & Berg, G. (2017). Discovery of polyesterases from moss-associated microorganisms. Appl. Environ. Microbiol., 83(4), e02641-16.	Carboxylesterase	00086	00086 | Carboxylesterase | Uncultured bacterium | PBAT	Yes	AOR05751.1	MGKQDLVRAVLENAVASGAVAGAVAAVTTASGTVLEVAAGQQSAEVPAPMAVDSVFWVASMTKALTTVAAMQLVEDGRLTLNDPIETILPDLANPMVLEGFADDGSPITRPARKKITLGQLLTHTAGFSYDFASADLARYLAVTGTPSAATGLKAGLRQPLLFEPGERWEYSIGIDWAGQAVEAVSGRRLDDYFAAYVTGPLGMKDTVFQPGKARDSRRAAMHQRTEDGGLKVVPFDPRPAPEFLSGGGGLYSTAPDYLAFMRMILNQGGDILAPETVEAMGRNQIGKLRAGRIGSANPAVIAPSDFYPGMDAKWGLGFLLNPAPGPFGRSAGSLTWAGLPNCYYWIDPAKGIAAVILMQLLPSGDPGALKTYAGFEAAVYASL	2017.0	Clear zone;HPLC	Milled PBAT, with a melting point of 125.3°C, a glass transition temperature of _x005	BASF	Yes	No				Yes		
Pseudomonas pseudoalcaligenes	301	PBAT	Wallace, P. W., Haernvall, K., Ribitsch, D., Zitzenbacher, S., Schittmayer, M., Steinkellner, G., ... & Birner-Gruenberger, R. (2017). PpEst is a novel PBAT degrading polyesterase identified by proteomic screening of Pseudomonas pseudoalcaligenes. Applied microbiology and biotechnology, 101(6), 2291-2303.	Polyesterase	00087	00087 | Polyesterase | Pseudomonas pseudoalcaligenes | PBAT	Yes	AMW89397.1	MGTLLVVGDSISAAFGLDSRQGWVALLEKRLSEEGFEHSVVNASISGDTSAGGAARLSALLAEHKPELVIIELGGNDGLRGQPPAQLQQNLASMVEQSQQAGAKVLLLGMKLPPNYGVRYTTAFAQVFTDLAEQKQVSLVPFFLEGVGGVPGMMQADGIHPAEAAQEILLDNVWPTLKPML	2017.0	MS	The PBAT film and aromatic polyester mimicking oligomer bis(4-(benzoyloxybutyl)terephthalate (BABuTABuBA) were synthesised as previously described (Perz et al. 2016a) and kindly provided by BASF SE (Germany)	BASF	Yes	No				Yes		
Uncultured bacterium	77133	PBAT	Müller, C. A., Perz, V., Provasnek, C., Quartinello, F., Guebitz, G. M., & Berg, G. (2017). Discovery of polyesterases from moss-associated microorganisms. Appl. Environ. Microbiol., 83(4), e02641-16.	Carboxylesterase	00088	00088 | Carboxylesterase | Uncultured bacterium | PBAT	Yes	AOR05753.1	MKKVIVFLVFMLFCTATYAQKVSKVVFFGDSLTDNGNLFRLVELIPKTPPYYQGRFSNGPTWAENLGEYFVKTNGAKYEIYAYAGATAAAHNIFETLAPTLLVDQVARYLETNPSDDKSKVLFVFWIGANDYLFLPTGNADELTTAAIQKTANGITTLLDQGAQNFLILDLPDLSKTPFAADLNMVSQMGSFTILHNQKLASLVDKMQKEHPQAQLMLFQLLQFSELIENPAKYNAKYHLNLSNTRAACWQGSVFDDIDTDNLANKTNKAISNPQPEVKEPILCEHPEQYVFFDHLHPTATVHQLLAALVEEAMNNRWS	2017.0	Clear zone;HPLC	Milled PBAT, with a melting point of 125.3°C, a glass transition temperature of _x005	BASF	Yes	No				Yes		
Uncultured bacterium	77133	PBAT	Müller, C. A., Perz, V., Provasnek, C., Quartinello, F., Guebitz, G. M., & Berg, G. (2017). Discovery of polyesterases from moss-associated microorganisms. Appl. Environ. Microbiol., 83(4), e02641-16.	Carboxylesterase	00089	00089 | Carboxylesterase | Uncultured bacterium | PBAT	Yes	AOR05749.1	MNEAMIRGVLEEAVASGGIAGAVVTVTDANATLFQLAVGRQSVAAPDPMRADSVFWIASMTKAITTVAALQLVEQGKLTLDEPIGDVLPELAEPVVLKGFGADGAPVVEPAQAKLTLKHLLTHTSGFSYEFANGDLARYLERTGHPSAATGLKAGLRQPLMFEPGARWEYGIGIDWAGQAVEAASGMTLDAYFAAYVTGPLGMTDTLFLPRADQAARRVAMHQRQPDGSLTAVPFEPRPAPEYLAGGAGLYSTAPDYAAFLRMILNKGMGLLKPETVAAMGTNQIGALRAGKIGSVNPGLTAEADFYPGMDSKWGLGFLINPEKGSFGRSADSLTWAGLPNCYYWIDREKGIGAVILMQSLPSGDMGALKAAAGFEYALYASL	2017.0	Clear zone;HPLC	Milled PBAT, with a melting point of 125.3°C, a glass transition temperature of _x005	BASF	Yes	No				Yes		
Uncultured bacterium	77133	PBAT	Müller, C. A., Perz, V., Provasnek, C., Quartinello, F., Guebitz, G. M., & Berg, G. (2017). Discovery of polyesterases from moss-associated microorganisms. Appl. Environ. Microbiol., 83(4), e02641-16.	Carboxylesterase	00090	00090 | Carboxylesterase | Uncultured bacterium | PBAT	Yes	AOR05750.1	MRTVDGRIGMVERRTRLVSLLAAAALAVSLSGCSATTVLNTLEPRWDVAATRDVAYAPGPRHDVDVYAPKKIGPHTPVVVFIYGGGWDSGEKSKYAFVGSALASHGYLVFIPNYRIYPEAHYPDFLQDCALAVRWAKDHAAQYGGDPGELFLMGHSAGAYNAAMLATDPQWLGAVGMDPHRDLKGMVGLAGPYDFLPLQSDELKAIFGAVGQEPASQPINHVDGREPPMFLAHDLGDTVVYPKNTINMAAKIQAAGGEVETKYYKGLSHALMIGVFAAPLRFLGPVFRDSTQFIDAHASSSASKP	2017.0	Clear zone;HPLC	Milled PBAT, with a melting point of 125.3°C, a glass transition temperature of _x005	BASF	Yes	No				Yes		
Uncultured bacterium	77133	PBAT	Müller, C. A., Perz, V., Provasnek, C., Quartinello, F., Guebitz, G. M., & Berg, G. (2017). Discovery of polyesterases from moss-associated microorganisms. Appl. Environ. Microbiol., 83(4), e02641-16.	Carboxylesterase	00091	00091 | Carboxylesterase | Uncultured bacterium | PBAT	Yes	AOR05748.1	MTTRPESLGLSAERLKRLDAHFDAKYVQTGKLPFAMTLVSRKGEVAHHGFSGLMDEARGKKVEADSLFRIYSMTKPLTSVLFMMLVEEGKVALDDPVHSLIPSWKNLGVYAGGWDMMASKPCARPMQMVDLLRHTSGLTYGFQQRTNVDAAYRKHNIGVFERQISLDATIEALAALPLEFSPGEAWNYSVSTDILGYLIGKIEGRPFEEVLKARLTGPLGMDDTDFQVKASERGRFAACSAINAKGERVLNDDPEKSSYLQPPVLVSGGGGLVSTAGDYLKFCQMMLNGGEANGTRFLSPKTIALMTSNHLPGGVDLPQLSKSLFSEVAYDGVGFGLGFSVTMDPAKTLLPGTAGEYAWGGAASTAFWIDPKEELIVIFMTQLIPSSFYPIRRELRTLAYSAITESFV	2017.0	Clear zone;HPLC	Milled PBAT, with a melting point of 125.3°C, a glass transition temperature of _x005	BASF	Yes	No				Yes		
Fusarium solani	169388	PMCL	De Hoe, G. X., Zumstein, M. T., Tiegs, B. J., Brutman, J. P., McNeill, K., Sander, M., ... & Hillmyer, M. A. (2018). Sustainable polyester elastomers from lactones: synthesis, properties, and enzymatic hydrolyzability. Journal of the American Chemical Society, 140(3), 963-973.	Cutinase	00092	00092 | Cutinase | Fusarium solani | PMCL	Yes	1AGY	LGRTTRDDLINGNSASCRDVIFIYARGSTETGNLGTLGPSIASNLESAFGKDGVWIQGVGGAYRATLGDNALPRGTSSAAIREMLGLFQQANTKCPDATLIAGGYSQGAALAAASIEDLDSAIRDKIAGTVLFGYTKNLQNRGRIPNYPADRTKVFCNTGDLVCTGSLIVAAPHLAYGPDARGPAPEFLIEKVRAVRGSA	2018.0	TOC;NMR	. In a typical polymerization, a 50 mL pressure vessel was loaded with MCL (20.0 g, 156 mmol) and pentaerythritol (137 mg, 1.01 mmol) under an inert atmosphere. A stock solution of SnOct2 was prepared in toluene and added (90 μL stock solution, 12.7 mg, 31.2 μmol of SnOct2) to the pressure vessel. A Teflon-coated magnetic stir bar was added to the pressure vessel, which was subsequently sealed, removed from inert atmosphere, and placed in a preheated silicone oil bath. The polymerization was allowed to proceed for 2 h at 160 °C; by the end of the reaction, the contents were still clear but had a slight yellow tinge, and the viscosity had increased drastically such that the stir bar was not stirring effectively. DCM was added to approximately double the volume in the pressure vessel, and the crude PMCL was dissolved overnight. PMCL was then precipitated from DCM twicefirst into methanol, then using hexanesand consolidated into a tared jar. The pure polymer was then dried under a stream of nitrogen gas for 24 h before being placed in a vacuum oven, where it was dried under a vacuum for 2 days. T		Yes	No				Yes		
Stenotrophomonas rhizophila	216778	PVA	Wei, Y., Fu, J., Wu, J., Jia, X., Zhou, Y., Li, C., ... & Chen, F. (2018). Bioinformatics analysis and characterization of highly efficient polyvinyl alcohol (PVA)-degrading enzymes from the novel PVA degrader Stenotrophomonas rhizophila QL-P4. Appl. Environ. Microbiol., 84(1), e01898-17.	PVA dehydrogenase	00093	00093 | PVA dehydrogenase | Stenotrophomonas rhizophila | PVA	Yes	AOA73724.1	MAALQQRTIDLLRTHQDTVVAQWSDQLAGSGQGQDGRLSTRELDAQVREFWRLFQTAVSTNGTGVAGSEWQDTRQFLEQLSRDRVLKGFSSSETASFLFSLKRPLFELVQQNFADDPKAVGDQLWAISELIDGLGLHSVKVYQKTREDVIQRQQEEMLELSTPVVKLWEGVLALPMIGTLDSQRTQVVMESLLQRIVDTGSEIAIIDITGVPTVDTLVAQHLLKTVTAIRLMGADAIISGVRPQIAQTIVHLGLDLQGIVTKANLADALALALKRTGQTVTKAAR	2018.0	Iodometric analysis;Spectrophotometry	PVA with an average polymerization degree of 1,750   50	Sinopharm Chemical Reagent		No	Leaf	Soil	China	No		
Pseudomonas sp.	306	PU	Stamps, B. W., Zingarelli, S., Hung, C. S., Drake, C. A., Varaljay, V. A., Stevenson, B. S., & Crookes-Goodson, W. J. (2018). Finished Genome Sequence of a Polyurethane-Degrading Pseudomonas Isolate. Genome Announc., 6(9), e00084-18.	Polyurethanase	00094	00094 | Polyurethanase | Pseudomonas sp. | PU	Yes	POM09750.1	MGIFDYKNLGTEGSKTLFADAMAITLYAYHNLDNGYAVGYQHNGLGLGLPATLVQALLGSTDSQGVIPGIPWNPDSEKAALDAVQQAGWTPISASSLGYTGKVDARGTFFGEKPGYTTAQVEVLGKYDDAGKLLEIGIGFRGTSGPREHLISDSIGDVISDLLAAFGPKDYAKNYVGEAFGGLLKNVAEFAGAHGLSGQDVLVSGHSLGGLAVNSMADLSDSKWSGFYKDANYVAYASPTQSGGDKVLNVGYENDPVFRALDGASFNLSSLGVHDKPHESTTDNIVSFNDHYASSLWNVLPFSILNLPTWVSHLPTGYGDGMTRILDSGFYEQMTRDSTVIVANLSDPARANTWVQDLNRNAEAHKGDTFIIGSHGDDLIQGGKGADFIEGGKGNDTIRDSSGHNTFLFSGHFGNDRVVGYQATDKLVFTDVQGSADYRDHAKLVGGDTVISFGADSVTLVG	2018.0									No		
Vibrio gazogenes	687	PCL	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	PETase	00095	00095 | PET-hydrolase | Vibrio gazogenes | PCL PET	Yes	ASA57064.1	MMNVLTKCKLALGIIAIFFSLPSFAVPCSDCSNGFERGQVPRVDQLESSRGPYSVKTINVSRLARGFGGGTIHYSTESGGQQGIIAVVPGYVSLEGSIKWWGPRLASWGFTVITIDTNTIYDQPDSRASQLSAAIDYVIDKGNDRSSPIYGLVDPNRVGVIGWSMGGGGSLKLATDRKIDAVIPQAPWYLGLSRFSSITSPTMIIACQADVVAPVSVHASRFYNQIPGTTPKAYFEIALGSHFCANTGYPSEDILGRNGVAWMKRFIDKDERYTQFLCGQNFDSSLRVSEYRDNCSYY	2018.0	Clear zone								Yes		
Vibrio gazogenes	687	PET	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	PETase	00095	00095 | PET-hydrolase | Vibrio gazogenes | PCL PET	Yes	ASA57064.1	MMNVLTKCKLALGIIAIFFSLPSFAVPCSDCSNGFERGQVPRVDQLESSRGPYSVKTINVSRLARGFGGGTIHYSTESGGQQGIIAVVPGYVSLEGSIKWWGPRLASWGFTVITIDTNTIYDQPDSRASQLSAAIDYVIDKGNDRSSPIYGLVDPNRVGVIGWSMGGGGSLKLATDRKIDAVIPQAPWYLGLSRFSSITSPTMIIACQADVVAPVSVHASRFYNQIPGTTPKAYFEIALGSHFCANTGYPSEDILGRNGVAWMKRFIDKDERYTQFLCGQNFDSSLRVSEYRDNCSYY	2018.0	Clear zone;HPLC								Yes		
Pseudideonella sakaiensis	1547922	PEF	Austin, H. P., Allen, M. D., Donohoe, B. S., Rorrer, N. A., Kearns, F. L., Silveira, R. L., ... & Mykhaylyk, V. (2018). Characterization and engineering of a plastic-degrading aromatic polyesterase. Proceedings of the National Academy of Sciences, 115(19), E4350-E4357.	PETase	00096	00096 | PETase | Ideonella sakaiensis | PET PEF	Yes		MNFPRASRLMQAAVLGGLMAVSAAATAQTNPYARGPNPTAASLEASAGPFTVRSFTVSRPSGYGAGTVYYPTNAGGTVGAIAIVPGYTARQSSIKWWGPRLASHGFVVITIDTNSTLDQPSSRSSQQMAALRQVASLNGTSSSPIYGKVDTARMGVMGWSMGGGGSLISAANNPSLKAAAPQAPWDSSTNFSSVTVPTLIFACENDSIAPVNSSALPIYDSMSRNAKQFLEINGGSHSCANSGNSNQALIGKKGVAWMKRFMDNDTRYSTFACENPNSTRVSDFRTANCS	2018.0	SEM;DSC;NMR;HPLC	Produced via the polycondensation of EG with FDCA			No	Soil	Plastic waste dumping site	Japan	Yes		
Oleispira antarctica	188908	PCL	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	PETase	00097	00097 | PETase | Oleispira antarctica | PCL PET	Yes	CCK74972.1	MNKSILKKLSFGTSVLLVSMNALSWTPSPTPNPDPIPDPTPCQDDCDFTRGPNPTPSSLEASTGPYSVATRSVASSVSGFGGGTLHYPTNTTGTMGAIAVVPGFLLQESSIDFWGPKLASHGFVVITISANSGFDQPASRATQLGRALDYVINQSNGSNSPISGMVDTTRLGVVGWSMGGGGALQLASGDRLSAAIPIAPWNQGGNRFDQIETPTLVIACENDVVASVNSHASPFYNRIPSTTDKAYLEINGGSHFCANDGGSIGGLLGKYGVSWMKRFIDNDLRYDAFLCGPDHAANRSVSEYRDTCNY	2018.0	Clear zone								Yes		
Oleispira antarctica	188908	PET	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	PETase	00097	00097 | PETase | Oleispira antarctica | PCL PET	Yes	CCK74972.1	MNKSILKKLSFGTSVLLVSMNALSWTPSPTPNPDPIPDPTPCQDDCDFTRGPNPTPSSLEASTGPYSVATRSVASSVSGFGGGTLHYPTNTTGTMGAIAVVPGFLLQESSIDFWGPKLASHGFVVITISANSGFDQPASRATQLGRALDYVINQSNGSNSPISGMVDTTRLGVVGWSMGGGGALQLASGDRLSAAIPIAPWNQGGNRFDQIETPTLVIACENDVVASVNSHASPFYNRIPSTTDKAYLEINGGSHFCANDGGSIGGLLGKYGVSWMKRFIDNDLRYDAFLCGPDHAANRSVSEYRDTCNY	2018.0	Clear zone;HPLC								Yes		
Uncultured bacterium	77133	PCL	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	PETase	00098	00098 | PETase | Uncultured bacterium | PCL PET	Yes	ACC95208.1	MPITARNTLASLLLASSALLLSGTAFAANPPGGDPDPGCQTDCNYQRGPDPTDAYLEAASGPYTVSTIRVSSLVPGFGGGTIHYPTNAGGGKMAGIVVIPGYLSFESSIEWWGPRLASHGFVVMTIDTNTIYDQPSQRRDQIEAALQYLVNQSNSSSSPISGMVDSSRLAAVGWSMGGGGTLQLAADGGIKAAIALAPWNSSINDFNRIQVPTLIFACQLDAIAPVALHASPFYNRIPNTTPKAFFEMTGGDHWCANGGNIYSALLGKYGVSWMKLHLDQDTRYAPFLCGPNHAAQTLISEYRGNCPY	2018.0	Clear zone								Yes		
Uncultured bacterium	77133	PET	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	PETase	00098	00098 | PETase | Uncultured bacterium | PCL PET	Yes	ACC95208.1	MPITARNTLASLLLASSALLLSGTAFAANPPGGDPDPGCQTDCNYQRGPDPTDAYLEAASGPYTVSTIRVSSLVPGFGGGTIHYPTNAGGGKMAGIVVIPGYLSFESSIEWWGPRLASHGFVVMTIDTNTIYDQPSQRRDQIEAALQYLVNQSNSSSSPISGMVDSSRLAAVGWSMGGGGTLQLAADGGIKAAIALAPWNSSINDFNRIQVPTLIFACQLDAIAPVALHASPFYNRIPNTTPKAFFEMTGGDHWCANGGNIYSALLGKYGVSWMKLHLDQDTRYAPFLCGPNHAAQTLISEYRGNCPY	2018.0	Clear zone								Yes		
Polyangium brachysporum	413882	PCL	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	PETase	00099	00099 | PETase | Polyangium brachysporum | PCL PET	Yes	AKJ29164.1	MPPDCVLPRRLAAAALLASATLVPLSAAAQTNPYQRGPDPTTRDLEDSRGPFRYASTNVRSPSGYGAGTIYYPTDVSGSVGAVAVVPGYLARQSSIRWWGPRLASHGFVVITLDTRSTSDQPASRSAQQMAALRQVVALSETRSSPIYGKVDPNRLAVMGWSMGGGGTLISARDNPSLKAAVPFAPWHNTANFSGVQVPTLVIACENDTVAPISRHASSFYNSFSSSLAKAYLEINNGSHTCANTGNSNQALIGKYGVAWIKRFVDNDTRYSPFLCGAPHQADLRSSRLSEYRESCPY	2018.0	Clear zone								Yes		
Polyangium brachysporum	413882	PET	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	PETase	00099	00099 | PETase | Polyangium brachysporum | PCL PET	Yes	AKJ29164.1	MPPDCVLPRRLAAAALLASATLVPLSAAAQTNPYQRGPDPTTRDLEDSRGPFRYASTNVRSPSGYGAGTIYYPTDVSGSVGAVAVVPGYLARQSSIRWWGPRLASHGFVVITLDTRSTSDQPASRSAQQMAALRQVVALSETRSSPIYGKVDPNRLAVMGWSMGGGGTLISARDNPSLKAAVPFAPWHNTANFSGVQVPTLVIACENDTVAPISRHASSFYNSFSSSLAKAYLEINNGSHTCANTGNSNQALIGKYGVAWIKRFVDNDTRYSPFLCGAPHQADLRSSRLSEYRESCPY	2018.0	Clear zone;HPLC								Yes		
Aspergillus fumigatus	746128	PBS	Jung, H. W., Yang, M. K., & Su, R. C. (2018). Purification, characterization, and gene cloning of an Aspergillus fumigatus polyhydroxybutyrate depolymerase used for degradation of polyhydroxybutyrate, polyethylene succinate, and polybutylene succinate. Polymer degradation and stability, 154, 186-194.	Esterase	00100	00100 | Esterase | Aspergillus fumigatus | PBS PCL PES PHB PLA PHA	Yes		MRGVWRYMPVYYYKCMLIPLLTFTKISIISKPQESRISLIICRTMPTVATFLGLAISGAAMASGAALGAYNVDPNSISVSGLSSGGFMSAQLGVAYSDTFKVGFGVFAGGPYDCARGQSYTTCMYNQNPSITTPVANMKSWSGNKINPVSNLQSRKIYMWTGTADTTVGPNVMSQLKTQLANFASAANVSYITTSGAAHTFPTDFDAAGDNSCSSSVSPYISNCQCDGAGAVLQWMYGPLNARNPGTLSGSIVSFSQTGEYGASGMDTTGYLYVPRACQPGSSTVCKLHVALHGCKQSYSMIGSKFVSNTGYNMWADTNDIIILYPQAVADNTMHTIWTGMPLPNPNGCWDWVGWYGANADQVGGVQMAAIVNQVARVVSGYGAGSSSSTTAATPTTTTGSITTTTTTTATVTTTAVAPLYGQCGGIGWTGPTACATGVCTAYSPYYAQCLLIV	2018.0	Clear zone;MS;Weight loss;SEM	Poly (1,4-butylene succinate) (PBS, Mn: unknown)	Sigma Aldrich	Yes	No	Soil	Hot spring	Taiwan	No		
Aspergillus fumigatus	746128	PCL	Jung, H. W., Yang, M. K., & Su, R. C. (2018). Purification, characterization, and gene cloning of an Aspergillus fumigatus polyhydroxybutyrate depolymerase used for degradation of polyhydroxybutyrate, polyethylene succinate, and polybutylene succinate. Polymer degradation and stability, 154, 186-194.	Esterase	00100	00100 | Esterase | Aspergillus fumigatus | PBS PCL PES PHB PLA PHA	Yes		MRGVWRYMPVYYYKCMLIPLLTFTKISIISKPQESRISLIICRTMPTVATFLGLAISGAAMASGAALGAYNVDPNSISVSGLSSGGFMSAQLGVAYSDTFKVGFGVFAGGPYDCARGQSYTTCMYNQNPSITTPVANMKSWSGNKINPVSNLQSRKIYMWTGTADTTVGPNVMSQLKTQLANFASAANVSYITTSGAAHTFPTDFDAAGDNSCSSSVSPYISNCQCDGAGAVLQWMYGPLNARNPGTLSGSIVSFSQTGEYGASGMDTTGYLYVPRACQPGSSTVCKLHVALHGCKQSYSMIGSKFVSNTGYNMWADTNDIIILYPQAVADNTMHTIWTGMPLPNPNGCWDWVGWYGANADQVGGVQMAAIVNQVARVVSGYGAGSSSSTTAATPTTTTGSITTTTTTTATVTTTAVAPLYGQCGGIGWTGPTACATGVCTAYSPYYAQCLLIV	2018.0	Clear zone;MS;Weight loss;SEM	polycaprolactone (PCL, average Mn: 80,000 Da)	Sigma Aldrich	Yes	No	Soil	Hot spring	Taiwan	No		
Aspergillus fumigatus	746128	PES	Jung, H. W., Yang, M. K., & Su, R. C. (2018). Purification, characterization, and gene cloning of an Aspergillus fumigatus polyhydroxybutyrate depolymerase used for degradation of polyhydroxybutyrate, polyethylene succinate, and polybutylene succinate. Polymer degradation and stability, 154, 186-194.	Esterase	00100	00100 | Esterase | Aspergillus fumigatus | PBS PCL PES PHB PLA PHA	Yes		MRGVWRYMPVYYYKCMLIPLLTFTKISIISKPQESRISLIICRTMPTVATFLGLAISGAAMASGAALGAYNVDPNSISVSGLSSGGFMSAQLGVAYSDTFKVGFGVFAGGPYDCARGQSYTTCMYNQNPSITTPVANMKSWSGNKINPVSNLQSRKIYMWTGTADTTVGPNVMSQLKTQLANFASAANVSYITTSGAAHTFPTDFDAAGDNSCSSSVSPYISNCQCDGAGAVLQWMYGPLNARNPGTLSGSIVSFSQTGEYGASGMDTTGYLYVPRACQPGSSTVCKLHVALHGCKQSYSMIGSKFVSNTGYNMWADTNDIIILYPQAVADNTMHTIWTGMPLPNPNGCWDWVGWYGANADQVGGVQMAAIVNQVARVVSGYGAGSSSSTTAATPTTTTGSITTTTTTTATVTTTAVAPLYGQCGGIGWTGPTACATGVCTAYSPYYAQCLLIV	2018.0	Clear zone;MS;Weight loss;SEM	Polyethylene glycol succinate (PES, Mn: unknown)	Tokuyama		No	Soil	Hot spring	Taiwan	No		
Aspergillus fumigatus	746128	PHB	Jung, H. W., Yang, M. K., & Su, R. C. (2018). Purification, characterization, and gene cloning of an Aspergillus fumigatus polyhydroxybutyrate depolymerase used for degradation of polyhydroxybutyrate, polyethylene succinate, and polybutylene succinate. Polymer degradation and stability, 154, 186-194.	Esterase	00100	00100 | Esterase | Aspergillus fumigatus | PBS PCL PES PHB PLA PHA	Yes		MRGVWRYMPVYYYKCMLIPLLTFTKISIISKPQESRISLIICRTMPTVATFLGLAISGAAMASGAALGAYNVDPNSISVSGLSSGGFMSAQLGVAYSDTFKVGFGVFAGGPYDCARGQSYTTCMYNQNPSITTPVANMKSWSGNKINPVSNLQSRKIYMWTGTADTTVGPNVMSQLKTQLANFASAANVSYITTSGAAHTFPTDFDAAGDNSCSSSVSPYISNCQCDGAGAVLQWMYGPLNARNPGTLSGSIVSFSQTGEYGASGMDTTGYLYVPRACQPGSSTVCKLHVALHGCKQSYSMIGSKFVSNTGYNMWADTNDIIILYPQAVADNTMHTIWTGMPLPNPNGCWDWVGWYGANADQVGGVQMAAIVNQVARVVSGYGAGSSSSTTAATPTTTTGSITTTTTTTATVTTTAVAPLYGQCGGIGWTGPTACATGVCTAYSPYYAQCLLIV	2018.0	Clear zone;MS;Weight loss;SEM	Poly [(R)-3-hydroxybutyric acid] (PHB, Mn: unknown)	Sigma Aldrich	Yes	No	Soil	Hot spring	Taiwan	No		
Aspergillus fumigatus	746128	PLA	Jung, H. W., Yang, M. K., & Su, R. C. (2018). Purification, characterization, and gene cloning of an Aspergillus fumigatus polyhydroxybutyrate depolymerase used for degradation of polyhydroxybutyrate, polyethylene succinate, and polybutylene succinate. Polymer degradation and stability, 154, 186-194.	Esterase	00100	00100 | Esterase | Aspergillus fumigatus | PBS PCL PES PHB PLA PHA	Yes		MRGVWRYMPVYYYKCMLIPLLTFTKISIISKPQESRISLIICRTMPTVATFLGLAISGAAMASGAALGAYNVDPNSISVSGLSSGGFMSAQLGVAYSDTFKVGFGVFAGGPYDCARGQSYTTCMYNQNPSITTPVANMKSWSGNKINPVSNLQSRKIYMWTGTADTTVGPNVMSQLKTQLANFASAANVSYITTSGAAHTFPTDFDAAGDNSCSSSVSPYISNCQCDGAGAVLQWMYGPLNARNPGTLSGSIVSFSQTGEYGASGMDTTGYLYVPRACQPGSSTVCKLHVALHGCKQSYSMIGSKFVSNTGYNMWADTNDIIILYPQAVADNTMHTIWTGMPLPNPNGCWDWVGWYGANADQVGGVQMAAIVNQVARVVSGYGAGSSSSTTAATPTTTTGSITTTTTTTATVTTTAVAPLYGQCGGIGWTGPTACATGVCTAYSPYYAQCLLIV	2018.0	Clear zone;MS;Weight loss;SEM	polylactic acid (PLA polymer 2002 D, Mn: approximately 200,000 Da)	NatureWorks LLC		No	Soil	Hot spring	Taiwan	No		
Aspergillus fumigatus	746128	PHA	Jung, H. W., Yang, M. K., & Su, R. C. (2018). Purification, characterization, and gene cloning of an Aspergillus fumigatus polyhydroxybutyrate depolymerase used for degradation of polyhydroxybutyrate, polyethylene succinate, and polybutylene succinate. Polymer degradation and stability, 154, 186-194.	Esterase	00100	00100 | Esterase | Aspergillus fumigatus | PBS PCL PES PHB PLA PHA	Yes		MRGVWRYMPVYYYKCMLIPLLTFTKISIISKPQESRISLIICRTMPTVATFLGLAISGAAMASGAALGAYNVDPNSISVSGLSSGGFMSAQLGVAYSDTFKVGFGVFAGGPYDCARGQSYTTCMYNQNPSITTPVANMKSWSGNKINPVSNLQSRKIYMWTGTADTTVGPNVMSQLKTQLANFASAANVSYITTSGAAHTFPTDFDAAGDNSCSSSVSPYISNCQCDGAGAVLQWMYGPLNARNPGTLSGSIVSFSQTGEYGASGMDTTGYLYVPRACQPGSSTVCKLHVALHGCKQSYSMIGSKFVSNTGYNMWADTNDIIILYPQAVADNTMHTIWTGMPLPNPNGCWDWVGWYGANADQVGGVQMAAIVNQVARVVSGYGAGSSSSTTAATPTTTTGSITTTTTTTATVTTTAVAPLYGQCGGIGWTGPTACATGVCTAYSPYYAQCLLIV	2018.0	Clear zone;MS;Weight loss;SEM	polylactic acid (PLA polymer 2002 D, Mn: approximately 200,000 Da)	NatureWorks LLC		No	Soil	Hot spring	Taiwan	No		
Azotobacter vinelandii	354	PHB	Adaya, L., Millán, M., Peña, C., Jendrossek, D., Espín, G., Tinoco-Valencia, R., ... & Segura, D. (2018). Inactivation of an intracellular poly-3-hydroxybutyrate depolymerase of Azotobacter vinelandii allows to obtain a polymer of uniform high molecular mass. Applied microbiology and biotechnology, 102(6), 2693-2707.	PHB depolymerase	00101	00101 | PHB depolymerase | Azotobacter vinelandii | PHB PHA	Yes	WP_012699077.1	MSQETFFAQQEDCFSSFHNYVQHIGKLQKLQSDNLQDGIRRRQEKSLQKLTACATRQIGPGDWLDYLSDFNQRTLLFWDTLRRRADGTLEHRRAGYPALLKFNYELLLDGRDLPAPVNYSLLHILPGPSQTTDPSLPPVIVIDPRGGHGAGIGGFKEDSEIGESLRAGHPTYFISFSHSSEPGQTLSDIALAEARFIELVSERHAHAGKPVLIGNCQAGWALMGLAALRPELPGLLIVVGAPLSYWAGVNGRNPMRYAGGLLGGAWMTRLGSDLGNGRFDGTWLVNNFENLDPAHALWGKYYDLFSSVDSEAQRFLDFERWWGSPNLFNSEEIETIVDELFIGNRLTGGQNTLTDLRKIEAPVVVFCSYGDNITPPQQALNWIADLYPSDLALHSSGRTIIYLKHASAGHLGIFVSGQVARREHRQLIGAIDAIKALPPGLFELIIDEVPHPDGGAQSYQVHFESRRIADILAEDDGHDDEREFELVDRVSAISSTFYDWTVRPWLSRAINEPVAEQLREHHPFHLQRQLWSSLNPATWWLSGTAELARRRRNPVRPDNPLLAWQEFFSDSVENTLDTWRDLRDASQELAFHTLYGWFSTLAGGQRTSAAEKFASERERTLLERLYAALPQGGAREAAIRILLLLARASGRLDKAMLEGIVKDYRRRAYADPHIPDVATLREITRQQNLLVFAYPEESLQTLPELLPDTSVRQRILAEVLNIEPGWQRSDGPLGALWRQLFEVLELPTAEFALLRLESPATAEQPAEVDAAATPESTPPTAEPKIRPAAETAAVPAKRQEVLIEPVPTAVPEPTETAAAPKAAAPEPIAAPAEPAGQAPAETSPAEAAPKPHIRVRANTVISEPLETLPSAEAAPADSGKPPAKAAATKRTTAQRTVKPRRPRKPGGTQPSDNT	2018.0	HPLC	or PHB production, A. vinelandii strains were grown on peptone-yeast (PY) medium supplemented with 2% sucrose as carbon source (PYS; in g l−1 , sucrose, 20; yeast extract, 3.0 and peptone, 5.0) (Peña et al. 2014). 		Yes	No				Yes		
Azotobacter vinelandii	354	PHA	Adaya, L., Millán, M., Peña, C., Jendrossek, D., Espín, G., Tinoco-Valencia, R., ... & Segura, D. (2018). Inactivation of an intracellular poly-3-hydroxybutyrate depolymerase of Azotobacter vinelandii allows to obtain a polymer of uniform high molecular mass. Applied microbiology and biotechnology, 102(6), 2693-2707.	PHB depolymerase	00101	00101 | PHB depolymerase | Azotobacter vinelandii | PHB PHA	Yes	WP_012699077.1	MSQETFFAQQEDCFSSFHNYVQHIGKLQKLQSDNLQDGIRRRQEKSLQKLTACATRQIGPGDWLDYLSDFNQRTLLFWDTLRRRADGTLEHRRAGYPALLKFNYELLLDGRDLPAPVNYSLLHILPGPSQTTDPSLPPVIVIDPRGGHGAGIGGFKEDSEIGESLRAGHPTYFISFSHSSEPGQTLSDIALAEARFIELVSERHAHAGKPVLIGNCQAGWALMGLAALRPELPGLLIVVGAPLSYWAGVNGRNPMRYAGGLLGGAWMTRLGSDLGNGRFDGTWLVNNFENLDPAHALWGKYYDLFSSVDSEAQRFLDFERWWGSPNLFNSEEIETIVDELFIGNRLTGGQNTLTDLRKIEAPVVVFCSYGDNITPPQQALNWIADLYPSDLALHSSGRTIIYLKHASAGHLGIFVSGQVARREHRQLIGAIDAIKALPPGLFELIIDEVPHPDGGAQSYQVHFESRRIADILAEDDGHDDEREFELVDRVSAISSTFYDWTVRPWLSRAINEPVAEQLREHHPFHLQRQLWSSLNPATWWLSGTAELARRRRNPVRPDNPLLAWQEFFSDSVENTLDTWRDLRDASQELAFHTLYGWFSTLAGGQRTSAAEKFASERERTLLERLYAALPQGGAREAAIRILLLLARASGRLDKAMLEGIVKDYRRRAYADPHIPDVATLREITRQQNLLVFAYPEESLQTLPELLPDTSVRQRILAEVLNIEPGWQRSDGPLGALWRQLFEVLELPTAEFALLRLESPATAEQPAEVDAAATPESTPPTAEPKIRPAAETAAVPAKRQEVLIEPVPTAVPEPTETAAAPKAAAPEPIAAPAEPAGQAPAETSPAEAAPKPHIRVRANTVISEPLETLPSAEAAPADSGKPPAKAAATKRTTAQRTVKPRRPRKPGGTQPSDNT	2018.0	HPLC	or PHB production, A. vinelandii strains were grown on peptone-yeast (PY) medium supplemented with 2% sucrose as carbon source (PYS; in g l−1 , sucrose, 20; yeast extract, 3.0 and peptone, 5.0) (Peña et al. 2014). 		Yes	No				Yes		
Streptomyces sp.	1931	PCL	Almeida, E. L., Carrillo Rincon, A. F., Jackson, S. A., & Dobson, A. D. (2019). In silico screening and heterologous expression of a Polyethylene Terephthalate hydrolase (PETase)-like enzyme (SM14est) with Polycaprolactone (PCL)-degrading activity, from the marine sponge-derived strain Streptomyces sp. SM14. Frontiers in microbiology, 10, 2187.	Hydrolase	00102	00102 | Hydrolase | Streptomyces sp. | PCL	Yes	DAC80635.1	MFQRVWALTAALMLMLSLGATSSHAAQNPHERGPDPSNSYIEQARGSYSVSQRSISRLGSDGFRDGTMYYPTSTADGRFGVVAISPGYTASESTIAWLGPRLASFGFVVVTINTDSRYDQPRQRATQLHAALDHAIGDSVVGPRIDTSRQAVMGHSMGGGGALQAAEERDEIRAAVPLTPWNLKKGWSGVDAATLVIGAENDAIAPVRSHSIPFYESLTNAERRAYLELRREGHFAPNSSNTLIAKYSVSWLKRYVDNDLRYDQFIDPGPRTGITTGVSDYRLG	2019.0	Clear zone	PCL with an average molecular weight of 80,000 was used (Sigma-Aldrich®). 	Sigma Aldrich	Yes	No	Sponge	Animal associated	Ireland	No		
Pseudozyma antarctica	84753	PBS	Sameshima-Yamashita, Y., Watanabe, T., Tanaka, T., Tsuboi, S., Yarimizu, T., Morita, T., ... & Kitamoto, H. (2019). Construction of a Pseudozyma antarctica strain without foreign DNA sequences (self-cloning strain) for high yield production of a biodegradable plastic-degrading enzyme. Bioscience, biotechnology, and biochemistry, 83(8), 1547-1556.	Esterase	00103	00103 | Esterase | Pseudozyma antarctica | PBS PBSA PCL	Yes	BBB03504.1	MQFKSTFAALVLAAAGLVQAAPLQERAGCSSYVIINTRGTSEPQGPSVGFRTMNTRIRSAVSGGSEYDTVYPAGIDQNSAQGTANIVAQVKAGLARNPNTCFLLEGYSQGAAATCNALPQLTGAAFDAVKGVILIGNPEHKPNLACNVDGNGGKTTFSARGISAAFTQGVPSNWVSKTLDICIYGDGVCDVSSGFGITPQHLTYGYNTNVQTMGANFGIKALQG	2019.0	Clear zone;Spectrophotometry	Bionolle EM-301	Showa Denko		No	Seeds	Plant associated	Japan	No		
Pseudozyma antarctica	84753	PBSA	Sameshima-Yamashita, Y., Watanabe, T., Tanaka, T., Tsuboi, S., Yarimizu, T., Morita, T., ... & Kitamoto, H. (2019). Construction of a Pseudozyma antarctica strain without foreign DNA sequences (self-cloning strain) for high yield production of a biodegradable plastic-degrading enzyme. Bioscience, biotechnology, and biochemistry, 83(8), 1547-1556.	Esterase	00103	00103 | Esterase | Pseudozyma antarctica | PBS PBSA PCL	Yes	BBB03504.1	MQFKSTFAALVLAAAGLVQAAPLQERAGCSSYVIINTRGTSEPQGPSVGFRTMNTRIRSAVSGGSEYDTVYPAGIDQNSAQGTANIVAQVKAGLARNPNTCFLLEGYSQGAAATCNALPQLTGAAFDAVKGVILIGNPEHKPNLACNVDGNGGKTTFSARGISAAFTQGVPSNWVSKTLDICIYGDGVCDVSSGFGITPQHLTYGYNTNVQTMGANFGIKALQG	2019.0	Clear zone;Spectrophotometry	Bionolle EM-301	Showa Denko		No	Seeds	Plant associated	Japan	No		
Pseudozyma antarctica	84753	PCL	Sameshima-Yamashita, Y., Watanabe, T., Tanaka, T., Tsuboi, S., Yarimizu, T., Morita, T., ... & Kitamoto, H. (2019). Construction of a Pseudozyma antarctica strain without foreign DNA sequences (self-cloning strain) for high yield production of a biodegradable plastic-degrading enzyme. Bioscience, biotechnology, and biochemistry, 83(8), 1547-1556.	Esterase	00103	00103 | Esterase | Pseudozyma antarctica | PBS PBSA PCL	Yes	BBB03504.1	MQFKSTFAALVLAAAGLVQAAPLQERAGCSSYVIINTRGTSEPQGPSVGFRTMNTRIRSAVSGGSEYDTVYPAGIDQNSAQGTANIVAQVKAGLARNPNTCFLLEGYSQGAAATCNALPQLTGAAFDAVKGVILIGNPEHKPNLACNVDGNGGKTTFSARGISAAFTQGVPSNWVSKTLDICIYGDGVCDVSSGFGITPQHLTYGYNTNVQTMGANFGIKALQG	2019.0	Clear zone;Spectrophotometry	Bionolle EM-301	Showa Denko		No	Seeds	Plant associated	Japan	No		
Paenibacillus sp.	58172	LDPE	Bardají, D. K. R., Furlan, J. P. R., & Stehling, E. G. (2019). Isolation of a polyethylene degrading Paenibacillus sp. from a landfill in Brazil. Archives of microbiology, 201(5), 699-704.	Alkane monooxygenase	00104	00104 | Alkane monooxygenase | Paenibacillus sp. | LDPE	Yes	AYO90679.1	YGHFYTEHNRGHHVRVATPEDPASSRLGESFWAFLPRSVWFSAVSAWNLERERLRKLGLPALHWKNAVLGAWMYSVVLWGAMIAWLGAAVIPFLIIQGIYGFSLLEVVNYVEHYGLKRQKLPNGRY	2019.0	Weight loss;FTIR;SEM	Polythene bags were collected from supermarkets	Local market	No	No	Soil	Landfill	Brazil	No		
Pseudomonas aestusnigri	857252	PET	Bollinger, A., Thies, S., Knieps-Grünhagen, E., Gertzen, C., Kobus, S., Höppner, A., ... & Jaeger, K. E. (2020). A Novel Polyester Hydrolase From the Marine Bacterium Pseudomonas aestusnigri–Structural and Functional Insights. Frontiers in Microbiology, 11, 114.	Polyester hydrolase	00105	00105 | Polyester hydrolase | Pseudomonas aestusnigri | PET PU	Yes	WP_088276085.1	MPFNKKSVLALCGAGALLFSMSALANNPAPTDPGDSGGGSAYQRGPDPSVSFLEADRGQYSVRSSRVSSLVSGFGGGTIYYPTGTTGTMGAVVVIPGFVSAESSIDWWGPKLASYGFVVMTIDTNTGFDQPPSRARQINNALDYLVSQNSRSSSPVRGMIDTNRLGVIGWSMGGGGTLRVASEGRIKAAIPLAPWDTTSYYASRSQAPTLIFACESDVIAPVLQHASPFYNSLPSSIDKAFVEINGGSHYCGNGGSIYNDVLSRFGVSWMKLHLDEDSRYKQFLCGPNHTSDSQISDYRGNCPY	2020.0	UPLC	Amorphous PET film (0.25 mm thickness, Goodfellow Cambridge, Ltd.)	Goodfellow Cambridge		No				Yes		
Pseudomonas aestusnigri	857252	PU	Bollinger, A., Thies, S., Knieps-Grünhagen, E., Gertzen, C., Kobus, S., Höppner, A., ... & Jaeger, K. E. (2020). A Novel Polyester Hydrolase From the Marine Bacterium Pseudomonas aestusnigri–Structural and Functional Insights. Frontiers in Microbiology, 11, 114.	Polyester hydrolase	00105	00105 | Polyester hydrolase | Pseudomonas aestusnigri | PET PU	Yes	WP_088276085.1	MPFNKKSVLALCGAGALLFSMSALANNPAPTDPGDSGGGSAYQRGPDPSVSFLEADRGQYSVRSSRVSSLVSGFGGGTIYYPTGTTGTMGAVVVIPGFVSAESSIDWWGPKLASYGFVVMTIDTNTGFDQPPSRARQINNALDYLVSQNSRSSSPVRGMIDTNRLGVIGWSMGGGGTLRVASEGRIKAAIPLAPWDTTSYYASRSQAPTLIFACESDVIAPVLQHASPFYNSLPSSIDKAFVEINGGSHYCGNGGSIYNDVLSRFGVSWMKLHLDEDSRYKQFLCGPNHTSDSQISDYRGNCPY	2020.0	Clear zone	Impranil	Covestro	No	No				No		
Thermobifida fusca	2021	PET	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	Cutinase	00106	00106 | Cutinase | Thermobifida fusca | PET	Yes	CBY05530.1	ANPYERGPNPTDALLEARSGPFSVSEENVSRLSASGFGGGTIYYPRENNTYGAVAISPGYTGTEASIAWLGERIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGSLRLASQRPDLKAAIPLTPWHLNKNWSSVTVPTLIIGADLDTIAPVATHAKPFYNSLPSSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2018.0											
Thermobifida alba	53522	PET	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	Cutinase	00107	00107 | Cutinase | Thermobifida alba | PET	Yes	ADV92525.1	MANPYERGPNPTDALLEASSGPFSVSEENVSRLSASGFGGGTIYYPRENNTYGAVAISPGYTGTEASIAWLGGRIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGTPRLASQRPDLKAAIPLTPWHLNKNRSSVTVPTLIIGADLDTIAPVATHAKPFYNSLPSSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYCSTCPF	2018.0											
Thermobifida halotolerans	483545	PET	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	Serine hydrolase	00108	00108 | Serine hydrolase | Thermobifida halotolerans | PET	Yes	AFA45122.1	MANPYERGPNPTNSSIEALRGPFRVDEERVSRLQARGFGGGTIYYPTDNNTFGAVAISPGYTGTQSSISWLGERLASHGFVVMTIDTNTTLDQPDSRASQLDAALDYMVEDSSYSVRNRIDSSRLAAMGHSMGGGGTLRLAERRPDLQAAIPLTPWHTDKTWGSVRVPTLIIGAENDTIASVRSHSEPFYNSLPGSLDKAYLELDGASHFAPNLSNTTIAKYSISWLKRFVDDDTRYTQFLCPGPSTGWGSDVEEYRSTCPF	2018.0											
Polyangium brachysporum	413882	PET	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	Triacylglycerol lipase	00109	00109 | Triacylglycerol lipase | Polyangium brachysporum | PET	Yes	AKJ29164.1	MPPDCVLPRRLAAAALLASATLVPLSAAAQTNPYQRGPDPTTRDLEDSRGPFRYASTNVRSPSGYGAGTIYYPTDVSGSVGAVAVVPGYLARQSSIRWWGPRLASHGFVVITLDTRSTSDQPASRSAQQMAALRQVVALSETRSSPIYGKVDPNRLAVMGWSMGGGGTLISARDNPSLKAAVPFAPWHNTANFSGVQVPTLVIACENDTVAPISRHASSFYNSFSSSLAKAYLEINNGSHTCANTGNSNQALIGKYGVAWIKRFVDNDTRYSPFLCGAPHQADLRSSRLSEYRESCPY	2018.0											
Thermomonospora curvata	2020	PET	Danso, D., Schmeisser, C., Chow, J., Zimmermann, W., Wei, R., Leggewie, C., ... & Streit, W. R. (2018). New insights into the function and global distribution of polyethylene terephthalate (PET)-degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl. Environ. Microbiol., 84(8), e02773-17.	Triacylglycerol lipase	00110	00110 | Triacylglycerol lipase | Thermomonospora curvata | PET	Yes	ACY96861.1	MSLRKSFGLLSATAALVAGLVAAPPAQAAANPYQRGPDPTESLLRAARGPFAVSEQSVSRLSVSGFGGGRIYYPTTTSQGTFGAIAISPGFTASWSSLAWLGPRLASHGFVVIGIETNTRLDQPDSRGRQLLAALDYLTQRSSVRNRVDASRLAVAGHSMGGGGTLEAAKSRTSLKAAIPIAPWNLDKTWPEVRTPTLIIGGELDSIAPVATHSIPFYNSLTNAREKAYLELNNASHFFPQFSNDTMAKFMISWMKRFIDDDTRYDQFLCPPPRAIGDISDYRDTCPHT	2018.0											
Acinetobacter johnsonii	40214	PS	Kim, H. W., Jo, J. H., Kim, Y. B., Le, T. K., Cho, C. W., Yun, C. H., ... & Yeom, S. J. (2021). Biodegradation of Polystyrene by Bacteria from the Soil in Common Environments. Journal of Hazardous Materials, 126239.	Alkane-1 monooxygenase	00111	00111 | Alkane-1 monooxygenase | Acinetobacter johnsonii | PS	Yes	AZN65426.1	MTLDLFSPEPQANLLPFDGQVQDLGLILTAKQSAKYLDYFLAHLAWQPDEVVLYGKRYVTERKVVWYGDAEYEYHYSGSAKQARLWNPALFRLKQHIEQLVGHPFNSCLANLYENGSQAVGWHSDDEPSLRSPQQENVVIASLSFGATRKFCFKHKFKQEKVGLMLHSGQLIVMRGQTQRYWKHALMKSSKITEPRLNLTFRYFYPAPQS	2021.0	Weight loss;GC-MS;FT-IR;SEM	Low molecular weight PS powder			No	Soil	Soil	South Korea	No		
Moniliophthora roreri	221103	PES	Vázquez-Alcántara, L., Oliart-Ros, R. M., García-Bórquez, A., & Peña-Montes, C. (2021). Expression of a Cutinase of Moniliophthora roreri with Polyester and PET-plastic residues degradation activity. Microbiology Spectrum, 9(3), e00976-21.	Cutinase	00113	00113 | Cutinase | Moniliophthora roreri | PES PCL PET	Yes	KTB31184.1	MVRVFGLTLLALLVPALAAPVPEDLEARQSGCADVMVVYARGTDQDSPIGDPASVGVLFRDNIKSLLGSRTFSFQGVNYAANVIGFLQGGDPAGSRQMTTDLTNVANSCPNAKIVSAGYSQGGQLVHNSAAQLTAAVRNRINAVVIFGDPKSDQAVTGIPSSNVKIICHDGDNICEGGFIVTSQHTNYQQDAPAAAQFVLSKV	2021.0	Weight loss;Titration	PES		Yes	No	Cacao pods	Plant associated	Mexico	Yes		
Moniliophthora roreri	221103	PCL	Vázquez-Alcántara, L., Oliart-Ros, R. M., García-Bórquez, A., & Peña-Montes, C. (2021). Expression of a Cutinase of Moniliophthora roreri with Polyester and PET-plastic residues degradation activity. Microbiology Spectrum, 9(3), e00976-21.	Cutinase	00113	00113 | Cutinase | Moniliophthora roreri | PES PCL PET	Yes	KTB31184.1	MVRVFGLTLLALLVPALAAPVPEDLEARQSGCADVMVVYARGTDQDSPIGDPASVGVLFRDNIKSLLGSRTFSFQGVNYAANVIGFLQGGDPAGSRQMTTDLTNVANSCPNAKIVSAGYSQGGQLVHNSAAQLTAAVRNRINAVVIFGDPKSDQAVTGIPSSNVKIICHDGDNICEGGFIVTSQHTNYQQDAPAAAQFVLSKV	2021.0	Weight loss;Titration	PCL		Yes	No	Cacao pods	Plant associated	Mexico	Yes		
Moniliophthora roreri	221103	PET	Vázquez-Alcántara, L., Oliart-Ros, R. M., García-Bórquez, A., & Peña-Montes, C. (2021). Expression of a Cutinase of Moniliophthora roreri with Polyester and PET-plastic residues degradation activity. Microbiology Spectrum, 9(3), e00976-21.	Cutinase	00113	00113 | Cutinase | Moniliophthora roreri | PES PCL PET	Yes	KTB31184.1	MVRVFGLTLLALLVPALAAPVPEDLEARQSGCADVMVVYARGTDQDSPIGDPASVGVLFRDNIKSLLGSRTFSFQGVNYAANVIGFLQGGDPAGSRQMTTDLTNVANSCPNAKIVSAGYSQGGQLVHNSAAQLTAAVRNRINAVVIFGDPKSDQAVTGIPSSNVKIICHDGDNICEGGFIVTSQHTNYQQDAPAAAQFVLSKV	2021.0	Weight loss;Titration	Commercial water bottles		No	No	Cacao pods	Plant associated	Mexico	Yes		
Streptomyces sp.	1931	NR	Yikmis, M., & Steinbüchel, A. (2012). Importance of the latex‐clearing protein (Lcp) for poly (cis‐1, 4‐isoprene) rubber cleavage in Streptomyces sp. K30. Microbiologyopen, 1(1), 13-24.	Latex-clearing protein	00114	00114 | Latex-clearing-protein | Streptomyces sp. | NR	Yes	Q3L8N0	MDGFSRRRMLMTGGALGAVGALGAATRALARPLWTWSPSASVAGTGVGVDPEYVWDEEADPVLAAVIDRGEVPAVNALLKQWTRNDQALPGGLPGDLREFMEHARRMPSWADKAALDRGAQFSKTKGIYVGALYGLGSGLMSTAIPRESRAVYYSKGGADMKDRIAKTARLGYDIGDLDAYLPHGSMIVTAVKTRMVHAAVRHLLPQSPAWSQTSGGQKIPISQADIMVTWHSLATFVMRKMKQWGVRVNTADAEAYLHVWQVSAHMLGVSDEYIPATWDAANAQSKQVLDPILAHTPEGEALTEVLLGIVAELDAGLTRPLIGAFSRYTLGGEVGDMIGLAKQPVLERLIATAWPLLVAFREGLIPLPAVPAVLWTLEEALRKFVLLFLSEGRRIAIDIPDVNRPS	2012.0	CO2;Clear zone	Synthetic poly(cis-1,4-isoprene) with an average molecular mass of 800 kDa		Yes	No	Soil	Soil	Germany	No		
Steroidobacter cummioxidans	1803913	NR	Tsuchii, A., & Takeda, K. (1990). Rubber-degrading enzyme from a bacterial culture. Applied and Environmental Microbiology, 56(1), 269-274.	Rubber-oxygenase	00115	00115 | Rubber-oxygenase | Steroidobacter cummioxidans | NR	Yes	Q7X0P3	MIARRLGLRRAWAALALTPILFIGQGAGGQALPLLDQASIRSPLMVGCNGKPDSTPLPVDPRSLVKQGVNSNPNAALQFNAYFVDLHNPPPPFVNRLPPRPTTCGQFRASATRGRVNLEERQFFQPMALATSYHFIFLQWGYLIRPPDFEEQVSKRYGLYPAPFRNPYPLPGEDPNQTNGGSGQLPLGLIQGKDDNGRWTGLIGASCSACHDSRLGTASEASFKWGLPNSANDAGLLASDMFRTTPITALGNLLPLPWSTGRGSSDAIGLISLLPALFDMETLTLAPSLLEYVADAPHAGMTKAPAWWARAFKTRQFWDGSLSSDNVHSEMAFGVANIFRDANARRGLEDEFEDINNFLISLSPATYPKTINTALAEQGAVIYHERDLWASGANGAIPKPAGNGSCASCHGVYSPRHAADPNYLPDPRLKGVAAVVTPIETIRTDPRRMRLMADERQRRAWNSGWWAYNNLSPSWTGYPSDNIVASELRRVPRAIYNNGGPIYSPLGPNIWEEPTGYIAPPLYGAWATAPYFHNGSVPNLWGVLKPSDRPKLWKRPYTAAGIGGKNAGYDYSFASYDWQKLGWKYTAVACNNSIFTSPFLPCTHNMATIDILYSMWDNVAAQYLNLAYQSPPPITDQQIKSRMVYNSYLYGNDNGGHDFTQSLTDSERWALIEYIKTL	1990.0	GPC;NMR;GC	Acommerciallatexofnaturalrubber(Soctex-c;60%rubber,dryweight)wasobtainedfromSocfinCo.Ltd.inMalaysia.Syntheticisoprenerubberlatex(MaxpreneIR-900;contentofcis-1,4structurewas78%,trans-1,4contentwas13%,and3,4-contentwas9%by1H-nuclearmagneticresonance[NMR])wasfromSeitetsuChemicalIndustryCo.Ltd.	SocfinCo.Ltd.inMalaysia	Yes	No				No		
Steroidobacter cummioxidans	1803913	NR	Tsuchii, A., & Takeda, K. (1990). Rubber-degrading enzyme from a bacterial culture. Applied and Environmental Microbiology, 56(1), 269-274.	Rubber-oxygenase	00116	00116 | Rubber-oxygenase | Steroidobacter cummioxidans | NR	Yes	A0A1S6Q8F9	MSSKQHRARAKVQRASIFVVLGLVAGHSSSTDAATDLIKSSRGGSQLWDYCEGKGDATLLPADPRSLVQPGIGTGRAVAFNAFWKDCHTDPAAVQEAGHPKTCGELRQRFYRGDGLLDTGSRTVAALFTGDNPTTIESVFGAATLTAAQYNSLWVSWGGFLLRPDNFDELVAERYGSVFGAGRNPYPKPLEDPNRTNGGTGRLPEMFTQLRNPDGSWSGRIGITCHACHSGAANGAHTPGSGSSLQDLHLLLRDAVPLGYLPSLASLANLTRTRGTNNASDINLAFLFPDQGLISISTALGVLASGSTASMDTPAWWNMGHRPVKFVDGVFPMDAPRVDMVFYTPAFGLFGSLGGPLSEAGQNWMRAHGPDANTWIESLKAPAYPGTIDTALAEQGAVLFHTLNLWASNRNNPVPKPSAGNGSCASCHGAYAPRYVNDPAFLASPALEGMAAYITPQRIIQTDPVRQQTNNEAVQIAGASNFFGYPSTAGTANDCGPQNRADLRGNRELGYLAPPLYGIWATAPYMHNGSVPNIWEVLKPSDRTPLWKRKSKTPRWDQTGRAIMGYDTSMQAYDTAKLGWKYDAIQCRRPSLLDPLPSPYLRCDPNDDLLLSWYDALLTNLYGNVILAWNVLFPPTITNTDIENRKIYNSYMFGQGNGGHTFNAVLTDNERKAIIEYLKTL	1990.0	GPC;NMR;GC	Acommerciallatexofnaturalrubber(Soctex-c;60%rubber,dryweight)wasobtainedfromSocfinCo.Ltd.inMalaysia.Syntheticisoprenerubberlatex(MaxpreneIR-900;contentofcis-1,4structurewas78%,trans-1,4contentwas13%,and3,4-contentwas9%by1H-nuclearmagneticresonance[NMR])wasfromSeitetsuChemicalIndustryCo.Ltd.	SocfinCo.Ltd.inMalaysia	Yes	No				No		
Rhizobacter gummiphilus	946333	NR	Kasai, D., Imai, S., Asano, S., Tabata, M., Iijima, S., Kamimura, N., ... & Fukuda, M. (2017). Identification of natural rubber degradation gene in Rhizobacter gummiphilus NS21. Bioscience, Biotechnology, and Biochemistry, 81(3), 614-620.	Rubber-oxygenase	00117	00117 | Rubber-oxygenase | Rhizobacter gummiphilus | NR	Yes	BAS44780.1	MSSQHPWAPARRLSMVLLLGLSAGLAASAQAATDLIQSSRGGSPLWDYCEGKPAATVLPADPRSLVQPGISTGKAVAFNAYWKDCHTDPAAVQEAGHPKTCGDLRDRFYRGGGLLETGSPTVAALFTGDNTRTLESVFGASTLTATQYNALWTTWGGFVVRPDNFDQLVAERYGSVFGTGRNPYPKPFEDPNRTNGGTGRLPEMFTQLRNPDGTWSGRIGVTCHACHSGAANGVPAPGGGSSLQDLHLFLRDALPLGYLASLASIANLTRTRGTNNASDINLAFVFPDQGLLPLDTFLGVLASGSTASMDTPAWWNMGHRPVKFVDGVFPMDAPRVDMVFYTPLLGLFGSVGGPLSEAGQTWMRAHGPDANTWIESLKSPPYPGTIDTALAEQGAVLFHTLNLWATSRNNPVPKPNEGNGSCASCHGAYAPRYVNDPAFLATPALEGMASYITPQRIIQTDIVRQKTNNEAVQVAGASNFFGYPTTKGTVNDCGPQNRADLRGNRELGYLAPPLYGVWATAPYLHNGSVPNVWEVLKPSDRKPLWRRVSNPPRWDQVGRTIMGYDTRMSAYDTQKMGWKYDTLQCRKPTLFDPIPSPYWRCDPKDEQLQAWYNELVRGLYSNVALTWNVLFPPTITNSDIEDRKIYNTYMFGQGNGGHTFNSVLTDAERKALIEYLKTL	2017.0	Clear zone;GPC				No	Soil	Soil		No		
Stutzerimonas stutzeri	316	PEG	Obradors, N., & Aguilar, J. (1991). Efficient biodegradation of high-molecular-weight polyethylene glycols by pure cultures of Pseudomonas stutzeri. Appl. Environ. Microbiol., 57(8), 2383-2388.	 PEG dehydrogenase			No			1991.0	Spectrophotometry;Chromatography;SEM	 PEGs except PEG 4000 were also from Merck. PEG 4000, Nitro Blue Tetrazolium, glyoxylic acid, and glycolic acid were from Sigma	Merck	Yes	No	Water	River/Lake	Spain	No		
Purpureocillium lilacinum	33203	PHB	Oda, Y., Asari, H., Urakami, T., & Tonomura, K. (1995). Microbial degradation of poly (3-hydroxybutyrate) and polycaprolactone by filamentous fungi. Journal of fermentation and bioengineering, 80(3), 265-269.	 PHB and PCL depolymerase			No			1995.0	HPLC	PHB of natural origin with molecular weight of 469,001	Sigma Aldrich	Yes	No	Soil	Soil		No		
Purpureocillium lilacinum	33203	PCL	Oda, Y., Asari, H., Urakami, T., & Tonomura, K. (1995). Microbial degradation of poly (3-hydroxybutyrate) and polycaprolactone by filamentous fungi. Journal of fermentation and bioengineering, 80(3), 265-269.	 PHB and PCL depolymerase			No			2002.0	HPLC	PCL was a commercial product (Placcel HIPTM) was in powder form and had average molecular weight of 10,001	Daicel Chemical Industries		No	Soil	Soil		No		
Pseudomonas vesicularis	41276	PVA	Kawagoshi, Y., & Fujita, M. (1998). Purification and properties of the polyvinyl alcohol-degrading enzyme 2, 4-pentanedione hydrolase obtained from Pseudomonas vesicularis var. povalolyticus PH. World Journal of Microbiology and Biotechnology, 14(1), 95-100.	2,4-Pentanedione hydrolase			No			1998.0	GPC	PVA (PVA117; Kuraray, Japan)	Kuraray		No				Yes		
Aspergillus sp.	5065	PET	Nimchua, T., Eveleigh, D. E., & Punnapayak, H. (2008). Screening of tropical fungi producing polyethylene terephthalate-hydrolyzing enzyme for fabric modification. Journal of industrial microbiology & biotechnology, 35(8), 843.	Cutinase			No			2008.0	Clear zone	PET fabrics (weave, warp, and weft: 167 dtex,192 g/m2) 	Asia Fiber Public Company	No	No	Soil	Soil	Thailand	No		
Bacillus sp.	1409	PCL	Adıgüzel, A. O., & Tunçer, M. (2017). Purification and characterization of cutinase from Bacillus sp. KY0701 isolated from plastic wastes. Preparative Biochemistry and Biotechnology, 47(9), 925-933.	Cutinase			No			2017.0	Weight loss;Clear zone	Plastic Waste		No	No	Plastic debris	Soil	Turkey	No		
Fusarium moniliforme	117187	PCL	Murphy, C. A., Cameron, J. A., Huang, S. J., & Vinopal, R. T. (1996). Fusarium polycaprolactone depolymerase is cutinase. Appl. Environ. Microbiol., 62(2), 456-460.	Cutinase			No			1996.0	Clear zone;Spectrophotometry	PCL (Cellomer Associates, Inc., Webster, N.Y.) with a molecular weight of approximately 10,000 was used.	Cellomer Associates	Yes	No	Culture collection	Culture collection		No		
Fusarium solani	169388	PCL	Murphy, C. A., Cameron, J. A., Huang, S. J., & Vinopal, R. T. (1996). Fusarium polycaprolactone depolymerase is cutinase. Appl. Environ. Microbiol., 62(2), 456-460.	Cutinase			No			1996.0	Clear zone;Spectrophotometry	PCL (Cellomer Associates, Inc., Webster, N.Y.) with a molecular weight of approximately 10,000 was used.	Cellomer Associates	Yes	No	Culture collection	Culture collection		No		
Fusarium solani	169388	PCL	Nimchua, T., Eveleigh, D. E., & Punnapayak, H. (2008). Screening of tropical fungi producing polyethylene terephthalate-hydrolyzing enzyme for fabric modification. Journal of industrial microbiology & biotechnology, 35(8), 843.	Cutinase			No			2008.0	Clear zone	PCL (mol. wt. 14,000)	Sigma Aldrich	Yes	No	Leaf	Soil	Thailand	No		
Fusarium solani	169388	PET	Nimchua, T., Eveleigh, D. E., & Punnapayak, H. (2008). Screening of tropical fungi producing polyethylene terephthalate-hydrolyzing enzyme for fabric modification. Journal of industrial microbiology & biotechnology, 35(8), 843.	Cutinase			No			2008.0	Clear zone	PET fabrics (weave, warp, and weft: 167 dtex,192 g/m2) 	Asia Fiber Public Company	No	No	Leaf	Soil	Thailand	No		
Fusarium solani	169388	PCL	Nimchua, T., Punnapayak, H., & Zimmermann, W. (2007). Comparison of the hydrolysis of polyethylene terephthalate fibers by a hydrolase from Fusarium oxysporum LCH I and Fusarium solani f. sp. pisi. Biotechnology Journal: Healthcare Nutrition Technology, 2(3), 361-364.	Cutinase			No			2007.0	Clear zone	Polycaprolactone (500 mg/L, mol. wt. 10 000)			No	Culture collection	Culture collection		No		
Fusarium solani	169388	PBAT	Zumstein, M. T., Rechsteiner, D., Roduner, N., Perz, V., Ribitsch, D., Guebitz, G. M., ... & Sander, M. (2017). Enzymatic hydrolysis of polyester thin films at the nanoscale: effects of polyester structure and enzyme active-site accessibility. Environmental science & technology, 51(13), 7476-7485.	Cutinase			No			2017.0	NMR;Spectrophotometry;QCM-D	All polyesters were provided by BASF SE and synthesized as previously described.37,38	BASF	Yes	No				Yes		
Humicola insolens	34413	PEF	Weinberger, S., Haernvall, K., Scaini, D., Ghazaryan, G., Zumstein, M. T., Sander, M., ... & Guebitz, G. M. (2017). Enzymatic surface hydrolysis of poly (ethylene furanoate) thin films of various crystallinities. Green Chemistry, 19(22), 5381-5384.	Cutinase			No			2017.0	QCM-D;SEM;AFM;HPLC				No				Yes		
Humicola insolens	34413	PET	Weinberger, S., Haernvall, K., Scaini, D., Ghazaryan, G., Zumstein, M. T., Sander, M., ... & Guebitz, G. M. (2017). Enzymatic surface hydrolysis of poly (ethylene furanoate) thin films of various crystallinities. Green Chemistry, 19(22), 5381-5384.	Cutinase			No			2017.0	QCM-D;SEM;AFM;HPLC				No				Yes		
Thermobifida cellulosilytica	144786	PEF	Weinberger, S., Haernvall, K., Scaini, D., Ghazaryan, G., Zumstein, M. T., Sander, M., ... & Guebitz, G. M. (2017). Enzymatic surface hydrolysis of poly (ethylene furanoate) thin films of various crystallinities. Green Chemistry, 19(22), 5381-5384.	Cutinase			No			2017.0	QCM-D;SEM;AFM;HPLC				No				Yes		
Thermobifida cellulosilytica	144786	PET	Weinberger, S., Haernvall, K., Scaini, D., Ghazaryan, G., Zumstein, M. T., Sander, M., ... & Guebitz, G. M. (2017). Enzymatic surface hydrolysis of poly (ethylene furanoate) thin films of various crystallinities. Green Chemistry, 19(22), 5381-5384.	Cutinase			No			2017.0	QCM-D;SEM;AFM;HPLC				No				Yes		
Arthrobacter sp.	1667	PC	Goel, R., Zaidi, M. G. H., Soni, R., Lata, K., & Shouche, Y. S. (2008). Implication of Arthrobacter and Enterobacter species for polycarbonate degradation. International Biodeterioration & Biodegradation, 61(2), 167-172.	Esterase			No			2008.0	FTIR;Spectrophotometry	Polybisphenol A carbonate with melt index 7, density 1.2 g/c was purchased from Aldrich Chemical Company, USA.	Sigma Aldrich		No	Soil	Plastic waste dumping site	India	No		
Aureobasidium pullulans	5580	PVC Blend	Webb, J. S., Nixon, M., Eastwood, I. M., Greenhalgh, M., Robson, G. D., & Handley, P. S. (2000). Fungal colonization and biodeterioration of plasticized polyvinyl chloride. Appl. Environ. Microbiol., 66(8), 3194-3200.	Esterase			No			2000.0	SEM;Weight loss;Clear zone	Sheets of pPVC, 0.5 mm thick, were formulated that contained the following components (parts per hundred resin): EP 6779 PVC resin, (European Vinyls Corporation Ltd., Runcorne, United Kingdom), 75; Vinnolit C65V PVC resin (Vinnolit, Cologne, Germany), 25; DOP plasticizer (Exxon Chemicals, Southampton, United Kingdom), 25; DOA plasticizer (Exxon Chemicals), 25; Lankromark LN138 calcium-zinc stabilizer, (Akcros Chemicals, Burnley, United Kingdom), 2; Lankroflex ED63 epoxidized oleate ester (Akcros Chemicals), 3; and titanium dioxide pigment (Tioxide Europe, Grimsby, United Kingdom), 10. Individual pPVC pieces were 4.2 by 7 cm and had two 6-mmdiameter holes in the corners of one of the long edges for attachment to in situ support racks.		No	No	Culture collection	Culture collection		No		
Bacillus licheniformis	1402	PLA	Arena, M., Abbate, C., Fukushima, K., & Gennari, M. (2011). Degradation of poly (lactic acid) and nanocomposites by Bacillus licheniformis. Environmental Science and Pollution Research, 18(6), 865-870.	Esterase			No			2011.0	SEM;Weight loss	Poly(lactic acid) (PLA, 4042D) (92% L, 8% D)	NatureWorks LLC		No		Compost		No		
Corynebacterium sp.	1720	PU	Kay, M. J., McCabe, R. W., & Morton, L. H. G. (1993). Chemical and physical changes occurring in polyester polyurethane during biodegradation. International biodeterioration & biodegradation, 31(3), 209-225.	Esterase			No			1993.0	Tensilometer;ATR-FTIR	Dumb-bell-shaped polyester polyurethane test pieces, produced by reacting polyethylene glycol adipate with a mixture of 2,4- and 2,6-toluene diisocyanates, were prepared.			No	Plastic debris			No		
Enterobacter sp.	42895	PC	Goel, R., Zaidi, M. G. H., Soni, R., Lata, K., & Shouche, Y. S. (2008). Implication of Arthrobacter and Enterobacter species for polycarbonate degradation. International Biodeterioration & Biodegradation, 61(2), 167-172.	Esterase			No			2008.0	FTIR;Spectrophotometry	Polybisphenol A carbonate with melt index 7, density 1.2 g/c was purchased from Aldrich Chemical Company, USA.	Sigma Aldrich		No	Soil	Plastic waste dumping site	India	No		
Leptothrix sp.	34030	PBSA	Nakajima-Kambe, T., Toyoshima, K., Saito, C., Takaguchi, H., Akutsu-Shigeno, Y., Sato, M., ... & Uchiyama, H. (2009). Rapid monomerization of poly (butylene succinate)-co-(butylene adipate) by Leptothrix sp. Journal of bioscience and bioengineering, 108(6), 513-516.	Esterase			No			2009.0	Clear zone;HPLC	The PBSA (Bionolle #3001 and #3020, mw 85,000 and 58,000)	Showa Denko		No			Japan	No		
Leptothrix sp.	34030	PCL	Nakajima-Kambe, T., Toyoshima, K., Saito, C., Takaguchi, H., Akutsu-Shigeno, Y., Sato, M., ... & Uchiyama, H. (2009). Rapid monomerization of poly (butylene succinate)-co-(butylene adipate) by Leptothrix sp. Journal of bioscience and bioengineering, 108(6), 513-516.	Esterase			No			2009.0	Clear zone;HPLC	Poly(.-caprolactone) (PCL; Mn=70,000–100,000)	Wako Pure Chemical		No			Japan	No		
Leptothrix sp.	34030	PES	Nakajima-Kambe, T., Toyoshima, K., Saito, C., Takaguchi, H., Akutsu-Shigeno, Y., Sato, M., ... & Uchiyama, H. (2009). Rapid monomerization of poly (butylene succinate)-co-(butylene adipate) by Leptothrix sp. Journal of bioscience and bioengineering, 108(6), 513-516.	Esterase			No			2009.0	Clear zone;HPLC	Poly(ethylene succinate) (PES; Mn=60,000)	Nippon Shokubai		No			Japan	No		
Pseudomonas aeruginosa	287	PU Blend	Mukherjee, K., Tribedi, P., Chowdhury, A., Ray, T., Joardar, A., Giri, S., & Sil, A. K. (2011). Isolation of a Pseudomonasaeruginosa strain from soil that can degrade polyurethane diol. Biodegradation, 22(2), 377-388.	Esterase			No			2011.0	TLC;HPLC;MS;Clear zone	PUR-diol (Sigma– Aldrich) (average mol. wt.*320) and Impranil DLN	Sigma Aldrich	No	No	Soil	Plastic waste dumping site	India	No		
Roseateles depolymerans	76731	PBSTIL	Shah, A. A., Eguchi, T., Mayumi, D., Kato, S., Shintani, N., Kamini, N. R., & Nakajima-Kambe, T. (2013). Purification and properties of novel aliphatic-aromatic co-polyesters degrading enzymes from newly isolated Roseateles depolymerans strain TB-87. Polymer degradation and stability, 98(2), 609-618.	Esterase			No			2013.0	Clear zone	Poly[(butylene succinate/terephthalate/isophthalate)-co-(lactate)] (PBSTIL) is a co-polyester of 1,4-butanediol, succinic acid, terephthalic acid, isophthalic acid and lactic acid. Poly (butylene succinate/terephthalate)(PBST: PBST46 and PBST55) are co-polyesters of 1,4-butanediol, succinic acid, and terephthalic acid. These plastics were synthesized by our group and the details are summarized in the previous report [1].			No	Freshwater	River/Lake	Japan	No		
Fusarium oxysporum	5507	PET	Nimchua, T., Punnapayak, H., & Zimmermann, W. (2007). Comparison of the hydrolysis of polyethylene terephthalate fibers by a hydrolase from Fusarium oxysporum LCH I and Fusarium solani f. sp. pisi. Biotechnology Journal: Healthcare Nutrition Technology, 2(3), 361-364.	Hydrolase			No			2007.0	Clear zone	PET yarn (small pieces of untreated pre-washed PET yarn, a kind gift of Dr. T. Böhme KG, Geretsried, Germany)			No			Thailand	No		
Rhodococcus ruber	1830	LDPE	Orr, I. G., Hadar, Y., & Sivan, A. (2004). Colonization, biofilm formation and biodegradation of polyethylene by a strain of Rhodococcus ruber. Applied microbiology and biotechnology, 65(1), 97-104.	Laccase			No			2004.0	Weight loss;SEM;FTIR	We have used a branched low-density (0.92 g cm−3) polyethylene (LDPE Ipiten 111) with an average molecular weight of 191,000, produced by Carmel Olefins (Haifa, Israel). All experiments were performed with films (0.2 mm thick) prepared from this polyethylene by Plastopil Hazorea (Kibbutz Hazorea, Israel).	Carmel Olefins		No				No		
Rhodococcus ruber	1830	PE	Sivan, A., Szanto, M., & Pavlov, V. (2006). Biofilm development of the polyethylene-degrading bacterium Rhodococcus ruber. Applied microbiology and biotechnology, 72(2), 346-352.	Laccase			No			2006.0	Weight loss;SEM	We have used a branched low-density (0.92 g cm−3) polyethylene (LDPE Ipiten 111) with an average molecular weight of 191,000, produced by Carmel Olefins (Haifa, Israel). All experiments were performed with films (0.2 mm thick) prepared from this polyethylene by Plastopil Hazorea (Kibbutz Hazorea, Israel).	Carmel Olefins		No				No		
Chaetomium sp.	1769349	PE	Sowmya, H. V., Ramalingappa, M., & Krishnappa, M. (2012). Degradation of polyethylene by Chaetomium sp. and Aspergillus flavus. Int. J. Recent Sci. Res, 3(513), e517.	Laccase and manganese peroxidase			No			2012.0	Weight loss;SEM	Pre-weighed discs of 1cm diameter prepared from polyethylene bags		No	No	Soil	Landfill	India	No		
Oscillatoria subbrevis	1136066	LDPE	Sarmah, P., & Rout, J. (2018). Efficient biodegradation of low-density polyethylene by cyanobacteria isolated from submerged polyethylene surface in domestic sewage water. Environmental Science and Pollution Research, 25(33), 33508-33520.	Laccase and manganese peroxidase			No			2018.0	FTIR;NMR;SEM;Weight loss;CHN;TGA;DSC;OP;Tensilometer	PE sheets of 20-µ thickness were dried under ambient conditions and cut into strips (1 cm × 1 cm), washed with 70% ethanol followed by distilled water.			No	Bag	Sewage/Sludge	India	No		
Phormidium lucidum	693231	LDPE	Sarmah, P., & Rout, J. (2018). Efficient biodegradation of low-density polyethylene by cyanobacteria isolated from submerged polyethylene surface in domestic sewage water. Environmental Science and Pollution Research, 25(33), 33508-33520.	Laccase and manganese peroxidase			No			2018.0	FTIR;NMR;SEM;Weight loss;CHN;TGA;DSC;OP;Tensilometer	PE sheets of 20-µ thickness were dried under ambient conditions and cut into strips (1 cm × 1 cm), washed with 70% ethanol followed by distilled water.			No	Bag	Sewage/Sludge	India	No		
Trichoderma harzianum	5544	PE	Sowmya, H. V., Krishnappa, M., & Thippeswamy, B. (2014). Degradation of polyethylene by Trichoderma harzianum—SEM, FTIR, and NMR analyses. Environmental monitoring and assessment, 186(10), 6577-6586.	Laccase and manganese peroxidase			No			2014.0	SEM;FTIR;NMR;Clear zone;Weight loss	The pre-weighed discs of autoclaved, surface-sterilized, and UV-treated polyethylene of 1 cm diameter prepared from polyethylene bags were aseptically transferred to the conical flask containing 50 ml of Mineral Salt Medium.		No	No	Soil	Plastic waste dumping site	India	No		
Rhizopus delemar	936053	PU	Walter, T., Augusta, J., Müller, R. J., Widdecke, H., & Klein, J. (1995). Enzymatic degradation of a model polyester by lipase from Rhizopus delemar. Enzyme and microbial technology, 17(3), 218-224.	Lipase			No			1995.0	Weight loss	Equimolar amounts of 1,3-propanediol and succinic acid were mixed in a flask equipped with a mechanical stirrer, and the mixture was heated slowly to 90°C under nitrogen atmosphere, while it was stirred mechanically. Then, 0.056% (wt/wt) methanesulfonitacid was added as catalyst. Immediately, the formation of water started, which was collected by the use of a microdistillation head and cooled at about 10°C. The temperature was raised to 100°C and kept there for 10 h. For an additional 3 h, the temperature was set to 130°C.		Yes					Yes		
Acidovorax delafieldii	47920	PBSA	Uchida, H., Nakajima-Kambe, T., Shigeno-Akutsu, Y., Nomura, N., Tokiwa, Y., & Nakahara, T. (2000). Properties of a bacterium which degrades solid poly (tetramethylene succinate)-co-adipate, a biodegradable plastic. FEMS Microbiology letters, 189(1), 25-29.	Lipase			No			2000.0	Weight loss	Cylindrical-shaped PBSA (Bionolle #3020) was used with a size of 2.5 mm diameter x 4 mm. The Mns of PBSA (Bionolle #3020) is 58 000.	Bayer 	No	No	Soil	Soil	Japan	No		
Bacillus pumilus	1408	PU	Nair, S., & Kumar, P. (2007). Molecular characterization of a lipase-producing Bacillus pumilus strain (NMSN-1d) utilizing colloidal water-dispersible polyurethane. World journal of microbiology and biotechnology, 23(10), 1441-1449.	Lipase			No			2007.0	Clear zone;FTIR;MS	Impranil DLN	Bayer 	No	No	Water;Soil	Plastic waste dumping site		No		
Diutina rugosa	5481	PU	Gautam, R., Bassi, A. S., & Yanful, E. K. (2007). Candida rugosa lipase-catalyzed polyurethane degradation in aqueous medium. Biotechnology letters, 29(7), 1081-1086.	Lipase			No			2007.0	Spectrophotometry;GC	Commercially-available, water-dispersed PUR suspension, named Impranil (Fig. 1) (milky white, opaque, 40% w/w solids, average particle size 0.2 lm, specific gravity at room temperature 1.0485) was obtained from Bayer, USA.	Bayer 	No	No				Yes		
Pseudomonas sp.	306	PEG	Skariyachan, S., Megha, M., Kini, M. N., Mukund, K. M., Rizvi, A., & Vasist, K. (2015). Selection and screening of microbial consortia for efficient and ecofriendly degradation of plastic garbage collected from urban and rural areas of Bangalore, India. Environmental monitoring and assessment, 187(1), 4174.	Lipase			No			2015.0	Clear zone;Weight loss	The plastic used in our study was UV-sterilized polyethylene glycol (PEG;(1.0 g/L)			No			India	No		
Rhizopus delemar	936053	PET	Nagata, M., Kiyotsukuri, T., Minami, S., Tsutsumi, N., & Sakai, W. (1997). Enzymatic degradation of poly (ethylene terephthalate) copolymers with aliphatic dicarboxylic acids and/or poly (ethylene glycol). European polymer journal, 33(10-12), 1701-1705.	Lipase			No			1997.0	GPC;Weight loss				No				Yes		
Rhizopus oryzae	64495	PBS	Zumstein, M. T., Kohler, H. P. E., McNeill, K., & Sander, M. (2016). Enzymatic hydrolysis of polyester thin films: real-time analysis of film mass changes and dissipation dynamics. Environmental science & technology, 50(1), 197-206.	Lipase			No			2016.0	QCM-D;Spectrophotometry	The polyesters included in this study were PBS (obtained as film), PBA, PET, and PLA (containing 11−13% Dlactide) (obtained as granules). These materials were kindly provided by BASF SE.	BASF	Yes	No				Yes		
Rhizopus oryzae	64495	PBSA	Zumstein, M. T., Kohler, H. P. E., McNeill, K., & Sander, M. (2016). Enzymatic hydrolysis of polyester thin films: real-time analysis of film mass changes and dissipation dynamics. Environmental science & technology, 50(1), 197-206.	Lipase			No			2016.0	QCM-D;Spectrophotometry	The polyesters included in this study were PBS (obtained as film), PBA, PET, and PLA (containing 11−13% Dlactide) (obtained as granules). These materials were kindly provided by BASF SE.	BASF	Yes	No				Yes		
Rhizopus oryzae	64495	PLA	Zumstein, M. T., Kohler, H. P. E., McNeill, K., & Sander, M. (2016). Enzymatic hydrolysis of polyester thin films: real-time analysis of film mass changes and dissipation dynamics. Environmental science & technology, 50(1), 197-206.	Lipase			No			2016.0	QCM-D;Spectrophotometry	The polyesters included in this study were PBS (obtained as film), PBA, PET, and PLA (containing 11−13% Dlactide) (obtained as granules). These materials were kindly provided by BASF SE.	BASF	Yes	No				Yes		
Rhizopus oryzae	64495	PBAT	Zumstein, M. T., Rechsteiner, D., Roduner, N., Perz, V., Ribitsch, D., Guebitz, G. M., ... & Sander, M. (2017). Enzymatic hydrolysis of polyester thin films at the nanoscale: effects of polyester structure and enzyme active-site accessibility. Environmental science & technology, 51(13), 7476-7485.	Lipase			No			2017.0	NMR;Spectrophotometry;QCM-D	All polyesters were provided by BASF SE and synthesized as previously described.37,38	BASF	Yes	No				Yes		
Pseudomonas sp.	306	PLA	Liang, T. W., Jen, S. N., Nguyen, A., & Wang, S. L. (2016). Application of chitinous materials in production and purification of a poly (L-lactic acid) depolymerase from Pseudomonas tamsuii TKU015. Polymers, 8(3), 98.	No			No			2016.0	Clear zone	Recycled PLA plastic wastes were prepared as powders and added to the basal liquid medium for the production of PLA-degrading enzymes. PLA pellets (2002D, number-average molecular weight, Mn: 1.25 _ 104) were obtained from Cargill Dow, Minnetonka, MN, USA. PLA powders (particle size 200–300 _m) for enzymatic assays were prepared by dissolving 50 mg of PLA pellets in 50 mL of dichloromethane mixed with 500 mL of methanol. PLA powders were obtained by homogenizing the PLA/dichloromethane/methanol solution with a homogenizer at 10,000 rpm for 5 min. PLA powders were filtered and air-dried for 24 h, then dried in a vacuum oven overnight at 30 _C. All chemicals used were of analytical grade.	Cargill Dow	Yes		Soil	Soil	Taiwan	No		
Arthrobacter sp.	1667	Nylon	Takehara, I., Kato, D. I., Takeo, M., & Negoro, S. (2017). Draft genome sequence of the nylon oligomer-degrading bacterium Arthrobacter sp. strain KI72. Genome Announc., 5(17), e00217-17.	No			No			2017.0									No		
Bacillus cereus	1396	PE	Shahnawaz, M., Sangale, M. K., & Ade, A. B. (2016). Bacteria-based polythene degradation products: GC-MS analysis and toxicity testing. Environmental Science and Pollution Research, 23(11), 10733-10741.	No			No			2016.0									No		
Niallia circulans	1397	LDPE	Watanabe, T., Ohtake, Y., Asabe, H., Murakami, N., & Furukawa, M. (2009). Biodegradability and degrading microbes of low‐density polyethylene. Journal of applied polymer science, 111(1), 551-559.	No			No			2009.0	SEM;FTIR	LDPE fine powder		No		Soil	Soil	Japan	No		
Bacillus sp.	1409	PE	Yang, Y., Chen, J., Wu, W. M., Zhao, J., & Yang, J. (2015). Complete genome sequence of Bacillus sp. YP1, a polyethylene-degrading bacterium from waxworm's gut. Journal of biotechnology, 200, 77-78.	No			No			2015.0						Waxworm's gut	Animal associated		No		
Brevibacillus borstelensis	45462	HDPE	Mohanrasu, K., Premnath, N., Prakash, G. S., Sudhakar, M., Boobalan, T., & Arun, A. (2018). Exploring multi potential uses of marine bacteria; an integrated approach for PHB production, PAHs and polyethylene biodegradation. Journal of Photochemistry and Photobiology B: Biology, 185, 55-65.	No			No			2018.0	FTIR;NMR;HPLC;CLSM;SEM;Weight loss	Polyethylene (HDPE) bags (41 µm thickness) were obtained from local markets	Local market	No			Marine	India	No		
Geomyces pannorum	79858	PU	Cosgrove, L., McGeechan, P. L., Robson, G. D., & Handley, P. S. (2007). Fungal communities associated with degradation of polyester polyurethane in soil. Appl. Environ. Microbiol., 73(18), 5817-5824.	No			No			2007.0	Clear zone	Impranil		No		PU coupons	Soil	UK	No		
Lysinibacillus fusiformis	28031	PE	Shahnawaz, M., Sangale, M. K., & Ade, A. B. (2016). Bacteria-based polythene degradation products: GC-MS analysis and toxicity testing. Environmental Science and Pollution Research, 23(11), 10733-10741.	No			No			2016.0									No		
Phoma sp.	1707701	PU	Cosgrove, L., McGeechan, P. L., Robson, G. D., & Handley, P. S. (2007). Fungal communities associated with degradation of polyester polyurethane in soil. Appl. Environ. Microbiol., 73(18), 5817-5824.	No			No			2007.0	Clear zone	Impranil		No		PU coupons	Soil	UK	No		
Pseudogymnoascus pannorum	79858	PU	Cosgrove, L., McGeechan, P. L., Robson, G. D., & Handley, P. S. (2007). Fungal communities associated with degradation of polyester polyurethane in soil. Appl. Environ. Microbiol., 73(18), 5817-5824.	No			No			2007.0	Clear zone	Impranil		No		PU coupons	Soil	UK	No		
Rhodococcus ruber	1830	PE	Gilan, I., & Sivan, A. (2013). Effect of proteases on biofilm formation of the plastic-degrading actinomycete Rhodococcus ruber C208. FEMS microbiology letters, 342(1), 18-23.	No			No			2013.0									No		
Staphylococcus epidermidis	1282	LDPE	Chatterjee, S., Roy, B., Roy, D., & Banerjee, R. (2010). Enzyme-mediated biodegradation of heat treated commercial polyethylene by Staphylococcal species. Polymer Degradation and Stability, 95(2), 195-200.	No			No			2010.0	SEM;FTIR;DLS	The LDPE films used in this work were obtained from local markets (Ganapati Polymers, Kolkata) where it was sold as 20 micron thick carrier bags.		No					No		
Absidia sp.	1982014	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Absidia sp.	1982014	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Acetobacterium sp.	1872094	PEG	Schramm, E., & Schink, B. (1991). Ether-cleaving enzyme and diol dehydratase involved in anaerobic polyethylene glycol degradation by a new Acetobacterium sp. Biodegradation, 2(2), 71-79.	No			No			1991.0	Spectrophotometry;GC	PEG's 300, 1000, 10000, and 20000	Merck	Yes	No	Sludge	Sewage/Sludge	Germany	No		
Achromobacter sp.	134375	PVC Blend	Das, G., Bordoloi, N. K., Rai, S. K., Mukherjee, A. K., & Karak, N. (2012). Biodegradable and biocompatible epoxidized vegetable oil modified thermostable poly (vinyl chloride): Thermal and performance characteristics post biodegradation with Pseudomonas aeruginosa and Achromobacter sp. Journal of hazardous materials, 209, 434-442.	No			No			2012.0	Weight loss;FTIR;SEM	PVC (molecular weight, Mn = 1.5 × 103 g/mol, density = 1.4 g/cc) was obtained from local market	Kumud Enterprise		No	Soil	Soil	India	No		
Achromobacter xylosoxidans	85698	HDPE	Kowalczyk, A., Chyc, M., Ryszka, P., & Latowski, D. (2016). Achromobacter xylosoxidans as a new microorganism strain colonizing high-density polyethylene as a key step to its biodegradation. Environmental Science and Pollution Research, 23(11), 11349-11356.	No			No			2016.0	FTIR-ATR;SEM;Weight loss	Microbial cultures were cultivated in liquid nutrient medium devoid of carbon. The source of this element for the microor ganisms was sectioned HDPE polyethylene foil, the polymeric material comprising in its chemical structure only carbon and hydrogen in the form of unbranched hydrocarbon chain. The biological material was cultivated on solidified Luria- Bertani Broth (LB) medium.			No	Soil	Plastic waste dumping site	Poland	No		
Acidovorax avenae	80867	PBSA	Mergaert, J., Ruffieux, K., Bourban, C., Storms, V., Wagemans, W., Wintermantel, E., & Swings, J. (2000). In vitro biodegradation of polyester-based plastic materials by selected bacterial cultures. Journal of Polymers and the Environment, 8(1), 17-27.	No			No			2000.0	Tensilometer;Weight loss;Clear zone	PBSBA, Poly(butylene succinate-co-butylene-adipate), Granules, films, test bars, Bionolle #3020	Showa Denko		No	Water			No		
Acidovorax avenae	80867	PCL	Mergaert, J., Ruffieux, K., Bourban, C., Storms, V., Wagemans, W., Wintermantel, E., & Swings, J. (2000). In vitro biodegradation of polyester-based plastic materials by selected bacterial cultures. Journal of Polymers and the Environment, 8(1), 17-27.	No			No			2000.0	Tensilometer;Weight loss;Clear zone	PCL, Poly(e-caprolactone), granules, films, test bars, TONE P787	Union Carbide		No	Water			No		
Acidovorax delafieldii	47920	PHBH	Morohoshi, T., Oi, T., Aiso, H., Suzuki, T., Okura, T., & Sato, S. (2018). Biofilm formation and degradation of commercially available biodegradable plastic films by bacterial consortiums in freshwater environments. Microbes and environments, ME18033.	No			No			2018.0	Clear zone;Weight loss				No	Water	River/Lake	Japan	No		
Acidovorax facilis	12917	PHBH	Morohoshi, T., Oi, T., Aiso, H., Suzuki, T., Okura, T., & Sato, S. (2018). Biofilm formation and degradation of commercially available biodegradable plastic films by bacterial consortiums in freshwater environments. Microbes and environments, ME18033.	No			No			2018.0	Clear zone;Weight loss				No	Water	River/Lake	Japan	No		
Acidovorax soli	592050	PHBH	Morohoshi, T., Oi, T., Aiso, H., Suzuki, T., Okura, T., & Sato, S. (2018). Biofilm formation and degradation of commercially available biodegradable plastic films by bacterial consortiums in freshwater environments. Microbes and environments, ME18033.	No			No			2018.0	Clear zone;Weight loss				No	Water	River/Lake	Japan	No		
Acidovorax sp.	1872122	PES	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly(ethylene succinate) (PESu) (Mn = 4.8 × 10^4, Mw/Mn = 1.9) 	Nippon Shokubai		No				No		
Acinetobacter baumannii	470	PET	Hussein, A. A., Alzuhairi, M., & Aljanabi, N. H. (2018). Degradation and depolymerization of plastic waste by local bacterial isolates and bubble column reactor. In AIP Conference Proceedings (Vol. 1968, No. 1, p. 030081). AIP Publishing.	No			No			2018.0	FTIR;Weight loss	The polyethylene terephthalate (PET) pieces used in this study were obtained from local water bottles. PET was cut into small pieces of about (2cm×2cm).		No	No		Plastic waste dumping site	Iraq	No		
Acinetobacter baumannii	470	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;SEM;FTIR;Tensilometer	LDPE, type “FGNX23-D022”;Bionolle (type #3001)	POLICHEM		No	Soil	Soil	Poland	No		
Acinetobacter baumannii	470	LDPE	Pramila, R., Padmavathy, K., Ramesh, K. V., & Mahalakshmi, K. (2012). Brevibacillus parabrevis, Acinetobacter baumannii and Pseudomonas citronellolis-Potential candidates for biodegradation of low density polyethylene (LDPE). African Journal of Bacteriology Research, 4(1), 9-14.	No			No			2012.0	CO2	LDPE sheets			No	Soil	Landfill	India	No		
Acinetobacter calcoaceticus	471	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Acinetobacter calcoaceticus	471	PHA	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHA (BIOPOL-D400P-PB36)	Monsanto		No	Soil	Soil	Japan	No		
Acinetobacter calcoaceticus	471	PHC	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHC (PCD-2000)	Toagosei		No	Soil	Soil	Japan	No		
Acinetobacter junii	40215	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Acinetobacter junii	40215	PHC	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHC (PCD-2000)	Toagosei		No	Soil	Soil	Japan	No		
Acinetobacter junii	40215	PTS	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PTS (BIONOLLE-1020)	Showa Denko		No	Soil	Soil	Japan	No		
Acinetobacter oleivorans	1148157	PES	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly(ethylene succinate) (PESu) (Mn = 4.8 × 10^4, Mw/Mn = 1.9) 	Nippon Shokubai		No				No		
Acinetobacter pittii	48296	LDPE	Montazer, Z., Habibi Najafi, M. B., & Levin, D. B. (2018). Microbial degradation of low-density polyethylene and synthesis of polyhydroxyalkanoate polymers. Canadian journal of microbiology, 65(3), 224-234.	No			No			2018.0	Weight loss;SEM;GC;FTIR	LDPE powder, with a particle size of 400 μm or less (screen retention of 50 mesh is 4.4%) and a molecular weight range between 20,000 and 150,000, was supplied by Alfa-Asar Company (USA; CAS number 9002-88-4). According to the supplier, the Feedstock Melt Index and density were 3.50 g/10 min (at 190 oC and 2.16 kg load) and 0.9227 g/cm3, respectively. According to supplier’s data sheet, the polymer was pure and free of stabilizing agents. The PE particles sterilized by exposure to UV-light (254 nm) for 1 hour while mixing.	Alfa-Asar Company		No	Soil	Plastic waste dumping site	Iran	No		
Acinetobacter pittii	48296	LDPE	Montazer, Z., Habibi-Najafi, M. B., Mohebbi, M., & Oromiehei, A. (2018). Microbial degradation of UV-pretreated low-density polyethylene films by novel polyethylene-degrading bacteria isolated from plastic-dump soil. Journal of Polymers and the Environment, 26(9), 3613-3625.	No			No			2018.0	FTIR;SEM;Microscopy;Weight loss;CG-FIT	Low density polyethylene (Poliran LF0200 grade) granules and film (10 μm thickness; 99.95% purity without any additives and plasticizers) used for pasteurized milk packaging were supplied by Iran Polymer and Petrochemical Institute (IPPI)	Polymer and Petrochemical Institute (IPPI)	Yes	No	Soil	Landfill	Iran	No		
Acinetobacter ursingii	108980	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Acremonium flavum	1036739	PU	Zafar, U., Nzeram, P., Langarica-Fuentes, A., Houlden, A., Heyworth, A., Saiani, A., & Robson, G. D. (2014). Biodegradation of polyester polyurethane during commercial composting and analysis of associated fungal communities. Bioresource technology, 158, 374-377.	No			No			2014.0	Clear zone	Impranil	Bayer 	No	No	PU coupons	Compost	UK	No		
Acremonium sp.	2046025	PHA	Boyandin, A. N., Prudnikova, S. V., Karpov, V. A., Ivonin, V. N., Đỗ, N. L., Nguyễn, T. H., ... & Volova, T. G. (2013). Microbial degradation of polyhydroxyalkanoates in tropical soils. International Biodeterioration & Biodegradation, 83, 77-84.	No			No			2013.0	Weight loss;GPC;X-ray	The polymers were synthesized in Wautersia eutropha B5786 microbial culture (the strain is registered in the Russian Collection of Industrial Microorganisms).			No	Soil	Soil	Vietnam	No		
Acremonium sp.	2046025	PHB	Mergaert, J., Webb, A., Anderson, C., Wouters, A., & Swings, J. (1993). Microbial degradation of poly (3-hydroxybutyrate) and poly (3-hydroxybutyrate-co-3-hydroxyvalerate) in soils. Appl. Environ. Microbiol., 59(10), 3233-3238.	No			No			1993.0	GPC;Tensilometer;Weight loss;Clear zone	Bioplastics were obtained from ICI Biological Products (Billingham, United Kingdom) as injection molded, dog bone-shaped tensile test pieces 83 mm long, 2 mm thick, and weighing approximately 1.75 g or as powder. Two polymers were investigated: homopolymer P(3HB) (high-purity grade; batch no. GV9/1) and copolymer P(3HB-co-10%3HV) (technical purity grade; batch no. P032). Tensile test pieces contained 0.5 [P(3HB)] or 1.0 [P(3HB-co-10%3HV)] part per hundred resin of boron nitride as a nucleant.	ICI, UK		No	Plastic debris	Soil	Belgium	No		
Acremonium sp.	2046025	PHBV	Mergaert, J., Webb, A., Anderson, C., Wouters, A., & Swings, J. (1993). Microbial degradation of poly (3-hydroxybutyrate) and poly (3-hydroxybutyrate-co-3-hydroxyvalerate) in soils. Appl. Environ. Microbiol., 59(10), 3233-3238.	No			No			1993.0	GPC;Tensilometer;Weight loss;Clear zone	Bioplastics were obtained from ICI Biological Products (Billingham, United Kingdom) as injection molded, dog bone-shaped tensile test pieces 83 mm long, 2 mm thick, and weighing approximately 1.75 g or as powder. Two polymers were investigated: homopolymer P(3HB) (high-purity grade; batch no. GV9/1) and copolymer P(3HB-co-10%3HV) (technical purity grade; batch no. P032). Tensile test pieces contained 0.5 [P(3HB)] or 1.0 [P(3HB-co-10%3HV)] part per hundred resin of boron nitride as a nucleant.	ICI, UK		No	Plastic debris	Soil	Belgium	No		
Actinomadura sp.	1989	PHBV	Shah, A. A., Hasan, F., & Hameed, A. (2010). Degradation of poly (3-hydroxybutyrate-co-3-hydroxyvalerate) by a newly isolated Actinomadura sp. AF-555, from soil. International Biodeterioration & Biodegradation, 64(4), 281-285.	No			No			2010.0	SEM;FTIR;Clear zone	Poly(3-hydroxybutyrate-co-3-hydroxyvalerate) containing 5% 3-hydroxyvalerate (3HV) in powder form	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Actinomucor elegans	64647	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Actinomucor elegans	64647	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Aestuariibacter halophilus	226011	PHBH	Morohoshi, T., Ogata, K., Okura, T., & Sato, S. (2018). Molecular characterization of the bacterial community in biofilms for degradation of poly (3-hydroxybutyrate-co-3-hydroxyhexanoate) films in seawater. Microbes and environments, ME17052.	No			No			2018.0	Clear zone;Weight loss	PHBH (3HHx=6 mol% and 11mol%) with mw 610,000 and 550,000, respectively. 	Kaneka Biodegrable		No	Water	Marine	Japan	No		
Agaricus bisporus	5341	PU	Brunner, I., Fischer, M., Rüthi, J., Stierli, B., & Frey, B. (2018). Ability of fungi isolated from plastic debris floating in the shoreline of a lake to degrade plastics. PloS one, 13(8), e0202047.	No			No			2018.0	Clear zone	Impranil	Bayer 	No	No		Culture collection	Switzerland	No		
Agrobacterium tumefaciens	358	PHA	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHA (BIOPOL-D400P-PB36)	Monsanto		No	Soil	Soil	Japan	No		
Alcaligenes faecalis	511	PHB	Gangurde, N. S., Patil, Y. P., Jain, R., & Sayyed, R. Z. (2017). Poly-β-hydroxybutyrate biodegradation by mixed culture population vis-à-vis single culture population under varying environmental conditions: A new approach.	No			No			2017.0	Weight loss;Clear zone	PHB production was carried out by Alcaligenes sp. RZS 4 (Gene bank accession No. JN374993) using two-step cultivation process.		Yes	No	Soil	Soil	India	No		
Alcaligenes sp.	512	PHB	Gangurde, N. S., Patil, Y. P., Jain, R., & Sayyed, R. Z. (2017). Poly-β-hydroxybutyrate biodegradation by mixed culture population vis-à-vis single culture population under varying environmental conditions: A new approach.	No			No			2017.0	Weight loss;Clear zone	PHB production was carried out by Alcaligenes sp. RZS 4 (Gene bank accession No. JN374993) using two-step cultivation process.		Yes	No	Soil	Soil	India	No		
Alcaligenes sp.	512	PS	Sekhar, V. C., Nampoothiri, K. M., Mohan, A. J., Nair, N. R., Bhaskar, T., & Pandey, A. (2016). Microbial degradation of high impact polystyrene (HIPS), an e-plastic with decabromodiphenyl oxide and antimony trioxide. Journal of hazardous materials, 318, 347-354.	No			No			2016.0	FTIR;TGA;NMR;Weight loss;HPLC	Indian Institute of petroleum (IIP), CSIR provided four types of e-plastic samples. These are virgin plastics samples used in electric and electronic appliance and are specially prepared for research purpose and not available commercially. The samples were coded as (1) AMS 01 (HIPS with decabromodiphenyl oxide or ether and antimony trioxide) (2) AMS 01S (HIPS with decabromodiphenyl oxide or ether) (3) AMS 02 (HIPS with decabromodiphenyl ethane and antimony trioxide) and (4) AMS 02S (HIPS with decabromodiphenyl ethane).	Indian Institute of petroleum (IIP), CSIR	No	No	Plastic debris	Plastic waste dumping site	India	No		
Alcanivorax borkumensis	59754	LDPE	Delacuvellerie, A., Cyriaque, V., Gobert, S., Benali, S., & Wattiez, R. (2019). The plastisphere in marine ecosystem hosts potential specific microbial degraders including Alcanivorax borkumensis as a key player for the low-density polyethylene degradation. Journal of hazardous materials, 380, 120899.	No			No			2019.0	Weight loss;SEM;FTIR	LDPE (ExxonMobil™ LDPE, LD 150BW Wire & Cable, density: 0.923 g/cm3 , Tm: 109 °C)	Wire & Cable		No				No		
Alcanivorax sp.	1872427	PCL	Sekiguchi, T., Saika, A., Nomura, K., Watanabe, T., Watanabe, T., Fujimoto, Y., ... & Kanehiro, H. (2011). Biodegradation of aliphatic polyesters soaked in deep seawaters and isolation of poly (ɛ-caprolactone)-degrading bacteria. Polymer degradation and stability, 96(7), 1397-1403.	No			No			2011.0	SEM;Tensilometer;Spectrophotometry;Clear zone	PCL fiber (Composition: Monofilament (300 denier); Strength (kgf): 1.02; Breaking elongation (%): 70)	Daicel Chemical Industries	NA 	No	Fiber	Marine	Japan	No		
Alcanivorax sp.	1872427	PCL	Sekiguchi, T., Saika, A., Nomura, K., Watanabe, T., Watanabe, T., Fujimoto, Y., ... & Kanehiro, H. (2011). Biodegradation of aliphatic polyesters soaked in deep seawaters and isolation of poly (ɛ-caprolactone)-degrading bacteria. Polymer degradation and stability, 96(7), 1397-1403.	No			No			2011.0	SEM;Tensilometer;Spectrophotometry;Clear zone	PCL fiber (Composition: Monofilament (300 denier); Strength (kgf): 1.02; Breaking elongation (%): 70)	Daicel Chemical Industries	NA 	No	Fiber	Marine	Japan	No		
Alcanivorax sp.	1872427	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Alcanivorax sp.	1872427	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Alicycliphilus sp.	1872437	PU	Oceguera-Cervantes, A., Carrillo-García, A., López, N., Bolaños-Nuñez, S., Cruz-Gómez, M. J., Wacher, C., & Loza-Tavera, H. (2007). Characterization of the polyurethanolytic activity of two Alicycliphilus sp. strains able to degrade polyurethane and N-methylpyrrolidone. Appl. Environ. Microbiol., 73(19), 6214-6223.	No			No			2007.0	FTIR;MS;SEM	Impranil DLN	Bayer 	No	No	Plastic debris	Plastic waste dumping site	Mexico	No		
Aliiglaciecola lipolytica	477689	PHBH	Morohoshi, T., Ogata, K., Okura, T., & Sato, S. (2018). Molecular characterization of the bacterial community in biofilms for degradation of poly (3-hydroxybutyrate-co-3-hydroxyhexanoate) films in seawater. Microbes and environments, ME17052.	No			No			2018.0	Clear zone;Weight loss	PHBH (3HHx=6 mol% and 11mol%) with mw 610,000 and 550,000, respectively. 	Kaneka Biodegrable		No	Water	Marine	Japan	No		
Alternaria alternata	5599	PHB	Gangurde, N. S., Patil, Y. P., Jain, R., & Sayyed, R. Z. (2017). Poly-β-hydroxybutyrate biodegradation by mixed culture population vis-à-vis single culture population under varying environmental conditions: A new approach.	No			No			2017.0	Weight loss;Clear zone	PHB production was carried out by Alcaligenes sp. RZS 4 (Gene bank accession No. JN374993) using two-step cultivation process.		Yes	No	Soil	Soil	India	No		
Alternaria Solani	48100	PU	Ibrahim, I. N. (2009). Polyester‐polyurethane biodegradation by Alternaria Solani, isolated from Northern Jordan Ibrahim N. Ibrahim, Anwar Maraqa, Khalid M. Hameed, Ismail M. Saadoun, Hamzah M Maswadeh and Toshiaki Nakajima‐Kambe 2 3. Adv Environ Biol, 3, 162-170.	No			No			2009.0	HPLC;Weight loss;Tensilometer;FTIR;TLC;Microscopy	Sheets (5 x 20 cm) of PS-PUR were supplied by Dr. Toshiaki Nakajima-Kambe from the Institute of Applied Biochemistry, University of Tsukuba, Ibaraki-Japan, and used as a source of carbon and nitrogen in the growing media.			No	Soil	Soil	Jordan	No		
Alternaria solani	48100	PU	Ibrahim, I. N., Maraqa, A., Hameed, K. M., Saadoun, I. M., & Maswadeh, H. M. (2011). Assessment of potential plastic-degrading fungi in Jordanian habitats. Turkish Journal of Biology, 35(5), 551-557.	No			No			2011.0	Weight loss;Clear zone	Sheets (5 × 20 cm) of PS-PUR were supplied by Dr. Toshiaki Nakajima-Kambe from the Institute of Applied Biochemistry, University of Tsukuba, Ibaraki- Japan, and used as a source of carbon and nitrogen in growth media.			No	Soil	Soil	Jordan	No		
Alternaria sp.	1715220	PU	Matsumiya, Y., Murata, N., Tanabe, E., Kubota, K., & Kubo, M. (2010). Isolation and characterization of an ether‐type polyurethane‐degrading micro‐organism and analysis of degradation mechanism by Alternaria sp. Journal of applied microbiology, 108(6), 1946-1953.	No			No			2010.0	SEM;MS;Clear zone	Cubical ether-PUR (1 cm3) and powdered ether-PUR–containing medium 		No	No				No		
Alteromonas sp.	232	PHBH	Kato, C., Honma, A., Sato, S., Okura, T., Fukuda, R., & Nogi, Y. (2019). Poly 3-hydroxybutyrate-co-3-hydroxyhexanoate films can be degraded by the deep-sea microbes at high pressure and low temperature conditions. High Pressure Research, 1-10.	No			No			2019.0	TEM;SEM;Microscopy;Clear zone	PHBH powder			No	Sediment	Marine	Japan	No		
Amycolatopsis alba	76020	PBS	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PTMS (BIONOLLE 1020; Mn D 2:9 _ 104) pellet 	Showa Denko		No	Culture collection	Culture collection		No		
Amycolatopsis alba	76020	PCL	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PCL (TONE P767; Mn D 1:8_104) pellet	Union Carbide		No	Culture collection	Culture collection		No		
Amycolatopsis alba	76020	PHB	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PHB powder 	Mitsubishi Gas Chemical		No	Culture collection	Culture collection		No		
Amycolatopsis alba	76020	PLA	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	LACTY 1012 (number-average molecular weight, Mn = 1.3 × 105)	Shimadzu		No	Culture collection	Culture collection		No		
Amycolatopsis azurea	36819	PBS	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PTMS (BIONOLLE 1020; Mn D 2:9 _ 104) pellet 	Showa Denko		No	Culture collection	Culture collection		No		
Amycolatopsis azurea	36819	PCL	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PCL (TONE P767; Mn D 1:8_104) pellet	Union Carbide		No	Culture collection	Culture collection		No		
Amycolatopsis azurea	36819	PHB	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PHB powder 	Mitsubishi Gas Chemical		No	Culture collection	Culture collection		No		
Amycolatopsis azurea	36819	PLA	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	LACTY 1012 (number-average molecular weight, Mn = 1.3 × 105)	Shimadzu		No	Culture collection	Culture collection		No		
Amycolatopsis coloradensis	76021	PCL	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PCL (TONE P767; Mn D 1:8_104) pellet	Union Carbide		No	Culture collection	Culture collection		No		
Amycolatopsis coloradensis	76021	PLA	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	LACTY 1012 (number-average molecular weight, Mn = 1.3 × 105)	Shimadzu		No	Culture collection	Culture collection		No		
Amycolatopsis fastidiosa	1816	PBS	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PTMS (BIONOLLE 1020; Mn D 2:9 _ 104) pellet 	Showa Denko		No	Culture collection	Culture collection		No		
Amycolatopsis fastidiosa	1816	PCL	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PCL (TONE P767; Mn D 1:8_104) pellet	Union Carbide		No	Culture collection	Culture collection		No		
Amycolatopsis fastidiosa	1816	PHB	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PHB powder 	Mitsubishi Gas Chemical		No	Culture collection	Culture collection		No		
Amycolatopsis fastidiosa	1816	PLA	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	LACTY 1012 (number-average molecular weight, Mn = 1.3 × 105)	Shimadzu		No	Culture collection	Culture collection		No		
Amycolatopsis mediterranei	33910	PBS	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PTMS (BIONOLLE 1020; Mn D 2:9 _ 104) pellet 	Showa Denko		No	Culture collection	Culture collection		No		
Amycolatopsis mediterranei	33910	PCL	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PCL (TONE P767; Mn D 1:8_104) pellet	Union Carbide		No	Culture collection	Culture collection		No		
Amycolatopsis mediterranei	33910	PHB	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PHB powder 	Mitsubishi Gas Chemical		No	Culture collection	Culture collection		No		
Amycolatopsis mediterranei	33910	PLA	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	LACTY 1012 (number-average molecular weight, Mn = 1.3 × 105)	Shimadzu		No	Culture collection	Culture collection		No		
Amycolatopsis methanolica	1814	PBS	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PTMS (BIONOLLE 1020; Mn D 2:9 _ 104) pellet 	Showa Denko		No	Culture collection	Culture collection		No		
Amycolatopsis methanolica	1814	PCL	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PCL (TONE P767; Mn D 1:8_104) pellet	Union Carbide		No	Culture collection	Culture collection		No		
Amycolatopsis methanolica	1814	PLA	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	LACTY 1012 (number-average molecular weight, Mn = 1.3 × 105)	Shimadzu		No	Culture collection	Culture collection		No		
Amycolatopsis orientalis	31958	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Amycolatopsis orientalis	31958	PBS	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PTMS (BIONOLLE 1020; Mn D 2:9 _ 104) pellet 	Showa Denko		No	Culture collection	Culture collection		No		
Amycolatopsis orientalis	31958	PCL	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PCL (TONE P767; Mn D 1:8_104) pellet	Union Carbide		No	Culture collection	Culture collection		No		
Amycolatopsis orientalis	31958	PHB	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PHB powder 	Mitsubishi Gas Chemical		No	Culture collection	Culture collection		No		
Amycolatopsis orientalis	31958	PLA	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	LACTY 1012 (number-average molecular weight, Mn = 1.3 × 105)	Shimadzu		No	Culture collection	Culture collection		No		
Amycolatopsis rugosa	43354	PBS	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PTMS (BIONOLLE 1020; Mn D 2:9 _ 104) pellet 	Showa Denko		No	Culture collection	Culture collection		No		
Amycolatopsis rugosa	43354	PCL	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PCL (TONE P767; Mn D 1:8_104) pellet	Union Carbide		No	Culture collection	Culture collection		No		
Amycolatopsis sp.	37632	PCL	Abou-Zeid, D. M., Müller, R. J., & Deckwer, W. D. (2001). Degradation of natural and synthetic polyesters under anaerobic conditions. Journal of biotechnology, 86(2), 113-126.	No			No			2001.0	Clear zone;Weight loss;Spectrophotometry	Poly(o-caprolactone) (PCL) from Polysciences, Inc. (Warrington, USA).	Polysciences		No	Film	Sewage/Sludge	Germany	No		
Amycolatopsis sp.	37632	PBS	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PTMS (BIONOLLE 1020; Mn D 2:9 _ 104) pellet 	Showa Denko		No	Culture collection	Culture collection		No		
Amycolatopsis sp.	37632	PCL	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PCL (TONE P767; Mn D 1:8_104) pellet	Union Carbide		No	Culture collection	Culture collection		No		
Amycolatopsis sp.	37632	PHB	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PHB powder 	Mitsubishi Gas Chemical		No	Culture collection	Culture collection		No		
Amycolatopsis sp.	37632	PLA	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	LACTY 1012 (number-average molecular weight, Mn = 1.3 × 105)	Shimadzu		No	Culture collection	Culture collection		No		
Amycolatopsis sp.	37632	PLA	Pranamuda, H., Tsuchii, A., & Tokiwa, Y. (2001). Poly (L‐lactide)‐Degrading Enzyme Produced by Amycolatopsis sp. Macromolecular Bioscience, 1(1), 25-29.	No			No			2001.0	Clear zone;TOC	A PLLA pellet “LACTY #1012” with a number average molecular weight (Mn) of 1.4x10^5.	Shimadzu		No				No		
Amycolatopsis sulphurea	76022	PBS	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PTMS (BIONOLLE 1020; Mn D 2:9 _ 104) pellet 	Showa Denko		No	Culture collection	Culture collection		No		
Amycolatopsis sulphurea	76022	PCL	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PCL (TONE P767; Mn D 1:8_104) pellet	Union Carbide		No	Culture collection	Culture collection		No		
Amycolatopsis thailandensis	589330	PLA	Chomchoei, A., Pathom-Aree, W., Yokota, A., Kanongnuch, C., & Lumyong, S. (2011). Amycolatopsis thailandensis sp. nov., a poly (l-lactic acid)-degrading actinomycete, isolated from soil. International journal of systematic and evolutionary microbiology, 61(4), 839-843.	No			No			2011.0	Clear zone	PLA film			No	Soil	Soil	Thailand	No		
Amycolatopsis tolypomycina	208445	PBS	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PTMS (BIONOLLE 1020; Mn D 2:9 _ 104) pellet 	Showa Denko		No	Culture collection	Culture collection		No		
Amycolatopsis tolypomycina	208445	PCL	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PCL (TONE P767; Mn D 1:8_104) pellet	Union Carbide		No	Culture collection	Culture collection		No		
Amycolatopsis tolypomycina	208445	PHB	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	PHB powder 	Mitsubishi Gas Chemical		No	Culture collection	Culture collection		No		
Amycolatopsis tolypomycina	208445	PLA	Pranamuda, H., & Tokiwa, Y. (1999). Degradation of poly (L-lactide) by strains belonging to genus Amycolatopsis. Biotechnology Letters, 21(10), 901-905.	No			No			1999.0	Clear zone;TOC	LACTY 1012 (number-average molecular weight, Mn = 1.3 × 105)	Shimadzu		No	Culture collection	Culture collection		No		
Aneurinibacillus aneurinilyticus	1391	PLA	Chaisu, K., Charles, A. L., Guu, Y. K., & Chiu, C. H. (2013). Microbial Degradation of Poly Lactic Acid (PLA) by Aneurinibacillus aneurinilyticus. Journal of Biobased Materials and Bioenergy, 7(4), 509-511.	No			No			2013.0	Weight loss;Clear zone;SEM	The PLA films sheets (3×3 cm^2)	Benison		No	Soil	Soil	Taiwan	No		
Arthrobacter oryzae	409290	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Plastic waste dumping site	Slovakia	No		
Arthrobacter oryzae	409290	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Arthrobacter sp.	1667	PCL	Adıgüzel, A. O., & Tunçer, M. (2017). Purification and characterization of cutinase from Bacillus sp. KY0701 isolated from plastic wastes. Preparative Biochemistry and Biotechnology, 47(9), 925-933.	No			No			2017.0	Weight loss;Clear zone	Plastic Waste		No	No	Plastic debris	Soil	Turkey	No		
Arthrobacter sp.	1667	HDPE	Balasubramanian, V., Natarajan, K., Hemambika, B., Ramesh, N., Sumathi, C. S., Kottaimuthu, R., & Rajesh Kannan, V. (2010). High‐density polyethylene (HDPE)‐degrading potential bacteria from marine ecosystem of Gulf of Mannar, India. Letters in applied microbiology, 51(2), 205-211.	No			No			2010.0	Weight loss;FTIR	Commercially available HDPE materials were used as substrate in this study, which is the grade of environmental pollution rather than pure polyethylene to access the direct impact on environment and application-oriented solution, because the composition of commercially available HDPE varies from pure polyethylene by the addition of additives like antioxidants and colourant.		No	No		Plastic waste dumping site	India	No		
Arthrobacter sp.	1667	HDPE	Satlewal, A., Soni, R., Zaidi, M. G. H., Shouche, Y., & Goel, R. (2008). Comparative biodegradation of HDPE and LDPE using an indigenously developed microbial consortium. J Microbiol Biotechnol, 18(3), 477-482.	No			No			2008.0	FTIR;TG;DTG;DTA;Weight loss	High-density polyethylene (HDPE) and low-density polyethylene (LDPE; purchased from Sigma-Aldrich Chemical Corporation, U.S.A.) beads were converted into powdered form through boiling with xylene followed by solvent evaporation at room temperature.	Sigma Aldrich	Yes	No	Waste	Plastic waste dumping site	India	No		
Arthrobacter sp.	1667	PU	Shah, A. A., Hasan, F., Akhter, J. I., Hameed, A., & Ahmed, S. (2008). Degradation of polyurethane by novel bacterial consortium isolated from soil. Annals of microbiology, 58(3), 381.	No			No			2008.0	Clear zone;CO2;SEM;FTIR	Poly [4,4’-methylenebis (phenyl isocyanate)-alt-1,4-butanediol/poly (butylene adipate)] (Polyurethane, PU) (Sigma-Aldrich, GmbH, Germany) having 1.220 g/ml density and melting temperature about 190 °C, was used in the present study.	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Arthrographis kalrae	241728	PU	Zafar, U., Nzeram, P., Langarica-Fuentes, A., Houlden, A., Heyworth, A., Saiani, A., & Robson, G. D. (2014). Biodegradation of polyester polyurethane during commercial composting and analysis of associated fungal communities. Bioresource technology, 158, 374-377.	No			No			2014.0	Clear zone	Impranil	Bayer 	No	No	PU coupons	Compost	UK	No		
Aspergillus awamori	105351	PE	Sangale, M. K., Shahnawaz, M., & Ade, A. B. (2019). Potential of fungi isolated from the dumping sites mangrove rhizosphere soil to degrade polythene. Scientific Reports, 9(1), 5390.	No			No			2019.0	Weight loss;Tensilometer;SEM;FTIR				No	Soil	Plant associated	India	No		
Aspergillus awamori	105351	PLA	Torres, A., Li, S. M., Roussos, S., & Vert, M. (1996). Screening of microorganisms for biodegradation of poly (lactic-acid) and lactic acid-containing polymers. Appl. Environ. Microbiol., 62(7), 2393-2397.	No			No			1996.0	HPLC;SEM	Typically, 1 liter of DL-LA commercial solution was heated under normal pressure to gently distillate water. When the temperature reached 1308C, vacuum was applied and distillation was controlled as desired. One fraction of racemic oligomers (Mw 5 1,000, I 5 Mw/Mn 5 1.3) was used for the screening of filamentous fungi, and another one (Mw 5 2,000, I 5 1.3) was used for soil screening. Molecular weights were determined by size exclusion chromatography. 	Sigma Aldrich	Yes	No		Culture collection		No		
Aspergillus calidoustus	454130	PLA	Antipova, T. V., Zhelifonova, V. P., Zaitsev, K. V., Nedorezova, P. M., Aladyshev, A. M., Klyamkina, A. N., ... & Kozlovsky, A. G. (2018). Biodegradation of Poly-ε-caprolactones and Poly-l-lactides by Fungi. Journal of Polymers and the Environment, 26(12), 4350-4359.	No			No			2018.0	Weight loss;MS	PLA was obtained upon ring-opening polymerization of l-lactide in the presence of catalytic amounts of aluminium complexes			No	Foci of corrosion of fiberglass СТР-4ТР	Culture collection		No		
Aspergillus clavatus	5057	LDPE	Gajendiran, A., Krishnamoorthy, S., & Abraham, J. (2016). Microbial degradation of low-density polyethylene (LDPE) by Aspergillus clavatus strain JASK1 isolated from landfill soil. 3 Biotech, 6(1), 52.	No			No			2016.0	Weight loss;CO2;SEM;AFM;Spectrophotometry	The LDPE films used in this study were collected from Vellore market, which were 20-lm-thick bags. For the biodegradation studies, LDPE films were cut into small strips and were sterilized with 70 % ethanol		No	No	Soil 	Landfill	India	No		
Aspergillus fischeri	36630	PCL	Benedict, C. V., Cameron, J. A., & Huang, S. J. (1983). Polycaprolactone degradation by mixed and pure cultures of bacteria and a yeast. Journal of Applied Polymer Science, 28(1), 335-342.	No			No			1983.0	Clear zone;GPC	Polycaprolactone 700 (PCL-700), PCL-300, and LPS-60 with molecular weights of 35,000,18,600, and 7,130 Wr, respectively, were obtained from Union Carbide Corp., New York, N.Y. The PCL designated LPS-60 by the manufacturer contains a phthalic acid residue covalently linked to the chain ends but otherwise is structurally identical to PCL-700 and PCL-300. No low molecular weight, contaminants were seen by chromatographic analysis of the polymers using THF, chloroform, or dichloromethane as solvents. Infrared spectroscopy of PCL-700 resulted in a spectrum identical to the published standard.6 All polymers showed broad molecular weight distributions. Polydispersities (Mv/Mn) ranged from 1.892 to 1.978.	Union Carbide	Yes	No	Culture collection	River/Lake	USA	No		
Aspergillus fischeri	36630	PCL	Bentham, R. H., Morton, L. H. G., & Allen, N. G. (1987). Rapid assessment of the microbial deterioration of polyurethanes. International biodeterioration, 23(6), 377-386.	No			No			1987.0	Clear zone;Tensilometer;Weight loss	Two similar formulations of polyurethane foam were investigated, supplied as dumbbell-shaped test pieces. The materials were both polyester polyurethanes, one formulation, however, contained VINYZENE BP (10,10'-oxybis-phenoxarsine) as the formulation biocide. Another formulation was also available, an unprotected polyester polyurethane elastomer.		No	No	Plastic debris	Compost		No		
Aspergillus flavus	5059	LDPE	Deepika, S., & Madhuri, R. J. (2015). Biodegradation of low density polyethylene by micro-organisms from garbage soil. Journal of Experimental Biology and Agricultural Sciences, 3(1), 15-21.	No			No			2015.0	Clear zone;Weight loss	Low density polyethylene powder (LDPE) with 53-75 µm particle size was obtained from Sigma Aldrich Chemical Co (Product of USA) with density 0.94g/ml at 250C. Low density polyethylene granules from Pack worth polymers and Pack mates India Private Ltd (Hyderabad, INDIA).	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	India	No		
Aspergillus flavus	5059	HDPE	Devi, R. S., Kannan, V. R., Nivas, D., Kannan, K., Chandru, S., & Antony, A. R. (2015). Biodegradation of HDPE by Aspergillus spp. from marine ecosystem of Gulf of Mannar, India. Marine pollution bulletin, 96(1-2), 32-40.	No			No			2015.0	Weight loss;FTIR;SEM;Spectrophotometry	Commercially available HDPE (40 lm in thickness and 0.95 g/cm3 in density) materials were purchased from the local market, Tiruchirappalli, Tamil Nadu, India. The composition of commercially available HDPE varies from pure polyethylene by the addition of additives like antioxidants and colorant.	Local market	No	No	Plastic debris	Plastic waste dumping site	India	No		
Aspergillus flavus	5059	PHB	Gangurde, N. S., Patil, Y. P., Jain, R., & Sayyed, R. Z. (2017). Poly-β-hydroxybutyrate biodegradation by mixed culture population vis-à-vis single culture population under varying environmental conditions: A new approach.	No			No			2017.0	Weight loss;Clear zone	PHB production was carried out by Alcaligenes sp. RZS 4 (Gene bank accession No. JN374993) using two-step cultivation process.		Yes	No	Soil	Soil	India	No		
Aspergillus flavus	5059	PU	Ibrahim, I. N., Maraqa, A., Hameed, K. M., Saadoun, I. M., & Maswadeh, H. M. (2011). Assessment of potential plastic-degrading fungi in Jordanian habitats. Turkish Journal of Biology, 35(5), 551-557.	No			No			2011.0	Weight loss;Clear zone	Sheets (5 × 20 cm) of PS-PUR were supplied by Dr. Toshiaki Nakajima-Kambe from the Institute of Applied Biochemistry, University of Tsukuba, Ibaraki- Japan, and used as a source of carbon and nitrogen in growth media.			No	Plastic debris		Jordan	No		
Aspergillus flavus	5059	LDPE	Jyoti, S., & Gupta, K. C. (2014). Screening and identification of low density polyethylene (LDPE) degrading soil fungi isolated from polythene polluted sites around Gwalior city (MP). International Journal of Current Microbiology and Applied Sciences, 3(6), 443-448.	No			No			2014.0	Clear zone;Weight loss	Low density polyethylene (LDPE) sheets were obtained from Gwalior Plastic Industry (Gwalior).	Gwalior Plastic Industry 		No	Soil	Plastic waste dumping site	India	No		
Aspergillus flavus	5059	PE	Mohan, S. K., & Suresh, B. (2015). Studies on Biodegradation of Plastics by Aspergillus sp. Isolated From Dye Effluent Enriched Soil. Indo American Journal of Pharmaceutical Sciences, 2(12), 1636-1639.	No			No			2015.0	Weight loss	Plastic carry bag strips		No	No	Dye effluent enriched soil	Plastic waste dumping site	India	No		
Aspergillus flavus	5059	LDPE	Usha, R., Sangeetha, T., & Palaniswamy, M. (2011). Screening of polyethylene degrading microorganisms from garbage soil. Libyan agriculture research center journal international, 2(4), 200-204.	No			No			2011.0	Clear zone	Low density polyethylene powder (LDPE)	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	India	No		
Aspergillus flavus	5059	LDPE	Zhang, J., Gao, D., Li, Q., Zhao, Y., Li, L., Lin, H., ... & Zhao, Y. (2020). Biodegradation of polyethylene microplastic particles by the fungus Aspergillus flavus from the guts of wax moth Galleria mellonella. Science of The Total Environment, 704, 135931.	No			No			2020.0	FTIR;Turbidity;Weight loss;GPC	Low-density polyethylene (LDPE) with density of 0.921 g·cm−3 (N210, China Petrochemical Corporation, Shanghai) and high-density polyethylene (HDPE) with density of 0.955 g·cm−3 (5502LW, China Petrochemical Corporation, Maoming) were used. All the particles were sieved through 120 mesh (125 μm) nylon sieve three times to prepare MPP with a size below 200 μm. MPP was irradiated under UV light for 5 h as a sterilization treatment (more details in supporting information).	China Petrochemical Corporation		No	Gut	Animal associated	China	No		
Aspergillus foetidus	63131	PE	Mohan, S. K., & Suresh, B. (2015). Studies on Biodegradation of Plastics by Aspergillus sp. Isolated From Dye Effluent Enriched Soil. Indo American Journal of Pharmaceutical Sciences, 2(12), 1636-1639.	No			No			2015.0	Weight loss	Plastic carry bag strips		No	No	Dye effluent enriched soil	Plastic waste dumping site	India	No		
Aspergillus foetidus	63131	PLA	Torres, A., Li, S. M., Roussos, S., & Vert, M. (1996). Screening of microorganisms for biodegradation of poly (lactic-acid) and lactic acid-containing polymers. Appl. Environ. Microbiol., 62(7), 2393-2397.	No			No			1996.0	HPLC;SEM	Typically, 1 liter of DL-LA commercial solution was heated under normal pressure to gently distillate water. When the temperature reached 1308C, vacuum was applied and distillation was controlled as desired. One fraction of racemic oligomers (Mw 5 1,000, I 5 Mw/Mn 5 1.3) was used for the screening of filamentous fungi, and another one (Mw 5 2,000, I 5 1.3) was used for soil screening. Molecular weights were determined by size exclusion chromatography. 	Sigma Aldrich	Yes	No		Culture collection		No		
Aspergillus fumigatus	746128	PU	Álvarez-Barragán, J., Domínguez-Malfavón, L., Vargas-Suárez, M., González-Hernández, R., Aguilar-Osorio, G., & Loza-Tavera, H. (2016). Biodegradative activities of selected environmental fungi on a polyester polyurethane varnish and polyether polyurethane foams. Appl. Environ. Microbiol., 82(17), 5225-5235.	No			No			2016.0	FTIR;MS;SEM;Clear zone	Impranil	Bayer 		No			Mexico	No		
Aspergillus fumigatus	746128	PBSA	Ishii, N., Inoue, Y., Tagaya, T., Mitomo, H., Nagai, D., & Kasuya, K. I. (2008). Isolation and characterization of poly (butylene succinate)-degrading fungi. Polymer Degradation and Stability, 93(5), 883-888.	No			No			2008.0	Clear zone;Weight loss;Microscopy;SEM;GPC;MS	PBSA (1,4-Butanediol/succinic acid/adipic acid; Tm 92;Mw x10-4)	Showa Denko		No	Soil	Soil	Japan	No		
Aspergillus fumigatus	746128	PCL	Ishii, N., Inoue, Y., Tagaya, T., Mitomo, H., Nagai, D., & Kasuya, K. I. (2008). Isolation and characterization of poly (butylene succinate)-degrading fungi. Polymer Degradation and Stability, 93(5), 883-888.	No			No			2008.0	Clear zone;Weight loss;Microscopy;SEM;GPC;MS	PCL (6-Hydroxyhexanoic acid; Tm 62; Mw 6.4x10^-4)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Aspergillus fumigatus	746128	PES	Ishii, N., Inoue, Y., Tagaya, T., Mitomo, H., Nagai, D., & Kasuya, K. I. (2008). Isolation and characterization of poly (butylene succinate)-degrading fungi. Polymer Degradation and Stability, 93(5), 883-888.	No			No			2008.0	Clear zone;Weight loss;Microscopy;SEM;GPC;MS	PES (Ethylene glycol/succinic acid; Tm 106; Mw 18/.1x10^-4)	Nippon Shokubai		No	Soil	Soil	Japan	No		
Aspergillus fumigatus	746128	PHB	Ishii, N., Inoue, Y., Tagaya, T., Mitomo, H., Nagai, D., & Kasuya, K. I. (2008). Isolation and characterization of poly (butylene succinate)-degrading fungi. Polymer Degradation and Stability, 93(5), 883-888.	No			No			2008.0	Clear zone;Weight loss;Microscopy;SEM;GPC;MS	PHB (3-Hydroxybutyrate; Tm 178; Mw 70x10^-4). Ralstonia eutropha ATCC17699 from fructose [20]		Yes	No	Soil	Soil	Japan	No		
Aspergillus fumigatus	746128	PHB	Mergaert, J., Webb, A., Anderson, C., Wouters, A., & Swings, J. (1993). Microbial degradation of poly (3-hydroxybutyrate) and poly (3-hydroxybutyrate-co-3-hydroxyvalerate) in soils. Appl. Environ. Microbiol., 59(10), 3233-3238.	No			No			1993.0	Weight loss;Tensilometer;Clear zone	The polymers were obtained from ZENECA Bio Products either as injection-moulded, dog bone-shaped tensile test pieces, 83 mm long, 2 mm thick, with a total surface area of approx. 19.5 cm2, and weighing approximately 1.75 g, or as powder. Three polymers were investigated: homopolymer P(3HB) batch G08, copolymer P(3HB-co-10%-3HV) batch PSMll+PSM20, and copolymer P(3HB-co-20%-3HV) batch PSM11.	Zeneca Bioproducts		No	Water		Belgium	No		
Aspergillus fumigatus	746128	PHBV	Mergaert, J., Webb, A., Anderson, C., Wouters, A., & Swings, J. (1993). Microbial degradation of poly (3-hydroxybutyrate) and poly (3-hydroxybutyrate-co-3-hydroxyvalerate) in soils. Appl. Environ. Microbiol., 59(10), 3233-3238.	No			No			1993.0	GPC;Tensilometer;Weight loss;Clear zone	Bioplastics were obtained from ICI Biological Products (Billingham, United Kingdom) as injection molded, dog bone-shaped tensile test pieces 83 mm long, 2 mm thick, and weighing approximately 1.75 g or as powder. Two polymers were investigated: homopolymer P(3HB) (high-purity grade; batch no. GV9/1) and copolymer P(3HB-co-10%3HV) (technical purity grade; batch no. P032). Tensile test pieces contained 0.5 [P(3HB)] or 1.0 [P(3HB-co-10%3HV)] part per hundred resin of boron nitride as a nucleant.	ICI, UK		No	Plastic debris	Soil	Belgium	No		
Aspergillus fumigatus	746128	LDPE	Zahra, S., Abbas, S. S., Mahsa, M. T., & Mohsen, N. (2010). Biodegradation of low-density polyethylene (LDPE) by isolated fungi in solid waste medium. Waste management, 30(3), 396-401.	No			No			2010.0	TOC;SEM;FTIR;GPC;	Commercial granules of LDPE were provided from one of the stocks of Iran’s National Petrochemical Commercial Company (INPCC). LDPE films with thickness of 15 um were made from this material using a blowing film extruder. LDPE films were irradiated for 25 days with UV-irradiation in a laminar flow cabinet and then cut into pieces of about 1x1 cm.	Iran’s National Petrochemical Commercial Company (INPCC)		No	Soil	Landfill	Iran	No		
Aspergillus glaucus	41413	PE	Kathiresan, K. (2003). Polythene and plastics-degrading microbes from the mangrove soil. Revista de biologia tropical, 51(3-4), 629-633.	No			No			2003.0	Weight loss	Pre weighed discs of 1cm diameter prepared from polythene bags and disposable plastic cups		No	No	Plastic debris	Mangrove	India	No		
Aspergillus japonicus	34381	LDPE	Jyoti, S., & Gupta, K. C. (2014). Screening and identification of low density polyethylene (LDPE) degrading soil fungi isolated from polythene polluted sites around Gwalior city (MP). International Journal of Current Microbiology and Applied Sciences, 3(6), 443-448.	No			No			2014.0	Clear zone;Weight loss	Low density polyethylene (LDPE) sheets were obtained from Gwalior Plastic Industry (Gwalior).	Gwalior Plastic Industry 		No	Soil	Plastic waste dumping site	India	No		
Aspergillus nidulans	162425	PLA	Torres, A., Li, S. M., Roussos, S., & Vert, M. (1996). Screening of microorganisms for biodegradation of poly (lactic-acid) and lactic acid-containing polymers. Appl. Environ. Microbiol., 62(7), 2393-2397.	No			No			1996.0	HPLC;SEM	Typically, 1 liter of DL-LA commercial solution was heated under normal pressure to gently distillate water. When the temperature reached 1308C, vacuum was applied and distillation was controlled as desired. One fraction of racemic oligomers (Mw 5 1,000, I 5 Mw/Mn 5 1.3) was used for the screening of filamentous fungi, and another one (Mw 5 2,000, I 5 1.3) was used for soil screening. Molecular weights were determined by size exclusion chromatography. 	Sigma Aldrich	Yes	No		Culture collection		No		
Aspergillus nidulans	162425	LDPE	Usha, R., Sangeetha, T., & Palaniswamy, M. (2011). Screening of polyethylene degrading microorganisms from garbage soil. Libyan agriculture research center journal international, 2(4), 200-204.	No			No			2011.0	Clear zone	Low density polyethylene powder (LDPE)	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	India	No		
Aspergillus niger	5061	PVC	Ali, M. I., Ahmed, S., Robson, G., Javed, I., Ali, N., Atiq, N., & Hameed, A. (2014). Isolation and molecular characterization of polyvinyl chloride (PVC) plastic degrading fungal isolates. Journal of basic microbiology, 54(1), 18-27.	No			No			2014.0	SEM;CO2;FTIR;Spectrophotometry;NMR;GPC	Thin films of PVC (2% w/v) were prepared in petri plates by dissolving 0.2 g of PVC (Aldrich) in 10 ml of solvent tetrahydrofuran (THF; 99%; Merck).	Sigma Aldrich		No	PVC film	Sewage/Sludge		No		
Aspergillus niger	5061	PCL	Bentham, R. H., Morton, L. H. G., & Allen, N. G. (1987). Rapid assessment of the microbial deterioration of polyurethanes. International biodeterioration, 23(6), 377-386.	No			No			1987.0	Clear zone;Tensilometer;Weight loss	Two similar formulations of polyurethane foam were investigated, supplied as dumbbell-shaped test pieces. The materials were both polyester polyurethanes, one formulation, however, contained VINYZENE BP (10,10'-oxybis-phenoxarsine) as the formulation biocide. Another formulation was also available, an unprotected polyester polyurethane elastomer.		No	No	Plastic debris	Compost		No		
Aspergillus niger	5061	LDPE	Deepika, S., & Madhuri, R. J. (2015). Biodegradation of low density polyethylene by micro-organisms from garbage soil. Journal of Experimental Biology and Agricultural Sciences, 3(1), 15-21.	No			No			2015.0	Clear zone;Weight loss	Low density polyethylene powder (LDPE) with 53-75 µm particle size was obtained from Sigma Aldrich Chemical Co (Product of USA) with density 0.94g/ml at 250C. Low density polyethylene granules from Pack worth polymers and Pack mates India Private Ltd (Hyderabad, INDIA).	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	India	No		
Aspergillus niger	5061	LDPE	Esmaeili, A., Pourbabaee, A. A., Alikhani, H. A., Shabani, F., & Esmaeili, E. (2013). Biodegradation of low-density polyethylene (LDPE) by mixed culture of Lysinibacillus xylanilyticus and Aspergillus niger in soil. Plos one, 8(9).	No			No			2013.0	CO2;Tensilometer;FTIR;X-ray;SEM	low-density polyethylene granules (LF0200, with a density of 0.920 gr.cm23)	Iranian petrochemical company 		No	Soil	Landfill	Iran	No		
Aspergillus niger	5061	PHB	Gangurde, N. S., Patil, Y. P., Jain, R., & Sayyed, R. Z. (2017). Poly-β-hydroxybutyrate biodegradation by mixed culture population vis-à-vis single culture population under varying environmental conditions: A new approach.	No			No			2017.0	Weight loss;Clear zone	PHB production was carried out by Alcaligenes sp. RZS 4 (Gene bank accession No. JN374993) using two-step cultivation process.		Yes	No	Soil	Soil	India	No		
Aspergillus niger	5061	PBS	Ishii, N., Inoue, Y., Tagaya, T., Mitomo, H., Nagai, D., & Kasuya, K. I. (2008). Isolation and characterization of poly (butylene succinate)-degrading fungi. Polymer Degradation and Stability, 93(5), 883-888.	No			No			2008.0	Clear zone;Weight loss;Microscopy;SEM;GPC;MS	PBSu (1,4-Butanediol/succinic acid;Tm 117;Mw 17.6x10-4)	Showa Denko		No	Soil	Soil	Japan	No		
Aspergillus niger	5061	PCL	Ishii, N., Inoue, Y., Tagaya, T., Mitomo, H., Nagai, D., & Kasuya, K. I. (2008). Isolation and characterization of poly (butylene succinate)-degrading fungi. Polymer Degradation and Stability, 93(5), 883-888.	No			No			2008.0	Clear zone;Weight loss;Microscopy;SEM;GPC;MS	PCL (6-Hydroxyhexanoic acid; Tm 62; Mw 6.4x10^-4)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Aspergillus niger	5061	LDPE	Jyoti, S., & Gupta, K. C. (2014). Screening and identification of low density polyethylene (LDPE) degrading soil fungi isolated from polythene polluted sites around Gwalior city (MP). International Journal of Current Microbiology and Applied Sciences, 3(6), 443-448.	No			No			2014.0	Clear zone;Weight loss	Low density polyethylene (LDPE) sheets were obtained from Gwalior Plastic Industry (Gwalior).	Gwalior Plastic Industry 		No	Soil	Plastic waste dumping site	India	No		
Aspergillus niger	5061	PE	Kathiresan, K. (2003). Polythene and plastics-degrading microbes from the mangrove soil. Revista de biologia tropical, 51(3-4), 629-633.	No			No			2003.0	Weight loss	Pre weighed discs of 1cm diameter prepared from polythene bags and disposable plastic cups		No	No	Plastic debris	Mangrove	India	No		
Aspergillus niger	5061	PETG	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	SG is a biodegradable aliphatic polyester, made of succinic acid, adipic acid, butanediol and ethylene glycol. It was donated by SKI in powder form (200 mm) with a melt index of 30 g/10 min at 190C.	SKI		No	Plastic debris	Soil	South Korea	No		
Aspergillus niger	5061	PHB	Kumaravel, S., Hema, R., & Lakshmi, R. (2010). Production of polyhydroxybutyrate (bioplastic) and its biodegradation by Pseudomonas lemoignei and Aspergillus niger. Journal of Chemistry, 7(S1), S536-S542.	No			No			2010.0	Clear zone;Weight loss	For production, the bio-industrial effluent such as sugarcane effluent waste was collected in sterile bottle and they were preceded for PHB production. 		Yes	No	Soil	Soil		No		
Aspergillus niger	5061	LDPE	Manzur, A., Limón‐González, M., & Favela‐Torres, E. (2004). Biodegradation of physicochemically treated LDPE by a consortium of filamentous fungi. Journal of Applied Polymer Science, 92(1), 265-271.	No			No			2004.0	CO2;DSC;WAXS;GC;FTIR;SEM	Commercial low density polyethylene was used (17,070, produced by Pemex, Mexico). Its density and flow index values were 0.917 g/cc and 7 g/10 min, respectively.	Pemex		No	Culture collection	Culture collection		No		
Aspergillus niger	5061	HDPE	Mathur, G., Mathur, A., & Prasad, R. (2011). Colonization and degradation of thermally oxidized high-density polyethylene by Aspergillus niger (ITCC No. 6052) isolated from plastic waste dumpsite. Bioremediation journal, 15(2), 69-76.	No			No			2011.0	SEM;Weight loss;Tensilometer;FTIR	The test material used in the present study was HDPE of 0.95 cm−3 density and 20 μ thickness	Carry and Packers Plastics	No	No	Soil	Plastic waste dumping site	India	No		
Aspergillus niger	5061	PE	Mohan, S. K., & Suresh, B. (2015). Studies on Biodegradation of Plastics by Aspergillus sp. Isolated From Dye Effluent Enriched Soil. Indo American Journal of Pharmaceutical Sciences, 2(12), 1636-1639.	No			No			2015.0	Weight loss	Plastic carry bag strips		No	No	Dye effluent enriched soil	Plastic waste dumping site	India	No		
Aspergillus niger	5061	PE	Raghavan, D., & Torma, A. E. (1992). DSC and FTIR Characterization of Biodegradation of Polyethylene. Polymer Engineering & Science, 32(6), 438-442.	No			No			1992.0	DSC;FTIR	Commercially available polyethylene films having a thickness of 10.16 um were used for biodegradation experiments.			No				No		
Aspergillus niger	5061	LDPE	Sáenz, M., Borodulina, T., Diaz, L., & Banchon, C. (2019). Minimal Conditions to Degrade Low Density Polyethylene by Aspergillus terreus and niger. Journal of Ecological Engineering, 20(6), 44-51.	No			No			2019.0	Weight loss	The LDPE films with a thickness of 100 μm were cut into squares of 2 cm2 and weighed us¬ing an analytical balance (Kerns, USA).			No	Soil	Mangrove	Ecuador	No		
Aspergillus niger	5061	PE	Sangale, M. K., Shahnawaz, M., & Ade, A. B. (2019). Potential of fungi isolated from the dumping sites mangrove rhizosphere soil to degrade polythene. Scientific Reports, 9(1), 5390.	No			No			2019.0	Weight loss;Tensilometer;SEM;FTIR				No	Soil	Plant associated	India	No		
Aspergillus niger	5061	PLA	Torres, A., Li, S. M., Roussos, S., & Vert, M. (1996). Screening of microorganisms for biodegradation of poly (lactic-acid) and lactic acid-containing polymers. Appl. Environ. Microbiol., 62(7), 2393-2397.	No			No			1996.0	HPLC;SEM	Typically, 1 liter of DL-LA commercial solution was heated under normal pressure to gently distillate water. When the temperature reached 1308C, vacuum was applied and distillation was controlled as desired. One fraction of racemic oligomers (Mw 5 1,000, I 5 Mw/Mn 5 1.3) was used for the screening of filamentous fungi, and another one (Mw 5 2,000, I 5 1.3) was used for soil screening. Molecular weights were determined by size exclusion chromatography. 	Sigma Aldrich	Yes	No		Culture collection		No		
Aspergillus niger	5061	LDPE	Volke‐Sepúlveda, T., Saucedo‐Castañeda, G., Gutiérrez‐Rojas, M., Manzur, A., & Favela‐Torres, E. (2002). Thermally treated low density polyethylene biodegradation by Penicillium pinophilum and Aspergillus niger. Journal of Applied Polymer Science, 83(2), 305-314.	No			No			2002.0	DSC;X-ray;FTIR;SEM;GC	Powdered LDPE (17070, supplied by PEMEX, Mexico City, Mexico) was heated (80°C, 15 days) under dry and dark air atmosphere. Thermally treated LDPE was then cooled by freezing (0°C) and milled in a grinder (particle size ,0.542 mm). TO-LDPE was sterilized with UV radiation (~350 mW/cm2, 20 h) before incubation with fungi. Untreated milled-LDPE was used as reference in all conditions.	Pemex		No	Culture collection	Culture collection		No		
Aspergillus nomiae	41061	LDPE	Munir, E., Harefa, R. S. M., Priyani, N., & Suryanto, D. (2018). Plastic degrading fungi Trichoderma viride and Aspergillus nomius isolated from local landfill soil in Medan. In IOP Conference Series: Earth and Environmental Science (Vol. 126, No. 1, p. 012145). IOP Publishing.	No			No			2018.0	SEM;Weight loss;Tensilometer;Clear zone	LDPE powder was prepared by dissolving LDPE beads in xylene with continuous stirring. The clump LDPE was rinsed with 96% ethanol and dried completely in an oven at 50° C. The LDPE was cut into small pieces and smashed with blander to get powder form.			No	Soil	Landfill	Indonesia	No		
Aspergillus oryzae	5062	LDPE	Muhonja, C. N., Makonde, H., Magoma, G., & Imbuga, M. (2018). Biodegradability of polyethylene by bacteria and fungi from Dandora dumpsite Nairobi-Kenya. PloS one, 13(7), e0198446.	No			No			2018.0	Weight loss;FTIR;MS	LDPE powder			No	Soil	Plastic waste dumping site	Kenya	No		
Aspergillus oryzae	5062	PLA	Torres, A., Li, S. M., Roussos, S., & Vert, M. (1996). Screening of microorganisms for biodegradation of poly (lactic-acid) and lactic acid-containing polymers. Appl. Environ. Microbiol., 62(7), 2393-2397.	No			No			1996.0	HPLC;SEM	Typically, 1 liter of DL-LA commercial solution was heated under normal pressure to gently distillate water. When the temperature reached 1308C, vacuum was applied and distillation was controlled as desired. One fraction of racemic oligomers (Mw 5 1,000, I 5 Mw/Mn 5 1.3) was used for the screening of filamentous fungi, and another one (Mw 5 2,000, I 5 1.3) was used for soil screening. Molecular weights were determined by size exclusion chromatography. 	Sigma Aldrich	Yes	No		Culture collection		No		
Aspergillus penicillioides	41959	PHB	Mergaert, J., Anderson, C., Wouters, A., Swings, J., & Kersters, K. F. E. M. S. (1992). Biodegradation of polyhydroxyalkanoates. FEMS microbiology reviews, 9(2-4), 317-321.	No			No			1992.0	Tensilometer;Weight loss	All bioplastics were obtained from ICI Biological Products (Billingham, UK), as injection moulded, dogbone-shaped tensile test pieces.	ICI, UK		No	Plastic debris		Belgium	No		
Aspergillus sp.	5065	LDPE	Das, M. P., & Kumar, S. (2014). Microbial deterioration of low density polyethylene by Aspergillus and Fusarium sp. Int J Chem Tech Res, 6(1), 299-305.	No			No			2014.0	SEM;FTIR;Weight loss;CO2	The LDPE films were cut into small pieces and were dipped in xylene and heated, when the plastic gets dissolved it was cooled to palm bearable heat and was crushed to fine particles. Later it was kept to evaporate the xylene and was washed with ethanol to remove xylene residues. Then it was dried in hot air oven at 50 °C for overnight.			No	LDPE film	Plastic waste dumping site	India	No		
Aspergillus sp.	5065	PU	Osman, M., Satti, S. M., Luqman, A., Hasan, F., Shah, Z., & Shah, A. A. (2018). Degradation of polyester polyurethane by Aspergillus sp. strain S45 isolated from soil. Journal of Polymers and the Environment, 26(1), 301-310.	No			No			2018.0	FTIR;DSC;Weight loss;CO2;SEM	Methylene diphenyl diisocyanate (MDI) polyester PU {poly[4,4-methylene-bis(phenyl isocyanate)-alt-1,4-butanediol/ poly (butylene adipate)]} pellets were obtained from Sigma-Aldrich, GmbH, Germany. 	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Aspergillus sp.	5065	PET	Sarkhel, R., Sengupta, S., Das, P., & Bhowal, A. (2020). Comparative biodegradation study of polymer from plastic bottle waste using novel isolated bacteria and fungi from marine source. Journal of Polymer Research, 27(1), 16.	No			No			2020.0	Weight loss;FTIR;SEM;X-ray	In this study, polymer films were obtained mainly from waste Plastic bottles, which is a thermoplastic polymer predominantly composed of polyolefins like Polyethylene Terephthalate (PET) 		No	No	Water	Mangrove	India	No		
Aspergillus sp.	5065	PHB	Tansengco, M., & Dogma Jr, I. (1999). Microbial degradation of poly‐β‐hydroxybutyrate using landfill soils. Acta biotechnologica, 19(3), 191-203.	No			No			1999.0	SEM;TOC;Weight loss;Clear zone	Samples of poly-&hydroxybutyrate or PHB granules (-O-CH(CH3)-CH2-CO-}n exhibiting an average molecular weight (Mw) of 9.4 x10^5, a melting temperature of 170 °C and a purity of 98%. 	Mitsubishi Gas Chemical	Yes	No	Soil	Landfill	Philippines	No		
Aspergillus sydowii	75750	PVC	Ali, M. I., Ahmed, S., Robson, G., Javed, I., Ali, N., Atiq, N., & Hameed, A. (2014). Isolation and molecular characterization of polyvinyl chloride (PVC) plastic degrading fungal isolates. Journal of basic microbiology, 54(1), 18-27.	No			No			2014.0	SEM;CO2;FTIR;Spectrophotometry;NMR;GPC	Thin films of PVC (2% w/v) were prepared in petri plates by dissolving 0.2 g of PVC (Aldrich) in 10 ml of solvent tetrahydrofuran (THF; 99%; Merck).	Sigma Aldrich		No	PVC film	Sewage/Sludge		No		
Aspergillus sydowii	75750	PE	Sangale, M. K., Shahnawaz, M., & Ade, A. B. (2019). Potential of fungi isolated from the dumping sites mangrove rhizosphere soil to degrade polythene. Scientific Reports, 9(1), 5390.	No			No			2019.0	Weight loss;Tensilometer;SEM;FTIR				No	Soil	Plant associated	India	No		
Aspergillus terreus	33178	HDPE	Balasubramanian, V., Natarajan, K., Rajeshkannan, V., & Perumal, P. (2014). Enhancement of in vitro high-density polyethylene (HDPE) degradation by physical, chemical, and biological treatments. Environmental Science and Pollution Research, 21(21), 12549-12562.	No			No			2014.0	Weight loss;FTIR;SEM;MS	Commercially available HDPE materials (40 μm in thickness) were used as substrate in this study, which is the grade of environmental pollution, rather than pure polyethylene in accessing the direct impact on environment and applicationoriented solution. The composition of commercially available HDPE varies from pure polyethylene by the addition of additives like antioxidants and colorant.			No	Soil	Plastic waste dumping site		No		
Aspergillus terreus	33178	LDPE	Sáenz, M., Borodulina, T., Diaz, L., & Banchon, C. (2019). Minimal Conditions to Degrade Low Density Polyethylene by Aspergillus terreus and niger. Journal of Ecological Engineering, 20(6), 44-51.	No			No			2019.0	Weight loss	The LDPE films with a thickness of 100 μm were cut into squares of 2 cm2 and weighed us¬ing an analytical balance (Kerns, USA).			No	Soil	Mangrove	Ecuador	No		
Aspergillus terreus	33178	PE	Sangale, M. K., Shahnawaz, M., & Ade, A. B. (2019). Potential of fungi isolated from the dumping sites mangrove rhizosphere soil to degrade polythene. Scientific Reports, 9(1), 5390.	No			No			2019.0	Weight loss;Tensilometer;SEM;FTIR				No	Soil	Plant associated	India	No		
Aspergillus terreus	33178	LDPE	Zahra, S., Abbas, S. S., Mahsa, M. T., & Mohsen, N. (2010). Biodegradation of low-density polyethylene (LDPE) by isolated fungi in solid waste medium. Waste management, 30(3), 396-401.	No			No			2010.0	TOC;SEM;FTIR;GPC;	Commercial granules of LDPE were provided from one of the stocks of Iran’s National Petrochemical Commercial Company (INPCC). LDPE films with thickness of 15 um were made from this material using a blowing film extruder. LDPE films were irradiated for 25 days with UV-irradiation in a laminar flow cabinet and then cut into pieces of about 1x1 cm.	Iran’s National Petrochemical Commercial Company (INPCC)		No	Soil	Landfill	Iran	No		
Aspergillus tubingensis	5068	HDPE	Devi, R. S., Kannan, V. R., Nivas, D., Kannan, K., Chandru, S., & Antony, A. R. (2015). Biodegradation of HDPE by Aspergillus spp. from marine ecosystem of Gulf of Mannar, India. Marine pollution bulletin, 96(1-2), 32-40.	No			No			2015.0	Weight loss;FTIR;SEM;Spectrophotometry	Commercially available HDPE (40 lm in thickness and 0.95 g/cm3 in density) materials were purchased from the local market, Tiruchirappalli, Tamil Nadu, India. The composition of commercially available HDPE varies from pure polyethylene by the addition of additives like antioxidants and colorant.	Local market	No	No	Plastic debris	Plastic waste dumping site	India	No		
Aspergillus tubingensis	5068	PU	Khan, S., Nadir, S., Shah, Z. U., Shah, A. A., Karunarathna, S. C., Xu, J., ... & Hasan, F. (2017). Biodegradation of polyester polyurethane by Aspergillus tubingensis. Environmental pollution, 225, 469-480.	No			No			2017.0	SEM;ATR-FTIR;Tensilometer	Polyester polyurethane beads (Aldrich Chemical Company, Inc. USA) (1 g) were dissolved in 100 ml of tetrahydrofuran (PanreacQuimica, SA) and sonicated for 30 m in 250 ml flask	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Aspergillus udagawae	91492	PBSA	Yamamoto-Tamura, K., Hoshino, Y. T., Tsuboi, S., Huang, C., Kishimoto-Mo, A. W., Sameshima-Yamashita, Y., & Kitamoto, H. (2020). Fungal community dynamics during degradation of poly (butylene succinate-co-adipate) film in two cultivated soils in Japan. Bioscience, Biotechnology, and Biochemistry, 1-11.	No			No			2020.0	Luminance	PBSA films used in this study were composed of Bionolle® 3001 (Showa Denko K. K., Tokyo, Japan)	Showa Denko	No	No	Soil	Soil	Japan	No		
Aspergillus ustus	40382	PCL	Bentham, R. H., Morton, L. H. G., & Allen, N. G. (1987). Rapid assessment of the microbial deterioration of polyurethanes. International biodeterioration, 23(6), 377-386.	No			No			1987.0	Clear zone;Tensilometer;Weight loss	Two similar formulations of polyurethane foam were investigated, supplied as dumbbell-shaped test pieces. The materials were both polyester polyurethanes, one formulation, however, contained VINYZENE BP (10,10'-oxybis-phenoxarsine) as the formulation biocide. Another formulation was also available, an unprotected polyester polyurethane elastomer.		No	No	Plastic debris	Compost		No		
Aspergillus ustus	40382	PHB	Gonda, K. E., Jendrossek, D., & Molitoris, H. P. (2000). Fungal degradation of the thermoplastic polymer poly-ß-hydroxybutyric acid (PHB) under simulated deep sea pressure. In Life at Interfaces and Under Extreme Conditions (pp. 173-183). Springer, Dordrecht.	No			No			2000.0	Clear zone;Spectrophotometry	PHB was isolated from sodium-gluconate-grown cells of the bacterium Ralstonia eutropha HI6 by sodium-hypochlorite treatment followed by acetone-ether (2: I, v/v) extraction.		Yes	No	Deep sea	Marine	Bay of Bengal	No		
Aspergillus versicolor	46472	PCL	Bentham, R. H., Morton, L. H. G., & Allen, N. G. (1987). Rapid assessment of the microbial deterioration of polyurethanes. International biodeterioration, 23(6), 377-386.	No			No			1987.0	Clear zone;Tensilometer;Weight loss	Two similar formulations of polyurethane foam were investigated, supplied as dumbbell-shaped test pieces. The materials were both polyester polyurethanes, one formulation, however, contained VINYZENE BP (10,10'-oxybis-phenoxarsine) as the formulation biocide. Another formulation was also available, an unprotected polyester polyurethane elastomer.		No	No	Plastic debris	Compost		No		
Aspergillus versicolor	46472	PBSA	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	PBSA (Bionolle 3020MD)	Showa Denko		No	Soil	Soil	Svalbard	No		
Aspergillus versicolor	46472	PBSA	Zhao, J. H., Wang, X. Q., Zeng, J., Yang, G., Shi, F. H., & Yan, Q. (2005). Biodegradation of poly (butylene succinate-co-butylene adipate) by Aspergillus versicolor. Polymer Degradation and Stability, 90(1), 173-179.	No			No			2005.0	Clear zone;DSC;SEM;Weight loss;NMR	PBSA (number average molecular weight, Mn= 5.59x10^4 g/mol) was synthesized by polycondensation of 1,4-butanediol (B) with succinic acid (S) and adipic acid (A). The molecular structure is shown in Scheme 1. The composition in copolyester (BS/BA) is 60/40 and is determined by 1H NMR. PBSA film was prepared by the hot-pressing method at 150 MPa and 120 _C. The film (about 40 mm thick) was cut into pieces of about 2 cm x 2 cm and sterilized with 5% (wt/vol) sodium hypochlorite before testing. PBSA powder with an average particle size of 42 um was obtained by precipitation with methanol after being dissolved in chloroform.		Yes	No	Compost	Compost		No		
Asteromyces cruciatus	1407621	PHA	Matavulj, M., & Molitoris, H. P. (2009). Marine fungi: degraders of poly-3-hydroxyalkanoate based plastic materials. Zb Mat Srp Prir Nauk, 116, 253-265.	No			No			2009.0	Clear zone;Turbidity	Granulated and powdered BIOPOL	ICI, UK		No	Culture collection	Culture collection		No		
Asteromyces cruciatus	1407621	PHB	Matavulj, M., & Molitoris, H. P. (2009). Marine fungi: degraders of poly-3-hydroxyalkanoate based plastic materials. Zb Mat Srp Prir Nauk, 116, 253-265.	No			No			2009.0	Clear zone;Turbidity	Granulated and powdered BIOPOL	ICI, UK		No	Culture collection	Culture collection		No		
Aureobasidium pullulans	5580	PU	Crabbe, J. R., Campbell, J. R., Thompson, L., Walz, S. L., & Schultz, W. W. (1994). Biodegradation of a colloidal ester-based polyurethane by soil fungi. International Biodeterioration & Biodegradation, 33(2), 103-113.	No			No			1994.0	Clear zone	The substrate used for all degradation experiments was an ester-based polyurethane (PU), and was obtained as a water-dispersed colloid (Impranil DLN, Miles Inc., Pittsburgh, PA, USA).	Miles	No	No	Soil	Soil	USA	No		
Aureobasidium pullulans	5580	PCL	Fields, R. D., Rodriguez, F., & Finn, R. K. (1974). Microbial degradation of polyesters: polycaprolactone degraded by P. pullulans. Journal of Applied Polymer Science, 18(12), 3571-3579.	No			No			1974.0	Weight loss;Tensilometer;Clear zone	Films of 1,250, 2,000, 15,000, and 30,000 molecular weight polycaprolactone (Union Carbide’s PCP-0230, PCP-0240, PCL-300, and PCL-700) were degraded by the method just described.	Union Carbide		No	Culture collection	Culture collection		No		
Aureobasidium pullulans	5580	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Aureobasidium pullulans	5580	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Bacillus altitudinis	293387	PES	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly(ethylene succinate) (PESu) (Mn = 4.8 × 10^4, Mw/Mn = 1.9) 	Nippon Shokubai		No				No		
Bacillus amyloliquefaciens	1390	LDPE	Das, M. P., & Kumar, S. (2015). An approach to low-density polyethylene biodegradation by Bacillus amyloliquefaciens. 3 Biotech, 5(1), 81-86.	No			No			2015.0	SEM;FTIR;Weight loss;CO2	Low-density polyethylene (LDPE) was obtained from B.N. Polymers, Bangalore, India. LDPE films were cut into small pieces, immersed into xylene and boiled for 15 min, followed by crushing with blender at 3,000 rpm. As obtained LDPE powder was further washed with ethanol, dried overnight in hot air oven at 60 _x00	B.N.Polymers		No	Soil	Landfill	India	No		
Bacillus amyloliquefaciens	1390	HDPE	Devi, R. S., Ramya, R., Kannan, K., Antony, A. R., & Kannan, V. R. (2019). Investigation of biodegradation potentials of high density polyethylene degrading marine bacteria isolated from the coastal regions of Tamil Nadu, India. Marine pollution bulletin, 138, 549-560.	No			No			2019.0	Weight loss;FTIR	Commercially available HDPE (40 μm in thickness and 0.95 g/cm3 in density) materials were used as substrate in this study. When compared to pure polyethylene, the composition of commercially available HDPE varies by the addition of additives like antioxidants and colorant.		No	No	Plastic debris	Plastic waste dumping site	India	No		
Bacillus amyloliquefaciens	1390	LDPE	Novotný, Č., Malachová, K., Adamus, G., Kwiecień, M., Lotti, N., Soccio, M., ... & Fava, F. (2018). Deterioration of irradiation/high-temperature pretreated, linear low-density polyethylene (LLDPE) by Bacillus amyloliquefaciens. International biodeterioration & biodegradation, 132, 259-267.	No			No			2018.0	Weight loss;FTIR;GPC;MS;DSC;TGA	Virgin LLDPE and LDPE films (density at 20 °C: 0.88–0.96 g cm−3; thickness: 40 and 70 μm for LLDPE and LDPE, respectively) were provided by Department of Civil, Chemical, Environmental, and Materials Engineering, University of Bologna, Italy. The films were kindly supplied by Versalis S.p.A. that prepared a neat formulation of the polymer films avoiding use of stabilizers and additives.	Versalis S.p.A	Yes	No	Plastic debris	Compost	Belgium	No		
Bacillus amyloliquefaciens	1390	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;SEM;FTIR;Tensilometer	LDPE, type “FGNX23-D022”;Bionolle (type #3001)	POLICHEM		No	Soil	Soil	Poland	No		
Bacillus amyloliquefaciens	1390	PE	Zhang, J., Chen, J., Jia, R., Dun, Z., Wang, B., Hu, X., & Wang, Y. (2018). Selection and evaluation of microorganisms for biodegradation of agricultural plastic film. 3 Biotech, 8(7), 308.	No			No			2018.0	Clear zone;Weight loss;SEM;FTIR	Used agricultural mulch film was collected from five counties in Gansu Province (Ma Ji, Dan, Zhang Ye, Yu Men and Ping Liang) and cut into 2 × 2 cm2 squares for screening promising strains. These squares were used for mulch seedling cultures of cabbage for 30 days. The soil moisture content of the field was maintained at 20% and the soil temperature during seedling culture was around 25 °C. New film was also bought and cut into 2 × 2 cm2 square.		No	No	Culture collection	Culture collection		No		
Bacillus aryabhattai	412384	HDPE	Devi, R. S., Ramya, R., Kannan, K., Antony, A. R., & Kannan, V. R. (2019). Investigation of biodegradation potentials of high density polyethylene degrading marine bacteria isolated from the coastal regions of Tamil Nadu, India. Marine pollution bulletin, 138, 549-560.	No			No			2019.0	Weight loss;FTIR	Commercially available HDPE (40 μm in thickness and 0.95 g/cm3 in density) materials were used as substrate in this study. When compared to pure polyethylene, the composition of commercially available HDPE varies by the addition of additives like antioxidants and colorant.		No	No	Plastic debris	Plastic waste dumping site	India	No		
Bacillus aryabhattai	412384	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Bacillus cereus	1396	PC	Arefian, M., Tahmourespour, A., & Zia, M. (2020). Polycarbonate biodegradation by newly isolated Bacillus strains. Archives of Environmental Protection, 46.	No			No			2020.0	Clear zone;AFM;FTIR	PC was used as granules (Petrochimi Co. Iran). 	Petrochimi		No	Plastic debris	Landfill	Iran	No		
Bacillus cereus	1396	PET	Auta, H. S., Emenike, C. U., & Fauziah, S. H. (2017). Screening of Bacillus strains isolated from mangrove ecosystems in Peninsular Malaysia for microplastic degradation. Environmental Pollution, 231, 1552-1559.	No			No			2017.0	Weight loss;SEM;FTIR	PET granules (granular/milky white) with density of 1.68 g/mL at 25 _x005	Sigma Aldrich	Yes	No	Sediment	Mangrove	Malaysia	No		
Bacillus cereus	1396	PS	Auta, H. S., Emenike, C. U., & Fauziah, S. H. (2017). Screening of Bacillus strains isolated from mangrove ecosystems in Peninsular Malaysia for microplastic degradation. Environmental Pollution, 231, 1552-1559.	No			No			2017.0	Weight loss;SEM;FTIR	PS granules (white/spherical) with density of 1.59 g/mL 	Sigma Aldrich	Yes	No	Sediment	Mangrove	Malaysia	No		
Bacillus cereus	1396	PHA	Boyandin, A. N., Prudnikova, S. V., Karpov, V. A., Ivonin, V. N., Đỗ, N. L., Nguyễn, T. H., ... & Volova, T. G. (2013). Microbial degradation of polyhydroxyalkanoates in tropical soils. International Biodeterioration & Biodegradation, 83, 77-84.	No			No			2013.0	Weight loss;GPC;X-ray	The polymers were synthesized in Wautersia eutropha B5786 microbial culture (the strain is registered in the Russian Collection of Industrial Microorganisms).			No	Soil	Soil	Vietnam	No		
Bacillus cereus	1396	HDPE	Devi, R. S., Ramya, R., Kannan, K., Antony, A. R., & Kannan, V. R. (2019). Investigation of biodegradation potentials of high density polyethylene degrading marine bacteria isolated from the coastal regions of Tamil Nadu, India. Marine pollution bulletin, 138, 549-560.	No			No			2019.0	Weight loss;FTIR	Commercially available HDPE (40 μm in thickness and 0.95 g/cm3 in density) materials were used as substrate in this study. When compared to pure polyethylene, the composition of commercially available HDPE varies by the addition of additives like antioxidants and colorant.		No	No	Plastic debris	Plastic waste dumping site	India	No		
Bacillus cereus	1396	PE	Dharmik, P.G., S.T. Nandy, and A.V. Gomashe. (2017). Exploration on biodegradability of polyethylene bags by Bacillus cereus isolated from dumpsite area. INTERNATIONAL JOURNAL OF RESEARCHES IN BIOSCIENCES, AGRICULTURE AND TECHNOLOGY. V(special issue 2): p. 1124-1130.	No			No			2017.0	Weight loss;FTIR;SEM	Discs of Autoclaved, Surface sterilized and UV treated polyethylene of 1cm diameter prepared from polyethylene bags.		No	No	Sediment	Mangrove	Malaysia	No		
Bacillus cereus	1396	LDPE	Muhonja, C. N., Makonde, H., Magoma, G., & Imbuga, M. (2018). Biodegradability of polyethylene by bacteria and fungi from Dandora dumpsite Nairobi-Kenya. PloS one, 13(7), e0198446.	No			No			2018.0	Weight loss;FTIR;MS	LDPE powder			No	Soil	Plastic waste dumping site	Kenya	No		
Bacillus cereus	1396	PE	Shahnawaz, M., Sangale, M. K., & Ade, A. B. (2016). Rhizosphere of Avicennia marina (Forsk.) Vierh. as a landmark for polythene degrading bacteria. Environmental Science and Pollution Research, 23(14), 14621-14635.	No			No			2016.0	Tensilometer;SEM;FTIR;Weight loss	The banned polythene carry bags (20 μmthick) were procured from the local market of the Pune City, Maharashtra, India. We purchased PE pickup bags from the vegetable vendors because the local plastic shop keepers are afraid to sell the banned PE carry bags legally. PE carrier bags less than 50 μm thickness is banned in Maharashtra and most states of India. With the aid of sharp surgical blade, 2 ×2 cm strips of the PE were made.		No	No	Soil	Plant associated	India	No		
Bacillus cereus	1396	Nylon	Sudhakar, M., Priyadarshini, C., Doble, M., Murthy, P. S., & Venkatesan, R. (2007). Marine bacteria mediated degradation of nylon 66 and 6. International Biodeterioration & Biodegradation, 60(3), 144-151.	No			No			2007.0	DSC;FTIR;Weight loss;EFM	Commercial grade nylon 6 (Mn ¼ 58,000) fibers (210D) and nylon 66 (Mn ¼ 55,000) pellets (Prime chips)	SRF		No		Marine	India	No		
Bacillus flexus	86664	PP	Aravinthan, A., Arkatkar, A., Juwarkar, A. A., & Doble, M. (2016). Synergistic growth of Bacillus and Pseudomonas and its degradation potential on pretreated polypropylene. Preparative Biochemistry and Biotechnology, 46(2), 109-115.	No			No			2016.0	FTIR;Weight loss;SEM	Commercial PP films (Reliance Industries Ltd., Mumbai, India) of size 1.5 × 1.5 cm and 0.05 mm thickness were used for the present experiments. The PP films were thermally pretreated at 100°C for 8 days in a hot-air oven (PP-TT) or short UV pretreated (PP-UV) at 225 nm for 6 days (Sigma instruments Chennai, India)	RB Industries	No	No	Soil	Plastic waste dumping site	India	No		
Bacillus flexus	86664	PP	Arkatkar, A., Arutchelvi, J., Bhaduri, S., Uppara, P. V., & Doble, M. (2009). Degradation of unpretreated and thermally pretreated polypropylene by soil consortia. International Biodeterioration & Biodegradation, 63(1), 106-111.	No			No			2009.0	Weight loss;Tensilometer;SEM;AFM;DSC	Commercial PP films of size 8  2.5 cm and 0.05 mm thickness	RB Industries		No	Soil	Plastic waste dumping site	India	No		
Bacillus flexus	86664	PP	Arkatkar, A., Juwarkar, A. A., Bhaduri, S., Uppara, P. V., & Doble, M. (2010). Growth of Pseudomonas and Bacillus biofilms on pretreated polypropylene surface. International Biodeterioration & Biodegradation, 64(6), 530-536.	No			No			2010.0	Weight loss;SEM;FTIR	Commercial PP films of size 1.5 1.5 cm and 0.05 mm thickness	RB Industries		No	Soil	Plastic waste dumping site	India	No		
Bacillus flexus	86664	PVC	Giacomucci, L., Raddadi, N., Soccio, M., Lotti, N., & Fava, F. (2019). Polyvinyl chloride biodegradation by Pseudomonas citronellolis and Bacillus flexus. New biotechnology, 52, 35-41.	No			No			2019.0	FTIR;GPC;Weight loss;TGA	PVC film contained about 30%w/w of additives/plasticizers		No	No	Culture collection	Culture collection		No		
Bacillus gottheilii	859144	PE	Auta, H. S., Emenike, C. U., & Fauziah, S. H. (2017). Screening of Bacillus strains isolated from mangrove ecosystems in Peninsular Malaysia for microplastic degradation. Environmental Pollution, 231, 1552-1559.	No			No			2017.0	Weight loss;SEM;FTIR	PE powder (white) with 75 mm particle size and density of 0.94 g/mL 	Sigma Aldrich	Yes	No	Sediment	Mangrove	Malaysia	No		
Bacillus gottheilii	859144	PET	Auta, H. S., Emenike, C. U., & Fauziah, S. H. (2017). Screening of Bacillus strains isolated from mangrove ecosystems in Peninsular Malaysia for microplastic degradation. Environmental Pollution, 231, 1552-1559.	No			No			2017.0	Weight loss;SEM;FTIR	PET granules (granular/milky white) with density of 1.68 g/mL 	Sigma Aldrich	Yes	No	Sediment	Mangrove	Malaysia	No		
Bacillus gottheilii	859144	PP	Auta, H. S., Emenike, C. U., & Fauziah, S. H. (2017). Screening of Bacillus strains isolated from mangrove ecosystems in Peninsular Malaysia for microplastic degradation. Environmental Pollution, 231, 1552-1559.	No			No			2017.0	Weight loss;SEM;FTIR	PP granules (white, spherical) with density of 0.9 g/mL 	Sigma Aldrich	Yes	No	Sediment	Mangrove	Malaysia	No		
Bacillus gottheilii	859144	PS	Auta, H. S., Emenike, C. U., & Fauziah, S. H. (2017). Screening of Bacillus strains isolated from mangrove ecosystems in Peninsular Malaysia for microplastic degradation. Environmental Pollution, 231, 1552-1559.	No			No			2017.0	Weight loss;SEM;FTIR	PS granules (white/spherical) with density of 1.59 g/mL 	Sigma Aldrich	Yes	No	Sediment	Mangrove	Malaysia	No		
Bacillus idriensis	324768	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Bacillus licheniformis	1402	HDPE	Devi, R. S., Ramya, R., Kannan, K., Antony, A. R., & Kannan, V. R. (2019). Investigation of biodegradation potentials of high density polyethylene degrading marine bacteria isolated from the coastal regions of Tamil Nadu, India. Marine pollution bulletin, 138, 549-560.	No			No			2019.0	Weight loss;FTIR	Commercially available HDPE (40 μm in thickness and 0.95 g/cm3 in density) materials were used as substrate in this study. When compared to pure polyethylene, the composition of commercially available HDPE varies by the addition of additives like antioxidants and colorant.		No	No	Plastic debris	Plastic waste dumping site	India	No		
Bacillus licheniformis	1402	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Bacillus licheniformis	1402	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Priestia megaterium	1404	PC	Arefian, M., Tahmourespour, A., & Zia, M. (2020). Polycarbonate biodegradation by newly isolated Bacillus strains. Archives of Environmental Protection, 46.	No			No			2020.0	Clear zone;AFM;FTIR	PC was used as granules (Petrochimi Co. Iran). 	Petrochimi		No	Plastic debris	Landfill	Iran	No		
Priestia megaterium	1404	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Priestia megaterium	1404	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Priestia megaterium	1404	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Priestia megaterium	1404	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Bacillus mycoides	1405	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;SEM;FTIR;Tensilometer	LDPE, type “FGNX23-D022”;Bionolle (type #3001)	POLICHEM		No	Soil	Soil	Poland	No		
Bacillus pseudomycoides	64104	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Bacillus pumilus	1408	PLA	Bonifer, K. S., Wen, X., Hasim, S., Phillips, E. K., Dunlap, R. N., Gann, E. R., ... & Reynolds, T. B. (2019). Bacillus pumilus B12 Degrades Polylactic Acid and Degradation Is Affected by Changing Nutrient Conditions. Frontiers in Microbiology, 10, 2548.	No			No			2019.0	AFM;SEM;Spectrophotometry	Polylactic acid films were created from PLA beads with an inherent viscosity of 1.8 dl/g and a molecular weight between 80,000 and 100,000 kDa (Polysciences, Inc.).	Polysciences	Yes	No	Soil	Soil	USA	No		
Bacillus pumilus	1408	HDPE	Devi, R. S., Ramya, R., Kannan, K., Antony, A. R., & Kannan, V. R. (2019). Investigation of biodegradation potentials of high density polyethylene degrading marine bacteria isolated from the coastal regions of Tamil Nadu, India. Marine pollution bulletin, 138, 549-560.	No			No			2019.0	Weight loss;FTIR	Commercially available HDPE (40 μm in thickness and 0.95 g/cm3 in density) materials were used as substrate in this study. When compared to pure polyethylene, the composition of commercially available HDPE varies by the addition of additives like antioxidants and colorant.		No	No	Plastic debris	Plastic waste dumping site	India	No		
Bacillus pumilus	1408	LDPE	Harshvardhan, K., & Jha, B. (2013). Biodegradation of low-density polyethylene by marine bacteria from pelagic waters, Arabian Sea, India. Marine Pollution Bulletin, 77(1-2), 100-106.	No			No			2013.0	Weight loss;SEM;FTIR	The biodegradation tests were performed on samples of lowdensity polyethylene film (i.e., pieces of polyethylene bags) that had been dried overnight at 60 C, weighed, disinfected (autoclaved at 105 C for 1 h) and added to each flask (approximately 50.0 mg of polyethylene film per flask) containing 50 ml of BH medium		No	No	Water	Marine	India	No		
Bacillus pumilus	1408	PBS	Hayase, N., Yano, H., Kudoh, E., Tsutsumi, C., Ushio, K., Miyahara, Y., ... & Nakagawa, K. (2004). Isolation and characterization of poly (butylene succinate-co-butylene adipate)-degrading microorganism. Journal of Bioscience and Bioengineering, 97(2), 131-133.	No			No			2004.0	Clear zone;X-ray;NMR	PBS (Bionolle #1001; Showa High-Polymer)	Showa Denko	No	No	Soil	Soil		No		
Bacillus pumilus	1408	PBS Blend	Hayase, N., Yano, H., Kudoh, E., Tsutsumi, C., Ushio, K., Miyahara, Y., ... & Nakagawa, K. (2004). Isolation and characterization of poly (butylene succinate-co-butylene adipate)-degrading microorganism. Journal of Bioscience and Bioengineering, 97(2), 131-133.	No			No			2004.0	Clear zone;X-ray;NMR	PBS blend 	Daicel Chemical Industries	No	No	Soil	Soil		No		
Bacillus pumilus	1408	PBSA	Hayase, N., Yano, H., Kudoh, E., Tsutsumi, C., Ushio, K., Miyahara, Y., ... & Nakagawa, K. (2004). Isolation and characterization of poly (butylene succinate-co-butylene adipate)-degrading microorganism. Journal of Bioscience and Bioengineering, 97(2), 131-133.	No			No			2004.0	Clear zone;X-ray;NMR	PBSA (Bionolle #3001; Showa High-Polymer)	Showa Denko	No	No	Soil	Soil		No		
Bacillus pumilus	1408	PCL Blend	Hayase, N., Yano, H., Kudoh, E., Tsutsumi, C., Ushio, K., Miyahara, Y., ... & Nakagawa, K. (2004). Isolation and characterization of poly (butylene succinate-co-butylene adipate)-degrading microorganism. Journal of Bioscience and Bioengineering, 97(2), 131-133.	No			No			2004.0	Clear zone;X-ray;NMR	PCL blend	Celgreen HB02B	No	No	Soil	Soil		No		
Bacillus pumilus	1408	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;SEM;FTIR;Tensilometer	LDPE, type “FGNX23-D022”;Bionolle (type #3001)	POLICHEM		No	Soil	Soil	Poland	No		
Bacillus pumilus	1408	PES	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly(ethylene succinate) (PESu) (Mn = 4.8 × 10^4, Mw/Mn = 1.9) 	Nippon Shokubai		No				No		
Bacillus pumilus	1408	PBSA	Tezuka, Y., Ishii, N., Kasuya, K. I., & Mitomo, H. (2004). Degradation of poly (ethylene succinate) by mesophilic bacteria. Polymer degradation and stability, 84(1), 115-121.	No			No			2004.0	Clear zone;SEM;Weight loss	Poly(butylene succinate/adipate) (PBSA)	Showa Denko		No	Freshwater	River/Lake	Japan	No		
Bacillus pumilus	1408	PCL	Tezuka, Y., Ishii, N., Kasuya, K. I., & Mitomo, H. (2004). Degradation of poly (ethylene succinate) by mesophilic bacteria. Polymer degradation and stability, 84(1), 115-121.	No			No			2004.0	Clear zone;SEM;Weight loss	Poly(E-caprolactone) (PCL) 	Daicel Chemical Industries		No	Freshwater	River/Lake	Japan	No		
Bacillus pumilus	1408	PES	Tezuka, Y., Ishii, N., Kasuya, K. I., & Mitomo, H. (2004). Degradation of poly (ethylene succinate) by mesophilic bacteria. Polymer degradation and stability, 84(1), 115-121.	No			No			2004.0	Clear zone;SEM;Weight loss	Poly(ethylene succinate) (PESu) 	Nippon Shokubai		No	Freshwater	River/Lake	Japan	No		
Bacillus pumilus	1408	PBS	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	PBS (Bionolle 1020MD)	Showa Denko		No	Soil	Soil	Svalbard	No		
Bacillus pumilus	1408	PBSA	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	PBSA (Bionolle 3020MD)	Showa Denko		No	Soil	Soil	Svalbard	No		
Bacillus pumilus	1408	PCL	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	 PCL pellets were purchased from TRESNO (Poland)	TRESNO		No	Soil	Soil	Svalbard	No		
Bacillus pumilus	1408	PLA	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	PLA pellets were obtained from BIOMAR (Germany).	BIOMAR		No	Soil	Soil	Svalbard	No		
Bacillus sp.	1409	PS	Atiq, N., Ahmed, S., Ali, M. I., Ahmad, B., & Robson, G. (2010). Isolation and identification of polystyrene biodegrading bacteria from soil. African Journal of Microbiology Research, 4(14), 1537-1541.	No			No			2010.0	SEM;FTIR;HPLC	Expanded polystyrene (EPS) solution (2%) in chloroform;Films of pure polystyrene (Mol. Wt. 100,000)	Fluka	Yes	No	Plastic film	Soil	Pakistan	No		
Bacillus sp.	1409	PP	Auta, H. S., Emenike, C. U., Jayanthi, B., & Fauziah, S. H. (2018). Growth kinetics and biodeterioration of polypropylene microplastics by Bacillus sp. and Rhodococcus sp. isolated from mangrove sediment. Marine pollution bulletin, 127, 15-21.	No			No			2018.0	Weight loss;SEM;FTIR;Clear zone	Isotactic PP microplastic granules (white, spherical) with a density of 0.9 g/ml at 25 °C, molecular weight of 250,000 Mw, average Mn of 67,000 and CAS number 9003-07-0	Sigma Aldrich	Yes	No	Sediment	Mangrove	Malaysia	No		
Bacillus sp.	1409	HDPE	Devi, R. S., Ramya, R., Kannan, K., Antony, A. R., & Kannan, V. R. (2019). Investigation of biodegradation potentials of high density polyethylene degrading marine bacteria isolated from the coastal regions of Tamil Nadu, India. Marine pollution bulletin, 138, 549-560.	No			No			2019.0	Weight loss;FTIR	Commercially available HDPE (40 μm in thickness and 0.95 g/cm3 in density) materials were used as substrate in this study. When compared to pure polyethylene, the composition of commercially available HDPE varies by the addition of additives like antioxidants and colorant.		No	No	Plastic debris	Plastic waste dumping site	India	No		
Bacillus sp.	1409	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Bacillus sp.	1409	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Bacillus sp.	1409	PHBH	Kato, C., Honma, A., Sato, S., Okura, T., Fukuda, R., & Nogi, Y. (2019). Poly 3-hydroxybutyrate-co-3-hydroxyhexanoate films can be degraded by the deep-sea microbes at high pressure and low temperature conditions. High Pressure Research, 1-10.	No			No			2019.0	TEM;SEM;Microscopy;Clear zone	PHBH powder			No	Sediment	Marine	Japan	No		
Bacillus sp.	1409	PLA	Kim, M. Y., Kim, C., Moon, J., Heo, J., Jung, S. P., & Kim, J. R. (2017). Polymer film-based screening and isolation of polylactic acid (PLA)-degrading microorganisms. J. Microbiol. Biotechnol, 27(2), 342-349.	No			No			2017.0	Clear zone;SEM;GC	PLA (Grade 4042D, 95.8% L-lactide, 4.2% D-lactide, number average molar mass Mn = 183,000 g/mol)	NatureWorks LLC		No	Digester sludge	Sewage/Sludge	South Korea	No		
Bacillus sp.	1409	HDPE	Kumari, A., Chaudhary, D. R., & Jha, B. (2019). Destabilization of polyethylene and polyvinylchloride structure by marine bacterial strain. Environmental Science and Pollution Research, 26(2), 1507-1516.	No			No			2019.0	FTIR;Weight loss;CO2;SEM;AFM;FTIR	Standard un-plasticized PE films (Goodfellow Cambridge Ltd., UK) were used in this study. HDPE has denser and rigid structure than LDPE due to less branching in polymeric chain.	Goodfellow Cambridge		No	Water	Plastic waste dumping site	India	No		
Bacillus sp.	1409	LDPE	Kumari, A., Chaudhary, D. R., & Jha, B. (2019). Destabilization of polyethylene and polyvinylchloride structure by marine bacterial strain. Environmental Science and Pollution Research, 26(2), 1507-1516.	No			No			2019.0	FTIR;Weight loss;CO2;SEM;AFM;FTIR	Standard un-plasticized PE films (Goodfellow Cambridge Ltd., UK) were used in this study. Similarly, the density and thickness of LDPE and HDPE were 0.92 g cm−3 and 0.95 g cm−3; and 0.015 mm and 0.01 mm, respectively. 	Goodfellow Cambridge		No	Water	Plastic waste dumping site	India	No		
Bacillus sp.	1409	PVC	Kumari, A., Chaudhary, D. R., & Jha, B. (2019). Destabilization of polyethylene and polyvinylchloride structure by marine bacterial strain. Environmental Science and Pollution Research, 26(2), 1507-1516.	No			No			2019.0	FTIR;Weight loss;CO2;SEM;AFM;FTIR	Standard un-plasticized PVC films (Goodfellow Cambridge Ltd., UK) were used in this study. The density and thickness of PVC were 1.4 g cm−3 and 0.2 mm, respectively.	Goodfellow Cambridge		No	Water	Plastic waste dumping site	India	No		
Bacillus sp.	1409	PVA	Liu, Y., Deng, Y., Chen, P., Duan, M., Lin, X., & Zhang, Y. (2019). Biodegradation analysis of polyvinyl alcohol during the compost burial course. Journal of basic microbiology, 59(4), 368-374.	No			No			2019.0	Iodometric analysis;Spectrophotometry	Commercial PVA (degree of polymerization, 1700; degree of alcoholysis, 88 or 99%)	Chang Chun Petrochemical		No	PVF foams	Compost	China	No		
Bacillus sp.	1409	PS Blend	Mohan, A. J., Sekhar, V. C., Bhaskar, T., & Nampoothiri, K. M. (2016). Microbial assisted high impact polystyrene (HIPS) degradation. Bioresource technology, 213, 204-207.	No			No			2016.0	HPLC;NMR;FTIR;TGA;Weight loss;SEM	HIPS with decabromodiphenyl oxide and antimony trioxide was in the form of small white opaque beads provided by CSIR-IIP and the films were made by dissolving 200 mg of beads in 10 ml of chloroform and pouring that into a wide open glass plate and were kept at room temperature for overnight in a fume hood to obtain films with consistent structure. 			No	Soil	Plastic waste dumping site	India	No		
Bacillus sp.	1409	PE	Shovitri, M., Nafi’ah, R., Antika, T. R., Alami, N. H., Kuswytasari, N. D., & Zulaikha, E. (2017). Soil burial method for plastic degradation performed by Pseudomonas PL-01, Bacillus PL-01, and indigenous bacteria. In AIP Conference Proceedings (Vol. 1854, No. 1, p. 020035). AIP Publishing.	No			No			2017.0	FTIR;Weight loss	Black and white plastic kresek and transparent bag for controls 		No	No				No		
Bacillus sp.	1409	LDPE	Usha, R., Sangeetha, T., & Palaniswamy, M. (2011). Screening of polyethylene degrading microorganisms from garbage soil. Libyan agriculture research center journal international, 2(4), 200-204.	No			No			2011.0	Clear zone	Low density polyethylene powder (LDPE)	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	India	No		
Bacillus sp.	1409	PHB	Volova, T. G., Boyandin, A. N., Vasiliev, A. D., Karpov, V. A., Prudnikova, S. V., Mishukova, O. V., ... & Dũng, V. V. (2010). Biodegradation of polyhydroxyalkanoates (PHAs) in tropical coastal waters and identification of PHA-degrading bacteria. Polymer Degradation and Stability, 95(12), 2350-2359.	No			No			2010.0	Weight loss;X-ray;SEM;Clear zone	The tested material was the PHA samples synthesized by the bacterium Ralstonia eutropha.		Yes	No	Plastic debris	Marine	Vietnam	No		
Bacillus sp.	1409	PHBV	Volova, T. G., Boyandin, A. N., Vasiliev, A. D., Karpov, V. A., Prudnikova, S. V., Mishukova, O. V., ... & Dũng, V. V. (2010). Biodegradation of polyhydroxyalkanoates (PHAs) in tropical coastal waters and identification of PHA-degrading bacteria. Polymer Degradation and Stability, 95(12), 2350-2359.	No			No			2010.0	Weight loss;X-ray;SEM;Clear zone	A polymer of 3-hydroxybutyric acid (3-PHB) and a copolymer of 3-hydroxybutyric and 3-hydroxyvaleric acids (3-PHB/3-PHV) containing 11 mol% of hydroxyvalerate, synthesized in the Institute of Biophysics SB RAS, Russia, were used in experiments [34].		Yes	No	Plastic debris	Marine	Vietnam	No		
Bacillus sp.	1409	LDPE	Yang, J., Yang, Y., Wu, W. M., Zhao, J., & Jiang, L. (2014). Evidence of polyethylene biodegradation by bacterial strains from the guts of plastic-eating waxworms. Environmental science & technology, 48(23), 13776-13784.	No			No			2014.0	SEM;AFM;XPS;GPC;MS;Weight loss	Linear low-density PE (LDPE) film (DFDA-9020, 22.5 μm thickness)	SINOPEC Beijing Yanshan Company		No	Waxworm's gut	Animal associated	India	No		
Bacillus sp.	1409	PU	Shah, A. A., Hasan, F., Akhter, J. I., Hameed, A., & Ahmed, S. (2008). Degradation of polyurethane by novel bacterial consortium isolated from soil. Annals of microbiology, 58(3), 381.	No			No			2008.0	Clear zone;CO2;SEM;FTIR	Poly [4,4’-methylenebis (phenyl isocyanate)-alt-1,4-butanediol/poly (butylene adipate)] (Polyurethane, PU) (Sigma-Aldrich, GmbH, Germany) having 1.220 g/ml density and melting temperature about 190 °C, was used in the present study.	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Bacillus sphericus	1421	Nylon	Sudhakar, M., Priyadarshini, C., Doble, M., Murthy, P. S., & Venkatesan, R. (2007). Marine bacteria mediated degradation of nylon 66 and 6. International Biodeterioration & Biodegradation, 60(3), 144-151.	No			No			2007.0	DSC;FTIR;Weight loss;EFM	Commercial grade nylon 6 (Mn ¼ 58,000) fibers (210D) and nylon 66 (Mn ¼ 55,000) pellets (Prime chips)	SRF		No		Marine	India	No		
Bacillus stratosphericus	293386	PES	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly(ethylene succinate) (PESu) (Mn = 4.8 × 10^4, Mw/Mn = 1.9) 	Nippon Shokubai		No				No		
Bacillus subtilis	1423	PP	Aravinthan, A., Arkatkar, A., Juwarkar, A. A., & Doble, M. (2016). Synergistic growth of Bacillus and Pseudomonas and its degradation potential on pretreated polypropylene. Preparative Biochemistry and Biotechnology, 46(2), 109-115.	No			No			2016.0	FTIR;Weight loss;SEM	Commercial PP films (Reliance Industries Ltd., Mumbai, India) of size 1.5 × 1.5 cm and 0.05 mm thickness were used for the present experiments. The PP films were thermally pretreated at 100°C for 8 days in a hot-air oven (PP-TT) or short UV pretreated (PP-UV) at 225 nm for 6 days (Sigma instruments Chennai, India)	RB Industries	No	No	Soil	Plastic waste dumping site	India	No		
Bacillus subtilis	1423	PP	Arkatkar, A., Juwarkar, A. A., Bhaduri, S., Uppara, P. V., & Doble, M. (2010). Growth of Pseudomonas and Bacillus biofilms on pretreated polypropylene surface. International Biodeterioration & Biodegradation, 64(6), 530-536.	No			No			2010.0	Weight loss;SEM;FTIR	Commercial PP films of size 1.5 1.5 cm and 0.05 mm thickness	RB Industries		No	Soil	Plastic waste dumping site	India	No		
Bacillus subtilis	1423	HDPE	Devi, R. S., Ramya, R., Kannan, K., Antony, A. R., & Kannan, V. R. (2019). Investigation of biodegradation potentials of high density polyethylene degrading marine bacteria isolated from the coastal regions of Tamil Nadu, India. Marine pollution bulletin, 138, 549-560.	No			No			2019.0	Weight loss;FTIR	Commercially available HDPE (40 μm in thickness and 0.95 g/cm3 in density) materials were used as substrate in this study. When compared to pure polyethylene, the composition of commercially available HDPE varies by the addition of additives like antioxidants and colorant.		No	No	Plastic debris	Plastic waste dumping site	India	No		
Bacillus subtilis	1423	LDPE	Harshvardhan, K., & Jha, B. (2013). Biodegradation of low-density polyethylene by marine bacteria from pelagic waters, Arabian Sea, India. Marine Pollution Bulletin, 77(1-2), 100-106.	No			No			2013.0	Weight loss;SEM;FTIR	The biodegradation tests were performed on samples of lowdensity polyethylene film (i.e., pieces of polyethylene bags) that had been dried overnight at 60 C, weighed, disinfected (autoclaved at 105 C for 1 h) and added to each flask (approximately 50.0 mg of polyethylene film per flask) containing 50 ml of BH medium		No	No	Water	Marine	India	No		
Bacillus subtilis	1423	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Bacillus subtilis	1423	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Bacillus subtilis	1423	PU	Nakkabi, A., Sadiki, M., Fahim, M., Ittobane, N., IbnsoudaKoraichi, S., & Barkai, H. (2015). Biodegradation of Poly (ester urethane) s by Bacillus subtilis. International Journal of Environmental Research, 9(1), 157-162.	No			No			2015.0	IR;Clear zone;Tensilometer	Impranil DLN	Bayer 	No	No	Wood	Plant associated	Morocco	No		
Bacillus subtilis	1423	PES	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly(ethylene succinate) (PESu) (Mn = 4.8 × 10^4, Mw/Mn = 1.9) 	Nippon Shokubai		No				No		
Bacillus subtilis	1423	PE	Vimala, P. P., & Mathew, L. (2016). Biodegradation of Polyethylene using Bacillus subtilis. Procedia Technology, 24, 232-239.	No			No			2016.0	Clear zone;Weight loss;FTIR	Polyethylene (PE) films of two thicknesses – 18u LDPE (Low density Polyethylene) and 41u HDPE (High density Polyethylene)-were purchased. PE films were cut in required size of approx. 2 cm x 2 cm and they were subjected to UV treatment for 72 hours.			No	Culture collection	Culture collection		No		
Bacillus thuringiensis	1428	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;SEM;FTIR;Tensilometer	LDPE, type “FGNX23-D022”;Bionolle (type #3001)	POLICHEM		No	Soil	Soil	Poland	No		
Bacillus vietnamensis	218284	LDPE	Rafiq, S., Fathima, F., Shahina, S. J., & Ramesh, K. V. (2018). Biodegradation of Low Density Polyethylene (LDPE) by Halophilic Bacteria Isolated from Solar Saltpans, Kovalam, Chennai. Nature Environment and Pollution Technology, 17(4), 1367-1371.	No			No			2018.0	Clear zone;SEM	LDPE sheets			No	Water	Others	India	No		
Bacteroides sp.	29523	PEG	Dwyer, D. F., & Tiedje, J. M. (1986). Metabolism of polyethylene glycol by two anaerobic bacteria, Desulfovibrio desulfuricans and a Bacteroides sp. Appl. Environ. Microbiol., 52(4), 852-856.	No			No			1986.0	Chromatography;GC				No	Sludge	Sewage/Sludge	USA	No		
Bjerkandera adusta	5331	Nylon	Friedrich, J., Zalar, P., Mohorčič, M., Klun, U., & Kržan, A. (2007). Ability of fungi to degrade synthetic polymer nylon-6. Chemosphere, 67(10), 2089-2095.	No			No			2007.0	SEM;DSC;HPLC;Clear zone	The composition was as follows: 1.0 g nylon-6 powder with particles <0.5 mm diameter (washed with distilled water to eliminate monomers and soluble oligomers).			No	Culture collection	Culture collection		No		
Bjerkandera adusta	5331	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Bjerkandera adusta	5331	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Bordetella petrii	94624	PLA	Kim, M. N., & Park, S. T. (2010). Degradation of poly (L‐lactide) by a mesophilic bacterium. Journal of applied polymer science, 117(1), 67-74.	No			No			2010.0	Weight loss;CO2;Clear zone;SEM;Tensilometer	PLAs with weight-average molecular weights (Mw’s) of 5000, 11,000, and 34,000 were synthesized, whereas PLA with a Mw of 256,000 g/mol was obtained in pellet form from NatureWorks (Minneapolis, MN).		Yes	No	Soil	Soil	South Korea	No		
Brevibacillus borstelensis	45462	LDPE	Muhonja, C. N., Makonde, H., Magoma, G., & Imbuga, M. (2018). Biodegradability of polyethylene by bacteria and fungi from Dandora dumpsite Nairobi-Kenya. PloS one, 13(7), e0198446.	No			No			2018.0	Weight loss;FTIR;MS	LDPE powder			No	Soil	Plastic waste dumping site	Kenya	No		
Brevibacillus brevis	1393	PCL	Abou-Zeid, D. M., Müller, R. J., & Deckwer, W. D. (2001). Degradation of natural and synthetic polyesters under anaerobic conditions. Journal of biotechnology, 86(2), 113-126.	No			No			2001.0	Weight loss;Clear zone;CO2	Poly(o-caprolactone) (PCL) 	Polysciences		No	Sludge	Sewage/Sludge	Germany	No		
Brevibacillus parabrevis	54914	LDPE	Pramila, R., Padmavathy, K., Ramesh, K. V., & Mahalakshmi, K. (2012). Brevibacillus parabrevis, Acinetobacter baumannii and Pseudomonas citronellolis-Potential candidates for biodegradation of low density polyethylene (LDPE). African Journal of Bacteriology Research, 4(1), 9-14.	No			No			2012.0	CO2	LDPE sheets			No	Soil	Landfill	India	No		
Brevibacillus reuszeri	54915	PHA	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHA (BIOPOL-D400P-PB36)	Monsanto		No	Soil	Soil	Japan	No		
Brevibacillus sp.	1882945	PCL	Adıgüzel, A. O., & Tunçer, M. (2017). Purification and characterization of cutinase from Bacillus sp. KY0701 isolated from plastic wastes. Preparative Biochemistry and Biotechnology, 47(9), 925-933.	No			No			2017.0	Weight loss;Clear zone	Plastic Waste		No	No	Plastic debris	Soil	Turkey	No		
Brevibacillus sp.	1882945	PE	Nanda, S., & Sahu, S. S. (2010). Biodegradability of polyethylene by Brevibacillus, Pseudomonas, and Rhodococcus spp. New York Science Journal, 3(7), 95-98.	No			No			2010.0	Clear zone	General grade polyethylene employed for commercial grocery carriage purpose was used to investigate its biodegradability nature.		No	No	Soil	Plastic waste dumping site	India	No		
Brevundimonas diminuta	293	PS	Sekhar, V. C., Nampoothiri, K. M., Mohan, A. J., Nair, N. R., Bhaskar, T., & Pandey, A. (2016). Microbial degradation of high impact polystyrene (HIPS), an e-plastic with decabromodiphenyl oxide and antimony trioxide. Journal of hazardous materials, 318, 347-354.	No			No			2016.0	FTIR;TGA;NMR;Weight loss;HPLC	Indian Institute of petroleum (IIP), CSIR provided four types of e-plastic samples. These are virgin plastics samples used in electric and electronic appliance and are specially prepared for research purpose and not available commercially. The samples were coded as (1) AMS 01 (HIPS with decabromodiphenyl oxide or ether and antimony trioxide) (2) AMS 01S (HIPS with decabromodiphenyl oxide or ether) (3) AMS 02 (HIPS with decabromodiphenyl ethane and antimony trioxide) and (4) AMS 02S (HIPS with decabromodiphenyl ethane).	Indian Institute of petroleum (IIP), CSIR	No	No	Plastic debris	Plastic waste dumping site	India	No		
Brevundimonas vesicularis	41276	Nylon	Sudhakar, M., Priyadarshini, C., Doble, M., Murthy, P. S., & Venkatesan, R. (2007). Marine bacteria mediated degradation of nylon 66 and 6. International Biodeterioration & Biodegradation, 60(3), 144-151.	No			No			2007.0	DSC;FTIR;Weight loss;EFM	Commercial grade nylon 6 (Mn ¼ 58,000) fibers (210D) and nylon 66 (Mn ¼ 55,000) pellets (Prime chips)	SRF		No		Marine	India	No		
Burkholderia cepacia	292	PLA Blend	Wu, C. S. (2009). Renewable resource-based composites of recycled natural fibers and maleated polylactide bioplastic: Characterization and biodegradability. Polymer Degradation and Stability, 94(7), 1076-1084.	No			No			2009.0	SEM;Weight loss;GPC	The polylactide was supplied by Cargill–Dow, and was composed of 95% L-lactide and 5% meso-lactide with a weight average molecular weight (Mw) of 9.73x10^4, a number average molecular weight (Mn) of 5.05x10^4, a polydispersity index of 1.93, an intrinsic viscosity (h) of 2.53 dL/g, and a melt-flow index of 18.6 g per 10 min. Maleic anhydride, obtained from Sigma–Aldrich, was purified before use by re-crystallization from chloroform. Benzoyl peroxide, used as an initiator, was also supplied by Sigma–Aldrich and was purified by dissolution in chloroform and re-precipitation in methanol. GCF was obtained from Pingtung. PLA-g-MA was synthesized according to procedures described in previous work [28], and had Mw of 9.37 _ 104, a Mn of 5.32 _ 104, a polydisperity index of 2.05, an h of 2.43 dL/g, and a melt-flow index of 19.6 g per 10 min. The grafting percentage of PLA-g-MA was approximately 0.96 wt%. At such a low degree of grafting, the structure of PLA-g-MA was not noticeably different than that of PLA. A slight decrease in molecular weight and intrinsic viscosity, as well as a slight increase in melt-flow index, was apparent in PLA-g-MA relative to PLA and was attributed to bond cracking induced by the grafting reaction.		No	No	Culture collection	Culture collection		No		
Burkholderia gladioli	28095	PU	Peng, Y. H., Shih, Y. H., Lai, Y. C., Liu, Y. Z., Liu, Y. T., & Lin, N. C. (2014). Degradation of polyurethane by bacterium isolated from soil and assessment of polyurethanolytic activity of a Pseudomonas putida strain. Environmental Science and Pollution Research, 21(16), 9529-9537.	No			No			2014.0	FTIR;Clear zone	Impranil DLN	Bayer 	No	No			Taiwan	No		
Burkholderia sp.	36773	PHA	Boyandin, A. N., Prudnikova, S. V., Karpov, V. A., Ivonin, V. N., Đỗ, N. L., Nguyễn, T. H., ... & Volova, T. G. (2013). Microbial degradation of polyhydroxyalkanoates in tropical soils. International Biodeterioration & Biodegradation, 83, 77-84.	No			No			2013.0	Weight loss;GPC;X-ray	The polymers were synthesized in Wautersia eutropha B5786 microbial culture (the strain is registered in the Russian Collection of Industrial Microorganisms).			No	Soil	Soil	Vietnam	No		
Burkholderia vietnamiensis	60552	PTS	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PTS (BIONOLLE-1020)	Showa Denko		No	Soil	Soil	Japan	No		
Candida rugosa	5481	PU	Zafar, U., Nzeram, P., Langarica-Fuentes, A., Houlden, A., Heyworth, A., Saiani, A., & Robson, G. D. (2014). Biodegradation of polyester polyurethane during commercial composting and analysis of associated fungal communities. Bioresource technology, 158, 374-377.	No			No			2014.0	Clear zone	Impranil	Bayer 	No	No	PU coupons	Compost	UK	No		
Cellulosimicrobium sp.	1871614	PHB	Tachibana, Y., Hayashi, S., Suzuki, M., Soulenthone, P., Tachibana, Y., & Kasuya, K. I. (2017). Identification of Cellulosimicrobium sp., a poly (3-hydroxybutyrate)-degrading bacterium isolated from washed rind cheese, Pont-l’évêque lait cru. Journal of Polymer Research, 24(10), 159.	No			No			2017.0	SEM;Clear zone;Weight loss	Poly(3-hydroxybutyrate) (P(3HB))	Mitsubishi Gas Chemical		No	Washed rind cheese	Others		No		
Cellulosimicrobium sp.	1871614	PHBV	Tachibana, Y., Hayashi, S., Suzuki, M., Soulenthone, P., Tachibana, Y., & Kasuya, K. I. (2017). Identification of Cellulosimicrobium sp., a poly (3-hydroxybutyrate)-degrading bacterium isolated from washed rind cheese, Pont-l’évêque lait cru. Journal of Polymer Research, 24(10), 159.	No			No			2017.0	SEM;Clear zone;Weight loss	poly(3-hydroxybutyrateco- 3-hydroxyvalerate) (PHBV)	Nippon Shokubai		No	Washed rind cheese	Others		No		
Cephalosporium sp.	1981612	HDPE	Chaudhary, A. K., & Vijayakumar, R. P. (2018). Effect of chemical treatment on biological degradation of high-density polyethylene (HDPE). Environment, Development and Sustainability, 1-12.	No			No			2018.0	Weight loss;FTIR;SEM;X-ray	Pre-treated HDPE flms		No	No		Culture collection		No		
Cephalosporium sp.	1981612	PHB	Matavulj, M., & Molitoris, H. P. (1992). Fungal degradation of polyhydroxyalkanoates and a semiquantitative assay for screening their degradation by terrestrial fungi. FEMS microbiology reviews, 9(2-4), 323-331.	No			No			1992.0	Clear zone;Weight loss	Granulated and powdered BIOPOL	ICI, UK		No	Culture collection	Culture collection		No		
Chaetomium globosum	38033	PCL	Vivi, V. K., Martins-Franchetti, S. M., & Attili-Angelis, D. (2019). Biodegradation of PCL and PVC: Chaetomium globosum (ATCC 16021) activity. Folia microbiologica, 64(1), 1-7.	No			No			2019.0	OM;Weight loss;SEM	Poly (ε-caprolactone) (PCL): (Solvay-K6800) -M: 85,000 g/mol	Sigma Aldrich		No	Culture collection	Culture collection		No		
Chaetomium globosum	38033	PVC	Vivi, V. K., Martins-Franchetti, S. M., & Attili-Angelis, D. (2019). Biodegradation of PCL and PVC: Chaetomium globosum (ATCC 16021) activity. Folia microbiologica, 64(1), 1-7.	No			No			2019.0	OM;Weight loss;SEM	Poly (vinyl chloride) (PVC): (Sigma-P-9401) - M: 73,491 g/mol	Sigma Aldrich		No	Culture collection	Culture collection		No		
Chitinimonas sp.	1934313	PHBH	Morohoshi, T., Oi, T., Aiso, H., Suzuki, T., Okura, T., & Sato, S. (2018). Biofilm formation and degradation of commercially available biodegradable plastic films by bacterial consortiums in freshwater environments. Microbes and environments, ME18033.	No			No			2018.0	Clear zone;Weight loss				No	Water	River/Lake	Japan	No		
Chryseomonas luteola	47886	PHB	Tansengco, M., & Dogma Jr, I. (1999). Microbial degradation of poly‐β‐hydroxybutyrate using landfill soils. Acta biotechnologica, 19(3), 191-203.	No			No			1999.0	SEM;TOC;Weight loss;Clear zone	Samples of poly-&hydroxybutyrate or PHB granules (-O-CH(CH3)-CH2-CO-}n exhibiting an average molecular weight (Mw) of 9.4 x10^5, a melting temperature of 170 °C and a purity of 98%. 	Mitsubishi Gas Chemical	Yes	No	Soil	Landfill	Philippines	No		
Chrysosporium sp.	40412	PC	Arefian, M., Zia, M., Tahmourespour, A., & Bayat, M. (2013). Polycarbonate biodegradation by isolated molds using clear-zone and atomic force microscopic methods. International Journal of Environmental Science and Technology, 10(6), 1319-1324.	No			No			2013.0	Clear zone;AFM				No	Soil	Soil	Iran	No		
Citrobacter amalonaticus	35703	LDPE	Montazer, Z., Habibi-Najafi, M. B., Mohebbi, M., & Oromiehei, A. (2018). Microbial degradation of UV-pretreated low-density polyethylene films by novel polyethylene-degrading bacteria isolated from plastic-dump soil. Journal of Polymers and the Environment, 26(9), 3613-3625.	No			No			2018.0	FTIR;SEM;Microscopy;Weight loss;CG-FIT	Low density polyethylene (Poliran LF0200 grade) granules and film (10 μm thickness; 99.95% purity without any additives and plasticizers) used for pasteurized milk packaging were supplied by Iran Polymer and Petrochemical Institute (IPPI)	Polymer and Petrochemical Institute (IPPI)	Yes	No	Soil	Landfill	Iran	No		
Citrobacter sedlakii	67826	PS	Sekhar, V. C., Nampoothiri, K. M., Mohan, A. J., Nair, N. R., Bhaskar, T., & Pandey, A. (2016). Microbial degradation of high impact polystyrene (HIPS), an e-plastic with decabromodiphenyl oxide and antimony trioxide. Journal of hazardous materials, 318, 347-354.	No			No			2016.0	FTIR;TGA;NMR;Weight loss;HPLC	Indian Institute of petroleum (IIP), CSIR provided four types of e-plastic samples. These are virgin plastics samples used in electric and electronic appliance and are specially prepared for research purpose and not available commercially. The samples were coded as (1) AMS 01 (HIPS with decabromodiphenyl oxide or ether and antimony trioxide) (2) AMS 01S (HIPS with decabromodiphenyl oxide or ether) (3) AMS 02 (HIPS with decabromodiphenyl ethane and antimony trioxide) and (4) AMS 02S (HIPS with decabromodiphenyl ethane).	Indian Institute of petroleum (IIP), CSIR	No	No	Plastic debris	Plastic waste dumping site	India	No		
Cladosporium asperulatum	887085	PU	Álvarez-Barragán, J., Domínguez-Malfavón, L., Vargas-Suárez, M., González-Hernández, R., Aguilar-Osorio, G., & Loza-Tavera, H. (2016). Biodegradative activities of selected environmental fungi on a polyester polyurethane varnish and polyether polyurethane foams. Appl. Environ. Microbiol., 82(17), 5225-5235.	No			No			2016.0	FTIR;MS;SEM;Clear zone	Impranil	Bayer 		No			Mexico	No		
Cladosporium cladosporioides	29917	O-PE	Bonhomme, S., Cuer, A., Delort, A. M., Lemaire, J., Sancelme, M., & Scott, G. (2003). Environmental biodegradation of polyethylene. Polymer Degradation and Stability, 81(3), 441-452.	No			No			2003.0	SEM;FTIR;GPC	Degradable polyethylene was a green film (LC) containing TDPA1 (thickness 36_2 mm)	EPI	No	No	Culture collection	Culture collection		No		
Cladosporium cladosporioides	29917	PET	Breuker, M., McNamara, C., Young, L., Perry, T., Young, A., & Mitchell, R. (2003). Fungal growth on synthetic cloth from Apollo spacesuits. Annals of microbiology, 53(1), 47-54.	No			No			2003.0	SEM;Weight loss	Non-woven Dacron (a polyester synthesized from terephthalic acid and ethylene glycol), were removed from samples of Apollo spacesuits.			No	Spacesuit	Others	USA	No		
Cladosporium cladosporioides	29917	PU	Brunner, I., Fischer, M., Rüthi, J., Stierli, B., & Frey, B. (2018). Ability of fungi isolated from plastic debris floating in the shoreline of a lake to degrade plastics. PloS one, 13(8), e0202047.	No			No			2018.0	Clear zone	Impranil	Bayer 	No	No	Plastic debris	River/Lake	Switzerland	No		
Cladosporium cladosporioides	29917	PE	Koutny, M., Sancelme, M., Dabin, C., Pichon, N., Delort, A. M., & Lemaire, J. (2006). Acquired biodegradability of polyethylenes containing pro-oxidant additives. Polymer degradation and stability, 91(7), 1495-1503.	No			No			2006.0	ATR-FTIR;SEC;Microscopy;NMR	The material samples were transparent HDPE film 20 mm thick and transparent LDPE film 60 mm thick. Both films contained iron photo-inducer, different from the Scott/Gilead compound (Schulman e Bornen, Belgium) supplying radicals through a photo-redox process and an organometallic type thermo-inducer (EPI, Vancouver, Canada) catalysing the primary hydroperoxide decomposition. Both additives were present in both films. 		No	No	Culture collection	Culture collection		No		
Cladosporium montecillanum	1758471	PU	Álvarez-Barragán, J., Domínguez-Malfavón, L., Vargas-Suárez, M., González-Hernández, R., Aguilar-Osorio, G., & Loza-Tavera, H. (2016). Biodegradative activities of selected environmental fungi on a polyester polyurethane varnish and polyether polyurethane foams. Appl. Environ. Microbiol., 82(17), 5225-5235.	No			No			2016.0	FTIR;MS;SEM;Clear zone	Impranil	Bayer 		No			Mexico	No		
Cladosporium pseudocladosporioides	887100	PU	Álvarez-Barragán, J., Domínguez-Malfavón, L., Vargas-Suárez, M., González-Hernández, R., Aguilar-Osorio, G., & Loza-Tavera, H. (2016). Biodegradative activities of selected environmental fungi on a polyester polyurethane varnish and polyether polyurethane foams. Appl. Environ. Microbiol., 82(17), 5225-5235.	No			No			2016.0	FTIR;MS;SEM;Clear zone	Impranil	Bayer 		No			Mexico	No		
Cladosporium sp.	1707700	PU	Crabbe, J. R., Campbell, J. R., Thompson, L., Walz, S. L., & Schultz, W. W. (1994). Biodegradation of a colloidal ester-based polyurethane by soil fungi. International Biodeterioration & Biodegradation, 33(2), 103-113.	No			No			1994.0	Clear zone	The substrate used for all degradation experiments was an ester-based polyurethane (PU), and was obtained as a water-dispersed colloid (Impranil DLN, Miles Inc., Pittsburgh, PA, USA).	Miles	No	No	Soil	Soil	USA	No		
Cladosporium sp.	1707700	PHB	Matavulj, M., & Molitoris, H. P. (1992). Fungal degradation of polyhydroxyalkanoates and a semiquantitative assay for screening their degradation by terrestrial fungi. FEMS microbiology reviews, 9(2-4), 323-331.	No			No			1992.0	Clear zone;Weight loss	Granulated and powdered BIOPOL	ICI, UK		No	Culture collection	Culture collection		No		
Cladosporium sp.	1707700	PBSA	Yamamoto-Tamura, K., Hoshino, Y. T., Tsuboi, S., Huang, C., Kishimoto-Mo, A. W., Sameshima-Yamashita, Y., & Kitamoto, H. (2020). Fungal community dynamics during degradation of poly (butylene succinate-co-adipate) film in two cultivated soils in Japan. Bioscience, Biotechnology, and Biochemistry, 1-11.	No			No			2020.0	Luminance	PBSA films used in this study were composed of Bionolle® 3001 (Showa Denko K. K., Tokyo, Japan)	Showa Denko	No	No	Soil	Soil	Japan	No		
Cladosporium sphaerospermum	92950	PLA	Nair, N. R., Sekhar, V. C., & Nampoothiri, K. M. (2016). Augmentation of a microbial consortium for enhanced polylactide (PLA) degradation. Indian journal of microbiology, 56(1), 59-63.	No			No			2016.0	Weight loss;SEM;Spectrophotometry	Commercial grade PLA with molecular weight of 85,000–160,000	Sigma Aldrich	Yes	No			India	No		
Cladosporium sphaerospermum	92950	PLA	Nair, N. R., Sekhar, V. C., & Nampoothiri, K. M. (2016). Augmentation of a microbial consortium for enhanced polylactide (PLA) degradation. Indian journal of microbiology, 56(1), 59-63.	No			No			2016.0	Weight loss;SEM;Spectrophotometry;Clear zone	Commercial grade PLA with molecular weight of 85,000–160,000	Sigma Aldrich	Yes	No			India	No		
Cladosporium subcinereum	1970644	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Cladosporium subcinereum	1970644	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Cladosporium tenuissimum	70808	PU	Álvarez-Barragán, J., Domínguez-Malfavón, L., Vargas-Suárez, M., González-Hernández, R., Aguilar-Osorio, G., & Loza-Tavera, H. (2016). Biodegradative activities of selected environmental fungi on a polyester polyurethane varnish and polyether polyurethane foams. Appl. Environ. Microbiol., 82(17), 5225-5235.	No			No			2016.0	FTIR;MS;SEM;Clear zone	Impranil	Bayer 		No			Mexico	No		
Clonostachys rosea	29856	PU	Barratt, S. R., Ennos, A. R., Greenhalgh, M., Robson, G. D., & Handley, P. S. (2003). Fungi are the predominant micro‐organisms responsible for degradation of soil‐buried polyester polyurethane over a range of soil water holding capacities. Journal of applied microbiology, 95(1), 78-85.	No			No			2003.0	Clear zone;SEM;Tensilometer				No	Plastic debris	Soil		No		
Clonostachys rosea	29856	PCL	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	 PCL pellets were purchased from TRESNO (Poland)	TRESNO		No	Soil	Soil	Svalbard	No		
Clostridium acetobutylicum	1488	PCL	Abou-Zeid, D. M., Müller, R. J., & Deckwer, W. D. (2001). Degradation of natural and synthetic polyesters under anaerobic conditions. Journal of biotechnology, 86(2), 113-126.	No			No			2001.0	Clear zone;Weight loss;Spectrophotometry	Poly(o-caprolactone) (PCL) from Polysciences, Inc. (Warrington, USA).	Polysciences		No	Film	Sewage/Sludge	Germany	No		
Clostridium acetobutylicum	1488	PHBV	Abou-Zeid, D. M., Müller, R. J., & Deckwer, W. D. (2001). Degradation of natural and synthetic polyesters under anaerobic conditions. Journal of biotechnology, 86(2), 113-126.	No			No			2001.0	Clear zone;Weight loss;Spectrophotometry	The bacterial poly(b-hydroxybutyrate-co-11.6%-b-hydroxyvalerate) (PHBV) were purchased from ICI (Billingham, UK) as Biopol BX G08 and Biopol BX P027, respectively.	ICI, UK		No	Film	Sewage/Sludge	Germany	No		
Clostridium botulinum	1491	PCL	Abou-Zeid, D. M., Müller, R. J., & Deckwer, W. D. (2001). Degradation of natural and synthetic polyesters under anaerobic conditions. Journal of biotechnology, 86(2), 113-126.	No			No			2001.0	Clear zone;Weight loss;Spectrophotometry	Poly(o-caprolactone) (PCL) from Polysciences, Inc. (Warrington, USA).	Polysciences		No	Film	Sewage/Sludge	Germany	No		
Clostridium botulinum	1491	PHBV	Abou-Zeid, D. M., Müller, R. J., & Deckwer, W. D. (2001). Degradation of natural and synthetic polyesters under anaerobic conditions. Journal of biotechnology, 86(2), 113-126.	No			No			2001.0	Clear zone;Weight loss;Spectrophotometry	The bacterial poly(b-hydroxybutyrate-co-11.6%-b-hydroxyvalerate) (PHBV) were purchased from ICI (Billingham, UK) as Biopol BX G08 and Biopol BX P027, respectively.	ICI, UK		No	Film	Sewage/Sludge	Germany	No		
Cochliobolus sp.	1756142	PVC	Sumathi, T., Viswanath, B., Sri Lakshmi, A., & SaiGopal, D. V. R. (2016). Production of laccase by Cochliobolus sp. isolated from plastic dumped soils and their ability to degrade low molecular weight PVC. Biochemistry research international, 2016.	No			No			2016.0	FTIR;SEM;MS;Clear zone	Instead of carbon source, polyvinyl chloride (sigma-Aldrich) was used as a carbon source (3 g/100mL) on agar plate for 3 months and with one-year time incubation in broth.	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	India	No		
Comamonas acidovorans	80866	PU	Nakajima-Kambe, T., Onuma, F., Kimpara, N., & Nakahara, T. (1995). Isolation and characterization of a bacterium which utilizes polyester polyurethane as a sole carbon and nitrogen source. FEMS microbiology letters, 129(1), 39-42.	No			No			1995.0	Weight loss;HPLC	PURs were synthesized by reacting poly(propylene glycol)s or poly(diethylene glycol adipate)s with 2,4-tolylene diisocyanate under anhydrous condition as described by Darby and Kaplan [l]. The properties of the synthesized PURs are shown in Table 1.		Yes	No	Soil	Soil	Japan	No		
Comamonas sp.	34028	PE	Peixoto, J., Silva, L. P., & Krüger, R. H. (2017). Brazilian Cerrado soil reveals an untapped microbial potential for unpretreated polyethylene biodegradation. Journal of hazardous materials, 324, 634-644.	No			No			2017.0	ATR-FTIR;SEM;Spectrophotometry;Clear zone	0.1% ultra-high molecular weight PE powder (Sigma Aldrich, USA)	Sigma Aldrich	Yes	No	Plastic debris	Soil	Brazil	No		
Comamonas sp.	34028	PHB	Quinteros, R., Goodwin, S., Lenz, R. W., & Park, W. H. (1999). Extracellular degradation of medium chain length poly (β-hydroxyalkanoates) by Comamonas sp. International journal of biological macromolecules, 25(1-3), 135-143.	No			No			1999.0	Clear zone;Spectrophotometry;CO2	The PHB and PHBV used in this study were purchased from Aldrich (Milwaukee, WI)	Sigma Aldrich	Yes	No	Compost	Compost		No		
Comamonas sp.	34028	PHBV	Quinteros, R., Goodwin, S., Lenz, R. W., & Park, W. H. (1999). Extracellular degradation of medium chain length poly (β-hydroxyalkanoates) by Comamonas sp. International journal of biological macromolecules, 25(1-3), 135-143.	No			No			1999.0	Clear zone;Spectrophotometry;CO2	The PHB and PHBV used in this study were purchased from Aldrich (Milwaukee, WI)	Sigma Aldrich	Yes	No	Compost	Compost		No		
Comamonas sp.	34028	PHO	Quinteros, R., Goodwin, S., Lenz, R. W., & Park, W. H. (1999). Extracellular degradation of medium chain length poly (β-hydroxyalkanoates) by Comamonas sp. International journal of biological macromolecules, 25(1-3), 135-143.	No			No			1999.0	Clear zone;Spectrophotometry;CO2	All other PHAs were synthesized by Pseudomonas oleo6orans grown in the laboratory on E* medium [13] with appropriate carbon sources.		Yes	No	Compost	Compost		No		
Comamonas testosteroni	285	PHB	Martínez-Tobón, D. I., Gul, M., Elias, A. L., & Sauvageau, D. (2018). Polyhydroxybutyrate (PHB) biodegradation using bacterial strains with demonstrated and predicted PHB depolymerase activity. Applied microbiology and biotechnology, 102(18), 8049-8067.	No			No			2018.0	Clear zone;Weight loss	PHB pellets (BRS Bulk Bio-pellets, Bulk Reef Supply, Golden Valley, USA) and acetic acid (Fisher Scientific) were used to produce PHB films by solvent casting as described by Anbukarasu et al. (2015).	Bulk Reef Supply	Yes	No		Culture collection		No		
Comamonas testosteroni	285	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Comamonas testosteroni	285	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Cordyceps confragosa	2714763	LDPE	Karlsson, S., Ljungquist, O., & Albertsson, A. C. (1988). Biodegradation of polyethylene and the influence of surfactants. Polymer degradation and stability, 21(3), 237-250.	No			No			1988.0	14C;CO2	LDPE labelled with 14C was produced by Imperial Chemical Industries, London and generously supplied by Akerlund & Rausing AB, Lund, Sweden. The polymer was made from ethylene with a rather high concentration of 14 C using a high pressure free radical process. This polymer was mixed with another batch of similar commercial polymer to yield a polymer with a fairly low concentration of 14C. This gave a distribution of 14C in which the labelled carbon was located in a few molecules. The density of the LDPE granules was 0.922 g/cm^3, and the molecular weights were M. -- 18.200 and M w = 84.000. Films, 0.16 mm thick, were made by heating and moulding the LDPE granules. One set of polyethylene samples (NDPE) contained 5% of an additive consisting of palmitate iron carboxylate-Fe(III)hydroxide to increase the photo-chemical degradation rate. A parallel set of samples contained no additive (PE).	Akerlund & Rausing AB	Yes	No				No		
Cordyceps farinosa	89141	PHB	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	PHB was provided by ICI in powder form (200 mm) and its weight average molecular weight was 470,000 g/ mol.	ICI, UK		No	Plastic debris	Soil	South Korea	No		
Cordyceps farinosa	89141	PETG	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	SG is a biodegradable aliphatic polyester, made of succinic acid, adipic acid, butanediol and ethylene glycol. It was donated by SKI in powder form (200 mm) with a melt index of 30 g/10 min at 190C.	SKI		No	Plastic debris	Soil	South Korea	No		
Cordyceps farinosa	89141	PHBV	Sang, B. I., Hori, K., Tanji, Y., & Unno, H. (2002). Fungal contribution to in situ biodegradation of poly (3-hydroxybutyrate-co-3-hydroxyvalerate) film in soil. Applied microbiology and biotechnology, 58(2), 241-247.	No			No			2002.0	Weight loss;SEM;Clear zone	PHBV containing 12% 3-hydroxyvalerate (3HV) in powder form	Sigma Aldrich		No	Soil	Soil	Japan	No		
Cordyceps fumosorosea	114497	PBS	Ishii, N., Inoue, Y., Tagaya, T., Mitomo, H., Nagai, D., & Kasuya, K. I. (2008). Isolation and characterization of poly (butylene succinate)-degrading fungi. Polymer Degradation and Stability, 93(5), 883-888.	No			No			2008.0	Clear zone;Weight loss;Microscopy;SEM;GPC;MS	PBSu (1,4-Butanediol/succinic acid;Tm 117;Mw 17.6x10-4)	Showa Denko		No	Soil	Soil	Japan	No		
Cordyceps fumosorosea	114497	PCL	Ishii, N., Inoue, Y., Tagaya, T., Mitomo, H., Nagai, D., & Kasuya, K. I. (2008). Isolation and characterization of poly (butylene succinate)-degrading fungi. Polymer Degradation and Stability, 93(5), 883-888.	No			No			2008.0	Clear zone;Weight loss;Microscopy;SEM;GPC;MS	PCL (6-Hydroxyhexanoic acid; Tm 62; Mw 6.4x10^-4)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Corynebacterium sp.	1720	PU	Kay, M. J., Morton, L. H. G., & Prince, E. L. (1991). Bacterial degradation of polyester polyurethane. International biodeterioration, 27(2), 205-222.	No			No			1991.0	Microscopy;Tensilometer;Weight loss	Biocide-free, dumb-bell shaped polyester polyurethane foam test pieces were used for these investigations			No	Plastic debris	Soil	UK	No		
Corynebacterium sp.	1720	PU	Shah, A. A., Hasan, F., Akhter, J. I., Hameed, A., & Ahmed, S. (2008). Degradation of polyurethane by novel bacterial consortium isolated from soil. Annals of microbiology, 58(3), 381.	No			No			2008.0	Clear zone;CO2;SEM;FTIR	Poly [4,4’-methylenebis (phenyl isocyanate)-alt-1,4-butanediol/poly (butylene adipate)] (Polyurethane, PU) (Sigma-Aldrich, GmbH, Germany) having 1.220 g/ml density and melting temperature about 190 °C, was used in the present study.	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Cupriavidus necator	106590	LDPE	Montazer, Z., Habibi Najafi, M. B., & Levin, D. B. (2018). Microbial degradation of low-density polyethylene and synthesis of polyhydroxyalkanoate polymers. Canadian journal of microbiology, 65(3), 224-234.	No			No			2018.0	Weight loss;SEM;GC;FTIR	LDPE powder, with a particle size of 400 μm or less (screen retention of 50 mesh is 4.4%) and a molecular weight range between 20,000 and 150,000, was supplied by Alfa-Asar Company (USA; CAS number 9002-88-4). According to the supplier, the Feedstock Melt Index and density were 3.50 g/10 min (at 190 oC and 2.16 kg load) and 0.9227 g/cm3, respectively. According to supplier’s data sheet, the polymer was pure and free of stabilizing agents. The PE particles sterilized by exposure to UV-light (254 nm) for 1 hour while mixing.	Alfa-Asar Company		No	Culture collection	Culture collection		No		
Cupriavidus sp.	1873897	PHA	Boyandin, A. N., Prudnikova, S. V., Karpov, V. A., Ivonin, V. N., Đỗ, N. L., Nguyễn, T. H., ... & Volova, T. G. (2013). Microbial degradation of polyhydroxyalkanoates in tropical soils. International Biodeterioration & Biodegradation, 83, 77-84.	No			No			2013.0	Weight loss;GPC;X-ray	The polymers were synthesized in Wautersia eutropha B5786 microbial culture (the strain is registered in the Russian Collection of Industrial Microorganisms).			No	Soil	Soil	Vietnam	No		
Cupriavidus sp.	1873897	PHB	Martínez-Tobón, D. I., Gul, M., Elias, A. L., & Sauvageau, D. (2018). Polyhydroxybutyrate (PHB) biodegradation using bacterial strains with demonstrated and predicted PHB depolymerase activity. Applied microbiology and biotechnology, 102(18), 8049-8067.	No			No			2018.0	Clear zone;Weight loss	PHB pellets (BRS Bulk Bio-pellets, Bulk Reef Supply, Golden Valley, USA) and acetic acid (Fisher Scientific) were used to produce PHB films by solvent casting as described by Anbukarasu et al. (2015).	Bulk Reef Supply	Yes	No		Culture collection		No		
Curvularia protuberata	671092	PETG	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	SG is a biodegradable aliphatic polyester, made of succinic acid, adipic acid, butanediol and ethylene glycol. It was donated by SKI in powder form (200 mm) with a melt index of 30 g/10 min at 190C.	SKI		No	Plastic debris	Soil	South Korea	No		
Curvularia senegalensis	215132	PU	Crabbe, J. R., Campbell, J. R., Thompson, L., Walz, S. L., & Schultz, W. W. (1994). Biodegradation of a colloidal ester-based polyurethane by soil fungi. International Biodeterioration & Biodegradation, 33(2), 103-113.	No			No			1994.0	Clear zone	The substrate used for all degradation experiments was an ester-based polyurethane (PU), and was obtained as a water-dispersed colloid (Impranil DLN, Miles Inc., Pittsburgh, PA, USA).	Miles	No	No	Soil	Soil	USA	No		
Debaryomyces hansenii	4959	PHB	Gonda, K. E., Jendrossek, D., & Molitoris, H. P. (2000). Fungal degradation of the thermoplastic polymer poly-ß-hydroxybutyric acid (PHB) under simulated deep sea pressure. In Life at Interfaces and Under Extreme Conditions (pp. 173-183). Springer, Dordrecht.	No			No			2000.0	Clear zone;Spectrophotometry	PHB was isolated from sodium-gluconate-grown cells of the bacterium Ralstonia eutropha HI6 by sodium-hypochlorite treatment followed by acetone-ether (2: I, v/v) extraction.		Yes	No	Water	Marine	North Sea	No		
Debaryomyces hansenii	4959	PHA	Matavulj, M., & Molitoris, H. P. (2009). Marine fungi: degraders of poly-3-hydroxyalkanoate based plastic materials. Zb Mat Srp Prir Nauk, 116, 253-265.	No			No			2009.0	Clear zone;Turbidity	Granulated and powdered BIOPOL	ICI, UK		No	Culture collection	Culture collection		No		
Debaryomyces hansenii	4959	PHB	Matavulj, M., & Molitoris, H. P. (2009). Marine fungi: degraders of poly-3-hydroxyalkanoate based plastic materials. Zb Mat Srp Prir Nauk, 116, 253-265.	No			No			2009.0	Clear zone;Turbidity	Granulated and powdered BIOPOL	ICI, UK		No	Culture collection	Culture collection		No		
Delftia acidovorans	80866	PU	Akutsu, Y., Nakajima-Kambe, T., Nomura, N., & Nakahara, T. (1998). Purification and properties of a polyester polyurethane-degrading enzyme from Comamonas acidovorans TB-35. Appl. Environ. Microbiol., 64(1), 62-67.	No			No			1998.0	SEM;GC;Weight loss	The polyester PUR used in this study was synthesized by reacting poly(diethylene glycol adipate) with 2,4-tolylene diisocyanate under anhydrous conditions as described previously (19).		Yes	No	Colllection	Culture collection		Yes		
Delftia acidovorans	80866	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Delftia sp.	1886637	PET	Liu, J., Xu, G., Dong, W., Xu, N., Xin, F., Ma, J., ... & Jiang, M. (2018). Biodegradation of diethyl terephthalate and polyethylene terephthalate by a novel identified degrader Delftia sp. WL‐3 and its proposed metabolic pathway. Letters in applied microbiology, 67(3), 254-261.	No			No			2018.0	SEM;HPLC	Diethyl terephthalate (99% purity) was obtained from the Sinopharm Chemical Reagent Co. Ltd (Shanghai, china). All other chemicals used in this study were of analytical grade or higher.	Sinopharm Chemical Reagent	Yes	No				No		
Delftia sp.	1886637	PE	Peixoto, J., Silva, L. P., & Krüger, R. H. (2017). Brazilian Cerrado soil reveals an untapped microbial potential for unpretreated polyethylene biodegradation. Journal of hazardous materials, 324, 634-644.	No			No			2017.0	ATR-FTIR;SEM;Spectrophotometry;Clear zone	0.1% ultra-high molecular weight PE powder (Sigma Aldrich, USA)	Sigma Aldrich	Yes	No	Plastic debris	Soil	Brazil	No		
Delftia tsuruhatensis	180282	LDPE	Montazer, Z., Habibi Najafi, M. B., & Levin, D. B. (2018). Microbial degradation of low-density polyethylene and synthesis of polyhydroxyalkanoate polymers. Canadian journal of microbiology, 65(3), 224-234.	No			No			2018.0	Weight loss;SEM;GC;FTIR	LDPE powder, with a particle size of 400 μm or less (screen retention of 50 mesh is 4.4%) and a molecular weight range between 20,000 and 150,000, was supplied by Alfa-Asar Company (USA; CAS number 9002-88-4). According to the supplier, the Feedstock Melt Index and density were 3.50 g/10 min (at 190 oC and 2.16 kg load) and 0.9227 g/cm3, respectively. According to supplier’s data sheet, the polymer was pure and free of stabilizing agents. The PE particles sterilized by exposure to UV-light (254 nm) for 1 hour while mixing.	Alfa-Asar Company		No	Soil	Plastic waste dumping site	Iran	No		
Delftia tsuruhatensis	180282	LDPE	Montazer, Z., Habibi-Najafi, M. B., Mohebbi, M., & Oromiehei, A. (2018). Microbial degradation of UV-pretreated low-density polyethylene films by novel polyethylene-degrading bacteria isolated from plastic-dump soil. Journal of Polymers and the Environment, 26(9), 3613-3625.	No			No			2018.0	FTIR;SEM;Microscopy;Weight loss;CG-FIT	Low density polyethylene (Poliran LF0200 grade) granules and film (10 μm thickness; 99.95% purity without any additives and plasticizers) used for pasteurized milk packaging were supplied by Iran Polymer and Petrochemical Institute (IPPI)	Polymer and Petrochemical Institute (IPPI)	Yes	No	Soil	Landfill	Iran	No		
Desulfovibrio desulfuricans	876	PEG	Dwyer, D. F., & Tiedje, J. M. (1986). Metabolism of polyethylene glycol by two anaerobic bacteria, Desulfovibrio desulfuricans and a Bacteroides sp. Appl. Environ. Microbiol., 52(4), 852-856.	No			No			1986.0	Chromatography;GC				No	Sludge	Sewage/Sludge	USA	No		
Duganella zoogloeoides	75659	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Duganella zoogloeoides	75659	PHA	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHA (BIOPOL-D400P-PB36)	Monsanto		No	Soil	Soil	Japan	No		
Duganella zoogloeoides	75659	PHC	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHC (PCD-2000)	Toagosei		No	Soil	Soil	Japan	No		
Duganella zoogloeoides	75659	PTS	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PTS (BIONOLLE-1020)	Showa Denko		No	Soil	Soil	Japan	No		
Emericella nidulans	162425	PCL	Bentham, R. H., Morton, L. H. G., & Allen, N. G. (1987). Rapid assessment of the microbial deterioration of polyurethanes. International biodeterioration, 23(6), 377-386.	No			No			1987.0	Clear zone;Tensilometer;Weight loss	Two similar formulations of polyurethane foam were investigated, supplied as dumbbell-shaped test pieces. The materials were both polyester polyurethanes, one formulation, however, contained VINYZENE BP (10,10'-oxybis-phenoxarsine) as the formulation biocide. Another formulation was also available, an unprotected polyester polyurethane elastomer.		No	No	Plastic debris	Compost		No		
Emericella nidulans	162425	PU	Zafar, U., Nzeram, P., Langarica-Fuentes, A., Houlden, A., Heyworth, A., Saiani, A., & Robson, G. D. (2014). Biodegradation of polyester polyurethane during commercial composting and analysis of associated fungal communities. Bioresource technology, 158, 374-377.	No			No			2014.0	Clear zone	Impranil	Bayer 	No	No	PU coupons	Compost	UK	No		
Parengyodontium album	37998	PP	Jeyakumar, D., Chirsteen, J., & Doble, M. (2013). Synergistic effects of pretreatment and blending on fungi mediated biodegradation of polypropylenes. Bioresource technology, 148, 78-85.	No			No			2013.0	Weight loss;SEM;FTIR;TGA;MS	Commercial PP films (PP) [Reliance Industries Ltd., Mumbai, India], Starch blended PP (ST-PP) [Biobags Ltd., Chennai, India], and Catalyst blended PP (MI-PP) [Symphony, Chennai, India] are received as gifts. Films of Size 8   2.5 cm and 0.05 mm thick were used in these experiments. All the chemicals were procured from (HIMEDIA Laboratories, India).	Reliance Industries	No	No		Plastic waste dumping site		No		
Enterobacter agglomerans	549	PU	Kay, M. J., Morton, L. H. G., & Prince, E. L. (1991). Bacterial degradation of polyester polyurethane. International biodeterioration, 27(2), 205-222.	No			No			1991.0	Microscopy;Tensilometer;Weight loss	Biocide-free, dumb-bell shaped polyester polyurethane foam test pieces were used for these investigations			No	Plastic debris	Soil	UK	No		
Enterobacter asburiae	61645	LDPE	Yang, J., Yang, Y., Wu, W. M., Zhao, J., & Jiang, L. (2014). Evidence of polyethylene biodegradation by bacterial strains from the guts of plastic-eating waxworms. Environmental science & technology, 48(23), 13776-13784.	No			No			2014.0	SEM;AFM;XPS;GPC;MS;Weight loss	Linear low-density PE (LDPE) film (DFDA-9020, 22.5 μm thickness)	SINOPEC Beijing Yanshan Company		No	Waxworm's gut	Animal associated	India	No		
Enterobacter sp.	42895	PS	Sekhar, V. C., Nampoothiri, K. M., Mohan, A. J., Nair, N. R., Bhaskar, T., & Pandey, A. (2016). Microbial degradation of high impact polystyrene (HIPS), an e-plastic with decabromodiphenyl oxide and antimony trioxide. Journal of hazardous materials, 318, 347-354.	No			No			2016.0	FTIR;TGA;NMR;Weight loss;HPLC	Indian Institute of petroleum (IIP), CSIR provided four types of e-plastic samples. These are virgin plastics samples used in electric and electronic appliance and are specially prepared for research purpose and not available commercially. The samples were coded as (1) AMS 01 (HIPS with decabromodiphenyl oxide or ether and antimony trioxide) (2) AMS 01S (HIPS with decabromodiphenyl oxide or ether) (3) AMS 02 (HIPS with decabromodiphenyl ethane and antimony trioxide) and (4) AMS 02S (HIPS with decabromodiphenyl ethane).	Indian Institute of petroleum (IIP), CSIR	No	No	Plastic debris	Plastic waste dumping site	India	No		
Enterobacter sp.	42895	LDPE	Skariyachan, S., Manjunatha, V., Sultana, S., Jois, C., Bai, V., & Vasist, K. S. (2016). Novel bacterial consortia isolated from plastic garbage processing areas demonstrated enhanced degradation for low density polyethylene. Environmental Science and Pollution Research, 23(18), 18307-18319.	No			No			2016.0	FTIR;GC;Tensilometer;SEM;Weight loss;Clear zone	Different forms of plastic used in the study were low-density polyethylene (LDPE) strips (5 × 1 cm) and LDPE pellets (1.0 g l^-1).			No	Soil	Plastic waste dumping site	India	No		
Enterobacter sp.	42895	PHB	Volova, T. G., Boyandin, A. N., Vasiliev, A. D., Karpov, V. A., Prudnikova, S. V., Mishukova, O. V., ... & Dũng, V. V. (2010). Biodegradation of polyhydroxyalkanoates (PHAs) in tropical coastal waters and identification of PHA-degrading bacteria. Polymer Degradation and Stability, 95(12), 2350-2359.	No			No			2010.0	Weight loss;X-ray;SEM;Clear zone	The tested material was the PHA samples synthesized by the bacterium Ralstonia eutropha.		Yes	No	Plastic debris	Marine	Vietnam	No		
Enterobacter sp.	42895	PHBV	Volova, T. G., Boyandin, A. N., Vasiliev, A. D., Karpov, V. A., Prudnikova, S. V., Mishukova, O. V., ... & Dũng, V. V. (2010). Biodegradation of polyhydroxyalkanoates (PHAs) in tropical coastal waters and identification of PHA-degrading bacteria. Polymer Degradation and Stability, 95(12), 2350-2359.	No			No			2010.0	Weight loss;X-ray;SEM;Clear zone	A polymer of 3-hydroxybutyric acid (3-PHB) and a copolymer of 3-hydroxybutyric and 3-hydroxyvaleric acids (3-PHB/3-PHV) containing 11 mol% of hydroxyvalerate, synthesized in the Institute of Biophysics SB RAS, Russia, were used in experiments [34].		Yes	No	Plastic debris	Marine	Vietnam	No		
Exiguobacterium sibiricum	332410	PS	Chauhan, D., Agrawal, G., Deshmukh, S., Roy, S. S., & Priyadarshini, R. (2018). Biofilm formation by Exiguobacterium sp. DR11 and DR14 alter polystyrene surface properties and initiate biodegradation. RSC Advances, 8(66), 37590-37599.	No			No			2018.0	Weight loss;AFM;FTIR	1x1 cm cut pieces of optically clear, sterile polystyrene Petri plates, 90 mm	Himedia Lab		No	Water	Soil	India	No		
Exiguobacterium sp.	44751	PS	Yang, Y., Yang, J., Wu, W. M., Zhao, J., Song, Y., Gao, L., ... & Jiang, L. (2015). Biodegradation and mineralization of polystyrene by plastic-eating mealworms: part 2. Role of gut microorganisms. Environmental science & technology, 49(20), 12087-12093.	No			No			2015.0	14C;SEM;MS;GPC;Weight loss;Clear zone;XPS	α 13C-labeled and β 13C-labeled PS	Sigma Aldrich	Yes	No	Mealworm's gut	Culture collection	China	No		
Exiguobacterium undae	169177	PS	Chauhan, D., Agrawal, G., Deshmukh, S., Roy, S. S., & Priyadarshini, R. (2018). Biofilm formation by Exiguobacterium sp. DR11 and DR14 alter polystyrene surface properties and initiate biodegradation. RSC Advances, 8(66), 37590-37599.	No			No			2018.0	Weight loss;AFM;FTIR	1x1 cm cut pieces of optically clear, sterile polystyrene Petri plates, 90 mm	Himedia Lab		No	Water	Soil	India	No		
Flammulina velutipes	38945	PVA	Tsujiyama, S. I., Nitta, T., & Maoka, T. (2011). Biodegradation of polyvinyl alcohol by Flammulina velutipes in an unsubmerged culture. Journal of bioscience and bioengineering, 112(1), 58-62.	No			No			2011.0	Clear zone;Iodometric analysis;Spectrophotometry	 PVA (Mw ≈90,000)	Nacalai Tesque	Yes	No				No		
Flavobacterium sp.	239	LDPE	Koutny, M., Amato, P., Muchova, M., Ruzicka, J., & Delort, A. M. (2009). Soil bacterial strains able to grow on the surface of oxidized polyethylene film containing prooxidant additives. International Biodeterioration & Biodegradation, 63(3), 354-357.	No			No			2009.0	Microscopy;Tensilometer	Preoxidized PE film was transparent LDPE film 60 mm thick containing prooxidant additives based on organometallic complexes. To balance the prodegradant activity phenolic antioxidants were used in the blends. 		No	No	Soil	Soil	France	No		
Fomitopsis pinicola	40483	PVA	Tsujiyama, S., & Okada, A. (2013). Biodegradation of polyvinyl alcohol by a brown-rot fungus, Fomitopsis pinicola. Biotechnology letters, 35(11), 1907-1911.	No			No			2013.0	GPC;Clear zone;Spectrophotometry;DRIFT	PVA [MW: approx. 90,000 or MW: approx. 50,000 (Sigma)	Sigma Aldrich	Yes	No				No		
Fusarium culmorum	5516	PCL	Bentham, R. H., Morton, L. H. G., & Allen, N. G. (1987). Rapid assessment of the microbial deterioration of polyurethanes. International biodeterioration, 23(6), 377-386.	No			No			1987.0	Clear zone;Tensilometer;Weight loss	Two similar formulations of polyurethane foam were investigated, supplied as dumbbell-shaped test pieces. The materials were both polyester polyurethanes, one formulation, however, contained VINYZENE BP (10,10'-oxybis-phenoxarsine) as the formulation biocide. Another formulation was also available, an unprotected polyester polyurethane elastomer.		No	No	Plastic debris	Compost		No		
Fusarium equiseti	61235	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Fusarium equiseti	61235	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Fusarium equiseti	61235	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Fusarium equiseti	61235	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Fusarium moniliforme	117187	PLA	Torres, A., Li, S. M., Roussos, S., & Vert, M. (1996). Screening of microorganisms for biodegradation of poly (lactic-acid) and lactic acid-containing polymers. Appl. Environ. Microbiol., 62(7), 2393-2397.	No			No			1996.0	HPLC;SEM	Typically, 1 liter of DL-LA commercial solution was heated under normal pressure to gently distillate water. When the temperature reached 1308C, vacuum was applied and distillation was controlled as desired. One fraction of racemic oligomers (Mw 5 1,000, I 5 Mw/Mn 5 1.3) was used for the screening of filamentous fungi, and another one (Mw 5 2,000, I 5 1.3) was used for soil screening. Molecular weights were determined by size exclusion chromatography. 	Sigma Aldrich	Yes	No		Culture collection		No		
Fusarium oxysporum	5507	PHB	Gangurde, N. S., Patil, Y. P., Jain, R., & Sayyed, R. Z. (2017). Poly-β-hydroxybutyrate biodegradation by mixed culture population vis-à-vis single culture population under varying environmental conditions: A new approach.	No			No			2017.0	Weight loss;Clear zone	PHB production was carried out by Alcaligenes sp. RZS 4 (Gene bank accession No. JN374993) using two-step cultivation process.		Yes	No	Soil	Soil	India	No		
Fusarium oxysporum	5507	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Fusarium oxysporum	5507	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Fusarium oxysporum	5507	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Fusarium oxysporum	5507	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Fusarium oxysporum	5507	PHBV	Sang, B. I., Hori, K., Tanji, Y., & Unno, H. (2002). Fungal contribution to in situ biodegradation of poly (3-hydroxybutyrate-co-3-hydroxyvalerate) film in soil. Applied microbiology and biotechnology, 58(2), 241-247.	No			No			2002.0	Weight loss;SEM;Clear zone	PHBV containing 12% 3-hydroxyvalerate (3HV) in powder form	Sigma Aldrich		No	Soil	Soil	Japan	No		
Fusarium oxysporum	5507	PBSA	Yamamoto-Tamura, K., Hoshino, Y. T., Tsuboi, S., Huang, C., Kishimoto-Mo, A. W., Sameshima-Yamashita, Y., & Kitamoto, H. (2020). Fungal community dynamics during degradation of poly (butylene succinate-co-adipate) film in two cultivated soils in Japan. Bioscience, Biotechnology, and Biochemistry, 1-11.	No			No			2020.0	Luminance	PBSA films used in this study were composed of Bionolle® 3001 (Showa Denko K. K., Tokyo, Japan)	Showa Denko	No	No	Soil	Soil	Japan	No		
Fusarium redolens	48865	LDPE	Albertsson, A. C., & Karlsson, S. (1990). The influence of biotic and abiotic environments on the degradation of polyethylene. Progress in Polymer science, 15(2), 177-192.	No			No			1990.0	14C;IR;Weight loss	LDPE labelled with 14C was produced by Imperial Chemical Industries, London, and generously supplied by Akerlund and Rausing AB, Lund, Sweden. From ethylene a polymer was made with a rather high concentration of 14C using a high pressure free radical process. This polymer was mixed with another batch of similar commercial polymer to yield a polymer with a fairly low concentration of 14C. The density of the LDPE granulate was 0.922g/cm 3, and its molecular weights were Mn =18200 and Mw = 84000. One set of PE samples (NDPE) contained 5% of an additive consisting of a mixture of Fe(III) palmitate and Fe(III) hydroxide to increase the photochemical degradation rate. A parallel set of samples (PE) contained no additive. Thick and thin films were made by moulding the LDPE granulates. The thick films had a thickness of 0.16 mm and the thin films 0.02 mm.	Imperial Chemical Industries		No	Plastic debris	Soil	Sweden	No		
Fusarium redolens	48865	LDPE	Karlsson, S., Ljungquist, O., & Albertsson, A. C. (1988). Biodegradation of polyethylene and the influence of surfactants. Polymer degradation and stability, 21(3), 237-250.	No			No			1988.0	14C;CO2	LDPE labelled with 14C was produced by Imperial Chemical Industries, London and generously supplied by Akerlund & Rausing AB, Lund, Sweden. The polymer was made from ethylene with a rather high concentration of 14 C using a high pressure free radical process. This polymer was mixed with another batch of similar commercial polymer to yield a polymer with a fairly low concentration of 14C. This gave a distribution of 14C in which the labelled carbon was located in a few molecules. The density of the LDPE granules was 0.922 g/cm^3, and the molecular weights were M. -- 18.200 and M w = 84.000. Films, 0.16 mm thick, were made by heating and moulding the LDPE granules. One set of polyethylene samples (NDPE) contained 5% of an additive consisting of palmitate iron carboxylate-Fe(III)hydroxide to increase the photo-chemical degradation rate. A parallel set of samples contained no additive (PE).	Akerlund & Rausing AB	Yes	No				No		
Fusarium solani	169388	PBS	Abe, M., Kobayashi, K., Honma, N., & Nakasaki, K. (2010). Microbial degradation of poly (butylene succinate) by Fusarium solani in soil environments. Polymer Degradation and Stability, 95(2), 138-143.	No			No			2010.0	CO2	The biodegradable plastic used in this study was GS Pla_x005F	Mitsubishi Gas Chemical		No	PBS Film	Soil	Japan	No		
Fusarium solani	169388	PCL	Antipova, T. V., Zhelifonova, V. P., Zaitsev, K. V., Nedorezova, P. M., Aladyshev, A. M., Klyamkina, A. N., ... & Kozlovsky, A. G. (2018). Biodegradation of Poly-ε-caprolactones and Poly-l-lactides by Fungi. Journal of Polymers and the Environment, 26(12), 4350-4359.	No			No			2018.0	Weight loss;MS	PLA was obtained upon ring-opening polymerization of l-lactide in the presence of catalytic amounts of aluminium complexes			No	Soil	Culture collection	Vietnam	No		
Fusarium solani	169388	PCL	Bentham, R. H., Morton, L. H. G., & Allen, N. G. (1987). Rapid assessment of the microbial deterioration of polyurethanes. International biodeterioration, 23(6), 377-386.	No			No			1987.0	Clear zone;Tensilometer;Weight loss	Two similar formulations of polyurethane foam were investigated, supplied as dumbbell-shaped test pieces. The materials were both polyester polyurethanes, one formulation, however, contained VINYZENE BP (10,10'-oxybis-phenoxarsine) as the formulation biocide. Another formulation was also available, an unprotected polyester polyurethane elastomer.		No	No	Plastic debris	Compost		No		
Fusarium solani	169388	PU	Crabbe, J. R., Campbell, J. R., Thompson, L., Walz, S. L., & Schultz, W. W. (1994). Biodegradation of a colloidal ester-based polyurethane by soil fungi. International Biodeterioration & Biodegradation, 33(2), 103-113.	No			No			1994.0	Clear zone	The substrate used for all degradation experiments was an ester-based polyurethane (PU), and was obtained as a water-dispersed colloid (Impranil DLN, Miles Inc., Pittsburgh, PA, USA).	Miles	No	No	Soil	Soil	USA	No		
Fusarium solani	169388	PU	Ibrahim, I. N., Maraqa, A., Hameed, K. M., Saadoun, I. M., & Maswadeh, H. M. (2011). Assessment of potential plastic-degrading fungi in Jordanian habitats. Turkish Journal of Biology, 35(5), 551-557.	No			No			2011.0	Weight loss;Clear zone	Sheets (5 × 20 cm) of PS-PUR were supplied by Dr. Toshiaki Nakajima-Kambe from the Institute of Applied Biochemistry, University of Tsukuba, Ibaraki- Japan, and used as a source of carbon and nitrogen in growth media.			No	Soil	Soil	Jordan	No		
Fusarium solani	169388	PBS	Ishii, N., Inoue, Y., Tagaya, T., Mitomo, H., Nagai, D., & Kasuya, K. I. (2008). Isolation and characterization of poly (butylene succinate)-degrading fungi. Polymer Degradation and Stability, 93(5), 883-888.	No			No			2008.0	Clear zone;Weight loss;Microscopy;SEM;GPC;MS	PBSu (1,4-Butanediol/succinic acid;Tm 117;Mw 17.6x10-4)	Showa Denko		No	Soil	Soil	Japan	No		
Fusarium solani	169388	PCL	Ishii, N., Inoue, Y., Tagaya, T., Mitomo, H., Nagai, D., & Kasuya, K. I. (2008). Isolation and characterization of poly (butylene succinate)-degrading fungi. Polymer Degradation and Stability, 93(5), 883-888.	No			No			2008.0	Clear zone;Weight loss;Microscopy;SEM;GPC;MS	PCL (6-Hydroxyhexanoic acid; Tm 62; Mw 6.4x10^-4)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Fusarium solani	169388	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Fusarium solani	169388	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Fusarium solani	169388	PHB	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	PHB was provided by ICI in powder form (200 mm) and its weight average molecular weight was 470,000 g/ mol.	ICI, UK		No	Plastic debris	Soil	South Korea	No		
Fusarium solani	169388	LDPE	Zahra, S., Abbas, S. S., Mahsa, M. T., & Mohsen, N. (2010). Biodegradation of low-density polyethylene (LDPE) by isolated fungi in solid waste medium. Waste management, 30(3), 396-401.	No			No			2010.0	TOC;SEM;FTIR;GPC;	Commercial granules of LDPE were provided from one of the stocks of Iran’s National Petrochemical Commercial Company (INPCC). LDPE films with thickness of 15 um were made from this material using a blowing film extruder. LDPE films were irradiated for 25 days with UV-irradiation in a laminar flow cabinet and then cut into pieces of about 1x1 cm.	Iran’s National Petrochemical Commercial Company (INPCC)		No	Soil	Landfill	Iran	No		
Fusarium sp.	29916	PC	Arefian, M., Zia, M., Tahmourespour, A., & Bayat, M. (2013). Polycarbonate biodegradation by isolated molds using clear-zone and atomic force microscopic methods. International Journal of Environmental Science and Technology, 10(6), 1319-1324.	No			No			2013.0	Clear zone;AFM				No	Soil	Soil	Iran	No		
Fusarium sp.	29916	PCL	Benedict, C. V., Cameron, J. A., & Huang, S. J. (1983). Polycaprolactone degradation by mixed and pure cultures of bacteria and a yeast. Journal of Applied Polymer Science, 28(1), 335-342.	No			No			1983.0	Clear zone;GPC	Polycaprolactone 700 (PCL-700), PCL-300, and LPS-60 with molecular weights of 35,000,18,600, and 7,130 Wr, respectively, were obtained from Union Carbide Corp., New York, N.Y. The PCL designated LPS-60 by the manufacturer contains a phthalic acid residue covalently linked to the chain ends but otherwise is structurally identical to PCL-700 and PCL-300. No low molecular weight, contaminants were seen by chromatographic analysis of the polymers using THF, chloroform, or dichloromethane as solvents. Infrared spectroscopy of PCL-700 resulted in a spectrum identical to the published standard.6 All polymers showed broad molecular weight distributions. Polydispersities (Mv/Mn) ranged from 1.892 to 1.978.	Union Carbide	Yes	No	Culture collection	River/Lake	USA	No		
Fusarium sp.	29916	LDPE	Das, M. P., & Kumar, S. (2014). Microbial deterioration of low density polyethylene by Aspergillus and Fusarium sp. Int J Chem Tech Res, 6(1), 299-305.	No			No			2014.0	SEM;FTIR;Weight loss;CO2	The LDPE films were cut into small pieces and were dipped in xylene and heated, when the plastic gets dissolved it was cooled to palm bearable heat and was crushed to fine particles. Later it was kept to evaporate the xylene and was washed with ethanol to remove xylene residues. Then it was dried in hot air oven at 50 °C for overnight.			No	LDPE film	Plastic waste dumping site	India	No		
Fusarium sp.	29916	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Fusarium sp.	29916	LDPE	Jyoti, S., & Gupta, K. C. (2014). Screening and identification of low density polyethylene (LDPE) degrading soil fungi isolated from polythene polluted sites around Gwalior city (MP). International Journal of Current Microbiology and Applied Sciences, 3(6), 443-448.	No			No			2014.0	Clear zone;Weight loss	Low density polyethylene (LDPE) sheets were obtained from Gwalior Plastic Industry (Gwalior).	Gwalior Plastic Industry 		No	Soil	Plastic waste dumping site	India	No		
Fusarium sp.	29916	PE	Shah, A. A., Hasan, F., Hameed, A., & Akhter, J. I. (2009). Isolation of Fusarium sp. AF4 from sewage sludge, with the ability to adhere the surface of polyethylene. African Journal of Microbiology Research, 3(10), 658-663.	No			No			2009.0	CO2;SEM	Polyethylene (PE) plastic bags were used as the standard polyethylene for the degradation experiments.			No	Sewage sludge	Sewage/Sludge	Pakistan	No		
Fusarium sp.	29916	Nylon	Tachibana, K., Hashimoto, K., Yoshikawa, M., & Okawa, H. (2010). Isolation and characterization of microorganisms degrading nylon 4 in the composted soil. Polymer degradation and stability, 95(6), 912-917.	No			No			2010.0	MS;SEM;BOD;Weight loss	Nylon 4 (Mn, 1.3x10^3 and Mw, 3.0x10^4) having benzamide and acyllactam at each chain end was prepared by the anionic ring-opening polymerization of 2-pyrrolidone using N-acyllactam and potassium t-butoxide as an initiator and a catalyst in a similar method to that described in our previous articles [17e19,25e27]. The average molecular weight was controlled by the mole ratio of the catalyst to the monomer to be from 1.3x10^3 to 3.0x10^4. The number average molecular weight of the low molecular weight nylon 4 (Mn, 1.3x10^3) was estimated from the 1H NMR and TOF-MS analyses and the weight average molecular weight of the relatively high molecular weight one (Mw, 3.0x10^4) was determined by viscometry [28]. 		Yes	No	Soil	Soil	Japan	No		
Gibellulopsis nigrescens	796325	PBSA	Yamamoto-Tamura, K., Hoshino, Y. T., Tsuboi, S., Huang, C., Kishimoto-Mo, A. W., Sameshima-Yamashita, Y., & Kitamoto, H. (2020). Fungal community dynamics during degradation of poly (butylene succinate-co-adipate) film in two cultivated soils in Japan. Bioscience, Biotechnology, and Biochemistry, 1-11.	No			No			2020.0	Luminance	PBSA films used in this study were composed of Bionolle® 3001 (Showa Denko K. K., Tokyo, Japan)	Showa Denko	No	No	Soil	Soil	Japan	No		
Gliocladium roseum	29856	PCL	Bentham, R. H., Morton, L. H. G., & Allen, N. G. (1987). Rapid assessment of the microbial deterioration of polyurethanes. International biodeterioration, 23(6), 377-386.	No			No			1987.0	Clear zone;Tensilometer;Weight loss	Two similar formulations of polyurethane foam were investigated, supplied as dumbbell-shaped test pieces. The materials were both polyester polyurethanes, one formulation, however, contained VINYZENE BP (10,10'-oxybis-phenoxarsine) as the formulation biocide. Another formulation was also available, an unprotected polyester polyurethane elastomer.		No	No	Plastic debris	Compost		No		
Gloeophyllum striatum	941527	PSS	Krueger, M. C., Hofmann, U., Moeder, M., & Schlosser, D. (2015). Potential of wood-rotting fungi to attack polystyrene sulfonate and its depolymerisation by Gloeophyllum trabeum via hydroquinone-driven Fenton chemistry. PloS one, 10(7), e0131773.	No			No			2015.0	SEC;HPLC;MS	Poly(sodium 4-styrenesulfonate) (PSS; Mw ~70,000 Da) was obtained from Sigma-Aldrich (Munich, Germany)	Sigma Aldrich	Yes	No	Culture collection	Culture collection		No		
Gloeophyllum trabeum	104355	PSS	Krueger, M. C., Hofmann, U., Moeder, M., & Schlosser, D. (2015). Potential of wood-rotting fungi to attack polystyrene sulfonate and its depolymerisation by Gloeophyllum trabeum via hydroquinone-driven Fenton chemistry. PloS one, 10(7), e0131773.	No			No			2015.0	SEC;HPLC;MS	Poly(sodium 4-styrenesulfonate) (PSS; Mw ~70,000 Da) was obtained from Sigma-Aldrich (Munich, Germany)	Sigma Aldrich	Yes	No	Culture collection	Culture collection		No		
Gloeophyllum trabeum	104355	PSS	Krueger, M. C., Seiwert, B., Prager, A., Zhang, S., Abel, B., Harms, H., & Schlosser, D. (2017). Degradation of polystyrene and selected analogues by biological Fenton chemistry approaches: Opportunities and limitations. Chemosphere, 173, 520-528.	No			No			2017.0	XPS;UPLC;MS	PSS Mw ~ 70,000	Sigma Aldrich	Yes	No		Culture collection		No		
Gongronella sp.	1981611	PHA	Boyandin, A. N., Prudnikova, S. V., Karpov, V. A., Ivonin, V. N., Đỗ, N. L., Nguyễn, T. H., ... & Volova, T. G. (2013). Microbial degradation of polyhydroxyalkanoates in tropical soils. International Biodeterioration & Biodegradation, 83, 77-84.	No			No			2013.0	Weight loss;GPC;X-ray	The polymers were synthesized in Wautersia eutropha B5786 microbial culture (the strain is registered in the Russian Collection of Industrial Microorganisms).			No	Soil	Soil	Vietnam	No		
Gracilibacillus sp.	1871618	PHB	Volova, T. G., Boyandin, A. N., Vasiliev, A. D., Karpov, V. A., Prudnikova, S. V., Mishukova, O. V., ... & Dũng, V. V. (2010). Biodegradation of polyhydroxyalkanoates (PHAs) in tropical coastal waters and identification of PHA-degrading bacteria. Polymer Degradation and Stability, 95(12), 2350-2359.	No			No			2010.0	Weight loss;X-ray;SEM;Clear zone	The tested material was the PHA samples synthesized by the bacterium Ralstonia eutropha.		Yes	No	Plastic debris	Marine	Vietnam	No		
Gracilibacillus sp.	1871618	PHBV	Volova, T. G., Boyandin, A. N., Vasiliev, A. D., Karpov, V. A., Prudnikova, S. V., Mishukova, O. V., ... & Dũng, V. V. (2010). Biodegradation of polyhydroxyalkanoates (PHAs) in tropical coastal waters and identification of PHA-degrading bacteria. Polymer Degradation and Stability, 95(12), 2350-2359.	No			No			2010.0	Weight loss;X-ray;SEM;Clear zone	A polymer of 3-hydroxybutyric acid (3-PHB) and a copolymer of 3-hydroxybutyric and 3-hydroxyvaleric acids (3-PHB/3-PHV) containing 11 mol% of hydroxyvalerate, synthesized in the Institute of Biophysics SB RAS, Russia, were used in experiments [34].		Yes	No	Plastic debris	Marine	Vietnam	No		
Hypocrea sp.	1715253	LDPE	Hikmah, M., Setyaningsih, R., & Pangastuti, A. (2018). The Potential of Lignolytic Trichoderma Isolates in LDPE (Low Density Polyethylene) Plastic Biodegradation. In IOP Conference Series: Materials Science and Engineering (Vol. 333, No. 1, p. 012076). IOP Publishing.	No			No			2018.0	Weight loss;SEM	LDPE polyethylene crystals			No	Leaf	Soil	Indonesia	No		
Inonotus circinatus	119078	PHB	Matavulj, M., & Molitoris, H. P. (1992). Fungal degradation of polyhydroxyalkanoates and a semiquantitative assay for screening their degradation by terrestrial fungi. FEMS microbiology reviews, 9(2-4), 323-331.	No			No			1992.0	Clear zone;Weight loss	Granulated and powdered BIOPOL	ICI, UK		No	Culture collection	Culture collection		No		
Janthinobacterium sp.	1871054	PVA	Du, G., Liu, L., Song, Z., Hua, Z., Zhu, Y., & Chen, J. (2007). Production of polyvinyl alcohol‐degrading enzyme with Janthinobacterium sp. and its application in cotton fabric desizing. Biotechnology Journal: Healthcare Nutrition Technology, 2(6), 752-758. 	No			No			2007.0	Iodometric analysis;Spectrophotometry	PVA used in the study had a 99.0% saponification degree and a polymerization degree of 1799. All chemicals in this study were purchased from Sigma (Sigma-Aldrich, St Louis, MO, USA). PVA and metal ions were analytical grade reagents.	Sigma Aldrich	Yes	No	Soil	Soil	China	No		
Kibdelosporangium aridum	2030	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Kibdelosporangium aridum	2030	PLA	Jarerat, A., Tokiwa, Y., & Tanaka, H. (2003). Poly (L-lactide) degradation by Kibdelosporangium aridum. Biotechnology letters, 25(23), 2035-2038.	No			No			2003.0	SEM;TOC;Weight loss	Poly(L-lactide) (PLA), Lacty 1012 (number-average molecular weight,Mn: 3.4× 105) was purchased from Shimadzu Co. Ltd., Kyoto, Japan.	Shimadzu		No	Culture collection	Culture collection		No		
Kineococcus sp.	1871184	PCL	Adıgüzel, A. O., & Tunçer, M. (2017). Purification and characterization of cutinase from Bacillus sp. KY0701 isolated from plastic wastes. Preparative Biochemistry and Biotechnology, 47(9), 925-933.	No			No			2017.0	Weight loss;Clear zone	Plastic Waste		No	No	Plastic debris	Soil	Turkey	No		
Kitasatospora phosalacinea	2065	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Klebsiella pneumoniae	573	HDPE	Awasthi, S., Srivastava, P., Singh, P., Tiwary, D., & Mishra, P. K. (2017). Biodegradation of thermally treated high-density polyethylene (HDPE) by Klebsiella pneumoniae CH001. 3 Biotech, 7(5), 332.	No			No			2017.0	Clear zone;Weight loss;UTM;SEM;AFM;FTIR;MS	High-density Polyethylene (HDPE) carry bags, (40 lm in thickness) which are used in cloth packaging, were procured from local market for use in the present study.			No		Plastic waste dumping site	India	No		
Kocuria palustris	71999	LDPE	Harshvardhan, K., & Jha, B. (2013). Biodegradation of low-density polyethylene by marine bacteria from pelagic waters, Arabian Sea, India. Marine Pollution Bulletin, 77(1-2), 100-106.	No			No			2013.0	Weight loss;SEM;FTIR	The biodegradation tests were performed on samples of lowdensity polyethylene film (i.e., pieces of polyethylene bags) that had been dried overnight at 60 C, weighed, disinfected (autoclaved at 105 C for 1 h) and added to each flask (approximately 50.0 mg of polyethylene film per flask) containing 50 ml of BH medium		No	No	Water	Marine	India	No		
Lentinus tigrinus	5365	PVC	Ali, M. I., Ahmed, S., Robson, G., Javed, I., Ali, N., Atiq, N., & Hameed, A. (2014). Isolation and molecular characterization of polyvinyl chloride (PVC) plastic degrading fungal isolates. Journal of basic microbiology, 54(1), 18-27.	No			No			2014.0	SEM;CO2;FTIR;Spectrophotometry;NMR;GPC	Thin films of PVC (2% w/v) were prepared in petri plates by dissolving 0.2 g of PVC (Aldrich) in 10 ml of solvent tetrahydrofuran (THF; 99%; Merck).	Sigma Aldrich		No	PVC film	Sewage/Sludge		No		
Lentzea albidocapillata	40571	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Lentzea waywayandensis	84724	PLA	Nair, N. R., Nampoothiri, K. M., & Pandey, A. (2012). Preparation of poly (L-lactide) blends and biodegradation by Lentzea waywayandensis. Biotechnology letters, 34(11), 2031-2035.	No			No			2012.0	Weight loss;SEM	Standard poly(L-lactide) pellets with an average MW of 85,000–160,000 were obtained from Sigma (USA).	Sigma Aldrich	Yes	No		Culture collection		No		
Leptobacillium leptobactrum	93594	PHB	Mergaert, J., Anderson, C., Wouters, A., & Swings, J. (1994). Microbial degradation of poly (3-hydroxybutyrate) and poly (3-hydroxybutyrate-co-3-hydroxyvalerate) in compost. Journal of environmental polymer degradation, 2(3), 177-183.	No			No			1994.0	GPC;Weight loss;Tensilometer;Clear zone	Bioplastics were obtained from ICI Biological Products (Billingham, U.K.) as injection molded, dog bone shaped tensile test pieces (83 mm long, 2 mm thick, and weighing approximately 1.75 g) or as powder. Three polymers were investigated: homopolymer P(3HB) (high-purity grade, batch No. GO8), copolymer P(3HB-co-10%3HV) [technical-purity grade, blend of 35% P(3HB-co-20%3HV), batch No. PSMI 1, and 65% P(3HB-co-5%3HV), batch No. PSM20], and copolymer P(3HB-co-20%3HV) (technical grade, batch No. PSM 11), Tensile test pieces contained 0.5 [P(3HB)] phr (parts per hundred resin) or 1.0 (copolymers) phr boron nitride as a nucleant.	ICI, UK		No	Plastic debris	Compost	Belgium	No		
Leptosphaeria sp.	1755431	PU	Brunner, I., Fischer, M., Rüthi, J., Stierli, B., & Frey, B. (2018). Ability of fungi isolated from plastic debris floating in the shoreline of a lake to degrade plastics. PloS one, 13(8), e0202047.	No			No			2018.0	Clear zone	Impranil	Bayer 	No	No	Plastic debris	River/Lake	Switzerland	No		
Leptothrix sp.	34030	PBAT	Nakajima-Kambe, T., Ichihashi, F., Matsuzoe, R., Kato, S., & Shintani, N. (2009). Degradation of aliphatic–aromatic copolyesters by bacteria that can degrade aliphatic polyesters. Polymer degradation and stability, 94(11), 1901-1905.	No			No			2009.0	HPLC;Clear zone;Weight loss	Ecoflex is a commercial copolymer (BASF, Land Rheinland-Pfalz, Germany), which consists of 1,4-butanediol, adipic acid, and terephthalic acid	BASF		No				No		
Leptothrix sp.	34030	PBST55	Nakajima-Kambe, T., Ichihashi, F., Matsuzoe, R., Kato, S., & Shintani, N. (2009). Degradation of aliphatic–aromatic copolyesters by bacteria that can degrade aliphatic polyesters. Polymer degradation and stability, 94(11), 1901-1905.	No			No			2009.0	HPLC;Clear zone;Weight loss	PBST55 is copolyester of 1,4-butanediol, succinic acid, and terephthalic acid			No				No		
Leucobacter sp.	1898440	HDPE	Devi, R. S., Ramya, R., Kannan, K., Antony, A. R., & Kannan, V. R. (2019). Investigation of biodegradation potentials of high density polyethylene degrading marine bacteria isolated from the coastal regions of Tamil Nadu, India. Marine pollution bulletin, 138, 549-560.	No			No			2019.0	Weight loss;FTIR	Commercially available HDPE (40 μm in thickness and 0.95 g/cm3 in density) materials were used as substrate in this study. When compared to pure polyethylene, the composition of commercially available HDPE varies by the addition of additives like antioxidants and colorant.		No	No	Plastic debris	Plastic waste dumping site	India	No		
Lichtheimia sp.	2420204	PU	Zafar, U., Nzeram, P., Langarica-Fuentes, A., Houlden, A., Heyworth, A., Saiani, A., & Robson, G. D. (2014). Biodegradation of polyester polyurethane during commercial composting and analysis of associated fungal communities. Bioresource technology, 158, 374-377.	No			No			2014.0	Clear zone	Impranil	Bayer 	No	No	PU coupons	Compost	UK	No		
Lulwoana uniseptata	339359	PE	Paço, A., Duarte, K., da Costa, J. P., Santos, P. S., Pereira, R., Pereira, M. E., ... & Rocha-Santos, T. A. (2017). Biodegradation of polyethylene microplastics by the marine fungus Zalerion maritimum. Science of the Total Environment, 586, 10-15.	No			No			2017.0	FTIR-ATR;NMR;SEM	Polyethylene pellets (PE, linear formula H(CH2CH2)nH), with a melt index of 1.0 g/10 min (190 °C/2.16 kg) were acquired from Sigma- Aldrich (USA). These exhibited spheroid morphology and were approximately 2–4mmin size. 	Sigma Aldrich		No				No		
Lysinibacillus fusiformis	28031	PE	Shahnawaz, M., Sangale, M. K., & Ade, A. B. (2016). Rhizosphere of Avicennia marina (Forsk.) Vierh. as a landmark for polythene degrading bacteria. Environmental Science and Pollution Research, 23(14), 14621-14635.	No			No			2016.0	Tensilometer;SEM;FTIR;Weight loss	The banned polythene carry bags (20 μmthick) were procured from the local market of the Pune City, Maharashtra, India. We purchased PE pickup bags from the vegetable vendors because the local plastic shop keepers are afraid to sell the banned PE carry bags legally. PE carrier bags less than 50 μm thickness is banned in Maharashtra and most states of India. With the aid of sharp surgical blade, 2 ×2 cm strips of the PE were made.		No	No	Soil	Plant associated	India	No		
Lysinibacillus sp.	1869345	PCL	XU, S., YAMAGUCHI, T., OSAWA, S., & SUYE, S. I. (2007). Biodegradation of Poly (ε-Caprolactone) Film in the Presence of Lysinibacillus sp. 70038 and Characterization of the Degraded Film. Biocontrol science, 12(3), 119-122.	No			No			2007.0	Weight loss;SEM;GPC;WAXD	PCL film weight- averaged molecular weight (Mw) of 47,000 and 160,000	Daicel Chemical Industries		No		Culture collection	Japan	No		
Lysinibacillus sphaericus	1421	PE	Sudhakar, M., Doble, M., Murthy, P. S., & Venkatesan, R. (2008). Marine microbe-mediated biodegradation of low-and high-density polyethylenes. International Biodeterioration & Biodegradation, 61(3), 203-213.	No			No			2008.0	FTIR;Weight loss;Tensilometer;AFM;DSC	In the present investigation pure LDPE and starch-blended (with 12–15% of starch) LDPE films of size 80_25mm with thickness 0.125mm and HDPE films of size 80_25mm with thickness 0.0981 were kindly provided by Excelcier Pvt. Ltd., Guindy, Chennai 600 025, India. Thermal treatment of LDPE and HDPE involved treating them at 80°C for 10 days in a hot air oven (Sigma, USA).	Excelcier	Yes	No	Water	Marine	India	No		
Lysinibacillus xylanilyticus	582475	LDPE	Esmaeili, A., Pourbabaee, A. A., Alikhani, H. A., Shabani, F., & Esmaeili, E. (2013). Biodegradation of low-density polyethylene (LDPE) by mixed culture of Lysinibacillus xylanilyticus and Aspergillus niger in soil. Plos one, 8(9).	No			No			2013.0	CO2;Tensilometer;FTIR;X-ray;SEM	low-density polyethylene granules (LF0200, with a density of 0.920 gr.cm23)	Iranian petrochemical company 		No	Soil	Landfill	Iran	No		
Marasmius oreades	181124	PU	Brunner, I., Fischer, M., Rüthi, J., Stierli, B., & Frey, B. (2018). Ability of fungi isolated from plastic debris floating in the shoreline of a lake to degrade plastics. PloS one, 13(8), e0202047.	No			No			2018.0	Clear zone	Impranil	Bayer 	No	No		Culture collection	Switzerland	No		
Marinobacter algicola	236100	PHB	Martínez-Tobón, D. I., Gul, M., Elias, A. L., & Sauvageau, D. (2018). Polyhydroxybutyrate (PHB) biodegradation using bacterial strains with demonstrated and predicted PHB depolymerase activity. Applied microbiology and biotechnology, 102(18), 8049-8067.	No			No			2018.0	Clear zone;Weight loss	PHB pellets (BRS Bulk Bio-pellets, Bulk Reef Supply, Golden Valley, USA) and acetic acid (Fisher Scientific) were used to produce PHB films by solvent casting as described by Anbukarasu et al. (2015).	Bulk Reef Supply	Yes	No		Culture collection		No		
Matsuebacter chitosanotabidus	65048	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Matsuebacter chitosanotabidus	65048	PHA	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHA (BIOPOL-D400P-PB36)	Monsanto		No	Soil	Soil	Japan	No		
Metarhizium anisopliae	5530	PHB	Gangurde, N. S., Patil, Y. P., Jain, R., & Sayyed, R. Z. (2017). Poly-β-hydroxybutyrate biodegradation by mixed culture population vis-à-vis single culture population under varying environmental conditions: A new approach.	No			No			2017.0	Weight loss;Clear zone	PHB production was carried out by Alcaligenes sp. RZS 4 (Gene bank accession No. JN374993) using two-step cultivation process.		Yes	No	Soil	Soil	India	No		
Metarhizium marquandii	64636	PHB	Mergaert, J., Anderson, C., Wouters, A., Swings, J., & Kersters, K. F. E. M. S. (1992). Biodegradation of polyhydroxyalkanoates. FEMS microbiology reviews, 9(2-4), 317-321.	No			No			1992.0	Tensilometer;Weight loss	All bioplastics were obtained from ICI Biological Products (Billingham, UK), as injection moulded, dogbone-shaped tensile test pieces.	ICI, UK		No	Plastic debris		Belgium	No		
Meyerozyma guilliermondii	4929	PHB	Gonda, K. E., Jendrossek, D., & Molitoris, H. P. (2000). Fungal degradation of the thermoplastic polymer poly-ß-hydroxybutyric acid (PHB) under simulated deep sea pressure. In Life at Interfaces and Under Extreme Conditions (pp. 173-183). Springer, Dordrecht.	No			No			2000.0	Clear zone;Spectrophotometry	PHB was isolated from sodium-gluconate-grown cells of the bacterium Ralstonia eutropha HI6 by sodium-hypochlorite treatment followed by acetone-ether (2: I, v/v) extraction.		Yes	No	Water	Marine	North Sea	No		
Meyerozyma guilliermondii	4929	PHB	Matavulj, M., & Molitoris, H. P. (2009). Marine fungi: degraders of poly-3-hydroxyalkanoate based plastic materials. Zb Mat Srp Prir Nauk, 116, 253-265.	No			No			2009.0	Clear zone;Turbidity	Granulated and powdered BIOPOL	ICI, UK		No	Culture collection	Culture collection		No		
Meyerozyma guilliermondii	4929	PE	Sangale, M. K., Shahnawaz, M., & Ade, A. B. (2019). Potential of fungi isolated from the dumping sites mangrove rhizosphere soil to degrade polythene. Scientific Reports, 9(1), 5390.	No			No			2019.0	Weight loss;Tensilometer;SEM;FTIR				No	Soil	Plant associated	India	No		
Microbacterium flavum	415216	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Microbacterium flavum	415216	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Microbacterium paraoxydans	199592	LDPE	Rajandas, H., Parimannan, S., Sathasivam, K., Ravichandran, M., & Yin, L. S. (2012). A novel FTIR-ATR spectroscopy based technique for the estimation of low-density polyethylene biodegradation. Polymer Testing, 31(8), 1094-1099.	No			No			2012.0	FTIR-ATR;Spectrophotometry;FTIR	Hundred grams of LDPE beads (Basell Polyolefins, Netherlands) were dissolved in 500 ml of O-Xylene (Hamburg Chemicals, Germany) by heating at 70  C until a homogenous solution formed. The solution was allowed to recrystallize and mechanically powdered using a mortar and pestle.	Basell Polyolefins		No				No		
Microbacterium sp.	51671	PCL	Adıgüzel, A. O., & Tunçer, M. (2017). Purification and characterization of cutinase from Bacillus sp. KY0701 isolated from plastic wastes. Preparative Biochemistry and Biotechnology, 47(9), 925-933.	No			No			2017.0	Weight loss;Clear zone	Plastic Waste		No	No	Plastic debris	Soil	Turkey	No		
Microbispora rosea	58117	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Micrococcus luteus	1270	LDPE	Montazer, Z., Habibi Najafi, M. B., & Levin, D. B. (2018). Microbial degradation of low-density polyethylene and synthesis of polyhydroxyalkanoate polymers. Canadian journal of microbiology, 65(3), 224-234.	No			No			2018.0	Weight loss;SEM;GC;FTIR	LDPE powder, with a particle size of 400 μm or less (screen retention of 50 mesh is 4.4%) and a molecular weight range between 20,000 and 150,000, was supplied by Alfa-Asar Company (USA; CAS number 9002-88-4). According to the supplier, the Feedstock Melt Index and density were 3.50 g/10 min (at 190 oC and 2.16 kg load) and 0.9227 g/cm3, respectively. According to supplier’s data sheet, the polymer was pure and free of stabilizing agents. The PE particles sterilized by exposure to UV-light (254 nm) for 1 hour while mixing.	Alfa-Asar Company		No	Soil	Plastic waste dumping site	Iran	No		
Micrococcus luteus	1270	LDPE	Montazer, Z., Habibi-Najafi, M. B., Mohebbi, M., & Oromiehei, A. (2018). Microbial degradation of UV-pretreated low-density polyethylene films by novel polyethylene-degrading bacteria isolated from plastic-dump soil. Journal of Polymers and the Environment, 26(9), 3613-3625.	No			No			2018.0	FTIR;SEM;Microscopy;Weight loss;CG-FIT	Low density polyethylene (Poliran LF0200 grade) granules and film (10 μm thickness; 99.95% purity without any additives and plasticizers) used for pasteurized milk packaging were supplied by Iran Polymer and Petrochemical Institute (IPPI)	Polymer and Petrochemical Institute (IPPI)	Yes	No	Soil	Landfill	Iran	No		
Micrococcus luteus	1270	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;SEM;FTIR;Tensilometer	LDPE, type “FGNX23-D022”;Bionolle (type #3001)	POLICHEM		No	Soil	Soil	Poland	No		
Micrococcus lylae	1273	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;SEM;FTIR;Tensilometer	LDPE, type “FGNX23-D022”;Bionolle (type #3001)	POLICHEM		No	Soil	Soil	Poland	No		
Micrococcus sp.	1271	PE	Kathiresan, K. (2003). Polythene and plastics-degrading microbes from the mangrove soil. Revista de biologia tropical, 51(3-4), 629-633.	No			No			2003.0	Weight loss	Pre weighed discs of 1cm diameter prepared from polythene bags and disposable plastic cups		No	No	Plastic debris	Mangrove	India	No		
Micrococcus sp.	1271	PU	Shah, A. A., Hasan, F., Akhter, J. I., Hameed, A., & Ahmed, S. (2008). Degradation of polyurethane by novel bacterial consortium isolated from soil. Annals of microbiology, 58(3), 381.	No			No			2008.0	Clear zone;CO2;SEM;FTIR	Poly [4,4’-methylenebis (phenyl isocyanate)-alt-1,4-butanediol/poly (butylene adipate)] (Polyurethane, PU) (Sigma-Aldrich, GmbH, Germany) having 1.220 g/ml density and melting temperature about 190 °C, was used in the present study.	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Monascus sp.	1963841	PU	El-Morsy, E. M., Hassan, H. M., & Ahmed, E. (2017). Biodegradative activities of fungal isolates from plastic contaminated soils. Mycosphere, 8(8), 1071-1087.	No			No			2017.0	SEM;Spectrophotometry;Clear zone	Impranil DLN		No	No	Soil	Plastic waste dumping site	Egypt	No		
Monocillium mucidum	3029106	PBSA	Yamamoto-Tamura, K., Hoshino, Y. T., Tsuboi, S., Huang, C., Kishimoto-Mo, A. W., Sameshima-Yamashita, Y., & Kitamoto, H. (2020). Fungal community dynamics during degradation of poly (butylene succinate-co-adipate) film in two cultivated soils in Japan. Bioscience, Biotechnology, and Biochemistry, 1-11.	No			No			2020.0	Luminance	PBSA films used in this study were composed of Bionolle® 3001 (Showa Denko K. K., Tokyo, Japan)	Showa Denko	No	No	Soil	Soil	Japan	No		
Moraxella sp.	479	PE	Kathiresan, K. (2003). Polythene and plastics-degrading microbes from the mangrove soil. Revista de biologia tropical, 51(3-4), 629-633.	No			No			2003.0	Weight loss	Pre weighed discs of 1cm diameter prepared from polythene bags and disposable plastic cups		No	No	Plastic debris	Mangrove	India	No		
Moritella sp.	78556	PCL	Sekiguchi, T., Sato, T., Enoki, M., Kanehiro, H., Uematsu, K., & Kato, C. (2011). Isolation and characterization of biodegradable plastic degrading bacteria from deep-sea environments. JAMSTEC Report of Research and Development, 11, 33-41.	No			No			2011.0	Clear zone	PCL films	Sigma Aldrich	Yes	No	Sediment	Marine	Japan	No		
Mortierella alpina	64518	PE	Koutny, M., Sancelme, M., Dabin, C., Pichon, N., Delort, A. M., & Lemaire, J. (2006). Acquired biodegradability of polyethylenes containing pro-oxidant additives. Polymer degradation and stability, 91(7), 1495-1503.	No			No			2006.0	Microscopy;FTIR;ATR-FTIR;SEC;SEM;NMR	The material samples were transparent HDPE film 20 mm thick and transparent LDPE film 60 mm thick. Both films contained iron photo-inducer, different from the Scott/Gilead compound (Schulman e Bornen, Belgium) supplying radicals through a photo-redox process and an organometallic type thermo-inducer (EPI, Vancouver, Canada) catalysing the primary hydroperoxide decomposition. Both additives were present in both films. To balance the prodegradant activity of the photo- and thermo-inducer during the first year of storage and use under indoor conditions phenolic antioxidants were used in the blends. Due to the added antioxidants the thermalinduction period was longer than 400 h at 60 _C in dark.		No	No	Culture collection	Culture collection		No		
Mortierella lignicola	979712	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Mortierella sp.	1715235	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Mortierella sp.	1715235	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Mucor circinelloides	36080	LDPE	Pramila, R., & Ramesh, K. V. (2011). Biodegradation of low density polyethylene (LDPE) by fungi isolated from marine water a SEM analysis. African Journal of Microbiology Research, 5(28), 5013-5018.	No			No			2011.0	SEM;CO2	LDPE sheets			No	Water	Marine	India	No		
Mucor sp.	1715236	LDPE	Jyoti, S., & Gupta, K. C. (2014). Screening and identification of low density polyethylene (LDPE) degrading soil fungi isolated from polythene polluted sites around Gwalior city (MP). International Journal of Current Microbiology and Applied Sciences, 3(6), 443-448.	No			No			2014.0	Clear zone;Weight loss	Low density polyethylene (LDPE) sheets were obtained from Gwalior Plastic Industry (Gwalior).	Gwalior Plastic Industry 		No	Soil	Plastic waste dumping site	India	No		
Mucor sp.	1715236	PHB	Matavulj, M., & Molitoris, H. P. (1992). Fungal degradation of polyhydroxyalkanoates and a semiquantitative assay for screening their degradation by terrestrial fungi. FEMS microbiology reviews, 9(2-4), 323-331.	No			No			1992.0	Clear zone;Weight loss	Granulated and powdered BIOPOL	ICI, UK		No	Culture collection	Culture collection		No		
Mucor sp.	1715236	PHB	Nishide, H., Toyota, K., & Kimura, M. (1999). Effects of soil temperature and anaerobiosis on degradation of biodegradable plastics in soil and their degrading microorganisms. Soil Science and Plant Nutrition, 45(4), 963-972.	No			No			1999.0	HPLC	PHB, of natural origin, was in powder form and had average molecular weight of 469,000	Sigma Aldrich	Yes	No	Soil	Soil		No		
Mycobacterium sp.	1785	PHA	Boyandin, A. N., Prudnikova, S. V., Karpov, V. A., Ivonin, V. N., Đỗ, N. L., Nguyễn, T. H., ... & Volova, T. G. (2013). Microbial degradation of polyhydroxyalkanoates in tropical soils. International Biodeterioration & Biodegradation, 83, 77-84.	No			No			2013.0	Weight loss;GPC;X-ray	The polymers were synthesized in Wautersia eutropha B5786 microbial culture (the strain is registered in the Russian Collection of Industrial Microorganisms).			No	Soil	Soil	Vietnam	No		
Mycosphaerella arachidis	143450	PHB	Gangurde, N. S., Patil, Y. P., Jain, R., & Sayyed, R. Z. (2017). Poly-β-hydroxybutyrate biodegradation by mixed culture population vis-à-vis single culture population under varying environmental conditions: A new approach.	No			No			2017.0	Weight loss;Clear zone	PHB production was carried out by Alcaligenes sp. RZS 4 (Gene bank accession No. JN374993) using two-step cultivation process.		Yes	No	Soil	Soil	India	No		
Myrothecium gramineum	226117	PU	Brunner, I., Fischer, M., Rüthi, J., Stierli, B., & Frey, B. (2018). Ability of fungi isolated from plastic debris floating in the shoreline of a lake to degrade plastics. PloS one, 13(8), e0202047.	No			No			2018.0	Clear zone	Impranil	Bayer 	No	No		Culture collection	Switzerland	No		
Nesiotobacter exalbescens	197461	LDPE	Rafiq, S., Fathima, F., Shahina, S. J., & Ramesh, K. V. (2018). Biodegradation of Low Density Polyethylene (LDPE) by Halophilic Bacteria Isolated from Solar Saltpans, Kovalam, Chennai. Nature Environment and Pollution Technology, 17(4), 1367-1371.	No			No			2018.0	Clear zone;SEM	LDPE sheets			No	Water	Others	India	No		
Nia vibrissa	155003	PHB	Matavulj, M., & Molitoris, H. P. (2009). Marine fungi: degraders of poly-3-hydroxyalkanoate based plastic materials. Zb Mat Srp Prir Nauk, 116, 253-265.	No			No			2009.0	Clear zone;Turbidity	Granulated and powdered BIOPOL	ICI, UK		No	Culture collection	Culture collection		No		
Nocardia asteroides	1824	PE	Koutny, M., Sancelme, M., Dabin, C., Pichon, N., Delort, A. M., & Lemaire, J. (2006). Acquired biodegradability of polyethylenes containing pro-oxidant additives. Polymer degradation and stability, 91(7), 1495-1503.	No			No			2006.0	Microscopy;FTIR;ATR-FTIR;SEC;SEM;NMR	The material samples were transparent HDPE film 20 mm thick and transparent LDPE film 60 mm thick. Both films contained iron photo-inducer, different from the Scott/Gilead compound (Schulman e Bornen, Belgium) supplying radicals through a photo-redox process and an organometallic type thermo-inducer (EPI, Vancouver, Canada) catalysing the primary hydroperoxide decomposition. Both additives were present in both films. To balance the prodegradant activity of the photo- and thermo-inducer during the first year of storage and use under indoor conditions phenolic antioxidants were used in the blends. Due to the added antioxidants the thermalinduction period was longer than 400 h at 60 _C in dark.		No	No				No		
Nocardiopsis sp.	310350	PHA	Boyandin, A. N., Prudnikova, S. V., Karpov, V. A., Ivonin, V. N., Đỗ, N. L., Nguyễn, T. H., ... & Volova, T. G. (2013). Microbial degradation of polyhydroxyalkanoates in tropical soils. International Biodeterioration & Biodegradation, 83, 77-84.	No			No			2013.0	Weight loss;GPC;X-ray	The polymers were synthesized in Wautersia eutropha B5786 microbial culture (the strain is registered in the Russian Collection of Industrial Microorganisms).			No	Soil	Soil	Vietnam	No		
Ochrobactrum intermedium	94625	LDPE	Montazer, Z., Habibi-Najafi, M. B., Mohebbi, M., & Oromiehei, A. (2018). Microbial degradation of UV-pretreated low-density polyethylene films by novel polyethylene-degrading bacteria isolated from plastic-dump soil. Journal of Polymers and the Environment, 26(9), 3613-3625.	No			No			2018.0	FTIR;SEM;Microscopy;Weight loss;CG-FIT	Low density polyethylene (Poliran LF0200 grade) granules and film (10 μm thickness; 99.95% purity without any additives and plasticizers) used for pasteurized milk packaging were supplied by Iran Polymer and Petrochemical Institute (IPPI)	Polymer and Petrochemical Institute (IPPI)	Yes	No	Soil	Landfill	Iran	No		
Ochrobactrum oryzae	335286	LDPE	Montazer, Z., Habibi-Najafi, M. B., Mohebbi, M., & Oromiehei, A. (2018). Microbial degradation of UV-pretreated low-density polyethylene films by novel polyethylene-degrading bacteria isolated from plastic-dump soil. Journal of Polymers and the Environment, 26(9), 3613-3625.	No			No			2018.0	FTIR;SEM;Microscopy;Weight loss;CG-FIT	Low density polyethylene (Poliran LF0200 grade) granules and film (10 μm thickness; 99.95% purity without any additives and plasticizers) used for pasteurized milk packaging were supplied by Iran Polymer and Petrochemical Institute (IPPI)	Polymer and Petrochemical Institute (IPPI)	Yes	No	Soil	Landfill	Iran	No		
Paecilomyces sp.	40383	PHA	Boyandin, A. N., Prudnikova, S. V., Karpov, V. A., Ivonin, V. N., Đỗ, N. L., Nguyễn, T. H., ... & Volova, T. G. (2013). Microbial degradation of polyhydroxyalkanoates in tropical soils. International Biodeterioration & Biodegradation, 83, 77-84.	No			No			2013.0	Weight loss;GPC;X-ray	The polymers were synthesized in Wautersia eutropha B5786 microbial culture (the strain is registered in the Russian Collection of Industrial Microorganisms).			No	Soil	Soil	Vietnam	No		
Paecilomyces variotii	264951	PHBV	Passos, T. M., Marconato, J. C., & Franchetti, S. M. M. (2015). Biodegradation of films of low density polyethylene (LDPE), poly (hydroxibutyrate-co-valerate)(PHBV), and LDPE/PHBV (70/30) blend with Paecilomyces variotii. Polímeros, 25(1), 29-34.	No			No			2015.0	OM;SEM;FTIR	The polymers Polyhydroxybutyrat e - covalerate- 18% HV (PHBV) (donated by the Department of Materials Engineering - Federal University of São Carlos)	Department of Materials Engineering - Federal University of São Carlos		No	Culture collection	Culture collection		No		
Paenibacillus macerans	44252	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;SEM;FTIR;Tensilometer	LDPE, type “FGNX23-D022”;Bionolle (type #3001)	POLICHEM		No	Soil	Soil	Poland	No		
Paenibacillus sp.	58172	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Paenibacillus sp.	58172	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Paenibacillus sp.	58172	PVA	Liu, Y., Deng, Y., Chen, P., Duan, M., Lin, X., & Zhang, Y. (2019). Biodegradation analysis of polyvinyl alcohol during the compost burial course. Journal of basic microbiology, 59(4), 368-374.	No			No			2019.0	Iodometric analysis;Spectrophotometry	Commercial PVA (degree of polymerization, 1700; degree of alcoholysis, 88 or 99%)	Chang Chun Petrochemical		No	PVF foams	Compost	China	No		
Paenibacillus urinalis	521520	PS	Atiq, N., Ahmed, S., Ali, M. I., Ahmad, B., & Robson, G. (2010). Isolation and identification of polystyrene biodegrading bacteria from soil. African Journal of Microbiology Research, 4(14), 1537-1541.	No			No			2010.0	SEM;FTIR;HPLC	Expanded polystyrene (EPS) solution (2%) in chloroform;Films of pure polystyrene (Mol. Wt. 100,000)	Fluka	Yes	No	Plastic film	Soil	Pakistan	No		
Pantoea sp.	69393	LDPE	Skariyachan, S., Manjunatha, V., Sultana, S., Jois, C., Bai, V., & Vasist, K. S. (2016). Novel bacterial consortia isolated from plastic garbage processing areas demonstrated enhanced degradation for low density polyethylene. Environmental Science and Pollution Research, 23(18), 18307-18319.	No			No			2016.0	FTIR;GC;Tensilometer;SEM;Weight loss;Clear zone	Different forms of plastic used in the study were low-density polyethylene (LDPE) strips (5 × 1 cm) and LDPE pellets (1.0 g l^-1).			No	Soil	Plastic waste dumping site	India	No		
Papiliotrema laurentii	5418	PCL	Benedict, C. V., Cameron, J. A., & Huang, S. J. (1983). Polycaprolactone degradation by mixed and pure cultures of bacteria and a yeast. Journal of Applied Polymer Science, 28(1), 335-342.	No			No			1983.0	Clear zone;GPC	Polycaprolactone 700 (PCL-700), PCL-300, and LPS-60 with molecular weights of 35,000,18,600, and 7,130 Wr, respectively, were obtained from Union Carbide Corp., New York, N.Y. The PCL designated LPS-60 by the manufacturer contains a phthalic acid residue covalently linked to the chain ends but otherwise is structurally identical to PCL-700 and PCL-300. No low molecular weight, contaminants were seen by chromatographic analysis of the polymers using THF, chloroform, or dichloromethane as solvents. Infrared spectroscopy of PCL-700 resulted in a spectrum identical to the published standard.6 All polymers showed broad molecular weight distributions. Polydispersities (Mv/Mn) ranged from 1.892 to 1.978.	Union Carbide		No	Sediment 	River/Lake	USA	No		
Papiliotrema laurentii	5418	PEA	Hung, C. S., Barlow, D. E., Varaljay, V. A., Drake, C. A., Crouch, A. L., Russell Jr, J. N., ... & Biffinger, J. C. (2019). The biodegradation of polyester and polyester polyurethane coatings using Papiliotrema laurentii. International Biodeterioration & Biodegradation, 139, 34-43.	No			No			2019.0	Clear zone;GPC;FTIR	Impranil DLN	Bayer 	No	No	Aircraft	Others		No		
Papiliotrema laurentii	5418	PES	Hung, C. S., Barlow, D. E., Varaljay, V. A., Drake, C. A., Crouch, A. L., Russell Jr, J. N., ... & Biffinger, J. C. (2019). The biodegradation of polyester and polyester polyurethane coatings using Papiliotrema laurentii. International Biodeterioration & Biodegradation, 139, 34-43.	No			No			2019.0	Clear zone;GPC;FTIR	Impranil DLN	Bayer 	No	No	Aircraft	Others		No		
Papiliotrema laurentii	5418	PU	Hung, C. S., Barlow, D. E., Varaljay, V. A., Drake, C. A., Crouch, A. L., Russell Jr, J. N., ... & Biffinger, J. C. (2019). The biodegradation of polyester and polyester polyurethane coatings using Papiliotrema laurentii. International Biodeterioration & Biodegradation, 139, 34-43.	No			No			2019.0	Clear zone;GPC;FTIR	Impranil DLN	Bayer 	No	No	Aircraft	Others		No		
Papiliotrema laurentii	5418	PBSA	Yamamoto-Tamura, K., Hoshino, Y. T., Tsuboi, S., Huang, C., Kishimoto-Mo, A. W., Sameshima-Yamashita, Y., & Kitamoto, H. (2020). Fungal community dynamics during degradation of poly (butylene succinate-co-adipate) film in two cultivated soils in Japan. Bioscience, Biotechnology, and Biochemistry, 1-11.	No			No			2020.0	Luminance	PBSA films used in this study were composed of Bionolle® 3001 (Showa Denko K. K., Tokyo, Japan)	Showa Denko	No	No	Soil	Soil	Japan	No		
Paraphoma chrysanthemicola	798071	PBS	Koitabashi, M., Noguchi, M. T., Sameshima-Yamashita, Y., Hiradate, S., Suzuki, K., Yoshida, S., ... & Kitamoto, H. K. (2012). Degradation of biodegradable plastic mulch films in soil environment by phylloplane fungi isolated from gramineous plants. AMB express, 2(1), 40.	No			No			2012.0	NMR;SEM;Clear zone	PBS film (Bionolle 1001G) have an average molecular weight 104 of 20 to 25 × and a thickness of 20 µm.	Showa Denko	No	No	Leaf	Plant associated	Japan	No		
Paraphoma chrysanthemicola	798071	PBSA	Koitabashi, M., Noguchi, M. T., Sameshima-Yamashita, Y., Hiradate, S., Suzuki, K., Yoshida, S., ... & Kitamoto, H. K. (2012). Degradation of biodegradable plastic mulch films in soil environment by phylloplane fungi isolated from gramineous plants. AMB express, 2(1), 40.	No			No			2012.0	NMR;SEM;Clear zone	PBSA (Bionolle EM- 104). 301, average molecular weight, 12 to 15 ×4;Bionelle 3001 G)	Showa Denko	No	No	Leaf	Plant associated	Japan	No		
Paraphoma chrysanthemicola	798071	PBS	Koitabashi, M., Sameshima–Yamashita, Y., Koike, H., Sato, T., Moriwaki, J., Morita, T., ... & Kitamoto, H. (2016). Biodegradable plastic-degrading activity of various species of Paraphoma. Journal of oleo science, 65(7), 621-627.	No			No			2016.0	Luminance 	PBS mulch film Bionolle 1001G, MW 20x10^4, thickness 20 um	Showa Denko	No	No	Barley	Plant associated	Japan	No		
Paraphoma chrysanthemicola	798071	PBSA	Koitabashi, M., Sameshima–Yamashita, Y., Koike, H., Sato, T., Moriwaki, J., Morita, T., ... & Kitamoto, H. (2016). Biodegradable plastic-degrading activity of various species of Paraphoma. Journal of oleo science, 65(7), 621-627.	No			No			2016.0	Luminance 	PBSA mulch film Bionolle 3001G, MW 25x10^4, thickness 20 um	Showa Denko	No	No	Barley	Plant associated	Japan	No		
Paraphoma radicina	437017	PBS	Koitabashi, M., Sameshima–Yamashita, Y., Koike, H., Sato, T., Moriwaki, J., Morita, T., ... & Kitamoto, H. (2016). Biodegradable plastic-degrading activity of various species of Paraphoma. Journal of oleo science, 65(7), 621-627.	No			No			2016.0	Luminance 	PBS mulch film Bionolle 1001G, MW 20x10^4, thickness 20 um	Showa Denko	No	No	Barley	Plant associated	Japan	No		
Paraphoma radicina	437017	PBSA	Koitabashi, M., Sameshima–Yamashita, Y., Koike, H., Sato, T., Moriwaki, J., Morita, T., ... & Kitamoto, H. (2016). Biodegradable plastic-degrading activity of various species of Paraphoma. Journal of oleo science, 65(7), 621-627.	No			No			2016.0	Luminance 	PBSA mulch film Bionolle 3001G, MW 25x10^4, thickness 20 um	Showa Denko	No	No	Barley	Plant associated	Japan	No		
Paraphoma sp.	1755435	PBS	Koitabashi, M., Sameshima–Yamashita, Y., Koike, H., Sato, T., Moriwaki, J., Morita, T., ... & Kitamoto, H. (2016). Biodegradable plastic-degrading activity of various species of Paraphoma. Journal of oleo science, 65(7), 621-627.	No			No			2016.0	Spectrophotometry	Bionolle1001G	Showa Denko		No	Barley	Plant associated	Japan	No		
Paraphoma sp.	1755435	PBSA	Koitabashi, M., Sameshima–Yamashita, Y., Koike, H., Sato, T., Moriwaki, J., Morita, T., ... & Kitamoto, H. (2016). Biodegradable plastic-degrading activity of various species of Paraphoma. Journal of oleo science, 65(7), 621-627.	No			No			2016.0	Spectrophotometry	Bionolle3001G	Showa Denko		No	Barley	Plant associated	Japan	No		
Paraphoma sp.	1755435	PBSA	Sameshima-Yamashita, Y., Koitabashi, M., Tsuchiya, W., Suzuki, K., Watanabe, T., Shinozaki, Y., ... & Kitamoto, H. (2016). Enhancement of biodegradable plastic-degrading enzyme production from Paraphoma-like fungus, strain B47-9. Journal of oleo science, ess15207.	No			No			2016.0	Spectrophotometry				No	Culture collection	Culture collection		No		
Parengyodontium album	37998	PLA	Antipova, T. V., Zhelifonova, V. P., Zaitsev, K. V., Nedorezova, P. M., Aladyshev, A. M., Klyamkina, A. N., ... & Kozlovsky, A. G. (2018). Biodegradation of Poly-ε-caprolactones and Poly-l-lactides by Fungi. Journal of Polymers and the Environment, 26(12), 4350-4359.	No			No			2018.0	Weight loss;MS	PLA was obtained upon ring-opening polymerization of l-lactide in the presence of catalytic amounts of aluminium complexes			No	Wall	Culture collection	Russia	No		
Parengyodontium album	37998	PLA	Jarerat, A., & Tokiwa, Y. (2001). Degradation of Poly (L‐lactide) by a Fungus. Macromolecular Bioscience, 1(4), 136-140.	No			No			2001.0	TOC;SEM;Weight loss	A PLA pellet, LACTY #1012 (number average molecular weight, M Ð n = 2.86105), and commercial PLA-blown film were obtained from Shimadzu Co. Ltd	Shimadzu		No	Culture collection	Culture collection		No		
Paucimonas lemoignei	29443	PHB	Martínez-Tobón, D. I., Gul, M., Elias, A. L., & Sauvageau, D. (2018). Polyhydroxybutyrate (PHB) biodegradation using bacterial strains with demonstrated and predicted PHB depolymerase activity. Applied microbiology and biotechnology, 102(18), 8049-8067.	No			No			2018.0	Clear zone;Weight loss	PHB pellets (BRS Bulk Bio-pellets, Bulk Reef Supply, Golden Valley, USA) and acetic acid (Fisher Scientific) were used to produce PHB films by solvent casting as described by Anbukarasu et al. (2015).	Bulk Reef Supply	Yes	No		Culture collection		No		
Penicillium adametzii	69763	PHB	Mergaert, J., Anderson, C., Wouters, A., Swings, J., & Kersters, K. F. E. M. S. (1992). Biodegradation of polyhydroxyalkanoates. FEMS microbiology reviews, 9(2-4), 317-321.	No			No			1992.0	Tensilometer;Weight loss	All bioplastics were obtained from ICI Biological Products (Billingham, UK), as injection moulded, dogbone-shaped tensile test pieces.	ICI, UK		No	Plastic debris		Belgium	No		
Penicillium aurantiogriseum	36655	PLA	Antipova, T. V., Zhelifonova, V. P., Zaitsev, K. V., Nedorezova, P. M., Aladyshev, A. M., Klyamkina, A. N., ... & Kozlovsky, A. G. (2018). Biodegradation of Poly-ε-caprolactones and Poly-l-lactides by Fungi. Journal of Polymers and the Environment, 26(12), 4350-4359.	No			No			2018.0	Weight loss;MS	PLA was obtained upon ring-opening polymerization of l-lactide in the presence of catalytic amounts of aluminium complexes			No	Barrel with fruit test	Culture collection	Ukraine	No		
Penicillium chermesinum	63820	PHB	Mergaert, J., Wouters, A., Swings, J., & Anderson, C. (1995). In situ biodegradation of poly (3-hydroxybutyrate) and poly (3-hydroxybutyrate-co-3-hydroxyvalerate) in natural waters. Canadian Journal of Microbiology, 41(13), 154-159.	No			No			1995.0	GPC;Tensilometer;Weight loss;Clear zone	Bioplastics were obtained from ICI Biological Products (Billingham, United Kingdom) as injection molded, dog bone-shaped tensile test pieces 83 mm long, 2 mm thick, and weighing approximately 1.75 g or as powder. Two polymers were investigated: homopolymer P(3HB) (high-purity grade; batch no. GV9/1) and copolymer P(3HB-co-10%3HV) (technical purity grade; batch no. P032). Tensile test pieces contained 0.5 [P(3HB)] or 1.0 [P(3HB-co-10%3HV)] part per hundred resin of boron nitride as a nucleant.	ICI, UK		No	Plastic debris	Soil	Belgium	No		
Penicillium chrysogenum	5076	PU	Álvarez-Barragán, J., Domínguez-Malfavón, L., Vargas-Suárez, M., González-Hernández, R., Aguilar-Osorio, G., & Loza-Tavera, H. (2016). Biodegradative activities of selected environmental fungi on a polyester polyurethane varnish and polyether polyurethane foams. Appl. Environ. Microbiol., 82(17), 5225-5235.	No			No			2016.0	FTIR;MS;SEM;Clear zone	Impranil	Bayer 		No			Mexico	No		
Penicillium chrysogenum	5076	PLA	Antipova, T. V., Zhelifonova, V. P., Zaitsev, K. V., Nedorezova, P. M., Aladyshev, A. M., Klyamkina, A. N., ... & Kozlovsky, A. G. (2018). Biodegradation of Poly-ε-caprolactones and Poly-l-lactides by Fungi. Journal of Polymers and the Environment, 26(12), 4350-4359.	No			No			2018.0	Weight loss;MS	PLA was obtained upon ring-opening polymerization of l-lactide in the presence of catalytic amounts of aluminium complexes			No	Soil	Culture collection	Russia	No		
Penicillium chrysogenum	5076	PCL	Bentham, R. H., Morton, L. H. G., & Allen, N. G. (1987). Rapid assessment of the microbial deterioration of polyurethanes. International biodeterioration, 23(6), 377-386.	No			No			1987.0	Clear zone;Tensilometer;Weight loss	Two similar formulations of polyurethane foam were investigated, supplied as dumbbell-shaped test pieces. The materials were both polyester polyurethanes, one formulation, however, contained VINYZENE BP (10,10'-oxybis-phenoxarsine) as the formulation biocide. Another formulation was also available, an unprotected polyester polyurethane elastomer.		No	No	Plastic debris	Compost		No		
Penicillium chrysogenum	5076	PLA	Nair, N. R., Sekhar, V. C., & Nampoothiri, K. M. (2016). Augmentation of a microbial consortium for enhanced polylactide (PLA) degradation. Indian journal of microbiology, 56(1), 59-63.	No			No			2016.0	Weight loss;SEM;Spectrophotometry	Commercial grade PLA with molecular weight of 85,000–160,000	Sigma Aldrich	Yes	No			India	No		
Penicillium chrysogenum	5076	PLA	Nair, N. R., Sekhar, V. C., & Nampoothiri, K. M. (2016). Augmentation of a microbial consortium for enhanced polylactide (PLA) degradation. Indian journal of microbiology, 56(1), 59-63.	No			No			2016.0	Weight loss;SEM;Spectrophotometry;Clear zone	Commercial grade PLA with molecular weight of 85,000–160,000	Sigma Aldrich	Yes	No			India	No		
Penicillium chrysogenum	5076	HDPE	Ojha, N., Pradhan, N., Singh, S., Barla, A., Shrivastava, A., Khatua, P., ... & Bose, S. (2017). Evaluation of HDPE and LDPE degradation by fungus, implemented by statistical optimization. Scientific reports, 7, 39515.	No			No			2017.0	SEM;AFM;FTIR;Weight loss	HDPE and LDPE sheets were collected from department of Biological Sciences and Earth Science laboratories situated at IISER Kolkata, Mohanpur Campus, West Bengal. The sheets (test samples) were cut into small strips of 6 * 6 cm and transferred to a fresh solution containing 70 ml Tween 80, 10 ml bleach, and 983 ml distilled water and stirring for 30 to 60 minutes and sterilized as followed by El-Shafei et al.27 with a few modifications.	Biological Sciences and Earth Science laboratories		No	Soil	Plastic waste dumping site	India	No		
Penicillium chrysogenum	5076	LDPE	Ojha, N., Pradhan, N., Singh, S., Barla, A., Shrivastava, A., Khatua, P., ... & Bose, S. (2017). Evaluation of HDPE and LDPE degradation by fungus, implemented by statistical optimization. Scientific reports, 7, 39515.	No			No			2017.0	SEM;AFM;FTIR;Weight loss	HDPE and LDPE sheets were collected from department of Biological Sciences and Earth Science laboratories situated at IISER Kolkata, Mohanpur Campus, West Bengal. The sheets (test samples) were cut into small strips of 6 * 6 cm and transferred to a fresh solution containing 70 ml Tween 80, 10 ml bleach, and 983 ml distilled water and stirring for 30 to 60 minutes and sterilized as followed by El-Shafei et al.27 with a few modifications.	Biological Sciences and Earth Science laboratories		No	Soil	Plastic waste dumping site	India	No		
Penicillium chrysogenum	5076	PE	Sangale, M. K., Shahnawaz, M., & Ade, A. B. (2019). Potential of fungi isolated from the dumping sites mangrove rhizosphere soil to degrade polythene. Scientific Reports, 9(1), 5390.	No			No			2019.0	Weight loss;Tensilometer;SEM;FTIR				No	Soil	Plant associated	India	No		
Penicillium daleae	63821	PHB	Mergaert, J., Anderson, C., Wouters, A., Swings, J., & Kersters, K. F. E. M. S. (1992). Biodegradation of polyhydroxyalkanoates. FEMS microbiology reviews, 9(2-4), 317-321.	No			No			1992.0	Tensilometer;Weight loss	All bioplastics were obtained from ICI Biological Products (Billingham, UK), as injection moulded, dogbone-shaped tensile test pieces.	ICI, UK		No	Plastic debris		Belgium	No		
Penicillium glabrum	69773	PE Blend	Seneviratne, G., Tennakoon, N. S., Nandasena, K. A., & Weerasekara, M. L. M. A. W. (2006). Polyethylene biodegradation by a developed Penicillium-Bacillus biofilm.	No			No			2006.0	Microscopy;CO2;GC;Weight loss	Fresh pieces of DPE (degradable by UV and oxidation, PDQ) 	Willow Ridge Plastics		No	Plastic debris	Soil		No		
Penicillium griseofulvum	5078	PU	Brunner, I., Fischer, M., Rüthi, J., Stierli, B., & Frey, B. (2018). Ability of fungi isolated from plastic debris floating in the shoreline of a lake to degrade plastics. PloS one, 13(8), e0202047.	No			No			2018.0	Clear zone	Impranil	Bayer 	No	No	Plastic debris	River/Lake	Switzerland	No		
Penicillium janthinellum	5079	PHB	Mergaert, J., Wouters, A., Swings, J., & Anderson, C. (1995). In situ biodegradation of poly (3-hydroxybutyrate) and poly (3-hydroxybutyrate-co-3-hydroxyvalerate) in natural waters. Canadian Journal of Microbiology, 41(13), 154-159.	No			No			1995.0	Weight loss;Tensilometer;Clear zone	The polymers were obtained from ZENECA Bio Products either as injection-moulded, dog bone-shaped tensile test pieces, 83 mm long, 2 mm thick, with a total surface area of approx. 19.5 cm2, and weighing approximately 1.75 g, or as powder. Three polymers were investigated: homopolymer P(3HB) batch G08, copolymer P(3HB-co-10%-3HV) batch PSMll+PSM20, and copolymer P(3HB-co-20%-3HV) batch PSM11.	Zeneca Bioproducts		No	Water		Belgium	No		
Penicillium ochrochloron	69780	PU	Barratt, S. R., Ennos, A. R., Greenhalgh, M., Robson, G. D., & Handley, P. S. (2003). Fungi are the predominant micro‐organisms responsible for degradation of soil‐buried polyester polyurethane over a range of soil water holding capacities. Journal of applied microbiology, 95(1), 78-85.	No			No			2003.0	Clear zone;SEM;Tensilometer				No	Plastic debris	Soil		No		
Penicillium ochrochloron	69780	PHB	Mergaert, J., Anderson, C., Wouters, A., Swings, J., & Kersters, K. F. E. M. S. (1992). Biodegradation of polyhydroxyalkanoates. FEMS microbiology reviews, 9(2-4), 317-321.	No			No			1992.0	Tensilometer;Weight loss	All bioplastics were obtained from ICI Biological Products (Billingham, UK), as injection moulded, dogbone-shaped tensile test pieces.	ICI, UK		No	Plastic debris		Belgium	No		
Penicillium oxalicum	69781	PCL	Li, F., Yu, D., Lin, X., Liu, D., Xia, H., & Chen, S. (2012). Biodegradation of poly (ε-caprolactone)(PCL) by a new Penicillium oxalicum strain DSYD05-1. World Journal of Microbiology and Biotechnology, 28(10), 2929-2935.	No			No			2012.0	MS;Clear zone;SEM;Weight loss;	Powdered PCL, molecular weight 8x10^4 Da, was obtained from the Solvay International Chemical Group (Belgium).	Solvay International Chemical Group		No	Soil	Soil	China	No		
Penicillium oxalicum	69781	HDPE	Ojha, N., Pradhan, N., Singh, S., Barla, A., Shrivastava, A., Khatua, P., ... & Bose, S. (2017). Evaluation of HDPE and LDPE degradation by fungus, implemented by statistical optimization. Scientific reports, 7, 39515.	No			No			2017.0	SEM;AFM;FTIR;Weight loss	HDPE and LDPE sheets were collected from department of Biological Sciences and Earth Science laboratories situated at IISER Kolkata, Mohanpur Campus, West Bengal. The sheets (test samples) were cut into small strips of 6 * 6 cm and transferred to a fresh solution containing 70 ml Tween 80, 10 ml bleach, and 983 ml distilled water and stirring for 30 to 60 minutes and sterilized as followed by El-Shafei et al.27 with a few modifications.	Biological Sciences and Earth Science laboratories		No	Soil	Plastic waste dumping site	India	No		
Penicillium oxalicum	69781	LDPE	Ojha, N., Pradhan, N., Singh, S., Barla, A., Shrivastava, A., Khatua, P., ... & Bose, S. (2017). Evaluation of HDPE and LDPE degradation by fungus, implemented by statistical optimization. Scientific reports, 7, 39515.	No			No			2017.0	SEM;AFM;FTIR;Weight loss	HDPE and LDPE sheets were collected from department of Biological Sciences and Earth Science laboratories situated at IISER Kolkata, Mohanpur Campus, West Bengal. The sheets (test samples) were cut into small strips of 6 * 6 cm and transferred to a fresh solution containing 70 ml Tween 80, 10 ml bleach, and 983 ml distilled water and stirring for 30 to 60 minutes and sterilized as followed by El-Shafei et al.27 with a few modifications.	Biological Sciences and Earth Science laboratories		No	Soil	Plastic waste dumping site	India	No		
Penicillium restrictum	69784	PHB	Mergaert, J., Anderson, C., Wouters, A., Swings, J., & Kersters, K. F. E. M. S. (1992). Biodegradation of polyhydroxyalkanoates. FEMS microbiology reviews, 9(2-4), 317-321.	No			No			1992.0	Tensilometer;Weight loss	All bioplastics were obtained from ICI Biological Products (Billingham, UK), as injection moulded, dogbone-shaped tensile test pieces.	ICI, UK		No	Plastic debris		Belgium	No		
Penicillium roqueforti	5082	PLA	Pranamuda, H., Tokiwa, Y., & Tanaka, H. (1997). Polylactide degradation by an Amycolatopsis sp. Appl. Environ. Microbiol., 63(4), 1637-1640.	No			No			1997.0	Clear zone;TOC;SEM	PLA with 100% L-lactic acid content was obtained from Shimadzu Co. Ltd., while PLA with 94% L-lactic acid content was obtained from Cargill Inc. The number-average molecular weights (Mn) were 1.88x10^5 and 1.22x10^4, respectively	Shimadzu	Yes	No	Soil	Soil	Japan	No		
Penicillium roqueforti	5082	PLA	Torres, A., Li, S. M., Roussos, S., & Vert, M. (1996). Screening of microorganisms for biodegradation of poly (lactic-acid) and lactic acid-containing polymers. Appl. Environ. Microbiol., 62(7), 2393-2397.	No			No			1996.0	HPLC;SEM	Typically, 1 liter of DL-LA commercial solution was heated under normal pressure to gently distillate water. When the temperature reached 1308C, vacuum was applied and distillation was controlled as desired. One fraction of racemic oligomers (Mw 5 1,000, I 5 Mw/Mn 5 1.3) was used for the screening of filamentous fungi, and another one (Mw 5 2,000, I 5 1.3) was used for soil screening. Molecular weights were determined by size exclusion chromatography. 	Sigma Aldrich	Yes	No		Culture collection		No		
Penicillium simplicissimum	69488	PETG	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	SG is a biodegradable aliphatic polyester, made of succinic acid, adipic acid, butanediol and ethylene glycol. It was donated by SKI in powder form (200 mm) with a melt index of 30 g/10 min at 190C.	SKI		No	Plastic debris	Soil	South Korea	No		
Penicillium simplicissimum	69488	PHB	Mergaert, J., Wouters, A., Swings, J., & Anderson, C. (1995). In situ biodegradation of poly (3-hydroxybutyrate) and poly (3-hydroxybutyrate-co-3-hydroxyvalerate) in natural waters. Canadian Journal of Microbiology, 41(13), 154-159.	No			No			1995.0	Spectrophotometry	Purified PHB granules wereprepared as described by Smibert and Krieg [14].		Yes	No	Culture collection	Culture collection		Yes		
Penicillium simplicissimum	69488	PHBV	Renstad, R., Karlsson, S., & Albertsson, A. C. (1999). The influence of processing induced differences in molecular structure on the biological and non-biological degradation of poly (3-hydroxybutyrate-co-3-hydroxyvalerate), P (3-HB-co-3-HV). Polymer degradation and stability, 63(2), 201-211.	No			No			1999.0	SEC;DSC;X-ray;FTIR;Tensilometer;Weight loss	Poly(3-hydroxybutyrate-co-3-hydroxyvalerate), P(3-HB-co-3-HV) was purchased from Zeneca Bio Products under the trade name Biopol D400G. The polymer contained 7% hydroxyvalerate and a nucleant, BN. The average molecular weights were Mw: 320 000 and Mn:110 000 according to the manufacturer.	Zeneca Bioproducts		No	Culture collection	Culture collection		No		
Penicillium simplicissimum	69488	PE	Yamada-Onodera, K., Mukumoto, H., Katsuyaya, Y., Saiganji, A., & Tani, Y. (2001). Degradation of polyethylene by a fungus, Penicillium simplicissimum YK. Polymer degradation and stability, 72(2), 323-327.	No			No			2001.0	GPC;FTIR	High density PE	Asahi Chemical Industry		No				No		
Penicillium sp.	5081	PC	Arefian, M., Zia, M., Tahmourespour, A., & Bayat, M. (2013). Polycarbonate biodegradation by isolated molds using clear-zone and atomic force microscopic methods. International Journal of Environmental Science and Technology, 10(6), 1319-1324.	No			No			2013.0	Clear zone;AFM				No	Soil	Soil	Iran	No		
Penicillium sp.	5081	PCL	Bentham, R. H., Morton, L. H. G., & Allen, N. G. (1987). Rapid assessment of the microbial deterioration of polyurethanes. International biodeterioration, 23(6), 377-386.	No			No			1987.0	Clear zone;Tensilometer;Weight loss	Two similar formulations of polyurethane foam were investigated, supplied as dumbbell-shaped test pieces. The materials were both polyester polyurethanes, one formulation, however, contained VINYZENE BP (10,10'-oxybis-phenoxarsine) as the formulation biocide. Another formulation was also available, an unprotected polyester polyurethane elastomer.		No	No	Plastic debris	Compost		No		
Penicillium sp.	5081	PHA	Boyandin, A. N., Prudnikova, S. V., Karpov, V. A., Ivonin, V. N., Đỗ, N. L., Nguyễn, T. H., ... & Volova, T. G. (2013). Microbial degradation of polyhydroxyalkanoates in tropical soils. International Biodeterioration & Biodegradation, 83, 77-84.	No			No			2013.0	Weight loss;GPC;X-ray	The polymers were synthesized in Wautersia eutropha B5786 microbial culture (the strain is registered in the Russian Collection of Industrial Microorganisms).			No	Soil	Soil	Vietnam	No		
Penicillium sp.	5081	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Penicillium sp.	5081	LDPE	Jyoti, S., & Gupta, K. C. (2014). Screening and identification of low density polyethylene (LDPE) degrading soil fungi isolated from polythene polluted sites around Gwalior city (MP). International Journal of Current Microbiology and Applied Sciences, 3(6), 443-448.	No			No			2014.0	Clear zone;Weight loss	Low density polyethylene (LDPE) sheets were obtained from Gwalior Plastic Industry (Gwalior).	Gwalior Plastic Industry 		No	Soil	Plastic waste dumping site	India	No		
Penicillium sp.	5081	PCL	Tokiwa, Y., & Suzuki, T. (1977). Hydrolysis of polyesters by lipases. Nature, 270(5632), 76-78.	No			No			1977.0	TOC	PCL was prepared by ring opening polymerisation of E-caprolactone in benzene in a nitrogen atmosphere at 60 °C with a diethylzinc-water catalyst system.		Yes	No				Yes		
Penicillium sp.	5081	PLA	Torres, A., Li, S. M., Roussos, S., & Vert, M. (1996). Screening of microorganisms for biodegradation of poly (lactic-acid) and lactic acid-containing polymers. Appl. Environ. Microbiol., 62(7), 2393-2397.	No			No			1996.0	HPLC;SEM	Typically, 1 liter of DL-LA commercial solution was heated under normal pressure to gently distillate water. When the temperature reached 1308C, vacuum was applied and distillation was controlled as desired. One fraction of racemic oligomers (Mw 5 1,000, I 5 Mw/Mn 5 1.3) was used for the screening of filamentous fungi, and another one (Mw 5 2,000, I 5 1.3) was used for soil screening. Molecular weights were determined by size exclusion chromatography. 	Sigma Aldrich	Yes	No		Culture collection		No		
Pestalotiopsis sp.	36460	PU	Lii, S. B. W., Wong, C., Al-Obaidi, J. R., Rahmad, N., Mujahid, A., & Mueller, M. (2017). Ability of endophytic fungi isolated from Nepenthes ampullaria to degrade polyurethane. Malysian Journal of Microbiology, 13(3), 172.	No			No			2017.0	Clear zone	Aqueous PUR dispersion	Bayer 		No	Nepenthes ampullaria	Plant associated		No		
Phanerochaete chrysosporium	2822231	PVC Blend	Ali, M. I., Ahmed, S., Javed, I., Ali, N., Atiq, N., Hameed, A., & Robson, G. (2014). Biodegradation of starch blended polyvinyl chloride films by isolated Phanerochaete chrysosporium PV1. International Journal of Environmental Science and Technology, 11(2), 339-348.	No			No			2014.0	SEM;GPC;FTIR;Spectrophotometry;CO2;NMR	Casting of polyvinyl chloride films blended with starch were carried out in petri plates by taking PVC and starch 2 % (w/v) in chloroform.			No	PVC film			No		
Phanerochaete chrysosporium	2822231	PVC	Ali, M. I., Ahmed, S., Robson, G., Javed, I., Ali, N., Atiq, N., & Hameed, A. (2014). Isolation and molecular characterization of polyvinyl chloride (PVC) plastic degrading fungal isolates. Journal of basic microbiology, 54(1), 18-27.	No			No			2014.0	SEM;CO2;FTIR;Spectrophotometry;NMR;GPC	Thin films of PVC (2% w/v) were prepared in petri plates by dissolving 0.2 g of PVC (Aldrich) in 10 ml of solvent tetrahydrofuran (THF; 99%; Merck).	Sigma Aldrich		No	PVC film	Sewage/Sludge		No		
Phanerochaete chrysosporium	2822231	PVC Blend	Ali, M. I., Perveen, Q., Ahmad, B., Javed, I., Razi-Ul-Hussnain, R., Andleeb, S., ... & Hameed, A. (2009). Studies on biodegradation of cellulose blended polyvinyl chloride films. Int J Agric Biol, 11(5), 577-580.	No			No			2009.0	FTIR;CO2	 Cellulose blended Polyvinyl chloride (PVC) films were prepared by casting in Petri plates			No	PVC film			No		
Phanerochaete chrysosporium	2822231	Nylon	Deguchi, T., Kakezawa, M., & Nishida, T. (1997). Nylon biodegradation by lignin-degrading fungi. Appl. Environ. Microbiol., 63(1), 329-331.	No			No			1997.0	GPC	Nylon-66 membrane	Sartrius		No				No		
Phanerochaete chrysosporium	2822231	PVA	Huang, M. H., Shih, Y. P., & Liu, S. M. (2002). Biodegradation of polyvinyl alcohol by Phanerochaete chrysosporium after pretreatment with Fenton's reagent. Journal of Environmental Science and Health, Part A, 37(1), 29-41.	No			No			2002.0	COD;TOC;GPC	PVA powder (BP05 and BF17, which have a polymerization degree of 550–650 and 1700–1800, respectively and a saponification degree of 86–89 mole% and 98.5–99.2 mole%, respectively	Chang Chun Petrochemical	No	No		Culture collection		No		
Phanerochaete chrysosporium	2822231	PP	Jeyakumar, D., Chirsteen, J., & Doble, M. (2013). Synergistic effects of pretreatment and blending on fungi mediated biodegradation of polypropylenes. Bioresource technology, 148, 78-85.	No			No			2013.0	Weight loss;SEM;FTIR;TGA;MS	Commercial PP films (PP) [Reliance Industries Ltd., Mumbai, India], Starch blended PP (ST-PP) [Biobags Ltd., Chennai, India], and Catalyst blended PP (MI-PP) [Symphony, Chennai, India] are received as gifts. Films of Size 8   2.5 cm and 0.05 mm thick were used in these experiments. All the chemicals were procured from (HIMEDIA Laboratories, India).	Reliance Industries	No	No	Culture collection	Culture collection		No		
Phanerochaete chrysosporium	2822231	PVC	Kırbaş, Z., Keskin, N., & Güner, A. (1999). Biodegradation of polyvinylchloride (PVC) by white rot fungi. Bulletin of environmental contamination and toxicology, 63(3), 335-342.	No			No			1999.0	FTIR;Spectrophotometry;Weight loss;Viscosimeter	PVC having low molecular weight was used for the studies. The polymer supplied from Aldrich Chemical Company Inc. PVC was transformed into films before adding in the liquid culture media.	Sigma Aldrich	Yes	No	Culture collection	Culture collection		No		
Phanerochaete chrysosporium	2822231	LDPE Blend	Lee, B., Pometto, A. L., Fratzke, A., & Bailey, T. B. (1991). Biodegradation of degradable plastic polyethylene by Phanerochaete and Streptomyces species. Appl. Environ. Microbiol., 57(3), 678-685.	No			No			1991.0	Weight loss;Tensilometer;GPC;GPC	Archer-Daniels-Midland POLYCLEAN masterbatch degradable plastic films made with linear low density polyethylene containing pro-oxidant and 6% starch were used. Pro-oxidants are mixtures of transition metals (i.e., Fe, Zn, Ni, and/or Mn) and lipids (i.e., corn or soybean oil) which are compounded into the final polyethylene product at very low levels. Films were commercially prepared according to Archer-Daniels-Midland-recommended specifications.	Archer-Daniels-Midland	No	No	Culture collection	Culture collection		No		
Phanerochaete chrysosporium	2822231	LDPE Blend	Manzur, A., Cuamatzi, F., & Favela, E. (1997). Effect of the growth of Phanerochaete chrysosporium in a blend of low density polyethylene and sugar cane bagasse. Journal of applied polymer science, 66(1), 105-111.	No			No			1997.0	DSC;WAXS;TGA;Weight loss	Washed SCB (sugar cane bagasse) was mixed with commercial LDPE (PX 17070, Pemex), in equal parts by weight (50:50), in a Banbury mixer at 1507C and 40 rpm for 10 min. The composite material was ground and sieved to obtain particle sizes between 0.8 and 2.4 mm.	Pemex	No	No				No		
Phanerochaete chrysosporium	2822231	LDPE	Manzur, A., Limón‐González, M., & Favela‐Torres, E. (2004). Biodegradation of physicochemically treated LDPE by a consortium of filamentous fungi. Journal of Applied Polymer Science, 92(1), 265-271.	No			No			2004.0	CO2;DSC;WAXS;GC;FTIR;SEM	Commercial low density polyethylene was used (17,070, produced by Pemex, Mexico). Its density and flow index values were 0.917 g/cc and 7 g/10 min, respectively.	Pemex		No	Culture collection	Culture collection		No		
Phanerochaete chrysosporium	2822231	LDPE Blend	Orhan, Y., & Büyükgüngör, H. (2000). Enhancement of biodegradability of disposable polyethylene in controlled biological soil. International biodeterioration & biodegradation, 45(1-2), 49-55.	No			No			2000.0	FTIR;CO2;Tensilometer;Viscosimeter	The film used in this study was low density polyethylene containing 12% starch (LDPE/starch), autoxidizable fatty acid ester and catalytic agents (transition metals). The biodegradable plastic has natural color, slightly grainy texture and corn-like smell (Krupp and Jewell, 1992). LDPE/starch blend (2.54x15.24 cm) were cut and disinfected.		No	No	Soil	Soil	Turkey	No		
Phanerochaete chrysosporium	2822231	PHBV	Renstad, R., Karlsson, S., & Albertsson, A. C. (1999). The influence of processing induced differences in molecular structure on the biological and non-biological degradation of poly (3-hydroxybutyrate-co-3-hydroxyvalerate), P (3-HB-co-3-HV). Polymer degradation and stability, 63(2), 201-211.	No			No			1999.0	SEC;DSC;X-ray;FTIR;Tensilometer;Weight loss	Poly(3-hydroxybutyrate-co-3-hydroxyvalerate), P(3-HB-co-3-HV) was purchased from Zeneca Bio Products under the trade name Biopol D400G. The polymer contained 7% hydroxyvalerate and a nucleant, BN. The average molecular weights were Mw: 320 000 and Mn:110 000 according to the manufacturer.	Zeneca Bioproducts		No	Culture collection	Culture collection		No		
Phanerochaete chrysosporium	2822231	PLA	Stoleru, E., Hitruc, E. G., Vasile, C., & Oprică, L. (2017). Biodegradation of poly (lactic acid)/chitosan stratified composites in presence of the Phanerochaete chrysosporium fungus. Polymer Degradation and Stability, 143, 118-129.	No			No			2017.0	FTIR;AFM;GPC;SEM	Poly(lactic acid) 2002D type has a Mw of 14.27 _ 104 g/mol, Mn of 7.54 _ 104 g/mol and polydispersity index (PDI) of 1.88.	NatureWorks LLC		No	Culture collection	Culture collection		No		
Plectosphaerella cucumerina	40658	PBSA	Yamamoto-Tamura, K., Hoshino, Y. T., Tsuboi, S., Huang, C., Kishimoto-Mo, A. W., Sameshima-Yamashita, Y., & Kitamoto, H. (2020). Fungal community dynamics during degradation of poly (butylene succinate-co-adipate) film in two cultivated soils in Japan. Bioscience, Biotechnology, and Biochemistry, 1-11.	No			No			2020.0	Luminance	PBSA films used in this study were composed of Bionolle® 3001 (Showa Denko K. K., Tokyo, Japan)	Showa Denko	No	No	Soil	Soil	Japan	No		
Pleurotus ostreatus	5322	O-PE	da Luz, J. M. R., Paes, S. A., Bazzolli, D. M. S., Tótola, M. R., Demuner, A. J., & Kasuya, M. C. M. (2014). Abiotic and biotic degradation of oxo-biodegradable plastic bags by Pleurotus ostreatus. PloS one, 9(11), e107438.	No			No			2014.0	SEM;CO2;Weight loss;Tensilometer	Oxo-biodegradable plastic bags	Fundação Arthur Bernandes	No	No	Culture collection	Culture collection		Yes		
Pleurotus ostreatus	5322	LDPE	da Luz, J. M. R., Paes, S. A., Nunes, M. D., da Silva, M. D. C. S., & Kasuya, M. C. M. (2013). Degradation of oxo-biodegradable plastic by Pleurotus ostreatus. Plos one, 8(8).	No			No			2013.0	SEM;FTIR;X-ray;HPLC	Plastic bags that are commonly used in supermarkets, with the description D2W or oxo-biodegradable, were cut into fragments cm61 (5 cm), and 10 g of this material was placed in a glass flask (100 mL) with 0.1 g of a commercially available paper towel. Five milliliters of the mineral medium [4,12] that was supplemented with sterile thiamine-HCl was added			No	Basidiocarp of mushrooms	Others	Brazil	No		
Pleurotus ostreatus	5322	LDPE Blend	da Luz, J. M. R., Paes, S. A., Nunes, M. D., da Silva, M. D. C. S., & Kasuya, M. C. M. (2013). Degradation of oxo-biodegradable plastic by Pleurotus ostreatus. Plos one, 8(8).	No			No			2013.0	SEM;FTIR;X-ray;HPLC	Plastic bags that are commonly used in supermarkets, with the description D2W or oxo-biodegradable, were cut into fragments cm61 (5 cm), and 10 g of this material was placed in a glass flask (100 mL) with 0.1 g of a commercially available paper towel. Five milliliters of the mineral medium [4,12] that was supplemented with sterile thiamine-HCl was added			No	Basidiocarp of mushrooms	Others	Brazil	No		
Pleurotus ostreatus	5322	PE Blend	da Luz, J. M. R., Paes, S. A., Ribeiro, K. V. G., Mendes, I. R., & Kasuya, M. C. M. (2015). Degradation of green polyethylene by Pleurotus ostreatus. PloS one, 10(6).	No			No			2015.0	CO2;SEM;FTIR;Tensilometer	Plastic bags	Fundação Arthur Bernandes		No		Culture collection		No		
Propionispora sp.	1871332	PCL	Abou-Zeid, D. M., Müller, R. J., & Deckwer, W. D. (2001). Degradation of natural and synthetic polyesters under anaerobic conditions. Journal of biotechnology, 86(2), 113-126.	No			No			2004.0	Weight loss;Clear zone;CO2	PLC (_x	Polyscence		No	Film		Germany	No		
Pseudoalteromonas lipolytica	570156	PHBH	Morohoshi, T., Ogata, K., Okura, T., & Sato, S. (2018). Molecular characterization of the bacterial community in biofilms for degradation of poly (3-hydroxybutyrate-co-3-hydroxyhexanoate) films in seawater. Microbes and environments, ME17052.	No			No			2018.0	Clear zone;Weight loss	PHBH (3HHx=6 mol% and 11mol%) with mw 610,000 and 550,000, respectively. 	Kaneka Biodegrable		No	Water	Marine	Japan	No		
Pseudogymnoascus pannorum	79858	PU	Barratt, S. R., Ennos, A. R., Greenhalgh, M., Robson, G. D., & Handley, P. S. (2003). Fungi are the predominant micro‐organisms responsible for degradation of soil‐buried polyester polyurethane over a range of soil water holding capacities. Journal of applied microbiology, 95(1), 78-85.	No			No			2003.0	Clear zone;SEM;Tensilometer				No	Plastic debris	Soil		No		
Pseudogymnoascus pannorum	79858	PVC	Sabev, H. A., Handley, P. S., & Robson, G. D. (2006). Fungal colonization of soil-buried plasticized polyvinyl chloride (pPVC) and the impact of incorporated biocides. Microbiology, 152(6), 1731-1739.	No			No			2003.0	Clear zone;SEM;Tensilometer;Weight loss	Biocide-containing pPVC was prepared by adding the biocides during plastic manufacture. Plastics were manufactured to contain (per g plastic) 500 mg dichloro-octylisothiazoline (DCOIT), 500 mg 2-n-octyl-4-isothiazolin-3-one (OIT), 2000 mg 10,109 oxybisphenoxarsine (OBPA) (all from Rohm & Haas), 2000 mg 2,3,5,6-tetrachloro-4-methylsulphonyl)pyridine (TCMP), 2000 mg n-butyl-1,2-benzisothiazolin-3-one (BBIT) (Avecia Biocides) or 10 000 mg n-(trichloromethylthio)phthalimide (NCMP) (Durham Chemical). Plastics were cut into 2?568 cm pieces, washed in Vero detergent (Verila JSC), rinsed in distilled water and surface sterilized by swabbing in 70% (v/v) ethanol.		No	No	Plastic debris	Soil	Bulgaria	No		
Pseudomonas aeruginosa	287	HDPE	Agamuthu, P., & Faizura, P. N. (2005). Biodegradability of degradable plastic waste. Waste management & research, 23(2), 95-100.	No			No			2005.0	Weight loss;FTIR;Tensilometer	Totally degradable plastics (TDP) additives (TDPATM) have been produced with a variety of polyolefin resins with 3 to 15% addition, by Environmental Plastics Inc., who supplied the samples (Table 1). Samples were HDPE or linear low density polyethylene (LLDPE) with 3 or 7% TDPATM additive. Plastic samples were obtained from McDonalds (Malaysia) and garbage bags from Japan or Hong Kong (Table 1).		No	No				No		
Pseudomonas aeruginosa	287	PS	Atiq, N., Ahmed, S., Ali, M. I., Ahmad, B., & Robson, G. (2010). Isolation and identification of polystyrene biodegrading bacteria from soil. African Journal of Microbiology Research, 4(14), 1537-1541.	No			No			2010.0	SEM;FTIR;HPLC	Expanded polystyrene (EPS) solution (2%) in chloroform;Films of pure polystyrene (Mol. Wt. 100,000)	Fluka	Yes	No	Plastic film	Soil	Pakistan	No		
Pseudomonas aeruginosa	287	PVC Blend	Das, G., Bordoloi, N. K., Rai, S. K., Mukherjee, A. K., & Karak, N. (2012). Biodegradable and biocompatible epoxidized vegetable oil modified thermostable poly (vinyl chloride): Thermal and performance characteristics post biodegradation with Pseudomonas aeruginosa and Achromobacter sp. Journal of hazardous materials, 209, 434-442.	No			No			2012.0	Weight loss;FTIR;SEM	PVC (molecular weight, Mn = 1.5 × 103 g/mol, density = 1.4 g/cc) was obtained from local market	Kumud Enterprise		No	Soil	Soil	India	No		
Pseudomonas aeruginosa	287	HDPE	Devi, R. S., Ramya, R., Kannan, K., Antony, A. R., & Kannan, V. R. (2019). Investigation of biodegradation potentials of high density polyethylene degrading marine bacteria isolated from the coastal regions of Tamil Nadu, India. Marine pollution bulletin, 138, 549-560.	No			No			2019.0	Weight loss;FTIR	Commercially available HDPE (40 μm in thickness and 0.95 g/cm3 in density) materials were used as substrate in this study. When compared to pure polyethylene, the composition of commercially available HDPE varies by the addition of additives like antioxidants and colorant.		No	No	Plastic debris	Plastic waste dumping site	India	No		
Pseudomonas aeruginosa	287	PHB	Gangurde, N. S., Patil, Y. P., Jain, R., & Sayyed, R. Z. (2017). Poly-β-hydroxybutyrate biodegradation by mixed culture population vis-à-vis single culture population under varying environmental conditions: A new approach.	No			No			2017.0	Weight loss;Clear zone	PHB production was carried out by Alcaligenes sp. RZS 4 (Gene bank accession No. JN374993) using two-step cultivation process.		Yes	No	Soil	Soil	India	No		
Pseudomonas aeruginosa	287	LDPE	Kyaw, B. M., Champakalakshmi, R., Sakharkar, M. K., Lim, C. S., & Sakharkar, K. R. (2012). Biodegradation of low density polythene (LDPE) by Pseudomonas species. Indian journal of microbiology, 52(3), 411-419.	No			No			2012.0	Weight loss;Tensilometer;FTIR-ATR;FTIR;MS;SEM	LDPE films (commercially used NTUC plastic bags) were cut into (5 cm 9 1 cm) strips and then washed with 70% ethanol for 30 min, washed with distilled water, and subsequently dried in incubator at 60 C and subsequently exposed to the bacterial culture medium		No	No	Culture collection	Culture collection		No		
Pseudomonas aeruginosa	287	LDPE	Montazer, Z., Habibi-Najafi, M. B., Mohebbi, M., & Oromiehei, A. (2018). Microbial degradation of UV-pretreated low-density polyethylene films by novel polyethylene-degrading bacteria isolated from plastic-dump soil. Journal of Polymers and the Environment, 26(9), 3613-3625.	No			No			2018.0	FTIR;SEM;Microscopy;Weight loss;CG-FIT	Low density polyethylene (Poliran LF0200 grade) granules and film (10 μm thickness; 99.95% purity without any additives and plasticizers) used for pasteurized milk packaging were supplied by Iran Polymer and Petrochemical Institute (IPPI)	Polymer and Petrochemical Institute (IPPI)	Yes	No	Soil	Landfill	Iran	No		
Pseudomonas aeruginosa	287	LDPE	Rajandas, H., Parimannan, S., Sathasivam, K., Ravichandran, M., & Yin, L. S. (2012). A novel FTIR-ATR spectroscopy based technique for the estimation of low-density polyethylene biodegradation. Polymer Testing, 31(8), 1094-1099.	No			No			2012.0	FTIR-ATR	Hundred grams of LDPE beads were dissolved in 500 ml of O-Xylene (Hamburg Chemicals, Germany) by heating at 70 C until a homogenous solution formed. The solution was allowed to recrystallize and mechanically powdered using a mortar and pestle.	Basell Polyolefins		No	Culture collection	Culture collection		No		
Pseudomonas aeruginosa	287	PU	Shah, Z., Hasan, F., Krumholz, L., Aktas, D. F., & Shah, A. A. (2013). Degradation of polyester polyurethane by newly isolated Pseudomonas aeruginosa strain MZA-85 and analysis of degradation products by GC–MS. International Biodeterioration & Biodegradation, 77, 114-122.	No			No			2013.0	MS;SEM;FTIR;GPC;CO2	Polyurethane {poly [4, 40-methylene-bis(phenyl isocyanate)-alt-1,4-butanediol/poly (butylene adipate)]} was purchased in the form of pellets from Sigma-Aldrich, GmbH, Germany	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Pseudomonas aeruginosa	287	PE	Shahreza, H., Sepahy, A. A., Hosseini, F., & Nejad, R. K. (2019). Molecular Identification of Pseudomonas Strains with Polyethylene Degradation Ability from Soil and Cloning of alkB Gene. Archives of Pharmacy Practice, 10(4). 	No			No			2019.0	Weight loss	After preparing the polyethylene granules (2 x 2 cm), they were placed in xylol and in 100 °C water bath for 15 minutes to be dissolved, then ethanol was added and the content dried at 60 °C oven. 			No	Plastic debris	Plastic waste dumping site	Iran	No		
Pseudomonas aeruginosa	287	PES	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly(ethylene succinate) (PESu) (Mn = 4.8 × 10^4, Mw/Mn = 1.9) 	Nippon Shokubai		No				No		
Pseudomonas aeruginosa	287	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Pseudomonas aestusnigri	857252	PCL	Molitor, R., Bollinger, A., Kubicki, S., Loeschcke, A., Jaeger, K. E., & Thies, S. (2020). Agar plate‐based screening methods for the identification of polyester hydrolysis by Pseudomonas species. Microbial biotechnology, 13(1), 274-284.	No			No			2020.0	Clear zone	PCL (average Mn ~10 000 by GPC, density 1.146 g ml_x005	Sigma Aldrich	Yes	No	Sand	Soil	Spain	No		
Pseudomonas aestusnigri	857252	PU	Molitor, R., Bollinger, A., Kubicki, S., Loeschcke, A., Jaeger, K. E., & Thies, S. (2020). Agar plate‐based screening methods for the identification of polyester hydrolysis by Pseudomonas species. Microbial biotechnology, 13(1), 274-284.	No			No			2020.0	Clear zone	 Impranil_x00	Covestro	No	No	Sand	Soil	Spain	No		
Pseudomonas alcaligenes	43263	PHO	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	Poly(3-hydroxyoctanoate-co-3-hydroxyhexanoate [11%]) [P(3HO) or mcl PHA]	Biopolis		No			Spain	No		
Pseudomonas alcaligenes	43263	PCL	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PCL	Sigma Aldrich	Yes	No			Spain	No		
Pseudomonas amygdali	47877	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Pseudomonas azotoformans	47878	PP	Aravinthan, A., Arkatkar, A., Juwarkar, A. A., & Doble, M. (2016). Synergistic growth of Bacillus and Pseudomonas and its degradation potential on pretreated polypropylene. Preparative Biochemistry and Biotechnology, 46(2), 109-115.	No			No			2016.0	FTIR;Weight loss;SEM	Commercial PP films (Reliance Industries Ltd., Mumbai, India) of size 1.5 × 1.5 cm and 0.05 mm thickness were used for the present experiments. The PP films were thermally pretreated at 100°C for 8 days in a hot-air oven (PP-TT) or short UV pretreated (PP-UV) at 225 nm for 6 days (Sigma instruments Chennai, India)	RB Industries	No	No		Culture collection		No		
Pseudomonas bauzanensis	653930	PCL	Molitor, R., Bollinger, A., Kubicki, S., Loeschcke, A., Jaeger, K. E., & Thies, S. (2020). Agar plate‐based screening methods for the identification of polyester hydrolysis by Pseudomonas species. Microbial biotechnology, 13(1), 274-284.	No			No			2020.0	Clear zone	PCL (average Mn ~10 000 by GPC, density 1.146 g ml_x005	Sigma Aldrich	Yes	No	Soil	Soil	Italy	No		
Pseudomonas bauzanensis	653930	PU	Molitor, R., Bollinger, A., Kubicki, S., Loeschcke, A., Jaeger, K. E., & Thies, S. (2020). Agar plate‐based screening methods for the identification of polyester hydrolysis by Pseudomonas species. Microbial biotechnology, 13(1), 274-284.	No			No			2020.0	Clear zone	 Impranil_x00	Covestro	No	No	Soil	Soil	Italy	No		
Pseudomonas beteli	40324	PHO	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	Poly(3-hydroxyoctanoate-co-3-hydroxyhexanoate [11%]) [P(3HO) or mcl PHA]	Biopolis		No			Spain	No		
Pseudomonas chlororaphis	587753	LDPE	Montazer, Z., Habibi Najafi, M. B., & Levin, D. B. (2018). Microbial degradation of low-density polyethylene and synthesis of polyhydroxyalkanoate polymers. Canadian journal of microbiology, 65(3), 224-234.	No			No			2018.0	Weight loss;SEM;GC;FTIR	LDPE powder, with a particle size of 400 μm or less (screen retention of 50 mesh is 4.4%) and a molecular weight range between 20,000 and 150,000, was supplied by Alfa-Asar Company (USA; CAS number 9002-88-4). According to the supplier, the Feedstock Melt Index and density were 3.50 g/10 min (at 190 oC and 2.16 kg load) and 0.9227 g/cm3, respectively. According to supplier’s data sheet, the polymer was pure and free of stabilizing agents. The PE particles sterilized by exposure to UV-light (254 nm) for 1 hour while mixing.	Alfa-Asar Company		No	Culture collection	Culture collection		No		
Pseudomonas citronellolis	53408	LDPE	Bhatia, M., Girdhar, A., Tiwari, A., & Nayarisseri, A. (2014). Implications of a novel Pseudomonas species on low density polyethylene biodegradation: an in vitro to in silico approach. SpringerPlus, 3(1), 497.	No			No			2014.0	SEM;FTIR;TGA;Weight loss	The LDPE sheets were immersed in xylene and boiled for 15 minutes to dissolve completely. The residue obtained was then crushed by hands, wearing gloves. The crushed residue was kept for evaporation and then dried in hot air oven at 60°C overnight. The obtained powder was stored at room temperature in a closed container (Sah et al. 2010).			No	Soil	Landfill	India	No		
Pseudomonas citronellolis	53408	PVC	Giacomucci, L., Raddadi, N., Soccio, M., Lotti, N., & Fava, F. (2019). Polyvinyl chloride biodegradation by Pseudomonas citronellolis and Bacillus flexus. New biotechnology, 52, 35-41.	No			No			2019.0	FTIR;GPC;Weight loss;TGA	PVC film contained about 30%w/w of additives/plasticizers		No	No	Culture collection	Culture collection		No		
Pseudomonas citronellolis	53408	LDPE	Pramila, R., Padmavathy, K., Ramesh, K. V., & Mahalakshmi, K. (2012). Brevibacillus parabrevis, Acinetobacter baumannii and Pseudomonas citronellolis-Potential candidates for biodegradation of low density polyethylene (LDPE). African Journal of Bacteriology Research, 4(1), 9-14.	No			No			2012.0	CO2	LDPE sheets			No	Soil	Landfill	India	No		
Pseudomonas fluorescens	294	HDPE	Baculi, R. Q., Melegrito, J. B., Sabaten, R. D. S., & Caranto, M. R. (2017). Biodegradation of High Density Polyethylene by Bacteria Isolated from Root Nodules of Phaseolus vulgaris. PHILIPPINE AGRICULTURAL SCIENTIST, 100, S21-S31.	No			No			2017.0	Weight loss;SEM;FTIR	Plastic bags	SM supermarket		No	Root nodules	Plant associated	Philippines	No		
Pseudomonas fluorescens	294	PHO	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	Poly(3-hydroxyoctanoate-co-3-hydroxyhexanoate [11%]) [P(3HO) or mcl PHA]	Biopolis		No			Spain	No		
Pseudomonas fluorescens	294	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;FTIR;SEM	PE powder (white) with 75 mmparticle size and density of 0.94 g/mL at 25 _x005F	Sigma Aldrich	No	No	Sediment	Mangrove	Malaysia	No		
Pseudomonas frederiksbergensis	104087	PBS	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	PBS (Bionolle 1020MD)	Showa Denko		No	Soil	Soil	Svalbard	No		
Pseudomonas frederiksbergensis	104087	PBSA	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	PBSA (Bionolle 3020MD)	Showa Denko		No	Soil	Soil	Svalbard	No		
Pseudomonas frederiksbergensis	104087	PCL	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	 PCL pellets were purchased from TRESNO (Poland)	TRESNO		No	Soil	Soil	Svalbard	No		
Pseudomonas frederiksbergensis	104087	PLA	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	PLA pellets were obtained from BIOMAR (Germany).	BIOMAR		No	Soil	Soil	Svalbard	No		
Pseudomonas lemoignei	29443	PHB	Kumaravel, S., Hema, R., & Lakshmi, R. (2010). Production of polyhydroxybutyrate (bioplastic) and its biodegradation by Pseudomonas lemoignei and Aspergillus niger. Journal of Chemistry, 7(S1), S536-S542.	No			No			2010.0	Clear zone;Weight loss	For production, the bio-industrial effluent such as sugarcane effluent waste was collected in sterile bottle and they were preceded for PHB production. 		Yes	No	Soil	Soil		No		
Pseudomonas lemoignei	29443	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Pseudomonas lemoignei	29443	PHA	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHA (BIOPOL-D400P-PB36)	Monsanto		No	Soil	Soil	Japan	No		
Pseudomonas lemoignei	29443	PHC	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHC (PCD-2000)	Toagosei		No	Soil	Soil	Japan	No		
Pseudomonas litoralis	797277	PCL	Molitor, R., Bollinger, A., Kubicki, S., Loeschcke, A., Jaeger, K. E., & Thies, S. (2020). Agar plate‐based screening methods for the identification of polyester hydrolysis by Pseudomonas species. Microbial biotechnology, 13(1), 274-284.	No			No			2020.0	Clear zone	PCL (average Mn ~10 000 by GPC, density 1.146 g ml_x005	Sigma Aldrich	Yes	No	Water	Marine	Spain	No		
Pseudomonas litoralis	797277	PU	Molitor, R., Bollinger, A., Kubicki, S., Loeschcke, A., Jaeger, K. E., & Thies, S. (2020). Agar plate‐based screening methods for the identification of polyester hydrolysis by Pseudomonas species. Microbial biotechnology, 13(1), 274-284.	No			No			2020.0	Clear zone	 Impranil_x00	Covestro	No	No	Water	Marine	Spain	No		
Pseudomonas mandelii	75612	PCL	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	 PCL pellets were purchased from TRESNO (Poland)	TRESNO		No	Soil	Soil	Svalbard	No		
Pseudomonas mendocina	300	P34HB	Gao, Z., Su, T., Li, P., & Wang, Z. (2017). Biodegradation of P (3HB-co-4HB) powder by Pseudomonas mendocina for preparation low-molecular-mass P (3HB-co-4HB). 3 Biotech, 7(5), 281.	No			No			2017.0	GPC;DSC;X-ray;FTIR;NMR	P(3HB-co-4HB) containing 12 mol% 4-hydroxybutyrate. The average Mw of P(3HB-co4HB) was approximately 520 kDa.	Shandong Ecomann Technology	Yes	No				No		
Pseudomonas mendocina	300	PHB	Wang, Z., Lin, X., An, J., Ren, C., & Yan, X. (2013). Biodegradation of polyhydroxybutyrate film by Pseudomonas mendocina DS04-T. Polymer-Plastics Technology and Engineering, 52(2), 195-199.	No			No			2013.0	SEM;DSC;TGA;Weight loss	PHB (powder), with a molecular weight of 7.31x10^5	Institute of Microbiology of the Chinese Academy of Science		No	Culture collection	Culture collection		No		
Pseudomonas monteilii	76759	LDPE	Montazer, Z., Habibi Najafi, M. B., & Levin, D. B. (2018). Microbial degradation of low-density polyethylene and synthesis of polyhydroxyalkanoate polymers. Canadian journal of microbiology, 65(3), 224-234.	No			No			2018.0	Weight loss;SEM;GC;FTIR	LDPE powder, with a particle size of 400 μm or less (screen retention of 50 mesh is 4.4%) and a molecular weight range between 20,000 and 150,000, was supplied by Alfa-Asar Company (USA; CAS number 9002-88-4). According to the supplier, the Feedstock Melt Index and density were 3.50 g/10 min (at 190 oC and 2.16 kg load) and 0.9227 g/cm3, respectively. According to supplier’s data sheet, the polymer was pure and free of stabilizing agents. The PE particles sterilized by exposure to UV-light (254 nm) for 1 hour while mixing.	Alfa-Asar Company		No	Culture collection	Culture collection		No		
Pseudomonas oceani	1708783	PCL	Molitor, R., Bollinger, A., Kubicki, S., Loeschcke, A., Jaeger, K. E., & Thies, S. (2020). Agar plate‐based screening methods for the identification of polyester hydrolysis by Pseudomonas species. Microbial biotechnology, 13(1), 274-284.	No			No			2020.0	Clear zone	PCL (average Mn ~10 000 by GPC, density 1.146 g ml_x005	Sigma Aldrich	Yes	No	Water	Marine	Pacific Ocean	No		
Pseudomonas oceani	1708783	PU	Molitor, R., Bollinger, A., Kubicki, S., Loeschcke, A., Jaeger, K. E., & Thies, S. (2020). Agar plate‐based screening methods for the identification of polyester hydrolysis by Pseudomonas species. Microbial biotechnology, 13(1), 274-284.	No			No			2020.0	Clear zone	 Impranil_x00	Covestro	No	No	Water	Marine	Pacific Ocean	No		
Pseudomonas otitidis	319939	PU	Peng, Y. H., Shih, Y. H., Lai, Y. C., Liu, Y. Z., Liu, Y. T., & Lin, N. C. (2014). Degradation of polyurethane by bacterium isolated from soil and assessment of polyurethanolytic activity of a Pseudomonas putida strain. Environmental Science and Pollution Research, 21(16), 9529-9537.	No			No			2014.0	FTIR;Clear zone	Impranil DLN	Bayer 	No	No			Taiwan	No		
Pseudomonas pachastrellae	254161	PCL	Suzuki, M., Tachibana, Y., Oba, K., Takizawa, R., & Kasuya, K. I. (2018). Microbial degradation of poly (ε-caprolactone) in a coastal environment. Polymer Degradation and Stability, 149, 1-8.	No			No			2018.0	Weight loss;GPC;SEM;Clear zone	Poly(ε-caprolactone) (PCL, Mn=1.7×104, Mw/Mn=1.6)	Daicel Chemical Industries		No	Plastic debris	Marine	Japan	No		
Pseudomonas pavonaceae	47881	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Pseudomonas pavonaceae	47881	PHC	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHC (PCD-2000)	Toagosei		No	Soil	Soil	Japan	No		
Pseudomonas pelagia	553151	PCL	Molitor, R., Bollinger, A., Kubicki, S., Loeschcke, A., Jaeger, K. E., & Thies, S. (2020). Agar plate‐based screening methods for the identification of polyester hydrolysis by Pseudomonas species. Microbial biotechnology, 13(1), 274-284.	No			No			2020.0	Clear zone	PCL (average Mn ~10 000 by GPC, density 1.146 g ml_x005	Sigma Aldrich	Yes	No	Algae	Marine	Antarctic Ocean	No		
Pseudomonas pelagia	553151	PU	Molitor, R., Bollinger, A., Kubicki, S., Loeschcke, A., Jaeger, K. E., & Thies, S. (2020). Agar plate‐based screening methods for the identification of polyester hydrolysis by Pseudomonas species. Microbial biotechnology, 13(1), 274-284.	No			No			2020.0	Clear zone	 Impranil_x00	Covestro	No	No	Algae	Marine	Antarctic Ocean	No		
Pseudomonas putida	303	PHA	Karmann, S., Panke, S., & Zinn, M. (2017). The Bistable behaviour of Pseudomonas putida KT2440 during PHA depolymerization under carbon limitation. Bioengineering, 4(2), 58.	No			No			2017.0	FCM	The accumulated PHA was a co-polymer of 3-hydroxyoctanoate and 10–11 mol % 3-hydroxyhexanoate.		Yes	No		Culture collection		No		
Pseudomonas putida	303	LDPE	Kyaw, B. M., Champakalakshmi, R., Sakharkar, M. K., Lim, C. S., & Sakharkar, K. R. (2012). Biodegradation of low density polythene (LDPE) by Pseudomonas species. Indian journal of microbiology, 52(3), 411-419.	No			No			2012.0	Weight loss;Tensilometer;FTIR-ATR;FTIR;MS;SEM	LDPE films (commercially used NTUC plastic bags) were cut into (5 cm 9 1 cm) strips and then washed with 70% ethanol for 30 min, washed with distilled water, and subsequently dried in incubator at 60 C and subsequently exposed to the bacterial culture medium		No	No	Culture collection	Culture collection		No		
Pseudomonas putida	303	LDPE	Montazer, Z., Habibi Najafi, M. B., & Levin, D. B. (2018). Microbial degradation of low-density polyethylene and synthesis of polyhydroxyalkanoate polymers. Canadian journal of microbiology, 65(3), 224-234.	No			No			2018.0	Weight loss;SEM;GC;FTIR	LDPE powder, with a particle size of 400 μm or less (screen retention of 50 mesh is 4.4%) and a molecular weight range between 20,000 and 150,000, was supplied by Alfa-Asar Company (USA; CAS number 9002-88-4). According to the supplier, the Feedstock Melt Index and density were 3.50 g/10 min (at 190 oC and 2.16 kg load) and 0.9227 g/cm3, respectively. According to supplier’s data sheet, the polymer was pure and free of stabilizing agents. The PE particles sterilized by exposure to UV-light (254 nm) for 1 hour while mixing.	Alfa-Asar Company		No	Soil	Plastic waste dumping site	Iran	No		
Pseudomonas putida	303	LDPE	Montazer, Z., Habibi-Najafi, M. B., Mohebbi, M., & Oromiehei, A. (2018). Microbial degradation of UV-pretreated low-density polyethylene films by novel polyethylene-degrading bacteria isolated from plastic-dump soil. Journal of Polymers and the Environment, 26(9), 3613-3625.	No			No			2018.0	FTIR;SEM;Microscopy;Weight loss;CG-FIT	Low density polyethylene (Poliran LF0200 grade) granules and film (10 μm thickness; 99.95% purity without any additives and plasticizers) used for pasteurized milk packaging were supplied by Iran Polymer and Petrochemical Institute (IPPI)	Polymer and Petrochemical Institute (IPPI)	Yes	No	Soil	Landfill	Iran	No		
Pseudomonas putida	303	PU	Peng, Y. H., Shih, Y. H., Lai, Y. C., Liu, Y. Z., Liu, Y. T., & Lin, N. C. (2014). Degradation of polyurethane by bacterium isolated from soil and assessment of polyurethanolytic activity of a Pseudomonas putida strain. Environmental Science and Pollution Research, 21(16), 9529-9537.	No			No			2014.0	FTIR;Clear zone	Impranil DLN	Bayer 	No	No			Taiwan	No		
Pseudomonas putida	303	PS	Savoldelli, J., Tomback, D., & Savoldelli, H. (2017). Breaking down polystyrene through the application of a two-step thermal degradation and bacterial method to produce usable byproducts. Waste Management, 60, 123-126.	No			No			2017.0	MS	The polystyrene utilized was pre-consumer waste polystyrene. Initially, the polystyrene was liquefied in the low temperature range (approximately 240 C) and the chosen bacteria were applied after the produced liquid cooled down.		No	No				No		
Pseudomonas rhodesiae	76760	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Pseudomonas sp.	306	HDPE	Balasubramanian, V., Natarajan, K., Hemambika, B., Ramesh, N., Sumathi, C. S., Kottaimuthu, R., & Rajesh Kannan, V. (2010). High‐density polyethylene (HDPE)‐degrading potential bacteria from marine ecosystem of Gulf of Mannar, India. Letters in applied microbiology, 51(2), 205-211.	No			No			2010.0	Weight loss;FTIR	Commercially available HDPE materials were used as substrate in this study, which is the grade of environmental pollution rather than pure polyethylene to access the direct impact on environment and application-oriented solution, because the composition of commercially available HDPE varies from pure polyethylene by the addition of additives like antioxidants and colourant.		No	No		Plastic waste dumping site	India	No		
Pseudomonas sp.	306	PHA Blend	Bhatt, R., Shah, D., Patel, K. C., & Trivedi, U. (2008). PHA–rubber blends: Synthesis, characterization and biodegradation. Bioresource technology, 99(11), 4615-4620.	No			No			2008.0	Weight loss;TGA;DSC;SEM	Different blends of PHA:rubbers (natural, nitrile and butadiene rubber) in the ratio of 5:95, 10:90, 15:85 (% w/w in mg) were synthesized. Different rubbers were dissolved in xylene and mcl-PHA in chloroform. PHA solution was then added into rubber solution and vigorously agitated for blending at room temperature for 30 min. The solution was then poured onto glass slides and allowed to crystallize for 5 days for complete removal of the solvent (Ramsay et al., 1993; Imam et al., 1998).			No	Soil	Soil		No		
Pseudomonas sp.	306	LDPE	Deepika, S., & Madhuri, R. J. (2015). Biodegradation of low density polyethylene by micro-organisms from garbage soil. Journal of Experimental Biology and Agricultural Sciences, 3(1), 15-21.	No			No			2015.0	Clear zone;Weight loss	Low density polyethylene powder (LDPE) with 53-75 µm particle size was obtained from Sigma Aldrich Chemical Co (Product of USA) with density 0.94g/ml at 250C. Low density polyethylene granules from Pack worth polymers and Pack mates India Private Ltd (Hyderabad, INDIA).	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	India	No		
Pseudomonas sp.	306	PHB	Gangurde, N. S., Patil, Y. P., Jain, R., & Sayyed, R. Z. (2017). Poly-β-hydroxybutyrate biodegradation by mixed culture population vis-à-vis single culture population under varying environmental conditions: A new approach.	No			No			2017.0	Weight loss;Clear zone	PHB production was carried out by Alcaligenes sp. RZS 4 (Gene bank accession No. JN374993) using two-step cultivation process.		Yes	No	Soil	Soil	India	No		
Pseudomonas sp.	306	PE	Kathiresan, K. (2003). Polythene and plastics-degrading microbes from the mangrove soil. Revista de biologia tropical, 51(3-4), 629-633.	No			No			2003.0	Weight loss	Pre weighed discs of 1cm diameter prepared from polythene bags and disposable plastic cups		No	No	Plastic debris	Mangrove	India	No		
Pseudomonas sp.	306	PHN	Kim, H. M., Ryu, K. E., Bae, K. S., & Rhee, Y. H. (2000). Purification and characterization of extracellular medium-chain-length polyhydroxyalkanoate depolymerase from Pseudomonas sp. RY-1. Journal of bioscience and bioengineering, 89(2), 196-198.	No			No			2000.0	Clear zone;Spectrophotometry	Produced by P.Oleovorans		Yes	No	Soil	Soil	South Korea	Yes		
Pseudomonas sp.	306	PHO	Kim, H. M., Ryu, K. E., Bae, K. S., & Rhee, Y. H. (2000). Purification and characterization of extracellular medium-chain-length polyhydroxyalkanoate depolymerase from Pseudomonas sp. RY-1. Journal of bioscience and bioengineering, 89(2), 196-198.	No			No			2000.0	Clear zone;Spectrophotometry	Produced by P.Oleovorans		Yes	No	Soil	Soil	South Korea	Yes		
Pseudomonas sp.	306	PLA	Kim, M. Y., Kim, C., Moon, J., Heo, J., Jung, S. P., & Kim, J. R. (2017). Polymer film-based screening and isolation of polylactic acid (PLA)-degrading microorganisms. J. Microbiol. Biotechnol, 27(2), 342-349.	No			No			2017.0	Clear zone;SEM;GC	PLA (Grade 4042D, 95.8% L-lactide, 4.2% D-lactide, number average molar mass Mn = 183,000 g/mol)	NatureWorks LLC		No	Digester sludge	Sewage/Sludge	South Korea	No		
Pseudomonas sp.	306	PS Blend	Mohan, A. J., Sekhar, V. C., Bhaskar, T., & Nampoothiri, K. M. (2016). Microbial assisted high impact polystyrene (HIPS) degradation. Bioresource technology, 213, 204-207.	No			No			2016.0	HPLC;NMR;FTIR;TGA;Weight loss;SEM	HIPS with decabromodiphenyl oxide and antimony trioxide was in the form of small white opaque beads provided by CSIR-IIP and the films were made by dissolving 200 mg of beads in 10 ml of chloroform and pouring that into a wide open glass plate and were kept at room temperature for overnight in a fume hood to obtain films with consistent structure. 			No	Soil	Plastic waste dumping site	India	No		
Pseudomonas sp.	306	PE	Nanda, S., & Sahu, S. S. (2010). Biodegradability of polyethylene by Brevibacillus, Pseudomonas, and Rhodococcus spp. New York Science Journal, 3(7), 95-98.	No			No			2010.0	Clear zone	General grade polyethylene employed for commercial grocery carriage purpose was used to investigate its biodegradability nature.		No	No	Soil	Plastic waste dumping site	India	No		
Pseudomonas sp.	306	PE	Nanda, S., Sahu, S., & Abraham, J. (2010). Studies on the biodegradation of natural and synthetic polyethylene by Pseudomonas spp. Journal of Applied Sciences and Environmental Management, 14(2).	No			No			2010.0	Weight loss	Polyethylene bags (both natural and synthetic) each having 50 microns thickness were used for comparative investigation of their biodegradability nature. The natural polyethylene bag used was made from a combination of virgin plastic vegetable starch (6%), organic minerals, and vegetable extracts, whereas the synthetic polyethylene bag was of conventional plastic polymer of petroleum origin.		No	No	Soil	Soil	India	No		
Pseudomonas sp.	306	PE	Satyalakshmi, S. (2016). ISOLATION AND IDENTIFICATION OF POLYTHENE BAGS DEGRADING BACTERIA FROM VISAKHAPATNAM DUMPING YARD. International Journal of Pharmaceutical Sciences and Research, 7(10), 4200.	No			No			2016.0	Clear zone;Weight loss	Low density polyethylene bag (LDPE) was obtained from plastic Industry		No	No	Soil	Plastic waste dumping site	India	No		
Pseudomonas sp.	306	PCL	Sekiguchi, T., Saika, A., Nomura, K., Watanabe, T., Watanabe, T., Fujimoto, Y., ... & Kanehiro, H. (2011). Biodegradation of aliphatic polyesters soaked in deep seawaters and isolation of poly (ɛ-caprolactone)-degrading bacteria. Polymer degradation and stability, 96(7), 1397-1403.	No			No			2011.0	SEM;Tensilometer;Spectrophotometry;Clear zone	PCL fiber (Composition: Monofilament (300 denier); Strength (kgf): 1.02; Breaking elongation (%): 70)	Daicel Chemical Industries	NA 	No	Fiber	Marine	Japan	No		
Pseudomonas sp.	306	PCL	Sekiguchi, T., Saika, A., Nomura, K., Watanabe, T., Watanabe, T., Fujimoto, Y., ... & Kanehiro, H. (2011). Biodegradation of aliphatic polyesters soaked in deep seawaters and isolation of poly (ɛ-caprolactone)-degrading bacteria. Polymer degradation and stability, 96(7), 1397-1403.	No			No			2011.0	SEM;Tensilometer;Spectrophotometry;Clear zone	PCL fiber (Composition: Monofilament (300 denier); Strength (kgf): 1.02; Breaking elongation (%): 70)	Daicel Chemical Industries	NA 	No	Fiber	Marine	Japan	No		
Pseudomonas sp.	306	PCL	Sekiguchi, T., Sato, T., Enoki, M., Kanehiro, H., Uematsu, K., & Kato, C. (2011). Isolation and characterization of biodegradable plastic degrading bacteria from deep-sea environments. JAMSTEC Report of Research and Development, 11, 33-41.	No			No			2011.0	Clear zone	PCL films	Sigma Aldrich	Yes	No	Sediment	Marine	Japan	No		
Pseudomonas sp.	306	PE	Shahreza, H., Sepahy, A. A., Hosseini, F., & Nejad, R. K. (2019). Molecular Identification of Pseudomonas Strains with Polyethylene Degradation Ability from Soil and Cloning of alkB Gene. Archives of Pharmacy Practice, 10(4). 	No			No			2019.0	Weight loss	After preparing the polyethylene granules (2 x 2 cm), they were placed in xylol and in 100 °C water bath for 15 minutes to be dissolved, then ethanol was added and the content dried at 60 °C oven. 			No	Plastic debris	Plastic waste dumping site	Iran	No		
Pseudomonas sp.	306	PVA	Shimao, M. A. S. A. Y. U. K. I., Saimoto, H. I. R. O. S. H. I., Kato, N. O. B. U. O., & Sakazawa, C. H. I. K. A. H. I. R. O. (1983). Properties and roles of bacterial symbionts of polyvinyl alcohol-utilizing mixed cultures. Appl. Environ. Microbiol., 46(3), 605-610.	No			No			1983.0	Spectrophotometry				No				No		
Pseudomonas sp.	306	PE	Shovitri, M., Nafi’ah, R., Antika, T. R., Alami, N. H., Kuswytasari, N. D., & Zulaikha, E. (2017). Soil burial method for plastic degradation performed by Pseudomonas PL-01, Bacillus PL-01, and indigenous bacteria. In AIP Conference Proceedings (Vol. 1854, No. 1, p. 020035). AIP Publishing.	No			No			2017.0	FTIR;Weight loss	Black and white plastic kresek and transparent bag for controls 		No	No				No		
Pseudomonas sp.	306	PES	Tribedi, P., & Sil, A. K. (2013). Bioaugmentation of polyethylene succinate-contaminated soil with Pseudomonas sp. AKS2 results in increased microbial activity and better polymer degradation. Environmental Science and Pollution Research, 20(3), 1318-1326.	No			No			2013.0	SEM;Weight loss	PES film			No	Soil	Plastic waste dumping site	India	No		
Pseudomonas sp.	306	LDPE	Tribedi, P., & Sil, A. K. (2013). Low-density polyethylene degradation by Pseudomonas sp. AKS2 biofilm. Environmental Science and Pollution Research, 20(6), 4146-4153.	No			No			2013.0	SEM;AFM;Tensilometer;Weight loss	The LDPE films used in this study were collected from local markets (Kolkata) where they were sold as 20-μmthick carrier bags. For the experiments, LDPE films were cut into small strips and sterilized with 70 % alcohol.		No	No	Soil	Plastic waste dumping site	India	No		
Pseudomonas sp.	306	PES	Tribedi, P., & Sil, A. K. (2014). Cell surface hydrophobicity: a key component in the degradation of polyethylene succinate by P seudomonas sp. AKS 2. Journal of applied microbiology, 116(2), 295-303.	No			No			2014.0	SEM;Weight loss	PES film			No	Soil	Plastic waste dumping site	India	No		
Pseudomonas sp.	306	PES	Tribedi, P., Sarkar, S., Mukherjee, K., & Sil, A. K. (2012). Isolation of a novel Pseudomonas sp from soil that can efficiently degrade polyethylene succinate. Environmental Science and Pollution Research, 19(6), 2115-2124.	No			No			2012.0	SEM;Weight loss;Clear zone	 PES (Aldrich, USA) (average Mn 10,000)	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	India	No		
Pseudomonas sp.	306	PBS	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	PBS (Bionolle 1020MD)	Showa Denko		No	Soil	Soil	Svalbard	No		
Pseudomonas sp.	306	PBSA	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	PBSA (Bionolle 3020MD)	Showa Denko		No	Soil	Soil	Svalbard	No		
Pseudomonas sp.	306	PCL	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	 PCL pellets were purchased from TRESNO (Poland)	TRESNO		No	Soil	Soil	Svalbard	No		
Pseudomonas sp.	306	PLA	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	PLA pellets were obtained from BIOMAR (Germany).	BIOMAR		No	Soil	Soil	Svalbard	No		
Pseudomonas sp.	306	LDPE	Usha, R., Sangeetha, T., & Palaniswamy, M. (2011). Screening of polyethylene degrading microorganisms from garbage soil. Libyan agriculture research center journal international, 2(4), 200-204.	No			No			2011.0	Clear zone	Low density polyethylene powder (LDPE)	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	India	No		
Pseudomonas sp.	306	PLA	Wang, Z., Wang, Y., Guo, Z., Li, F., & Chen, S. (2011). Purification and characterization of poly (L‐lactic acid) depolymerase from Pseudomonas sp. strain DS04‐T. Polymer Engineering & Science, 51(3), 454-459.	No			No			2011.0	SEM;Weight loss;MS	PLA powders with a number-average molecular weight (Mn) of 400,000	Zhejiang Hisun Biomaterial		No	Sludge	Sewage/Sludge	China	No		
Stutzerimonas stutzeri	316	P3HP	Kasuya, T., Nakajima, H., & Kitamoto, K. (1999). Cloning and characterization of the bipA gene encoding ER chaperone BiP from Aspergillus oryzae. Journal of bioscience and bioengineering, 88(5), 472-478.	No			No			1999.0	Spectrophotometry	Poly (3-hydroxyoctanoate) (PHO) 			No	Water	Marine	South Korea	No		
Stutzerimonas stutzeri	316	PHB	Martínez-Tobón, D. I., Gul, M., Elias, A. L., & Sauvageau, D. (2018). Polyhydroxybutyrate (PHB) biodegradation using bacterial strains with demonstrated and predicted PHB depolymerase activity. Applied microbiology and biotechnology, 102(18), 8049-8067.	No			No			2018.0	Clear zone;Weight loss	PHB pellets (BRS Bulk Bio-pellets, Bulk Reef Supply, Golden Valley, USA) and acetic acid (Fisher Scientific) were used to produce PHB films by solvent casting as described by Anbukarasu et al. (2015).	Bulk Reef Supply	Yes	No		Culture collection		No		
Stutzerimonas stutzeri	316	PE	Sharma, A., & Sharma, A. (2004). Degradation assessment of low density polythene (LDP) and polythene (PP) by an indigenous isolate of Pseudomonas stutzeri.	No			No			2004.0	Tensilometer;Biochemical oxygen demand	PE	Manufacturing factories	No	No		Plastic waste dumping site	India	No		
Stutzerimonas stutzeri	316	PP	Sharma, A., & Sharma, A. (2004). Degradation assessment of low density polythene (LDP) and polythene (PP) by an indigenous isolate of Pseudomonas stutzeri.	No			No			2004.0	Tensilometer;Biochemical oxygen demand	PP	Manufacturing factories	No	No		Plastic waste dumping site	India	No		
Pseudomonas syringae	317	LDPE	Kyaw, B. M., Champakalakshmi, R., Sakharkar, M. K., Lim, C. S., & Sakharkar, K. R. (2012). Biodegradation of low density polythene (LDPE) by Pseudomonas species. Indian journal of microbiology, 52(3), 411-419.	No			No			2012.0	Weight loss;Tensilometer;FTIR-ATR;FTIR;MS;SEM	LDPE films (commercially used NTUC plastic bags) were cut into (5 cm 9 1 cm) strips and then washed with 70% ethanol for 30 min, washed with distilled water, and subsequently dried in incubator at 60 C and subsequently exposed to the bacterial culture medium		No	No	Culture collection	Culture collection		No		
Pseudomonas veronii	76761	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Pseudomonas veronii	76761	PHC	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHC (PCD-2000)	Toagosei		No	Soil	Soil	Japan	No		
Pseudonocardia alni	33907	PLA	Konkit, M., Jarerat, A., Khanongnuch, C., Lumyong, S., & Pathom-Aree, W. (2012). Poly (lactide) degradation by Pseudonocardia alni AS4. 1531T.	No			No			2012.0	Weight loss;SEM	Poly(lactide)(PLA),4042D (Mw=74,000) was purchased from NatureWorks® LLC (U.S.). A PLA film was prepared by casting 100 mg of PLA in 10 ml chloroform.	NatureWorks LLC		No	Culture collection	Culture collection		No		
Pseudoxanthomonas sp.	1871049	PCL	Adıgüzel, A. O., & Tunçer, M. (2017). Purification and characterization of cutinase from Bacillus sp. KY0701 isolated from plastic wastes. Preparative Biochemistry and Biotechnology, 47(9), 925-933.	No			No			2017.0	Weight loss;Clear zone	Plastic Waste		No	No	Plastic debris	Soil	Turkey	No		
Pseudozyma sp.	1902915	PCL	Abdel-Motaal, F. F., El-Sayed, M. A., El-Zayat, S. A., & Ito, S. I. (2014). Biodegradation of poly (ε-caprolactone)(PCL) film and foam plastic by Pseudozyma japonica sp. nov., a novel cutinolytic ustilaginomycetous yeast species. 3 Biotech, 4(5), 507-512.	No			No			2014.0	Weight loss	Poly (e-caprolactone) (PCL) with molecular weight 70,000–100,000 Da	Sigma Aldrich	Yes	No				No		
Psychrobacillus sp.	1871623	PHBH	Kato, C., Honma, A., Sato, S., Okura, T., Fukuda, R., & Nogi, Y. (2019). Poly 3-hydroxybutyrate-co-3-hydroxyhexanoate films can be degraded by the deep-sea microbes at high pressure and low temperature conditions. High Pressure Research, 1-10.	No			No			2019.0	TEM;SEM;Microscopy;Clear zone	PHBH powder			No	Sediment	Marine	Japan	No		
Psychrobacter sp.	56811	PCL	Sekiguchi, T., Sato, T., Enoki, M., Kanehiro, H., Uematsu, K., & Kato, C. (2011). Isolation and characterization of biodegradable plastic degrading bacteria from deep-sea environments. JAMSTEC Report of Research and Development, 11, 33-41.	No			No			2011.0	Clear zone	PCL films	Sigma Aldrich	Yes	No	Sediment	Marine	Japan	No		
Purpureocillium lilacinum	33203	PHBV	Sang, B. I., Hori, K., Tanji, Y., & Unno, H. (2002). Fungal contribution to in situ biodegradation of poly (3-hydroxybutyrate-co-3-hydroxyvalerate) film in soil. Applied microbiology and biotechnology, 58(2), 241-247.	No			No			2002.0	Weight loss;SEM;Clear zone	PHBV containing 12% 3-hydroxyvalerate (3HV) in powder form	Sigma Aldrich		No	Soil	Soil	Japan	No		
Purpureocillium lilacinum	33203	PBSA	Yamamoto-Tamura, K., Hoshino, Y. T., Tsuboi, S., Huang, C., Kishimoto-Mo, A. W., Sameshima-Yamashita, Y., & Kitamoto, H. (2020). Fungal community dynamics during degradation of poly (butylene succinate-co-adipate) film in two cultivated soils in Japan. Bioscience, Biotechnology, and Biochemistry, 1-11.	No			No			2020.0	Luminance	PBSA films used in this study were composed of Bionolle® 3001 (Showa Denko K. K., Tokyo, Japan)	Showa Denko	No	No	Soil	Soil	Japan	No		
Pyrenochaetopsis sp.	1756125	PBSA	Yamamoto-Tamura, K., Hoshino, Y. T., Tsuboi, S., Huang, C., Kishimoto-Mo, A. W., Sameshima-Yamashita, Y., & Kitamoto, H. (2020). Fungal community dynamics during degradation of poly (butylene succinate-co-adipate) film in two cultivated soils in Japan. Bioscience, Biotechnology, and Biochemistry, 1-11.	No			No			2020.0	Luminance	PBSA films used in this study were composed of Bionolle® 3001 (Showa Denko K. K., Tokyo, Japan)	Showa Denko	No	No	Soil	Soil	Japan	No		
Rahnella aquatilis	34038	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;SEM;FTIR;Tensilometer	LDPE, type “FGNX23-D022”;Bionolle (type #3001)	POLICHEM		No	Soil	Soil	Poland	No		
Ralstonia eutropha	106590	PHA	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHA (BIOPOL-D400P-PB36)	Monsanto		No	Soil	Soil	Japan	No		
Ralstonia pickettii	329	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Ralstonia pickettii	329	PHA	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHA (BIOPOL-D400P-PB36)	Monsanto		No	Soil	Soil	Japan	No		
Ralstonia pickettii	329	PHC	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHC (PCD-2000)	Toagosei		No	Soil	Soil	Japan	No		
Ralstonia pickettii	329	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Ralstonia sp.	54061	LDPE	Koutny, M., Amato, P., Muchova, M., Ruzicka, J., & Delort, A. M. (2009). Soil bacterial strains able to grow on the surface of oxidized polyethylene film containing prooxidant additives. International Biodeterioration & Biodegradation, 63(3), 354-357.	No			No			2009.0	Microscopy;Tensilometer	Preoxidized PE film was transparent LDPE film 60 mm thick containing prooxidant additives based on organometallic complexes. To balance the prodegradant activity phenolic antioxidants were used in the blends. 		No	No	Soil	Soil	France	No		
Ralstonia sp.	54061	PHB	Martínez-Tobón, D. I., Gul, M., Elias, A. L., & Sauvageau, D. (2018). Polyhydroxybutyrate (PHB) biodegradation using bacterial strains with demonstrated and predicted PHB depolymerase activity. Applied microbiology and biotechnology, 102(18), 8049-8067.	No			No			2018.0	Clear zone;Weight loss	PHB pellets (BRS Bulk Bio-pellets, Bulk Reef Supply, Golden Valley, USA) and acetic acid (Fisher Scientific) were used to produce PHB films by solvent casting as described by Anbukarasu et al. (2015).	Bulk Reef Supply	Yes	No		Culture collection		No		
Rheinheimera sp.	1869214	PHBH	Kato, C., Honma, A., Sato, S., Okura, T., Fukuda, R., & Nogi, Y. (2019). Poly 3-hydroxybutyrate-co-3-hydroxyhexanoate films can be degraded by the deep-sea microbes at high pressure and low temperature conditions. High Pressure Research, 1-10.	No			No			2019.0	TEM;SEM;Microscopy;Clear zone	PHBH powder			No	Sediment	Marine	Japan	No		
Rhizobium viscosum	1673	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;SEM;FTIR;Tensilometer	LDPE, type “FGNX23-D022”;Bionolle (type #3001)	POLICHEM		No	Soil	Soil	Poland	No		
Rhizopus oligosporus	4847	PLA	Torres, A., Li, S. M., Roussos, S., & Vert, M. (1996). Screening of microorganisms for biodegradation of poly (lactic-acid) and lactic acid-containing polymers. Appl. Environ. Microbiol., 62(7), 2393-2397.	No			No			1996.0	HPLC;SEM	Typically, 1 liter of DL-LA commercial solution was heated under normal pressure to gently distillate water. When the temperature reached 1308C, vacuum was applied and distillation was controlled as desired. One fraction of racemic oligomers (Mw 5 1,000, I 5 Mw/Mn 5 1.3) was used for the screening of filamentous fungi, and another one (Mw 5 2,000, I 5 1.3) was used for soil screening. Molecular weights were determined by size exclusion chromatography. 	Sigma Aldrich	Yes	No		Culture collection		No		
Rhodococcus equi	43767	PHO	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	Poly(3-hydroxyoctanoate-co-3-hydroxyhexanoate [11%]) [P(3HO) or mcl PHA]	Biopolis		No			Spain	No		
Rhodococcus erythropolis	1833	LDPE	Albertsson, A. C., Erlandsson, B., Hakkarainen, M., & Karlsson, S. (1998). Molecular weight changes and polymeric matrix changes correlated with the formation of degradation products in biodegraded polyethylene. Journal of Environmental Polymer Degradation, 6(4), 187-195.	No			No			1998.0	GC;MS;X-ray;SEC;FTIR;Spectrophotometry	LDPE films (80mm) were made by a conventional blown-film process using a Betol extruder with a 25 mm screw of L : D 20 : 1, a blow-up ratio of about 2.5 : 1 and die temperature 185°C. The polymer was a conventional LDPE grade of MFI 2 acquired from AT0 (France), which incorporated a conventional thermal stabilizer of undisclosed composition. Prodegradant additives were incorporated into the LDPE matrix in the form of a masterbatch (MB) in the amount of 20%, mostly consisting of corn starch (7.7%), styrene-butadiene copolymer (SBS), manganese stearate and linear LDPE. Degradation took place according to the following procedure.	AT0	Yes	No				No		
Rhodococcus erythropolis	1833	LDPE	Koutny, M., Amato, P., Muchova, M., Ruzicka, J., & Delort, A. M. (2009). Soil bacterial strains able to grow on the surface of oxidized polyethylene film containing prooxidant additives. International Biodeterioration & Biodegradation, 63(3), 354-357.	No			No			2009.0	Microscopy;Tensilometer	Preoxidized PE film was transparent LDPE film 60 mm thick containing prooxidant additives based on organometallic complexes. To balance the prodegradant activity phenolic antioxidants were used in the blends. 		No	No	Soil	Soil	France	No		
Rhodococcus rhodochrous	1829	O-PE	Bonhomme, S., Cuer, A., Delort, A. M., Lemaire, J., Sancelme, M., & Scott, G. (2003). Environmental biodegradation of polyethylene. Polymer Degradation and Stability, 81(3), 441-452.	No			No			2003.0	SEM;FTIR;GPC	Degradable polyethylene was a green film (LC) containing TDPA1 (thickness 36_2 mm)	EPI	No	No	Culture collection	Culture collection		No		
Rhodococcus rhodochrous	1829	LLDPE	Fontanella, S., Bonhomme, S., Koutny, M., Husarova, L., Brusson, J. M., Courdavault, J. P., ... & Delort, A. M. (2010). Comparison of the biodegradability of various polyethylene films containing pro-oxidant additives. Polymer Degradation and Stability, 95(6), 1011-1021.	No			No			2010.0	SEM;SEC;NMR;FTIR	The material samples were transparent HDPE, LDPE and LLDPE films whose thickness ranged from 43 to 59 mm (Table 1). The films contained iron photo-inducer supplying radicals through a photoredox process and an organometallic type cobalt and/or manganese thermo-inducer, catalyzing the primary hydroperoxide decomposition (see Table 1). To antagonise the prodegradant activity of the photo- and thermo-inductor during the first year of storage and use under indoor conditions phenolic antioxidants were utilized in the blends. Due to the added antioxidants the thermal induction period was longer than 400 h at 60 C in the dark. The oxidation state of the catalysts was Co2þ, Mn2þ and Fe3þ and the ligand was stearate.		No	No	Culture collection	Culture collection		No		
Rhodococcus rhodochrous	1829	PE	Koutny, M., Sancelme, M., Dabin, C., Pichon, N., Delort, A. M., & Lemaire, J. (2006). Acquired biodegradability of polyethylenes containing pro-oxidant additives. Polymer degradation and stability, 91(7), 1495-1503.	No			No			2006.0	ATR-FTIR;SEC;Microscopy;NMR	The material samples were transparent HDPE film 20 mm thick and transparent LDPE film 60 mm thick. Both films contained iron photo-inducer, different from the Scott/Gilead compound (Schulman e Bornen, Belgium) supplying radicals through a photo-redox process and an organometallic type thermo-inducer (EPI, Vancouver, Canada) catalysing the primary hydroperoxide decomposition. Both additives were present in both films. 		No	No	Culture collection	Culture collection		No		
Rhodococcus ruber	1830	PS	Mor, R., & Sivan, A. (2008). Biofilm formation and partial biodegradation of polystyrene by the actinomycete Rhodococcus ruber. Biodegradation, 19(6), 851-858.	No			No			2008.0	Weight loss;Spectrophotometry;SEM	Three forms of polystyrene were used in this study: (a) pure standard polystyrene flakes comprising a mixture of polymers of two different molecular weights, 4,000 and 200,000 (Sigma Cat. Number 33,165-1); (b) polystyrene powder produced by grinding the above polystyrene flakes in a coffee grinder and screening to obtain 10–50 lM particles; and (c) ELISA 96-well microtiter plates manufactured from pure polystyrene (C96 MicroWellTM, Nalgene Nunc International, USA).	Sigma Aldrich	Yes	No				No		
Rhodococcus sp.	1831	PCL	Adıgüzel, A. O., & Tunçer, M. (2017). Purification and characterization of cutinase from Bacillus sp. KY0701 isolated from plastic wastes. Preparative Biochemistry and Biotechnology, 47(9), 925-933.	No			No			2017.0	Weight loss;Clear zone	Plastic Waste		No	No	Plastic debris	Soil	Turkey	No		
Rhodococcus sp.	1831	PP	Auta, H. S., Emenike, C. U., Jayanthi, B., & Fauziah, S. H. (2018). Growth kinetics and biodeterioration of polypropylene microplastics by Bacillus sp. and Rhodococcus sp. isolated from mangrove sediment. Marine pollution bulletin, 127, 15-21.	No			No			2018.0	Weight loss;SEM;FTIR;Clear zone	Isotactic PP microplastic granules (white, spherical) with a density of 0.9 g/ml at 25 °C, molecular weight of 250,000 Mw, average Mn of 67,000 and CAS number 9003-07-0	Sigma Aldrich	Yes	No	Sediment	Mangrove	Malaysia	No		
Rhodococcus sp.	1831	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Rhodococcus sp.	1831	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Rhodococcus sp.	1831	PE	Nanda, S., & Sahu, S. S. (2010). Biodegradability of polyethylene by Brevibacillus, Pseudomonas, and Rhodococcus spp. New York Science Journal, 3(7), 95-98.	No			No			2010.0	Clear zone	General grade polyethylene employed for commercial grocery carriage purpose was used to investigate its biodegradability nature.		No	No	Soil	Plastic waste dumping site	India	No		
Rhodococcus sp.	1831	PCL	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	 PCL pellets were purchased from TRESNO (Poland)	TRESNO		No	Soil	Soil	Svalbard	No		
Rhodoferax fermentans	28066	PHA	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHA (BIOPOL-D400P-PB36)	Monsanto		No	Soil	Soil	Japan	No		
Rhodotorula mucilaginosa	5537	PLA	Nair, N. R., Sekhar, V. C., & Nampoothiri, K. M. (2016). Augmentation of a microbial consortium for enhanced polylactide (PLA) degradation. Indian journal of microbiology, 56(1), 59-63.	No			No			2016.0	Weight loss;SEM;Spectrophotometry	Commercial grade PLA with molecular weight of 85,000–160,000	Sigma Aldrich	Yes	No			India	No		
Rhodotorula mucilaginosa	5537	PLA	Nair, N. R., Sekhar, V. C., & Nampoothiri, K. M. (2016). Augmentation of a microbial consortium for enhanced polylactide (PLA) degradation. Indian journal of microbiology, 56(1), 59-63.	No			No			2016.0	Weight loss;SEM;Spectrophotometry;Clear zone	Commercial grade PLA with molecular weight of 85,000–160,000	Sigma Aldrich	Yes	No			India	No		
Rhodotorula sphaerocarpa	86839	PHB	Gonda, K. E., Jendrossek, D., & Molitoris, H. P. (2000). Fungal degradation of the thermoplastic polymer poly-ß-hydroxybutyric acid (PHB) under simulated deep sea pressure. In Life at Interfaces and Under Extreme Conditions (pp. 173-183). Springer, Dordrecht.	No			No			2000.0	Clear zone;Spectrophotometry	PHB was isolated from sodium-gluconate-grown cells of the bacterium Ralstonia eutropha HI6 by sodium-hypochlorite treatment followed by acetone-ether (2: I, v/v) extraction.		Yes	No	Deep sea	Marine	Thaiti	No		
Roseateles depolymerans	76731	PBSA	Ahmad, A., Tsutsui, A., Iijima, S., Suzuki, T., Shah, A. A., & Nakajima-Kambe, T. (2019). Gene structure and comparative study of two different plastic-degrading esterases from Roseateles depolymerans strain TB-87. Polymer Degradation and Stability, 164, 109-117.	No			No			2019.0	Clear zone				No				No		
Roseateles depolymerans	76731	PCL	Lee, S. H., Choe, H., Kim, S. G., Park, D. S., Nasir, A., Kim, B. K., & Kim, K. M. (2016). Complete genome of biodegradable plastics-decomposing Roseateles depolymerans KCTC 42856T (= 61AT). Journal of biotechnology, 220, 47-48.	No			No			2016.0					No		River/Lake	Japan	No		
Roseateles depolymerans	76731	PHC	Lee, S. H., Choe, H., Kim, S. G., Park, D. S., Nasir, A., Kim, B. K., & Kim, K. M. (2016). Complete genome of biodegradable plastics-decomposing Roseateles depolymerans KCTC 42856T (= 61AT). Journal of biotechnology, 220, 47-48.	No			No			2016.0					No		River/Lake	Japan	No		
Roseateles depolymerans	76731	PTC	Lee, S. H., Choe, H., Kim, S. G., Park, D. S., Nasir, A., Kim, B. K., & Kim, K. M. (2016). Complete genome of biodegradable plastics-decomposing Roseateles depolymerans KCTC 42856T (= 61AT). Journal of biotechnology, 220, 47-48.	No			No			2016.0					No		River/Lake	Japan	No		
Roseateles depolymerans	76731	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Roseateles depolymerans	76731	PHC	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHC (PCD-2000)	Toagosei		No	Soil	Soil	Japan	No		
Roseateles depolymerans	76731	PTS	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PTS (BIONOLLE-1020)	Showa Denko		No	Soil	Soil	Japan	No		
Saccharothrix australiensis	2072	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Saccharothrix coeruleofusca	33919	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Saccharothrix cryophilis	43355	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Saccharothrix espanaensis	103731	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Saccharothrix longispora	33920	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Saccharothrix mutabilis	33921	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Saccharothrix syringae	103733	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Saccharothrix texasensis	103734	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Saccharothrix waywayandensis	84724	PLA	Jarerat, A., & Tokiwa, Y. (2003). Poly (L-lactide) degradation by Saccharothrix waywayandensis. Biotechnology letters, 25(5), 401-404.	No			No			2003.0	TOC;SEM;Weight loss	Poly(L-lactide) (PLA), Lacty 1012 (number-average molecular weight, Mn = 1.3 × 105) was purchased from Shimadzu Co. Ltd., Kyoto, Japan.	Shimadzu		No	Culture collection	Culture collection	Japan	No		
Saccharothrix waywayandensis	84724	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Saccharothrix waywayandensis	84724	PLA	Tokiwa, Y., & Jarerat, A. (2005). Accelerated Microbial Degradation of Poly (l‐lactide). In Macromolecular Symposia (Vol. 224, No. 1, pp. 367-376). Weinheim: WILEY‐VCH Verlag.	No			No			2005.0	Weight loss;Clear zone;TOC	High molecular weight (1.3 × 105) PLA film			No				No		
Salmonella sp.	599	PS	Savoldelli, J., Tomback, D., & Savoldelli, H. (2017). Breaking down polystyrene through the application of a two-step thermal degradation and bacterial method to produce usable byproducts. Waste Management, 60, 123-126.	No			No			2017.0	MS	The polystyrene utilized was pre-consumer waste polystyrene. Initially, the polystyrene was liquefied in the low temperature range (approximately 240 C) and the chosen bacteria were applied after the produced liquid cooled down.		No	No				No		
Sarocladium kiliense	45277	LDPE	Karlsson, S., Ljungquist, O., & Albertsson, A. C. (1988). Biodegradation of polyethylene and the influence of surfactants. Polymer degradation and stability, 21(3), 237-250.	No			No			1988.0	14C;CO2	LDPE labelled with 14C was produced by Imperial Chemical Industries, London and generously supplied by Akerlund & Rausing AB, Lund, Sweden. The polymer was made from ethylene with a rather high concentration of 14 C using a high pressure free radical process. This polymer was mixed with another batch of similar commercial polymer to yield a polymer with a fairly low concentration of 14C. This gave a distribution of 14C in which the labelled carbon was located in a few molecules. The density of the LDPE granules was 0.922 g/cm^3, and the molecular weights were M. -- 18.200 and M w = 84.000. Films, 0.16 mm thick, were made by heating and moulding the LDPE granules. One set of polyethylene samples (NDPE) contained 5% of an additive consisting of palmitate iron carboxylate-Fe(III)hydroxide to increase the photo-chemical degradation rate. A parallel set of samples contained no additive (PE).	Akerlund & Rausing AB	Yes	No				No		
Sarocladium strictum	5046	PBSA	Yamamoto-Tamura, K., Hoshino, Y. T., Tsuboi, S., Huang, C., Kishimoto-Mo, A. W., Sameshima-Yamashita, Y., & Kitamoto, H. (2020). Fungal community dynamics during degradation of poly (butylene succinate-co-adipate) film in two cultivated soils in Japan. Bioscience, Biotechnology, and Biochemistry, 1-11.	No			No			2020.0	Luminance	PBSA films used in this study were composed of Bionolle® 3001 (Showa Denko K. K., Tokyo, Japan)	Showa Denko	No	No	Soil	Soil	Japan	No		
Schlegelella thermodepolymerans	215580	PHB	Elbanna, K., Lütke-Eversloh, T., Jendrossek, D., Luftmann, H., & Steinbüchel, A. (2004). Studies on the biodegradability of polythioester copolymers and homopolymers by polyhydroxyalkanoate (PHA)-degrading bacteria and PHA depolymerases. Archives of microbiology, 182(2-3), 212-225.	No			No			2004.0	GC;NMR;FTIR;MS;MALDI-TOF	Poly(3HB) and poly(3HB-co-3MP) were isolated from R. eutropha H16 (DSM428).		Yes	No				No		
Serratia marcescens	615	LDPE	Azeko, S. T., Etuk-Udo, G. A., Odusanya, O. S., Malatesta, K., Anuku, N., & Soboyejo, W. O. (2015). Biodegradation of linear low density polyethylene by Serratia marcescens subsp. marcescens and its cell free extracts. Waste and biomass valorization, 6(6), 1047-1057.	No			No			2015.0	SEM;DSC;FTIR;Weight loss	LLDPE packages that were produced for the packaging of portable water called ‘‘pure water’’ in Abuja, Nigeria, were obtained.			No	Soil	Soil	Nigeria	No		
Serratia marcescens	615	HDPE	Baculi, R. Q., Melegrito, J. B., Sabaten, R. D. S., & Caranto, M. R. (2017). Biodegradation of High Density Polyethylene by Bacteria Isolated from Root Nodules of Phaseolus vulgaris. PHILIPPINE AGRICULTURAL SCIENTIST, 100, S21-S31.	No			No			2017.0	Weight loss;SEM;FTIR	Plastic bags	SM supermarket		No	Root nodules	Plant associated	Philippines	No		
Serratia marcescens	615	PLA	Nair, N. R., Sekhar, V. C., & Nampoothiri, K. M. (2016). Augmentation of a microbial consortium for enhanced polylactide (PLA) degradation. Indian journal of microbiology, 56(1), 59-63.	No			No			2016.0	Weight loss;SEM;Spectrophotometry	Commercial grade PLA with molecular weight of 85,000–160,000	Sigma Aldrich	Yes	No			India	No		
Serratia marcescens	615	PLA	Nair, N. R., Sekhar, V. C., & Nampoothiri, K. M. (2016). Augmentation of a microbial consortium for enhanced polylactide (PLA) degradation. Indian journal of microbiology, 56(1), 59-63.	No			No			2016.0	Weight loss;SEM;Spectrophotometry;Clear zone	Commercial grade PLA with molecular weight of 85,000–160,000	Sigma Aldrich	Yes	No			India	No		
Serratia marcescens	615	LDPE	Odusanya, S. A., Nkwogu, J. V., Alu, N., Udo, G. E., Ajao, J. A., Osinkolu, G. A., & Uzomah, A. C. (2013). Preliminary studies on microbial degradation of plastics used in packaging potable water in Nigeria. Nigerian Food Journal, 31(2), 63-72.	No			No			2013.0	SEM;DSC	The linear low density polyethylene (LLDPE) used for packaging water were randomly selected and washed thoroughly in deionized water.		No	No	Soil	Soil	Nigeria	No		
Serratia marcescens	615	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Serratia rubidaea	61652	PU	Kay, M. J., Morton, L. H. G., & Prince, E. L. (1991). Bacterial degradation of polyester polyurethane. International biodeterioration, 27(2), 205-222.	No			No			1991.0	Microscopy;Tensilometer;Weight loss	Biocide-free, dumb-bell shaped polyester polyurethane foam test pieces were used for these investigations			No	Plastic debris	Soil	UK	No		
Shewanella sp.	50422	PCL	Sekiguchi, T., Sato, T., Enoki, M., Kanehiro, H., Uematsu, K., & Kato, C. (2011). Isolation and characterization of biodegradable plastic degrading bacteria from deep-sea environments. JAMSTEC Report of Research and Development, 11, 33-41.	No			No			2011.0	Clear zone	PCL films	Sigma Aldrich	Yes	No	Sediment	Marine	Japan	No		
Shewanella sp.	50422	PHB	Sung, C. C., Tachibana, Y., Suzuki, M., Hsieh, W. C., & Kasuya, K. I. (2016). Identification of a poly (3-hydroxybutyrate)-degrading bacterium isolated from coastal seawater in Japan as Shewanella sp. Polymer degradation and stability, 129, 268-274.	No			No			2016.0	Clear zone;SEM;Weight loss	P(3HB)	Mitsubishi Gas Chemical		No	Sewater	Soil	Japan	No		
Shewanella sp.	50422	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Sphingobacterium multivorum	28454	LDPE	Montazer, Z., Habibi-Najafi, M. B., Mohebbi, M., & Oromiehei, A. (2018). Microbial degradation of UV-pretreated low-density polyethylene films by novel polyethylene-degrading bacteria isolated from plastic-dump soil. Journal of Polymers and the Environment, 26(9), 3613-3625.	No			No			2018.0	FTIR;SEM;Microscopy;Weight loss;CG-FIT	Low density polyethylene (Poliran LF0200 grade) granules and film (10 μm thickness; 99.95% purity without any additives and plasticizers) used for pasteurized milk packaging were supplied by Iran Polymer and Petrochemical Institute (IPPI)	Polymer and Petrochemical Institute (IPPI)	Yes	No	Soil	Landfill	Iran	No		
Sphingomonas sp.	28214	PVA	Hatanaka, T., Asahi, N., & Tsuji, M. (1995). Purification and characterization of poly (vinyl alcohol) dehydrogenase from Pseudomonas sp. 113P3. Bioscience, biotechnology, and biochemistry, 59(10), 1813-1816.	No			No			1995.0	Clear zone;Spectrophotometry	PVA 117	Kuraray		No	Activated sludge	Plastic waste dumping site	Japan	No		
Sphingomonas sp.	28214	PVA	Hatanaka, T., Asahi, N., & Tsuji, M. (1995). Purification and characterization of poly (vinyl alcohol) dehydrogenase from Pseudomonas sp. 113P3. Bioscience, biotechnology, and biochemistry, 59(10), 1813-1816.	No			No			1995.0	Clear zone;Spectrophotometry	PVA 117 was prepared by Kuraray Co., Ltd. The polymerization degree of PVA was 1700 and the saponification degree was 98.5%, and the tacticity was 55.0	Kuraray		No	Activated sludge	Plastic waste dumping site	Japan	No		
Staphylococcus cohnii	29382	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;SEM;FTIR;Tensilometer	LDPE, type “FGNX23-D022”;Bionolle (type #3001)	POLICHEM		No	Soil	Soil	Poland	No		
Staphylococcus epidermidis	1282	PU	Jansen, B., Schumacher-Perdreau, F., Peters, G., & Pulverer, G. (1991). Evidence for degradation of synthetic polyurethanes by Staphylococcus epidermidis. Zentralblatt für Bakteriologie, 276(1), 36-45.	No			No			1991.0	Weight loss;SEM;ATR-FTIR	Polyetherurethane TUFTANE (4 X 4 cm) was supplied as film of 400 um thickness. The polymer is composed of 4-4' diisocyanato diphenylmethane and poly(tetramethyleneglycol). To remove residual solvents or other low-molecular compounds, the polymers were extracted in acetone, ethanol and water before all experiments.	B. F. Goodrich		No	Catheter	Animal associated	Germany	No		
Staphylococcus sp.	29387	PCL	Adıgüzel, A. O., & Tunçer, M. (2017). Purification and characterization of cutinase from Bacillus sp. KY0701 isolated from plastic wastes. Preparative Biochemistry and Biotechnology, 47(9), 925-933.	No			No			2017.0	Weight loss;Clear zone	Plastic Waste		No	No	Plastic debris	Soil	Turkey	No		
Staphylococcus sp.	29387	PE	Kathiresan, K. (2003). Polythene and plastics-degrading microbes from the mangrove soil. Revista de biologia tropical, 51(3-4), 629-633.	No			No			2003.0	Weight loss	Pre weighed discs of 1cm diameter prepared from polythene bags and disposable plastic cups		No	No	Plastic debris	Mangrove	India	No		
Staphylococcus sp.	29387	LDPE	Usha, R., Sangeetha, T., & Palaniswamy, M. (2011). Screening of polyethylene degrading microorganisms from garbage soil. Libyan agriculture research center journal international, 2(4), 200-204.	No			No			2011.0	Clear zone	Low density polyethylene powder (LDPE)	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	India	No		
Staphylococcus xylosus	1288	LDPE	Nowak, B., Pająk, J., Drozd-Bratkowicz, M., & Rymarz, G. (2011). Microorganisms participating in the biodegradation of modified polyethylene films in different soils under laboratory conditions. International biodeterioration & biodegradation, 65(6), 757-767.	No			No			2011.0	Weight loss;SEM;FTIR;Tensilometer	LDPE, type “FGNX23-D022”;Bionolle (type #3001)	POLICHEM		No	Soil	Soil	Poland	No		
Stenotrophomonas humi	405444	LDPE	Montazer, Z., Habibi-Najafi, M. B., Mohebbi, M., & Oromiehei, A. (2018). Microbial degradation of UV-pretreated low-density polyethylene films by novel polyethylene-degrading bacteria isolated from plastic-dump soil. Journal of Polymers and the Environment, 26(9), 3613-3625.	No			No			2018.0	FTIR;SEM;Microscopy;Weight loss;CG-FIT	Low density polyethylene (Poliran LF0200 grade) granules and film (10 μm thickness; 99.95% purity without any additives and plasticizers) used for pasteurized milk packaging were supplied by Iran Polymer and Petrochemical Institute (IPPI)	Polymer and Petrochemical Institute (IPPI)	Yes	No	Soil	Landfill	Iran	No		
Stenotrophomonas maltophilia	40324	PHO	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	Poly(3-hydroxyoctanoate-co-3-hydroxyhexanoate [11%]) [P(3HO) or mcl PHA]	Biopolis		No			Spain	No		
Stenotrophomonas maltophilia	40324	PLA	Jeon, H. J., & Kim, M. N. (2013). Biodegradation of poly (l-lactide)(PLA) exposed to UV irradiation by a mesophilic bacterium. International Biodeterioration & Biodegradation, 85, 289-293.	No			No			2013.0	Weight loss;Tensilometer;GPC;SEC;FTIR	A 0.3 mm thick PLA sheet, which was made of NatureWorks  PLA Polymer 2003D, was donated by Green Chemical Co. (Seoul, Korea). Because biological degradation of PLA may be affected by a releasing agent such as silicone, which is usually sprayed on commercial PLA sheets, neat PLA powder with about 50 mmin diameter was prepared by grinding NatureWorks  PLA Polymer 4032D pellets.	Green Chemical		No	Compost	Soil	South Korea	No		
Stenotrophomonas maltophilia	40324	LDPE	Montazer, Z., Habibi-Najafi, M. B., Mohebbi, M., & Oromiehei, A. (2018). Microbial degradation of UV-pretreated low-density polyethylene films by novel polyethylene-degrading bacteria isolated from plastic-dump soil. Journal of Polymers and the Environment, 26(9), 3613-3625.	No			No			2018.0	FTIR;SEM;Microscopy;Weight loss;CG-FIT	Low density polyethylene (Poliran LF0200 grade) granules and film (10 μm thickness; 99.95% purity without any additives and plasticizers) used for pasteurized milk packaging were supplied by Iran Polymer and Petrochemical Institute (IPPI)	Polymer and Petrochemical Institute (IPPI)	Yes	No	Soil	Landfill	Iran	No		
Stenotrophomonas panacihumi	676599	PE	Jeon, H. J., & Kim, M. N. (2016). Isolation of mesophilic bacterium for biodegradation of polypropylene. International Biodeterioration & Biodegradation, 115, 244-249.	No			No			2016.0	Clear zone;GPC;CO2	YUHWA that was manufactured in a commercial scale polymerization reactor was used as PP. Low molecular weight polypropylene (LMWPP), LMWPP-1 having number average molecular weight (Mn) and weight average molecular weight (Mw) of 2800 and 10,300, respectively, and LMWPP-2 having Mn andMwof 3600 and 19,700, respectively, were also used. The LMWPPs were prepared by thermal degradation of a commercial PP under a strict nitrogen atmosphere.			No	Soil	Plastic waste dumping site	South Korea	No		
Stenotrophomonas panacihumi	676599	PP	Jeon, H. J., & Kim, M. N. (2016). Isolation of mesophilic bacterium for biodegradation of polypropylene. International Biodeterioration & Biodegradation, 115, 244-249.	No			No			2016.0	Clear zone;GPC;CO2	Low molecular weight polyethylene (LMWPE), LMWPE-1 (Mn: 790, Mw: 1700) and LMWPE-2 (Mn: 5,200, Mw: 23,700) were manufactured by thermal degradation of a commercial high density polyethylene (HDPE) and low density polyethylene (LDPE), respectively, under a strict nitrogen atmosphere.			No	Soil	Plastic waste dumping site	South Korea	No		
Stenotrophomonas sp.	69392	LDPE	Koutny, M., Amato, P., Muchova, M., Ruzicka, J., & Delort, A. M. (2009). Soil bacterial strains able to grow on the surface of oxidized polyethylene film containing prooxidant additives. International Biodeterioration & Biodegradation, 63(3), 354-357.	No			No			2009.0	Microscopy;Tensilometer	Preoxidized PE film was transparent LDPE film 60 mm thick containing prooxidant additives based on organometallic complexes. To balance the prodegradant activity phenolic antioxidants were used in the blends. 		No	No	Soil	Soil	France	No		
Stenotrophomonas sp.	69392	PE	Peixoto, J., Silva, L. P., & Krüger, R. H. (2017). Brazilian Cerrado soil reveals an untapped microbial potential for unpretreated polyethylene biodegradation. Journal of hazardous materials, 324, 634-644.	No			No			2017.0	ATR-FTIR;SEM;Spectrophotometry;Clear zone	0.1% ultra-high molecular weight PE powder (Sigma Aldrich, USA)	Sigma Aldrich	Yes	No	Plastic debris	Soil	Brazil	No		
Stenotrophomonas sp.	69392	Nylon	Tachibana, K., Hashimoto, K., Yoshikawa, M., & Okawa, H. (2010). Isolation and characterization of microorganisms degrading nylon 4 in the composted soil. Polymer degradation and stability, 95(6), 912-917.	No			No			2010.0	MS;SEM;BOD;Weight loss	Nylon 4 (Mn, 1.3x10^3 and Mw, 3.0x10^4) having benzamide and acyllactam at each chain end was prepared by the anionic ring-opening polymerization of 2-pyrrolidone using N-acyllactam and potassium t-butoxide as an initiator and a catalyst in a similar method to that described in our previous articles [17e19,25e27]. The average molecular weight was controlled by the mole ratio of the catalyst to the monomer to be from 1.3x10^3 to 3.0x10^4. The number average molecular weight of the low molecular weight nylon 4 (Mn, 1.3x10^3) was estimated from the 1H NMR and TOF-MS analyses and the weight average molecular weight of the relatively high molecular weight one (Mw, 3.0x10^4) was determined by viscometry [28]. 		Yes	No	Soil	Soil	Japan	No		
Stenotrophomonas sp.	69392	PVA	Ullah, M., Weng, C. H., Li, H., Sun, S. W., Zhang, H., Song, A. H., & Zhu, H. (2018). Degradation of polyvinyl alcohol by a novel bacterial strain Stenotrophomonas sp. SA21. Environmental technology, 39(16), 2056-2061.	No			No			2018.0	Clear zone;SEM;FTIR;Spectrophotometry	PVA1799			No	Sludge	Sewage/Sludge	China	No		
Stenotrophomonas sp.	69392	PHB	Wani, S. J., Shaikh, S. S., Tabassum, B., Thakur, R., Gulati, A., & Sayyed, R. Z. (2016). Stenotrophomonas sp. RZS 7, a novel PHB degrader isolated from plastic contaminated soil in Shahada, Maharashtra, Western India. 3 Biotech, 6(2), 179.	No			No			2016.0	Weight loss;Spectrophotometry				No	Soil	Plastic waste dumping site	India	No		
Strain IZU-154	175245	Nylon	Deguchi, T., Kakezawa, M., & Nishida, T. (1997). Nylon biodegradation by lignin-degrading fungi. Appl. Environ. Microbiol., 63(1), 329-331.	No			No			1997.0	NMR;GPC	Nylon-66 membrane	Sartrius		No				No		
Strain IZU-154	175245	Nylon	Deguchi, T., Kitaoka, Y., Kakezawa, M., & Nishida, T. (1998). Purification and characterization of a nylon-degrading enzyme. Applied and environmental microbiology, 64(4), 1366-1371.	No			No			1999.0	NMR;SEM;GPC	Nylon-66 membrane	Sartorius		No	Culture collection	Culture collection		Yes		
Streptoalloteichus hindustanus	2017	PLA	Jarerat, A., Pranamuda, H., & Tokiwa, Y. (2002). Poly (L‐lactide)‐degrading activity in various actinomycetes. Macromolecular Bioscience, 2(9), 420-428.	No			No			2002.0	Clear zone;SEM;TOC;SEC	 LACTY 1012 (number-average molecular weight, Mn ¼ 3.4 _x005F	Shimadzu		No	Culture collection	Culture collection		No		
Streptococcus sp.	1306	PE	Kathiresan, K. (2003). Polythene and plastics-degrading microbes from the mangrove soil. Revista de biologia tropical, 51(3-4), 629-633.	No			No			2003.0	Weight loss	Pre weighed discs of 1cm diameter prepared from polythene bags and disposable plastic cups		No	No	Plastic debris	Mangrove	India	No		
Streptomyces albogriseolus	1887	PE	Shao, H., Chen, M., Fei, X., Zhang, R., Zhong, Y., Ni, W., ... & Tan, X. (2019). Complete Genome Sequence and Characterization of a Polyethylene Biodegradation Strain, Streptomyces Albogriseolus LBX-2. Microorganisms, 7(10), 379.	No			No			2019.0	SEM;Tensilometer;Weight loss	PE powder samples (Sinopec Maoming petrochemical company, Maoming, Guangdong, China) with a molecular weight (MW) of 5000 Da and 10,000 Da	Sinopec Maoming petrochemical company		No	Soil	Soil	China	No		
Streptomyces albovinaceus	66867	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Streptomyces anulatus	1892	PHO	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	Poly(3-hydroxyoctanoate-co-3-hydroxyhexanoate [11%]) [P(3HO) or mcl PHA]	Biopolis		No			Spain	No		
Streptomyces anulatus	1892	P3HP	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	P3HP	CIBA		No			Spain	No		
Streptomyces anulatus	1892	PCL	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PCL	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces anulatus	1892	PHB	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PHB	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces anulatus	1892	PHBV	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PHBV	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces atratus	1893	PHO	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	Poly(3-hydroxyoctanoate-co-3-hydroxyhexanoate [11%]) [P(3HO) or mcl PHA]	Biopolis		No			Spain	No		
Streptomyces atratus	1893	P3HP	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	P3HP	CIBA		No			Spain	No		
Streptomyces atratus	1893	PHB	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PHB	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces atratus	1893	PHBV	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PHBV	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces badius	1941	LDPE Blend	Lee, B., Pometto, A. L., Fratzke, A., & Bailey, T. B. (1991). Biodegradation of degradable plastic polyethylene by Phanerochaete and Streptomyces species. Appl. Environ. Microbiol., 57(3), 678-685.	No			No			1991.0	Weight loss;Tensilometer;GPC;GPC	Archer-Daniels-Midland POLYCLEAN masterbatch degradable plastic films made with linear low density polyethylene containing pro-oxidant and 6% starch were used. Pro-oxidants are mixtures of transition metals (i.e., Fe, Zn, Ni, and/or Mn) and lipids (i.e., corn or soybean oil) which are compounded into the final polyethylene product at very low levels. Films were commercially prepared according to Archer-Daniels-Midland-recommended specifications.	Archer-Daniels-Midland	No	No	Culture collection	Culture collection		No		
Streptomyces badius	1941	PE Blend	Pometto, A. L., Lee, B. T., & Johnson, K. E. (1992). Production of an extracellular polyethylene-degrading enzyme (s) by Streptomyces species. Appl. Environ. Microbiol., 58(2), 731-733.	No			No			1992.0	FTIR;Tensilometer;Weight loss;GPC	The 6% starch-polyethylene-prooxidant degradable plastic was prepared commercially with POLYCLEAN masterbatch	Archer-Daniels-Midland	No	No	Culture collection	Culture collection		No		
Streptomyces beijiangensis	163361	PHO	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	Poly(3-hydroxyoctanoate-co-3-hydroxyhexanoate [11%]) [P(3HO) or mcl PHA]	Biopolis		No			Spain	No		
Streptomyces beijiangensis	163361	PCL	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PCL	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces beijiangensis	163361	PHB	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PHB	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces beijiangensis	163361	PHBV	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PHBV	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces ciscaucasicus	58343	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Streptomyces ciscaucasicus	58343	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Streptomyces cyaneogriseus	68192	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Streptomyces cyaneogriseus	68192	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Streptomyces griseus	1911	LDPE Blend	Lee, B., Pometto, A. L., Fratzke, A., & Bailey, T. B. (1991). Biodegradation of degradable plastic polyethylene by Phanerochaete and Streptomyces species. Appl. Environ. Microbiol., 57(3), 678-685.	No			No			1991.0	Weight loss;Tensilometer;GPC;GPC	Archer-Daniels-Midland POLYCLEAN masterbatch degradable plastic films made with linear low density polyethylene containing pro-oxidant and 6% starch were used. Pro-oxidants are mixtures of transition metals (i.e., Fe, Zn, Ni, and/or Mn) and lipids (i.e., corn or soybean oil) which are compounded into the final polyethylene product at very low levels. Films were commercially prepared according to Archer-Daniels-Midland-recommended specifications.	Archer-Daniels-Midland	No	No	Culture collection	Culture collection		No		
Streptomyces griseus	1911	PE Blend	Pometto, A. L., Lee, B. T., & Johnson, K. E. (1992). Production of an extracellular polyethylene-degrading enzyme (s) by Streptomyces species. Appl. Environ. Microbiol., 58(2), 731-733.	No			No			1992.0	FTIR;Tensilometer;Weight loss;GPC	The 6% starch-polyethylene-prooxidant degradable plastic was prepared commercially with POLYCLEAN masterbatch	Archer-Daniels-Midland	No	No	Culture collection	Culture collection		No		
Streptomyces lateritius	67313	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Streptomyces lateritius	67313	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Streptomyces omiyaensis	68247	PHO	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	Poly(3-hydroxyoctanoate-co-3-hydroxyhexanoate [11%]) [P(3HO) or mcl PHA]	Biopolis		No			Spain	No		
Streptomyces omiyaensis	68247	P3HP	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	P3HP	CIBA		No			Spain	No		
Streptomyces omiyaensis	68247	PCL	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PCL	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces omiyaensis	68247	PHB	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PHB	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces omiyaensis	68247	PHBV	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PHBV	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces polychromogenes	67342	PHB	Suzuki, M., Tachibana, Y., Kazahaya, J. I., Takizawa, R., Muroi, F., & Kasuya, K. I. (2017). Difference in environmental degradability between poly (ethylene succinate) and poly (3-hydroxybutyrate). Journal of Polymer Research, 24(12), 217.	No			No			2017.0	Clear zone	Poly (3-hydroxybutric acid) (P(3HB) (Mn = 6.8 × 10^4, Mn/Mw = 2.6)	Mitsubishi Gas Chemical		No				No		
Streptomyces pulveraceus	68258	PHO	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	Poly(3-hydroxyoctanoate-co-3-hydroxyhexanoate [11%]) [P(3HO) or mcl PHA]	Biopolis		No			Spain	No		
Streptomyces pulveraceus	68258	PCL	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PCL	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces pulveraceus	68258	PHB	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PHB	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces pulveraceus	68258	PHBV	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PHBV	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces roseolus	67358	P3HP	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	P3HP	CIBA		No			Spain	No		
Streptomyces roseolus	67358	PHB	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PHB	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces roseolus	67358	PHBV	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	No			No			2012.0	Clear zone	PHBV	Sigma Aldrich	Yes	No			Spain	No		
Streptomyces sp.	1931	PCL	Adıgüzel, A. O., & Tunçer, M. (2017). Purification and characterization of cutinase from Bacillus sp. KY0701 isolated from plastic wastes. Preparative Biochemistry and Biotechnology, 47(9), 925-933.	No			No			2017.0	Weight loss;Clear zone	Plastic Waste		No	No	Plastic debris	Soil	Turkey	No		
Streptomyces sp.	1931	PHB	Calabia, B. P., & Tokiwa, Y. (2004). Microbial degradation of poly (D-3-hydroxybutyrate) by a new thermophilic Streptomyces isolate. Biotechnology letters, 26(1), 15-19.	No			No			2004.0	Clear zone;TOC	PHB powder, with a number-average molecular weight (Mn) of 2.1 × 105 (Mitsubishi Gas Chemical)	Mitsubishi Gas Chemical		No		Culture collection		No		
Streptomyces sp.	1931	LDPE	Deepika, S., & Madhuri, R. J. (2015). Biodegradation of low density polyethylene by micro-organisms from garbage soil. Journal of Experimental Biology and Agricultural Sciences, 3(1), 15-21.	No			No			2015.0	Clear zone;Weight loss	Low density polyethylene powder (LDPE) with 53-75 µm particle size was obtained from Sigma Aldrich Chemical Co (Product of USA) with density 0.94g/ml at 250C. Low density polyethylene granules from Pack worth polymers and Pack mates India Private Ltd (Hyderabad, INDIA).	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	India	No		
Streptomyces sp.	1931	PHB	Gangurde, N. S., Patil, Y. P., Jain, R., & Sayyed, R. Z. (2017). Poly-β-hydroxybutyrate biodegradation by mixed culture population vis-à-vis single culture population under varying environmental conditions: A new approach.	No			No			2017.0	Weight loss;Clear zone	PHB production was carried out by Alcaligenes sp. RZS 4 (Gene bank accession No. JN374993) using two-step cultivation process.		Yes	No	Soil	Soil	India	No		
Streptomyces sp.	1931	PES	Hoang, K. C., Lee, C. Y., Lai, Y. C., & Liau, C. Y. (2008). TH‐11, a Streptomyces sp. Strain that Degrades Poly (3‐Hydroxybutyrate) and Poly (Ethylene Succinate). Journal of the Chinese Chemical Society, 55(6), 1214-1220.	No			No			2008.0	Clear zone;Weight loss;SEM;Microscopy;TOC	Poly(ethylene succinate) (PES) (Mn of 1.0   104)	Sigma Aldrich	Yes	No	Sediment	River/Lake	Taiwan	No		
Streptomyces sp.	1931	PHB	Hoang, K. C., Lee, C. Y., Lai, Y. C., & Liau, C. Y. (2008). TH‐11, a Streptomyces sp. Strain that Degrades Poly (3‐Hydroxybutyrate) and Poly (Ethylene Succinate). Journal of the Chinese Chemical Society, 55(6), 1214-1220.	No			No			2008.0	Clear zone;Weight loss;SEM;Microscopy;TOC	Poly(3-hydroxybutyrate) (PHB), with a number- average molecular weight (Mn) of 2.1   105	Sigma Aldrich	Yes	No	Sediment	River/Lake	Taiwan	No		
Streptomyces sp.	1931	PCL	Hoang, K. C., Lee, C. Y., Tseng, M., & Chu, W. S. (2007). Polyester-degrading actinomycetes isolated from the Touchien River of Taiwan. World Journal of Microbiology and Biotechnology, 23(2), 201-205.	No			No			2007.0	Clear zone	Poly(e-caprolactone) (PCL, Mn = 6.8x10^5)	Sigma Aldrich	Yes	No	Sediment	River/Lake	Taiwan	No		
Streptomyces sp.	1931	PES	Hoang, K. C., Lee, C. Y., Tseng, M., & Chu, W. S. (2007). Polyester-degrading actinomycetes isolated from the Touchien River of Taiwan. World Journal of Microbiology and Biotechnology, 23(2), 201-205.	No			No			2007.0	Clear zone	Poly(ethylene succinate) (PES) with a number-average molecular weight ( Mn) of 1.0x10^4	Sigma Aldrich	Yes	No	Sediment	River/Lake	Taiwan	No		
Streptomyces sp.	1931	PHB	Hoang, K. C., Lee, C. Y., Tseng, M., & Chu, W. S. (2007). Polyester-degrading actinomycetes isolated from the Touchien River of Taiwan. World Journal of Microbiology and Biotechnology, 23(2), 201-205.	No			No			2007.0	Clear zone	Poly(b-hydroxybutyrate) (PHB, Mn = 5.4x10^5)	Sigma Aldrich	Yes	No	Sediment	River/Lake	Taiwan	No		
Streptomyces sp.	1931	LDPE Blend	Lee, B., Pometto, A. L., Fratzke, A., & Bailey, T. B. (1991). Biodegradation of degradable plastic polyethylene by Phanerochaete and Streptomyces species. Appl. Environ. Microbiol., 57(3), 678-685.	No			No			1991.0	Weight loss;Tensilometer;GPC;GPC	Archer-Daniels-Midland POLYCLEAN masterbatch degradable plastic films made with linear low density polyethylene containing pro-oxidant and 6% starch were used. Pro-oxidants are mixtures of transition metals (i.e., Fe, Zn, Ni, and/or Mn) and lipids (i.e., corn or soybean oil) which are compounded into the final polyethylene product at very low levels. Films were commercially prepared according to Archer-Daniels-Midland-recommended specifications.	Archer-Daniels-Midland	No	No	Culture collection	Culture collection		No		
Streptomyces sp.	1931	PHB	Mabrouk, M. M., & Sabry, S. A. (2001). Degradation of poly (3-hydroxybutyrate) and its copolymer poly (3-hydroxybutyrate-co-3-hydroxyvalerate) by a marine Streptomyces sp. SNG9. Microbiological research, 156(4), 323-335.	No			No			2001.0	Clear zone;SEM	Homopolymer P(3HB), and copolymers P(3HB-co-10%-3HV) and P(3HB-co-20%-3HV) were obtained as powder. Circular films (1-1.5 mm thickness) of P(3HB) and copolymers P(3HB-co-10%-3HV) and (P3HB-co-20%-3HV) were prepared by solvent casting techniques from chloroform solutions of polyesters. The solution-cast films were aged for at least one month to reach equilibrium crystalinity prior to analysis (Bloembergen et al. 1986).	Sigma Aldrich	Yes	No	Sediment	Marine	Egypt	No		
Streptomyces sp.	1931	PHBV	Mabrouk, M. M., & Sabry, S. A. (2001). Degradation of poly (3-hydroxybutyrate) and its copolymer poly (3-hydroxybutyrate-co-3-hydroxyvalerate) by a marine Streptomyces sp. SNG9. Microbiological research, 156(4), 323-335.	No			No			2001.0	Clear zone;SEM	Homopolymer P(3HB), and copolymers P(3HB-co-10%-3HV) and P(3HB-co-20%-3HV) were obtained as powder. Circular films (1-1.5 mm thickness) of P(3HB) and copolymers P(3HB-co-10%-3HV) and (P3HB-co-20%-3HV) were prepared by solvent casting techniques from chloroform solutions of polyesters. The solution-cast films were aged for at least one month to reach equilibrium crystalinity prior to analysis (Bloembergen et al. 1986).	Sigma Aldrich	Yes	No	Sediment	Marine	Egypt	No		
Streptomyces sp.	1931	PHB	Tansengco, M., & Dogma Jr, I. (1999). Microbial degradation of poly‐β‐hydroxybutyrate using landfill soils. Acta biotechnologica, 19(3), 191-203.	No			No			1999.0	SEM;TOC;Weight loss;Clear zone	Samples of poly-&hydroxybutyrate or PHB granules (-O-CH(CH3)-CH2-CO-}n exhibiting an average molecular weight (Mw) of 9.4 x10^5, a melting temperature of 170 °C and a purity of 98%. 	Mitsubishi Gas Chemical	Yes	No	Soil	Landfill	Philippines	No		
Streptomyces sp.	1931	LDPE	Usha, R., Sangeetha, T., & Palaniswamy, M. (2011). Screening of polyethylene degrading microorganisms from garbage soil. Libyan agriculture research center journal international, 2(4), 200-204.	No			No			2011.0	Clear zone	Low density polyethylene powder (LDPE)	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	India	No		
Streptomyces thermocarboxydovorans	59298	PHB	Calabia, B. P., & Tokiwa, Y. (2004). Microbial degradation of poly (D-3-hydroxybutyrate) by a new thermophilic Streptomyces isolate. Biotechnology letters, 26(1), 15-19.	No			No			2004.0	Clear zone;TOC	PHB powder, with a number-average molecular weight (Mn) of 2.1 × 105 (Mitsubishi Gas Chemical)	Mitsubishi Gas Chemical		No		Culture collection		No		
Streptomyces viridosporus	67581	LDPE Blend	Lee, B., Pometto, A. L., Fratzke, A., & Bailey, T. B. (1991). Biodegradation of degradable plastic polyethylene by Phanerochaete and Streptomyces species. Appl. Environ. Microbiol., 57(3), 678-685.	No			No			1991.0	Weight loss;Tensilometer;GPC;GPC	Archer-Daniels-Midland POLYCLEAN masterbatch degradable plastic films made with linear low density polyethylene containing pro-oxidant and 6% starch were used. Pro-oxidants are mixtures of transition metals (i.e., Fe, Zn, Ni, and/or Mn) and lipids (i.e., corn or soybean oil) which are compounded into the final polyethylene product at very low levels. Films were commercially prepared according to Archer-Daniels-Midland-recommended specifications.	Archer-Daniels-Midland	No	No	Culture collection	Culture collection		No		
Streptomyces viridosporus	67581	PE Blend	Pometto, A. L., Lee, B. T., & Johnson, K. E. (1992). Production of an extracellular polyethylene-degrading enzyme (s) by Streptomyces species. Appl. Environ. Microbiol., 58(2), 731-733.	No			No			1992.0	FTIR;Tensilometer;Weight loss;GPC	The 6% starch-polyethylene-prooxidant degradable plastic was prepared commercially with POLYCLEAN masterbatch	Archer-Daniels-Midland	No	No	Culture collection	Culture collection		No		
Talaromyces funiculosus	28572	PCL	Benedict, C. V., Cameron, J. A., & Huang, S. J. (1983). Polycaprolactone degradation by mixed and pure cultures of bacteria and a yeast. Journal of Applied Polymer Science, 28(1), 335-342.	No			No			1983.0	Clear zone;GPC	Polycaprolactone 700 (PCL-700), PCL-300, and LPS-60 with molecular weights of 35,000,18,600, and 7,130 Wr, respectively, were obtained from Union Carbide Corp., New York, N.Y. The PCL designated LPS-60 by the manufacturer contains a phthalic acid residue covalently linked to the chain ends but otherwise is structurally identical to PCL-700 and PCL-300. No low molecular weight, contaminants were seen by chromatographic analysis of the polymers using THF, chloroform, or dichloromethane as solvents. Infrared spectroscopy of PCL-700 resulted in a spectrum identical to the published standard.6 All polymers showed broad molecular weight distributions. Polydispersities (Mv/Mn) ranged from 1.892 to 1.978.	Union Carbide	Yes	No	Culture collection	River/Lake	USA	No		
Talaromyces minioluteus	28574	PHB	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	PHB was provided by ICI in powder form (200 mm) and its weight average molecular weight was 470,000 g/ mol.	ICI, UK		No	Plastic debris	Soil	South Korea	No		
Talaromyces variabilis	28576	PS	Tian, L., Kolvenbach, B., Corvini, N., Wang, S., Tavanaie, N., Wang, L., ... & Ji, R. (2017). Mineralisation of 14C-labelled polystyrene plastics by Penicillium variabile after ozonation pre-treatment. New biotechnology, 38, 101-105.	No			No			2017.0	14C;SEM;FTIR;GPC	Two 14C-labelled PS polymers were synthesisedwith molecular weight (MW) of 15 and 29 kDa	Sigma Aldrich	Yes	No				No		
Terrabacter tumescens	60443	PHA	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHA (BIOPOL-D400P-PB36)	Monsanto		No	Soil	Soil	Japan	No		
Terracoccus luteus	53356	PHA	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHA (BIOPOL-D400P-PB36)	Monsanto		No	Soil	Soil	Japan	No		
Trametes versicolor	5325	Nylon	Deguchi, T., Kakezawa, M., & Nishida, T. (1997). Nylon biodegradation by lignin-degrading fungi. Appl. Environ. Microbiol., 63(1), 329-331.	No			No			1997.0	GPC	Nylon-66 membrane	Sartrius		No				No		
Trametes versicolor	5325	PVC	Kırbaş, Z., Keskin, N., & Güner, A. (1999). Biodegradation of polyvinylchloride (PVC) by white rot fungi. Bulletin of environmental contamination and toxicology, 63(3), 335-342.	No			No			1999.0	FTIR;Spectrophotometry;Weight loss;Viscosimeter	PVC having low molecular weight was used for the studies. The polymer supplied from Aldrich Chemical Company Inc. PVC was transformed into films before adding in the liquid culture media.	Sigma Aldrich	Yes	No	Culture collection	Culture collection		No		
Trichoderma hamatum	49224	PBSA	Yamamoto-Tamura, K., Hoshino, Y. T., Tsuboi, S., Huang, C., Kishimoto-Mo, A. W., Sameshima-Yamashita, Y., & Kitamoto, H. (2020). Fungal community dynamics during degradation of poly (butylene succinate-co-adipate) film in two cultivated soils in Japan. Bioscience, Biotechnology, and Biochemistry, 1-11.	No			No			2020.0	Luminance	PBSA films used in this study were composed of Bionolle® 3001 (Showa Denko K. K., Tokyo, Japan)	Showa Denko	No	No	Soil	Soil	Japan	No		
Trichoderma harzianum	5544	PCL	Bentham, R. H., Morton, L. H. G., & Allen, N. G. (1987). Rapid assessment of the microbial deterioration of polyurethanes. International biodeterioration, 23(6), 377-386.	No			No			1987.0	Clear zone;Tensilometer;Weight loss	Two similar formulations of polyurethane foam were investigated, supplied as dumbbell-shaped test pieces. The materials were both polyester polyurethanes, one formulation, however, contained VINYZENE BP (10,10'-oxybis-phenoxarsine) as the formulation biocide. Another formulation was also available, an unprotected polyester polyurethane elastomer.		No	No	Plastic debris	Compost		No		
Trichoderma harzianum	5544	PHB	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PHB granules	Panara		No	Soil	Soil	Slovakia	No		
Trichoderma harzianum	5544	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Trichoderma harzianum	5544	PLA	Jeszeová, L., Puškárová, A., Bučková, M., Kraková, L., Grivalský, T., Danko, M., ... & Pangallo, D. (2018). Microbial communities responsible for the degradation of poly (lactic acid)/poly (3-hydroxybutyrate) blend mulches in soil burial respirometric tests. World Journal of Microbiology and Biotechnology, 34(7), 101.	No			No			2018.0	CO2;Clear zone	PLA granules	Polymer Institute, SAS		No	Soil	Soil	Slovakia	No		
Trichoderma harzianum	5544	PLA	Torres, A., Li, S. M., Roussos, S., & Vert, M. (1996). Screening of microorganisms for biodegradation of poly (lactic-acid) and lactic acid-containing polymers. Appl. Environ. Microbiol., 62(7), 2393-2397.	No			No			1996.0	HPLC;SEM	Typically, 1 liter of DL-LA commercial solution was heated under normal pressure to gently distillate water. When the temperature reached 1308C, vacuum was applied and distillation was controlled as desired. One fraction of racemic oligomers (Mw 5 1,000, I 5 Mw/Mn 5 1.3) was used for the screening of filamentous fungi, and another one (Mw 5 2,000, I 5 1.3) was used for soil screening. Molecular weights were determined by size exclusion chromatography. 	Sigma Aldrich	Yes	No		Culture collection		No		
Trichoderma sp.	1715253	PHA	Boyandin, A. N., Prudnikova, S. V., Karpov, V. A., Ivonin, V. N., Đỗ, N. L., Nguyễn, T. H., ... & Volova, T. G. (2013). Microbial degradation of polyhydroxyalkanoates in tropical soils. International Biodeterioration & Biodegradation, 83, 77-84.	No			No			2013.0	Weight loss;GPC;X-ray	The polymers were synthesized in Wautersia eutropha B5786 microbial culture (the strain is registered in the Russian Collection of Industrial Microorganisms).			No	Soil	Soil	Vietnam	No		
Trichoderma sp.	1715253	PU	Loredo-Treviño, A., García, G., Velasco-Téllez, A., Rodríguez-Herrera, R., & Aguilar, C. N. (2011). Polyurethane foam as substrate for fungal strains. Advances in Bioscience and Biotechnology, 2(2), 52.	No			No			2011.0	Clear zone	All reagents were analytical grade and all analysis was performed by triplicate. PU was provided by Nemak corporation and these PU was used for every test unless indicated otherwise.	Nemak corporation		No	Culture collection	Culture collection		No		
Trichoderma sp.	1715253	PLA	Torres, A., Li, S. M., Roussos, S., & Vert, M. (1996). Screening of microorganisms for biodegradation of poly (lactic-acid) and lactic acid-containing polymers. Appl. Environ. Microbiol., 62(7), 2393-2397.	No			No			1996.0	HPLC;SEM	Typically, 1 liter of DL-LA commercial solution was heated under normal pressure to gently distillate water. When the temperature reached 1308C, vacuum was applied and distillation was controlled as desired. One fraction of racemic oligomers (Mw 5 1,000, I 5 Mw/Mn 5 1.3) was used for the screening of filamentous fungi, and another one (Mw 5 2,000, I 5 1.3) was used for soil screening. Molecular weights were determined by size exclusion chromatography. 	Sigma Aldrich	Yes	No		Culture collection		No		
Trichoderma sp.	1715253	PCL	Urbanek, A. K., Rymowicz, W., Strzelecki, M. C., Kociuba, W., Franczak, Ł., & Mirończuk, A. M. (2017). Isolation and characterization of Arctic microorganisms decomposing bioplastics. AMB Express, 7(1), 148.	No			No			2017.0	Clear zone	 PCL pellets were purchased from TRESNO (Poland)	TRESNO		No	Soil	Soil	Svalbard	No		
Trichoderma virens	29875	LDPE	Manzur, A., Limón‐González, M., & Favela‐Torres, E. (2004). Biodegradation of physicochemically treated LDPE by a consortium of filamentous fungi. Journal of Applied Polymer Science, 92(1), 265-271.	No			No			2004.0	CO2;DSC;WAXS;FTIR;SEM;GC	Commercial low density polyethylene was used (17,070, produced by Pemex, Mexico). Its density and flow index values were 0.917 g/cc and 7 g/10 min, respectively.	Pemex		No				No		
Trichoderma viride	5547	PLA	Lipsa, R., Tudorachi, N., Darie-Nita, R. N., Oprică, L., Vasile, C., & Chiriac, A. (2016). Biodegradation of poly (lactic acid) and some of its based systems with Trichoderma viride. International journal of biological macromolecules, 88, 515-526.	No			No			2016.0	Weight loss;FTIR-ATR;GPC;SEM;TGA	PLA utilized in this study was 2002 D grade, purchased from NatureWorks LLC (Minnetonka, USA), with 1.24 g/cm3densitymelt flow index (MFI): 5–7 g/10 min (at 210◦C/2.16 kg). The aver-age number molecular weight (Mn) and polydispersity index (PDI), determined by GPC in tetrahydrofuran (THF), at 20◦C were106 × 103g/mol and 1.64 respectively.	NatureWorks LLC		No	Soil	Soil		No		
Trichoderma viride	5547	LDPE	Munir, E., Harefa, R. S. M., Priyani, N., & Suryanto, D. (2018). Plastic degrading fungi Trichoderma viride and Aspergillus nomius isolated from local landfill soil in Medan. In IOP Conference Series: Earth and Environmental Science (Vol. 126, No. 1, p. 012145). IOP Publishing.	No			No			2018.0	SEM;Weight loss;Tensilometer;Clear zone	LDPE powder was prepared by dissolving LDPE beads in xylene with continuous stirring. The clump LDPE was rinsed with 96% ethanol and dried completely in an oven at 50° C. The LDPE was cut into small pieces and smashed with blander to get powder form.			No	Soil	Landfill	Indonesia	No		
Tritirachium album	37998	PLA	Tokiwa, Y., & Jarerat, A. (2005). Accelerated Microbial Degradation of Poly (l‐lactide). In Macromolecular Symposia (Vol. 224, No. 1, pp. 367-376). Weinheim: WILEY‐VCH Verlag.	No			No			2005.0	Weight loss;Clear zone;TOC	High molecular weight (1.3 × 105) PLA film			No				No		
Ulocladium sp.	1914427	PC	Arefian, M., Zia, M., Tahmourespour, A., & Bayat, M. (2013). Polycarbonate biodegradation by isolated molds using clear-zone and atomic force microscopic methods. International Journal of Environmental Science and Technology, 10(6), 1319-1324.	No			No			2013.0	Clear zone;AFM				No	Soil	Soil	Iran	No		
Undibacterium pigrum	401470	PHBH	Morohoshi, T., Oi, T., Aiso, H., Suzuki, T., Okura, T., & Sato, S. (2018). Biofilm formation and degradation of commercially available biodegradable plastic films by bacterial consortiums in freshwater environments. Microbes and environments, ME18033.	No			No			2018.0	Clear zone;Weight loss				No	Water	River/Lake	Japan	No		
Variovorax paradoxus	34073	PHB	Mergaert, J., Ruffieux, K., Bourban, C., Storms, V., Wagemans, W., Wintermantel, E., & Swings, J. (2000). In vitro biodegradation of polyester-based plastic materials by selected bacterial cultures. Journal of Polymers and the Environment, 8(1), 17-27.	No			No			2000.0	Tensilometer;Weight loss;Clear zone	PHB, Poly(3-hydroxybutyrate), powder, Biopol G08	Zeneca Bioproducts		No	Soil	Soil		No		
Variovorax paradoxus	34073	PHB	Mergaert, J., Ruffieux, K., Bourban, C., Storms, V., Wagemans, W., Wintermantel, E., & Swings, J. (2000). In vitro biodegradation of polyester-based plastic materials by selected bacterial cultures. Journal of Polymers and the Environment, 8(1), 17-27.	No			No			2000.0	Weight loss;Tensilometer;Clear zone	The polymers were obtained from ZENECA Bio Products either as injection-moulded, dog bone-shaped tensile test pieces, 83 mm long, 2 mm thick, with a total surface area of approx. 19.5 cm2, and weighing approximately 1.75 g, or as powder. Three polymers were investigated: homopolymer P(3HB) batch G08, copolymer P(3HB-co-10%-3HV) batch PSMll+PSM20, and copolymer P(3HB-co-20%-3HV) batch PSM11.	Zeneca Bioproducts		No	Water		Belgium	No		
Variovorax paradoxus	34073	PHBV	Mergaert, J., Ruffieux, K., Bourban, C., Storms, V., Wagemans, W., Wintermantel, E., & Swings, J. (2000). In vitro biodegradation of polyester-based plastic materials by selected bacterial cultures. Journal of Polymers and the Environment, 8(1), 17-27.	No			No			2000.0	Tensilometer;Weight loss;Clear zone	PHBXV, poly(3-hydroxybutyrate-co-x% 3-hydroxyvalerate), films, granules, powder, Biopol	Zeneca Bioproducts		No	Soil	Soil		No		
Variovorax paradoxus	34073	PCL	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PCL (PLACCEL-230)	Daicel Chemical Industries		No	Soil	Soil	Japan	No		
Variovorax paradoxus	34073	PHA	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHA (BIOPOL-D400P-PB36)	Monsanto		No	Soil	Soil	Japan	No		
Variovorax paradoxus	34073	PHC	Suyama, T., Tokiwa, Y., Ouichanpagdee, P., Kanagawa, T., & Kamagata, Y. (1998). Phylogenetic affiliation of soil bacteria that degrade aliphatic polyesters available commercially as biodegradable plastics. Appl. Environ. Microbiol., 64(12), 5008-5011.	No			No			1998.0	Clear zone	PHC (PCD-2000)	Toagosei		No	Soil	Soil	Japan	No		
Vibrio alginolyticus	663	PVA Blend	Raghul, S. S., Bhat, S. G., Chandrasekaran, M., Francis, V., & Thachil, E. T. (2014). Biodegradation of polyvinyl alcohol-low linear density polyethylene-blended plastic film by consortium of marine benthic vibrios. International Journal of Environmental Science and Technology, 11(7), 1827-1834.	No			No			2014.0	Tensilometer;SEM;Clear zone	Molecular formula of polyvinyl alcohol is (C4H10O)n, having a molecular weight of 17,300 and its viscosity at 4 % concentration in water at 20C is 3 mPa s	Rolex Chemical Industries		No	Sediment 	Marine	India	No		
Vibrio alginolyticus	663	LLDPE Blend	Raghul, S. S., Bhat, S. G., Chandrasekaran, M., Francis, V., & Thachil, E. T. (2014). Biodegradation of polyvinyl alcohol-low linear density polyethylene-blended plastic film by consortium of marine benthic vibrios. International Journal of Environmental Science and Technology, 11(7), 1827-1834.	No			No			2015.0	Tensilometer;SEM;Clear zone	Film-grade LLDPE with the density of 0.920 g/cm3	Reliance Industries		No	Sediment 	Marine	India	No		
Vibrio furnisii	29494	Nylon	Sudhakar, M., Priyadarshini, C., Doble, M., Murthy, P. S., & Venkatesan, R. (2007). Marine bacteria mediated degradation of nylon 66 and 6. International Biodeterioration & Biodegradation, 60(3), 144-151.	No			No			2007.0	DSC;FTIR;Weight loss;EFM	Commercial grade nylon 6 (Mn ¼ 58,000) fibers (210D) and nylon 66 (Mn ¼ 55,000) pellets (Prime chips)	SRF		No		Marine	India	No		
Vibrio parahaemolyticus	670	PVA Blend	Raghul, S. S., Bhat, S. G., Chandrasekaran, M., Francis, V., & Thachil, E. T. (2014). Biodegradation of polyvinyl alcohol-low linear density polyethylene-blended plastic film by consortium of marine benthic vibrios. International Journal of Environmental Science and Technology, 11(7), 1827-1834.	No			No			2016.0	Tensilometer;SEM;Clear zone	Molecular formula of polyvinyl alcohol is (C4H10O)n, having a molecular weight of 17,300 and its viscosity at 4 % concentration in water at 20C is 3 mPa s	Rolex Chemical Industries		No	Sediment 	Marine	India	No		
Vibrio parahaemolyticus	670	LLDPE Blend	Raghul, S. S., Bhat, S. G., Chandrasekaran, M., Francis, V., & Thachil, E. T. (2014). Biodegradation of polyvinyl alcohol-low linear density polyethylene-blended plastic film by consortium of marine benthic vibrios. International Journal of Environmental Science and Technology, 11(7), 1827-1834.	No			No			2017.0	Tensilometer;SEM;Clear zone	Film-grade LLDPE with the density of 0.920 g/cm3	Reliance Industries		No	Sediment 	Marine	India	No		
Vibrio sp.	678	PET	Sarkhel, R., Sengupta, S., Das, P., & Bhowal, A. (2020). Comparative biodegradation study of polymer from plastic bottle waste using novel isolated bacteria and fungi from marine source. Journal of Polymer Research, 27(1), 16.	No			No			2020.0	Weight loss;FTIR;SEM;X-ray	In this study, polymer films were obtained mainly from waste Plastic bottles, which is a thermoplastic polymer predominantly composed of polyolefins like Polyethylene Terephthalate (PET) 		No	No	Water	Mangrove	India	No		
Virgibacillus halodenitrificans	1482	LDPE	Roy, P. K., Titus, S., Surekha, P., Tulsi, E., Deshmukh, C., & Rajagopal, C. (2008). Degradation of abiotically aged LDPE films containing pro-oxidant by bacterial consortium. Polymer degradation and stability, 93(10), 1917-1922.	No			No			2008.0	MS;Weight loss;TGA;Tensilometer;FTIR;SEM;DSC	General purpose film grade ‘LDPE 24FS040’ has been used to prepare films			No	Culture collection	Culture collection		No		
Actinomadura keratinilytica	547461	PLA	Sukkhum, S., Tokuyama, S., & Kitpreechavanich, V. (2009). Development of fermentation process for PLA-degrading enzyme production by a new thermophilic Actinomadura sp. T16-1. Biotechnology and Bioprocess Engineering, 14(3), 302.	No			No			2009.0	Clear zone	PLA pellet 	LACEA		Yes	Soil	Soil	Thailand	Yes		
Actinomadura keratinilytica	547461	PLA	Sukkhum, S., Tokuyama, S., Tamura, T., & Kitpreechavanich, V. (2009). A novel poly (L-lactide) degrading actinomycetes isolated from Thai forest soil, phylogenic relationship and the enzyme characterization. The Journal of general and applied microbiology, 55(6), 459-467.	No			No			2009.0	Clear zone;SEM	PLA pellet	LACEA		Yes	Soil	Soil	Thailand	No		
Actinomadura sp.	1989	PBS	Sriyapai, P., Chansiri, K., & Sriyapai, T. (2018). Isolation and Characterization of Polyester-Based Plastics-Degrading Bacteria from Compost Soils. Microbiology, 87(2), 290-300.	No			No			2018.0	Clear zone;SEM	BPS	Sigma Aldrich	Yes	Yes	Soil	Compost	Thailand	No		
Actinomadura sp.	1989	PBSA	Sriyapai, P., Chansiri, K., & Sriyapai, T. (2018). Isolation and Characterization of Polyester-Based Plastics-Degrading Bacteria from Compost Soils. Microbiology, 87(2), 290-300.	No			No			2018.0	Clear zone;SEM	PBSA (Mn 1.0 ×105)	Sigma Aldrich	Yes	Yes	Soil	Compost	Thailand	No		
Actinomadura sp.	1989	PCL	Sriyapai, P., Chansiri, K., & Sriyapai, T. (2018). Isolation and Characterization of Polyester-Based Plastics-Degrading Bacteria from Compost Soils. Microbiology, 87(2), 290-300.	No			No			2018.0	Clear zone;SEM	PCL (Mn 1.0 × 105)	Sigma Aldrich	Yes	Yes	Soil	Compost	Thailand	No		
Actinomadura sp.	1989	PLA	Sriyapai, P., Chansiri, K., & Sriyapai, T. (2018). Isolation and Characterization of Polyester-Based Plastics-Degrading Bacteria from Compost Soils. Microbiology, 87(2), 290-300.	No			No			2018.0	Clear zone;SEM	PLA (Mn 5.4 × 103 )	Sigma Aldrich	Yes	Yes	Soil	Compost	Thailand	No		
Actinomadura sp.	1989	PLA	Sriyapai, P., Chansiri, K., & Sriyapai, T. (2018). Isolation and Characterization of Polyester-Based Plastics-Degrading Bacteria from Compost Soils. Microbiology, 87(2), 290-300.	No			No			2018.0	Clear zone;SEM	PLA (Mn 5.4 × 103 )	Sigma Aldrich	Yes	Yes	Soil	Compost	Thailand	No		
Aneurinibacillus aneurinilyticus	1391	HDPE	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Aneurinibacillus aneurinilyticus	1391	LDPE	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Aneurinibacillus aneurinilyticus	1391	PP	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Aspergillus fumigatus	746128	PBAT-Blend	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	MB pellet form was pressed into films	Novamont		Yes	Plastic debris	Soil	South Korea	No		
Aspergillus fumigatus	746128	PHB	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	PHB was provided by ICI in powder form (200 mm) and its weight average molecular weight was 470,000 g/ mol.	ICI, UK		Yes	Plastic debris	Soil	South Korea	No		
Aspergillus fumigatus	746128	PETG	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	SG is a biodegradable aliphatic polyester, made of succinic acid, adipic acid, butanediol and ethylene glycol. It was donated by SKI in powder form (200 mm) with a melt index of 30 g/10 min at 190C.	SKI		Yes	Plastic debris	Soil	South Korea	No		
Aspergillus fumigatus	746128	PBSA	Sanchez, J. G., Tsuchii, A., & Tokiwa, Y. (2000). Degradation of polycaprolactone at 50° C by a thermotolerant Aspergillus sp. Biotechnology Letters, 22(10), 849-853.	No			No			2000.0	TOC;Clear zone;HPLC;SEM	Poly[tetramethylene succinate] (PTMS/A, Bionolle, mw 2.0x10^4)	Showa Denko		Yes	Culture collection	Culture collection		No		
Aspergillus fumigatus	746128	PCL	Sanchez, J. G., Tsuchii, A., & Tokiwa, Y. (2000). Degradation of polycaprolactone at 50° C by a thermotolerant Aspergillus sp. Biotechnology Letters, 22(10), 849-853.	No			No			2000.0	TOC;Clear zone;HPLC;SEM	PCL pellet (mw 6.73x10^4) 	Union Carbide		Yes	Culture collection	Culture collection		No		
Aspergillus fumigatus	746128	PHB	Sanchez, J. G., Tsuchii, A., & Tokiwa, Y. (2000). Degradation of polycaprolactone at 50° C by a thermotolerant Aspergillus sp. Biotechnology Letters, 22(10), 849-853.	No			No			2000.0	TOC;Clear zone;HPLC;SEM	PHB (mw 1.45x10^5) 	Mitsubishi Gas Chemical		Yes	Culture collection	Culture collection		No		
Aspergillus fumigatus	746128	PU	Zafar, U., Nzeram, P., Langarica-Fuentes, A., Houlden, A., Heyworth, A., Saiani, A., & Robson, G. D. (2014). Biodegradation of polyester polyurethane during commercial composting and analysis of associated fungal communities. Bioresource technology, 158, 374-377.	No			No			2014.0	Clear zone	Impranil	Bayer 	No	Yes	PU coupons	Compost	UK	No		
Aspergillus sp.	5065	PBSA	Nishide, H., Toyota, K., & Kimura, M. (1999). Effects of soil temperature and anaerobiosis on degradation of biodegradable plastics in soil and their degrading microorganisms. Soil Science and Plant Nutrition, 45(4), 963-972.	No			No			1999.0	Weight loss	PBSA (poly-butylene succinate and agipate copolymer, Showa Highpolymer Co.)	Showa Denko		Yes	Soil	Soil	Japan	No		
Aspergillus ustus	40382	PETG	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	SG is a biodegradable aliphatic polyester, made of succinic acid, adipic acid, butanediol and ethylene glycol. It was donated by SKI in powder form (200 mm) with a melt index of 30 g/10 min at 190C.	SKI		Yes	Plastic debris	Soil	South Korea	No		
Bacillus brevis	1393	PLA	Tomita, K., Kuroki, Y., & Nagai, K. (1999). Isolation of thermophiles degrading poly (L-lactic acid). Journal of bioscience and bioengineering, 87(6), 752-755.	No			No			1999.0	TOC;GPC	Poly (L-actic acid) PLA, poly(L-lactic acid), was in the form of a 50-um-thick film which had a number average molecular weight (Mn) of 45000, a Tg of 58°C and a melting temperature of 175 °C	Shimadzu		Yes	Soil	Soil	Japan	No		
Bacillus licheniformis	1402	PLA	Kim, M. N., Kim, W. G., Weon, H. Y., & Lee, S. H. (2008). Poly (L‐lactide)‐degrading activity of a newly isolated bacterium. Journal of applied polymer science, 109(1), 234-239.	No			No			2008.0	CO2;SEM;Clear zone	The polycondensation reaction was 1808C continued at 1 torr and for different reaction time. The polycondensation reaction for 8, 22, and 40 h yielded PLLA having weight average molecular weight (Mw) of 5,000 (P5,000); 11,000 (P11,000); and 34,000 (P34,000), respectively (Table II).		Yes	Yes	Compost	Others		No		
Bacillus licheniformis	1402	PLA	Sukkhum, S., Tokuyama, S., Tamura, T., & Kitpreechavanich, V. (2009). A novel poly (L-lactide) degrading actinomycetes isolated from Thai forest soil, phylogenic relationship and the enzyme characterization. The Journal of general and applied microbiology, 55(6), 459-467.	No			No			2009.0	Clear zone;SEM	PLA pellet	LACEA		Yes	Soil	Soil	Thailand	No		
Bacillus sp.	1409	PBS	Tansengco, M. L., & Tokiwa, Y. (1997). Thermophilic microbial degradation of polyethylene succinate. World Journal of Microbiology and Biotechnology, 14(1), 133-138.	No			No			1997.0	Clear zone;SEM;Weight loss	 poly(butylene succinate) (PBS, Mn 3.5 ´ 104 , Tm 114 °C, BIONOLLE #1020, Showa High Polymer Co., Ltd.)	Showa Denko		Yes	Soil	Soil	Japan	No		
Bacillus sp.	1409	PCL	Tansengco, M. L., & Tokiwa, Y. (1997). Thermophilic microbial degradation of polyethylene succinate. World Journal of Microbiology and Biotechnology, 14(1), 133-138.	No			No			1997.0	Clear zone;Weight loss	 (PCL TONE P-767, Mn 6.73 ´ 104 , Tm 62 °C, Union Carbide Corp.)	Union Carbide		Yes	Soil	Soil	Japan	No		
Bacillus sp.	1409	PES	Tansengco, M. L., & Tokiwa, Y. (1997). Thermophilic microbial degradation of polyethylene succinate. World Journal of Microbiology and Biotechnology, 14(1), 133-138.	No			No			1997.0	Clear zone;SEM;Weight loss	As the polyethylene succinate (PES) sample, LUNARE SE from Nippon Shokubai Co., Ltd., Tokyo, was used in this study. The sample contains 4% mineral to stimulate crystallization. It has a number average molecular weight (Mn) of 5.92 ´ 104 and a melting temperature (Tm) of 100 °C.	Nippon Shokubai		Yes	Soil	Soil	Japan	No		
Bacillus sp.	1409	PHB	Tansengco, M. L., & Tokiwa, Y. (1997). Thermophilic microbial degradation of polyethylene succinate. World Journal of Microbiology and Biotechnology, 14(1), 133-138.	No			No			1997.0	Clear zone;Weight loss	poly(beta-hydroxybutyrate) (PHB, Mn 1.45 ´ 105 , Tm 175 °C, Mitsubishi Gas Chemicals, Inc.)	Mitsubishi Gas Chemical		Yes	Soil	Soil	Japan	No		
Bacillus sp.	1409	PLA	Tansengco, M. L., & Tokiwa, Y. (1997). Thermophilic microbial degradation of polyethylene succinate. World Journal of Microbiology and Biotechnology, 14(1), 133-138.	No			No			1997.0	Clear zone;Weight loss	poly(L-lactide) (PLA, Mn 1.88 ´ 105 , Tm 175 °C, Shimadzu Co., Ltd.)	Shimadzu		Yes	Soil	Soil	Japan	No		
Bacillus stearothermophilus	1422	PLA	Tomita, K., Tsuji, H., Nakajima, T., Kikuchi, Y., Ikarashi, K., & Ikeda, N. (2003). Degradation of poly (D-lactic acid) by a thermophile. Polymer degradation and stability, 81(1), 167-171.	No			No			2003.0	DSC;TOC;GPC	PDLA, poly(d-lactic acid), was synthesized from dlactic acid using stannous octoate as a catalyst according to our method previously reported [15], and made into the form of a 30-mm-thick film from its methylene chloride solution. 		Yes	Yes	Soil	Soil	Japan	No		
Bacillus thermoamylovorans	35841	PCL	Hu, X., Thumarat, U., Zhang, X., Tang, M., & Kawai, F. (2010). Diversity of polyester-degrading bacteria in compost and molecular analysis of a thermoactive esterase from Thermobifida alba AHK119. Applied microbiology and biotechnology, 87(2), 771-779.	No			No			2010.0	Clear zone	Apexa® (formerly Biomax® 4026 and 4027) is a thermostable polyethylene terephthalate copolymer that is synthesized with terephthalic acid and ethylene glycol and an undisclosed component to be compostable; the product was kindly supplied by Dupont (Tokyo, Japan).	Apexa		Yes	Film	Compost		No		
Bacillus vallismortis	72361	HDPE	Skariyachan, S., Setlur, A. S., Naik, S. Y., Naik, A. A., Usharani, M., & Vasist, K. S. (2017). Enhanced biodegradation of low and high-density polyethylene by novel bacterial consortia formulated from plastic-contaminated cow dung under thermophilic conditions. Environmental Science and Pollution Research, 24(9), 8443-8457.	No			No			2017.0	Clear zone;FTIR;SEM;EDS;NMR	Fine HDPE powder	RB Industries		Yes	Cow dung	Plastic waste dumping site	India	No		
Bacillus vallismortis	72361	LDPE	Skariyachan, S., Setlur, A. S., Naik, S. Y., Naik, A. A., Usharani, M., & Vasist, K. S. (2017). Enhanced biodegradation of low and high-density polyethylene by novel bacterial consortia formulated from plastic-contaminated cow dung under thermophilic conditions. Environmental Science and Pollution Research, 24(9), 8443-8457.	No			No			2017.0	Clear zone;FTIR;SEM;EDS;NMR	Fine LDPE powder	RB Industries		Yes	Cow dung	Plastic waste dumping site	India	No		
Brevibacillus agri	51101	HDPE	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Brevibacillus agri	51101	LDPE	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Brevibacillus agri	51101	PP	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Brevibacillus borstelensis	45462	LDPE	Hadad, D., Geresh, S., & Sivan, A. (2005). Biodegradation of polyethylene by the thermophilic bacterium Brevibacillus borstelensis. Journal of applied microbiology, 98(5), 1093-1100.	No			No			2005.0	FTIR;Weight loss;	Branched low-density (0Æ92 g cm)3) polyethylene (LDPE) with an average molecular weight of 191 000 (Ipiten111) (Carmel Olefins, Haifa, Israel) produced in film form by Plastophil Hazorea (Kibbutz Hazorea, Israel) was used. The type designated LDPE did not contain any additives, whereas the type designated LDPE-L0235 contained a u.v. photosensitizer (an undisclosed compound designated L0235). 	Ipiten111	Yes	Yes	Soil	Plastic waste dumping site	Israel	No		
Brevibacillus brevis	1393	HDPE	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Brevibacillus brevis	1393	LDPE	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Brevibacillus brevis	1393	LDPE	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Brevibacillus brevis	1393	PP	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Brevibacillus sp.	1882945	HDPE	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Brevibacillus sp.	1882945	LDPE	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Brevibacillus sp.	1882945	PP	Skariyachan, S., Patil, A. A., Shankar, A., Manjunath, M., Bachappanavar, N., & Kiran, S. (2018). Enhanced polymer degradation of polyethylene and polypropylene by novel thermophilic consortia of Brevibacillus sps. and Aneurinibacillus sp. screened from waste management landfills and sewage treatment plants. Polymer degradation and stability, 149, 52-68.	No			No			2018.0	Weight loss;FTIR;SEM;AFM;NMR;EDS;MS;Clear zone	Polymer films and pellets	Local market	No	Yes			India	No		
Caenibacterium thermophilum	215580	PHB	Romen, F., Reinhardt, S., & Jendrossek, D. (2004). Thermotolerant poly (3-hydroxybutyrate)-degrading bacteria from hot compost and characterization of the PHB depolymerase of Schlegelella sp. KB1a. Archives of microbiology, 182(2-3), 157-164.	No			No			2004.0	Clear zone;Spectrophotometry	PHB and poly(3-hydroxyvalerate) (PHV) were isolated from gluconate-grown or valerate-grown cells of Ralstonia eutropha H16 (DSMZ428) or Chromobacterium violaceum (DSMZ30191), respectively, by sodium hypochlorite digestion and subsequent solvent extraction with acetone/diethylether as described elsewhere (Jendrossek et al. 1993b). 		Yes	Yes	Compost	Compost	Germany	No		
Caenibacterium thermophilum	215580	PHV	Romen, F., Reinhardt, S., & Jendrossek, D. (2004). Thermotolerant poly (3-hydroxybutyrate)-degrading bacteria from hot compost and characterization of the PHB depolymerase of Schlegelella sp. KB1a. Archives of microbiology, 182(2-3), 157-164.	No			No			2004.0	Clear zone;Spectrophotometry	PHB and poly(3-hydroxyvalerate) (PHV) were isolated from gluconate-grown or valerate-grown cells of Ralstonia eutropha H16 (DSMZ428) or Chromobacterium violaceum (DSMZ30191), respectively, by sodium hypochlorite digestion and subsequent solvent extraction with acetone/diethylether as described elsewhere (Jendrossek et al. 1993b). 		Yes	Yes	Compost	Compost	Germany	No		
Cunninghamella sp.	2044285	PBSA	Nishide, H., Toyota, K., & Kimura, M. (1999). Effects of soil temperature and anaerobiosis on degradation of biodegradable plastics in soil and their degrading microorganisms. Soil Science and Plant Nutrition, 45(4), 963-972.	No			No			1999.0	Weight loss	PBSA (poly-butylene succinate and agipate copolymer, Showa Highpolymer Co.)	Showa Denko		Yes	Soil	Soil	Japan	No		
Geobacillus thermocatenulatus	33938	Nylon	Tomita, K., Ikeda, N., & Ueno, A. (2003). Isolation and characterization of a thermophilic bacterium, Geobacillus thermocatenulatus, degrading nylon 12 and nylon 66. Biotechnology letters, 25(20), 1743-1746.	No			No			2003.0	TOC;HPLC;Weight loss;Viscosimeter	Nylon 12 was used as a 30 μm thick film, viscosity average molecular weight (Mv) of 41 000, a glasstransition temperature (T g) of 51 ◦C and a melting temperature (T m) of 179 ◦C	Daicel Chemical Industries		Yes	Soil	Soil	Japan	No		
Geobacillus thermocatenulatus	33938	Nylon	Tomita, K., Ikeda, N., & Ueno, A. (2003). Isolation and characterization of a thermophilic bacterium, Geobacillus thermocatenulatus, degrading nylon 12 and nylon 66. Biotechnology letters, 25(20), 1743-1746.	No			No			2003.0	TOC;HPLC	Nylon 66 was used as references were as 30 μm thick films which had Mv of 43 000, Tg of 50 ◦C and Tm of 227 ◦C and 265 ◦C	Asahi Chemical Industry		Yes	Soil	Soil	Japan	No		
Geobacillus thermocatenulatus	33938	PLA	Tomita, K., Nakajima, T., Kikuchi, Y., & Miwa, N. (2004). Degradation of poly (L-lactic acid) by a newly isolated thermophile. Polymer Degradation and Stability, 84(3), 433-438.	No			No			2004.0	TOC;GPC;DSC	The PLA used in this study was in the form of a 50-mm-thick film which had a number average molecular weight (Mn) of 47,000	Shimadzu		Yes	Soil	Soil	Japan	No		
Geobacillus thermoleovorans	33941	PLA	Castro-Aguirre, E., Auras, R., Selke, S., Rubino, M., & Marsh, T. (2018). Enhancing the biodegradation rate of poly (lactic acid) films and PLA bio-nanocomposites in simulated composting through bioaugmentation. Polymer degradation and stability, 154, 46-54.	No			No			2018.0	CO2;SEC	Ingeo™ 2003D resin, poly (lactic acid), was acquired from NatureWorks LLC. (Minnetonka, MN, USA).	NatureWorks LLC		Yes	Compost	Compost		No		
Laceyella sacchari	37482	PLA	Hanphakphoom, S., Maneewong, N., Sukkhum, S., Tokuyama, S., & Kitpreechavanich, V. (2014). Characterization of poly (L-lactide)-degrading enzyme produced by thermophilic filamentous bacteria Laceyella sacchari LP175. The Journal of general and applied microbiology, 60(1), 13-22.	No			No			2014.0	Clear zone				Yes	Soil	Soil	Thailand	No		
Laceyella sacchari	37482	PLA	Sukkhum, S., Tokuyama, S., Tamura, T., & Kitpreechavanich, V. (2009). A novel poly (L-lactide) degrading actinomycetes isolated from Thai forest soil, phylogenic relationship and the enzyme characterization. The Journal of general and applied microbiology, 55(6), 459-467.	No			No			2009.0	Clear zone;SEM	PLA pellet	LACEA		Yes	Soil	Soil	Thailand	No		
Laceyella sp.	1960874	PBS	Sriyapai, P., Chansiri, K., & Sriyapai, T. (2018). Isolation and Characterization of Polyester-Based Plastics-Degrading Bacteria from Compost Soils. Microbiology, 87(2), 290-300.	No			No			2018.0	Clear zone;SEM	BPS	Sigma Aldrich	Yes	Yes	Soil	Compost	Thailand	No		
Laceyella sp.	1960874	PBSA	Sriyapai, P., Chansiri, K., & Sriyapai, T. (2018). Isolation and Characterization of Polyester-Based Plastics-Degrading Bacteria from Compost Soils. Microbiology, 87(2), 290-300.	No			No			2018.0	Clear zone;SEM	PBSA (Mn 1.0 ×105)	Sigma Aldrich	Yes	Yes	Soil	Compost	Thailand	No		
Laceyella sp.	1960874	PCL	Sriyapai, P., Chansiri, K., & Sriyapai, T. (2018). Isolation and Characterization of Polyester-Based Plastics-Degrading Bacteria from Compost Soils. Microbiology, 87(2), 290-300.	No			No			2018.0	Clear zone;SEM	PCL (Mn 1.0 × 105)	Sigma Aldrich	Yes	Yes	Soil	Compost	Thailand	No		
Malbranchea cinnamomea	5041	PU	Zafar, U., Nzeram, P., Langarica-Fuentes, A., Houlden, A., Heyworth, A., Saiani, A., & Robson, G. D. (2014). Biodegradation of polyester polyurethane during commercial composting and analysis of associated fungal communities. Bioresource technology, 158, 374-377.	No			No			2014.0	Clear zone	Impranil	Bayer 	No	Yes	PU coupons	Compost	UK	No		
Micromonospora echinospora	1877	PLA	Sukkhum, S., Tokuyama, S., Tamura, T., & Kitpreechavanich, V. (2009). A novel poly (L-lactide) degrading actinomycetes isolated from Thai forest soil, phylogenic relationship and the enzyme characterization. The Journal of general and applied microbiology, 55(6), 459-467.	No			No			2009.0	Clear zone;SEM	PLA pellet	LACEA		Yes	Soil	Soil	Thailand	No		
Micromonospora viridifaciens	1881	PLA	Sukkhum, S., Tokuyama, S., Tamura, T., & Kitpreechavanich, V. (2009). A novel poly (L-lactide) degrading actinomycetes isolated from Thai forest soil, phylogenic relationship and the enzyme characterization. The Journal of general and applied microbiology, 55(6), 459-467.	No			No			2009.0	Clear zone;SEM	PLA pellet	LACEA		Yes	Soil	Soil	Thailand	No		
Nonomuraea fastidiosa	46173	PLA	Sukkhum, S., Tokuyama, S., Tamura, T., & Kitpreechavanich, V. (2009). A novel poly (L-lactide) degrading actinomycetes isolated from Thai forest soil, phylogenic relationship and the enzyme characterization. The Journal of general and applied microbiology, 55(6), 459-467.	No			No			2009.0	Clear zone;SEM	PLA pellet	LACEA		Yes	Soil	Soil	Thailand	No		
Nonomuraea terrinata	137662	PLA	Sukkhum, S., Tokuyama, S., Tamura, T., & Kitpreechavanich, V. (2009). A novel poly (L-lactide) degrading actinomycetes isolated from Thai forest soil, phylogenic relationship and the enzyme characterization. The Journal of general and applied microbiology, 55(6), 459-467.	No			No			2009.0	Clear zone;SEM	PLA pellet	LACEA		Yes	Soil	Soil	Thailand	No		
Paecilomyces sp.	40383	PCL	Nishide, H., Toyota, K., & Kimura, M. (1999). Effects of soil temperature and anaerobiosis on degradation of biodegradable plastics in soil and their degrading microorganisms. Soil Science and Plant Nutrition, 45(4), 963-972.	No			No			1999.0	Weight loss	PCL (poly-caprolactone, Daicel Chemical Industries)	Daicel Chemical Industries		Yes	Soil	Soil	Japan	No		
Paenibacillus sp.	58172	HDPE	Skariyachan, S., Setlur, A. S., Naik, S. Y., Naik, A. A., Usharani, M., & Vasist, K. S. (2017). Enhanced biodegradation of low and high-density polyethylene by novel bacterial consortia formulated from plastic-contaminated cow dung under thermophilic conditions. Environmental Science and Pollution Research, 24(9), 8443-8457.	No			No			2017.0	Clear zone;FTIR;SEM;EDS;NMR	Fine HDPE powder	RB Industries		Yes	Cow dung	Plastic waste dumping site	India	No		
Paenibacillus sp.	58172	LDPE	Skariyachan, S., Setlur, A. S., Naik, S. Y., Naik, A. A., Usharani, M., & Vasist, K. S. (2017). Enhanced biodegradation of low and high-density polyethylene by novel bacterial consortia formulated from plastic-contaminated cow dung under thermophilic conditions. Environmental Science and Pollution Research, 24(9), 8443-8457.	No			No			2017.0	Clear zone;FTIR;SEM;EDS;NMR	Fine LDPE powder	RB Industries		Yes	Cow dung	Plastic waste dumping site	India	No		
Penicillium simplicissimum	69488	PHB	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	PHB was provided by ICI in powder form (200 mm) and its weight average molecular weight was 470,000 g/ mol.	ICI, UK		Yes	Plastic debris	Soil	South Korea	No		
Pseudomonas protegens	380021	HDPE	Skariyachan, S., Setlur, A. S., Naik, S. Y., Naik, A. A., Usharani, M., & Vasist, K. S. (2017). Enhanced biodegradation of low and high-density polyethylene by novel bacterial consortia formulated from plastic-contaminated cow dung under thermophilic conditions. Environmental Science and Pollution Research, 24(9), 8443-8457.	No			No			2017.0	Clear zone;FTIR;SEM;EDS;NMR	Fine HDPE powder	RB Industries		Yes	Cow dung	Plastic waste dumping site	India	No		
Pseudomonas protegens	380021	LDPE	Skariyachan, S., Setlur, A. S., Naik, S. Y., Naik, A. A., Usharani, M., & Vasist, K. S. (2017). Enhanced biodegradation of low and high-density polyethylene by novel bacterial consortia formulated from plastic-contaminated cow dung under thermophilic conditions. Environmental Science and Pollution Research, 24(9), 8443-8457.	No			No			2017.0	Clear zone;FTIR;SEM;EDS;NMR	Fine LDPE powder	RB Industries		Yes	Cow dung	Plastic waste dumping site	India	No		
Pseudonocardia sp.	60912	PLA	Apinya, T., Sombatsompop, N., & Prapagdee, B. (2015). Selection of a Pseudonocardia sp. RM423 that accelerates the biodegradation of poly (lactic) acid in submerged cultures and in soil microcosms. International Biodeterioration & Biodegradation, 99, 23-30.	No			No			2015.0	Clear zone;CO2;SEM	6-mm-diameter mycelium disc of actinomycetes grown on GYE agar plates were placed on emulsified PLA agar containing 0.1% PLA (w/v) without surface active agent addition, modified from Jarerat et al. (2002).			Yes		Culture collection	Thailand	No		
Rasamsonia argillacea	69808	PCL	Sanchez, J. G., Tsuchii, A., & Tokiwa, Y. (2000). Degradation of polycaprolactone at 50° C by a thermotolerant Aspergillus sp. Biotechnology Letters, 22(10), 849-853. 	No			No			2000.0	TOC;Clear zone;HPLC;SEM	PCL pellet (mw 6.73x10^4) 	Union Carbide		Yes	Culture collection	Culture collection		No		
Saccharomonospora viridis	1852	PCL	Hu, X., Thumarat, U., Zhang, X., Tang, M., & Kawai, F. (2010). Diversity of polyester-degrading bacteria in compost and molecular analysis of a thermoactive esterase from Thermobifida alba AHK119. Applied microbiology and biotechnology, 87(2), 771-779.	No			No			2010.0	Clear zone	Apexa® (formerly Biomax® 4026 and 4027) is a thermostable polyethylene terephthalate copolymer that is synthesized with terephthalic acid and ethylene glycol and an undisclosed component to be compostable; the product was kindly supplied by Dupont (Tokyo, Japan).	Apexa		Yes	Film	Compost		No		
Schlegelella thermodepolymerans	215580	PHB	Romen, F., Reinhardt, S., & Jendrossek, D. (2004). Thermotolerant poly (3-hydroxybutyrate)-degrading bacteria from hot compost and characterization of the PHB depolymerase of Schlegelella sp. KB1a. Archives of microbiology, 182(2-3), 157-164.	No			No			2004.0	Clear zone;Spectrophotometry	PHB and poly(3-hydroxyvalerate) (PHV) were isolated from gluconate-grown or valerate-grown cells of Ralstonia eutropha H16 (DSMZ428) or Chromobacterium violaceum (DSMZ30191), respectively, by sodium hypochlorite digestion and subsequent solvent extraction with acetone/diethylether as described elsewhere (Jendrossek et al. 1993b). 		Yes	Yes	Compost	Compost	Germany	No		
Schlegelella thermodepolymerans	215580	PHV	Romen, F., Reinhardt, S., & Jendrossek, D. (2004). Thermotolerant poly (3-hydroxybutyrate)-degrading bacteria from hot compost and characterization of the PHB depolymerase of Schlegelella sp. KB1a. Archives of microbiology, 182(2-3), 157-164.	No			No			2004.0	Clear zone;Spectrophotometry	PHB and poly(3-hydroxyvalerate) (PHV) were isolated from gluconate-grown or valerate-grown cells of Ralstonia eutropha H16 (DSMZ428) or Chromobacterium violaceum (DSMZ30191), respectively, by sodium hypochlorite digestion and subsequent solvent extraction with acetone/diethylether as described elsewhere (Jendrossek et al. 1993b). 		Yes	Yes	Compost	Compost	Germany	No		
Stenotrophomonas sp.	69392	HDPE	Skariyachan, S., Setlur, A. S., Naik, S. Y., Naik, A. A., Usharani, M., & Vasist, K. S. (2017). Enhanced biodegradation of low and high-density polyethylene by novel bacterial consortia formulated from plastic-contaminated cow dung under thermophilic conditions. Environmental Science and Pollution Research, 24(9), 8443-8457.	No			No			2017.0	Clear zone;FTIR;SEM;EDS;NMR	Fine HDPE powder	RB Industries		Yes	Cow dung	Plastic waste dumping site	India	No		
Stenotrophomonas sp.	69392	LDPE	Skariyachan, S., Setlur, A. S., Naik, S. Y., Naik, A. A., Usharani, M., & Vasist, K. S. (2017). Enhanced biodegradation of low and high-density polyethylene by novel bacterial consortia formulated from plastic-contaminated cow dung under thermophilic conditions. Environmental Science and Pollution Research, 24(9), 8443-8457.	No			No			2017.0	Clear zone;FTIR;SEM;EDS;NMR	Fine LDPE powder	RB Industries		Yes	Cow dung	Plastic waste dumping site	India	No		
Streptomyces sp.	1931	PBS	Calabia, B. P., & Tokiwa, Y. (2004). Microbial degradation of poly (D-3-hydroxybutyrate) by a new thermophilic Streptomyces isolate. Biotechnology letters, 26(1), 15-19.	No			No			2004.0	Clear zone	poly(butylene succinate (PBS), Bionolle 1020, (Mn 4.8 × 104) from Showa Highpolymer	Showa Denko		Yes	Soil	Soil	Japan	No		
Streptomyces sp.	1931	PCL	Calabia, B. P., & Tokiwa, Y. (2004). Microbial degradation of poly (D-3-hydroxybutyrate) by a new thermophilic Streptomyces isolate. Biotechnology letters, 26(1), 15-19.	No			No			2004.0	Clear zone	polycaprolactone (PCL), Tone P-767, (Mn 6.73 × 104) from Union Carbide	Union Carbide		Yes	Soil	Soil	Japan	No		
Streptomyces sp.	1931	PEC	Calabia, B. P., & Tokiwa, Y. (2004). Microbial degradation of poly (D-3-hydroxybutyrate) by a new thermophilic Streptomyces isolate. Biotechnology letters, 26(1), 15-19.	No			No			2004.0	Clear zone	poly(ester carbonate) (PEC), with a carbonate content of 18 mol%, (Mn 2.4 × 105) from Mitsubishi Gas Chemical,	Mitsubishi Gas Chemical		Yes	Soil	Soil	Japan	No		
Streptomyces sp.	1931	PES	Calabia, B. P., & Tokiwa, Y. (2004). Microbial degradation of poly (D-3-hydroxybutyrate) by a new thermophilic Streptomyces isolate. Biotechnology letters, 26(1), 15-19.	No			No			2004.0	Clear zone	poly(ethylene succinate) (PES), Lunare, (Mn 5.92 × 104) from Nippon Shokubai	Nippon Shokubai		Yes	Soil	Soil	Japan	No		
Streptomyces sp.	1931	PHB	Calabia, B. P., & Tokiwa, Y. (2004). Microbial degradation of poly (D-3-hydroxybutyrate) by a new thermophilic Streptomyces isolate. Biotechnology letters, 26(1), 15-19.	No			No			2004.0	Clear zone;SEM;TOC	PHB powder, with a number-average molecular weight (Mn) of 2.1 × 105 (Mitsubishi Gas Chemical)	Mitsubishi Gas Chemical		Yes	Soil	Soil	Japan	No		
Streptomyces sp.	1931	PHB	Calabia, B. P., & Tokiwa, Y. (2004). Microbial degradation of poly (D-3-hydroxybutyrate) by a new thermophilic Streptomyces isolate. Biotechnology letters, 26(1), 15-19.	No			No			2004.0	Clear zone;TOC	PHB powder, with a number-average molecular weight (Mn) of 2.1 × 105 (Mitsubishi Gas Chemical)	Mitsubishi Gas Chemical		Yes		Culture collection		No		
Streptomyces sp.	1931	PEA	Calabia, B. P., & Tokiwa, Y. (2006). A novel PHB depolymerase from a thermophilic Streptomyces sp. Biotechnology letters, 28(6), 383-388.	No			No			2006.0	TOC	Poly(ethylene adipate) (PEA), (Mn 1.0 10^3)	Dainippon Ink and Chemicals		Yes				Yes		
Streptomyces sp.	1931	PEA	Calabia, B. P., & Tokiwa, Y. (2006). A novel PHB depolymerase from a thermophilic Streptomyces sp. Biotechnology letters, 28(6), 383-388.	No			No			2006.0	TOC	(PEA), (Mn 1.0 10^3)	Dainippon Ink and Chemicals		Yes				Yes		
Streptomyces sp.	1931	PES	Calabia, B. P., & Tokiwa, Y. (2006). A novel PHB depolymerase from a thermophilic Streptomyces sp. Biotechnology letters, 28(6), 383-388.	No			No			2006.0	TOC	Poly(ethylene succinate) (PES), Lunare (Mn 5.92 10^4)	Nippon Shokubai		Yes				Yes		
Streptomyces sp.	1931	PES	Calabia, B. P., & Tokiwa, Y. (2006). A novel PHB depolymerase from a thermophilic Streptomyces sp. Biotechnology letters, 28(6), 383-388.	No			No			2006.0	TOC	(PES), Lunare (Mn 5.92 10^4)	Nippon Shokubai		Yes				Yes		
Streptomyces sp.	1931	PHB	Calabia, B. P., & Tokiwa, Y. (2006). A novel PHB depolymerase from a thermophilic Streptomyces sp. Biotechnology letters, 28(6), 383-388.	No			No			2006.0	TOC	PHB powder, with a number-average molecular weight (Mn) of 2.1x10^5	Mitsubishi Gas Chemical		Yes				Yes		
Streptomyces sp.	1931	PHB	Calabia, B. P., & Tokiwa, Y. (2006). A novel PHB depolymerase from a thermophilic Streptomyces sp. Biotechnology letters, 28(6), 383-388.	No			No			2006.0	TOC	PHB powder, with a number-average molecular weight (Mn) of 2.1 10^5	Mitsubishi Gas Chemical		Yes				Yes		
Streptomyces sp.	1931	PHBV	Calabia, B. P., & Tokiwa, Y. (2006). A novel PHB depolymerase from a thermophilic Streptomyces sp. Biotechnology letters, 28(6), 383-388.	No			No			2006.0	TOC	Poly(3-hydroxybutyrate-co- 19%-3-hydroxyvalerate),(Mn4.3 104), poly(3-hydroxybuty- rate-co-6%-3-hydroxyvalerate), PHB/ HV, (Mn 4.2 104)	ICI, UK		Yes				Yes		
Streptomyces sp.	1931	PHBV	Calabia, B. P., & Tokiwa, Y. (2006). A novel PHB depolymerase from a thermophilic Streptomyces sp. Biotechnology letters, 28(6), 383-388.	No			No			2006.0	TOC	Poly(3-hydroxybutyrate-co- 19%-3-hydroxyvalerate),(Mn4.3 104), poly(3-hydroxybuty- rate-co-6%-3-hydroxyvalerate), PHB/ HV, (Mn 4.2 104)	ICI, UK		Yes				Yes		
Streptomyces sp.	1931	PPL	Calabia, B. P., & Tokiwa, Y. (2006). A novel PHB depolymerase from a thermophilic Streptomyces sp. Biotechnology letters, 28(6), 383-388.	No			No			2006.0	TOC	(PPL), (Mn 4.1 10^3) was prepared as described in our previous report (Nishida et al. 2000)		Yes	Yes				Yes		
Streptomyces sp.	1931	PPL	Calabia, B. P., & Tokiwa, Y. (2006). A novel PHB depolymerase from a thermophilic Streptomyces sp. Biotechnology letters, 28(6), 383-388.	No			No			2006.0	TOC	(PPL), (Mn 4.1 10^3) was prepared as described in our previous report (Nishida et al. 2000)			Yes				Yes		
Streptomyces sp.	1931	PBS	Phithakrotchanakoon, C., Rudeekit, Y., Tanapongpipat, S., Leejakpai, T., Aiba, S. I., Noda, I., & Champreda, V. (2009). Microbial degradation and physico-chemical alteration of polyhydroxyalkanoates by a thermophilic Streptomyces sp. Biologia, 64(2), 246-251.	No			No			2009.0	DSC;SEM;Clear zone;HPLC;GPC	Polybutylene-succinate (PBS) 	Sigma Aldrich	Yes	Yes		Landfill	Thailand	No		
Streptomyces sp.	1931	PCL	Phithakrotchanakoon, C., Rudeekit, Y., Tanapongpipat, S., Leejakpai, T., Aiba, S. I., Noda, I., & Champreda, V. (2009). Microbial degradation and physico-chemical alteration of polyhydroxyalkanoates by a thermophilic Streptomyces sp. Biologia, 64(2), 246-251.	No			No			2009.0	DSC;SEM;Clear zone;HPLC;GPC	Poly(ε-caprolactone) (PCL) 	Sigma Aldrich	Yes	Yes		Landfill	Thailand	No		
Streptomyces sp.	1931	PHB	Phithakrotchanakoon, C., Rudeekit, Y., Tanapongpipat, S., Leejakpai, T., Aiba, S. I., Noda, I., & Champreda, V. (2009). Microbial degradation and physico-chemical alteration of polyhydroxyalkanoates by a thermophilic Streptomyces sp. Biologia, 64(2), 246-251.	No			No			2009.0	DSC;SEM;Clear zone;HPLC;GPC	PHB powder (natural origin)	Sigma Aldrich	Yes	Yes		Landfill	Thailand	No		
Streptomyces sp.	1931	PHBH	Phithakrotchanakoon, C., Rudeekit, Y., Tanapongpipat, S., Leejakpai, T., Aiba, S. I., Noda, I., & Champreda, V. (2009). Microbial degradation and physico-chemical alteration of polyhydroxyalkanoates by a thermophilic Streptomyces sp. Biologia, 64(2), 246-251.	No			No			2009.0	DSC;SEM;Clear zone;HPLC;GPC	PHBHx (6.9 mol% HHx) 	Procter & Gamble		Yes		Landfill	Thailand	No		
Streptomyces sp.	1931	PHBV	Phithakrotchanakoon, C., Rudeekit, Y., Tanapongpipat, S., Leejakpai, T., Aiba, S. I., Noda, I., & Champreda, V. (2009). Microbial degradation and physico-chemical alteration of polyhydroxyalkanoates by a thermophilic Streptomyces sp. Biologia, 64(2), 246-251.	No			No			2009.0	DSC;SEM;Clear zone;HPLC;GPC	Poly[(R)-3-hydroxybutyrateco-3-hydroxyvalerate] (PHBV 8 mol% and 12 mol% HV)	Sigma Aldrich	Yes	Yes		Landfill	Thailand	No		
Streptomyces sp.	1931	PBS	Sriyapai, P., Chansiri, K., & Sriyapai, T. (2018). Isolation and Characterization of Polyester-Based Plastics-Degrading Bacteria from Compost Soils. Microbiology, 87(2), 290-300.	No			No			2018.0	Clear zone;SEM	BPS	Sigma Aldrich	Yes	Yes	Soil	Compost	Thailand	No		
Streptomyces sp.	1931	PCL	Sriyapai, P., Chansiri, K., & Sriyapai, T. (2018). Isolation and Characterization of Polyester-Based Plastics-Degrading Bacteria from Compost Soils. Microbiology, 87(2), 290-300.	No			No			2018.0	Clear zone;SEM	PCL (Mn 1.0 × 105)	Sigma Aldrich	Yes	Yes	Soil	Compost	Thailand	No		
Streptomyces sp.	1931	PLA	Sriyapai, P., Chansiri, K., & Sriyapai, T. (2018). Isolation and Characterization of Polyester-Based Plastics-Degrading Bacteria from Compost Soils. Microbiology, 87(2), 290-300.	No			No			2018.0	Clear zone;SEM	PLA (Mn 5.4 × 103 )	Sigma Aldrich	Yes	Yes	Soil	Compost	Thailand	No		
Streptomyces sp.	1931	PLA	Sriyapai, P., Chansiri, K., & Sriyapai, T. (2018). Isolation and Characterization of Polyester-Based Plastics-Degrading Bacteria from Compost Soils. Microbiology, 87(2), 290-300.	No			No			2018.0	Clear zone;SEM	PLA (Mn 5.4 × 103 )	Sigma Aldrich	Yes	Yes	Soil	Compost	Thailand	No		
Streptomyces thermogriseus	75292	PCL	Hu, X., Thumarat, U., Zhang, X., Tang, M., & Kawai, F. (2010). Diversity of polyester-degrading bacteria in compost and molecular analysis of a thermoactive esterase from Thermobifida alba AHK119. Applied microbiology and biotechnology, 87(2), 771-779.	No			No			2010.0	Clear zone	Apexa® (formerly Biomax® 4026 and 4027) is a thermostable polyethylene terephthalate copolymer that is synthesized with terephthalic acid and ethylene glycol and an undisclosed component to be compostable; the product was kindly supplied by Dupont (Tokyo, Japan).	Apexa		Yes	Film	Compost		No		
Streptomyces thermonitrificans	1934	PCL	Nakasaki, K., Matsuura, H., Tanaka, H., & Sakai, T. (2006). Synergy of two thermophiles enables decomposition of poly-ɛ-caprolactone under composting conditions. FEMS microbiology ecology, 58(3), 373-383.	No			No			2006.0	CO2;GPC;MS;HPLC;Clear zone	The biodegradable polymer used in this study consisted of fine particles of poly caprolactone (PCL) with the trade TM name PLACCEL H7 (Daicel Chemical Industries Ltd Tokio). The molecular weight of the PCL was c. 70 000 and the diameter of the PCL particles ranged from 63 to 250 mm.	Daicel Chemical Industries		Yes		Compost	Japan	No		
Streptomyces thermovulgaris	1934	PHB	Calabia, B. P., & Tokiwa, Y. (2004). Microbial degradation of poly (D-3-hydroxybutyrate) by a new thermophilic Streptomyces isolate. Biotechnology letters, 26(1), 15-19.	No			No			2004.0	Clear zone;TOC	PHB powder, with a number-average molecular weight (Mn) of 2.1 × 105 (Mitsubishi Gas Chemical)	Mitsubishi Gas Chemical		Yes		Culture collection		No		
Talaromyces verruculosus	198730	PBAT-Blend	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	No			No			2000.0	Weight loss;SEM;CO2	MB pellet form was pressed into films	Novamont		Yes	Plastic debris	Soil	South Korea	No		
Thermoactinomyces vulgaris	2026	PLA	Sukkhum, S., Tokuyama, S., Tamura, T., & Kitpreechavanich, V. (2009). A novel poly (L-lactide) degrading actinomycetes isolated from Thai forest soil, phylogenic relationship and the enzyme characterization. The Journal of general and applied microbiology, 55(6), 459-467.	No			No			2009.0	Clear zone;SEM	PLA pellet	LACEA		Yes	Soil	Soil	Thailand	No		
Thermoascus aurantiacus	5087	PHB	Sanchez, J. G., Tsuchii, A., & Tokiwa, Y. (2000). Degradation of polycaprolactone at 50° C by a thermotolerant Aspergillus sp. Biotechnology Letters, 22(10), 849-853.	No			No			2000.0	TOC;Clear zone;HPLC;SEM	PHB (mw 1.45x10^5) 	Mitsubishi Gas Chemical		Yes	Culture collection	Culture collection		No		
Thermoascus aurantiacus	5087	PBS	Sanchez, J. G., Tsuchii, A., & Tokiwa, Y. (2000). Degradation of polycaprolactone at 50° C by a thermotolerant Aspergillus sp. Biotechnology Letters, 22(10), 849-853. 	No			No			2000.0	TOC;Clear zone;HPLC;SEM	Poly[tetramethylene succinate] (mw 2.0x10^4) 	Showa Denko		Yes	Culture collection	Culture collection		No		
Thermoascus aurantiacus	5087	PCL	Sanchez, J. G., Tsuchii, A., & Tokiwa, Y. (2000). Degradation of polycaprolactone at 50° C by a thermotolerant Aspergillus sp. Biotechnology Letters, 22(10), 849-853. 	No			No			2000.0	TOC;Clear zone;HPLC;SEM	PCL pellet (mw 6.73x10^4) 	Union Carbide		Yes	Culture collection	Culture collection		No		
Thermobifida fusca	2021	PCL	Hu, X., Thumarat, U., Zhang, X., Tang, M., & Kawai, F. (2010). Diversity of polyester-degrading bacteria in compost and molecular analysis of a thermoactive esterase from Thermobifida alba AHK119. Applied microbiology and biotechnology, 87(2), 771-779.	No			No			2010.0	Clear zone	Apexa® (formerly Biomax® 4026 and 4027) is a thermostable polyethylene terephthalate copolymer that is synthesized with terephthalic acid and ethylene glycol and an undisclosed component to be compostable; the product was kindly supplied by Dupont (Tokyo, Japan).	Apexa		Yes	Film	Compost		No		
Thermobifida fusca	2021	PBAT-Blend	Kleeberg, I., Hetz, C., Kroppenstedt, R. M., Müller, R. J., & Deckwer, W. D. (1998). Biodegradation of aliphatic-aromatic copolyesters by Thermomonospora fusca and other thermophilic compost isolates. Appl. Environ. Microbiol., 64(5), 1731-1735.	No			No			1998.0	Weight loss	Polymer films 100 mm thick and 25 mm in diameter were prepared as described by Witt et al. (35)			Yes	Compost	Compost	Germany	No		
Thermomyces dupontii	28565	PCL	Sanchez, J. G., Tsuchii, A., & Tokiwa, Y. (2000). Degradation of polycaprolactone at 50° C by a thermotolerant Aspergillus sp. Biotechnology Letters, 22(10), 849-853. 	No			No			2000.0	TOC;Clear zone;HPLC;SEM	PCL pellet (mw 6.73x10^4) 	Union Carbide		Yes	Culture collection	Culture collection		No		
Thermomyces lanuginosus	5541	PU	Zafar, U., Nzeram, P., Langarica-Fuentes, A., Houlden, A., Heyworth, A., Saiani, A., & Robson, G. D. (2014). Biodegradation of polyester polyurethane during commercial composting and analysis of associated fungal communities. Bioresource technology, 158, 374-377.	No			No			2014.0	Clear zone	Impranil	Bayer 	No	Yes	PU coupons	Compost	UK	No		
Thermopolyspora flexuosa	103836	PLA	Husárová, L., Pekařová, S., Stloukal, P., Kucharzcyk, P., Verney, V., Commereuc, S., ... & Koutny, M. (2014). Identification of important abiotic and biotic factors in the biodegradation of poly (l-lactic acid). International journal of biological macromolecules, 71, 155-162.	No			No			2014.0	GPC;DSC;CO2	Polylactic acid samples PLA1 and PLA2 were synthesized through direct melt polycondensation of l-lactic acid [24,25]. PLA3 was purchased from NatureWorks® IngeoTM, grade 2002D (USA), and PLA4 from VUCHV a.s. (Svit, Slovak Republic).	NatureWorks LLC	Yes	Yes	Compost	Compost	Czech Republic	No		
Cobetia sp.	1873876	LDPE	Khandare, S. D., Chaudhary, D. R., & Jha, B. (2021). Marine bacterial biodegradation of low-density polyethylene (LDPE) plastic. Biodegradation, 1-17.	No						2021.0	Weight loss;CO2;SEM;FTIR	LDPE of 0.2 l thickness	Goodfellow Cambridge Ltd		No		Marine	India	No		
Halomonas sp.	1486246	LDPE	Khandare, S. D., Chaudhary, D. R., & Jha, B. (2021). Marine bacterial biodegradation of low-density polyethylene (LDPE) plastic. Biodegradation, 1-17.	No						2021.0	Weight loss;CO2;SEM;FTIR	LDPE of 0.2 l thickness	Goodfellow Cambridge Ltd		No		Marine	India	No		
Exiguobacterium sp.	44751	LDPE	Khandare, S. D., Chaudhary, D. R., & Jha, B. (2021). Marine bacterial biodegradation of low-density polyethylene (LDPE) plastic. Biodegradation, 1-17.	No						2021.0	Weight loss;CO2;SEM;FTIR	LDPE of 0.2 l thickness	Goodfellow Cambridge Ltd		No		Marine	India	No		
Alcanivorax sp.	1872427	LDPE	Khandare, S. D., Chaudhary, D. R., & Jha, B. (2021). Marine bacterial biodegradation of low-density polyethylene (LDPE) plastic. Biodegradation, 1-17.	No						2021.0	Weight loss;CO2;SEM;FTIR	LDPE of 0.2 l thickness	Goodfellow Cambridge Ltd		No		Marine	India	No		
Pseudomonas aeruginosa	287	LDPE	Rojas, A. M. H., Nakayo, J. J., Bulnes, J. L. L., & Anzualdo, V. I. T. (2020). Microbial biodegradation of polyethylene of low density, under controlled thermal conditions in air lift bio-reactor.	No						2020.0	Weight loss	LDPE bags		No	No				No		
Aspergillus brasiliensis	319629	LDPE	Rojas, A. M. H., Nakayo, J. J., Bulnes, J. L. L., & Anzualdo, V. I. T. (2020). Microbial biodegradation of polyethylene of low density, under controlled thermal conditions in air lift bio-reactor.	No						2020.0	Weight loss	LDPE bags		No	No				No		
Vibrio proteolyticus	671	PHA	Vogel, F. A. D., Schlundt, C., Stote, R. E., Ratto, J. A., & Amaral-Zettler, L. A. (2021). Comparative genomics of marine bacteria from a historically defined plastic biodegradation consortium with the capacity to biodegrade polyhydroxyalkanoates. Microorganisms, 9(1), 186.	No						2021.0	Clear zone	0.2 w/v% PHA film or 0.2 w/v% of grounded polymer powder	Imperial Chemical Industries		No	Culture collection	Culture collection		No		
Bacillus atrophaeus	1452	PHA	Vogel, F. A. D., Schlundt, C., Stote, R. E., Ratto, J. A., & Amaral-Zettler, L. A. (2021). Comparative genomics of marine bacteria from a historically defined plastic biodegradation consortium with the capacity to biodegrade polyhydroxyalkanoates. Microorganisms, 9(1), 186.	No						2021.0	Clear zone	0.2 w/v% PHA film or 0.2 w/v% of grounded polymer powder	Imperial Chemical Industries		No			USA	No		
Bacillus vietnamensis	218284	PHA	Vogel, F. A. D., Schlundt, C., Stote, R. E., Ratto, J. A., & Amaral-Zettler, L. A. (2021). Comparative genomics of marine bacteria from a historically defined plastic biodegradation consortium with the capacity to biodegrade polyhydroxyalkanoates. Microorganisms, 9(1), 186.	No						2021.0	Clear zone	0.2 w/v% PHA film or 0.2 w/v% of grounded polymer powder	Imperial Chemical Industries		No	Plastic debris	Marine	USA	No		
Pseudomonas lini	163011	PS	Kim, H. W., Jo, J. H., Kim, Y. B., Le, T. K., Cho, C. W., Yun, C. H., ... & Yeom, S. J. (2021). Biodegradation of Polystyrene by Bacteria from the Soil in Common Environments. Journal of Hazardous Materials, 126239.	No						2021.0	Weight loss;GC-MS;FT-IR;SEM	Low molecular weight PS powder			No	Soil	Soil	South Korea	No		
Bacillus sp.	1409	PHB	Cho, J. Y., Park, S. L., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., ... & Yang, Y. H. (2021). Polyhydroxyalkanoates (PHAs) degradation by the newly isolated marine Bacillus sp. JY14. Chemosphere, 131172.	No			No			2021.0	FTIR;SEM;GPC;GC	(P(88 mol% 3HB-co12 mol% 3HV)) pellets were obtained from Sigma-Aldrich (St. Louis, MO, USA). PHB pellets were obtained from Goodfellow Cambridge Ltd. (Huntingdon, UK). PBAT and PBS pellets were obtained from Gio Soltech Co., Ltd. (Wonju, Republic of Korea). Poly-3-hydroxybutyrate-co-4-hydroxybutyrate (P(60 mol% 3HB-co-40 mol% 4HB)) pellets were obtained from CJ (Suwon, Republic of Korea).	 Sigma-Aldrich and  Goodfellow Cambridge Ltd.	Yes	No	Soil	Soil	South Korea	No		
Bacillus sp.	1409	P34HB	Cho, J. Y., Park, S. L., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., ... & Yang, Y. H. (2021). Polyhydroxyalkanoates (PHAs) degradation by the newly isolated marine Bacillus sp. JY14. Chemosphere, 131172.	No			No			2021.0	FTIR;SEM;GPC;GC	(P(88 mol% 3HB-co12 mol% 3HV)) pellets were obtained from Sigma-Aldrich (St. Louis, MO, USA). PHB pellets were obtained from Goodfellow Cambridge Ltd. (Huntingdon, UK). PBAT and PBS pellets were obtained from Gio Soltech Co., Ltd. (Wonju, Republic of Korea). Poly-3-hydroxybutyrate-co-4-hydroxybutyrate (P(60 mol% 3HB-co-40 mol% 4HB)) pellets were obtained from CJ (Suwon, Republic of Korea).	 Sigma-Aldrich and  Goodfellow Cambridge Ltd.	Yes	No	Soil	Soil	South Korea	No		
Bacillus sp.	1409	PHBV	Cho, J. Y., Park, S. L., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., ... & Yang, Y. H. (2021). Polyhydroxyalkanoates (PHAs) degradation by the newly isolated marine Bacillus sp. JY14. Chemosphere, 131172.	No			No			2021.0	FTIR;SEM;GPC;GC	(P(88 mol% 3HB-co12 mol% 3HV)) pellets were obtained from Sigma-Aldrich (St. Louis, MO, USA). PHB pellets were obtained from Goodfellow Cambridge Ltd. (Huntingdon, UK). PBAT and PBS pellets were obtained from Gio Soltech Co., Ltd. (Wonju, Republic of Korea). Poly-3-hydroxybutyrate-co-4-hydroxybutyrate (P(60 mol% 3HB-co-40 mol% 4HB)) pellets were obtained from CJ (Suwon, Republic of Korea).	 Sigma-Aldrich and  Goodfellow Cambridge Ltd.	Yes	No	Soil	Soil	South Korea	No		
Comamonas testosteroni	285	PHB	Cho, J. Y., Park, S. L., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., ... & Yang, Y. H. (2021). Polyhydroxyalkanoates (PHAs) degradation by the newly isolated marine Bacillus sp. JY14. Chemosphere, 131172.	No			No			2021.0	FTIR;SEM;GPC;GC	(P(88 mol% 3HB-co12 mol% 3HV)) pellets were obtained from Sigma-Aldrich (St. Louis, MO, USA). PHB pellets were obtained from Goodfellow Cambridge Ltd. (Huntingdon, UK). PBAT and PBS pellets were obtained from Gio Soltech Co., Ltd. (Wonju, Republic of Korea). Poly-3-hydroxybutyrate-co-4-hydroxybutyrate (P(60 mol% 3HB-co-40 mol% 4HB)) pellets were obtained from CJ (Suwon, Republic of Korea).	 Sigma-Aldrich and  Goodfellow Cambridge Ltd.	Yes	No	Soil	Soil	South Korea	No		
Bacillus aryabhattai	412384	PHB	Cho, J. Y., Park, S. L., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., ... & Yang, Y. H. (2021). Polyhydroxyalkanoates (PHAs) degradation by the newly isolated marine Bacillus sp. JY14. Chemosphere, 131172.	No			No			2021.0	FTIR;SEM;GPC;GC	(P(88 mol% 3HB-co12 mol% 3HV)) pellets were obtained from Sigma-Aldrich (St. Louis, MO, USA). PHB pellets were obtained from Goodfellow Cambridge Ltd. (Huntingdon, UK). PBAT and PBS pellets were obtained from Gio Soltech Co., Ltd. (Wonju, Republic of Korea). Poly-3-hydroxybutyrate-co-4-hydroxybutyrate (P(60 mol% 3HB-co-40 mol% 4HB)) pellets were obtained from CJ (Suwon, Republic of Korea).	 Sigma-Aldrich and  Goodfellow Cambridge Ltd.	Yes	No	Soil	Soil	South Korea	No		
Priestia megaterium	1404	PHB	Cho, J. Y., Park, S. L., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., ... & Yang, Y. H. (2021). Polyhydroxyalkanoates (PHAs) degradation by the newly isolated marine Bacillus sp. JY14. Chemosphere, 131172.	No			No			2021.0	FTIR;SEM;GPC;GC	(P(88 mol% 3HB-co12 mol% 3HV)) pellets were obtained from Sigma-Aldrich (St. Louis, MO, USA). PHB pellets were obtained from Goodfellow Cambridge Ltd. (Huntingdon, UK). PBAT and PBS pellets were obtained from Gio Soltech Co., Ltd. (Wonju, Republic of Korea). Poly-3-hydroxybutyrate-co-4-hydroxybutyrate (P(60 mol% 3HB-co-40 mol% 4HB)) pellets were obtained from CJ (Suwon, Republic of Korea).	 Sigma-Aldrich and  Goodfellow Cambridge Ltd.	Yes	No	Soil	Soil	South Korea	No		
Bacillus zanthoxyli	2663026	PHB	Cho, J. Y., Park, S. L., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., ... & Yang, Y. H. (2021). Polyhydroxyalkanoates (PHAs) degradation by the newly isolated marine Bacillus sp. JY14. Chemosphere, 131172.	No			No			2021.0	FTIR;SEM;GPC;GC	(P(88 mol% 3HB-co12 mol% 3HV)) pellets were obtained from Sigma-Aldrich (St. Louis, MO, USA). PHB pellets were obtained from Goodfellow Cambridge Ltd. (Huntingdon, UK). PBAT and PBS pellets were obtained from Gio Soltech Co., Ltd. (Wonju, Republic of Korea). Poly-3-hydroxybutyrate-co-4-hydroxybutyrate (P(60 mol% 3HB-co-40 mol% 4HB)) pellets were obtained from CJ (Suwon, Republic of Korea).	 Sigma-Aldrich and  Goodfellow Cambridge Ltd.	Yes	No	Soil	Soil	South Korea	No		
Alkalihalobacillus algicola	225844	PHB	Cho, J. Y., Park, S. L., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., ... & Yang, Y. H. (2021). Polyhydroxyalkanoates (PHAs) degradation by the newly isolated marine Bacillus sp. JY14. Chemosphere, 131172.	No			No			2021.0	FTIR;SEM;GPC;GC	(P(88 mol% 3HB-co12 mol% 3HV)) pellets were obtained from Sigma-Aldrich (St. Louis, MO, USA). PHB pellets were obtained from Goodfellow Cambridge Ltd. (Huntingdon, UK). PBAT and PBS pellets were obtained from Gio Soltech Co., Ltd. (Wonju, Republic of Korea). Poly-3-hydroxybutyrate-co-4-hydroxybutyrate (P(60 mol% 3HB-co-40 mol% 4HB)) pellets were obtained from CJ (Suwon, Republic of Korea).	 Sigma-Aldrich and  Goodfellow Cambridge Ltd.	Yes	No	Soil	Soil	South Korea	No		
Alkalihalobacillus hwajinpoensis	208199	PHB	Cho, J. Y., Park, S. L., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., ... & Yang, Y. H. (2021). Polyhydroxyalkanoates (PHAs) degradation by the newly isolated marine Bacillus sp. JY14. Chemosphere, 131172.	No			No			2021.0	FTIR;SEM;GPC;GC	(P(88 mol% 3HB-co12 mol% 3HV)) pellets were obtained from Sigma-Aldrich (St. Louis, MO, USA). PHB pellets were obtained from Goodfellow Cambridge Ltd. (Huntingdon, UK). PBAT and PBS pellets were obtained from Gio Soltech Co., Ltd. (Wonju, Republic of Korea). Poly-3-hydroxybutyrate-co-4-hydroxybutyrate (P(60 mol% 3HB-co-40 mol% 4HB)) pellets were obtained from CJ (Suwon, Republic of Korea).	 Sigma-Aldrich and  Goodfellow Cambridge Ltd.	Yes	No	Soil	Soil	South Korea	No		
Penicillium simplicissimum	69488	PET	Moyses, D. N., Teixeira, D. A., Waldow, V. A., Freire, D. M., & Castro, A. M. (2021). Fungal and enzymatic bio-depolymerization of waste post-consumer poly (ethylene terephthalate)(PET) bottles using Penicillium species. 3 Biotech, 11(10), 1-12.	No			No			2021.0	Weight loss;HPLC	Post-consumer (PC) PET packages		No	No	Babassu palm	Plant associated	Brazil	No		
Massilia sp.	1882437	PS	Jiang, S., Su, T., Zhao, J., & Wang, Z. (2021). Isolation, identification, and characterization of polystyrene-degrading bacteria from the gut of Galleria mellonella (Lepidoptera: Pyralidae) larvae. Frontiers in Bioengineering and Biotechnology, 746.	No			No			2021.0	Weight loss;SEM;X-ray	PS foam board was obtained from Nannan Building Materials Co. (Zhejiang, China) and contained polystyrene purity over 98%. The number-average molecular weight (Mn) and weightaverage molecular weight (Mw) of the PS were 64400 and 144,400 Da, respectively, as measured by gel permeation chromatography. 	 Nannan Building Materials Co. (Zhejiang, China)	Yes	No	Gut	Animal associated	China	No		
Bacillus licheniformis	1402	PU	Yazhini VS, Prabha ML, Issac R. Characterization and Molecular Identification of Poly Urethane Degrading Bacteria. J Pure Appl Microbiol. 2021;15(3):1291-1300.	No			No			2021.0	SEM;Weight loss	PU sheets were purchased from Sigma-Aldrich.	Sigma Aldrich	Yes	No	Plastic debris	Soil	India	No		
Thermomyces lanuginosus	5541	LDPE	Chaudhary, A. K., Chaitanya, K., Dalmia, R., & Vijayakumar, R. P. (2021). Synergistic effect of UV, thermal, and chemical treatment on biological degradation of low-density polyethylene (LDPE) by Thermomyces lanuginosus. Environmental Monitoring and Assessment, 193(8), 1-11.	No			No			2021.0	SEM;Weight loss;FTIR;TGA			No	No	Culture collection	Culture collection	India	No		
Diaporthe italiana	2315965	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2021). Low-Density Polyethylene Film Biodegradation Potential by Fungal Species from Thailand. Journal of Fungi, 7(8), 594.	No			No			2021.0	CO2;Weight loss;Tensilometer;FTIR;SEM;MS	White and amorphous LDPE microplastic granules, 5 mm nominal size, (SigmaAldrich, Singapore) were used in this study.	Sigma Aldrich	Yes	No	Culture collection	Culture collection	Thailand	No		
Thyrostroma jaczewskii	2565323	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2021). Low-Density Polyethylene Film Biodegradation Potential by Fungal Species from Thailand. Journal of Fungi, 7(8), 594.	No			No			2021.0	CO2;Weight loss;Tensilometer;FTIR;SEM;MS	White and amorphous LDPE microplastic granules, 5 mm nominal size, (SigmaAldrich, Singapore) were used in this study.	Sigma Aldrich	Yes	No	Culture collection	Culture collection	Thailand	No		
Colletotrichum fructicola	690256	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2021). Low-Density Polyethylene Film Biodegradation Potential by Fungal Species from Thailand. Journal of Fungi, 7(8), 594.	No			No			2021.0	CO2;Weight loss;Tensilometer;FTIR;SEM;MS	White and amorphous LDPE microplastic granules, 5 mm nominal size, (SigmaAldrich, Singapore) were used in this study.	Sigma Aldrich	Yes	No	Culture collection	Culture collection	Thailand	No		
Stagonosporopsis citrulli	1623247	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2021). Low-Density Polyethylene Film Biodegradation Potential by Fungal Species from Thailand. Journal of Fungi, 7(8), 594.	No			No			2021.0	CO2;Weight loss;Tensilometer;FTIR;SEM;MS	White and amorphous LDPE microplastic granules, 5 mm nominal size, (SigmaAldrich, Singapore) were used in this study.	Sigma Aldrich	Yes	No	Culture collection	Culture collection	Thailand	No		
Aspergillus niger	5061	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2021). Low-Density Polyethylene Film Biodegradation Potential by Fungal Species from Thailand. Journal of Fungi, 7(8), 594.	No			No			2021.0	CO2;Weight loss;Tensilometer;FTIR;SEM;MS	White and amorphous LDPE microplastic granules, 5 mm nominal size, (SigmaAldrich, Singapore) were used in this study.	Sigma Aldrich	Yes	No	Culture collection	Culture collection	Thailand	No		
Bacillus licheniformis	1402	LDPE	Kučić Grgić, D., Miloloža, M., Lovrinčić, E., Kovačević, A., Cvetnić, M., Ocelić Bulatović, V., ... & Bolanča, T. (2021). Bioremediation of MP-polluted Waters Using Bacteria Bacillus licheniformis, Lysinibacillus massiliensis, and Mixed Culture of Bacillus sp. and Delftia acidovorans. Chemical and Biochemical Engineering Quarterly, 35(2), 205-224.	No			No			2021.0	FTIR;TOC	In this work, two types of MPs were used, LDPE (LDPE bags) and PS (disposable cutlery).		No	No	Sludge	Sewage/Sludge	Croatia	No		
Bacillus licheniformis	1402	PS	Kučić Grgić, D., Miloloža, M., Lovrinčić, E., Kovačević, A., Cvetnić, M., Ocelić Bulatović, V., ... & Bolanča, T. (2021). Bioremediation of MP-polluted Waters Using Bacteria Bacillus licheniformis, Lysinibacillus massiliensis, and Mixed Culture of Bacillus sp. and Delftia acidovorans. Chemical and Biochemical Engineering Quarterly, 35(2), 205-224.	No			No			2021.0	FTIR;TOC	In this work, two types of MPs were used, LDPE (LDPE bags) and PS (disposable cutlery).		No	No	Sludge	Sewage/Sludge	Croatia	No		
Ureibacillus massiliensis	292806	LDPE	Kučić Grgić, D., Miloloža, M., Lovrinčić, E., Kovačević, A., Cvetnić, M., Ocelić Bulatović, V., ... & Bolanča, T. (2021). Bioremediation of MP-polluted Waters Using Bacteria Bacillus licheniformis, Lysinibacillus massiliensis, and Mixed Culture of Bacillus sp. and Delftia acidovorans. Chemical and Biochemical Engineering Quarterly, 35(2), 205-224.	No			No			2021.0	FTIR;TOC	In this work, two types of MPs were used, LDPE (LDPE bags) and PS (disposable cutlery).		No	No	Sludge	Sewage/Sludge	Croatia	No		
Ureibacillus massiliensis	292806	PS	Kučić Grgić, D., Miloloža, M., Lovrinčić, E., Kovačević, A., Cvetnić, M., Ocelić Bulatović, V., ... & Bolanča, T. (2021). Bioremediation of MP-polluted Waters Using Bacteria Bacillus licheniformis, Lysinibacillus massiliensis, and Mixed Culture of Bacillus sp. and Delftia acidovorans. Chemical and Biochemical Engineering Quarterly, 35(2), 205-224.	No			No			2021.0	FTIR;TOC	In this work, two types of MPs were used, LDPE (LDPE bags) and PS (disposable cutlery).		No	No	Sludge	Sewage/Sludge	Croatia	No		
Serratia sp.	616	LDPE	Nadeem, H., Alia, K. B., Muneer, F., Rasul, I., Siddique, M. H., Azeem, F., & Zubair, M. (2021). Isolation and identification of low-density polyethylene degrading novel bacterial strains. Archives of Microbiology, 1-7.	No			No			2021.0	Weight loss;FTIR	Each reaction contains 45 mL of growth medium along with 5 mL of microbial culture and 50 mg (5 plastic pieces of 10 mg) of polyethylene pieces. 		No	No	Plastic debris	Plastic waste dumping site	Pakistan	No		
Stenotrophomonas sp.	69392	LDPE	Nadeem, H., Alia, K. B., Muneer, F., Rasul, I., Siddique, M. H., Azeem, F., & Zubair, M. (2021). Isolation and identification of low-density polyethylene degrading novel bacterial strains. Archives of Microbiology, 1-7.	No			No			2021.0	Weight loss;FTIR	Each reaction contains 45 mL of growth medium along with 5 mL of microbial culture and 50 mg (5 plastic pieces of 10 mg) of polyethylene pieces. 		No	No	Plastic debris	Plastic waste dumping site	Pakistan	No		
Pseudomonas sp.	306	LDPE	Nadeem, H., Alia, K. B., Muneer, F., Rasul, I., Siddique, M. H., Azeem, F., & Zubair, M. (2021). Isolation and identification of low-density polyethylene degrading novel bacterial strains. Archives of Microbiology, 1-7.	No			No			2021.0	Weight loss;FTIR	Each reaction contains 45 mL of growth medium along with 5 mL of microbial culture and 50 mg (5 plastic pieces of 10 mg) of polyethylene pieces. 		No	No	Plastic debris	Plastic waste dumping site	Pakistan	No		
Hericium erinaceus	91752	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	USA	No		
Dichostereum effuscatum	169328	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Aspergillus giganteus	5060	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Penicillium variabile	28576	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Aspergillus terreus	33178	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Paecilomyces variotii	264951	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Aspergillus tamarii	41984	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Papua New Guinea	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	China	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	China	No		
Aspergillus awamori	105351	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Aspergillus giganteus	5060	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Belgium	No		
Aspergillus tamarii	41984	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Congo [DRC]	No		
Aspergillus tamarii	41984	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Brazil	No		
Aspergillus tamarii	41984	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Rwanda	No		
Aspergillus sydowii	75750	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	USA	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Sudan	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Australia	No		
Trichothecium roseum	47278	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Polyporus tuberaster	38806	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Bulgaria	No		
Cyathus pallidus	380665	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	China	No		
Heterobasidion annosum	13563	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Pycnoporus cinnabarinus	5643	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Pycnoporus cinnabarinus	5643	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Trichaptum abietinum	40452	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Canada	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Guadeloupe	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Guadeloupe	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Guadeloupe	No		
Penicillium sp.	5081	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Aspergillus terreus	33178	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	South Africa	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Bahamas	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Bahamas	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Bahamas	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Bahamas	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Bahamas	No		
Aspergillus niger	5061	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Bahamas	No		
Aspergillus oryzae	5062	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Laetisaria arvalis	228946	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	USA	No		
Laetisaria arvalis	228946	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	USA	No		
Heterobasidion annosum	13563	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Bjerkandera adusta	5331	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Gloeophyllum sepiarium	40444	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Porodaedalea pini	108901	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Phlebia radiata	5308	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Sweden	No		
Pycnoporus cinnabarinus	5643	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Sweden	No		
Gloeophyllum sepiarium	40444	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Sweden	No		
Mycena sanguinolenta	230812	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	India	No		
Microporus sp.	2007320	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Madagascar	No		
Trichaptum biforme	50381	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Ceriporiopsis gilvescens	3063201	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Polyporus arcularius	5639	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus xanthodermus	83518	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Marasmiellus ramealis	71897	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Gloeophyllum odoratum	139427	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Panaeolus sphinctrinus	201082	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Xerula longipes	302555	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Mycena galericulata	71905	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Aspergillus awamori	105351	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Germany	No		
Lepista nuda	64659	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Piptoporus betulinus	40450	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Gymnopilus junonius	109634	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Podospora anserina	2587412	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Eutypa sp.	1955094	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Amauroderma calcigenum	1382549	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Coniochaeta sp.	1849801	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Xylaria adscendens	665660	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Xylaria telfairii	477509	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Xylaria comosoides	2108243	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Fomitopsis palustris	2870670	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Trametes sp.	1849818	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Fomitopsis palustris	2870670	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fomitopsis palustris	2870670	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Leiotrametes menziesii	2136021	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Hypomyces luteovirens	101000	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Grammothele fuligo	139413	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Gabon	No		
Lasionectria martinicensis	1707197	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Thelonectria veuillotiana	144050	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Neonectria sp.	1755434	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Neonectria sp.	1755434	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Stereum sp.	1849817	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Phellinus robustus	89466	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Mycosphaerella lateris	112483	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	South Africa	No		
Septoria eucalyptorum	361270	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	India	No		
Colletotrichum theobromicola 	912112	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Panama	No		
Lophiostoma arundinis	1762941	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Switzerland	No		
Cosmospora sp.	1849802	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Pestalotiopsis sp.	36460	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	New Caledonia	No		
Fusarium avenaceum	40199	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium culmorum	5516	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium culmorum	5516	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium graminearum	5518	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium graminearum	5518	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium graminearum	5518	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium graminearum	5518	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium culmorum	5516	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium culmorum	5516	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium proliferatum	948311	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Fusarium verticillioides	117187	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Fusarium verticillioides	117187	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Fusarium subglutinans	42677	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Fusarium verticillioides	117187	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Fusarium verticillioides	117187	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Fusarium verticillioides	117187	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Fusarium verticillioides	117187	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection		No		
Fomes meliae	383679	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Fusarium tricinctum	61284	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Phoma aliena	749643	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Clonostachys buxi	122427	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Stagonosporopsis dorenboschii	749892	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Peethambara spirostriata	267683	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Fomitiporia neotropica	1393926	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Fomitiporia sp.	1962509	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Haploporus alabamae	596163	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Amylosporus sp.	1905290	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Tropicoporus linteus	1659895	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Tropicoporus linteus	1659895	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Phellinus apiahynus	195178	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Nigrofomes melanoporus	1755789	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Phellinus amazonicus	1871133	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Phellinus amazonicus	1871133	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Phellinus amazonicus	1871133	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Nigrofomes melanoporus	1755789	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Perenniporia martia	1350019	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Perenniporia sp.	1881144	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Fomitiporia sp.	1962509	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Fomitiporia sp.	1962509	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Fomitiporia sp.	1962509	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Fuscoporia sp.	1968534	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Fomitopsis sp.	1905291	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Fulvifomes sp.	2267873	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Amauroderma sp.	34473	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Fulvifomes sp.	2267873	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Metacordyceps chlamydosporia	280754	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Martinique	No		
Pleospora leptosphaerulinoides	318714	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Spain	No		
Chrysonectria finisterensis 	2025093	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Verticillium sp.	5107	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Metarhizium robertsii	568076	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Gibberella sp.	29916	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Gibberella sp.	29916	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Gibberella sp.	29916	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium sp.	29916	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium sp.	29916	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Heterobasidion annosum	13563	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium sp.	29916	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Geonectria subalpina	2152714	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Pseudonectria foliicola	1634538	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium sp.	29916	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium sp.	29916	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Phoma sp.	1707701	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium sp.	29916	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Phoma sp.	1707701	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Phoma sp.	1707701	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Septoria sp.	1707704	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Calonectria pseudonaviculata	196064	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Phoma sp.	1707701	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium sp.	29916	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Phoma aliena	749643	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium sp.	29916	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Phoma aliena	749643	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Botrytis sp.	1849799	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Phoma sp.	1707701	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Phoma sp.	1707701	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Gloeophyllum sepiarium	40444	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Gloeophyllum sepiarium	40444	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Gloeophyllum sepiarium	40444	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Inonotus hispidus	40469	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Dichomitus squalens	114155	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Trichaptum abietinum	40452	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Sistotrema brinkmannii	139132	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agrocybe praecox	71668	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agrocybe sp.	1967158	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Gloeophyllum abietinum	180171	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Verticillium sp.	5107	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Trichaptum byssogenum	195175	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Guadeloupe	No		
Stemphylium lucomagnoense	2017760	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Tunisia	No		
Heterobasidion annosum	13563	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Coprinopsis lagopus	71712	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agrocybe dura	84604	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Trichothecium sp.	1945622	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Agaricus bisporus	5341	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Penicillium sp.	5081	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Hypoxylon sp.	1896109	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Heterobasidion sp.	2040811	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Lenzites warnieri	2885935	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Fusarium sp.	29916	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Phoma aliena	749643	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Botrytis cinerea	40559	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Greece	No		
Verticillium dahliae	27337	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Belgium	No		
Sclerotinia sclerotiorum	5180	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Netherlands	No		
Alternaria brassicae	29911	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	Netherlands	No		
Aspergillus sp.	5065	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	France	No		
Hypoxylon fendleri	558530	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Hydropisphaera saulensis	2705044	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Chaetopsina pnagiana	2692714	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Albosynnema elegans	110562	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Clonostachys pnagiana	2720620	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	French Guiana	No		
Agaricus subrufescens	87252	PU	Navarro, D., Chaduli, D., Taussac, S., Lesage-Meessen, L., Grisel, S., Haon, M., ... & Favel, A. (2021). Large-scale phenotyping of 1,000 fungal strains for the degradation of non-natural, industrial compounds.	No			No			2021.0	Clear zone	Impranil	 Covestro (Leverkusen, Germany)	No	No	Culture collection	Culture collection	China	No		
Microbacterium oleivorans	273677	PET	Yan, Z. F., Wang, L., Xia, W., Liu, Z. Z., Gu, L. T., & Wu, J. (2021). Synergistic biodegradation of poly (ethylene terephthalate) using Microbacterium oleivorans and Thermobifida fusca cutinase. Applied Microbiology and Biotechnology, 1-10.	No			No			2021.0	HPLC;SEM	The highly crystalline PET film was obtained from Colleague Hareware Co., Ltd. (Shanghai, China).	Colleague Hareware Co., Ltd. (Shanghai, China).	Yes	No			China	No		
Aspergillus clavatus	5057	PES	Ishii, N., Inoue, Y., Shimada, K. I., Tezuka, Y., Mitomo, H., & Kasuya, K. I. (2007). Fungal degradation of poly (ethylene succinate). Polymer degradation and stability, 92(1), 44-52.	P(3HB) depolymerase			No			2007.0	SEM;GPC;DSC;Tensilometer	Poly(ethylene succinate) (PESu) (Mw, 181x103; Mw/Mn, 2.2; Tm, 106 C)	Nippon Shokubai		No	Culture collection	Culture collection		No		
Aspergillus sp.	5065	PBS	Li, F., Hu, X., Guo, Z., Wang, Z., Wang, Y., Liu, D., ... & Chen, S. (2011). Purification and characterization of a novel poly (butylene succinate)-degrading enzyme from Aspergillus sp. XH0501-a. World Journal of Microbiology and Biotechnology, 27(11), 2591-2596.	PBS degrading enzyme			No			2011.0	Clear zone;Spectrophotometry;MS	PBS powder with a molecular weight of 9.02 9 10 was obtained from Showa Highpolymer Co. (Japan).	Showa Denko		No	Soil	Soil		No		
Alcaligenes faecalis	511	PCL	Oda, Y., Oida, N., Urakami, T., & Tonomura, K. (1997). Polycaprolactone depolymerase produced by the bacterium Alcaligenes faecalis. FEMS Microbiology letters, 152(2), 339-343.	PCL Depolymerase			No			1997.0	HPLC;Clear zone;Spectrophotometry	A commercial product of PCL Placcel H1P with an average molecular mass of 10000 Da was treated as previously described (10) and used as the suspension (1.6 mg ml^-1), unless otherwise stated.	Daicel Chemical Industries		No				No		
Brevundimonas sp.	1871086	PCL	Nawaz, A., Hasan, F., & Shah, A. A. (2015). Degradation of poly (ɛ-caprolactone)(PCL) by a newly isolated Brevundimonas sp. strain MRL-AN1 from soil. FEMS microbiology letters, 362(1), 1-7.	PCL depolymerase			No			2015.0	Clear zone;SEM;FTIR	Poly( -caprolactone) [PCL; 8×104]	Sigma Aldrich	Yes	No	Soil	Soil	Pakistan	No		
Pelobacter venetianus	44672	PEG	Frings, J., Schramm, E., & Schink, B. (1992). Enzymes involved in anaerobic polyethylene glycol degradation by Pelobacter venetianus and Bacteroides strain PG1. Appl. Environ. Microbiol., 58(7), 2164-2167.	PEG acetaldehyde lyase			No			1992.0	Spectrophotometry	All of the chemicals used were of analytical or reagent grade and were obtained from Merck (Darmstadt, Germany), Sigma (Munich, Germany), Fluka (Neu-Ulm, Germany), Serva (Heidelberg, Germany), and Boehringer (Mannheim, Germany).		Yes	No		Culture collection		Yes		
Acidovorax sp.	1872122	P3HP	Wang, Y., Inagawa, Y., Saito, T., Kasuya, K. I., Doi, Y., & Inoue, Y. (2002). Enzymatic hydrolysis of bacterial poly (3-hydroxybutyrate-co-3-hydroxypropionate) s by poly (3-hydroxyalkanoate) depolymerase from Acidovorax sp. TP4. Biomacromolecules, 3(4), 828-834.	PHA depolymerase			No			2002.0	SEM;FTIR;X-ray;Tensilometer;CO2	Oxo-biodegradable plastic bags			No	Culture collection	Culture collection		No		
Pseudomonas indica	137658	P(3HB-co-3MP)	Elbanna, K., Lütke-Eversloh, T., Jendrossek, D., Luftmann, H., & Steinbüchel, A. (2004). Studies on the biodegradability of polythioester copolymers and homopolymers by polyhydroxyalkanoate (PHA)-degrading bacteria and PHA depolymerases. Archives of microbiology, 182(2-3), 212-225.	PHA depolymerase			No			2004.0	GC;NMR;FTIR;MS;MALDI-TOF	Poly(3HB) and poly(3HB-co-3MP) were isolated from R. eutropha H16 (DSM428).		Yes	No				No		
Ralstonia pickettii	329	P3HP	Wang, Y., Inagawa, Y., Saito, T., Kasuya, K. I., Doi, Y., & Inoue, Y. (2002). Enzymatic hydrolysis of bacterial poly (3-hydroxybutyrate-co-3-hydroxypropionate) s by poly (3-hydroxyalkanoate) depolymerase from Acidovorax sp. TP4. Biomacromolecules, 3(4), 828-834.	PHA depolymerase			No			2002.0	HPLC;NMR;Weight loss	P(3HB-co-3HP) samples were biosynthesized by one-stage fermentation with Alcaligenes latus (ATCC 29713) at 30 C in a fermentor.		Yes	No				No		
Streptomyces roseolus	67358	PHO	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	PHA depolymerase			No			2012.0	Clear zone	Poly(3-hydroxyoctanoate-co-3-hydroxyhexanoate [11%]) [P(3HO) or mcl PHA]	Biopolis		No			Spain	No		
Streptomyces roseolus	67358	PCL	Gangoiti, J., Santos, M., Prieto, M. A., de la Mata, I., Serra, J. L., & Llama, M. J. (2012). Characterization of a novel subgroup of extracellular medium-chain-length polyhydroxyalkanoate depolymerases from actinobacteria. Appl. Environ. Microbiol., 78(20), 7229-7237.	PHA depolymerase			No			2012.0	Clear zone	PCL	Sigma Aldrich	Yes	No			Spain	No		
Schlegelella thermodepolymerans	215580	PHB	Romen, F., Reinhardt, S., & Jendrossek, D. (2004). Thermotolerant poly (3-hydroxybutyrate)-degrading bacteria from hot compost and characterization of the PHB depolymerase of Schlegelella sp. KB1a. Archives of microbiology, 182(2-3), 157-164.	PHA depolymerase			No			2004.0	Clear zone;Spectrophotometry	PHB and poly(3-hydroxyvalerate) (PHV) were isolated from gluconate-grown or valerate-grown cells of Ralstonia eutropha H16 (DSMZ428) or Chromobacterium violaceum (DSMZ30191), respectively, by sodium hypochlorite digestion and subsequent solvent extraction with acetone/diethylether as described elsewhere (Jendrossek et al. 1993b). 		Yes	Yes	Compost	Compost	Germany	No		
Talaromyces funiculosus	28572	PCL	Oda, Y., Asari, H., Urakami, T., & Tonomura, K. (1995). Microbial degradation of poly (3-hydroxybutyrate) and polycaprolactone by filamentous fungi. Journal of fermentation and bioengineering, 80(3), 265-269.	PHB and PCL depolymerase			No			1995.0	HPLC	PCL was a commercial product (Placcel HIPTM) was in powder form and had average molecular weight of 10,000	Daicel Chemical Industries		No	Soil	Soil		No		
Talaromyces funiculosus	28572	PHB	Oda, Y., Asari, H., Urakami, T., & Tonomura, K. (1995). Microbial degradation of poly (3-hydroxybutyrate) and polycaprolactone by filamentous fungi. Journal of fermentation and bioengineering, 80(3), 265-269.	PHB and PCL depolymerase			No			1995.0	HPLC	PHB of natural origin with molecular weight of 469,000	Sigma Aldrich	Yes	No	Soil	Soil		Yes		
Alcaligenes faecalis	511	PHB	Kita, K., Ishimaru, K., Teraoka, M., Yanase, H., & Kato, N. (1995). Properties of poly (3-hydroxybutyrate) depolymerase from a marine bacterium, Alcaligenes faecalis AE122. Appl. Environ. Microbiol., 61(5), 1727-1730.	PHB depolymerase			No			1995.0	GC	PHB	Sigma Aldrich	Yes	No	Seawater	Soil	Japan	No		
Arthrobacter sp.	1667	PHB	Asano, Y., & Watanabe, S. (2001). Isolation of poly (3-hydroxybutyrate)(PHB)-degrading microorganisms and characterization of PHB-depolymerase from Arthrobacter sp. strain W6. Bioscience, biotechnology, and biochemistry, 65(5), 1191-1194.	PHB depolymerase			No			2001.0	Clear zone;Spectrophotometry;GC	PHB	Sigma Aldrich	Yes	No	Soil	Soil	Japan	No		
Arthrobacter sp.	1667	PHBV	Asano, Y., & Watanabe, S. (2001). Isolation of poly (3-hydroxybutyrate)(PHB)-degrading microorganisms and characterization of PHB-depolymerase from Arthrobacter sp. strain W6. Bioscience, biotechnology, and biochemistry, 65(5), 1191-1194.	PHB depolymerase			No			2001.0	GC	PHBV	Sigma Aldrich	Yes	No	Soil	Soil	Japan	No		
Paecilomyces lilacinus	33203	PHBV	Sang, B. I., Lee, W. K., Hori, K., & Unno, H. (2006). Purification and characterization of fungal poly (3-hydroxybutyrate) depolymerase from Paecilomyces lilacinus F4-5 and enzymatic degradation of poly (3-hydroxybutyrate-co-3-hydroxyvalerate) film. World Journal of Microbiology and Biotechnology, 22(1), 51-57.	PHB depolymerase			No			2006.0	SEM;Spectrophotometry	P(3HB) and P(3HB-co-3HV) containing 12% 3-hydroxyvalerate in powder form	Sigma Aldrich		No	Soil	Soil		No		
Penicillium expansum	27334	PHB	Gowda, V. U., & Shivakumar, S. (2015). Poly (-β-hydroxybutyrate)(PHB) depolymerase PHAZ Pen from Penicillium expansum: purification, characterization and kinetic studies. 3 Biotech, 5(6), 901-909.	PHB depolymerase			No			2015.0	Spectrophotometry	PHB was obtained as a kind gift from Biomer Inc., Germany. The molecular weight of PHB was 470,000 g/mol	Biomer	Yes	No	Water	Sewage/Sludge	India	Yes		
Penicillium expansum	27334	PHBV	Gowda, V. U., & Shivakumar, S. (2015). Poly (-β-hydroxybutyrate)(PHB) depolymerase PHAZ Pen from Penicillium expansum: purification, characterization and kinetic studies. 3 Biotech, 5(6), 901-909.	PHB depolymerase			No			2015.0	Spectrophotometry			Yes	No	Water	Sewage/Sludge	India	Yes		
Penicillium pinophilum	128442	PHB	Panagiotidou, E., Konidaris, C., Baklavaridis, A., Zuburtikudis, I., Achilias, D., & Mitlianga, P. (2014). A simple route for purifying extracellular poly (3-hydroxybutyrate)-depolymerase from Penicillium pinophilum. Enzyme research, 2014.	PHB depolymerase			No			2014.0	Spectrophotometry;Weight loss;SEM	PHB	Sigma Aldrich	Yes	No		Culture collection	Germany	Yes		
Pseudomonas aeruginosa	287	PHB	Colak, A., & Güner, S. (2004). Polyhydroxyalkanoate degrading hydrolase-like activities by Pseudomonas sp. isolated from soil. International biodeterioration & biodegradation, 53(2), 103-109.	PHB depolymerase			No			2004.0	Weight loss;SEM;GPC	P(3HB) and P(3HB-co-3HV) were obtained from Aldrich (Steinheim, Germany)	Sigma Aldrich	Yes	No	Soil	Soil		No		
Pseudomonas alcaligenes	43263	PHB	Asano, Y., & Watanabe, S. (2001). Isolation of poly (3-hydroxybutyrate)(PHB)-degrading microorganisms and characterization of PHB-depolymerase from Arthrobacter sp. strain W6. Bioscience, biotechnology, and biochemistry, 65(5), 1191-1194.	PHB depolymerase			No			2001.0	Clear zone;Spectrophotometry;GC	PHB	Sigma Aldrich	Yes	No	Soil	Soil	Japan	No		
Pseudomonas alcaligenes	43263	PHB	Kim, D. Y., Nam, J. S., & Rhee, Y. H. (2002). Characterization of an Extracellular Medium-Chain-Length Poly (3-hydroxyalkanoate) Depolymerase from Pseudomonas a lcaligenes LB19. Biomacromolecules, 3(2), 291-296.	PHB depolymerase			No			2002.0	Spectrophotometry	 Aliphatic and aromatic MCL-PHAs were produced by culturing P. oleoVorans ATCC 29347 and P. putida KCTC 2407 		Yes	No	Soil	Soil	South Korea	Yes		
Pseudomonas fluorescens	294	PHB	Colak, A., & Güner, S. (2004). Polyhydroxyalkanoate degrading hydrolase-like activities by Pseudomonas sp. isolated from soil. International biodeterioration & biodegradation, 53(2), 103-109.	PHB depolymerase			No			2004.0	Weight loss;SEM;GPC	P(3HB) and P(3HB-co-3HV) were obtained from Aldrich (Steinheim, Germany)	Sigma Aldrich	Yes	No	Soil	Soil		No		
Pseudomonas putida	303	PHB	Colak, A., & Güner, S. (2004). Polyhydroxyalkanoate degrading hydrolase-like activities by Pseudomonas sp. isolated from soil. International biodeterioration & biodegradation, 53(2), 103-109.	PHB depolymerase			No			2004.0	Weight loss;SEM;GPC	P(3HB) and P(3HB-co-3HV) were obtained from Aldrich (Steinheim, Germany)	Sigma Aldrich	Yes	No	Soil	Soil		No		
Streptomyces bangladeshensis	295352	PHB	Hsu, K. J., Tseng, M., Don, T. M., & Yang, M. K. (2012). Biodegradation of Poly (β-hydroxybutyrate) by a novel isolate of Streptomyces bangladeshensis 77T-4. Botanical studies, 53(3).	PHB depolymerase			No			2012.0	Spectrophotometry;Weight loss;SEM	The extracellular PHB depolymerase was produced by growing 77T-4 cells in a basal medium containing PHB films at 45°C for 12 h with rotary shaking.		Yes	No	Soil	Soil	Taiwan	No		
Streptomyces lydicus	47763	PHB	Aly, M. M., Tork, S., Qari, H. A., & Al-Seeni, M. N. (2015). Poly-A3/4-hydroxy butyrate Depolymerase from Streptomyces lydicus MM10, Isolated from Wastewater Sample. International Journal of Agriculture and Biology, 17(5).	PHB depolymerase			No			2015.0	Clear zone;Spectrophotometry;Weight loss				No	Wastewater	Sewage/Sludge	Saudi Arabia	No		
Streptomyces sp.	1931	PHB	Kim, H. J., Nam, J. S., Bae, K. S., & Rhee, Y. H. (2003). Characterization of an extracellular medium-chain-length poly (3-hydroxyalkanoate) depolymerase from Streptomyces sp. KJ-72. Antonie van Leeuwenhoek, 83(2), 183-189.	PHB depolymerase			No			2003.0	Clear zone;Spectrophotometry;MS	PHB was isolated from Ralstonia eutropha as previ-clear zone around the colony, was selected for further ously described (Kim et al. 2000b). 		Yes	No	Soil	Soil	South Korea	No		
Talaromyces funiculosus	28572	PHB	Brucato, C. L., & Wong, S. S. (1991). Extracellular poly (3-hydroxybutyrate) depolymerase from Penicillium funiculosum: general characteristics and active site studies. Archives of Biochemistry and Biophysics, 290(2), 497-502.	PHB depolymerase			No			1991.0	Spectrophotometry	PHB	Imperial Chemical Industries		No	Culture collection	Culture collection		Yes		
Penicillium citrinum	5077	PHB	Shivakumar, S., Jagadish, S. J., Zatakia, H., & Dutta, J. (2011). Purification, characterization and kinetic studies of a novel poly (β) hydroxybutyrate (PHB) depolymerase PhaZ Pen from Penicillium citrinum S2. Applied biochemistry and biotechnology, 164(8), 1225-1236.	PHB depolymerase			No			2011.0	Spectrophotometry;Chromatography	PHB was obtained as a kind gift from Biomer Inc., Germany. The molecular weight of PHB was 470,000 g/mol. All experiments were performed using PHB powder.	Biomer	Yes	Yes	Water	Sewage/Sludge	India	Yes		
Talaromyces pinophilus	128442	PHB	Kim, M. N., Lee, A. R., Yoon, J. S., & Chin, I. J. (2000). Biodegradation of poly (3-hydroxybutyrate), Sky-Green® and Mater-Bi® by fungi isolated from soils. European Polymer Journal, 36(8), 1677-1685.	PHB depolymerase			No			2000.0	Weight loss;SEM;CO2	PHB was provided by ICI in powder form (200 mm) and its weight average molecular weight was 470,000 g/ mol.	ICI, UK		Yes	Plastic debris	Soil	South Korea	No		
Penicillium simplicissimum	69488	PHB	McLellan, D. W., & Halling, P. J. (1988). Acid-tolerant poly (3-hydroxybutyrate) hydrolases from moulds. FEMS microbiology letters, 52(3), 215-218.	PHB hydrolase			No			1988.0	GPC;HPLC;Clear zone;Titration of free carboxyl groups	Intact granules,and extracted and precipitated polymer	ICI, UK		No	Soil	Soil		No		
Penicillium sp.	5081	PHB	McLellan, D. W., & Halling, P. J. (1988). Acid-tolerant poly (3-hydroxybutyrate) hydrolases from moulds. FEMS microbiology letters, 52(3), 215-218.	PHB hydrolase			No			1988.0	GPC;HPLC;Clear zone;Titration of free carboxyl groups	Intact granules,and extracted and precipitated polymer	ICI, UK		No	Soil	Soil		No		
Xanthomonas sp.	29446	PHPV	Kim, H., Ju, H. S., & Kim, J. (2000). Characterization of an extracellular poly (3-hydroxy-5-phenylvalerate) depolymerase from Xanthomonas sp. JS02. Applied microbiology and biotechnology, 53(3), 323-327.	PHPV depolymerase			No			2000.0	Clear zone	PHPV was produced by growing Pseudomonas putida BM01 in a mineral medium containing 30 mM phenylvalerate and 20 mM butyrate as the carbon sources for 40 h at 30 °C (Yoon et al. 1994).		Yes	No	Water	Sewage/Sludge		No		
Amycolatopsis orientalis	31958	PLA	Jarerat, A., Tokiwa, Y., & Tanaka, H. (2006). Production of poly (L-lactide)-degrading enzyme by Amycolatopsis orientalis for biological recycling of poly (L-lactide). Applied microbiology and biotechnology, 72(4), 726-731.	PLA degrading enzyme			No			2006.0	TOC	PLA pellet, Lacty 1012 (number-average molecular weight, Mn: 3.4×105), was obtained from Shimadzu, Japan.	Shimadzu		No	Culture collection	Culture collection		No		
Amycolatopsis sp.	37632	PLA	Penkhrue, W., Kanpiengjai, A., Khanongnuch, C., Masaki, K., Pathom-Aree, W., Punyodom, W., & Lumyong, S. (2017). Effective enhancement of polylactic acid-degrading enzyme production by Amycolatopsis sp. strain SCM_MK2-4 using statistical and one-factor-at-a-time approaches. Preparative Biochemistry and Biotechnology, 47(7), 730-738.	PLA degrading enzyme			No			2017.0	Spectrophotometry;HPLC;Weight loss;SEM	Polylactic acid pellets (4043D grade) with a number-average molecular weight ðMnÞ of 1.30 × 105 g mol 1 and a weightaverage molecular weight ðMwÞ of 1.50 × 105 g mol	NatureWorks LLC		No		Soil	Thailand	No		
Amycolatopsis sp.	37632	PLA	Nakamura, K., Tomita, T., Abe, N., & Kamio, Y. (2001). Purification and characterization of an extracellular poly (L-lactic acid) depolymerase from a soil isolate, Amycolatopsis sp. strain K104-1. Appl. Environ. Microbiol., 67(1), 345-353.	PLA Depolymerase			No			2001.0	Clear zone;SEM	PLA with a number-average molecular weight (Mn) of 220,000	Shimadzu		No	Soil	Soil	Japan	No		
Bacillus smithii	1479	PLA	Sakai, K., Kawano, H., Iwami, A., Nakamura, M., & Moriguchi, M. (2001). Isolation of a thermophilic poly-L-lactide degrading bacterium from compost and its enzymatic characterization. Journal of bioscience and bioengineering, 92(3), 298-300.	PLA depolymerase			No			2001.0	GPC	1.0% PLLA (Nacalai tesque, Kyoto, M.W. lO,OOO)	Nacalai Tesque		Yes	Garbage	Plastic waste dumping site	Japan	No		
Acinetobacter gerneri	202952	PU	Howard, G. T., Norton, W. N., & Burks, T. (2012). Growth of Acinetobacter gerneri P7 on polyurethane and the purification and characterization of a polyurethanase enzyme. Biodegradation, 23(4), 561-573.	Polyurethanase			No			2012.0	SEM;Clear zone	Impranil DLN (Bayer Co., Pittsburg, PA)	Bayer 	No	No	Soil	Soil		No		
Pseudomonas chlororaphis	587753	PU	Howard, G. T., Ruiz, C., & Hilliard, N. P. (1999). Growth of Pseudomonas chlororaphis on apolyester–polyurethane and the purification andcharacterization of a polyurethanase–esterase enzyme. International biodeterioration & biodegradation, 43(1-2), 7-12.	Polyurethanase esterase			No			1999.0	Clear zone	Impranil DLN		No	No	Culture collection	Culture collection		No		
Stenotrophomonas geniculata	86188	PLA	Bubpachat, T., Sombatsompop, N., & Prapagdee, B. (2018). Isolation and role of polylactic acid-degrading bacteria on degrading enzymes productions and PLA biodegradability at mesophilic conditions. Polymer degradation and stability, 152, 75-85.	Protease			No			2018.0	Weight loss;SEM;GPC	PLA granules 2003D (Ingeo™) were supplied by Natureworks LLC, USA. PLA 2003D has a specific gravity of 1.24, aweight-average molecular weight (Mw) of 157503 Da, a number-average molecular weight (Mn) of 96113 Da and a polydispersity (PI) of 1.64.	NatureWorks LLC		No	Soil	Soil	Thailand	No		
Stenotrophomonas pavanii	487698	PLA	Bubpachat, T., Sombatsompop, N., & Prapagdee, B. (2018). Isolation and role of polylactic acid-degrading bacteria on degrading enzymes productions and PLA biodegradability at mesophilic conditions. Polymer degradation and stability, 152, 75-85.	Protease			No			2018.0	Weight loss;SEM;GPC	PLA granules 2003D (Ingeo™) were supplied by Natureworks LLC, USA. PLA 2003D has a specific gravity of 1.24, aweight-average molecular weight (Mw) of 157503 Da, a number-average molecular weight (Mn) of 96113 Da and a polydispersity (PI) of 1.64.	NatureWorks LLC		No	Soil	Soil	Thailand	No		
Paenibacillus amylolyticus	1451	PBS	Teeraphatpornchai, T., Nakajima-Kambe, T., Shigeno-Akutsu, Y., Nakayama, M., Nomura, N., Nakahara, T., & Uchiyama, H. (2003). Isolation and characterization of a bacterium that degrades various polyester-based biodegradable plastics. Biotechnology letters, 25(1), 23-28.	Protease and esterase 			No			2003.0	Clear zone	Cylindrical shaped poly(butylene succinate) (Bionolle no. 1020; MW = 1.4×10^5)	Showa Denko		No	Soil	Soil	Japan	No		
Paenibacillus amylolyticus	1451	PBSA	Teeraphatpornchai, T., Nakajima-Kambe, T., Shigeno-Akutsu, Y., Nakayama, M., Nomura, N., Nakahara, T., & Uchiyama, H. (2003). Isolation and characterization of a bacterium that degrades various polyester-based biodegradable plastics. Biotechnology letters, 25(1), 23-28.	Protease and esterase 			No			2003.0	Clear zone	Poly(butylenes succinateco- adipate) (Bionolle no. 3020; MW = 1.4×10^5) 	Showa Denko		No	Soil	Soil	Japan	No		
Paenibacillus amylolyticus	1451	PCL	Teeraphatpornchai, T., Nakajima-Kambe, T., Shigeno-Akutsu, Y., Nakayama, M., Nomura, N., Nakahara, T., & Uchiyama, H. (2003). Isolation and characterization of a bacterium that degrades various polyester-based biodegradable plastics. Biotechnology letters, 25(1), 23-28.	Protease and esterase 			No			2003.0	Clear zone	Poly(ε-caprolactone) (PCL) 	Wako Pure Chemical		No	Soil	Soil	Japan	No		
Paenibacillus amylolyticus	1451	PES	Teeraphatpornchai, T., Nakajima-Kambe, T., Shigeno-Akutsu, Y., Nakayama, M., Nomura, N., Nakahara, T., & Uchiyama, H. (2003). Isolation and characterization of a bacterium that degrades various polyester-based biodegradable plastics. Biotechnology letters, 25(1), 23-28.	Protease and esterase 			No			2003.0	Clear zone	Poly(ethylene succinate) (PES) 	Nippon Shokubai		No	Soil	Soil	Japan	No		
Paenibacillus amylolyticus	1451	PLA	Teeraphatpornchai, T., Nakajima-Kambe, T., Shigeno-Akutsu, Y., Nakayama, M., Nomura, N., Nakahara, T., & Uchiyama, H. (2003). Isolation and characterization of a bacterium that degrades various polyester-based biodegradable plastics. Biotechnology letters, 25(1), 23-28.	Protease and esterase 			No			2003.0	Clear zone;Weight loss;SEM	Poly (lactic acid) (PLA) enantiomer materials used in this study, namely, PLA05, PLA10, PLA15, PLA20 having average molecular weights of 0.5×10^4, 1×10^4, 1.5×10^4, and 2×10^4	Wako Pure Chemical		No	Soil	Soil	Japan	No		
Delftia acidovorans	80866	PLA	Akutsu, Y., Nakajima-Kambe, T., Nomura, N., & Nakahara, T. (1998). Purification and properties of a polyester polyurethane-degrading enzyme from Comamonas acidovorans TB-35. Appl. Environ. Microbiol., 64(1), 62-67.	PUR esterase			No			1998.0	SEM;GC;Weight loss	Poly(lactic acid)s 	Wako Pure Chemical		No	Colllection	Culture collection		Yes		
Bacillus niacini	86668	PVA	Bian, H., Cao, M., Wen, H., Tan, Z., Jia, S., & Cui, J. (2019). Biodegradation of polyvinyl alcohol using cross-linked enzyme aggregates of degrading enzymes from Bacillus niacini. International journal of biological macromolecules, 124, 10-16.	PVAase			No			2019.0	Clear zone				No	Sludge	Sewage/Sludge	China	No		
Pestalotiopsis microspora	85828	PU	Russell, J. R., Huang, J., Anand, P., Kucera, K., Sandoval, A. G., Dantzler, K. W., ... & Marks, D. H. (2011). Biodegradation of polyester polyurethane by endophytic fungi. Appl. Environ. Microbiol., 77(17), 6076-6084.	Serine hydrolase			No			2011.0	IR;Clear zone	Impranil DLF	Bayer 	No	No	Woody plants	Soil	Ecuador	No		
Pseudomonas chlororaphis	587753	PU	Ruiz, C., Main, T., Hilliard, N. P., & Howard, G. T. (1999). Purification and characterization of twopolyurethanase enzymes from Pseudomonas chlororaphis. International biodeterioration & biodegradation, 43(1-2), 43-47.	Serine hydrolase			No			1999.0	Clear zone	Impranil DLN	Bayer 	No	No	Culture collection	Culture collection		No		
Pseudomonas oleovorans	301	PCL	Inglis, G. D., Yanke, L. J., & Selinger, L. B. (2011). Cutinolytic esterase activity of bacteria isolated from mixed-plant compost and characterization of a cutinase gene from Pseudomonas pseudoalcaligenes. Canadian journal of microbiology, 57(11), 902-913.	Cutinase	00118	00118 | Cutinase | Pseudomonas oleovorans | PCL PET	Yes	ADK73612.1	MINRTLPNSLLSMLAAGALLLSTSVMATNPPVDEPTDPGDSYARGPDPTVAFLEASSGPYSTRTSRVSGLVSGFGGGTIHYPTGTTGTMAAIVVIPGFVSAESSIDWWGPKLASHGFVVMTIDTNTGFDQPPSRARQINNALDYLVDQNSRRTSPVNGMIDTDRLGVIGWSMGGGGTLRVASQGRIKAAIPLAPWDTTNARSVQAPTLIFACQADIIAPVGVHASPFYNQLPNDIEKAYVEISGGSHYCANGGGLNNDVLSRLGVSWMKRFLDNDTRYSQFLCGPNHTSDRRVSEYRGNCPY	2011.0	Clear zone				No	Compost	Compost	Canada	No		
Pseudomonas oleovorans	301	PET	Haernvall, K., Zitzenbacher, S., Wallig, K., Yamamoto, M., Schick, M. B., Ribitsch, D., & Guebitz, G. M. (2017). Hydrolysis of ionic phthalic acid based polyesters by wastewater microorganisms and their enzymes. Environmental science & technology, 51(8), 4596-4605.	Cutinase	00118	00118 | Cutinase | Pseudomonas oleovorans | PCL PET	Yes	ADK73612.1	MINRTLPNSLLSMLAAGALLLSTSVMATNPPVDEPTDPGDSYARGPDPTVAFLEASSGPYSTRTSRVSGLVSGFGGGTIHYPTGTTGTMAAIVVIPGFVSAESSIDWWGPKLASHGFVVMTIDTNTGFDQPPSRARQINNALDYLVDQNSRRTSPVNGMIDTDRLGVIGWSMGGGGTLRVASQGRIKAAIPLAPWDTTNARSVQAPTLIFACQADIIAPVGVHASPFYNQLPNDIEKAYVEISGGSHYCANGGGLNNDVLSRLGVSWMKRFLDNDTRYSQFLCGPNHTSDRRVSEYRGNCPY	2017.0	HPLC				No	Culture collection	Culture collection		No		
Halopseudomonas pelagia	553151	PET	Haernvall, K., Zitzenbacher, S., Wallig, K., Yamamoto, M., Schick, M. B., Ribitsch, D., & Guebitz, G. M. (2017). Hydrolysis of ionic phthalic acid based polyesters by wastewater microorganisms and their enzymes. Environmental science & technology, 51(8), 4596-4605.	Lipase	00119	00119 | Lipase | Halopseudomonas pelagia | PET	Yes	ANP21910.1	MKNTLIPKSLSTLFAASALMLSATVMAANPAPPQDPVEPGGFARGPDPSVSFLEADRGPYSVNTSRVSGLVSGFGGGTIHYPSGTTGTMAAIVVIPGYVSAESSIEWWGPKLASHGFVVMTIDTNTSFDQPPSRARQINSALDYLIDQNTATRSAVRGMIDTNRLGVVGWSMGGGGTLRVATEGRISAAIPLAPWDTSSLQFRNVQAPTLIFACESDIIAPVGSHASPFYNRLPGDLNKAFVEIDGGNHYCANGAASFGRYDSVLSRMGVSWMKLHLDQDERYKQFLCGPNHTADNRISEYRGNCPY	2017.0	HPLC				No	Culture collection	Culture collection		No		
Pseudomonas mendocina	300	PET	Ronkvist, Å. M., Xie, W., Lu, W., & Gross, R. A. (2009). Cutinase-catalyzed hydrolysis of poly (ethylene terephthalate). Macromolecules, 42(14), 5128-5138.	Cutinase	00120	00120 | Cutinase | Pseudomonas mendocina | PET	Yes	2FX5_A	APLPDTPGAPFPAVANFDRSGPYTVSSQSEGPSCRIYRPRDLGQGGVRHPVILWGNGTGAGPSTYAGLLSHWASHGFVVAAAETSNAGTGREMLACLDYLVRENDTPYGTYSGKLNTGRVGTSGHSQGGGGSIMAGQDTRVRTTAPIQPYTLGLGHDSASQRRQQGPMFLMSGGGDTIAFPYLNAQPVYRRANVPVFWGERRYVSHFEPVGSGGAYRGPSTAWFRFQLMDDQDARATFYGAQCSLCTSLLWSVERRGL	2009.0	Weight loss;SEM;DSC;HPLC	Lowcrystallinity PET films (lcPET, product number 029-198-54) and biaxially oriented PET films (boPTE, product number 543-716-95), both with a thickness of 250 μm	Goodfellow Co	Yes	No				Yes		
Humicola insolens	34413	PET	Ronkvist, Å. M., Xie, W., Lu, W., & Gross, R. A. (2009). Cutinase-catalyzed hydrolysis of poly (ethylene terephthalate). Macromolecules, 42(14), 5128-5138.	Cutinase	00121	00121 | Cutinase | Humicola insolens | PET	Yes	A0A075B5G4	QLGAIENGLESGSANACPDAILIFARGSTEPGNMGITVGPALANGLESHIRNIWIQGVGGPYDAALATNFLPRGTSQANIDEGKRLFALANQKCPNTPVVAGGYSQGAALIAAAVSELSGAVKEQVKGVALFGYTQNLQNRGGIPNYPRERTKVFCNVGDAVCTGTLIITPAHLSYTIEARGEAARFLRDRIRA	2009.0	Weight loss;SEM;DSC;HPLC	Lowcrystallinity PET films (lcPET, product number 029-198-54) and biaxially oriented PET films (boPTE, product number 543-716-95), both with a thickness of 250 μm	Goodfellow Co	Yes	No				Yes		
Fusarium solani	169388	PET	Ronkvist, Å. M., Xie, W., Lu, W., & Gross, R. A. (2009). Cutinase-catalyzed hydrolysis of poly (ethylene terephthalate). Macromolecules, 42(14), 5128-5138.	Cutinase	00122	00122 | Cutinase | Fusarium solani | PET	Yes	AAA33335.1	MKFFALTTLLAATASALPTSNPAQELEARQLGRTTRDDLINGNSASCADVIFIYARGSTETGNLGTLGPSIASNLESAFGKDGVWIQGVGGAYAATLGDNALPRGTSSAAIREMLGLFQQANTKCPDATLIAGGYSQGAALAAASIEDLDSAIRDKIAGTVLFGYTKNLQNRGRIPNYPADRTKVFCNTGDLVCTGSLIVAAPHLAYGPDARGPAPEFLIEKVRAVRGSA	2009.0	Weight loss;SEM;DSC;HPLC	Lowcrystallinity PET films (lcPET, product number 029-198-54) and biaxially oriented PET films (boPTE, product number 543-716-95), both with a thickness of 250 μm	Goodfellow Co	Yes	No				Yes		
Moesziomyces antarcticus	84753	PET	Carniel, A., Valoni, É., Junior, J. N., da Conceição Gomes, A., & de Castro, A. M. (2017). Lipase from Candida antarctica (CALB) and cutinase from Humicola insolens act synergistically for PET hydrolysis to terephthalic acid. Process Biochemistry, 59, 84-90.	Lipase	00123	00123 | Lipase | Moesziomyces antarcticus | PET	Yes	P41365	MKLLSLTGVAGVLATCVAATPLVKRLPSGSDPAFSQPKSVLDAGLTCQGASPSSVSKPILLVPGTGTTGPQSFDSNWIPLSTQLGYTPCWISPPPFMLNDTQVNTEYMVNAITALYAGSGNNKLPVLTWSQGGLVAQWGLTFFPSIRSKVDRLMAFAPDYKGTVLAGPLDALAVSAPSVWQQTTGSALTTALRNAGGLTQIVPTTNLYSATDEIVQPQVSNSPLDSSYLFNGKNVQAQAVCGPLFVIDHAGSLTSQFSYVVGRSALRSTTGQARSADYGITDCNPLPANDLTPEQKVAAAALLAPAAAAIVAGPKQNCEPDLMPYARPFAVGKRTCSGIVTP	2009.0	HPLC;SEM;DSC	PET used was from non-carbonated mineral water bottles (brand Crystal©). It presented 0.1 mm thickness and was cut in squares of aprox. 0.5 cm.	Crystal©	No	No				Yes		
Uncultured bacterium	77133	PET	Xi, X., Ni, K., Hao, H., Shang, Y., Zhao, B., & Qian, Z. (2021). Secretory expression in Bacillus subtilis and biochemical characterization of a highly thermostable polyethylene terephthalate hydrolase from bacterium HR29. Enzyme and microbial technology, 143, 109715.	PETase	00125	00125 | PETase | Uncultured bacterium | PET	Yes	GBD22443.1	MQVVLGRVRSAGLLAALLALAAWALVWASPSAEAQSNPYQRGPNPTRSALTTDGPFSVATYSVSRLSVSGFGGGVIYYPTGTTLTFGGIAMSPGYTADASSLAWLGRRLASHGFVVIVINTNSRLDFPDSRASQLSAALNYLRTSSPSAVRARLDANRLAVAGHSMGGGATLRISEQIPTLKAGVPLTPWHTDKTFNTPVPQLIVGAEADTVAPVSQHAIPFYQNLPSTTPKVYVELDNATHFAPNSPNAAISVYTISWMKLWVDNDTRYRQFLCNVNDPALSDFRSNNRHCQ	2021.0	DSC;HPLC	Amorphous polyethylene terephthalate pellets (PET, Cat#138) were purchased from Scientific Polymer Products (US). The powder form PET was prepared by grinding the pellets through a 400 μm sieve by the manufacturer (particle size <400 microns).	Scientific Polymer Products (US)	Yes	Yes				Yes		
Thermobifida fusca	2021	PET	Dresler, K., van den Heuvel, J., Müller, R. J., & Deckwer, W. D. (2006). Production of a recombinant polyester-cleaving hydrolase from Thermobifida fusca in Escherichia coli. Bioprocess and biosystems engineering, 29(3), 169-183.	Hydrolase	00126	00126 | Hydrolase | Thermobifida fusca | PET	Yes	Q6A0I4	MAVMTPRRERSSLLSRALQVTAAAATALVTAVSLAAPAHAANPYERGPNPTDALLEASSGPFSVSEENVSRLSASGFGGGTIYYPRENNTYGAVAISPGYTGTEASIAWLGERIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVTVPTLIIGADLDTIAPVATHAKPFYNSLPSSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2006.0									Yes		
Thermobifida fusca	2021	PET	Müller, R. J., Schrader, H., Profe, J., Dresler, K., & Deckwer, W. D. (2005). Enzymatic degradation of poly (ethylene terephthalate): rapid hydrolyse using a hydrolase from T. fusca. Macromolecular rapid communications, 26(17), 1400-1405.	Hydrolase	00126	00126 | Hydrolase | Thermobifida fusca | PET	Yes	Q6A0I4	MAVMTPRRERSSLLSRALQVTAAAATALVTAVSLAAPAHAANPYERGPNPTDALLEASSGPFSVSEENVSRLSASGFGGGTIYYPRENNTYGAVAISPGYTGTEASIAWLGERIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVTVPTLIIGADLDTIAPVATHAKPFYNSLPSSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2005.0									Yes		
Thermobifida fusca	2021	PET	Kleeberg, I., Welzel, K., VandenHeuvel, J., Müller, R. J., & Deckwer, W. D. (2005). Characterization of a new extracellular hydrolase from thermobifida fusca degrading aliphatic− aromatic copolyesters. Biomacromolecules, 6(1), 262-270.	Hydrolase	00126	00126 | Hydrolase | Thermobifida fusca | PET	Yes	Q6A0I4	MAVMTPRRERSSLLSRALQVTAAAATALVTAVSLAAPAHAANPYERGPNPTDALLEASSGPFSVSEENVSRLSASGFGGGTIYYPRENNTYGAVAISPGYTGTEASIAWLGERIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVTVPTLIIGADLDTIAPVATHAKPFYNSLPSSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2005.0									Yes		
Thermobifida fusca	2021	PET	Dresler, K., van den Heuvel, J., Müller, R. J., & Deckwer, W. D. (2006). Production of a recombinant polyester-cleaving hydrolase from Thermobifida fusca in Escherichia coli. Bioprocess and biosystems engineering, 29(3), 169-183.	Hydrolase	00127	00127 | Hydrolase | Thermobifida fusca | PET	Yes	CAH17554.1	MAVMTPRRERSSLLSRALRFTAAAATALVTAVSLAAPAHAANPYERGPNPTDALLEARSGPFSVSEERASRFGADGFGGGTIYYPRENNTYGAVAISPGYTGTQASVAWLGKRIASHGFVVITIDTNTTLDQPDSRARQLNAALDYMINDASSAVRSRIDSSRLAVMGHSMGGGGSLRLASQRPDLKAAIPLTPWHLNKNWSSVRVPTLIIGADLDTIAPVLTHARPFYNSLPTSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2006.0									Yes		
Thermobifida fusca	2021	PET	Müller, R. J., Schrader, H., Profe, J., Dresler, K., & Deckwer, W. D. (2005). Enzymatic degradation of poly (ethylene terephthalate): rapid hydrolyse using a hydrolase from T. fusca. Macromolecular rapid communications, 26(17), 1400-1405.	Hydrolase	00127	00127 | Hydrolase | Thermobifida fusca | PET	Yes	CAH17554.1	MAVMTPRRERSSLLSRALRFTAAAATALVTAVSLAAPAHAANPYERGPNPTDALLEARSGPFSVSEERASRFGADGFGGGTIYYPRENNTYGAVAISPGYTGTQASVAWLGKRIASHGFVVITIDTNTTLDQPDSRARQLNAALDYMINDASSAVRSRIDSSRLAVMGHSMGGGGSLRLASQRPDLKAAIPLTPWHLNKNWSSVRVPTLIIGADLDTIAPVLTHARPFYNSLPTSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2005.0									Yes		
Thermobifida fusca	2021	PET	Kleeberg, I., Welzel, K., VandenHeuvel, J., Müller, R. J., & Deckwer, W. D. (2005). Characterization of a new extracellular hydrolase from thermobifida fusca degrading aliphatic− aromatic copolyesters. Biomacromolecules, 6(1), 262-270.	Hydrolase	00127	00127 | Hydrolase | Thermobifida fusca | PET	Yes	CAH17554.1	MAVMTPRRERSSLLSRALRFTAAAATALVTAVSLAAPAHAANPYERGPNPTDALLEARSGPFSVSEERASRFGADGFGGGTIYYPRENNTYGAVAISPGYTGTQASVAWLGKRIASHGFVVITIDTNTTLDQPDSRARQLNAALDYMINDASSAVRSRIDSSRLAVMGHSMGGGGSLRLASQRPDLKAAIPLTPWHLNKNWSSVRVPTLIIGADLDTIAPVLTHARPFYNSLPTSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2005.0									Yes		
Thermobifida fusca	2021	PET	Chen, S., Tong, X., Woodard, R. W., Du, G., Wu, J., & Chen, J. (2008). Identification and characterization of bacterial cutinase. Journal of biological chemistry, 283(38), 25854-25862.	Cutinase	00128	00128 | Cutinase | Thermobifida fusca | PET	Yes	Q47RJ6	MAVMTPRRERSSLLSRALQVTAAAATALVTAVSLAAPAHAANPYERGPNPTDALLEASSGPFSVSEENVSRLSASGFGGGTIYYPRENNTYGAVAISPGYTGTEASIAWLGERIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVTVPTLIIGADLDTIAPVATHAKPFYNSLPSSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2008.0									Yes		
Thermobifida fusca	2021	PET	Chen, S., Tong, X., Woodard, R. W., Du, G., Wu, J., & Chen, J. (2008). Identification and characterization of bacterial cutinase. Journal of biological chemistry, 283(38), 25854-25862.	Cutinase	00129	00129 | Cutinase | Thermobifida fusca | PET	Yes	AET05798.1	MPPHAARPGPAQNRRGRAMAVITPRRERSSLLSRALRFTAAAATALVTAVSLAAPAHAANPYERGPNPTDALLEARSGPFSVSEERASRFGADGFGGGTIYYPRENNTYGAVAISPGYTGTQASVAWLGERIASHGFVVITIDTNTTLDQPDSRARQLNAALDYMINDASSAVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVRVPTLIIGADLDTIAPVLTHARPFYNSLPTSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2008.0									Yes		
Thermobifida fusca	2021	PET	Hegde, K., & Veeranki, V. D. (2013). Production optimization and characterization of recombinant cutinases from Thermobifida fusca sp. NRRL B-8184. Applied biochemistry and biotechnology, 170(3), 654-675.	Cutinase	00129	00129 | Cutinase | Thermobifida fusca | PET	Yes	AET05798.1	MPPHAARPGPAQNRRGRAMAVITPRRERSSLLSRALRFTAAAATALVTAVSLAAPAHAANPYERGPNPTDALLEARSGPFSVSEERASRFGADGFGGGTIYYPRENNTYGAVAISPGYTGTQASVAWLGERIASHGFVVITIDTNTTLDQPDSRARQLNAALDYMINDASSAVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVRVPTLIIGADLDTIAPVLTHARPFYNSLPTSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2013.0									Yes		
Thermobifida fusca	2021	PET	Hegde, K., & Veeranki, V. D. (2013). Production optimization and characterization of recombinant cutinases from Thermobifida fusca sp. NRRL B-8184. Applied biochemistry and biotechnology, 170(3), 654-675.	Cutinase	00131	00131 | Cutinase | Thermobifida fusca | PET	Yes	AET05799.1	MAVMTPRRERSSLLSRALQVTAAAATALVTAVSLAAPAHAANPYERGPNPTDALLEASSGPFSVSEENVSRLSASGFGGGTIYYPRENNTYGAVAISPGYTGTEASIAWLGERIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVTVPTLIIGADLDTIAPVATHAKPFYNSLPSSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2013.0									Yes		
Thermobifida cellulosilytica	144786	PET	Herrero Acero, E., Ribitsch, D., Steinkellner, G., Gruber, K., Greimel, K., Eiteljoerg, I., ... & Guebitz, G. (2011). Enzymatic surface hydrolysis of PET: effect of structural diversity on kinetic properties of cutinases from Thermobifida. Macromolecules, 44(12), 4632-4640.	Cutinase	00132	00132 | Cutinase | Thermobifida cellulosilytica | PET PLA	Yes	ADV92526.1	MANPYERGPNPTDALLEASSGPFSVSEENVSRLSASGFGGGTIYYPRENNTYGAVAISPGYTGTEASIAWLGERIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVTVPTLIIGADLDTIAPVATHAKPFYNSLPSSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2011.0	HPLC;FTIR	PET films were kindly provided by Dr. Vincent Nierstrasz from Ghent University. PET had a crystallinity degree of 37% measured by DSC.			Yes				Yes		
Thermobifida cellulosilytica	144786	PLA	Ribitsch, D., Hromic, A., Zitzenbacher, S., Zartl, B., Gamerith, C., Pellis, A., ... & Guebitz, G. M. (2017). Small cause, large effect: structural characterization of cutinases from Thermobifida cellulosilytica. Biotechnology and Bioengineering, 114(11), 2481-2488.	Cutinase	00132	00132 | Cutinase | Thermobifida cellulosilytica | PET PLA	Yes	ADV92526.1	MANPYERGPNPTDALLEASSGPFSVSEENVSRLSASGFGGGTIYYPRENNTYGAVAISPGYTGTEASIAWLGERIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVTVPTLIIGADLDTIAPVATHAKPFYNSLPSSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2017.0	HPLC	Poly(L-lactic acid) PLLA films, thickness 0.05 mm	Goodfellow (Cambridge, UK)	Yes	No				Yes		
Thermobifida cellulosilytica	144786	PET	Herrero Acero, E., Ribitsch, D., Steinkellner, G., Gruber, K., Greimel, K., Eiteljoerg, I., ... & Guebitz, G. (2011). Enzymatic surface hydrolysis of PET: effect of structural diversity on kinetic properties of cutinases from Thermobifida. Macromolecules, 44(12), 4632-4640.	Cutinase	00133	00133 | Cutinase | Thermobifida cellulosilytica | PET PLA	Yes	ADV92527.1	MANPYERGPNPTDALLEARSGPFSVSEERASRFGADGFGGGTIYYPRENNTYGAVAISPGYTGTQASVAWLGERIASHGFVVITIDTNTTLDQPDSRARQLNAALDYMINDASSAVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVRVPTLIIGADLDTIAPVLTHARPFYNSLPTSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2011.0	HPLC;FTIR	PET films were kindly provided by Dr. Vincent Nierstrasz from Ghent University. PET had a crystallinity degree of 37% measured by DSC.			Yes				Yes		
Thermobifida cellulosilytica	144786	PLA	Ribitsch, D., Hromic, A., Zitzenbacher, S., Zartl, B., Gamerith, C., Pellis, A., ... & Guebitz, G. M. (2017). Small cause, large effect: structural characterization of cutinases from Thermobifida cellulosilytica. Biotechnology and Bioengineering, 114(11), 2481-2488.	Cutinase	00133	00133 | Cutinase | Thermobifida cellulosilytica | PET PLA	Yes	ADV92527.1	MANPYERGPNPTDALLEARSGPFSVSEERASRFGADGFGGGTIYYPRENNTYGAVAISPGYTGTQASVAWLGERIASHGFVVITIDTNTTLDQPDSRARQLNAALDYMINDASSAVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVRVPTLIIGADLDTIAPVLTHARPFYNSLPTSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPF	2017.0	HPLC	Poly(L-lactic acid) PLLA films, thickness 0.05 mm	Goodfellow (Cambridge, UK)	Yes	No				Yes		
Bacillus subtilis	1423	PET	Ribitsch, D., Heumann, S., Trotscha, E., Herrero Acero, E., Greimel, K., Leber, R., ... & Guebitz, G. M. (2011). Hydrolysis of polyethyleneterephthalate by p‐nitrobenzylesterase from Bacillus subtilis. Biotechnology progress, 27(4), 951-960.	P-nitrobenzylesterase	00134	00134 | nitrobenzylesterase | Bacillus subtilis | PET	Yes	ADH43200.1	MTHQIVTTQYGKVKGTTENGVHKWKGIPYAKPPVGQWRFKAPEPPEVWEDVLDATAYGPICPQPSDLLSLSYTELPRQSEDCLYVNVFAPDTPSQNLPVMVWIHGGAFYLGAGSEPLYDGSKLAAQGEVIVVTLNYRLGPFGFLHLSSFNEAYSDNLGLLDQAAALKWVRENISAFGGDPDNVTVFGESAGGMSIAALLAMPAAKGLFQKAIMESGASRTMTKEQAASTSAAFLQVLGINEGQLDKLHTVSAEDSLKAADQLRIAEKENIFQLFFQPALDPKTLPEEPEKAIAEGAASGIPLLIGTTRDEGYLFFTPDSDVHSQETLDAALEYLLGKPLAEKAADLYPRSLESQIHMMTDLLFWRPAVAYASAQSHYAPVWMYRFDWHPKKPPYNKAFHALELPFVFGNLDGLERMAKAEITDEVKQLSHTIQSAWITFAKTGNPSTEAVNWPAYHEETRETLILDSEITIENDPESEKRQKLFPSKGE	2011.0	HPLC;FTIR;WCA	Semi-crystalline Hostaphan RNK 75 PET films with a thickness of 75 lm	Mitsubishi Polyester Film	Yes	No				No		
Thermomonospora curvata	2020	PET	Wei, R., Oeser, T., Then, J., Kühn, N., Barth, M., Schmidt, J., & Zimmermann, W. (2014). Functional characterization and structural modeling of synthetic polyester-degrading hydrolases from Thermomonospora curvata. AMB express, 4(1), 1-10.	Hydrolase	00135	00135 | Hydrolase | Thermomonospora curvata | PET PCL	Yes	D1A2H1	MKRTLKRALSLLPAAALAASALVAASPAQAAANPYQRGPNPTEASITAARGPFNTAEITVSRLSVSGFGGGKIYYPTTTSEGTFGAIAISPGFTAYWSSLEWLGHRLASQGFVVIGIETNTTLDQPDQRGQQLLAALDYLTQRSAVRDRVDASRLAVAGHSMGGGGSLEAAKARTSLKAAIPLAPWNLDKTWPEVRTPTLIIGGELDAVAPVATHSIPFYNSLSNAPEKAYLELDNASHFFPNITNTQMAKYMIAWMKRFIDDDTRYTQFLCPPPSTGLLSDFSDARFTCPM	2014.0	Spectrophotometry	low-crystallinity PET film	Goodfellow GmbH, Bad Nauheim, Germany	Yes	No				Yes		
Thermomonospora curvata	2020	PCL	Wei, R., Oeser, T., Then, J., Kühn, N., Barth, M., Schmidt, J., & Zimmermann, W. (2014). Functional characterization and structural modeling of synthetic polyester-degrading hydrolases from Thermomonospora curvata. AMB express, 4(1), 1-10.	Hydrolase	00135	00135 | Hydrolase | Thermomonospora curvata | PET PCL	Yes	D1A2H1	MKRTLKRALSLLPAAALAASALVAASPAQAAANPYQRGPNPTEASITAARGPFNTAEITVSRLSVSGFGGGKIYYPTTTSEGTFGAIAISPGFTAYWSSLEWLGHRLASQGFVVIGIETNTTLDQPDQRGQQLLAALDYLTQRSAVRDRVDASRLAVAGHSMGGGGSLEAAKARTSLKAAIPLAPWNLDKTWPEVRTPTLIIGGELDAVAPVATHSIPFYNSLSNAPEKAYLELDNASHFFPNITNTQMAKYMIAWMKRFIDDDTRYTQFLCPPPSTGLLSDFSDARFTCPM	2014.0	Spectrophotometry	amorphous PCL	Sigma-Aldrich Co., St. Louis, USA	Yes	No				Yes		
Uncultured bacterium	77133	PET	Unpublished	Hydrolase	00136	00136 | Hydrolase | Uncultured bacterium | PET	Yes	7CUV_A	ANPYERGPDPTESSIEAVRGPFAVAQTTVSRLQADGFGGGTIYYPTDTSQGTFGAVAISPGFTAGQESIAWLGPRIASQGFVVITIDTITRLDQPDSRGRQLQAALDHLRTNSVVRNRIDPNRMAVMGHSMGGGGALSAAANNTSLEAAIPLQGWHTRKNWSSVRTPTLVVGAQLDTIAPVSSHSEAFYNSLPSDLDKAYMELRGASHLVSNTPDTTTAKYSIAWLKRFVDDDLRYEQFLCPAPDDFAISEYRSTCPF										Yes		
Uncultured bacterium	77133	PET	Sonnendecker, C., Oeser, J., Richter, P. K., Hille, P., Zhao, Z., Fischer, C., ... & Zimmermann, W. (2021). Low Carbon Footprint Recycling of Post‐Consumer PET Plastic with a Metagenomic Polyester Hydrolase. ChemSusChem.	Polyester hydrolase	00137	00137 | Polyester hydrolase | Uncultured bacterium | PET PCL	Yes	7NEI_B	MANPYERGPDPTESSIEAVRGPFAVAQTTVSRLQADGFGGGTIYYPTDTSQGTFGAVAISPGFTAGQESIAWLGPRIASQGFVVITIDTITRLDQPDSRGRQLQAALDHLRTNSVVRNRIDPNRMAVMGHSMGGGGALSAAANNTSLEAAIPLQGWHTRKNWSSVRTPTLVVGAQLDTIAPVSSHSEAFYNSLPSDLDKAYMELRGASHLVSNTPDTTTAKYSIAWLKRFVDDDLRYEQFLCPAPDDFAISEYRSTCPFLEHHHHHH	2021.0	Weight loss;HPLC;SEM;MS	Amorphous polyethylene terephthalate (PET) films (G-PET, ES301445, thickness 250 μm) and biaxially oriented PET films (ES301450, thickness 250 μm)	Goodfellow GmbH (Bad Nauheim, Germany)	Yes	Yes				Yes		
Uncultured bacterium	77133	PCL	Sonnendecker, C., Oeser, J., Richter, P. K., Hille, P., Zhao, Z., Fischer, C., ... & Zimmermann, W. (2021). Low Carbon Footprint Recycling of Post‐Consumer PET Plastic with a Metagenomic Polyester Hydrolase. ChemSusChem.	Polyester hydrolase	00137	00137 | Polyester hydrolase | Uncultured bacterium | PET PCL	Yes	7NEI_B	MANPYERGPDPTESSIEAVRGPFAVAQTTVSRLQADGFGGGTIYYPTDTSQGTFGAVAISPGFTAGQESIAWLGPRIASQGFVVITIDTITRLDQPDSRGRQLQAALDHLRTNSVVRNRIDPNRMAVMGHSMGGGGALSAAANNTSLEAAIPLQGWHTRKNWSSVRTPTLVVGAQLDTIAPVSSHSEAFYNSLPSDLDKAYMELRGASHLVSNTPDTTTAKYSIAWLKRFVDDDLRYEQFLCPAPDDFAISEYRSTCPFLEHHHHHH	2021.0	Weight loss;HPLC;SEM;MS	Amorphous polyethylene terephthalate (PET) films (G-PET, ES301445, thickness 250 μm) and biaxially oriented PET films (ES301450, thickness 250 μm)	Goodfellow GmbH (Bad Nauheim, Germany)	Yes	Yes				Yes		
Uncultured bacterium	77133	PET	Sonnendecker, C., Oeser, J., Richter, P. K., Hille, P., Zhao, Z., Fischer, C., ... & Zimmermann, W. (2021). Low Carbon Footprint Recycling of Post‐Consumer PET Plastic with a Metagenomic Polyester Hydrolase. ChemSusChem.	Polyester hydrolase	00138	00138 | Polyester hydrolase | Uncultured bacterium | PET	Yes	LT571440	MANPYERGPDPTVQSIEAVRGPFSVSETNVSRLVVTGFGGGTIYYPRDTSQGTFGAVAIAPGFTASEGSMAWYGPRIASQGFVVFTIDTLTRLDQPDSRGRQLLAALDYLTQRSSVRSRIDSSRLAVMGHSMGGGGSLEASESRPSLKASIPLTPWNLKKNWRNNRVPTLIVGAENDSIASVRTHAEPFYESIPSTTNKAYLELNNATHFAPNISNTTIAKYSISWLKRFVDNDTRYEQFLCPPPRPDRDIEEYRCTCPY	2021.0	Weight loss;HPLC	Amorphous polyethylene terephthalate (PET) films (G-PET, ES301445, thickness 250 μm) and biaxially oriented PET films (ES301450, thickness 250 μm)	Goodfellow GmbH (Bad Nauheim, Germany)	Yes	Yes				Yes		
Uncultured bacterium	77133	PET	Sonnendecker, C., Oeser, J., Richter, P. K., Hille, P., Zhao, Z., Fischer, C., ... & Zimmermann, W. (2021). Low Carbon Footprint Recycling of Post‐Consumer PET Plastic with a Metagenomic Polyester Hydrolase. ChemSusChem.	Polyester hydrolase	00139	00139 | Polyester hydrolase | Uncultured bacterium | PET	Yes	LT571441	MANPYERGPAPTTSSIEASRGPFAIASVTVSRSSVSGFGGGTIYYPRDTSEGTFGAVAIAPGFTADEGSMAWYGPRIASQGFVVFTIDTITRLDQPDSRGRQLLAALDYLTQRSSVRSRIDSSRLAVMGHSMGGGGSLEASVSRPSLKAAIPLTPWNLKKNWRDVRVPTLIVGAESDSIASVRTHAEPFYESIPSTTNKAYLELNNATHFAPNISNTTIAKYSISWLKRFVDNDTRYEQFLCPPPRPDRDIEEYRSTCPH	2021.0	Weight loss;HPLC	Amorphous polyethylene terephthalate (PET) films (G-PET, ES301445, thickness 250 μm) and biaxially oriented PET films (ES301450, thickness 250 μm)	Goodfellow GmbH (Bad Nauheim, Germany)	Yes	Yes				Yes		
Uncultured bacterium	77133	PET	Sonnendecker, C., Oeser, J., Richter, P. K., Hille, P., Zhao, Z., Fischer, C., ... & Zimmermann, W. (2021). Low Carbon Footprint Recycling of Post‐Consumer PET Plastic with a Metagenomic Polyester Hydrolase. ChemSusChem.	Polyester hydrolase	00140	00140 | Polyester hydrolase | Uncultured bacterium | PET	Yes	LT571442	MENPYERGPDPTESSIEAVRGPFAVAQTTVSRLQADGFGGGTIYYPTDTSQGTFGAVAISPGFTAGQESIAWLGPRIASQGFVVITIDTITRLDQPDSRGRQLQAALDHLRTNSVVRNRIDPNRMAVMGHSMGGGGALSAAANNTSLEAAIPLQGWHTRKNWSSVRTPTLVVGAQLDTIAPVSSHSEAFYNSLPSDLDKAYMELRGASHFVSNTPDTTTAKYSIAWLKRFVDNDLRYEQFLCPAPDDFAISEYRATCPF	2021.0	Weight loss;HPLC	Amorphous polyethylene terephthalate (PET) films (G-PET, ES301445, thickness 250 μm) and biaxially oriented PET films (ES301450, thickness 250 μm)	Goodfellow GmbH (Bad Nauheim, Germany)	Yes	Yes				Yes		
Uncultured bacterium	77133	PET	Sonnendecker, C., Oeser, J., Richter, P. K., Hille, P., Zhao, Z., Fischer, C., ... & Zimmermann, W. (2021). Low Carbon Footprint Recycling of Post‐Consumer PET Plastic with a Metagenomic Polyester Hydrolase. ChemSusChem.	Polyester hydrolase	00141	00141 | Polyester hydrolase | Uncultured bacterium | PET	Yes	LT571443	MENPYERGPDPTTQSVEAARGPYAVSQITVGGQFGSYSGGTIYYPTSTADGKFGAVAIAPGFLSFQSSVAWLGPRIASQGFVVMTIDTGTIFDQPAQRGDQLLDALDFLTQRSSVKDRIDPNRLAVAGWSWGGGGSLEAAADRPSLKAAIPMAGWNLNTNWSRLTTPVLVVGVQNDLIAPVAMHSEPFYNSIRSEKAYLELAGGSHFTVTSANTPQAKLMISWLKRFVDNDTRYEQFICPGPSRGFSVSEYRSTCPY	2021.0	Weight loss;HPLC	Amorphous polyethylene terephthalate (PET) films (G-PET, ES301445, thickness 250 μm) and biaxially oriented PET films (ES301450, thickness 250 μm)	Goodfellow GmbH (Bad Nauheim, Germany)	Yes	Yes				Yes		
Uncultured bacterium	77133	PET	Sonnendecker, C., Oeser, J., Richter, P. K., Hille, P., Zhao, Z., Fischer, C., ... & Zimmermann, W. (2021). Low Carbon Footprint Recycling of Post‐Consumer PET Plastic with a Metagenomic Polyester Hydrolase. ChemSusChem.	Polyester hydrolase	00142	00142 | Polyester hydrolase | Uncultured bacterium | PET	Yes	LT571444	MDNPYERGPDPTTQSVEAARGPYAVSQITVGGQFGSYSGGTIYYPTSTADGKFGAVAIAPGFLSFQSSVAWLGPRLASQGFVVMTIDTGTIFDQPAQRGDQLLDALDFLTQRSSVKDRIDPNRLAVAGWSMGGGGSLEAAADRPSLKAAIPMAGWNLNTNWSRLTTPVLVVGVQNDLIAPVGSHSEPFYNSIRSEKAYLELAGGSHFTVTSANTPQAKLMISWLKRFVDNDTRYEQFICPGPSRGFSVSEYRSTCPF	2021.0	Weight loss;HPLC	Amorphous polyethylene terephthalate (PET) films (G-PET, ES301445, thickness 250 μm) and biaxially oriented PET films (ES301450, thickness 250 μm)	Goodfellow GmbH (Bad Nauheim, Germany)	Yes	Yes				Yes		
Uncultured bacterium	77133	PET	Sonnendecker, C., Oeser, J., Richter, P. K., Hille, P., Zhao, Z., Fischer, C., ... & Zimmermann, W. (2021). Low Carbon Footprint Recycling of Post‐Consumer PET Plastic with a Metagenomic Polyester Hydrolase. ChemSusChem.	Polyester hydrolase	00143	00143 | Polyester hydrolase | Uncultured bacterium | PET	Yes	LT571445	MDNPYERGPDPTTQSVEAARGPYAVSQITVGGQFGSYSGGTIYYPTSTTDGKFGAVAIAPGFLSFQSSVAWLGPRIASQGFVVMTIDTGTIFDQPAQRGDQLLDALDFLTQRSSVKDRIDPNRLAVAGWSMGGGGSLEAAADRPSLKAAIPMAGWNLNTNWSRLTTPVLVVGVQNDLIAPVAMHSEPFYNSIRSEKAYLELAGGSHFTVTSANTPQAKLMISWLKRFVDNDTRYEQFICPGPSRGFSVSEYRSTCPF	2021.0	Weight loss;HPLC	Amorphous polyethylene terephthalate (PET) films (G-PET, ES301445, thickness 250 μm) and biaxially oriented PET films (ES301450, thickness 250 μm)	Goodfellow GmbH (Bad Nauheim, Germany)	Yes	Yes				Yes		
Aequorivita sp.	1872390	PET	Zhang, H., Perez-Garcia, P., Dierkes, R. F., Applegate, V., Schumacher, J., Chibani, C. M., ... & Streit, W. R. (2021). The Bacteroidetes Aequorivita sp. and Kaistella jeonii Produce Promiscuous Esterases With PET-Hydrolyzing Activity. Frontiers in microbiology, 12.	Esterase	00144	00144 | Esterase | Aequorivita sp. | PET PU PCL	Yes	WP_111881932.1	MKKIYAVALFFLATSFAPNIIFAQCGDVTIESLTNPGPYEVATLTEADGLRNGPDYQGATVYYPTNATPPFASIAIVPGFTALPSSVEEWGPFYASHGIVTIIIGTNSLFDFPEERAVALIDALETMRQENTRSSSPLENQLDVDKFAVSGWSMGGGGAQRAAVLDNTIKGVVALCPWLPNASLNHDSPVLIFSGENDPTAPPAQHADLHYAATPNTTNKLLFEIENGNHSVANTPNGGNGAVGKIALSWLKLYVDENDCYCPLLTESLLVDPPAASKVLSSFECELLSVPDNSFAISVYPNPTHDFVNINSTNPVHFEVYSALGQRLLSGELTQSEKQIDFSNFAKGLYYVRLGNETVKIVRN	2022.0	HPLC;Clear zone	Low-crystallinity PET film	Goodfellow GmbH, Bad Nauheim, Germany	Yes	Yes				Yes		
Aequorivita sp.	1872390	PU	Zhang, H., Perez-Garcia, P., Dierkes, R. F., Applegate, V., Schumacher, J., Chibani, C. M., ... & Streit, W. R. (2021). The Bacteroidetes Aequorivita sp. and Kaistella jeonii Produce Promiscuous Esterases With PET-Hydrolyzing Activity. Frontiers in microbiology, 12.	Esterase	00144	00144 | Esterase | Aequorivita sp. | PET PU PCL	Yes	WP_111881932.1	MKKIYAVALFFLATSFAPNIIFAQCGDVTIESLTNPGPYEVATLTEADGLRNGPDYQGATVYYPTNATPPFASIAIVPGFTALPSSVEEWGPFYASHGIVTIIIGTNSLFDFPEERAVALIDALETMRQENTRSSSPLENQLDVDKFAVSGWSMGGGGAQRAAVLDNTIKGVVALCPWLPNASLNHDSPVLIFSGENDPTAPPAQHADLHYAATPNTTNKLLFEIENGNHSVANTPNGGNGAVGKIALSWLKLYVDENDCYCPLLTESLLVDPPAASKVLSSFECELLSVPDNSFAISVYPNPTHDFVNINSTNPVHFEVYSALGQRLLSGELTQSEKQIDFSNFAKGLYYVRLGNETVKIVRN	2022.0	HPLC;Clear zone	 Impranil DLN		Yes	Yes				Yes		
Aequorivita sp.	1872390	PCL	Zhang, H., Perez-Garcia, P., Dierkes, R. F., Applegate, V., Schumacher, J., Chibani, C. M., ... & Streit, W. R. (2021). The Bacteroidetes Aequorivita sp. and Kaistella jeonii Produce Promiscuous Esterases With PET-Hydrolyzing Activity. Frontiers in microbiology, 12.	Esterase	00144	00144 | Esterase | Aequorivita sp. | PET PU PCL	Yes	WP_111881932.1	MKKIYAVALFFLATSFAPNIIFAQCGDVTIESLTNPGPYEVATLTEADGLRNGPDYQGATVYYPTNATPPFASIAIVPGFTALPSSVEEWGPFYASHGIVTIIIGTNSLFDFPEERAVALIDALETMRQENTRSSSPLENQLDVDKFAVSGWSMGGGGAQRAAVLDNTIKGVVALCPWLPNASLNHDSPVLIFSGENDPTAPPAQHADLHYAATPNTTNKLLFEIENGNHSVANTPNGGNGAVGKIALSWLKLYVDENDCYCPLLTESLLVDPPAASKVLSSFECELLSVPDNSFAISVYPNPTHDFVNINSTNPVHFEVYSALGQRLLSGELTQSEKQIDFSNFAKGLYYVRLGNETVKIVRN	2022.0	HPLC;Clear zone	PCL		Yes	Yes				Yes		
Kaistella jeonii	266749	PET	Zhang, H., Perez-Garcia, P., Dierkes, R. F., Applegate, V., Schumacher, J., Chibani, C. M., ... & Streit, W. R. (2021). The Bacteroidetes Aequorivita sp. and Kaistella jeonii Produce Promiscuous Esterases With PET-Hydrolyzing Activity. Frontiers in microbiology, 12.	Esterase	00145	00145 | Esterase | Kaistella jeonii | PET PU PCL	Yes	WP_039353427.1	MRKLYLFLFLTLISPISISIFHAQCTGATVESLTNPGPYTVATLSEADGVRNGPKYAGSTIYYPTNATPPYASIAIVPGFTAAPSSVQEWGPFYASHGIVAIIIGTNSLYDQPEARALALLDALETIKQENGRATSPLIGKLDVTKLAVSGWSMGGGGAQRAAVLDNTISAVVALCPYLTSPQLNHTVPVLIFSGQSDPTAPPSQHANVHYNTTPGTTNKLLFEVKNGNHSVANSPTGGGGAVGKLALSWLKIYLEKNDCYCSVLATAIVNSTTVSSKISQSYQCNNALGVVDSKTRFNLYPNPTKDFVQVNVREMASYQLSSSTGQIVLKGIVTSSKNQIDLSKLPAGVYYLQINGETIKVIKKQ	2022.0	HPLC;Clear zone	Low-crystallinity PET film	Goodfellow GmbH, Bad Nauheim, Germany	Yes	Yes				Yes		
Kaistella jeonii	266749	PU	Zhang, H., Perez-Garcia, P., Dierkes, R. F., Applegate, V., Schumacher, J., Chibani, C. M., ... & Streit, W. R. (2021). The Bacteroidetes Aequorivita sp. and Kaistella jeonii Produce Promiscuous Esterases With PET-Hydrolyzing Activity. Frontiers in microbiology, 12.	Esterase	00145	00145 | Esterase | Kaistella jeonii | PET PU PCL	Yes	WP_039353427.1	MRKLYLFLFLTLISPISISIFHAQCTGATVESLTNPGPYTVATLSEADGVRNGPKYAGSTIYYPTNATPPYASIAIVPGFTAAPSSVQEWGPFYASHGIVAIIIGTNSLYDQPEARALALLDALETIKQENGRATSPLIGKLDVTKLAVSGWSMGGGGAQRAAVLDNTISAVVALCPYLTSPQLNHTVPVLIFSGQSDPTAPPSQHANVHYNTTPGTTNKLLFEVKNGNHSVANSPTGGGGAVGKLALSWLKIYLEKNDCYCSVLATAIVNSTTVSSKISQSYQCNNALGVVDSKTRFNLYPNPTKDFVQVNVREMASYQLSSSTGQIVLKGIVTSSKNQIDLSKLPAGVYYLQINGETIKVIKKQ	2022.0	HPLC;Clear zone	 Impranil DLN		Yes	Yes				Yes		
Kaistella jeonii	266749	PCL	Zhang, H., Perez-Garcia, P., Dierkes, R. F., Applegate, V., Schumacher, J., Chibani, C. M., ... & Streit, W. R. (2021). The Bacteroidetes Aequorivita sp. and Kaistella jeonii Produce Promiscuous Esterases With PET-Hydrolyzing Activity. Frontiers in microbiology, 12.	Esterase	00145	00145 | Esterase | Kaistella jeonii | PET PU PCL	Yes	WP_039353427.1	MRKLYLFLFLTLISPISISIFHAQCTGATVESLTNPGPYTVATLSEADGVRNGPKYAGSTIYYPTNATPPYASIAIVPGFTAAPSSVQEWGPFYASHGIVAIIIGTNSLYDQPEARALALLDALETIKQENGRATSPLIGKLDVTKLAVSGWSMGGGGAQRAAVLDNTISAVVALCPYLTSPQLNHTVPVLIFSGQSDPTAPPSQHANVHYNTTPGTTNKLLFEVKNGNHSVANSPTGGGGAVGKLALSWLKIYLEKNDCYCSVLATAIVNSTTVSSKISQSYQCNNALGVVDSKTRFNLYPNPTKDFVQVNVREMASYQLSSSTGQIVLKGIVTSSKNQIDLSKLPAGVYYLQINGETIKVIKKQ	2022.0	HPLC;Clear zone	PCL		Yes	Yes				Yes		
Aequorivita viscosa	797419	PU	Zhang, H., Perez-Garcia, P., Dierkes, R. F., Applegate, V., Schumacher, J., Chibani, C. M., ... & Streit, W. R. (2021). The Bacteroidetes Aequorivita sp. and Kaistella jeonii Produce Promiscuous Esterases With PET-Hydrolyzing Activity. Frontiers in microbiology, 12.	Esterase	00146	00146 | Esterase | Aequorivita viscosa | PU PCL	Yes	WP_073216622.1	MKIIYPLAVLFLITSLAPNTIFAQCEDVTIESLTNPGPYEVATLTEDDGIRNGPDYLDATVYYPTNATPPYASIAIVPGFTAQPSSVEEWGPFYASHGIVTIIIGTNSPFEFPDLRATALLDALETLRQENERQNSPLENQLDVDKFAVSGWSMGGGGAQLAAQMDSSIKAVLALCPWYPQATFNHNSPVLIFSGQDDTVAPPGIHADVHYNVTPDTTNKLLFEVANGSHSVANTPTGGDGVVGKIALSWLKLYLDDNDCYCPLLTDSLLVDPPAASKVEASFECEPIIGIAENNIDISIFPNPTDNFITVSIPTIASYKVYSALGQLLLSGEIDQSNKQIDFSQFAKGMYYVRVENETIRIIRK	2022.0	Clear zone	 Impranil DLN		Yes	No				Yes		
Aequorivita viscosa	797419	PCL	Zhang, H., Perez-Garcia, P., Dierkes, R. F., Applegate, V., Schumacher, J., Chibani, C. M., ... & Streit, W. R. (2021). The Bacteroidetes Aequorivita sp. and Kaistella jeonii Produce Promiscuous Esterases With PET-Hydrolyzing Activity. Frontiers in microbiology, 12.	Esterase	00146	00146 | Esterase | Aequorivita viscosa | PU PCL	Yes	WP_073216622.1	MKIIYPLAVLFLITSLAPNTIFAQCEDVTIESLTNPGPYEVATLTEDDGIRNGPDYLDATVYYPTNATPPYASIAIVPGFTAQPSSVEEWGPFYASHGIVTIIIGTNSPFEFPDLRATALLDALETLRQENERQNSPLENQLDVDKFAVSGWSMGGGGAQLAAQMDSSIKAVLALCPWYPQATFNHNSPVLIFSGQDDTVAPPGIHADVHYNVTPDTTNKLLFEVANGSHSVANTPTGGDGVVGKIALSWLKLYLDDNDCYCPLLTDSLLVDPPAASKVEASFECEPIIGIAENNIDISIFPNPTDNFITVSIPTIASYKVYSALGQLLLSGEIDQSNKQIDFSQFAKGMYYVRVENETIRIIRK	2022.0	Clear zone	PCL		Yes	No				Yes		
Aequorivita vladivostokensis	171194	PU	Zhang, H., Perez-Garcia, P., Dierkes, R. F., Applegate, V., Schumacher, J., Chibani, C. M., ... & Streit, W. R. (2021). The Bacteroidetes Aequorivita sp. and Kaistella jeonii Produce Promiscuous Esterases With PET-Hydrolyzing Activity. Frontiers in microbiology, 12.	Esterase	00147	00147 | Esterase | Aequorivita vladivostokensis | PU PCL	Yes	WP_052671284.1	MKKLYAVALFFLAISFPPNIIFAQCGDVTLESLTNPGPYEVATLTEADGLRNGPDYAGATVYYPTNATPPFASIAIVPGFTALPSSVEEWGPFYASHGIVTIIIGTNSLFDFPEQRATALLDALETMRQENTRSTSPLENQLDVDKFAVSGWSMGGGGAQRAAVLDNTIKGVVALCPWLPNASLNHDSPVLIFSGENDPTAPPAQHADLHYAATPNTTNKLLFEVENGNHSVANTPNGGNGAVGKIALSWLKLYLDDNDCYCPLLTDELLVNPPAASKVLSSFECELVLGVAENTVDISLYPNPTQDFVYINVSKVTYYEVYSALGQRLLSGKLTQGEKQIDFSNFAQGLYYVGVGNETMKVIRE	2022.0	Clear zone	 Impranil DLN		Yes	No				Yes		
Aequorivita vladivostokensis	171194	PCL	Zhang, H., Perez-Garcia, P., Dierkes, R. F., Applegate, V., Schumacher, J., Chibani, C. M., ... & Streit, W. R. (2021). The Bacteroidetes Aequorivita sp. and Kaistella jeonii Produce Promiscuous Esterases With PET-Hydrolyzing Activity. Frontiers in microbiology, 12.	Esterase	00147	00147 | Esterase | Aequorivita vladivostokensis | PU PCL	Yes	WP_052671284.1	MKKLYAVALFFLAISFPPNIIFAQCGDVTLESLTNPGPYEVATLTEADGLRNGPDYAGATVYYPTNATPPFASIAIVPGFTALPSSVEEWGPFYASHGIVTIIIGTNSLFDFPEQRATALLDALETMRQENTRSTSPLENQLDVDKFAVSGWSMGGGGAQRAAVLDNTIKGVVALCPWLPNASLNHDSPVLIFSGENDPTAPPAQHADLHYAATPNTTNKLLFEVENGNHSVANTPNGGNGAVGKIALSWLKLYLDDNDCYCPLLTDELLVNPPAASKVLSSFECELVLGVAENTVDISLYPNPTQDFVYINVSKVTYYEVYSALGQRLLSGKLTQGEKQIDFSNFAQGLYYVGVGNETMKVIRE	2022.0	Clear zone	PCL		Yes	No				Yes		
Amycolatopsis orientalis	31958	PLA	Li, F., Wang, S., Liu, W., & Chen, G. (2008). Purification and characterization of poly (L-lactic acid)-degrading enzymes from Amycolatopsis orientalis ssp. orientalis. FEMS microbiology letters, 282(1), 52-58.	Protease	00148	00148 | Protease | Amycolatopsis orientalis | PLA	Yes	B0FLR6	MGLAIAAAAVFSLPGVATATEPTGGVQPNIVGGGNATQVYSFMVSQQSSSGGHQCGGSLISSTWVVTAKHCGTPYQVRVGTTNRTSGGTVARVAQRIAHPSADLALLRLSTAVPQAPVTIADASGAVGTATRIIGWGQTCAPQGGCGAPITLQELNTSIVSDSRCLGISGASEICTNNPNGNSGACYGDSGGPQIKQVNGVWQLIGATSRAGNNSSTCATGPSIYVDVPYFRSWIRTNTGV	2008.0	Weight loss;Clear zone;SEM;Biosensor	PLA (solid) with a molecular weight range of 85 000–160 000. PLA powder and film (300–500 mm) with a molecular weight of 20 000 and 200 000.	 Sigma Chemical Co and  Chengdu Organic Chemicals Company Ltd of Chinese Academy of Sciences (COCC)	Yes	No				No		
Amycolatopsis orientalis	31958	PLA	Li, F., Wang, S., Liu, W., & Chen, G. (2008). Purification and characterization of poly (L-lactic acid)-degrading enzymes from Amycolatopsis orientalis ssp. orientalis. FEMS microbiology letters, 282(1), 52-58.	Protease	00149	00149 | Protease | Amycolatopsis orientalis | PLA	Yes	B0FY08	YDVRGGDAYYINNSPRCSIGFSVNGGFLTAGHCGPGTVTGSNRVAMGSFARASFPGNDYGHVRVNSNWVPRGIINNGTRVSGSSEASTGASICKSGSTTGWTCGTVGAKNQTVRYAEGTVYGMTATNARSQAGDSGGSFIAGNQAQGMLSGGNSTVTYFFPVRPALSATGTSLVLG	2008.0	Weight loss;Clear zone;SEM;Biosensor	PLA (solid) with a molecular weight range of 85 000–160 000. PLA powder and film (300–500 mm) with a molecular weight of 20 000 and 200 000.	 Sigma Chemical Co and  Chengdu Organic Chemicals Company Ltd of Chinese Academy of Sciences (COCC)	Yes	No				No		
Alcanivorax borkumensis	59754	PLA	Hajighasemi, M., Nocek, B. P., Tchigvintsev, A., Brown, G., Flick, R., Xu, X., ... & Yakunin, A. F. (2016). Biochemical and structural insights into enzymatic depolymerization of polylactic acid and other polyesters by microbial carboxylesterases. Biomacromolecules, 17(6), 2027-2039.	Hydrolase	00150	00150 | Hydrolase | Alcanivorax borkumensis | PLA PHBV PCL PBSA PES PHA	Yes	Q0VLQ1	MQSGTVASNGIELFYESRGPENGEPMVFVMGLSAQMVFWPDTLLDALAAKGYRVIRFDNRDVGKSTQIRKPIKQGPVSAILRRIIGLPVESPYTLHDMVADTVGLLDALNIERAHFVGASMGGMISQLMAGTHPERVLSLTSIMSSNNSSLLPPPKPSALRVLIAPRVKVETEEQFVTFGLEMMSKLAGTLPQGKEELAAMYRAAWARGINPRGIRNQFLAITATGSLSKTLKQIQCPTTVIHGGADPLIRPAGGKASARAIRGAKLVIIPGMGHDFPPSVIDRIGELIAETAGRANSVVPPAVG	2016.0	Spectrometry;Clear zone;LC-MS;GPC	poly(D,L-lactide) PLA10 (average molecular weight Mw 1.0–1.8 × 104) and PLA18 (Mw 1.8–2.4 × 104)	Sigma Aldrich	Yes	No				Yes		
Alcanivorax borkumensis	59754	PHA	Hajighasemi, M., Nocek, B. P., Tchigvintsev, A., Brown, G., Flick, R., Xu, X., ... & Yakunin, A. F. (2016). Biochemical and structural insights into enzymatic depolymerization of polylactic acid and other polyesters by microbial carboxylesterases. Biomacromolecules, 17(6), 2027-2039.	Hydrolase	00150	00150 | Hydrolase | Alcanivorax borkumensis | PLA PHBV PCL PBSA PES PHA	Yes	Q0VLQ1	MQSGTVASNGIELFYESRGPENGEPMVFVMGLSAQMVFWPDTLLDALAAKGYRVIRFDNRDVGKSTQIRKPIKQGPVSAILRRIIGLPVESPYTLHDMVADTVGLLDALNIERAHFVGASMGGMISQLMAGTHPERVLSLTSIMSSNNSSLLPPPKPSALRVLIAPRVKVETEEQFVTFGLEMMSKLAGTLPQGKEELAAMYRAAWARGINPRGIRNQFLAITATGSLSKTLKQIQCPTTVIHGGADPLIRPAGGKASARAIRGAKLVIIPGMGHDFPPSVIDRIGELIAETAGRANSVVPPAVG	2016.0	Spectrometry;Clear zone	poly(3-hydroxybutyric acid-co-3-hydroxyvaleric acid)	Sigma Aldrich	Yes	No				Yes		
Alcanivorax borkumensis	59754	PHBV	Hajighasemi, M., Nocek, B. P., Tchigvintsev, A., Brown, G., Flick, R., Xu, X., ... & Yakunin, A. F. (2016). Biochemical and structural insights into enzymatic depolymerization of polylactic acid and other polyesters by microbial carboxylesterases. Biomacromolecules, 17(6), 2027-2039.	Hydrolase	00150	00150 | Hydrolase | Alcanivorax borkumensis | PLA PHBV PCL PBSA PES PHA	Yes	Q0VLQ1	MQSGTVASNGIELFYESRGPENGEPMVFVMGLSAQMVFWPDTLLDALAAKGYRVIRFDNRDVGKSTQIRKPIKQGPVSAILRRIIGLPVESPYTLHDMVADTVGLLDALNIERAHFVGASMGGMISQLMAGTHPERVLSLTSIMSSNNSSLLPPPKPSALRVLIAPRVKVETEEQFVTFGLEMMSKLAGTLPQGKEELAAMYRAAWARGINPRGIRNQFLAITATGSLSKTLKQIQCPTTVIHGGADPLIRPAGGKASARAIRGAKLVIIPGMGHDFPPSVIDRIGELIAETAGRANSVVPPAVG	2016.0	Spectrometry;Clear zone	poly(3-hydroxybutyric acid-co-3-hydroxyvaleric acid)	Sigma Aldrich	Yes	No				Yes		
Alcanivorax borkumensis	59754	PCL	Hajighasemi, M., Nocek, B. P., Tchigvintsev, A., Brown, G., Flick, R., Xu, X., ... & Yakunin, A. F. (2016). Biochemical and structural insights into enzymatic depolymerization of polylactic acid and other polyesters by microbial carboxylesterases. Biomacromolecules, 17(6), 2027-2039.	Hydrolase	00150	00150 | Hydrolase | Alcanivorax borkumensis | PLA PHBV PCL PBSA PES PHA	Yes	Q0VLQ1	MQSGTVASNGIELFYESRGPENGEPMVFVMGLSAQMVFWPDTLLDALAAKGYRVIRFDNRDVGKSTQIRKPIKQGPVSAILRRIIGLPVESPYTLHDMVADTVGLLDALNIERAHFVGASMGGMISQLMAGTHPERVLSLTSIMSSNNSSLLPPPKPSALRVLIAPRVKVETEEQFVTFGLEMMSKLAGTLPQGKEELAAMYRAAWARGINPRGIRNQFLAITATGSLSKTLKQIQCPTTVIHGGADPLIRPAGGKASARAIRGAKLVIIPGMGHDFPPSVIDRIGELIAETAGRANSVVPPAVG	2016.0	Spectrometry;Clear zone	PCL10 (Mw 1.0 × 104), PCL 45 (Mw 4.5 × 104),PCL70 (Mw 7.0–9.0 × 104)	Sigma Aldrich	Yes	No				Yes		
Alcanivorax borkumensis	59754	PBSA	Hajighasemi, M., Nocek, B. P., Tchigvintsev, A., Brown, G., Flick, R., Xu, X., ... & Yakunin, A. F. (2016). Biochemical and structural insights into enzymatic depolymerization of polylactic acid and other polyesters by microbial carboxylesterases. Biomacromolecules, 17(6), 2027-2039.	Hydrolase	00150	00150 | Hydrolase | Alcanivorax borkumensis | PLA PHBV PCL PBSA PES PHA	Yes	Q0VLQ1	MQSGTVASNGIELFYESRGPENGEPMVFVMGLSAQMVFWPDTLLDALAAKGYRVIRFDNRDVGKSTQIRKPIKQGPVSAILRRIIGLPVESPYTLHDMVADTVGLLDALNIERAHFVGASMGGMISQLMAGTHPERVLSLTSIMSSNNSSLLPPPKPSALRVLIAPRVKVETEEQFVTFGLEMMSKLAGTLPQGKEELAAMYRAAWARGINPRGIRNQFLAITATGSLSKTLKQIQCPTTVIHGGADPLIRPAGGKASARAIRGAKLVIIPGMGHDFPPSVIDRIGELIAETAGRANSVVPPAVG	2016.0	Spectrometry;Clear zone	BionolleTM 3001MD, and BionolleTM 3020MD	Showa Denko K.K., Japan	Yes	No				Yes		
Alcanivorax borkumensis	59754	PES	Hajighasemi, M., Nocek, B. P., Tchigvintsev, A., Brown, G., Flick, R., Xu, X., ... & Yakunin, A. F. (2016). Biochemical and structural insights into enzymatic depolymerization of polylactic acid and other polyesters by microbial carboxylesterases. Biomacromolecules, 17(6), 2027-2039.	Hydrolase	00150	00150 | Hydrolase | Alcanivorax borkumensis | PLA PHBV PCL PBSA PES PHA	Yes	Q0VLQ1	MQSGTVASNGIELFYESRGPENGEPMVFVMGLSAQMVFWPDTLLDALAAKGYRVIRFDNRDVGKSTQIRKPIKQGPVSAILRRIIGLPVESPYTLHDMVADTVGLLDALNIERAHFVGASMGGMISQLMAGTHPERVLSLTSIMSSNNSSLLPPPKPSALRVLIAPRVKVETEEQFVTFGLEMMSKLAGTLPQGKEELAAMYRAAWARGINPRGIRNQFLAITATGSLSKTLKQIQCPTTVIHGGADPLIRPAGGKASARAIRGAKLVIIPGMGHDFPPSVIDRIGELIAETAGRANSVVPPAVG	2016.0	Spectrometry;Clear zone	poly(ethylene succinate)	Sigma Aldrich	Yes	No				Yes		
Rhodopseudomonas palustris	1076	PLA	Hajighasemi, M., Nocek, B. P., Tchigvintsev, A., Brown, G., Flick, R., Xu, X., ... & Yakunin, A. F. (2016). Biochemical and structural insights into enzymatic depolymerization of polylactic acid and other polyesters by microbial carboxylesterases. Biomacromolecules, 17(6), 2027-2039.	Hydrolase	00151	00151 | Hydrolase | Rhodopseudomonas palustris | PLA PCL PBSA	Yes	Q6N9M9	MSDLVWSRDGLDWPHREASRFIEAGGFRWHVQRMGSPAAPAILLIHGTGAASHSWRGLAPLLSRHYHVVAPDLPGHGFTQTPRGHRMSLPGMASDLAALLRVLQVAPQLVVGHSAGAAILARMCLDGSIDPKILFSLNGAFLPYGGPAASFFSPLAKMLVMNPFVPSLFAWQAGHRGAVERLIGNTGSTIDPAGIKLYGKLVSSPNHVAAALRMMANWDLEPLLKALPNLKPLLVLVAAEGDRAIPPSVAVKVREILPKAVIERIPALGHLAHEERPALIAALIERYAEKLENIE	2016.0	Spectrometry;Clear zone;LC-MS;GPC	poly(D,L-lactide) PLA10 (average molecular weight Mw 1.0–1.8 × 104) and PLA18 (Mw 1.8–2.4 × 104)	Sigma Aldrich	Yes	No				Yes		
Rhodopseudomonas palustris	1076	PCL	Hajighasemi, M., Nocek, B. P., Tchigvintsev, A., Brown, G., Flick, R., Xu, X., ... & Yakunin, A. F. (2016). Biochemical and structural insights into enzymatic depolymerization of polylactic acid and other polyesters by microbial carboxylesterases. Biomacromolecules, 17(6), 2027-2039.	Hydrolase	00151	00151 | Hydrolase | Rhodopseudomonas palustris | PLA PCL PBSA	Yes	Q6N9M9	MSDLVWSRDGLDWPHREASRFIEAGGFRWHVQRMGSPAAPAILLIHGTGAASHSWRGLAPLLSRHYHVVAPDLPGHGFTQTPRGHRMSLPGMASDLAALLRVLQVAPQLVVGHSAGAAILARMCLDGSIDPKILFSLNGAFLPYGGPAASFFSPLAKMLVMNPFVPSLFAWQAGHRGAVERLIGNTGSTIDPAGIKLYGKLVSSPNHVAAALRMMANWDLEPLLKALPNLKPLLVLVAAEGDRAIPPSVAVKVREILPKAVIERIPALGHLAHEERPALIAALIERYAEKLENIE	2016.0	Spectrometry;Clear zone	PCL10 (Mw 1.0 × 104), PCL 45 (Mw 4.5 × 104),PCL70 (Mw 7.0–9.0 × 104)	Sigma Aldrich	Yes	No				Yes		
Rhodopseudomonas palustris	1076	PBSA	Hajighasemi, M., Nocek, B. P., Tchigvintsev, A., Brown, G., Flick, R., Xu, X., ... & Yakunin, A. F. (2016). Biochemical and structural insights into enzymatic depolymerization of polylactic acid and other polyesters by microbial carboxylesterases. Biomacromolecules, 17(6), 2027-2039.	Hydrolase	00151	00151 | Hydrolase | Rhodopseudomonas palustris | PLA PCL PBSA	Yes	Q6N9M9	MSDLVWSRDGLDWPHREASRFIEAGGFRWHVQRMGSPAAPAILLIHGTGAASHSWRGLAPLLSRHYHVVAPDLPGHGFTQTPRGHRMSLPGMASDLAALLRVLQVAPQLVVGHSAGAAILARMCLDGSIDPKILFSLNGAFLPYGGPAASFFSPLAKMLVMNPFVPSLFAWQAGHRGAVERLIGNTGSTIDPAGIKLYGKLVSSPNHVAAALRMMANWDLEPLLKALPNLKPLLVLVAAEGDRAIPPSVAVKVREILPKAVIERIPALGHLAHEERPALIAALIERYAEKLENIE	2016.0	Spectrometry;Clear zone	BionolleTM 3001MD, and BionolleTM 3020MD	Showa Denko K.K., Japan	Yes	No				Yes		
Uncultured bacterium	77133	PCL	Sulaiman, S., Yamato, S., Kanaya, E., Kim, J. J., Koga, Y., Takano, K., & Kanaya, S. (2012). Isolation of a novel cutinase homolog with polyethylene terephthalate-degrading activity from leaf-branch compost by using a metagenomic approach. Appl. Environ. Microbiol., 78(5), 1556-1562.	Cutinase	00062	00062 | Cutinase | Uncultured bacterium | PCL PET	Yes	AEV21261.1	MDGVLWRVRTAALMAALLALAAWALVWASPSVEAQSNPYQRGPNPTRSALTADGPFSVATYTVSRLSVSGFGGGVIYYPTGTSLTFGGIAMSPGYTADASSLAWLGRRLASHGFVVLVINTNSRFDYPDSRASQLSAALNYLRTSSPSAVRARLDANRLAVAGHSMGGGGTLRIAEQNPSLKAAVPLTPWHTDKTFNTSVPVLIVGAEADTVAPVSQHAIPFYQNLPSTTPKVYVELDNASHFAPNSNNAAISVYTISWMKLWVDNDTRYRQFLCNVNDPALSDFRTNNRHCQ	2012.0	Weight loss	PCL (Wako Pure Chemical, Osaka, Japan)	Wako Pure Chemical	Yes	No				Yes		
Uncultured bacterium	77133	PET	Sulaiman, S., Yamato, S., Kanaya, E., Kim, J. J., Koga, Y., Takano, K., & Kanaya, S. (2012). Isolation of a novel cutinase homolog with polyethylene terephthalate-degrading activity from leaf-branch compost by using a metagenomic approach. Appl. Environ. Microbiol., 78(5), 1556-1562.	Cutinase	00062	00062 | Cutinase | Uncultured bacterium | PCL PET	Yes	AEV21261.1	MDGVLWRVRTAALMAALLALAAWALVWASPSVEAQSNPYQRGPNPTRSALTADGPFSVATYTVSRLSVSGFGGGVIYYPTGTSLTFGGIAMSPGYTADASSLAWLGRRLASHGFVVLVINTNSRFDYPDSRASQLSAALNYLRTSSPSAVRARLDANRLAVAGHSMGGGGTLRIAEQNPSLKAAVPLTPWHTDKTFNTSVPVLIVGAEADTVAPVSQHAIPFYQNLPSTTPKVYVELDNASHFAPNSNNAAISVYTISWMKLWVDNDTRYRQFLCNVNDPALSDFRTNNRHCQ	2012.0	Weight loss	For preparation of PET film, a plastic package made of PET was cut into _		No	No				Yes		
Aspergillus oryzae	5062	PBS	Maeda, H., Yamagata, Y., Abe, K., Hasegawa, F., Machida, M., Ishioka, R., ... & Nakajima, T. (2005). Purification and characterization of a biodegradable plastic-degrading enzyme from Aspergillus oryzae. Applied microbiology and biotechnology, 67(6), 778-788.	Cutinase	00034	00034 | Cutinase | Aspergillus oryzae | PBS PBSA	Yes		MHLRNIVIALAATAVASPVDLQDRQLTGGDELRDGPCKPITFIFARASTEPGLLGISTGPAVCNRLKLARSGDVACQGVGPRYTADLPSNALPEGTSQAAIAEAQGLFEQAVSKCPDTQIVAGGYSQGTAVMNGAIKRLSADVQDKIKGVVLFGYTRNAQERGQIANFPKDKVKVYCAVGDLVCLGTLIVAPPHFSYLSDTGDASDFLLSQLG	2005.0	Clear zone	PBS film (Bionolle #1001; weight-average molecular weight, 1.0×105; thickness, 20-μm) and emulsified PBS (Bionolle EM-150; weight average molecular weight, 1.0×105) were obtained from Showa Highpolymer (Tokyo, Japan).	Showa Denko	No	No	Culture collection	Culture collection		No		
Aspergillus oryzae	5062	PBSA	Maeda, H., Yamagata, Y., Abe, K., Hasegawa, F., Machida, M., Ishioka, R., ... & Nakajima, T. (2005). Purification and characterization of a biodegradable plastic-degrading enzyme from Aspergillus oryzae. Applied microbiology and biotechnology, 67(6), 778-788.	Cutinase	00034	00034 | Cutinase | Aspergillus oryzae | PBS PBSA	Yes		MHLRNIVIALAATAVASPVDLQDRQLTGGDELRDGPCKPITFIFARASTEPGLLGISTGPAVCNRLKLARSGDVACQGVGPRYTADLPSNALPEGTSQAAIAEAQGLFEQAVSKCPDTQIVAGGYSQGTAVMNGAIKRLSADVQDKIKGVVLFGYTRNAQERGQIANFPKDKVKVYCAVGDLVCLGTLIVAPPHFSYLSDTGDASDFLLSQLG	2005.0	Clear zone	PBSA film (Bionolle #3001; weight-average molecular weight, 2.2×105; thickness, 50-μm) and PBSA (Bionolle EM-301; weight-average molecular weight, 1.0×105) were purchased from Nacalai Tesque (Kyoto, Japan). 	Showa Denko	No	No	Culture collection	Culture collection		No		
Aspergillus oryzae	5062	PCL	Liu, Z., Gosser, Y., Baker, P. J., Ravee, Y., Lu, Z., Alemu, G., ... & Montclare, J. K. (2009). Structural and functional studies of Aspergillus oryzae cutinase: enhanced thermostability and hydrolytic activity of synthetic ester and polyester degradation. Journal of the American chemical society, 131(43), 15711-15716.	Cutinase	00051	00051 | Cutinase | Aspergillus oryzae | PCL	Yes	3GBS_A	SPVDLQDRQLTGGDELRDGPCKPITFIFARASTEPGLLGISTGPAVCNRLKLARSGDVACQGVGPRYTADLPSNALPEGTSQAAIAEAQGLFEQAVSKCPDTQIVAGGYSQGTAVMNGAIKRLSADVQDKIKGVVLFGYTRNAQERGQIANFPKDKVKVYCAVGDLVCLGTLIVAPPHFSYLSDTGDASDFLLSQLG	2009.0	Weight loss	Thin films of poly(εcaprolactone) (PCL) were cut to 1.0 cm × 1.0 cm with an approximate thickness of 250 µm 			No				Yes		
Aspergillus oryzae	5062	PBSA	Garrido, S. M., Kitamoto, N., Watanabe, A., Shintani, T., & Gomi, K. (2012). Functional analysis of FarA transcription factor in the regulation of the genes encoding lipolytic enzymes and hydrophobic surface binding protein for the degradation of biodegradable plastics in Aspergillus oryzae. Journal of bioscience and bioengineering, 113(5), 549-555.	Cutinase	00034	00034 | Cutinase | Aspergillus oryzae | PBS PBSA	Yes		MHLRNIVIALAATAVASPVDLQDRQLTGGDELRDGPCKPITFIFARASTEPGLLGISTGPAVCNRLKLARSGDVACQGVGPRYTADLPSNALPEGTSQAAIAEAQGLFEQAVSKCPDTQIVAGGYSQGTAVMNGAIKRLSADVQDKIKGVVLFGYTRNAQERGQIANFPKDKVKVYCAVGDLVCLGTLIVAPPHFSYLSDTGDASDFLLSQLG	2012.0	Clear zone				No	Culture collection	Culture collection		No		
Talaromyces funiculosus	28572	PHB	Miyazaki, S., Takahashi, K., Shiraki, M., Saito, T., Tezuka, Y., & Kasuya, K. I. (2000). Properties of a poly (3-hydroxybutyrate) depolymerase from Penicillium funiculosum. Journal of Polymers and the Environment, 8(4), 175-182.	PHB depolymerase	00020	00020 | PHB depolymerase | Talaromyces funiculosus | PHB PHA	Yes	BAG32152.1	MFDSVKIAWLVALGAAQVAATALPAFNVNPNSVSVSGLSSGGYMAAQLGVAYSDVFNVGFGVFAGGPYDCARNQYYTSCMYNGYPSITTPTANMKSWSGNQIASVANLGQRKIYMWTGSSDTTVGPNVMNQLKAQLGNFDNSANVSYVTTTGAVHTFPTDFNGAGDNSCSLSTSPYISNCNYDGAGAALKWIYGSLNARNTGTLSGSVLSFAQSGSYGANGMDTTGYLYVPQSCASGATVCSLHVALHGCLQSYSSIGSRFIQNTGYNKWADTNNMIILYPQAIPDYTIHAIWNGGVLSNPNGCWDWVGWYGSNADQIGGVQMAAIVGQVKQIVSGFQG	2000.0	Spectrophotometry			No	No	Culture collection	Culture collection		Yes		
Talaromyces funiculosus	28572	PHA	Miyazaki, S., Takahashi, K., Shiraki, M., Saito, T., Tezuka, Y., & Kasuya, K. I. (2000). Properties of a poly (3-hydroxybutyrate) depolymerase from Penicillium funiculosum. Journal of Polymers and the Environment, 8(4), 175-182.	PHB depolymerase	00020	00020 | PHB depolymerase | Talaromyces funiculosus | PHB PHA	Yes	BAG32152.1	MFDSVKIAWLVALGAAQVAATALPAFNVNPNSVSVSGLSSGGYMAAQLGVAYSDVFNVGFGVFAGGPYDCARNQYYTSCMYNGYPSITTPTANMKSWSGNQIASVANLGQRKIYMWTGSSDTTVGPNVMNQLKAQLGNFDNSANVSYVTTTGAVHTFPTDFNGAGDNSCSLSTSPYISNCNYDGAGAALKWIYGSLNARNTGTLSGSVLSFAQSGSYGANGMDTTGYLYVPQSCASGATVCSLHVALHGCLQSYSSIGSRFIQNTGYNKWADTNNMIILYPQAIPDYTIHAIWNGGVLSNPNGCWDWVGWYGSNADQIGGVQMAAIVGQVKQIVSGFQG	2000.0	Spectrophotometry			No	No	Culture collection	Culture collection		Yes		
Talaromyces funiculosus	28572	PHB	Kasuya, K. I., Tezuka, Y., Ishii, N., Yamagata, Y., Shiraki, M., Saito, T., ... & Doi, Y. (2007, April). Molecular characterization of the poly (3‐hydroxybutyrate) depolymerase gene from Penicillium funiculosum. In Macromolecular Symposia (Vol. 249, No. 1, pp. 540-544). Weinheim: WILEY‐VCH Verlag.	PHB depolymerase	00020	00020 | PHB depolymerase | Talaromyces funiculosus | PHB PHA	Yes	BAG32152.1	MFDSVKIAWLVALGAAQVAATALPAFNVNPNSVSVSGLSSGGYMAAQLGVAYSDVFNVGFGVFAGGPYDCARNQYYTSCMYNGYPSITTPTANMKSWSGNQIASVANLGQRKIYMWTGSSDTTVGPNVMNQLKAQLGNFDNSANVSYVTTTGAVHTFPTDFNGAGDNSCSLSTSPYISNCNYDGAGAALKWIYGSLNARNTGTLSGSVLSFAQSGSYGANGMDTTGYLYVPQSCASGATVCSLHVALHGCLQSYSSIGSRFIQNTGYNKWADTNNMIILYPQAIPDYTIHAIWNGGVLSNPNGCWDWVGWYGSNADQIGGVQMAAIVGQVKQIVSGFQG	2007.0									Yes		
Talaromyces funiculosus	28572	PHA	Kasuya, K. I., Tezuka, Y., Ishii, N., Yamagata, Y., Shiraki, M., Saito, T., ... & Doi, Y. (2007, April). Molecular characterization of the poly (3‐hydroxybutyrate) depolymerase gene from Penicillium funiculosum. In Macromolecular Symposia (Vol. 249, No. 1, pp. 540-544). Weinheim: WILEY‐VCH Verlag.	PHB depolymerase	00020	00020 | PHB depolymerase | Talaromyces funiculosus | PHB PHA	Yes	BAG32152.1	MFDSVKIAWLVALGAAQVAATALPAFNVNPNSVSVSGLSSGGYMAAQLGVAYSDVFNVGFGVFAGGPYDCARNQYYTSCMYNGYPSITTPTANMKSWSGNQIASVANLGQRKIYMWTGSSDTTVGPNVMNQLKAQLGNFDNSANVSYVTTTGAVHTFPTDFNGAGDNSCSLSTSPYISNCNYDGAGAALKWIYGSLNARNTGTLSGSVLSFAQSGSYGANGMDTTGYLYVPQSCASGATVCSLHVALHGCLQSYSSIGSRFIQNTGYNKWADTNNMIILYPQAIPDYTIHAIWNGGVLSNPNGCWDWVGWYGSNADQIGGVQMAAIVGQVKQIVSGFQG	2007.0									Yes		
Pseudomonas fluorescens	294	PU	Howard, G. T., & Blake, R. C. (1998). Growth of Pseudomonas fluorescens on a polyester–polyurethane and the purification and characterization of a polyurethanase–protease enzyme. International biodeterioration & biodegradation, 42(4), 213-220.	Protease	00130	00130 | Protease | Pseudomonas fluorescens | PU	Yes	AAF66684.1	MAITLYSYHNLDNGFAVGYQNNGLGLGLPATLVSALIGGSNAQGVIPGIPWNPDSEKPALEAVQAAGWTPISASTLGYTARSMHAAPTLAKNSATARRRPRCWASTMTLATAGNRHQFPRHFRASGKCDHRLHRRCDQRPARRLRAQGLCQELRGGGFWRVAQRLADTPLPGLGGNDVVVSGHSLGGMAVNSMADLSDSTWSGFYKDANYLAYASPTQSAGDKVLNVGYENDPVFRALDGSSFNLSSLGVHDKAHESSTDNIVSLNDHYASSLWNVLPFSILNLPTWVSHLPTGYGDGMTRILDSGFYEQMTRDSTVIVANLSDPARATTWVQDLNRNAEAHKGNTFIIGSDGDDFIKGGRGADFIEGGKGNDTIRDSSGHNTFLFSGQFGNDRVIGYQATDKLVFNDVAGSTDYRDHVKVVGGDTVIGFGTDSVTLVGVSSLSGEGIVIS	1998.0	Clear zone;Zymogram;Particle counter	 Impranil DLN		No	No			USA	No		
Pseudomonas fluorescens	294	PU	Vega, R. E., Main, T., & Howard, G. T. (1999). Cloning and expression in Escherichia coli of apolyurethane-degrading enzyme from Pseudomonasfluorescens. International biodeterioration & biodegradation, 43(1-2), 49-55.	Protease	00130	00130 | Protease | Pseudomonas fluorescens | PU	Yes	AAF66684.1	MAITLYSYHNLDNGFAVGYQNNGLGLGLPATLVSALIGGSNAQGVIPGIPWNPDSEKPALEAVQAAGWTPISASTLGYTARSMHAAPTLAKNSATARRRPRCWASTMTLATAGNRHQFPRHFRASGKCDHRLHRRCDQRPARRLRAQGLCQELRGGGFWRVAQRLADTPLPGLGGNDVVVSGHSLGGMAVNSMADLSDSTWSGFYKDANYLAYASPTQSAGDKVLNVGYENDPVFRALDGSSFNLSSLGVHDKAHESSTDNIVSLNDHYASSLWNVLPFSILNLPTWVSHLPTGYGDGMTRILDSGFYEQMTRDSTVIVANLSDPARATTWVQDLNRNAEAHKGNTFIIGSDGDDFIKGGRGADFIEGGKGNDTIRDSSGHNTFLFSGQFGNDRVIGYQATDKLVFNDVAGSTDYRDHVKVVGGDTVIGFGTDSVTLVGVSSLSGEGIVIS	1999.0	Spectrophotometry	 Impranil DLN		No	No			USA	No		
Agromyces sp. 	51513	Nylon	Yasuhira, K., Uedo, Y., Takeo, M., Kato, D. I., & Negoro, S. (2007). Genetic organization of nylon-oligomer-degrading enzymes from alkalophilic bacterium, Agromyces sp. KY5R. Journal of bioscience and bioengineering, 104(6), 521-524.	Nylon hydrolase	00045	00045 | Nylon hydrolase | Agromyces sp. | Nylon	Yes	BAE97622.2	MNTTPVHALTDIDGGIAVDPAPRLAGPPVFGGPGNDAFDLAPVRSTGREMLRFDFPGVSIGAAHYEEGPTGATVIHIPAGARTAVDARGGAVGLSGGYDFNHAICLAGGASYGLEAGAGVSGALLERLEYRTGFAEAQLVSSAVIYDFSARSTAVYPDKALGRAALEFAVPGEFPQGRAGAGMSASAGKVDWDRTEITGQGAAFRRLGDVRILAVVVPNPVGVIMDRAGTVVRGNYDAQTGVRRHPVFDYQEAFAEQVPPVTEAGNTTISAIVTNVRMSPVELNQFAKQVHSSMHRGIQPFHTDMDGDTLFAVTTDEIDLPTTPGSSRGRLSVNATALGAIASEVMWDAVLEAGK	2007.0	Spectrophotometry				No	Sludge	Sewage/Sludge	Japan	No		
Agromyces sp.	51513	Nylon	Negoro, S., Shibata, N., Tanaka, Y., Yasuhira, K., Shibata, H., Hashimoto, H., ... & Goto, Y. (2012). Three-dimensional structure of nylon hydrolase and mechanism of nylon-6 hydrolysis. Journal of Biological Chemistry, 287(7), 5079-5090.	Nylon hydrolase	00045	00045 | Nylon hydrolase | Agromyces sp. | Nylon	Yes	BAE97622.2	MNTTPVHALTDIDGGIAVDPAPRLAGPPVFGGPGNDAFDLAPVRSTGREMLRFDFPGVSIGAAHYEEGPTGATVIHIPAGARTAVDARGGAVGLSGGYDFNHAICLAGGASYGLEAGAGVSGALLERLEYRTGFAEAQLVSSAVIYDFSARSTAVYPDKALGRAALEFAVPGEFPQGRAGAGMSASAGKVDWDRTEITGQGAAFRRLGDVRILAVVVPNPVGVIMDRAGTVVRGNYDAQTGVRRHPVFDYQEAFAEQVPPVTEAGNTTISAIVTNVRMSPVELNQFAKQVHSSMHRGIQPFHTDMDGDTLFAVTTDEIDLPTTPGSSRGRLSVNATALGAIASEVMWDAVLEAGK	2012.0	MS;TLC	Nylon-6 that was mechanically disintegrated to a powder was a generous gift from Toyobo Co. (Tsuruga, Japan).	Toyobo		No	Sludge	Sewage/Sludge	Japan	Yes		
Parengyodontium album	37998	PLA	Yamashita, K., Kikkawa, Y., Kurokawa, K., & Doi, Y. (2005). Enzymatic degradation of poly (L-lactide) film by proteinase K: quartz crystal microbalance and atomic force microscopy study. Biomacromolecules, 6(2), 850-857.	Protease	00040	00040 | Protease | Parengyodontium album | PLA	Yes	P06873	MRLSVLLSLLPLALGAPAVEQRSEAAPLIEARGEMVANKYIVKFKEGSALSALDAAMEKISGKPDHVYKNVFSGFAATLDENMVRVLRAHPDVEYIEQDAVVTINAAQTNAPWGLARISSTSPGTSTYYYDESAGQGSCVYVIDTGIEASHPEFEGRAQMVKTYYYSSRDGNGHGTHCAGTVGSRTYGVAKKTQLFGVKVLDDNGSGQYSTIIAGMDFVASDKNNRNCPKGVVASLSLGGGYSSSVNSAAARLQSSGVMVAVAAGNNNADARNYSPASEPSVCTVGASDRYDRRSSFSNYGSVLDIFGPGTSILSTWIGGSTRSISGTSMATPHVAGLAAYLMTLGKTTAASACRYIADTANKGDLSNIPFGTVNLLAYNNYQA	2005.0	QCM;AFM	PLLA purchased from Polyscience Inc. was purified by reprecipitation with methanol from chloroform solution and dried in vacuo. The number-average molecular weight (Mn) and polydispersity (Mw/Mn) were evaluated to be 410 000 and 1.7, respectively, by gel permeation chromatography (GPC) with polystyrene standards.	Polyscience Inc						Yes		
Paucimonas lemoignei	29443	PHB	Jendrossek, D., Hermawan, S., Subedi, B., & Papageorgiou, A. C. (2013). Biochemical analysis and structure determination of P aucimonas lemoignei poly (3‐hydroxybutyrate)(PHB) depolymerase PhaZ 7 muteins reveal the PHB binding site and details of substrate–enzyme interactions. Molecular microbiology, 90(3), 649-664.	PHB depolymerase	00063	00063 | PHB depolymerase | Paucimonas lemoignei | PHB PHA	Yes	Q939Q9	MISKLMGAQRFLPAVAATVTSLVWGLAGTLVAPGEAQALTCGTNSGFVCKGTQTQYAGGFAPGVGYGGFGGGSCTATKTPVIFIHGNGDNAISFDMPPGNVSGYGTPARSVYAELKARGYNDCEIFGVTYLSSSEQGSAQYNYHSSTKYAIIKTFIDKVKAYTGKSQVDIVAHSMGVSMSLATLQYYNNWTSVRKFINLAGGIRGLYSCYYTGYANAAAPTCGSQNYYNSYTFGFFPEGWYYGVWVSNPWTGSGSTNSMRDMPAKRTAVSFYTLSAGFKDQVGCATASFWAGCDSAAKFASTTSNVKAQINVGAGSNATQADYDWADGMPYNAGGGDTTNGVGHFRTKTNTGAIIQRMLLTTCTGLDCAAEYTTGPKAAY	2013.0	Spectrometry				No				Yes		
Paucimonas lemoignei	29443	PHA	Jendrossek, D., Hermawan, S., Subedi, B., & Papageorgiou, A. C. (2013). Biochemical analysis and structure determination of P aucimonas lemoignei poly (3‐hydroxybutyrate)(PHB) depolymerase PhaZ 7 muteins reveal the PHB binding site and details of substrate–enzyme interactions. Molecular microbiology, 90(3), 649-664.	PHB depolymerase	00063	00063 | PHB depolymerase | Paucimonas lemoignei | PHB PHA	Yes	Q939Q9	MISKLMGAQRFLPAVAATVTSLVWGLAGTLVAPGEAQALTCGTNSGFVCKGTQTQYAGGFAPGVGYGGFGGGSCTATKTPVIFIHGNGDNAISFDMPPGNVSGYGTPARSVYAELKARGYNDCEIFGVTYLSSSEQGSAQYNYHSSTKYAIIKTFIDKVKAYTGKSQVDIVAHSMGVSMSLATLQYYNNWTSVRKFINLAGGIRGLYSCYYTGYANAAAPTCGSQNYYNSYTFGFFPEGWYYGVWVSNPWTGSGSTNSMRDMPAKRTAVSFYTLSAGFKDQVGCATASFWAGCDSAAKFASTTSNVKAQINVGAGSNATQADYDWADGMPYNAGGGDTTNGVGHFRTKTNTGAIIQRMLLTTCTGLDCAAEYTTGPKAAY	2013.0	Spectrometry				No				Yes		
Delftia acidovorans	80866	PHB	Kasuya, K. I., Inoue, Y., Tanaka, T., Akehata, T., Iwata, T., Fukui, T., & Doi, Y. (1997). Biochemical and molecular characterization of the polyhydroxybutyrate depolymerase of Comamonas acidovorans YM1609, isolated from freshwater. Applied and Environmental Microbiology, 63(12), 4844-4852.	PHB depolymerase	00112	00112 | PHB depolymerase | Delftia acidovorans | PHB PHA	Yes	KFJ10595.1	MLKREEMVSSIPATPWRWAFTALAAAALAACGSGEHEPSNDLPKGFTELGATVYPATATGTGATAATQDLLTGGLGKTGLGAAAAPLYADPANPTAAELRRNALYSNYRGILDPTAGGGYGTLYGPNITANGQVTAGEGLIPGREYLAVLDDGTGRKQTMVAVQVPDSFDRNRPCIVLGPSSGSRGVYGAIGTAGEWGLKKGCAVALTDAGKGVGLHNLSDDTVNKLDGTRATRTDAGSLSFFAARLTDAARAAYNAAFPNRIAIKHAHSQQNPEKDWGNDTLAAARYALYVLNARYGTTQDPVPFGKDNTLVLAGSASNGGAAVLRAAELDADGLIDGVVASEPVTEMPTRQGYTIAVGNATMPNPGRTLAEYTTYGNIYQPCAALAPDAALTETSIFNYIGLTAMTARAEARCTSLAAKGLVIGATTADRAANALSKLRLYGWTRDHDRMHNAHYALGNGPILSAMYTMAYGRFGVDANLCRTSFAAANATGDVVPATGAALAQSFATANGTANGTPATVVYNDSVGGAKAWQFAVSPSTRVADLGLDNALCQHALVTGFDPVTGFNLSESSVPTRAQSDAVRAGIAEVLHTAKLRGKPTIIVAGRSDALVPVNHNARAYTVLNRGLDGSNTRLRYIEVVNAQHFDAFLPFSGFDTRFVPLHPYFNQAMDAVWANLRSSTALPASQVVRTTPRGGQPGAAPAITAAQVPPFVARPSTANTIEVSDGLIRIPE	1997.0	Spectrophotometry;HPLC	P(3HB) was produced by Ralstonia eutropha			No	Freshwater	River/Lake	Japan	No		
Delftia acidovorans	80866	PHA	Kasuya, K. I., Inoue, Y., Tanaka, T., Akehata, T., Iwata, T., Fukui, T., & Doi, Y. (1997). Biochemical and molecular characterization of the polyhydroxybutyrate depolymerase of Comamonas acidovorans YM1609, isolated from freshwater. Applied and Environmental Microbiology, 63(12), 4844-4852.	PHB depolymerase	00112	00112 | PHB depolymerase | Delftia acidovorans | PHB PHA	Yes	KFJ10595.1	MLKREEMVSSIPATPWRWAFTALAAAALAACGSGEHEPSNDLPKGFTELGATVYPATATGTGATAATQDLLTGGLGKTGLGAAAAPLYADPANPTAAELRRNALYSNYRGILDPTAGGGYGTLYGPNITANGQVTAGEGLIPGREYLAVLDDGTGRKQTMVAVQVPDSFDRNRPCIVLGPSSGSRGVYGAIGTAGEWGLKKGCAVALTDAGKGVGLHNLSDDTVNKLDGTRATRTDAGSLSFFAARLTDAARAAYNAAFPNRIAIKHAHSQQNPEKDWGNDTLAAARYALYVLNARYGTTQDPVPFGKDNTLVLAGSASNGGAAVLRAAELDADGLIDGVVASEPVTEMPTRQGYTIAVGNATMPNPGRTLAEYTTYGNIYQPCAALAPDAALTETSIFNYIGLTAMTARAEARCTSLAAKGLVIGATTADRAANALSKLRLYGWTRDHDRMHNAHYALGNGPILSAMYTMAYGRFGVDANLCRTSFAAANATGDVVPATGAALAQSFATANGTANGTPATVVYNDSVGGAKAWQFAVSPSTRVADLGLDNALCQHALVTGFDPVTGFNLSESSVPTRAQSDAVRAGIAEVLHTAKLRGKPTIIVAGRSDALVPVNHNARAYTVLNRGLDGSNTRLRYIEVVNAQHFDAFLPFSGFDTRFVPLHPYFNQAMDAVWANLRSSTALPASQVVRTTPRGGQPGAAPAITAAQVPPFVARPSTANTIEVSDGLIRIPE	1997.0	Spectrophotometry;HPLC	P(3HB) was produced by Ralstonia eutropha			No	Freshwater	River/Lake	Japan	No		
Pseudomonas sp.	306	Nylon	Kanagawa, K. A. Z. U. O., Negoro, S. E. I. J. I., Takada, N. O. B. U. O., & Okada, H. I. R. O. S. U. K. E. (1989). Plasmid dependence of Pseudomonas sp. strain NK87 enzymes that degrade 6-aminohexanoate-cyclic dimer. Journal of bacteriology, 171(6), 3181-3186.	Hydrolase	00065	00065 | Hydrolase | Pseudomonas sp. | Nylon	Yes	P13397	MSKVDLWQDATAQAELVRSGEISRTELLEATIAHVQAVNPEINAVIIPLFEKARRESELASGPFAGVPYLLKDLTVVSQGDINTSSIKGMKESGYRADHDAYFVQRMRAAGFVLLGKVNTPEMGTQVTTEPEAWGATRNPWNLGRSVGGSSGGSGAAVAAALSPVAHGNDAAGSVRIPASVCGVVGLKPTRGRISPGPLVTDSDNVAGAAHEGLFARSVRDIAALLDVVSGHRPGDTFCAPTASRPYAQGISENPGSLRVGVLTHNPVGDFALDPECAAAARGAAAALAALGHDVNDAYPEALGDRSFLKDYLTICDVAIAREIERNGELIGRPLTEDDVEWTSWEMVKRADQVTGRAFAACVDELRYYAGKVERWWEAGWDLLILPTVTRQTPEIGELMLAKGTDLEGRHTALISGSLRMLAFTVPFNVSGQPAISLPIGMSSDGMPIGVQIVAAYGREDLLLQVAAQLEGALPWVARRPQLLNPSRKIPAA	1989.0	Paper chromatography			Yes	No	Wastewater	Plastic waste dumping site	Japan	No		
Lederbergia lenta	1467	PLA	Oda, Y., Yonetsu, A., Urakami, T., & Tonomura, K. (2000). Degradation of polylactide by commercial proteases. Journal of Polymers and the Environment, 8(1), 29-32.	Protease	00152	00152 | Protease | Lederbergia lenta | PLA	Yes	P29600	AQSVPWGISRVQAPAAHNRGLTGSGVKVAVLDTGISTHPDLNIRGGASFVPGEPSTQDGNGHGTHVAGTIAALNNSIGVLGVAPSAELYAVKVLGASGSGSVSSIAQGLEWAGNNGMHVANLSLGSPSPSATLEQAVNSATSRGVLVVAASGNSGAGSISYPARYANAMAVGATDQNNNRASFSQYGAGLDIVAPGVNVQSTYPGSTYASLNGTSMATPHVAGAAALVKQKNPSWSNVQIRNHLKNTATSLGSTNLYGSGLVNAEAATR	2000.0	HPLC	Polylactide, Lacty 1012, with an average molecular weight of 233,000	Shimadzu Co	Yes	No				Yes		
Lederbergia lenta	1467	PLA	Oda, Y., Yonetsu, A., Urakami, T., & Tonomura, K. (2000). Degradation of polylactide by commercial proteases. Journal of Polymers and the Environment, 8(1), 29-32.	Protease	00153	00153 | Protease | Lederbergia lenta | PLA	Yes	P29599	AQSVPWGISRVQAPAAHNRGLTGSGVKVAVLDTGISTHPDLNIRGGASFVPGEPSTQDGNGHGTHVAGTIAALNNSIGVLGVAPSAELYAVKVLGADGRGAISSIAQGLEWAGNNGMHVANLSLGSPSPSATLEQAVNSATSRGVLVVAASGNSGASSISYPARYANAMAVGATDQNNNRASFSQYGAGLDIVAPGVNVQSTYPGSTYASLNGTSMATPHVAGAAALVKQKNPSWSNVQIRNHLKNTATSLGSTNLYGSGLVNAEAATR	2000.0	HPLC	Polylactide, Lacty 1012, with an average molecular weight of 233,000	Shimadzu Co	Yes	No				Yes		
Bacillus licheniformis	1402	PLA	Oda, Y., Yonetsu, A., Urakami, T., & Tonomura, K. (2000). Degradation of polylactide by commercial proteases. Journal of Polymers and the Environment, 8(1), 29-32.	Protease	00154	00154 | Protease | Bacillus licheniformis | PLA	Yes	P00780	MMRKKSFWLGMLTAFMLVFTMAFSDSASAAQPAKNVEKDYIVGFKSGVKTASVKKDIIKESGGKVDKQFRIINAAKAKLDKEALKEVKNDPDVAYVEEDHVAHALAQTVPYGIPLIKADKVQAQGFKGANVKVAVLDTGIQASHPDLNVVGGASFVAGEAYNTDGNGHGTHVAGTVAALDNTTGVLGVAPSVSLYAVKVLNSSGSGSYSGIVSGIEWATTNGMDVINMSLGGASGSTAMKQAVDNAYAKGVVVVAAAGNSGSSGNTNTIGYPAKYDSVIAVGAVDSNSNRASFSSVGAELEVMAPGAGVYSTYPTNTYATLNGTSMASPHVAGAAALILSKHPNLSASQVRNRLSSTATYLGSSFYYGKGLINVEAAAQ	2000.0	HPLC	Polylactide, Lacty 1012, with an average molecular weight of 233,000	Shimadzu Co	Yes	No				Yes		
Alcanivorax borkumensis	59754	PLA	Tchigvintsev, A., Tran, H., Popovic, A., Kovacic, F., Brown, G., Flick, R., ... & Yakunin, A. F. (2015). The environment shapes microbial enzymes: five cold-active and salt-resistant carboxylesterases from marine metagenomes. Applied microbiology and biotechnology, 99(5), 2165-2178.	Esterase	00155	00155 | Esterase | Alcanivorax borkumensis | PLA PCL PBSA	Yes	CAL16645.1	MQLKHLFLFIVCSFFLSGCEDITNWAYEKGLAMEKNRAGLKDQILTTADGITWHILTSETSAEPIAEKEAVLLIHGFSADSSNWVRFANELEGDFFFIVPDLPGHGETTRNLDLTYTMSAQATRLLTLMDALQIQHFHVAGNSMGGAISLALAQQAPQRVLSIGLIDSAGLTRQTEGFKTILADSNSNPLIPHTAEQFQATLQWAMEEPPYLPSFVVDIMGKKKAANAAVAEKVWRDLLEDPGMMLEDKNVLPSIQIPTLVLWGREDRLLGVDNVGAFLEELPQSRAIVLDGIGHVPMAEAPGKSADAFRAFWREVRP	2015.0	Clear zone	poly (DL-lactide) (average M.w. 2,000)	PolySciTech, USA	Yes	No				Yes		
Alcanivorax borkumensis	59754	PCL	Tchigvintsev, A., Tran, H., Popovic, A., Kovacic, F., Brown, G., Flick, R., ... & Yakunin, A. F. (2015). The environment shapes microbial enzymes: five cold-active and salt-resistant carboxylesterases from marine metagenomes. Applied microbiology and biotechnology, 99(5), 2165-2178.	Esterase	00155	00155 | Esterase | Alcanivorax borkumensis | PLA PCL PBSA	Yes	CAL16645.1	MQLKHLFLFIVCSFFLSGCEDITNWAYEKGLAMEKNRAGLKDQILTTADGITWHILTSETSAEPIAEKEAVLLIHGFSADSSNWVRFANELEGDFFFIVPDLPGHGETTRNLDLTYTMSAQATRLLTLMDALQIQHFHVAGNSMGGAISLALAQQAPQRVLSIGLIDSAGLTRQTEGFKTILADSNSNPLIPHTAEQFQATLQWAMEEPPYLPSFVVDIMGKKKAANAAVAEKVWRDLLEDPGMMLEDKNVLPSIQIPTLVLWGREDRLLGVDNVGAFLEELPQSRAIVLDGIGHVPMAEAPGKSADAFRAFWREVRP	2015.0	Clear zone				No				Yes		
Alcanivorax borkumensis	59754	PBSA	Tchigvintsev, A., Tran, H., Popovic, A., Kovacic, F., Brown, G., Flick, R., ... & Yakunin, A. F. (2015). The environment shapes microbial enzymes: five cold-active and salt-resistant carboxylesterases from marine metagenomes. Applied microbiology and biotechnology, 99(5), 2165-2178.	Esterase	00155	00155 | Esterase | Alcanivorax borkumensis | PLA PCL PBSA	Yes	CAL16645.1	MQLKHLFLFIVCSFFLSGCEDITNWAYEKGLAMEKNRAGLKDQILTTADGITWHILTSETSAEPIAEKEAVLLIHGFSADSSNWVRFANELEGDFFFIVPDLPGHGETTRNLDLTYTMSAQATRLLTLMDALQIQHFHVAGNSMGGAISLALAQQAPQRVLSIGLIDSAGLTRQTEGFKTILADSNSNPLIPHTAEQFQATLQWAMEEPPYLPSFVVDIMGKKKAANAAVAEKVWRDLLEDPGMMLEDKNVLPSIQIPTLVLWGREDRLLGVDNVGAFLEELPQSRAIVLDGIGHVPMAEAPGKSADAFRAFWREVRP	2015.0	Clear zone				No				Yes		
Uncultured bacterium	77133	PLA	Tchigvintsev, A., Tran, H., Popovic, A., Kovacic, F., Brown, G., Flick, R., ... & Yakunin, A. F. (2015). The environment shapes microbial enzymes: five cold-active and salt-resistant carboxylesterases from marine metagenomes. Applied microbiology and biotechnology, 99(5), 2165-2178.	Esterase	00156	00156 | Esterase | Uncultured bacterium | PLA PCL PBSA	Yes	AGT96415.1	MELNSMQFLLGLIGLLLLIVTSLRRWLLRRESPQKQAVDFHGELYQVGSAVIARSRADAPAGSVIVMHGFVENFLYFTEHYADPDIQLIMLTSADYHLPVNQPRFTKADWIKIPGQRPGTIAYDAAVLNQALEHLATGTQIRVHGHSRGGAVTLEAARQRPDLFARVEVILEAPVLPQGKPYKAVSPLARWFAPFYLFAWQQQPISPANAKVFGPLDNPRKRELIMALPFNPRYGRTFVNNIKDLADWMDSTGTDIYQHVKFGAILVPSHDLILNASAMLQSAQQAESLQIIEVEGCSHLITADRPDSIPPLPG	2015.0	Clear zone	poly (DL-lactide) (average M.w. 2,000)	PolySciTech, USA	Yes	No				Yes		
Uncultured bacterium	77133	PCL	Tchigvintsev, A., Tran, H., Popovic, A., Kovacic, F., Brown, G., Flick, R., ... & Yakunin, A. F. (2015). The environment shapes microbial enzymes: five cold-active and salt-resistant carboxylesterases from marine metagenomes. Applied microbiology and biotechnology, 99(5), 2165-2178.	Esterase	00156	00156 | Esterase | Uncultured bacterium | PLA PCL PBSA	Yes	AGT96415.1	MELNSMQFLLGLIGLLLLIVTSLRRWLLRRESPQKQAVDFHGELYQVGSAVIARSRADAPAGSVIVMHGFVENFLYFTEHYADPDIQLIMLTSADYHLPVNQPRFTKADWIKIPGQRPGTIAYDAAVLNQALEHLATGTQIRVHGHSRGGAVTLEAARQRPDLFARVEVILEAPVLPQGKPYKAVSPLARWFAPFYLFAWQQQPISPANAKVFGPLDNPRKRELIMALPFNPRYGRTFVNNIKDLADWMDSTGTDIYQHVKFGAILVPSHDLILNASAMLQSAQQAESLQIIEVEGCSHLITADRPDSIPPLPG	2015.0	Clear zone				No				Yes		
Uncultured bacterium	77133	PBSA	Tchigvintsev, A., Tran, H., Popovic, A., Kovacic, F., Brown, G., Flick, R., ... & Yakunin, A. F. (2015). The environment shapes microbial enzymes: five cold-active and salt-resistant carboxylesterases from marine metagenomes. Applied microbiology and biotechnology, 99(5), 2165-2178.	Esterase	00156	00156 | Esterase | Uncultured bacterium | PLA PCL PBSA	Yes	AGT96415.1	MELNSMQFLLGLIGLLLLIVTSLRRWLLRRESPQKQAVDFHGELYQVGSAVIARSRADAPAGSVIVMHGFVENFLYFTEHYADPDIQLIMLTSADYHLPVNQPRFTKADWIKIPGQRPGTIAYDAAVLNQALEHLATGTQIRVHGHSRGGAVTLEAARQRPDLFARVEVILEAPVLPQGKPYKAVSPLARWFAPFYLFAWQQQPISPANAKVFGPLDNPRKRELIMALPFNPRYGRTFVNNIKDLADWMDSTGTDIYQHVKFGAILVPSHDLILNASAMLQSAQQAESLQIIEVEGCSHLITADRPDSIPPLPG	2015.0	Clear zone				No				Yes		
Alcanivorax borkumensis	59754	PLA	Tchigvintsev, A., Tran, H., Popovic, A., Kovacic, F., Brown, G., Flick, R., ... & Yakunin, A. F. (2015). The environment shapes microbial enzymes: five cold-active and salt-resistant carboxylesterases from marine metagenomes. Applied microbiology and biotechnology, 99(5), 2165-2178.	Esterase	00157	00157 | Esterase | Alcanivorax borkumensis | PLA PBSA	Yes	CAL16699.1	MTAIIRQGRYQGLSSKGVTEYRGIPFAKAPLGEWRFKAPQPLPDSEDCVNADRYPLASLQPRNPIMGIQESGEDCLYLNIWAPEGEGPFPVMVWFHGGGYMAGSTSQALYNGAELARSQKVVVVNAAYRLGAMGFADFSAVAPELDADTNLGLRDQLAALQWVQENIAAFAGDDKQVTIFGESAGGFSVCSLLACPQADELFQAAIVQSGGADFVLAPDQVRKVTNAFVAALPGDGSAAEKLLSADNKGWIKAQNAAVKVLVDRGLRTTTPQFAMNFLPMVDGDVLPQLPVDAIAAGAAANKRVMAGVCRDEFNFFQYAGVLAGTTTMDALREISDEEIVSRFERALPGNGRRAFDYYQTAVEPDARRSRLDWLAAMESDRLFRVPTVRLLDAQSQHAQCWGFQFTWPSEPFGVPLGACHVVDVPFVFGVTDTPAGMYFTGGTSEARALSHQVQAAWGTFARGDAPGWNAWQSDRQVCQLGPGETMASLLDESGEQLWRDIIPVV	2015.0	Clear zone	poly (DL-lactide) (average M.w. 2,000)	PolySciTech, USA	Yes	No				Yes		
Alcanivorax borkumensis	59754	PBSA	Tchigvintsev, A., Tran, H., Popovic, A., Kovacic, F., Brown, G., Flick, R., ... & Yakunin, A. F. (2015). The environment shapes microbial enzymes: five cold-active and salt-resistant carboxylesterases from marine metagenomes. Applied microbiology and biotechnology, 99(5), 2165-2178.	Esterase	00157	00157 | Esterase | Alcanivorax borkumensis | PLA PBSA	Yes	CAL16699.1	MTAIIRQGRYQGLSSKGVTEYRGIPFAKAPLGEWRFKAPQPLPDSEDCVNADRYPLASLQPRNPIMGIQESGEDCLYLNIWAPEGEGPFPVMVWFHGGGYMAGSTSQALYNGAELARSQKVVVVNAAYRLGAMGFADFSAVAPELDADTNLGLRDQLAALQWVQENIAAFAGDDKQVTIFGESAGGFSVCSLLACPQADELFQAAIVQSGGADFVLAPDQVRKVTNAFVAALPGDGSAAEKLLSADNKGWIKAQNAAVKVLVDRGLRTTTPQFAMNFLPMVDGDVLPQLPVDAIAAGAAANKRVMAGVCRDEFNFFQYAGVLAGTTTMDALREISDEEIVSRFERALPGNGRRAFDYYQTAVEPDARRSRLDWLAAMESDRLFRVPTVRLLDAQSQHAQCWGFQFTWPSEPFGVPLGACHVVDVPFVFGVTDTPAGMYFTGGTSEARALSHQVQAAWGTFARGDAPGWNAWQSDRQVCQLGPGETMASLLDESGEQLWRDIIPVV	2015.0	Clear zone				No				Yes		
Uncultured bacterium	77133	PLA	Tchigvintsev, A., Tran, H., Popovic, A., Kovacic, F., Brown, G., Flick, R., ... & Yakunin, A. F. (2015). The environment shapes microbial enzymes: five cold-active and salt-resistant carboxylesterases from marine metagenomes. Applied microbiology and biotechnology, 99(5), 2165-2178.	Esterase	00158	00158 | Esterase | Uncultured bacterium | PLA	Yes	AHG30919.1	MNAKTPFTTPEDVGLSSTRLARLPAHFGEYVKRGKLAGVSTLVSRAGKIAHFETVGERDRENGLAMEKDTIFRIYSMSKPITSVALMMLYEEGRFQLSHEVARYIPSFANLKVWDGGTSDEYKTKPCERPMTIRDLLTHTSGLTYGFMHAHPVDKIYRKRGIDGAATANGMNLEVFCDALSEIPLLFSPGTQWSYSVATDVCGRLVEILSGQSLDVFFQSRIFDPLGMVDTGFVVPKDKLTRFAANYEKDPRTREVRLFDTSDETSTYASAKPFLSGGGGLVSTMVDYWRFCQMFLNGGELEGVRLLSRKTVDYMTLNHLPGGKTMPEMDQSAFSETGSEGTGFGLGFSVIIDEADAQAVTSAGNHSWGGAASTYFWIDPEEDLIGILMTQLMPSRAYPLRPQMQQLVYGAIED	2015.0	Clear zone	poly (DL-lactide) (average M.w. 2,000)	PolySciTech, USA	Yes	No				Yes		
Uncultured bacterium	77133	PLA	Tchigvintsev, A., Tran, H., Popovic, A., Kovacic, F., Brown, G., Flick, R., ... & Yakunin, A. F. (2015). The environment shapes microbial enzymes: five cold-active and salt-resistant carboxylesterases from marine metagenomes. Applied microbiology and biotechnology, 99(5), 2165-2178.	Esterase	00159	00159 | Esterase | Uncultured bacterium | PLA	Yes	AGT96414.1	MSNVQGYFDPRFERVRELFAEQQQDEQARGAALCVTVGGDTVLDLWQGVTDKENQQVWEQDTLVNVFSCTKPLGAVALLQQVAAGRIELDAPLAEVWPEFAQAGKQDITLRQVLSHRSGLSAIAKALPPEALFDWSTMSAALAEQAPWWEPGTAHGYAPVTYAWLLGEPLSRLTNESPGNYIQQHICAPLGMDFHVGVPDKDLARIAHVSRLRNQSGDEGARKLFAAMGEPEGLTAKAFGNPVSMMTSTNKREWQQAEILSANGTGNARSLARFWQLLAHGGELDGVKLLDSELVSLMQQEHSQGQDRTLLCPTRFGLGVMLEQDAPGGGFGMGPQAFGHPGAGGSLGFCDPEAKVGFGYVTNTMGPYVLMDPRALALSQAVHDCLRELD	2015.0	Clear zone	poly (DL-lactide) (average M.w. 2,000)	PolySciTech, USA	Yes	No				Yes		
Moraxella sp.	479	PET	Blázquez-Sánchez, P., Engelberger, F., Cifuentes-Anticevic, J., Sonnendecker, C., Griñén, A., Reyes, J., ... & Ramírez-Sarmiento, C. A. (2021). Antarctic polyester hydrolases degrade aliphatic and aromatic polyesters at moderate temperatures. Applied and Environmental Microbiology, 88(1), e01842-21.	Polyester hydrolase	00124	00124 | Polyester hydrolase | Moraxella sp. | PET PCL PU PHB PBS PLA PHA	Yes	P19833	MFIMIKKSELAKAIIVTGALVFSIPTLAEVTLSETTVSSIKSEATVSSTKKALPATPSDCIADSKITAVALSDTRDNGPFSIRTKRISRQSAKGFGGGTIHYPTNASGCGLLGAIAVVPGYVSYENSIKWWGPRLASWGFVVITINTNSIYDDPDSRAAQLNAALDNMIADDTVGSMIDPKRLGAIGWSMGGGGALKLATERSTVRAIMPLAPYHDKSYGEVKTPTLVIACEDDRIAETKKYANAFYKNAIGPKMKVEVNNGSHFCPSYRFNEILLSKPGIAWMQRYINNDTRFDKFLCANENYSKSPRISAYDYKDCP	2021.0	Weight loss	Amorphous PET films with a size of 0.5 cm _x0001_ 3 cm (;45 mg) (250 mm thickness; product number ES301445	Goodfellow Co	Yes	No				Yes		
Moraxella sp.	479	PCL	Blázquez-Sánchez, P., Engelberger, F., Cifuentes-Anticevic, J., Sonnendecker, C., Griñén, A., Reyes, J., ... & Ramírez-Sarmiento, C. A. (2021). Antarctic polyester hydrolases degrade aliphatic and aromatic polyesters at moderate temperatures. Applied and Environmental Microbiology, 88(1), e01842-21.	Polyester hydrolase	00124	00124 | Polyester hydrolase | Moraxella sp. | PET PCL PU PHB PBS PLA PHA	Yes	P19833	MFIMIKKSELAKAIIVTGALVFSIPTLAEVTLSETTVSSIKSEATVSSTKKALPATPSDCIADSKITAVALSDTRDNGPFSIRTKRISRQSAKGFGGGTIHYPTNASGCGLLGAIAVVPGYVSYENSIKWWGPRLASWGFVVITINTNSIYDDPDSRAAQLNAALDNMIADDTVGSMIDPKRLGAIGWSMGGGGALKLATERSTVRAIMPLAPYHDKSYGEVKTPTLVIACEDDRIAETKKYANAFYKNAIGPKMKVEVNNGSHFCPSYRFNEILLSKPGIAWMQRYINNDTRFDKFLCANENYSKSPRISAYDYKDCP	2021.0	Clear zone			Yes	No				Yes		
Moraxella sp.	479	PET	Nikolaivits, E., Taxeidis, G., Gkountela, C., Vouyiouka, S., Maslak, V., Nikodinovic-Runic, J., & Topakas, E. (2022). A polyesterase from the Antarctic bacterium Moraxella sp. degrades highly crystalline synthetic polymers. Journal of Hazardous Materials, 434, 128900.	Polyester hydrolase	00124	00124 | Polyester hydrolase | Moraxella sp. | PET PCL PU PHB PBS PLA PHA	Yes	P19833	MFIMIKKSELAKAIIVTGALVFSIPTLAEVTLSETTVSSIKSEATVSSTKKALPATPSDCIADSKITAVALSDTRDNGPFSIRTKRISRQSAKGFGGGTIHYPTNASGCGLLGAIAVVPGYVSYENSIKWWGPRLASWGFVVITINTNSIYDDPDSRAAQLNAALDNMIADDTVGSMIDPKRLGAIGWSMGGGGALKLATERSTVRAIMPLAPYHDKSYGEVKTPTLVIACEDDRIAETKKYANAFYKNAIGPKMKVEVNNGSHFCPSYRFNEILLSKPGIAWMQRYINNDTRFDKFLCANENYSKSPRISAYDYKDCP	2022.0	Weight loss;GPC;HPLC	PET (PAPET clear)	Lotte Chemical, UK	Yes	No				Yes		
Moraxella sp.	479	PU	Nikolaivits, E., Taxeidis, G., Gkountela, C., Vouyiouka, S., Maslak, V., Nikodinovic-Runic, J., & Topakas, E. (2022). A polyesterase from the Antarctic bacterium Moraxella sp. degrades highly crystalline synthetic polymers. Journal of Hazardous Materials, 434, 128900.	Polyester hydrolase	00124	00124 | Polyester hydrolase | Moraxella sp. | PET PCL PU PHB PBS PLA PHA	Yes	P19833	MFIMIKKSELAKAIIVTGALVFSIPTLAEVTLSETTVSSIKSEATVSSTKKALPATPSDCIADSKITAVALSDTRDNGPFSIRTKRISRQSAKGFGGGTIHYPTNASGCGLLGAIAVVPGYVSYENSIKWWGPRLASWGFVVITINTNSIYDDPDSRAAQLNAALDNMIADDTVGSMIDPKRLGAIGWSMGGGGALKLATERSTVRAIMPLAPYHDKSYGEVKTPTLVIACEDDRIAETKKYANAFYKNAIGPKMKVEVNNGSHFCPSYRFNEILLSKPGIAWMQRYINNDTRFDKFLCANENYSKSPRISAYDYKDCP	2022.0	Weight loss;GPC	LPR7560	Coim, Laripur	Yes	No				Yes		
Moraxella sp.	479	PCL	Nikolaivits, E., Taxeidis, G., Gkountela, C., Vouyiouka, S., Maslak, V., Nikodinovic-Runic, J., & Topakas, E. (2022). A polyesterase from the Antarctic bacterium Moraxella sp. degrades highly crystalline synthetic polymers. Journal of Hazardous Materials, 434, 128900.	Polyester hydrolase	00124	00124 | Polyester hydrolase | Moraxella sp. | PET PCL PU PHB PBS PLA PHA	Yes	P19833	MFIMIKKSELAKAIIVTGALVFSIPTLAEVTLSETTVSSIKSEATVSSTKKALPATPSDCIADSKITAVALSDTRDNGPFSIRTKRISRQSAKGFGGGTIHYPTNASGCGLLGAIAVVPGYVSYENSIKWWGPRLASWGFVVITINTNSIYDDPDSRAAQLNAALDNMIADDTVGSMIDPKRLGAIGWSMGGGGALKLATERSTVRAIMPLAPYHDKSYGEVKTPTLVIACEDDRIAETKKYANAFYKNAIGPKMKVEVNNGSHFCPSYRFNEILLSKPGIAWMQRYINNDTRFDKFLCANENYSKSPRISAYDYKDCP	2022.0	Weight loss;GPC	CAPA 6500	Ravago Chemicals, Belgium	Yes	No				Yes		
Moraxella sp.	479	PHB	Nikolaivits, E., Taxeidis, G., Gkountela, C., Vouyiouka, S., Maslak, V., Nikodinovic-Runic, J., & Topakas, E. (2022). A polyesterase from the Antarctic bacterium Moraxella sp. degrades highly crystalline synthetic polymers. Journal of Hazardous Materials, 434, 128900.	Polyester hydrolase	00124	00124 | Polyester hydrolase | Moraxella sp. | PET PCL PU PHB PBS PLA PHA	Yes	P19833	MFIMIKKSELAKAIIVTGALVFSIPTLAEVTLSETTVSSIKSEATVSSTKKALPATPSDCIADSKITAVALSDTRDNGPFSIRTKRISRQSAKGFGGGTIHYPTNASGCGLLGAIAVVPGYVSYENSIKWWGPRLASWGFVVITINTNSIYDDPDSRAAQLNAALDNMIADDTVGSMIDPKRLGAIGWSMGGGGALKLATERSTVRAIMPLAPYHDKSYGEVKTPTLVIACEDDRIAETKKYANAFYKNAIGPKMKVEVNNGSHFCPSYRFNEILLSKPGIAWMQRYINNDTRFDKFLCANENYSKSPRISAYDYKDCP	2022.0	Weight loss;GPC	Biomer P226	Biomer, Germany	Yes	No				Yes		
Moraxella sp.	479	PBS	Nikolaivits, E., Taxeidis, G., Gkountela, C., Vouyiouka, S., Maslak, V., Nikodinovic-Runic, J., & Topakas, E. (2022). A polyesterase from the Antarctic bacterium Moraxella sp. degrades highly crystalline synthetic polymers. Journal of Hazardous Materials, 434, 128900.	Polyester hydrolase	00124	00124 | Polyester hydrolase | Moraxella sp. | PET PCL PU PHB PBS PLA PHA	Yes	P19833	MFIMIKKSELAKAIIVTGALVFSIPTLAEVTLSETTVSSIKSEATVSSTKKALPATPSDCIADSKITAVALSDTRDNGPFSIRTKRISRQSAKGFGGGTIHYPTNASGCGLLGAIAVVPGYVSYENSIKWWGPRLASWGFVVITINTNSIYDDPDSRAAQLNAALDNMIADDTVGSMIDPKRLGAIGWSMGGGGALKLATERSTVRAIMPLAPYHDKSYGEVKTPTLVIACEDDRIAETKKYANAFYKNAIGPKMKVEVNNGSHFCPSYRFNEILLSKPGIAWMQRYINNDTRFDKFLCANENYSKSPRISAYDYKDCP	2022.0	Weight loss;GPC	initial grade NaturePlast PBE003	NaturePlast, France	Yes	No				Yes		
Moraxella sp.	479	PLA	Nikolaivits, E., Taxeidis, G., Gkountela, C., Vouyiouka, S., Maslak, V., Nikodinovic-Runic, J., & Topakas, E. (2022). A polyesterase from the Antarctic bacterium Moraxella sp. degrades highly crystalline synthetic polymers. Journal of Hazardous Materials, 434, 128900.	Polyester hydrolase	00124	00124 | Polyester hydrolase | Moraxella sp. | PET PCL PU PHB PBS PLA PHA	Yes	P19833	MFIMIKKSELAKAIIVTGALVFSIPTLAEVTLSETTVSSIKSEATVSSTKKALPATPSDCIADSKITAVALSDTRDNGPFSIRTKRISRQSAKGFGGGTIHYPTNASGCGLLGAIAVVPGYVSYENSIKWWGPRLASWGFVVITINTNSIYDDPDSRAAQLNAALDNMIADDTVGSMIDPKRLGAIGWSMGGGGALKLATERSTVRAIMPLAPYHDKSYGEVKTPTLVIACEDDRIAETKKYANAFYKNAIGPKMKVEVNNGSHFCPSYRFNEILLSKPGIAWMQRYINNDTRFDKFLCANENYSKSPRISAYDYKDCP	2022.0	Weight loss;GPC	4043D	NatureWorks, USA	Yes	No				Yes		
Moraxella sp.	479	PHA	Nikolaivits, E., Taxeidis, G., Gkountela, C., Vouyiouka, S., Maslak, V., Nikodinovic-Runic, J., & Topakas, E. (2022). A polyesterase from the Antarctic bacterium Moraxella sp. degrades highly crystalline synthetic polymers. Journal of Hazardous Materials, 434, 128900.	Polyester hydrolase	00124	00124 | Polyester hydrolase | Moraxella sp. | PET PCL PU PHB PBS PLA PHA	Yes	P19833	MFIMIKKSELAKAIIVTGALVFSIPTLAEVTLSETTVSSIKSEATVSSTKKALPATPSDCIADSKITAVALSDTRDNGPFSIRTKRISRQSAKGFGGGTIHYPTNASGCGLLGAIAVVPGYVSYENSIKWWGPRLASWGFVVITINTNSIYDDPDSRAAQLNAALDNMIADDTVGSMIDPKRLGAIGWSMGGGGALKLATERSTVRAIMPLAPYHDKSYGEVKTPTLVIACEDDRIAETKKYANAFYKNAIGPKMKVEVNNGSHFCPSYRFNEILLSKPGIAWMQRYINNDTRFDKFLCANENYSKSPRISAYDYKDCP	2022.0	Weight loss;GPC	Biomer P226	Biomer, Germany	Yes	No				Yes		
Cupriavidus necator	106590	PHA	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00160	00160 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ92291.1	MLYQLHEFQRSILHPLTAWAQATAKTFTNPLSPLSLVPGAPRLAAGYELLYRLGKEYEKPAFDIKSVRSNGRDIPIVEQTVLEKPFCKLVRFKRYADDPETIKLLKDEPVVLVAAPLSGHHATLLRDTVRTLLQDHKVYVTDWIDARMVPVEEGAFHLSDYIYYIQEFIRHIGAENLHVISVCQPTVPVLAAISLMASAGEKTPRTMTMMGGPIDARKSPTAVNSLATNKSFEWFENNVIYTVPANYPGHGRRVYPGFLQHAGFVAMNPDRHLSSHYDFYLSLVEGDADDAEAHVRFYDEYNAVLDMAAEYYLDTIREVFQEFRLANGTWAIDGNPVRPQDIKSTALMTVEGELDDISGAGQTAAAHDLCAGIPKIRKQHLNAAHCGHYGIFSGRRWREEIYPQLRDFIRKYHQASATR	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHB	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00160	00160 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ92291.1	MLYQLHEFQRSILHPLTAWAQATAKTFTNPLSPLSLVPGAPRLAAGYELLYRLGKEYEKPAFDIKSVRSNGRDIPIVEQTVLEKPFCKLVRFKRYADDPETIKLLKDEPVVLVAAPLSGHHATLLRDTVRTLLQDHKVYVTDWIDARMVPVEEGAFHLSDYIYYIQEFIRHIGAENLHVISVCQPTVPVLAAISLMASAGEKTPRTMTMMGGPIDARKSPTAVNSLATNKSFEWFENNVIYTVPANYPGHGRRVYPGFLQHAGFVAMNPDRHLSSHYDFYLSLVEGDADDAEAHVRFYDEYNAVLDMAAEYYLDTIREVFQEFRLANGTWAIDGNPVRPQDIKSTALMTVEGELDDISGAGQTAAAHDLCAGIPKIRKQHLNAAHCGHYGIFSGRRWREEIYPQLRDFIRKYHQASATR	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHA	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00161	00161 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ93939.1	MLYHAYQIYADMILPACTLAELAAATLAANPRSGGFDAVPRLRAACELIALVRLTHHRPAFGIDHATVGGQPVPVTEEVVARTPFCSLLHFRRHGIVGQPRVLLVAPMSGHFATLLRGTVQTMLADHDVYLTDWHNPRDIPLLAGRFGFDEFVQHLIGFLQTLGGGTHLVAICQPAVAALAAAALMAEDGDPAQPPSLTLMAGPIDARVNPTKVNALAMSQPLEWFERTLIGMVPLRFAGAMRRVYPGHVQLLAFMSMNPERHEQALRELYALRERGEHDKADAIRDFYIEYFATMDLTAEFYLETVSLVFQRFLLAQGLLDVSGRRVRTRAIHRTALLTVEGERDDICAIGQTVAAQDLCSSLRPYMRMHHVQTGVGHYGVFNGRRWETQVYPLVRNTIYTSS	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHB	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00161	00161 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ93939.1	MLYHAYQIYADMILPACTLAELAAATLAANPRSGGFDAVPRLRAACELIALVRLTHHRPAFGIDHATVGGQPVPVTEEVVARTPFCSLLHFRRHGIVGQPRVLLVAPMSGHFATLLRGTVQTMLADHDVYLTDWHNPRDIPLLAGRFGFDEFVQHLIGFLQTLGGGTHLVAICQPAVAALAAAALMAEDGDPAQPPSLTLMAGPIDARVNPTKVNALAMSQPLEWFERTLIGMVPLRFAGAMRRVYPGHVQLLAFMSMNPERHEQALRELYALRERGEHDKADAIRDFYIEYFATMDLTAEFYLETVSLVFQRFLLAQGLLDVSGRRVRTRAIHRTALLTVEGERDDICAIGQTVAAQDLCSSLRPYMRMHHVQTGVGHYGVFNGRRWETQVYPLVRNTIYTSS	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHA	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00162	00162 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ95139.1	MLYQLVEYQRALLAPFTAWAASAANAFIDPASPFAYVPGASCFAAGYEMLYRLGRTCEKPSFGIITAIRRDGHVIAVAEQVIVEGPFCRLLRFAPDMGALDPCTAPTPPVLVCAPLAGHHAVMLREVVQALLPEHVVYVTDWNDARRVPVAEGPFHLDDQVAHLQAFIRRIGAEPLHVLAICQATVPALAAVSLLASAGEPTPRSLILVGGPVDARRSPTALGRLAARHSLAWFQRNLIYAVPQPYPGAGRKVCPSFLQLAGLAAAQPERLGEAYWDYCLDLVRCDPVRAKEHRRACDAYHAVLDMAAEFYLDTIQLVFQEFQLARGSWQVRGEAVRPQDIRTTALLTIEGEQDEISGRGQTQAAHDLCQGIAACDKRHLTARQCGHYDLFCGPRWCTDVYPRIRDLTGHDT	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHB	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00162	00162 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ95139.1	MLYQLVEYQRALLAPFTAWAASAANAFIDPASPFAYVPGASCFAAGYEMLYRLGRTCEKPSFGIITAIRRDGHVIAVAEQVIVEGPFCRLLRFAPDMGALDPCTAPTPPVLVCAPLAGHHAVMLREVVQALLPEHVVYVTDWNDARRVPVAEGPFHLDDQVAHLQAFIRRIGAEPLHVLAICQATVPALAAVSLLASAGEPTPRSLILVGGPVDARRSPTALGRLAARHSLAWFQRNLIYAVPQPYPGAGRKVCPSFLQLAGLAAAQPERLGEAYWDYCLDLVRCDPVRAKEHRRACDAYHAVLDMAAEFYLDTIQLVFQEFQLARGSWQVRGEAVRPQDIRTTALLTIEGEQDEISGRGQTQAAHDLCQGIAACDKRHLTARQCGHYDLFCGPRWCTDVYPRIRDLTGHDT	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHA	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00163	00163 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	AAP85930.1	MLRDVVQSLLQEHIVYVTDWSNGAIALLASRDEATPTSLTLIGGPIDARRSPTAIGRLASSRSIQWFRRNLVYPVPHPYAGAGRQVCPSFVQLSGLAAAQSSPLWGLCEGYWANLARGDAERANVHWQALLDYSAVLDMAAEFYLDTVRTVFQEFQIAFGTWRVRGQLVRPQDIRSTALLTIEGELDDISGRGQTHAAHDLCRGLSAHDRRLVTIAGCTHYDLFRGPVWHTEVFPWICDMTRDDM	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHB	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00163	00163 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	AAP85930.1	MLRDVVQSLLQEHIVYVTDWSNGAIALLASRDEATPTSLTLIGGPIDARRSPTAIGRLASSRSIQWFRRNLVYPVPHPYAGAGRQVCPSFVQLSGLAAAQSSPLWGLCEGYWANLARGDAERANVHWQALLDYSAVLDMAAEFYLDTVRTVFQEFQIAFGTWRVRGQLVRPQDIRSTALLTIEGELDDISGRGQTHAAHDLCRGLSAHDRRLVTIAGCTHYDLFRGPVWHTEVFPWICDMTRDDM	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHA	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00164	00164 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ95805.1	MALYALRELTLQSLGPLGAMIEAGYRAVNFWGESVAWLPGLREADAALELFTRLTKAYGKPSFEIDEVFVRGQRVAVTETALIEEPFCRLLHFRKDMSNPGPRVLLVAPLSGHYATLLRPTVEALLPGHDVYITDWADARLVPLDAGHFDLGCYVDYLKKFLRYLGAGTHIVAVCQPGVPVLCAVAQMAEDNEQVQPRSMTLIAAPIDTRVSPTAVDQFAQQYSLAWFEANVIERVPAGYPGNGRRVYPGFLQLAGFVSMNVAHHAGAHLDFYRHLVDGRQSEAARHRKFYDEYNAVLDVPAEYYLETIQKVFLEHHLCRGRMEVGQRRVYPEAIANVSLLTIEGSEDDITGRGQTEAAHALCAGLAADRKEHLVVDGVGHYGTFAGQRFRESILPAMTQFIQRCAD	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHB	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00164	00164 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ95805.1	MALYALRELTLQSLGPLGAMIEAGYRAVNFWGESVAWLPGLREADAALELFTRLTKAYGKPSFEIDEVFVRGQRVAVTETALIEEPFCRLLHFRKDMSNPGPRVLLVAPLSGHYATLLRPTVEALLPGHDVYITDWADARLVPLDAGHFDLGCYVDYLKKFLRYLGAGTHIVAVCQPGVPVLCAVAQMAEDNEQVQPRSMTLIAAPIDTRVSPTAVDQFAQQYSLAWFEANVIERVPAGYPGNGRRVYPGFLQLAGFVSMNVAHHAGAHLDFYRHLVDGRQSEAARHRKFYDEYNAVLDVPAEYYLETIQKVFLEHHLCRGRMEVGQRRVYPEAIANVSLLTIEGSEDDITGRGQTEAAHALCAGLAADRKEHLVVDGVGHYGTFAGQRFRESILPAMTQFIQRCAD	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHA	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00165	00165 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ97183.1	MPRSSGAKLWSTLNKAAARNARRLQRAVNQNLTRPMTEAIVRNAVKQSAAVTAATQRALSGVVSPVQAPQNRGSGRWEEGAWGAPVAPRRYRIFVPAGVTASRRAPMLVLLHGCGQDAASFAAVTRAAAVAREAGWVVLLPEQTSQANAQRCWNWFRPGAQGGVEAGLLMALIDQACRGHPVAADRISVLGLSAGGAMALMLGLRYPGRFAAVGSHSGAVPWSASNAAQAARAMRGGHGPDAKAMQALRFGLAGRRPPPLLLLHGDADHVVDFSNATAAAGMWMHLQPEDAHALSAAPARRIQRGMRRAMDVFDWAEGKSPYVRLVRIEGLGHAWSGGAGGQAFSDPAGPDGLKLALRFFLEVGG	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHB	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00165	00165 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ97183.1	MPRSSGAKLWSTLNKAAARNARRLQRAVNQNLTRPMTEAIVRNAVKQSAAVTAATQRALSGVVSPVQAPQNRGSGRWEEGAWGAPVAPRRYRIFVPAGVTASRRAPMLVLLHGCGQDAASFAAVTRAAAVAREAGWVVLLPEQTSQANAQRCWNWFRPGAQGGVEAGLLMALIDQACRGHPVAADRISVLGLSAGGAMALMLGLRYPGRFAAVGSHSGAVPWSASNAAQAARAMRGGHGPDAKAMQALRFGLAGRRPPPLLLLHGDADHVVDFSNATAAAGMWMHLQPEDAHALSAAPARRIQRGMRRAMDVFDWAEGKSPYVRLVRIEGLGHAWSGGAGGQAFSDPAGPDGLKLALRFFLEVGG	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHA	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00166	00166 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ93348.1	MHSTQIPPQQKQKRRLRLTVLAAAASMLAAACVSGDDNNNGNGSNPNTKPANIGTVTINSYNGTTDDLLTAGLGKDGLASATAPLPANPTAPTAAELRRYAIHTNYRAIVDTTASGGYGSLYGPNVDAQGNVTGSDGKVAGVEYLAFSDDGSGQQNVTMLVQIPASFNTSKPCMITATSSGSRGVYGAIATGEWGLKRGCAVAYTDKGTGAAPHDLDTDTVPLIDGTRATRAAAGKNAQFAAPAGATSLADFTAANPHRLAFKHAHSQRNPEKDWGKFTLQAVEFAIWAINDRFGAVSANGTRQRTLDKDRIVVIASSVSNGGGAAVAAAEQDAGGLIDGVAVGEPNLNMPPNTGIVVQRGATPVAASGRTLYDYTTTANLLQHCAARATALTQAPFYTNPATATFFANRCQTLAEKGLVSGANTDEQSASALQALHDAGWEAESDDLHPSLAVFDVAAAISVNYANAYAQASVTDRLCGYSFASTLTDLKPAAIAPAALASMFATGNGVPPQPPVQLINDLDPQHGPYLNLASVSPSTLREDLNYDGANCLRSLLAGSDAAARALQAGQALTLRNGNLRGKPAVIVHGRSDGLLPVNHTSRPYLGLNRQQEGVTSKLSYVEVENAQHFDAFIGLVPGYSNRYVPLHVYLNRALDAVYDNLTAGKALPPSQVLRTTPRGGTLNTPAPALLPSNVPPFAASPAAGNAITVNANAVQVPD	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHB	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00166	00166 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ93348.1	MHSTQIPPQQKQKRRLRLTVLAAAASMLAAACVSGDDNNNGNGSNPNTKPANIGTVTINSYNGTTDDLLTAGLGKDGLASATAPLPANPTAPTAAELRRYAIHTNYRAIVDTTASGGYGSLYGPNVDAQGNVTGSDGKVAGVEYLAFSDDGSGQQNVTMLVQIPASFNTSKPCMITATSSGSRGVYGAIATGEWGLKRGCAVAYTDKGTGAAPHDLDTDTVPLIDGTRATRAAAGKNAQFAAPAGATSLADFTAANPHRLAFKHAHSQRNPEKDWGKFTLQAVEFAIWAINDRFGAVSANGTRQRTLDKDRIVVIASSVSNGGGAAVAAAEQDAGGLIDGVAVGEPNLNMPPNTGIVVQRGATPVAASGRTLYDYTTTANLLQHCAARATALTQAPFYTNPATATFFANRCQTLAEKGLVSGANTDEQSASALQALHDAGWEAESDDLHPSLAVFDVAAAISVNYANAYAQASVTDRLCGYSFASTLTDLKPAAIAPAALASMFATGNGVPPQPPVQLINDLDPQHGPYLNLASVSPSTLREDLNYDGANCLRSLLAGSDAAARALQAGQALTLRNGNLRGKPAVIVHGRSDGLLPVNHTSRPYLGLNRQQEGVTSKLSYVEVENAQHFDAFIGLVPGYSNRYVPLHVYLNRALDAVYDNLTAGKALPPSQVLRTTPRGGTLNTPAPALLPSNVPPFAASPAAGNAITVNANAVQVPD	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHA	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00167	00167 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ92475.1	MSASPRLGFVQCISPAGLHRMAYHEWGDPANPRVLVCAHGLTRTGRDFDTVASALCGDYRVVCPDVAGRGRSEWLADANGYVVPQYVSDMVTLIARLNVEKVDWFGTSMGGLIGMGLAGLPKSPVRKLLLNDVGPKLAPSAVERIGAYLGLPVRFKTFEEGLAYLQTISASFGRHTPEQWRELNAAILKPVQGTDGLEWGLHYDPQLAVPFRKSTPEAIAAGEAALWRSFEAIEGPVLVVRGAQSDLLLRETVAEMVARGKHVSSVEVPDVGHAPTFVDPAQIAIAPQFFTGA	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHB	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00167	00167 | PHA depolymerase | Cupriavidus necator | PHA PHB	Yes	CAJ92475.1	MSASPRLGFVQCISPAGLHRMAYHEWGDPANPRVLVCAHGLTRTGRDFDTVASALCGDYRVVCPDVAGRGRSEWLADANGYVVPQYVSDMVTLIARLNVEKVDWFGTSMGGLIGMGLAGLPKSPVRKLLLNDVGPKLAPSAVERIGAYLGLPVRFKTFEEGLAYLQTISASFGRHTPEQWRELNAAILKPVQGTDGLEWGLHYDPQLAVPFRKSTPEAIAAGEAALWRSFEAIEGPVLVVRGAQSDLLLRETVAEMVARGKHVSSVEVPDVGHAPTFVDPAQIAIAPQFFTGA	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHA	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00038	00038 | PHB depolymerase | Cupriavidus necator | PHB PHA	Yes	CAJ96855.1	MTKSFAADWHAQIRRLSRAQARTEAQVKSWLDRVDSLNPLTPARPDRPPGKVRPARPAPAPGSLPGTWQAHRLRLAPLPGELVPQLSYHLYIPSKAHRGPLPVVVVLHGCRQTPDDLSAGTRMNALAEREGFIVAYPQQPLRRQVQRCWQWFDLGAAEGGREAQAVAALIDALAARHDVREREIYLAGMSAGAAMAAVVALRYPGKVAAAALHSGVVIGAADNPRAGLRAMQQGSAADPSWLLDAAGVTPGGPEMPALVIHGLADDAVHPVNGRLLARQFLAYNGLEDRLAGAPAQSGPEDEAPGRSHEYRFGRWRRDLVTLVEVEGLGHAWSGGDASYGYHSDIGPDASTMMWQFFSQHRR	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHB	Brigham, C. J., Reimer, E. N., Rha, C., & Sinskey, A. J. (2012). Examination of PHB depolymerases in Ralstonia eutropha: further elucidation of the roles of enzymes in PHB homeostasis. AMB express, 2(1), 1-13.	PHA depolymerase	00038	00038 | PHB depolymerase | Cupriavidus necator | PHB PHA	Yes	CAJ96855.1	MTKSFAADWHAQIRRLSRAQARTEAQVKSWLDRVDSLNPLTPARPDRPPGKVRPARPAPAPGSLPGTWQAHRLRLAPLPGELVPQLSYHLYIPSKAHRGPLPVVVVLHGCRQTPDDLSAGTRMNALAEREGFIVAYPQQPLRRQVQRCWQWFDLGAAEGGREAQAVAALIDALAARHDVREREIYLAGMSAGAAMAAVVALRYPGKVAAAALHSGVVIGAADNPRAGLRAMQQGSAADPSWLLDAAGVTPGGPEMPALVIHGLADDAVHPVNGRLLARQFLAYNGLEDRLAGAPAQSGPEDEAPGRSHEYRFGRWRRDLVTLVEVEGLGHAWSGGDASYGYHSDIGPDASTMMWQFFSQHRR	2012.0	HPLC;Microscopy			Yes	No				No		
Cupriavidus necator	106590	PHB	Abe, T., Kobayashi, T., & Saito, T. (2005). Properties of a novel intracellular poly (3-hydroxybutyrate) depolymerase with high specific activity (PhaZd) in Wautersia eutropha H16. Journal of Bacteriology, 187(20), 6982-6990.	PHB depolymerase	00038	00038 | PHB depolymerase | Cupriavidus necator | PHB PHA	Yes	CAJ96855.1	MTKSFAADWHAQIRRLSRAQARTEAQVKSWLDRVDSLNPLTPARPDRPPGKVRPARPAPAPGSLPGTWQAHRLRLAPLPGELVPQLSYHLYIPSKAHRGPLPVVVVLHGCRQTPDDLSAGTRMNALAEREGFIVAYPQQPLRRQVQRCWQWFDLGAAEGGREAQAVAALIDALAARHDVREREIYLAGMSAGAAMAAVVALRYPGKVAAAALHSGVVIGAADNPRAGLRAMQQGSAADPSWLLDAAGVTPGGPEMPALVIHGLADDAVHPVNGRLLARQFLAYNGLEDRLAGAPAQSGPEDEAPGRSHEYRFGRWRRDLVTLVEVEGLGHAWSGGDASYGYHSDIGPDASTMMWQFFSQHRR	2005.0	Spectrophotometry;HPLC	Semicrystalline PHB was prepared from PHB-rich W. eutropha H16 cells as described previously (39). Artificial amorphous PHB granules were prepared from the purified semicrystalline PHB granules as described by Horowitz and Sanders (11).		Yes	No		Culture collection		Yes		
Cupriavidus necator	106590	PHA	Abe, T., Kobayashi, T., & Saito, T. (2005). Properties of a novel intracellular poly (3-hydroxybutyrate) depolymerase with high specific activity (PhaZd) in Wautersia eutropha H16. Journal of Bacteriology, 187(20), 6982-6990.	PHB depolymerase	00038	00038 | PHB depolymerase | Cupriavidus necator | PHB PHA	Yes	CAJ96855.1	MTKSFAADWHAQIRRLSRAQARTEAQVKSWLDRVDSLNPLTPARPDRPPGKVRPARPAPAPGSLPGTWQAHRLRLAPLPGELVPQLSYHLYIPSKAHRGPLPVVVVLHGCRQTPDDLSAGTRMNALAEREGFIVAYPQQPLRRQVQRCWQWFDLGAAEGGREAQAVAALIDALAARHDVREREIYLAGMSAGAAMAAVVALRYPGKVAAAALHSGVVIGAADNPRAGLRAMQQGSAADPSWLLDAAGVTPGGPEMPALVIHGLADDAVHPVNGRLLARQFLAYNGLEDRLAGAPAQSGPEDEAPGRSHEYRFGRWRRDLVTLVEVEGLGHAWSGGDASYGYHSDIGPDASTMMWQFFSQHRR	2005.0	Spectrophotometry;HPLC	Semicrystalline PHB was prepared from PHB-rich W. eutropha H16 cells as described previously (39). Artificial amorphous PHB granules were prepared from the purified semicrystalline PHB granules as described by Horowitz and Sanders (11).		Yes	No		Culture collection		Yes		
Paenarthrobacter ureafaciens	37931	Nylon	Kinoshita, S., Kageyama, S., Iba, K., Yamada, Y., & Okada, H. (1975). Utilization of a Cyclic Dimer and Linear Oligomers of ε-Aminocaproic Acid by Achrornobacter guttatus KI 72. Agricultural and Biological Chemistry, 39(6), 1219-1223.	Hydrolase	00168	00168 | Hydrolase | Paenarthrobacter ureafaciens | Nylon	Yes	P13398	MSKVDLWQDATAQAELVRSGEISRTELLEATIAHVQAVNPEINAVIIPLFEKARRESELASGPFAGVPYLLKDLTVVSQGDINTSSIKGMKESGYRADHDAYFVQRMRAAGFVLLGKTNTPEMGNQVTTEPEAWGATRNPWNLGRSVGGSSGGSGAAVAAALSPVAHGNDAAGSVRIPASVCGVVGLKPTRGRISPGPLVTDSDNVAGAAHEGLFARSVRDIAALLDVVSGHRPGDTFCAPTASRPYAQGISENPGSLRVGVLTHNPVGDFALDPECAAAARGAAAALAALGHDVNDAYPEALGDRSFLKDYSTICDVAIAREIERNGELIGRPLTEDDVEWTSWEMVKRADQVTGRAFAACVDELRYYAGKVERWWEAGWDLLILPTVTRQTPEIGELMLAKGTDLEGRQSAFISGSLQMLAFTVPFNVSGQPAISLPIGMSSDGMPIGVQIVAAYGREDLLLQVAAQLEGALPWVARRPQLLNPSRKIPAA	1975.0	TLC			Yes	No	Sludge	Sewage/Sludge	Japan	No		
Paenarthrobacter ureafaciens	37931	Nylon	Kinoshita, S., Kageyama, S., Iba, K., Yamada, Y., & Okada, H. (1975). Utilization of a Cyclic Dimer and Linear Oligomers of ε-Aminocaproic Acid by Achrornobacter guttatus KI 72. Agricultural and Biological Chemistry, 39(6), 1219-1223.	Hydrolase	00169	00169 | Hydrolase | Paenarthrobacter ureafaciens | Nylon	Yes	P07061	MNARSTGQHPARYPGAAAGEPTLDSWQEAPHNRWAFARLGELLPTAAVSRRDPATPAEPVVRLDALATRLPDLEQRLEETCTDAFLVLRGSEVLAEYYRAGFAPDDRHLLMSVSKSLCGTVVGALIDEGRIDPAQPVTEYVPELAGSVYDGPSVLQVLDMQISIDYNEDYVDPASEVQTHDRSAGWRTRRDGDPADTYEFLTTLRGDGGTGEFQYCSANTDVLAWIVERVTGLRYVEALSTYLWAKLDADRDATITVDQTGFGFANGGVSCTARDLARVGRMMLDGGVAPGGRVVSQGWVESVLAGGSREAMTDEGFTSAFPEGSYTRQWWCTGNERGNVSGIGIHGQNLWLDPRTDSVIVKLSSWPDPDTRHWHGLQSGILLDVSRALDAV	1975.0	TLC			Yes	No	Sludge	Sewage/Sludge	Japan	No		
Paenarthrobacter ureafaciens	37931	Nylon	Kinoshita, S., Kageyama, S., Iba, K., Yamada, Y., & Okada, H. (1975). Utilization of a Cyclic Dimer and Linear Oligomers of ε-Aminocaproic Acid by Achrornobacter guttatus KI 72. Agricultural and Biological Chemistry, 39(6), 1219-1223.	Hydrolase	00170	00170 | Hydrolase | Paenarthrobacter ureafaciens | Nylon	Yes	Q79F77	MNTTPVHALTDIDGGIAVDPAPRLAGPPVFGGPGNDAFDLAPVRSTGREMLRFDFPGVSIGAAHYEEGPTGATVIHIPAGARTAVDARGGAVGLSGGYDFNHAICLAGGAGYGLEAGAGVSDALLERLEHRTGFAELQLVSSAVIYDFSARSTAVYPDKALGRAALEFAVPGEFPQGRAGAGMSASAGKVDWDRTEITGQGAAFRRLGDVRILAVVVPNPVGVIVDRAGTVVRGNYDAQTGVRRHPVFDYQEAFAEQVPPVTEAGNTTISAIVTNVRMSPVELNQFAKQVHSSMHRGIQPFHTDMDGDTLFAVTTDEIDLPTTPGSSRGRLSVNATALGAIASEVMWDAVLEAGK	1975.0	TLC			Yes	No	Sludge	Sewage/Sludge	Japan	No		
Kocuria sp.	1871328	Nylon	Yasuhira, K., Tanaka, Y., Shibata, H., Kawashima, Y., Ohara, A., Kato, D. I., ... & Negoro, S. (2007). 6-Aminohexanoate oligomer hydrolases from the alkalophilic bacteria Agromyces sp. strain KY5R and Kocuria sp. strain KY2. Applied and environmental microbiology, 73(21), 7099-7102.	Nylon hydrolase	00171	00171 | Nylon hydrolase | Paenarthrobacter ureafaciens | Nylon	Yes	Q1EPR4	MNTTPVHALTDIDGGIAVDPAPRLAGPPVFGGPGNAAFDLVPVRSTGRETLRFDFPGVSVGSAHYEEGPTGATVIHIPAGARTAVDARGGAVGLSGGYDFNHAICLAGGASYGLEAGAGVSGALLERLEYRTGFAEAQLVSSAVIYDFSARSTAVYPDKALGRAALEFAVPGEFPQGRAGAGMSASAGKVDWDRTEITGQGAAFRRLGDVRILAVVVPNPVGVIMDRAGGIVRGNYDAQTGVRRHPVFDYQEAFAEQLPPVTQAGNTTISAIVTNVRMSPVELNQFAKQVHSSMHRGIQPFHTDMDGDTLFAVTTDEIDLPTTPGSSRGRLSVNATALGAIASEVMWDAVLEAAK	2007.0	Clear zone			Yes	No	Sludge	Sewage/Sludge	Japan	No		
Nocardia farcinica	37329	Nylon	Heumann, S., Eberl, A., Fischer‐Colbrie, G., Pobeheim, H., Kaufmann, F., Ribitsch, D., ... & Guebitz, G. M. (2009). A novel aryl acylamidase from Nocardia farcinica hydrolyses polyamide. Biotechnology and bioengineering, 102(4), 1003-1011.	Polyamidase	00172	00172 | Polyamidase | Nocardia farcinica | Nylon	Yes	WP_011209364.1	MDVAEYAAHDATGLAELIREGQVSAAEVWTAAATALDAVEPELAAVAGERFDKPLDYDESGPFAGVPFALKDLIAHAGGVPSRSGSRLFGAGVAHPEDTHLVARFRRAGLAIGAITRSPEFGFNATTEAIAYGGPSRNPWATDRSPGGSSGASAALVASGALPMAHANDGGGSIRIPAAACGAVGLKPSRGRTTPGPDFADPLLGLGIEFAVTRTVRDCARLLDAVHGAEPGDRYLLPGPVRSYAEHAAAGSRPLRIAVTTTPMDAGRAVDPECVAAVNRVAERLAELGHVVEEAAPELDVAAFDKANLDAWCSFLADAVLGASAQLGVQPSREYLEATTLACVEYGKTLSAFDIFTADRVFNQTTRAVAGFLTRYDVLLTPTTSAPPIPLGHLDADDASLSAREWYDRIFDYGSFTALFNVTGMPAISLPLAESTAGLPIGIQFAGRYGDEATLLALAGDLERAMPWADRRPAVHVGR	2009.0	HPLC;Tensilometer	Polymers were synthesized 		Yes	No	Soil	Soil		No		
Pseudomonas sp.	306	PET	Edwards, S., León-Zayas, R., Ditter, R., Laster, H., Sheehan, G., Anderson, O., ... & Mellies, J. L. (2022). Microbial Consortia and Mixed Plastic Waste: Pangenomic Analysis Reveals Potential for Degradation of Multiple Plastic Types via Previously Identified PET Degrading Bacteria. International Journal of Molecular Sciences, 23(10), 5612.	Esterase	00173	00173 | Esterase | Pseudomonas sp. | PET	Yes	WP_085690612.1	MTEPLILQPVKPADACVIWLHGLGADRYDFLPVAEALQESLLSTRFVLPQAPTRPVTINGGYAMPSWYDIKAMSPARAIDRDELEASADRIIELIEEQRSSGIDASRIFLAGFSQGGAVVYHTAFLKWQGPLGGVLALSTYAPTFSDELELSASQQRIPVLSLHGQFDNVVQNSMGRTAYEYLKAHGVTVTWQEYPMEHEVLPEEIRDIGTWLSERLR	2022.0	HPLC	Post consumer PET		No	No	Petroleum-soil	Soil	EUA	No		
Rhodococcus ruber	1830	LDPE	Santo, M., Weitsman, R., & Sivan, A. (2013). The role of the copper-binding enzyme–laccase–in the biodegradation of polyethylene by the actinomycete Rhodococcus ruber. International Biodeterioration & Biodegradation, 84, 204-210.	Laccase	00174	00174 | Laccase | Rhodococcus ruber | LDPE	Yes		GAWGCGDLLRRSHCYGARGGLPDTGALNTINFFPTLSDGIWHGIVLSNDMDGAATVTDAGSHRPGRCVHLRIHRPPPRALLYHSHSGVQLDRGLYGVVVIDDPAEPGGYDDEWVVVLDDWVDGTGRTPDDVARELGMAASGEGSESAGEMGGMDHGSMEDMEGMGDMGAETMQSDLLGGAGDVNYPYYLVNGRIPTDPVSLTAVPGRRIRLRIVNAGSDTAFRLALGGMRMTVTHSDGFPVTPRETDALLIGMGERFDVLVTLADGVFPLYAAAEGKPGYGVALVRTGAGSAGPTDTRPAELDRQVLLGTDLSPREQVRLASKSHDNYLSVDMGGTMSPYRWTLNGRAFPDAAPLAVAQGQRVRMRFRNMSMMFHPMHVHGMTFALVSGGARKDTVTVRPMQTVEVEFDADNPGQWALHCHNRL	2013.0	ATR-FTIR;DSC;GPC;Weight loss	Branched low-density (0.92 g cm^-3) polyethylene (LDPE) film, with an average molecular weight of 191,000 (Ipiten 111; Carmel Olefins, Haifa, Israel) and thickness of 0.2 mm was produced by Plastopil Hazorea (Hazarded, Israel) 	Carmel Olefins		No	Culture collection	Culture collection		No		
Phanerochaete chrysosporium	2822231	PE	Iiyoshi, Y., Tsutsumi, Y., & Nishida, T. (1998). Polyethylene degradation by lignin-degrading fungi and manganese peroxidase. Journal of wood science, 44(3), 222-229.	No			No			1998.0	Tensilometer;GPC	Two strips (1 × 6 cm, 100 ~tm thick) of polyethylene membrane (HIPORE1100)	Asahi Kasei		No				No		
Strain IZU-154	175245	PE	Iiyoshi, Y., Tsutsumi, Y., & Nishida, T. (1998). Polyethylene degradation by lignin-degrading fungi and manganese peroxidase. Journal of wood science, 44(3), 222-229.	No			No			1998.0	Tensilometer;GPC	Two strips (1 × 6 cm, 100 ~tm thick) of polyethylene membrane (HIPORE1100)	Asahi Kasei		No				No		
Trametes versicolor	5325	PE	Iiyoshi, Y., Tsutsumi, Y., & Nishida, T. (1998). Polyethylene degradation by lignin-degrading fungi and manganese peroxidase. Journal of wood science, 44(3), 222-229.	No			No			1998.0	Tensilometer;GPC	Two strips (1 × 6 cm, 100 ~tm thick) of polyethylene membrane (HIPORE1100)	Asahi Kasei		No				No		
Uncultured bacterium	77133	PET	Eiamthong, B., Meesawat, P., Wongsatit, T., Jitdee, J., Sangsri, R., Patchsung, M., ... & Uttamapinant, C. Discovery and Genetic Code Expansion of a Polyethylene Terephthalate (PET) Hydrolase from the Human Saliva Metagenome for the Degradation and Bio‐Functionalization of PET. Angewandte Chemie International Edition.	Hydrolase	00175	00175 | Hydrolase | Uncultured bacterium | PET	Yes		MKALTFSKSFLSAIAAGALMLSASAMANNPPPPDDPGAPSPYQRGPDPTVSFVEASRGNYRVATSNVSSLVSGFGGGTIHYPSNATGTMGAIVVIPGYVSGEGSIDWWGPKLASYGFVVMTIGTNSGFDQPPSRARQINNALDYLVEQNTRTGSPVRGMIDPSRLGVIGWSMGGGGTIRVAGEGRIKAAIPLAPWDTSSIPSRGVQAPTLIFACQSDVVAPVRSHASPFYNALPGSISKAFVNLNNGNHFCANGGSSFGRYDAALGRLGVSWMKRFLDEDRRYSQFLCGPNHTGDRQITEYRGNCPY	2022.0	HPLC	PET powder (~0.3µm-diameter powder)	PTT Innovation Institute		No				Yes		
Rhizobacter gummiphilus	946333	PET	Sagong, H. Y., Son, H. F., Seo, H., Hong, H., Lee, D., & Kim, K. J. (2021). Implications for the PET decomposition mechanism through similarity and dissimilarity between PETases from Rhizobacter gummiphilus and Ideonella sakaiensis. Journal of Hazardous Materials, 416, 126075.	Hydrolase	00176	00176 | Hydrolase | Rhizobacter gummiphilus | PET	Yes	A0A1W6L588_9BURK	MFGKLPFARASLAVGALLLSAAAVAQTNPYQRGPDPTVSSLEATRGPFSTSSFTVSRPSGYGAGTVYYPTNAGGKVGAIAVVPGYTARQSSINWWGPRLASHGFVVITIDTNSTLDQPSSRSSQQMAALRQVVSLAGTSSSPIYNKVDTARLGVMGWSMGGGGSLISAKNNPSLRAAAPQAPWAQESFSSVTVPTLIVSCENDSIAPNSSHSFPFYNQMTRNKKANLVINGGSHSCANSGNSDAGLIGKYGVAWMKRFMDDDTRYSKFLCGAEHQADLSKRAVEAYKENCPY	2021.0		The mc-PET was obtained from a commercial PET bottle. lcPET film with a thickness of 0.25 mm.	Goodfellow	Yes	No				Yes		
Pseudomonas putida	303	PHA	de Eugenio, L. I., Garci, P., Luengo, J. M., San Roma, J., & Garci, J. L. (2007). Biochemical evidence that phaZ gene encodes a specific intracellular medium chain length polyhydroxyalkanoate depolymerase in Pseudomonas putida KT2442: characterization of a paradigmatic enzyme. Journal of Biological Chemistry, 282(7), 4951-4962.	PHA depolymerase	00177	00177 | PHA depolymerase | Pseudomonas putida | PHA	Yes	AAN70570.1	MPQPYIFRTVELDNQSIRTAVRPGKPHLTPLLIFNGIGANLELVFPFIDALDPDLEVIAFDVPGVGGSSTPRNPYRFPGLAKLTARMLDYLDYGQVNVIGVSWGGALAQQFAHDYPERCKKLVLAATAAGAVMVPGKPKVLWMMASPRRYVQPSHVIRIAPMIYGGGFRRDPDLAMHHAAKVRSGGKLGYYWQLFAGLGWTSIHWLHKIRQPTLVLAGDDDPLIPLINMRLLAWRIPNAQLHIIDDGHLFLITRAEAVAPIIMKFLQEERQRAVMHPRPASGG	2007.0	Radiolabeling;Spectrophotometry	For polyhydroxyphenylalkanoates (PHPhAs) production, the strain P. putida U was cultured in a chemically defined medium as described before (33., 39.) containing different concentrations of n-phenylalkanoic acids as the sole carbon sources.		Yes	No				No		
Rhodococcus fascians	1828	PBAT	Soulenthone, P., Tachibana, Y., Muroi, F., Suzuki, M., Ishii, N., Ohta, Y., & Kasuya, K. I. (2020). Characterization of a mesophilic actinobacteria that degrades poly (butylene adipate-co-terephthalate). Polymer Degradation and Stability, 181, 109335.				No			2020.0	Clear zone;Weight loss	Poly(51mol% butylene adipate-co-49mol% butylene terephthalate) (PBAT: ecoflex®, Mn = 1.0×104, Mw/Mn = 1.6)		Yes	No	Soil	Soil	Japan	No		
Rhodococcus fascians	1828	PBS	Soulenthone, P., Tachibana, Y., Muroi, F., Suzuki, M., Ishii, N., Ohta, Y., & Kasuya, K. I. (2020). Characterization of a mesophilic actinobacteria that degrades poly (butylene adipate-co-terephthalate). Polymer Degradation and Stability, 181, 109335.				No			2020.0	Clear zone	poly(butylene succinate)(PBSu,Mn = 3.7×104, Mw/Mn = 4.5)		Yes	No	Soil	Soil	Japan	No		
Rhodococcus fascians	1828	PBSA	Soulenthone, P., Tachibana, Y., Muroi, F., Suzuki, M., Ishii, N., Ohta, Y., & Kasuya, K. I. (2020). Characterization of a mesophilic actinobacteria that degrades poly (butylene adipate-co-terephthalate). Polymer Degradation and Stability, 181, 109335.				No			2020.0	Clear zone	poly(butylene succinate-co-butylene adipate) (PBSA, Mn = 3.4×104, Mw/Mn = 5.1)		Yes	No	Soil	Soil	Japan	No		
Rhodococcus fascians	1828	PCL	Soulenthone, P., Tachibana, Y., Muroi, F., Suzuki, M., Ishii, N., Ohta, Y., & Kasuya, K. I. (2020). Characterization of a mesophilic actinobacteria that degrades poly (butylene adipate-co-terephthalate). Polymer Degradation and Stability, 181, 109335.				No			2020.0	Clear zone	poly(ε-caprolactone) (PCL,Mn = 1.5×104, Mw/Mn = 1.4)		Yes	No	Soil	Soil	Japan	No		
Rhodococcus fascians	1828	PES	Soulenthone, P., Tachibana, Y., Muroi, F., Suzuki, M., Ishii, N., Ohta, Y., & Kasuya, K. I. (2020). Characterization of a mesophilic actinobacteria that degrades poly (butylene adipate-co-terephthalate). Polymer Degradation and Stability, 181, 109335.				No			2020.0	Clear zone	poly(ethylene succinate) (PESu, Mw = 1.5×104, Mw/Mn = 2.8)		Yes	No	Soil	Soil	Japan	No		
Rhodococcus fascians	1828	PBAT	Soulenthone, P., Tachibana, Y., Suzuki, M., Mizuno, T., Ohta, Y., & Kasuya, K. I. (2021). Characterization of a poly (butylene adipate-co-terephthalate) hydrolase from the mesophilic actinobacteria Rhodococcus fascians. Polymer Degradation and Stability, 184, 109481.	Hydrolase	00178	00178 | Hydrolase | Rhodococcus fascians | PBAT PBS PBSA PCL PES	Yes	A0A7I8E2Z4_RHOSO	MKRRLIAYSIAALAISATAVALPTGVASAAPCSDVDVSFARGTGELPGLGITGTPFVNSVKSQLSDRSVSTYAVNYAADFTQASAGPGSRDLVAHLNSVAASCPSTKFVIGGYSQGATVVTNAVGLRTPSSFTGAVIPAAIADRIEAVVVFGNPFGLTGRKIETASSTYGSRTNSFCNFGDPVCQIGGFNTFAHLTYGTNGSTTQGASFAAAQVRS	2021.0	GPC;HPLC;SEM	Poly(butylene adipate-co-terephthalate) (PBAT, ecoflex® Mn = 4.0 × 104, Mw/Mn = 2.1	BASF Japan Ltd	Yes	No	Soil	Soil	Japan	No		
Rhodococcus fascians	1828	PBS	Soulenthone, P., Tachibana, Y., Suzuki, M., Mizuno, T., Ohta, Y., & Kasuya, K. I. (2021). Characterization of a poly (butylene adipate-co-terephthalate) hydrolase from the mesophilic actinobacteria Rhodococcus fascians. Polymer Degradation and Stability, 184, 109481.	Hydrolase	00178	00178 | Hydrolase | Rhodococcus fascians | PBAT PBS PBSA PCL PES	Yes	A0A7I8E2Z4_RHOSO	MKRRLIAYSIAALAISATAVALPTGVASAAPCSDVDVSFARGTGELPGLGITGTPFVNSVKSQLSDRSVSTYAVNYAADFTQASAGPGSRDLVAHLNSVAASCPSTKFVIGGYSQGATVVTNAVGLRTPSSFTGAVIPAAIADRIEAVVVFGNPFGLTGRKIETASSTYGSRTNSFCNFGDPVCQIGGFNTFAHLTYGTNGSTTQGASFAAAQVRS	2021.0	GPC;HPLC;SEM	poly(butylene succinate)(PBSu,Mn = 3.7×104, Mw/Mn = 4.5)		Yes	No	Soil	Soil	Japan	No		
Rhodococcus fascians	1828	PBSA	Soulenthone, P., Tachibana, Y., Suzuki, M., Mizuno, T., Ohta, Y., & Kasuya, K. I. (2021). Characterization of a poly (butylene adipate-co-terephthalate) hydrolase from the mesophilic actinobacteria Rhodococcus fascians. Polymer Degradation and Stability, 184, 109481.	Hydrolase	00178	00178 | Hydrolase | Rhodococcus fascians | PBAT PBS PBSA PCL PES	Yes	A0A7I8E2Z4_RHOSO	MKRRLIAYSIAALAISATAVALPTGVASAAPCSDVDVSFARGTGELPGLGITGTPFVNSVKSQLSDRSVSTYAVNYAADFTQASAGPGSRDLVAHLNSVAASCPSTKFVIGGYSQGATVVTNAVGLRTPSSFTGAVIPAAIADRIEAVVVFGNPFGLTGRKIETASSTYGSRTNSFCNFGDPVCQIGGFNTFAHLTYGTNGSTTQGASFAAAQVRS	2021.0	GPC;HPLC;SEM	poly(butylene succinate-co-butylene adipate) (PBSA, Mn = 3.4×104, Mw/Mn = 5.1)		Yes	No	Soil	Soil	Japan	No		
Rhodococcus fascians	1828	PCL	Soulenthone, P., Tachibana, Y., Suzuki, M., Mizuno, T., Ohta, Y., & Kasuya, K. I. (2021). Characterization of a poly (butylene adipate-co-terephthalate) hydrolase from the mesophilic actinobacteria Rhodococcus fascians. Polymer Degradation and Stability, 184, 109481.	Hydrolase	00178	00178 | Hydrolase | Rhodococcus fascians | PBAT PBS PBSA PCL PES	Yes	A0A7I8E2Z4_RHOSO	MKRRLIAYSIAALAISATAVALPTGVASAAPCSDVDVSFARGTGELPGLGITGTPFVNSVKSQLSDRSVSTYAVNYAADFTQASAGPGSRDLVAHLNSVAASCPSTKFVIGGYSQGATVVTNAVGLRTPSSFTGAVIPAAIADRIEAVVVFGNPFGLTGRKIETASSTYGSRTNSFCNFGDPVCQIGGFNTFAHLTYGTNGSTTQGASFAAAQVRS	2021.0	GPC;HPLC;SEM	poly(ε-caprolactone) (PCL,Mn = 1.5×104, Mw/Mn = 1.4)		Yes	No	Soil	Soil	Japan	No		
Rhodococcus fascians	1828	PES	Soulenthone, P., Tachibana, Y., Suzuki, M., Mizuno, T., Ohta, Y., & Kasuya, K. I. (2021). Characterization of a poly (butylene adipate-co-terephthalate) hydrolase from the mesophilic actinobacteria Rhodococcus fascians. Polymer Degradation and Stability, 184, 109481.	Hydrolase	00178	00178 | Hydrolase | Rhodococcus fascians | PBAT PBS PBSA PCL PES	Yes	A0A7I8E2Z4_RHOSO	MKRRLIAYSIAALAISATAVALPTGVASAAPCSDVDVSFARGTGELPGLGITGTPFVNSVKSQLSDRSVSTYAVNYAADFTQASAGPGSRDLVAHLNSVAASCPSTKFVIGGYSQGATVVTNAVGLRTPSSFTGAVIPAAIADRIEAVVVFGNPFGLTGRKIETASSTYGSRTNSFCNFGDPVCQIGGFNTFAHLTYGTNGSTTQGASFAAAQVRS	2021.0	GPC;HPLC;SEM	poly(ethylene succinate) (PESu, Mw = 1.5×104, Mw/Mn = 2.8)		Yes	No	Soil	Soil	Japan	No		
Bacillus pumilus	1408	PBAT	Muroi, F., Tachibana, Y., Soulenthone, P., Yamamoto, K., Mizuno, T., Sakurai, T., ... & Kasuya, K. I. (2017). Characterization of a poly (butylene adipate-co-terephthalate) hydrolase from the aerobic mesophilic bacterium Bacillus pumilus. Polymer Degradation and Stability, 137, 11-22.	Hydrolase	00179	00179 | Hydrolase | Bacillus pumilus | PBAT PBSA PES PCL	Yes	A0A1E1FNX8_BACPU	MKVILFKKRSLQILVALALVIGSMAFIQPKEVKAAEHNPVVMVHGIGGASYNFASIKSYLVGQGWDRNQLYAIDFIDKTGNNRNNGPRLSKFVQDVLDKTGAKKVDIVAHSMGGANTLYYIKNLDGGDKIENVVTIGGANGLVSSRALPGTDPNQKILYTSVYSSADLIVVNSLSRLIGAKNVLIHGVGHIGLLTSSQVKGYIKEGLNGGGQNTN	2017.0	Clear zone;Weight loss;SEM	Poly(butylene adipate-co-terephthalate) 	BASF		No	Soil	Soil	Japan	No		
Bacillus pumilus	1408	PBSA	Muroi, F., Tachibana, Y., Soulenthone, P., Yamamoto, K., Mizuno, T., Sakurai, T., ... & Kasuya, K. I. (2017). Characterization of a poly (butylene adipate-co-terephthalate) hydrolase from the aerobic mesophilic bacterium Bacillus pumilus. Polymer Degradation and Stability, 137, 11-22.	Hydrolase	00179	00179 | Hydrolase | Bacillus pumilus | PBAT PBSA PES PCL	Yes	A0A1E1FNX8_BACPU	MKVILFKKRSLQILVALALVIGSMAFIQPKEVKAAEHNPVVMVHGIGGASYNFASIKSYLVGQGWDRNQLYAIDFIDKTGNNRNNGPRLSKFVQDVLDKTGAKKVDIVAHSMGGANTLYYIKNLDGGDKIENVVTIGGANGLVSSRALPGTDPNQKILYTSVYSSADLIVVNSLSRLIGAKNVLIHGVGHIGLLTSSQVKGYIKEGLNGGGQNTN	2017.0	Clear zone;Weight loss;SEM	Poly(butylene adipate-co-terephthalate) 	BASF		No	Soil	Soil	Japan	No		
Bacillus pumilus	1408	PES	Muroi, F., Tachibana, Y., Soulenthone, P., Yamamoto, K., Mizuno, T., Sakurai, T., ... & Kasuya, K. I. (2017). Characterization of a poly (butylene adipate-co-terephthalate) hydrolase from the aerobic mesophilic bacterium Bacillus pumilus. Polymer Degradation and Stability, 137, 11-22.	Hydrolase	00179	00179 | Hydrolase | Bacillus pumilus | PBAT PBSA PES PCL	Yes	A0A1E1FNX8_BACPU	MKVILFKKRSLQILVALALVIGSMAFIQPKEVKAAEHNPVVMVHGIGGASYNFASIKSYLVGQGWDRNQLYAIDFIDKTGNNRNNGPRLSKFVQDVLDKTGAKKVDIVAHSMGGANTLYYIKNLDGGDKIENVVTIGGANGLVSSRALPGTDPNQKILYTSVYSSADLIVVNSLSRLIGAKNVLIHGVGHIGLLTSSQVKGYIKEGLNGGGQNTN	2017.0	Clear zone;Weight loss;SEM	Poly(butylene adipate-co-terephthalate) 	BASF		No	Soil	Soil	Japan	No		
Bacillus pumilus	1408	PCL	Muroi, F., Tachibana, Y., Soulenthone, P., Yamamoto, K., Mizuno, T., Sakurai, T., ... & Kasuya, K. I. (2017). Characterization of a poly (butylene adipate-co-terephthalate) hydrolase from the aerobic mesophilic bacterium Bacillus pumilus. Polymer Degradation and Stability, 137, 11-22.	Hydrolase	00179	00179 | Hydrolase | Bacillus pumilus | PBAT PBSA PES PCL	Yes	A0A1E1FNX8_BACPU	MKVILFKKRSLQILVALALVIGSMAFIQPKEVKAAEHNPVVMVHGIGGASYNFASIKSYLVGQGWDRNQLYAIDFIDKTGNNRNNGPRLSKFVQDVLDKTGAKKVDIVAHSMGGANTLYYIKNLDGGDKIENVVTIGGANGLVSSRALPGTDPNQKILYTSVYSSADLIVVNSLSRLIGAKNVLIHGVGHIGLLTSSQVKGYIKEGLNGGGQNTN	2017.0	Clear zone;Weight loss;SEM	Poly(butylene adipate-co-terephthalate) 	BASF		No	Soil	Soil	Japan	No		
Psychrobacter sp.	56811	PE	Zhang, A., Hou, Y., Wang, Q., & Wang, Y. (2022). Characteristics and Polyethylene Biodegradation Function of a Novel Cold-adapted Bacterial Laccase From Antarctic Sea Ice Psychrophile Psychrobacter sp. NJ228. Journal of Hazardous Materials, 129656.	Laccase	00180	00180 | Laccase | Psychrobacter sp. | PE	Yes	UVG67878.1	MASSALGHSSRSGSQGATINSDQNTHKVPILTGKEFDLYVSKQSAIVNGKKSMATLINNSLPAPTLKMREGDTVVIRVHNQMDESTSIHWHGLLVPFEMDGVPGISFDGIPANSTFTYKFKLKQSGTYWYHSHSGFQEQTGMLGAIVIEPKGRERHPIEEDHVIVLSDWTSRNPHNLLKLLKQRADFDNYHLPDFKKLLSDIAETDMKTAFDKRKMWNQMRMMPTDFTDLSGENTFTYLINGKTTAANWAQIVKAGQRVKLRFINASAQTIFDVRIPGLKMTVVATDGIDVAPVAIDDFRIGVAETYDVIVTPTKDAHTIFAQNIDRSGYVAATLATKEGARAATPAMDKIEWLTMADMMGAMGADGYKAKHAKTEYDFKSDMRVDSPRMNLDDPGINLRNIDRKVLNYSQLRSVDEAIFAEQRKPTREIELHLTGNMERYIWAFDGVKFSEATPVNIKPNERVRITLVNDTMMNHPMHLHGMWSDLRMPNGEFQVRKHTIMVQPAQKISFDVTGEAGRWAWHCHLLYHMEAGMFREVAVI	2022.0	Weight loss;WCA;SEM;FTIR;XRD	PE particles with a particle size of 1000 µm and films were produced separately by Thermo Fisher Scientific, and Haimen Yangzi Medical Equipment Co., Ltd. Films (30 mm × 20 mm square sheets)	Thermo Fisher Scientific;Haimen Yangzi Medical Equipment Co	Yes	No	Ice	Marine	Antarctic Ocean	Yes		
Paracoccus sp.	267	PET	Cheng, Y., Chen, J., Bao, M., & Li, Y. (2022). Surface modification ability of Paracoccus sp. indicating its potential for polyethylene terephthalate degradation. International Biodeterioration & Biodegradation, 173, 105454.				No			2022.0	SEM;WCA;FTIR;XPS	Virgin PET pallet (Bottle Grade, BG 80) with crystallinity of 53%; Pure PET film we applied in the experiment was 0.12 mm, with crystallinity of 47%.	Sinopec Yizheng Chemical Fiber Co.	Yes	No	Soil	Soil	China	No		
Lysinibacillus xylanilyticus	582475	LDPE	Oluwole, O. A., Oluyege, J. O., & Olowomofe, T. O. (2022). Biodegradation of polyethylene based films used in water packaging by dumpsite bacteria. Bioremediation Journal, 1-13.				No			2022.0	Weight loss;FTIR;SEM	Fresh polyethylene films used for sachet water packaging were used for the study		No	No	Soil	Plastic waste dumping site	Nigeria	No		
Pseudomonas aeruginosa	287	LDPE	Oluwole, O. A., Oluyege, J. O., & Olowomofe, T. O. (2022). Biodegradation of polyethylene based films used in water packaging by dumpsite bacteria. Bioremediation Journal, 1-13.				No			2022.0	Weight loss;FTIR;SEM	Fresh polyethylene films used for sachet water packaging were used for the study		No	No	Soil	Plastic waste dumping site	Nigeria	No		
Stenotrophomonas maltophilia	40324	LDPE	Oluwole, O. A., Oluyege, J. O., & Olowomofe, T. O. (2022). Biodegradation of polyethylene based films used in water packaging by dumpsite bacteria. Bioremediation Journal, 1-13.				No			2022.0	Weight loss;FTIR;SEM	Fresh polyethylene films used for sachet water packaging were used for the study		No	No	Soil	Plastic waste dumping site	Nigeria	No		
Achromobacter xylosoxidans	85698	LDPE	Oluwole, O. A., Oluyege, J. O., & Olowomofe, T. O. (2022). Biodegradation of polyethylene based films used in water packaging by dumpsite bacteria. Bioremediation Journal, 1-13.				No			2022.0	Weight loss;FTIR;SEM	Fresh polyethylene films used for sachet water packaging were used for the study		No	No	Soil	Plastic waste dumping site	Nigeria	No		
Bacillus licheniformis	1402	PE	Saeed, S., Iqbal, A., & Deeba, F. (2022). Biodegradation study of Polyethylene and PVC using naturally occurring plastic degrading microbes. Archives of Microbiology, 204(8), 1-14.				No			2022.0	Weight loss;FTIR;SEM	PE	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Bacillus licheniformis	1402	PVC	Saeed, S., Iqbal, A., & Deeba, F. (2022). Biodegradation study of Polyethylene and PVC using naturally occurring plastic degrading microbes. Archives of Microbiology, 204(8), 1-14.				No			2022.0	Weight loss;FTIR;SEM	PVC	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Achromobacter xylosoxidans	85698	PE	Saeed, S., Iqbal, A., & Deeba, F. (2022). Biodegradation study of Polyethylene and PVC using naturally occurring plastic degrading microbes. Archives of Microbiology, 204(8), 1-14.				No			2022.0	Weight loss;FTIR;SEM	PE	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Achromobacter xylosoxidans	85698	PVC	Saeed, S., Iqbal, A., & Deeba, F. (2022). Biodegradation study of Polyethylene and PVC using naturally occurring plastic degrading microbes. Archives of Microbiology, 204(8), 1-14.				No			2022.0	Weight loss;FTIR;SEM	PVC	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Aspergillus niger	5061	PE	Saeed, S., Iqbal, A., & Deeba, F. (2022). Biodegradation study of Polyethylene and PVC using naturally occurring plastic degrading microbes. Archives of Microbiology, 204(8), 1-14.				No			2022.0	Weight loss;FTIR;SEM	PE	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Aspergillus niger	5061	PVC	Saeed, S., Iqbal, A., & Deeba, F. (2022). Biodegradation study of Polyethylene and PVC using naturally occurring plastic degrading microbes. Archives of Microbiology, 204(8), 1-14.				No			2022.0	Weight loss;FTIR;SEM	PVC	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Aspergillus glaucus	41413	PE	Saeed, S., Iqbal, A., & Deeba, F. (2022). Biodegradation study of Polyethylene and PVC using naturally occurring plastic degrading microbes. Archives of Microbiology, 204(8), 1-14.				No			2022.0	Weight loss;FTIR;SEM	PE	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Aspergillus glaucus	41413	PVC	Saeed, S., Iqbal, A., & Deeba, F. (2022). Biodegradation study of Polyethylene and PVC using naturally occurring plastic degrading microbes. Archives of Microbiology, 204(8), 1-14.				No			2022.0	Weight loss;FTIR;SEM	PVC	Sigma Aldrich	Yes	No	Soil	Plastic waste dumping site	Pakistan	No		
Cladosporium halotolerans	1052096	PU	Zhang, K., Hu, J., Yang, S., Xu, W., Wang, Z., Zhuang, P., ... & Luo, Z. (2022). Biodegradation of polyester polyurethane by the marine fungus Cladosporium halotolerans 6UPA1. Journal of Hazardous Materials, 437, 129406.				No			2022.0	FTIR;GCMS;SEM;Spectrophotometry;CO2	Impranil DLN;PU foam	Daye Tengfei Foam Factory (Changzhou, China)	No	No	Sediment	Deep sea	Pacific Ocean	No		
Nocardioides zeae	1457234	PLA	Mistry, A. N., Kachenchart, B., Wongthanaroj, A., Somwangthanaroj, A., & Luepromchai, E. (2022). Rapid biodegradation of high molecular weight semi-crystalline polylactic acid at ambient temperature via enzymatic and alkaline hydrolysis by a defined bacterial consortium. Polymer Degradation and Stability, 202, 110051.				No			2022.0	Weight loss;FTIR;DSC	Commercial grade polylactic acid (PLA) polymer, Ingeo 4032D (Dlactide content = 1.4 mol%, melt flow rate (MFR) = 0.7 g/min (210 ◦C, 2.16 kg), density = 1.24 g/cc)	NatureWorks (USA)	Yes	No	Plastic debris	Plastic waste dumping site	Thailand	No		
Stenotrophomonas pavanii	487698	PLA	Mistry, A. N., Kachenchart, B., Wongthanaroj, A., Somwangthanaroj, A., & Luepromchai, E. (2022). Rapid biodegradation of high molecular weight semi-crystalline polylactic acid at ambient temperature via enzymatic and alkaline hydrolysis by a defined bacterial consortium. Polymer Degradation and Stability, 202, 110051.				No			2022.0	Weight loss;FTIR;DSC	Commercial grade polylactic acid (PLA) polymer, Ingeo 4032D (Dlactide content = 1.4 mol%, melt flow rate (MFR) = 0.7 g/min (210 ◦C, 2.16 kg), density = 1.24 g/cc)	NatureWorks (USA)	Yes	No	Plastic debris	Plastic waste dumping site	Thailand	No		
Gordonia desulfuricans	89051	PLA	Mistry, A. N., Kachenchart, B., Wongthanaroj, A., Somwangthanaroj, A., & Luepromchai, E. (2022). Rapid biodegradation of high molecular weight semi-crystalline polylactic acid at ambient temperature via enzymatic and alkaline hydrolysis by a defined bacterial consortium. Polymer Degradation and Stability, 202, 110051.				No			2022.0	Weight loss;FTIR;DSC	Commercial grade polylactic acid (PLA) polymer, Ingeo 4032D (Dlactide content = 1.4 mol%, melt flow rate (MFR) = 0.7 g/min (210 ◦C, 2.16 kg), density = 1.24 g/cc)	NatureWorks (USA)	Yes	No	Plastic debris	Plastic waste dumping site	Thailand	No		
Chitinophaga jiangningensis	1419482	PLA	Mistry, A. N., Kachenchart, B., Wongthanaroj, A., Somwangthanaroj, A., & Luepromchai, E. (2022). Rapid biodegradation of high molecular weight semi-crystalline polylactic acid at ambient temperature via enzymatic and alkaline hydrolysis by a defined bacterial consortium. Polymer Degradation and Stability, 202, 110051.				No			2022.0	Weight loss;FTIR;DSC	Commercial grade polylactic acid (PLA) polymer, Ingeo 4032D (Dlactide content = 1.4 mol%, melt flow rate (MFR) = 0.7 g/min (210 ◦C, 2.16 kg), density = 1.24 g/cc)	NatureWorks (USA)	Yes	No	Plastic debris	Plastic waste dumping site	Thailand	No		
Pseudomonas chlororaphis	587753	PLA	Mohanan, N., Wong, C. H., Budisa, N., & Levin, D. B. (2022). Characterization of Polymer Degrading Lipases, LIP1 and LIP2 From Pseudomonas chlororaphis PA23. Frontiers in bioengineering and biotechnology, 555.	Lipase	00181	00181 | Lipase | Pseudomonas chlororaphis | PLA PHA PES PCL	Yes	AIC18917.1	MTMTLLYRDMNQAQLDAAYNNTQAVPDFPGIYAALQARSASFYASAAGRLNLPYGTAPRQRYDWLPCGKADAPTLIFIHGGYWQNCSKEDFAFIAAGPLAAGFNIVLAEYTLAPQASMTQIVSEIGSLLEHLQADADQLGIAGHKVVLSGHSAGGHLALQFRSHPWVTDVLAISALVDLEPISLSWLNEKLSLSEAEIDAYSPLYHIDKGANTWVAVGADELSELVRQSDEYAKQALARGESVQLIHVPGCTHFSVLDEMAKPQGALLQALSSIR	2022.0	GPC;Clear zone	PLA	Sigma Aldrich	Yes	No	Soybean rhizosphere	Soil		No		
Pseudomonas chlororaphis	587753	PHA	Mohanan, N., Wong, C. H., Budisa, N., & Levin, D. B. (2022). Characterization of Polymer Degrading Lipases, LIP1 and LIP2 From Pseudomonas chlororaphis PA23. Frontiers in bioengineering and biotechnology, 555.	Lipase	00181	00181 | Lipase | Pseudomonas chlororaphis | PLA PHA PES PCL	Yes	AIC18917.1	MTMTLLYRDMNQAQLDAAYNNTQAVPDFPGIYAALQARSASFYASAAGRLNLPYGTAPRQRYDWLPCGKADAPTLIFIHGGYWQNCSKEDFAFIAAGPLAAGFNIVLAEYTLAPQASMTQIVSEIGSLLEHLQADADQLGIAGHKVVLSGHSAGGHLALQFRSHPWVTDVLAISALVDLEPISLSWLNEKLSLSEAEIDAYSPLYHIDKGANTWVAVGADELSELVRQSDEYAKQALARGESVQLIHVPGCTHFSVLDEMAKPQGALLQALSSIR	2022.0	GPC;Clear zone	To prepare the various PHA polymers, the P. putidaLS46 was cultivated in Ramsay’s minimal medium (RMM)		Yes	No	Soybean rhizosphere	Soil		No		
Pseudomonas chlororaphis	587753	PCL	Mohanan, N., Wong, C. H., Budisa, N., & Levin, D. B. (2022). Characterization of Polymer Degrading Lipases, LIP1 and LIP2 From Pseudomonas chlororaphis PA23. Frontiers in bioengineering and biotechnology, 555.	Lipase	00181	00181 | Lipase | Pseudomonas chlororaphis | PLA PHA PES PCL	Yes	AIC18917.1	MTMTLLYRDMNQAQLDAAYNNTQAVPDFPGIYAALQARSASFYASAAGRLNLPYGTAPRQRYDWLPCGKADAPTLIFIHGGYWQNCSKEDFAFIAAGPLAAGFNIVLAEYTLAPQASMTQIVSEIGSLLEHLQADADQLGIAGHKVVLSGHSAGGHLALQFRSHPWVTDVLAISALVDLEPISLSWLNEKLSLSEAEIDAYSPLYHIDKGANTWVAVGADELSELVRQSDEYAKQALARGESVQLIHVPGCTHFSVLDEMAKPQGALLQALSSIR	2022.0	GPC;Clear zone	PCL	Sigma Aldrich	Yes	No	Soybean rhizosphere	Soil		No		
Pseudomonas chlororaphis	587753	PES	Mohanan, N., Wong, C. H., Budisa, N., & Levin, D. B. (2022). Characterization of Polymer Degrading Lipases, LIP1 and LIP2 From Pseudomonas chlororaphis PA23. Frontiers in bioengineering and biotechnology, 555.	Lipase	00181	00181 | Lipase | Pseudomonas chlororaphis | PLA PHA PES PCL	Yes	AIC18917.1	MTMTLLYRDMNQAQLDAAYNNTQAVPDFPGIYAALQARSASFYASAAGRLNLPYGTAPRQRYDWLPCGKADAPTLIFIHGGYWQNCSKEDFAFIAAGPLAAGFNIVLAEYTLAPQASMTQIVSEIGSLLEHLQADADQLGIAGHKVVLSGHSAGGHLALQFRSHPWVTDVLAISALVDLEPISLSWLNEKLSLSEAEIDAYSPLYHIDKGANTWVAVGADELSELVRQSDEYAKQALARGESVQLIHVPGCTHFSVLDEMAKPQGALLQALSSIR	2022.0	GPC;Clear zone	PES	Sigma Aldrich	Yes	No	Soybean rhizosphere	Soil		No		
Pseudomonas chlororaphis	587753	PLA	Mohanan, N., Wong, C. H., Budisa, N., & Levin, D. B. (2022). Characterization of Polymer Degrading Lipases, LIP1 and LIP2 From Pseudomonas chlororaphis PA23. Frontiers in bioengineering and biotechnology, 555.	Lipase	00182	00182 | Lipase | Pseudomonas chlororaphis | PLA PHA PES PCL	Yes	AIC19151.1	MSTLSWVRGVNGTLGWVAPTLVASKMRLAFMTPRERLPRDWELPLLARSERITLRFGLSALRWGQGPAVLLMHGWEGRPTQFASLIDALVGAGYSVVALDGPAHGRSPGHEANVMLFARAMLEAAAELPPLRAVIGHSMGGASAMLAVQLGLRTETLVSIAAPARILGVLRGFARYVRLPPKARSAFIRQVEQDVGMRAAAMDVAHYQLDMPGLIVHAEDDNFVPVKESDLIHEAWFDSRLLRLKEGGHQRVLADPRVIEGVLTLLAGRSLQARQSA	2022.0	GPC;Clear zone	PLA	Sigma Aldrich	Yes	No	Soybean rhizosphere	Soil		No		
Pseudomonas chlororaphis	587753	PHA	Mohanan, N., Wong, C. H., Budisa, N., & Levin, D. B. (2022). Characterization of Polymer Degrading Lipases, LIP1 and LIP2 From Pseudomonas chlororaphis PA23. Frontiers in bioengineering and biotechnology, 555.	Lipase	00182	00182 | Lipase | Pseudomonas chlororaphis | PLA PHA PES PCL	Yes	AIC19151.1	MSTLSWVRGVNGTLGWVAPTLVASKMRLAFMTPRERLPRDWELPLLARSERITLRFGLSALRWGQGPAVLLMHGWEGRPTQFASLIDALVGAGYSVVALDGPAHGRSPGHEANVMLFARAMLEAAAELPPLRAVIGHSMGGASAMLAVQLGLRTETLVSIAAPARILGVLRGFARYVRLPPKARSAFIRQVEQDVGMRAAAMDVAHYQLDMPGLIVHAEDDNFVPVKESDLIHEAWFDSRLLRLKEGGHQRVLADPRVIEGVLTLLAGRSLQARQSA	2022.0	GPC;Clear zone	To prepare the various PHA polymers, the P. putidaLS46 was cultivated in Ramsay’s minimal medium (RMM)		Yes	No	Soybean rhizosphere	Soil		No		
Pseudomonas chlororaphis	587753	PCL	Mohanan, N., Wong, C. H., Budisa, N., & Levin, D. B. (2022). Characterization of Polymer Degrading Lipases, LIP1 and LIP2 From Pseudomonas chlororaphis PA23. Frontiers in bioengineering and biotechnology, 555.	Lipase	00182	00182 | Lipase | Pseudomonas chlororaphis | PLA PHA PES PCL	Yes	AIC19151.1	MSTLSWVRGVNGTLGWVAPTLVASKMRLAFMTPRERLPRDWELPLLARSERITLRFGLSALRWGQGPAVLLMHGWEGRPTQFASLIDALVGAGYSVVALDGPAHGRSPGHEANVMLFARAMLEAAAELPPLRAVIGHSMGGASAMLAVQLGLRTETLVSIAAPARILGVLRGFARYVRLPPKARSAFIRQVEQDVGMRAAAMDVAHYQLDMPGLIVHAEDDNFVPVKESDLIHEAWFDSRLLRLKEGGHQRVLADPRVIEGVLTLLAGRSLQARQSA	2022.0	GPC;Clear zone	PCL	Sigma Aldrich	Yes	No	Soybean rhizosphere	Soil		No		
Pseudomonas chlororaphis	587753	PES	Mohanan, N., Wong, C. H., Budisa, N., & Levin, D. B. (2022). Characterization of Polymer Degrading Lipases, LIP1 and LIP2 From Pseudomonas chlororaphis PA23. Frontiers in bioengineering and biotechnology, 555.	Lipase	00182	00182 | Lipase | Pseudomonas chlororaphis | PLA PHA PES PCL	Yes	AIC19151.1	MSTLSWVRGVNGTLGWVAPTLVASKMRLAFMTPRERLPRDWELPLLARSERITLRFGLSALRWGQGPAVLLMHGWEGRPTQFASLIDALVGAGYSVVALDGPAHGRSPGHEANVMLFARAMLEAAAELPPLRAVIGHSMGGASAMLAVQLGLRTETLVSIAAPARILGVLRGFARYVRLPPKARSAFIRQVEQDVGMRAAAMDVAHYQLDMPGLIVHAEDDNFVPVKESDLIHEAWFDSRLLRLKEGGHQRVLADPRVIEGVLTLLAGRSLQARQSA	2022.0	GPC;Clear zone	PES	Sigma Aldrich	Yes	No	Soybean rhizosphere	Soil		No		
Marinobacter sp.	50741	PET	Meyer Cifuentes, I. E., Wu, P., Zhao, Y., Liu, W., Neumann-Schaal, M., Pfaff, L., ... & Öztürk, B. (2022). Molecular and biochemical differences of the tandem and cold-adapted PET hydrolases Ple628 and Ple629, Isolated From a Marine Microbial Consortium. Frontiers in Bioengineering and Biotechnology, 1010.	PETase	00183	00183 | PETase | Marinobacter sp. | PET PBSeT PBAT Ecovio-FT	Yes	UUT36764.1	MFRTIAKNPVRSLIAAGSLLLSASAFAAGGGGDGGDGGCTSDCGFQRGPDPTVSFLEASSGPYSVRTDNVSSLVGGFGGGTVHYPTGTTGTMAAVVVIPGFVSAESSIEWWGPKLASYGFVVMTIDTNSGFDQPPSRATQINNALDYLLEENDSSSSPYSGMIDPNRLGVIGWSMGGGGTLRVAAEGRIQAAIPLAPWDTSSLRFRNIETPTLIFACESDVIAPVGSHADPFYEAIPDSTDKAFFELNNGSHYCGNGGNSYNNELGRLGVSWMKLHLDQDQRYNQFLCGPDHEDEYRISEYRGTCPY	2022.0	HPLC	PET was in-house synthesized		Yes	No	Marine	Marine		No		
Marinobacter sp.	50741	PBSeT	Meyer Cifuentes, I. E., Wu, P., Zhao, Y., Liu, W., Neumann-Schaal, M., Pfaff, L., ... & Öztürk, B. (2022). Molecular and biochemical differences of the tandem and cold-adapted PET hydrolases Ple628 and Ple629, Isolated From a Marine Microbial Consortium. Frontiers in Bioengineering and Biotechnology, 1010.	PETase	00183	00183 | PETase | Marinobacter sp. | PET PBSeT PBAT Ecovio-FT	Yes	UUT36764.1	MFRTIAKNPVRSLIAAGSLLLSASAFAAGGGGDGGDGGCTSDCGFQRGPDPTVSFLEASSGPYSVRTDNVSSLVGGFGGGTVHYPTGTTGTMAAVVVIPGFVSAESSIEWWGPKLASYGFVVMTIDTNSGFDQPPSRATQINNALDYLLEENDSSSSPYSGMIDPNRLGVIGWSMGGGGTLRVAAEGRIQAAIPLAPWDTSSLRFRNIETPTLIFACESDVIAPVGSHADPFYEAIPDSTDKAFFELNNGSHYCGNGGNSYNNELGRLGVSWMKLHLDQDQRYNQFLCGPDHEDEYRISEYRGTCPY	2022.0	HPLC	Ecovio®FT 2341, and its blend components PBAT and PBSeT were supplied by BASF SE as plastic films.	BASF	Yes	No	Marine	Marine		No		
Marinobacter sp.	50741	PBAT	Meyer Cifuentes, I. E., Wu, P., Zhao, Y., Liu, W., Neumann-Schaal, M., Pfaff, L., ... & Öztürk, B. (2022). Molecular and biochemical differences of the tandem and cold-adapted PET hydrolases Ple628 and Ple629, Isolated From a Marine Microbial Consortium. Frontiers in Bioengineering and Biotechnology, 1010.	PETase	00183	00183 | PETase | Marinobacter sp. | PET PBSeT PBAT Ecovio-FT	Yes	UUT36764.1	MFRTIAKNPVRSLIAAGSLLLSASAFAAGGGGDGGDGGCTSDCGFQRGPDPTVSFLEASSGPYSVRTDNVSSLVGGFGGGTVHYPTGTTGTMAAVVVIPGFVSAESSIEWWGPKLASYGFVVMTIDTNSGFDQPPSRATQINNALDYLLEENDSSSSPYSGMIDPNRLGVIGWSMGGGGTLRVAAEGRIQAAIPLAPWDTSSLRFRNIETPTLIFACESDVIAPVGSHADPFYEAIPDSTDKAFFELNNGSHYCGNGGNSYNNELGRLGVSWMKLHLDQDQRYNQFLCGPDHEDEYRISEYRGTCPY	2022.0	HPLC	Ecovio®FT 2341, and its blend components PBAT and PBSeT were supplied by BASF SE as plastic films.	BASF	Yes	No	Marine	Marine		No		
Marinobacter sp.	50741	Ecovio-FT	Meyer Cifuentes, I. E., Wu, P., Zhao, Y., Liu, W., Neumann-Schaal, M., Pfaff, L., ... & Öztürk, B. (2022). Molecular and biochemical differences of the tandem and cold-adapted PET hydrolases Ple628 and Ple629, Isolated From a Marine Microbial Consortium. Frontiers in Bioengineering and Biotechnology, 1010.	PETase	00183	00183 | PETase | Marinobacter sp. | PET PBSeT PBAT Ecovio-FT	Yes	UUT36764.1	MFRTIAKNPVRSLIAAGSLLLSASAFAAGGGGDGGDGGCTSDCGFQRGPDPTVSFLEASSGPYSVRTDNVSSLVGGFGGGTVHYPTGTTGTMAAVVVIPGFVSAESSIEWWGPKLASYGFVVMTIDTNSGFDQPPSRATQINNALDYLLEENDSSSSPYSGMIDPNRLGVIGWSMGGGGTLRVAAEGRIQAAIPLAPWDTSSLRFRNIETPTLIFACESDVIAPVGSHADPFYEAIPDSTDKAFFELNNGSHYCGNGGNSYNNELGRLGVSWMKLHLDQDQRYNQFLCGPDHEDEYRISEYRGTCPY	2022.0	HPLC	Ecovio®FT 2341, and its blend components PBAT and PBSeT were supplied by BASF SE as plastic films.	BASF	Yes	No	Marine	Marine		No		
Marinobacter sp.	50741	PET	Meyer Cifuentes, I. E., Wu, P., Zhao, Y., Liu, W., Neumann-Schaal, M., Pfaff, L., ... & Öztürk, B. (2022). Molecular and biochemical differences of the tandem and cold-adapted PET hydrolases Ple628 and Ple629, Isolated From a Marine Microbial Consortium. Frontiers in Bioengineering and Biotechnology, 1010.	PETase	00184	00184 | PETase | Marinobacter sp. | PET PBSeT PBAT Ecovio-FT	Yes	UUT36763.1	MFNQIGKKSALSLMAAGSLMFSATALAIGGGGSGGGNNGGGGGCEADCGYERGPDPSVSLLEASTGPFSVRTSNVSSSVRGFGGGTIHYPTNTTGTMAAIVVIPGFVSPESSIAWWGPKLASHGFVVMTIGTNSGFDQPASRASQLNNALDYLIEQNGSSRSPINGMIDTDRLGVMGWSMGGGGTLRVATEGRVSAAIPLAPWDSSSSQFRSIDTPTLIFACENDSTAPVRSHADPFYDAIPDSTAKAFVELDGGGHTCANGSSGFGGSYNDVLSRLGVSWMKLHLDKDQRYNQFVCGPNHESDRSISEYRGTCPY	2022.0	HPLC	PET was in-house synthesized		Yes	No	Marine	Marine		No		
Marinobacter sp.	50741	PBSeT	Meyer Cifuentes, I. E., Wu, P., Zhao, Y., Liu, W., Neumann-Schaal, M., Pfaff, L., ... & Öztürk, B. (2022). Molecular and biochemical differences of the tandem and cold-adapted PET hydrolases Ple628 and Ple629, Isolated From a Marine Microbial Consortium. Frontiers in Bioengineering and Biotechnology, 1010.	PETase	00184	00184 | PETase | Marinobacter sp. | PET PBSeT PBAT Ecovio-FT	Yes	UUT36763.1	MFNQIGKKSALSLMAAGSLMFSATALAIGGGGSGGGNNGGGGGCEADCGYERGPDPSVSLLEASTGPFSVRTSNVSSSVRGFGGGTIHYPTNTTGTMAAIVVIPGFVSPESSIAWWGPKLASHGFVVMTIGTNSGFDQPASRASQLNNALDYLIEQNGSSRSPINGMIDTDRLGVMGWSMGGGGTLRVATEGRVSAAIPLAPWDSSSSQFRSIDTPTLIFACENDSTAPVRSHADPFYDAIPDSTAKAFVELDGGGHTCANGSSGFGGSYNDVLSRLGVSWMKLHLDKDQRYNQFVCGPNHESDRSISEYRGTCPY	2022.0	HPLC	Ecovio®FT 2341, and its blend components PBAT and PBSeT were supplied by BASF SE as plastic films.	BASF	Yes	No	Marine	Marine		No		
Marinobacter sp.	50741	PBAT	Meyer Cifuentes, I. E., Wu, P., Zhao, Y., Liu, W., Neumann-Schaal, M., Pfaff, L., ... & Öztürk, B. (2022). Molecular and biochemical differences of the tandem and cold-adapted PET hydrolases Ple628 and Ple629, Isolated From a Marine Microbial Consortium. Frontiers in Bioengineering and Biotechnology, 1010.	PETase	00184	00184 | PETase | Marinobacter sp. | PET PBSeT PBAT Ecovio-FT	Yes	UUT36763.1	MFNQIGKKSALSLMAAGSLMFSATALAIGGGGSGGGNNGGGGGCEADCGYERGPDPSVSLLEASTGPFSVRTSNVSSSVRGFGGGTIHYPTNTTGTMAAIVVIPGFVSPESSIAWWGPKLASHGFVVMTIGTNSGFDQPASRASQLNNALDYLIEQNGSSRSPINGMIDTDRLGVMGWSMGGGGTLRVATEGRVSAAIPLAPWDSSSSQFRSIDTPTLIFACENDSTAPVRSHADPFYDAIPDSTAKAFVELDGGGHTCANGSSGFGGSYNDVLSRLGVSWMKLHLDKDQRYNQFVCGPNHESDRSISEYRGTCPY	2022.0	HPLC	Ecovio®FT 2341, and its blend components PBAT and PBSeT were supplied by BASF SE as plastic films.	BASF	Yes	No	Marine	Marine		No		
Marinobacter sp.	50741	Ecovio-FT	Meyer Cifuentes, I. E., Wu, P., Zhao, Y., Liu, W., Neumann-Schaal, M., Pfaff, L., ... & Öztürk, B. (2022). Molecular and biochemical differences of the tandem and cold-adapted PET hydrolases Ple628 and Ple629, Isolated From a Marine Microbial Consortium. Frontiers in Bioengineering and Biotechnology, 1010.	PETase	00184	00184 | PETase | Marinobacter sp. | PET PBSeT PBAT Ecovio-FT	Yes	UUT36763.1	MFNQIGKKSALSLMAAGSLMFSATALAIGGGGSGGGNNGGGGGCEADCGYERGPDPSVSLLEASTGPFSVRTSNVSSSVRGFGGGTIHYPTNTTGTMAAIVVIPGFVSPESSIAWWGPKLASHGFVVMTIGTNSGFDQPASRASQLNNALDYLIEQNGSSRSPINGMIDTDRLGVMGWSMGGGGTLRVATEGRVSAAIPLAPWDSSSSQFRSIDTPTLIFACENDSTAPVRSHADPFYDAIPDSTAKAFVELDGGGHTCANGSSGFGGSYNDVLSRLGVSWMKLHLDKDQRYNQFVCGPNHESDRSISEYRGTCPY	2022.0	HPLC	Ecovio®FT 2341, and its blend components PBAT and PBSeT were supplied by BASF SE as plastic films.	BASF	Yes	No	Marine	Marine		No		
Uncultured bacterium	77133	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00185	00185 | PETase | Uncultured bacterium | PET	Yes		MQSPAQSSAPTVELDSGAIAGSTADGVVSFKGIPYAAPPVGNLRWRAPQPVASWTGVRAATEYGYDCIQLPLEGDAAASGGEMSEDCLVLNVWRPAEIAPGERLPVLVWIHGGGFLNGSAAAPIYDGTAFAQQGLVVVSFNYRLGRLGFFAHPALTAANEGPLGNYGLMDQIAALEWVQRNIAAFGGDPARITLMGQSAGGISVMYHLTAPESQGLFHQAAVLSGGGRTYLLGLRNLRESTDALPSAEQSGLAFGRRFGIRGRGRAALRSLRSLSAEEVNGDLSMAALVEKPADYAGLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan102	
Uncultured bacterium	77133	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00186	00186 | PETase | Uncultured bacterium | PET	Yes		MVDITGNGMAATAPTDERIVDKPLPQPQIRSGNVRAMPAARKLAQEHGIDLSTLTGSGPGGVIVKEDVERAITARAVPVSPLQRVNFYSAGYRLDGLLYTPRHLPAGERRPGVVLLVGYTYLKTMVMPDIAKVLNAAGYVALVFDYRGFGESEGPRGRLIPLEQVADARAALTFLAEQSMVDPDRLAVIGISLGGAHAITTAALDQRVRAVVALEPPGHGARWLRSLRRHWEWRQFLSRLAEDRRQRVLSGGSTMVDPLEIVLPDPESQAFLDQVAAEFPQMKVTLPLESAEALIEYVSEDLAGRIAPRPLLIIHSDADQLVPVAEAQAIAERAGSSAQLEIIPGMSHFNWVMPGSPGFTRVTDSIVKFLRNTLPVSADNLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan202	
Uncultured bacterium	77133	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00187	00187 | PETase | Uncultured bacterium | PET	Yes		MVPSAGVGLSGVLHLPAGVSRPVLFLHGFTGNKTESGRLYTDMARVLCSAGYAALRFDFRGHGDSPLPFEEFRISLAVEDARNAAGFLKNVPEVDGTRFGVVGLSMGGGVAVSLAAGREDVGALVLLSPALDWPELFQRARGFFRAEEGYVYWGPHRMRDVYAMETMNFSVMGLAEEIQAPTLIIHSVDDMVVPISQAKRFYEKLKVEKKFIEIEHGGHVFDDYNVRRRIEQEVLDWVKRHLLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan204	
Uncultured bacterium	77133	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00188	00188 | PETase | Uncultured bacterium | PET	Yes		MLIRPVTFRNMNQQIIGILHTPDNIRLNEKVPGILMFHGFTGNKTEAHRLFVHVARSLSEHGFIVLRFDFRGSGDSDGEFEDMTLPGEVSDAERALTFLLRQRNVDKNRIGVIGLSMGGRVAAILASKDRRVKFAVLYSPALGPLRDRSLSFMSKEKIERLNSGEAVEFFAEGWYIKKAFFETVDYIVPLDIMDSIKVPVLIVHGDKDPLIPVGEAIRAYEKIKGVNEKNELYIVRGGDHTFSKKEHTLEVIKKTLDWIRSLGILEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan211	
Uncultured bacterium	77133	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00189	00189 | PETase | Uncultured bacterium | PET	Yes		MARAAPISPLQRVNFYSAGYRLDGLLYTPRHLPAGERRPGVVLLVGYTYLKTMVMPDIAKVLNAAGYVALVFDYRGFGESEGPRGRLIPLEQVADARAALTFLAEQSMVDPDRLAVIGISLGGAHAITTAALDQRVRAVVAIEPPGHGAHWLRSLRRHWEWSQFLSRLTEDRRQRVLSGVSSTVDPLEIVLPDPESQAFLDQVAAEFPQMKVTLPLESAEALIEYVPEDLAGRIAPRPLLLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan214	
Uncultured bacterium	77133	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00190	00190 | PETase | Uncultured bacterium | PET	Yes		MQPYPVGTRTITYQDPVRNNRNIQTYLYYPATAAGANQPVAGGQFPVVVVGHGFTMNYAPYAFWGNALAESGYIVAIPNTETGFSPSHSAFAADMAFLVAKLYTENTNSSSPFYQHVQYNSCIIGHSMGGGCTYLAAQNNADVSATVTFAAAETNPSATAAAANVNCPSLVFSGSADCITPPAQHQVPMYNALPDCKAYGGSSRVDLQACKLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan301	
Uncultured bacterium	77133	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00191	00191 | PETase | Uncultured bacterium | PET	Yes		MQVIQQTVTLQKTQLRLTKEGFVTNYRFPVDFYYPDSPESFPVILISHGFGSVRENFRTLAQHLASHGFLVAVPQHIGSDLQYRQELIKGTLSSALSPVEFLARPTDLSTIIDYLQATQNTGSWQKRANLQQIGVIGDSLGGTTALTIGGAPLDIPRLQTKCTSDNVIVNVALILQCQASFLPPSEYNLADSRVKAVIATHPLISGIFSPDSLAKIQIPVMITAGNFDIITPLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan305	
Uncultured bacterium	77133	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00192	00192 | PETase | Uncultured bacterium | PET	Yes		MQTVTSMLKDLDAVITQVSEKFPQIDNKRVCLIGHSQGAYVSFLHATKDERIKCLVSWMGRLSDLKEFWSKLWFDEIERKGYIYEWDYKITKKYVRDSLKYNLSKAAWRIKVPTLLIYGELDDIVPPSEGMKFYRNIKSPKKIVIVKDLNHTFSGEKAKKSVIRITLKWLSKWLKRLDLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan307	
Uncultured bacterium	77133	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00193	00193 | PETase | Uncultured bacterium | PET	Yes		MANPPGGDPDPGCQTDCNYQRGPDPTDAYLEAASGPYTVSTIRVSSLVPGFGGGTIHYPTNAGGGKMAGIVVIPGYLSFESSIEWWGPRLASHGFVVMTIDTNTIYDQPSQRRDQIEAALQYLVNQSNSSSSPISGMVDSSRLAAVGWSMGGGGTLQLAADGGIKAAIALAPWNSSINDFNRIQVPTLIFACQLDAIAPVALHASPFYNRIPNTTPKAFFEMTGGDHWCANGGNIYSALLGKYGVSWMKLHLDQDTRYAPFLCGPNHAAQTLISEYRGNCPYLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan401	
Ketobacter sp.	2083498	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00194	00194 | PETase | Ketobacter sp. | PET	Yes		MTTPTPTPEPEPEPPGGCGDCYQRGPDPTVAALEADRGPYSVRTINVSSWVSGFGGGTIHYPVGTQGTMGAIAVIPGYVSYENSIEWWGGRLASWGFVVITIDTNSIYDQPDSRANQLSAALDYVIAQSNSSRSAIQGMVDPNRLGAIGWSMGGGGTLKLSTDRYLKAAIPQAPWYSGFNPFDEITTPTLIIACQLDAVAPVAQHASPFYNEIPNSTAKAFLEIRNGDHFCANSGYPDEDILGKYGVAWMKRFIDDDRRYDAFLCGPNHEAEWDISEYRDTCNYLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan403	
Actinomycetota bacterium	2900548	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00195	00195 | PETase | Actinomycetota bacterium | PET	Yes		MQADTDTTAVAPAAANPYERGPAPTEASVTAARGPFAIAQVNVPSGSGAGFNDGTIYYPTDTSQGTFGAVAVIPGFISPQAVIQWFGPRLASQGFVVFTLDSNGLADLPDARGRQLLAALDYLTTQSTVRTRIDPNRLAVMGHSMGGGGTLLAAENRPTLKAAIPLAPWEPDTSWEGVKVPTMIIGGESDVVAPVSSMAIPDYNSLSSAPEKAYLELRSGDHLAPASESPTVAEYALSWLKRFVDDDTRYDQFLCPGPTPDTDISQYLDTCPNGSLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan405	
Micromonosporaceae bacterium	1873464	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00196	00196 | PETase | Micromonosporaceae bacterium | PET	Yes		MADNPYQRGPDPTRDSVAASRGTFATASTTVGSGNGFGAGFIYYPTDTSQGTFGAVAIVPGYTATWAAEGAWMGHWLASFGFVVIGIDTINRNDWDTARGTQLLAALDYLTQRSTVRDRVDASRLAVMGHSMGGGGAMYAALQRPSLKAAVGLAPFSPSQNLNGMRVPTMLLAGQHDTTTTPASITSLYNGIPAATEKAYLELSGAGHGFPTSNNSVMMRKVIPWLKIFVDSDVRYTQFLCPLMDNTGIRSYQSTCPLLPGTPTPPNRYEAETSPAVCTGTIASNHTGYSGTGFCDGNNATNAYAQFTVNASAAGSMTLRVRFANGTTTARPASLIVNGSTVQTPSFEGTGAWTTWATKTLTVTLNAGNNTIRFNPTTANGLPNLDYIEIAAPLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan407	
Ketobacter sp.	2083498	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00197	00197 | PETase | Ketobacter sp. | PET	Yes		MGDCPATAICRSESPGAYSGNGPYGSRSYTLSRFQTPGGATVYYPANAEPPYAGMVFTPPYTGTQAMFAAWGPFFASHGFVLVTMDTSTTLDSVDQRAAQQKEVLNALKSENTRSGSPLRGKLDTARLGAVGWSMGGGATWINSAEYSGLKTAMSLAGHNLTAVDIDSKGYNTRVPTLLFNGAQDLTYLGGLGQSDGVYNNIPAGIPKVFYEVSSAGHFDWGSPTAANRSVASLALAFHKAYLDGDTRWLQYITRPSSDVTTWRTANIRLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan409	
Ketobacter alkanivorans	1917421	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00198	00198 | PETase | Ketobacter alkanivorans | PET	Yes		MSQVPPTPPTDDPMGDCPSTAICRGEAPGSYSGNGPYGSRSYTLSRFQTPGGATVYYPSNAEPPYSGLVFTPPYTGTQAMFRAWGPFFASHGIVLVTMDTSTTVDTVDQRASQQKRVLDVLKQENTRSGSPLRGKLDTSRLGAVGWSMGGGATWINSAEYNGLKTAMSLAGHNMTAIDLDSKGGNTRVPTLLFNGALDLTMLGGLGQSIGVYNAIPRGIPKVIYEVASAGHFDWGSPTAANRSVAGIALAFHKTFLDGDTRWVSYIKRPSSDVATWRTENLPQLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan412	
Nocardioidaceae bacterium	1871072	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00199	00199 | PETase | Nocardioidaceae bacterium | PET	Yes		MESPYERGPDPTSASVLDNGTFSLSSTSVSSLVTGFGGGTIYYPTSTTQGTFGGVVLAPGYTASSSSYSSVARRVASHGFVVFAIDTNSRYDQPDSRGSQILAAVSYLKNSASSTVASRLDETRIAVSGHSMGGGGTLAAANQDSSIKAAVALQPWHTDKTWPGIQIPTMIIGAENDSVAPVASHSIPFYTSMTGAREKAYGEINNGDHFIANTDDDWQGRLFVTWLKRYVDDDTRYSQFLCPAPSSIYLSDYRNTCPDLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan503	
Caldimonas taiwanensis	307483	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00200	00200 | PETase | Caldimonas taiwanensis | PET	Yes		MQAQYQKGPDPTASALERNGPFAIRSTSVSRTSVSGFGGGRLYYPTASGTYGAIAVSPGFTGTSSTMTFWGERLASHGFVVLVIDTITLYDQPDSRARQLKAALDYLATQNGRSSSPIYRKVDTSRRAVAGHSMGGGGSLLAARDNPSYKAAIPMAPWNTSSTAFRTVSVPTMIFGCQDDSIAPVFSHAIPFYNAIPNSTRKNYVEIRNDDHFCVMNGGGHDATLGKLGISWMKRFVDNDTRYSPFVCGAEYNRVVSSYEVSRSYNNCPYLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan504	
Marinactinospora thermotolerans	531310	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00201	00201 | PETase | Marinactinospora thermotolerans | PET	Yes		MSNPYERGPAPTESSVTAVRGYFDTDTDTVSSLVSGFGGGTIYYPTDTSEGTFGGVVIAPGYTASQSSMAWMGHRIASQGFVVFTIDTITRYDQPDSRGRQIEAALDYLVEDSDVADRVDGNRLAVMGHSMGGGGTLAAAENRPELRAAIPLTPWHLQKNWSDVEVPTMIIGAENDTVASVRTHSIPFYESLDEDLERAYLELDGASHFAPNISNTVIAKYSISWLKRFVDEDERYEQFLCPPPDTGLFSDFSDYRDSCPHTTLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan606	
Saccharopolyspora flava	95161	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00202	00202 | PETase | Saccharopolyspora flava | PET	Yes		MAEPADVHGPDPTEESITAPRGPFEVDEESVSRLSVSGFGGGTIYYPTDTTDGLFSAVSISPGFTGTQETMAWYGPRLASQGFVVFTIDTITTTDQPDSRARQLQASLDYLVNDSDVKDIIDPARLGVMGHSMGGGGSLKAALDNPALKAAIPLTPWHTTKDFSGVQTPTLIIGAQNDTVAPVSQHAKPFYESLPDDPGKAYLELAGASHLAPNTDNTTIAKFSIAWLKRFLDDDTRYDQFLCPPPENDDSISDYQSTCPYLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan611	
Thermobifida fusca	2021	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00203	00203 | PETase | Thermobifida fusca | PET	Yes		MANPYERGPNPTDALLEARSGPFSVSEENVSRLSASGFGGGTIYYPRENNTYGAVAISPGYTGTEASIAWLGKRIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGSLRLASQRPDLKAAIPLTPWHLNKNWSSVRVPTLIIGADLDTIAPVLTHARPFYNSLPTSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPFLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan701	
Thermobifida fusca	2021	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00204	00204 | PETase | Thermobifida fusca | PET	Yes		MAANPYERGPNPTDALLEARSGPFSVSEENVSRLSASGFGGGTIYYPRESNTYGAVAISPGYTGTEASIAWLGERIASHGFVVITIDTITTLDQPDSRAEQLNAALNHMINRASSTVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVTVPTLIIGADLDTIAPVATHAKPFYNSLPSSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKWFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPFLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan702	
Thermobifida alba	53522	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00205	00205 | PETase | Thermobifida alba | PET	Yes		MANPYERGPNPTESMLEARSGPFSVSEERASRLGADGFGGGTIYYPRENNTYGAIAISPGYTGTQSSIAWLGERIASHGFVVIAIDTNTTLDQPDSRARQLNAALDYMLTDASSSVRNRIDASRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKSWRDITVPTLIIGADLDTIAPVSSHSEPFYNSIPSSTDKAYLELNNATHFAPNITNKTIGMYSVAWLKRFVDEDTRYTQFLCPGPRTGLLSDVDEYRSTCPFLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan708	
Thermobifida cellulosilytica	144786	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00206	00206 | PETase | Thermobifida cellulosilytica | PET	Yes		MANPYERGPDPTQASLEASRGPFPVSEERVSSPVSGFGGGTIYYPQENNTYGAVAISPGYTATQSSVAWLGERIASHGFVVITIDTNTTLDQPDSRADQLEAALDHMVDGASSTVRSRIDRNRLAVMGHSMGGGGTLRLASRRPDLKAAIPLTPWHLNKSWSNVQVPTLIIGAENDTVAPVALHAEPSYTSIPTSTRKAYLELNGASHFAPSVANATIGMYGVAWLKRFVDEDTRYTRFLCPGPRTGLFSDVEEYRSTCPFLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan711	
Thermobifida halotolerans	483545	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00207	00207 | PETase | Thermobifida halotolerans | PET	Yes		MANPYERGPNPTNSSIEALRGPYSVSEDSVSSLVSGFGGGTIYYPTGTNETFGAVAISPGYTGTQSSISWLGPRLASQGFVVMTIDTNTTLDQPDSRASQLDAALDYMVNRSSSTVRNRIDLEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan712	
Thermobifida cellulosilytica	144786	PET	Erickson, E., Gado, J. E., Avilán, L., Bratti, F., Brizendine, R. K., Cox, P. A., ... & McGeehan, J. E. (2022). Sourcing thermotolerant poly (ethylene terephthalate) hydrolase scaffolds from natural diversity. Nature Communications, 13(1), 7850.	PETase	00208	00208 | PETase | Thermobifida cellulosilytica | PET	Yes		MANPYERGPNPTDALLEARSGPFSVSEENVSRFGADGFGGGTIYYPRENNTYGAVAISPGYTGTQASVAWLGERIASHGFVVITIDTNTTLDQPDSRARQLNAALDYMINDASSAVRSRIDSSRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKNWSSVRVPTLIIGADLDTIAPVLTHARPFYNSLPTSISKAYLELDGATHFAPNIPNKIIGKYSVAWLKRFVDNDTRYTQFLCPGPRDGLFGEVEEYRSTCPFALELEHHHHHH	2022.0	HPLC	Amorphous PET film (Goodfellow Product ES30-FM-000145) and crystalline PET powder (Goodfellow Product ES30-PD-006031) were purchased from Goodfellow Corporation (USA). 	Goodfellow Corporation (USA)	Yes	Yes				Yes	PETcan716	
Bacillus velezensis	492670	PU	Gui, Z., Liu, G., Liu, X., Cai, R., Liu, R., & Sun, C. (2023). A Deep-Sea Bacterium Is Capable of Degrading Polyurethane. Microbiology Spectrum, e00073-23.	Oxidoreductase	00209	00209 | Oxidoreductase | Bacillus velezensis | PU PBAT	Yes	UOM43036.1	MGSAQLTGRVIFKGDPGYTQAVKNWNPYVDVCPLVFVFAQNSYDVSNAIKWAREKNVPMRVRSGRHALDKNLSTVSDGIVIDVSDMNKVFLDEKNAVATVQTGIHVGPLVKGLAREGFMAPFGDSPTVGIGGITMGGGFGVLSRSIGLISDNLLALKMVDAKGRIIQANQSRNEDLLWASRGGGGGNFGYNTQYTFKVHRAPKTATVFNIIWPWEQLETVFKAWQKWAPFTDERLGCYLEIYSKVNGLCHVEGLFLGSKPELVQLLKPLLNAGTPAQTVIKTLYYPDCIDFLDPDEPIPGRSDQSVKFSSAWALNLWPEEPIAVMRQFLEKATGTETNFFFINWGGAISRVPSSETAFYWRRPLFYTEWTASWKNKSQEASNLASVERVRQLMKPYVTGSYVNVPDQNIENFGKAYYGSNFARLQRIKAKYDPENVFRFPQSIPPSYK	2023.0	Clear zone;LCMS;FTIR	Waterbourne polyurethane (8 mL/L)		No	No	Sediment	Marine	China	No		
Bacillus velezensis	492670	PBAT	Gui, Z., Liu, G., Liu, X., Cai, R., Liu, R., & Sun, C. (2023). A Deep-Sea Bacterium Is Capable of Degrading Polyurethane. Microbiology Spectrum, e00073-23.	Oxidoreductase	00209	00209 | Oxidoreductase | Bacillus velezensis | PU PBAT	Yes	UOM43036.1	MGSAQLTGRVIFKGDPGYTQAVKNWNPYVDVCPLVFVFAQNSYDVSNAIKWAREKNVPMRVRSGRHALDKNLSTVSDGIVIDVSDMNKVFLDEKNAVATVQTGIHVGPLVKGLAREGFMAPFGDSPTVGIGGITMGGGFGVLSRSIGLISDNLLALKMVDAKGRIIQANQSRNEDLLWASRGGGGGNFGYNTQYTFKVHRAPKTATVFNIIWPWEQLETVFKAWQKWAPFTDERLGCYLEIYSKVNGLCHVEGLFLGSKPELVQLLKPLLNAGTPAQTVIKTLYYPDCIDFLDPDEPIPGRSDQSVKFSSAWALNLWPEEPIAVMRQFLEKATGTETNFFFINWGGAISRVPSSETAFYWRRPLFYTEWTASWKNKSQEASNLASVERVRQLMKPYVTGSYVNVPDQNIENFGKAYYGSNFARLQRIKAKYDPENVFRFPQSIPPSYK	2023.0	Clear zone;LCMS;SEM	PBAT film		No	No	Sediment	Marine	China	No		
Thermobifida fusca	2021	PBAT	Yang, Y., Min, J., Xue, T., Jiang, P., Liu, X., Peng, R., Huang, J. W., Qu, Y., Li, X., Ma, N., Tsai, F. C., Dai, L., Zhang, Q., Liu, Y., Chen, C. C., & Guo, R. T. (2023). Complete bio-degradation of poly (butylene adipate-co-terephthalate) via engineered cutinases. Nature Communications, 14(1), 1645.	Cutinase			No			2023.0	Weight loss	UV-treated PBAT film	Shanghai Hongrui Biotechnology Co., Ltd	Yes	No				No		
Pseudomonas chlororaphis	587753	PHBV	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	Lipase	00210	00210 | Lipase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_02420	MSQELATRYPLVLVPGMLGFIRLVLYSYWFGIASALRRGGATVIAVQVSPLHSTEVRGEQLLARIEEIRRETGADKVNLIGHSQGALTARYAAAKRPGWVASVTSVAGPNHGSELADYIERHHSIDTLRGRVLSFILRVIAVLMSWLDTGYRGPKLPADIHASHRSLTSEGVALFNRQYPQGLPETWGGQGPEEVNGVRYYSWSGTLQPGKTNRGRNLFDGTNRSCRLFARTFVREAGQCDGMVGRYSSHLGTVIGDDYPLDHFDIVNQSLGLVGRGAEPIRLFVEHAQRLKAAGV	2023.0	GPC;Weight loss	Prepared from biodiesel fatty acid supplemented with 0.5% valeric acid using Cuprividusnecator H16		No	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PHA	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	Lipase	00210	00210 | Lipase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_02420	MSQELATRYPLVLVPGMLGFIRLVLYSYWFGIASALRRGGATVIAVQVSPLHSTEVRGEQLLARIEEIRRETGADKVNLIGHSQGALTARYAAAKRPGWVASVTSVAGPNHGSELADYIERHHSIDTLRGRVLSFILRVIAVLMSWLDTGYRGPKLPADIHASHRSLTSEGVALFNRQYPQGLPETWGGQGPEEVNGVRYYSWSGTLQPGKTNRGRNLFDGTNRSCRLFARTFVREAGQCDGMVGRYSSHLGTVIGDDYPLDHFDIVNQSLGLVGRGAEPIRLFVEHAQRLKAAGV	2023.0	GPC;Weight loss	Various PHA polymers synthesised by cultivating Pseudomonas putida in a bioreactor with Ramsey's minimal medium with either hexanoic, octanoic, nonanoic, or decanoic acid as the sole carbon source		No	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PLA	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	Lipase	00210	00210 | Lipase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_02420	MSQELATRYPLVLVPGMLGFIRLVLYSYWFGIASALRRGGATVIAVQVSPLHSTEVRGEQLLARIEEIRRETGADKVNLIGHSQGALTARYAAAKRPGWVASVTSVAGPNHGSELADYIERHHSIDTLRGRVLSFILRVIAVLMSWLDTGYRGPKLPADIHASHRSLTSEGVALFNRQYPQGLPETWGGQGPEEVNGVRYYSWSGTLQPGKTNRGRNLFDGTNRSCRLFARTFVREAGQCDGMVGRYSSHLGTVIGDDYPLDHFDIVNQSLGLVGRGAEPIRLFVEHAQRLKAAGV	2023.0	GPC;Weight loss		Sigma-Aldrich	Yes	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PCL	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	Lipase	00210	00210 | Lipase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_02420	MSQELATRYPLVLVPGMLGFIRLVLYSYWFGIASALRRGGATVIAVQVSPLHSTEVRGEQLLARIEEIRRETGADKVNLIGHSQGALTARYAAAKRPGWVASVTSVAGPNHGSELADYIERHHSIDTLRGRVLSFILRVIAVLMSWLDTGYRGPKLPADIHASHRSLTSEGVALFNRQYPQGLPETWGGQGPEEVNGVRYYSWSGTLQPGKTNRGRNLFDGTNRSCRLFARTFVREAGQCDGMVGRYSSHLGTVIGDDYPLDHFDIVNQSLGLVGRGAEPIRLFVEHAQRLKAAGV	2023.0	GPC;Weight loss		Sigma-Aldrich	Yes	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PES	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	Lipase	00210	00210 | Lipase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_02420	MSQELATRYPLVLVPGMLGFIRLVLYSYWFGIASALRRGGATVIAVQVSPLHSTEVRGEQLLARIEEIRRETGADKVNLIGHSQGALTARYAAAKRPGWVASVTSVAGPNHGSELADYIERHHSIDTLRGRVLSFILRVIAVLMSWLDTGYRGPKLPADIHASHRSLTSEGVALFNRQYPQGLPETWGGQGPEEVNGVRYYSWSGTLQPGKTNRGRNLFDGTNRSCRLFARTFVREAGQCDGMVGRYSSHLGTVIGDDYPLDHFDIVNQSLGLVGRGAEPIRLFVEHAQRLKAAGV	2023.0	GPC;Weight loss		Sigma-Aldrich	Yes	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PHBV	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	Lipase	00211	00211 | Lipase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_21540	MNTFSKVLTGSLLALSINTAFAEGGVEHNTQAFLDALNAGSGKPMEQMTPKEARAVLVGAQAGVKLTLPKADVSQKTIKVDGQDISLTIVRPAGVKGTLPVFMFFHGGGWVLGDFPTHERLVRDLVVGSGAAAVFVNYTPSPEAHYPVAINQAYAATKWVAEHGQEINVDGKRLAVAGNSVGGNMAAVVSLMAKDKGTPAIRFQLLLWPVTDANFETASYNQYAEGHFLSKNMMKWFWDNYTTDARQRNEIYASPLRATSAQLKGLPPALIQTAGADVLRDEGEAYARKLDEAGVTVTSVRYNGMIHDYGLLNVVSQVPAVRSALLQASEELKQHLK	2023.0	GPC;Weight loss	Prepared from biodiesel fatty acid supplemented with 0.5% valeric acid using Cuprividusnecator H16		No	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PHO	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	Lipase	00211	00211 | Lipase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_21540	MNTFSKVLTGSLLALSINTAFAEGGVEHNTQAFLDALNAGSGKPMEQMTPKEARAVLVGAQAGVKLTLPKADVSQKTIKVDGQDISLTIVRPAGVKGTLPVFMFFHGGGWVLGDFPTHERLVRDLVVGSGAAAVFVNYTPSPEAHYPVAINQAYAATKWVAEHGQEINVDGKRLAVAGNSVGGNMAAVVSLMAKDKGTPAIRFQLLLWPVTDANFETASYNQYAEGHFLSKNMMKWFWDNYTTDARQRNEIYASPLRATSAQLKGLPPALIQTAGADVLRDEGEAYARKLDEAGVTVTSVRYNGMIHDYGLLNVVSQVPAVRSALLQASEELKQHLK	2023.0	GPC;Weight loss	Various PHA polymers synthesised by cultivating Pseudomonas putida in a bioreactor with Ramsey's minimal medium with either hexanoic, octanoic, nonanoic, or decanoic acid as the sole carbon source		No	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PLA	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	Lipase	00211	00211 | Lipase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_21540	MNTFSKVLTGSLLALSINTAFAEGGVEHNTQAFLDALNAGSGKPMEQMTPKEARAVLVGAQAGVKLTLPKADVSQKTIKVDGQDISLTIVRPAGVKGTLPVFMFFHGGGWVLGDFPTHERLVRDLVVGSGAAAVFVNYTPSPEAHYPVAINQAYAATKWVAEHGQEINVDGKRLAVAGNSVGGNMAAVVSLMAKDKGTPAIRFQLLLWPVTDANFETASYNQYAEGHFLSKNMMKWFWDNYTTDARQRNEIYASPLRATSAQLKGLPPALIQTAGADVLRDEGEAYARKLDEAGVTVTSVRYNGMIHDYGLLNVVSQVPAVRSALLQASEELKQHLK	2023.0	GPC;Weight loss		Sigma-Aldrich	Yes	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PCL	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	Lipase	00211	00211 | Lipase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_21540	MNTFSKVLTGSLLALSINTAFAEGGVEHNTQAFLDALNAGSGKPMEQMTPKEARAVLVGAQAGVKLTLPKADVSQKTIKVDGQDISLTIVRPAGVKGTLPVFMFFHGGGWVLGDFPTHERLVRDLVVGSGAAAVFVNYTPSPEAHYPVAINQAYAATKWVAEHGQEINVDGKRLAVAGNSVGGNMAAVVSLMAKDKGTPAIRFQLLLWPVTDANFETASYNQYAEGHFLSKNMMKWFWDNYTTDARQRNEIYASPLRATSAQLKGLPPALIQTAGADVLRDEGEAYARKLDEAGVTVTSVRYNGMIHDYGLLNVVSQVPAVRSALLQASEELKQHLK	2023.0	GPC;Weight loss		Sigma-Aldrich	Yes	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PES	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	Lipase	00211	00211 | Lipase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_21540	MNTFSKVLTGSLLALSINTAFAEGGVEHNTQAFLDALNAGSGKPMEQMTPKEARAVLVGAQAGVKLTLPKADVSQKTIKVDGQDISLTIVRPAGVKGTLPVFMFFHGGGWVLGDFPTHERLVRDLVVGSGAAAVFVNYTPSPEAHYPVAINQAYAATKWVAEHGQEINVDGKRLAVAGNSVGGNMAAVVSLMAKDKGTPAIRFQLLLWPVTDANFETASYNQYAEGHFLSKNMMKWFWDNYTTDARQRNEIYASPLRATSAQLKGLPPALIQTAGADVLRDEGEAYARKLDEAGVTVTSVRYNGMIHDYGLLNVVSQVPAVRSALLQASEELKQHLK	2023.0	GPC;Weight loss		Sigma-Aldrich	Yes	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PHBV	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	PHA depolymerase	00212	00212 | PHA depolymerase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_01535	MPQPFIFRTVDLDGQTIRTAVRPGKPHLTPLLIFNGIGANLELVFPFVQALDPDLEVIAFDVPGVGGSSTPSRPYRFPGLAKLTTRMLDYLDYGQVNVVGVSWGGALAQQFAYDYPERCKKLVLAATAAGAFMVPGKPKVLWMMASPRRYIQPSHVIRIAPLIYGGSFRRDPNLAAEHASKVRSAGKLGYYWQLFAGLGWTSIHWLHKIHQPTLVLAGDDDPLIPLINMRMLAWRIPNAQLHIIDDGHLFLITRAEAVAPIIMKFLEEERQRAVMHPHPTPFSGT	2023.0	GPC;Weight loss	Prepared from biodiesel fatty acid supplemented with 0.5% valeric acid using Cuprividusnecator H16		No	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PHO	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	PHA depolymerase	00212	00212 | PHA depolymerase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_01535	MPQPFIFRTVDLDGQTIRTAVRPGKPHLTPLLIFNGIGANLELVFPFVQALDPDLEVIAFDVPGVGGSSTPSRPYRFPGLAKLTTRMLDYLDYGQVNVVGVSWGGALAQQFAYDYPERCKKLVLAATAAGAFMVPGKPKVLWMMASPRRYIQPSHVIRIAPLIYGGSFRRDPNLAAEHASKVRSAGKLGYYWQLFAGLGWTSIHWLHKIHQPTLVLAGDDDPLIPLINMRMLAWRIPNAQLHIIDDGHLFLITRAEAVAPIIMKFLEEERQRAVMHPHPTPFSGT	2023.0	GPC;Weight loss	Various PHA polymers synthesised by cultivating Pseudomonas putida in a bioreactor with Ramsey's minimal medium with either hexanoic, octanoic, nonanoic, or decanoic acid as the sole carbon source		No	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PLA	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	PHA depolymerase	00212	00212 | PHA depolymerase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_01535	MPQPFIFRTVDLDGQTIRTAVRPGKPHLTPLLIFNGIGANLELVFPFVQALDPDLEVIAFDVPGVGGSSTPSRPYRFPGLAKLTTRMLDYLDYGQVNVVGVSWGGALAQQFAYDYPERCKKLVLAATAAGAFMVPGKPKVLWMMASPRRYIQPSHVIRIAPLIYGGSFRRDPNLAAEHASKVRSAGKLGYYWQLFAGLGWTSIHWLHKIHQPTLVLAGDDDPLIPLINMRMLAWRIPNAQLHIIDDGHLFLITRAEAVAPIIMKFLEEERQRAVMHPHPTPFSGT	2023.0	GPC;Weight loss		Sigma-Aldrich	Yes	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PCL	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	PHA depolymerase	00212	00212 | PHA depolymerase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_01535	MPQPFIFRTVDLDGQTIRTAVRPGKPHLTPLLIFNGIGANLELVFPFVQALDPDLEVIAFDVPGVGGSSTPSRPYRFPGLAKLTTRMLDYLDYGQVNVVGVSWGGALAQQFAYDYPERCKKLVLAATAAGAFMVPGKPKVLWMMASPRRYIQPSHVIRIAPLIYGGSFRRDPNLAAEHASKVRSAGKLGYYWQLFAGLGWTSIHWLHKIHQPTLVLAGDDDPLIPLINMRMLAWRIPNAQLHIIDDGHLFLITRAEAVAPIIMKFLEEERQRAVMHPHPTPFSGT	2023.0	GPC;Weight loss		Sigma-Aldrich	Yes	No	Rhizosphere of soybean	Plant associated		No		
Pseudomonas chlororaphis	587753	PES	Mohanan, N., Wong, M. C. H., Budisa, N., & Levin, D. B. (2023). Polymer-Degrading Enzymes of Pseudomonas chloroaphis PA23 Display Broad Substrate Preferences. International Journal of Molecular Sciences, 24(5), 4501.	PHA depolymerase	00212	00212 | PHA depolymerase | Pseudomonas chlororaphis | PHBV PHA PLA PCL PES	Yes	EY04_01535	MPQPFIFRTVDLDGQTIRTAVRPGKPHLTPLLIFNGIGANLELVFPFVQALDPDLEVIAFDVPGVGGSSTPSRPYRFPGLAKLTTRMLDYLDYGQVNVVGVSWGGALAQQFAYDYPERCKKLVLAATAAGAFMVPGKPKVLWMMASPRRYIQPSHVIRIAPLIYGGSFRRDPNLAAEHASKVRSAGKLGYYWQLFAGLGWTSIHWLHKIHQPTLVLAGDDDPLIPLINMRMLAWRIPNAQLHIIDDGHLFLITRAEAVAPIIMKFLEEERQRAVMHPHPTPFSGT	2023.0	GPC;Weight loss		Sigma-Aldrich	Yes	No	Rhizosphere of soybean	Plant associated		No		
Aquabacterium sp.	1872578	PCL	Yoon, Y., Park, H., An, S., Ahn, J. H., Kim, B., Shin, J., Kim, Y., Yeon, J., Chung, J., Kim, D., & Cho, M. (2023). Bacterial degradation kinetics of poly (Ɛ-caprolactone)(PCL) film by Aquabacterium sp. CY2-9 isolated from plastic-contaminated landfill. Journal of Environmental Management, 335, 117493.	No			No			2023.0	Clear zone;TGA;DSC;SEM;FTIR	PCL pellets of different number average molecular weights were dissolved in chloroform to create PCL film for use both in agar media and dried	Sigma-Aldrich	Yes	No	Soil	Landfill	South Korea	No		
Bacillus cereus	1396	HDPE	Gupta, K. K., Sharma, K. K., & Chandra, H. (2023). Utilization of Bacillus cereus strain CGK5 associated with cow feces in the degradation of commercially available high-density polyethylene (HDPE). Archives of Microbiology, 205(3), 101.	No			No			2023.0	FTIR;FE-SEM;EDX;Weight loss	High density polyethylene films (0.95 g/cm3) were purchased from Uttarakhand Packaging Industries Haridwar, India. Films were cut into small pieces (dimension 1 × 1 cm), immersed in xylene, and boiled for 5–15 min to dissolve completely. The resulting residue was crushed followed by washing with ethanol 2–3 times to eliminate residual xylene. The polyethylene powder thus obtained was kept for ethanol evaporation and then dried at 60 °C overnight in a hot air oven.	Uttarakhand Packaging Industries Haridwar 	No	No	Cow dung	Animal associated	India	No		
Sarcina aurantiaca	1266	PET	Maheswaran, B., Al-Ansari, M., Al-Humaid, L., Raj, J. S., Kim, W., Karmegam, N., & Rafi, K. M. (2023). In vivo degradation of polyethylene terephthalate using microbial isolates from plastic polluted environment. Chemosphere, 310, 136757.	No			No			2023.0	Weight loss;FE-SEM;FTIR	PET packaging plastic was cut into square sheet strips of 3 cm × 3 cm size and was used as a major carbon source. Following the weighing and disinfecting with 70% alcohol for 30 min, the thin PET film was trans- ferred to sterile aquadest for 20 min and then UV irradiated for 15 min at 365 nm wavelength		No	No	Sediment	River	India	No		
Bacillus subtilis	1423	PET	Maheswaran, B., Al-Ansari, M., Al-Humaid, L., Raj, J. S., Kim, W., Karmegam, N., & Rafi, K. M. (2023). In vivo degradation of polyethylene terephthalate using microbial isolates from plastic polluted environment. Chemosphere, 310, 136757.	No			No			2023.0	Weight loss;FE-SEM;FTIR	PET packaging plastic was cut into square sheet strips of 3 cm × 3 cm size and was used as a major carbon source. Following the weighing and disinfecting with 70% alcohol for 30 min, the thin PET film was trans- ferred to sterile aquadest for 20 min and then UV irradiated for 15 min at 365 nm wavelength		No	No	Sediment	River	India	No		
Aspergillus flavus	5059	PET	Maheswaran, B., Al-Ansari, M., Al-Humaid, L., Raj, J. S., Kim, W., Karmegam, N., & Rafi, K. M. (2023). In vivo degradation of polyethylene terephthalate using microbial isolates from plastic polluted environment. Chemosphere, 310, 136757.	No			No			2023.0	Weight loss;FE-SEM;FTIR	PET packaging plastic was cut into square sheet strips of 3 cm × 3 cm size and was used as a major carbon source. Following the weighing and disinfecting with 70% alcohol for 30 min, the thin PET film was trans- ferred to sterile aquadest for 20 min and then UV irradiated for 15 min at 365 nm wavelength		No	No	Sediment	River	India	No		
Aspergillus niger	5061	PET	Maheswaran, B., Al-Ansari, M., Al-Humaid, L., Raj, J. S., Kim, W., Karmegam, N., & Rafi, K. M. (2023). In vivo degradation of polyethylene terephthalate using microbial isolates from plastic polluted environment. Chemosphere, 310, 136757.	No			No			2023.0	Weight loss;FE-SEM;FTIR	PET packaging plastic was cut into square sheet strips of 3 cm × 3 cm size and was used as a major carbon source. Following the weighing and disinfecting with 70% alcohol for 30 min, the thin PET film was trans- ferred to sterile aquadest for 20 min and then UV irradiated for 15 min at 365 nm wavelength		No	No	Sediment	River	India	No		
Sterigmatomyces halophilus	5617	LDPE	Elsamahy, T., Sun, J., Elsilk, S. E., & Ali, S. S. (2023). Biodegradation of low-density polyethylene plastic waste by a constructed tri-culture yeast consortium from wood-feeding termite: Degradation mechanism and pathway. Journal of Hazardous Materials, 448, 130944.	No			No			2023.0	Weight loss;WCA;Tensile strengh;FTIR;SEM	Flexible film of LDPE Labware (25 μm thickness, Tg = − 125 ◦C, and crystallinity of 50%) was purchased from ThermoFisher Scientific Co., China. Twenty sheets of LDPE film were used in the experiments with a weight of 0.025 g per sheet. Each LDPE sheet was cut into equal pieces with the same surface area (2.5 ×2.5 cm2) and washed with 75% ethanol.	ThermoFisher Scientific Co.	Yes	No	Termite gut	Animal associated		No		
Meyerozyma guilliermondii	4929	LDPE	Elsamahy, T., Sun, J., Elsilk, S. E., & Ali, S. S. (2023). Biodegradation of low-density polyethylene plastic waste by a constructed tri-culture yeast consortium from wood-feeding termite: Degradation mechanism and pathway. Journal of Hazardous Materials, 448, 130944.	No			No			2023.0	Weight loss;WCA;Tensile strengh;FTIR;SEM	Flexible film of LDPE Labware (25 μm thickness, Tg = − 125 ◦C, and crystallinity of 50%) was purchased from ThermoFisher Scientific Co., China. Twenty sheets of LDPE film were used in the experiments with a weight of 0.025 g per sheet. Each LDPE sheet was cut into equal pieces with the same surface area (2.5 ×2.5 cm2) and washed with 75% ethanol.	ThermoFisher Scientific Co.	Yes	No	Termite gut	Animal associated		No		
Meyerozyma caribbica	66948	LDPE	Elsamahy, T., Sun, J., Elsilk, S. E., & Ali, S. S. (2023). Biodegradation of low-density polyethylene plastic waste by a constructed tri-culture yeast consortium from wood-feeding termite: Degradation mechanism and pathway. Journal of Hazardous Materials, 448, 130944.	No			No			2023.0	Weight loss;WCA;Tensile strengh;FTIR;SEM	Flexible film of LDPE Labware (25 μm thickness, Tg = − 125 ◦C, and crystallinity of 50%) was purchased from ThermoFisher Scientific Co., China. Twenty sheets of LDPE film were used in the experiments with a weight of 0.025 g per sheet. Each LDPE sheet was cut into equal pieces with the same surface area (2.5 ×2.5 cm2) and washed with 75% ethanol.	ThermoFisher Scientific Co.	Yes	No	Termite gut	Animal associated		No		
Fusarium solani	169388	PBAT	Santos-Beneit, F., Chen, L. M., Bordel, S., Frutos de la Flor, R., García-Depraect, O., Lebrero, R., Rodriguez-Vega, S., Muñoz, R., Börner, R. A., & Börner, T. (2023). Screening enzymes that can depolymerize commercial biodegradable polymers: Heterologous expression of Fusarium solani cutinase in Escherichia coli. Microorganisms, 11(2), 328.	Cutinase			No			2023.0	HPLC;LC-HRMS	The plastic materials, which were initially in a pellet form, were grinded in a commercial blender (Cecotec Titanium 2000 pro, Valencia, Spain) equipped with titanium blades. Repeated crushing (~3 min on, ~5 min off) using dry ice as a cooling strategy was employed to avoid melting and recrystallization, as reported elsewhere [6]. Finally, the polymer powders were sieved using an electromagnetic sieve (CISA RP-20, Barcelona, Spain) with stainless-steel sieves of 100, 250, 500 and 1000 μm and then dried at room temperature. The different powder fractions were stored in closed packaging under dark and dry conditions at room temperature until usage. Prior to the experiments the resins and powders were washed once with 0.1% Sodium Dodecyl Sulfate (SDS) so- lution, three times with Milli-Q water, once with 70% ethanol and then 100% ethanol. The resins and powders were subsequently dried in a SpeedVac concentrator (Savant, Barnstable, MA, USA) until complete dryness.	Bio-Fed	Yes	No				Yes		
Fusarium solani	169388	PBS	Santos-Beneit, F., Chen, L. M., Bordel, S., Frutos de la Flor, R., García-Depraect, O., Lebrero, R., Rodriguez-Vega, S., Muñoz, R., Börner, R. A., & Börner, T. (2023). Screening enzymes that can depolymerize commercial biodegradable polymers: Heterologous expression of Fusarium solani cutinase in Escherichia coli. Microorganisms, 11(2), 328.	Cutinase			No			2023.0	HPLC;LC-HRMS	The plastic materials, which were initially in a pellet form, were grinded in a commercial blender (Cecotec Titanium 2000 pro, Valencia, Spain) equipped with titanium blades. Repeated crushing (~3 min on, ~5 min off) using dry ice as a cooling strategy was employed to avoid melting and recrystallization, as reported elsewhere [6]. Finally, the polymer powders were sieved using an electromagnetic sieve (CISA RP-20, Barcelona, Spain) with stainless-steel sieves of 100, 250, 500 and 1000 μm and then dried at room temperature. The different powder fractions were stored in closed packaging under dark and dry conditions at room temperature until usage. Prior to the experiments the resins and powders were washed once with 0.1% Sodium Dodecyl Sulfate (SDS) so- lution, three times with Milli-Q water, once with 70% ethanol and then 100% ethanol. The resins and powders were subsequently dried in a SpeedVac concentrator (Savant, Barnstable, MA, USA) until complete dryness.	PTT MCC Biochem	Yes	No				Yes		
Fusarium solani	169388	PCL	Santos-Beneit, F., Chen, L. M., Bordel, S., Frutos de la Flor, R., García-Depraect, O., Lebrero, R., Rodriguez-Vega, S., Muñoz, R., Börner, R. A., & Börner, T. (2023). Screening enzymes that can depolymerize commercial biodegradable polymers: Heterologous expression of Fusarium solani cutinase in Escherichia coli. Microorganisms, 11(2), 328.	Cutinase			No			2023.0	HPLC;LC-HRMS	The plastic materials, which were initially in a pellet form, were grinded in a commercial blender (Cecotec Titanium 2000 pro, Valencia, Spain) equipped with titanium blades. Repeated crushing (~3 min on, ~5 min off) using dry ice as a cooling strategy was employed to avoid melting and recrystallization, as reported elsewhere [6]. Finally, the polymer powders were sieved using an electromagnetic sieve (CISA RP-20, Barcelona, Spain) with stainless-steel sieves of 100, 250, 500 and 1000 μm and then dried at room temperature. The different powder fractions were stored in closed packaging under dark and dry conditions at room temperature until usage. Prior to the experiments the resins and powders were washed once with 0.1% Sodium Dodecyl Sulfate (SDS) so- lution, three times with Milli-Q water, once with 70% ethanol and then 100% ethanol. The resins and powders were subsequently dried in a SpeedVac concentrator (Savant, Barnstable, MA, USA) until complete dryness.	Sigma-Aldrich	Yes	No				Yes		
Alcanivorax borkumensis	59754	PBAT	Santos-Beneit, F., Chen, L. M., Bordel, S., Frutos de la Flor, R., García-Depraect, O., Lebrero, R., Rodriguez-Vega, S., Muñoz, R., Börner, R. A., & Börner, T. (2023). Screening enzymes that can depolymerize commercial biodegradable polymers: Heterologous expression of Fusarium solani cutinase in Escherichia coli. Microorganisms, 11(2), 328.	Esterase			No			2023.0	HPLC;LC-HRMS	The plastic materials, which were initially in a pellet form, were grinded in a commercial blender (Cecotec Titanium 2000 pro, Valencia, Spain) equipped with titanium blades. Repeated crushing (~3 min on, ~5 min off) using dry ice as a cooling strategy was employed to avoid melting and recrystallization, as reported elsewhere [6]. Finally, the polymer powders were sieved using an electromagnetic sieve (CISA RP-20, Barcelona, Spain) with stainless-steel sieves of 100, 250, 500 and 1000 μm and then dried at room temperature. The different powder fractions were stored in closed packaging under dark and dry conditions at room temperature until usage. Prior to the experiments the resins and powders were washed once with 0.1% Sodium Dodecyl Sulfate (SDS) so- lution, three times with Milli-Q water, once with 70% ethanol and then 100% ethanol. The resins and powders were subsequently dried in a SpeedVac concentrator (Savant, Barnstable, MA, USA) until complete dryness.	Bio-Fed	Yes	No				Yes		
Pseudomonas pseudoalcaligenes	301	PBAT	Santos-Beneit, F., Chen, L. M., Bordel, S., Frutos de la Flor, R., García-Depraect, O., Lebrero, R., Rodriguez-Vega, S., Muñoz, R., Börner, R. A., & Börner, T. (2023). Screening enzymes that can depolymerize commercial biodegradable polymers: Heterologous expression of Fusarium solani cutinase in Escherichia coli. Microorganisms, 11(2), 328.	Arylesyrtase			No			2023.0	HPLC;LC-HRMS	The plastic materials, which were initially in a pellet form, were grinded in a commercial blender (Cecotec Titanium 2000 pro, Valencia, Spain) equipped with titanium blades. Repeated crushing (~3 min on, ~5 min off) using dry ice as a cooling strategy was employed to avoid melting and recrystallization, as reported elsewhere [6]. Finally, the polymer powders were sieved using an electromagnetic sieve (CISA RP-20, Barcelona, Spain) with stainless-steel sieves of 100, 250, 500 and 1000 μm and then dried at room temperature. The different powder fractions were stored in closed packaging under dark and dry conditions at room temperature until usage. Prior to the experiments the resins and powders were washed once with 0.1% Sodium Dodecyl Sulfate (SDS) so- lution, three times with Milli-Q water, once with 70% ethanol and then 100% ethanol. The resins and powders were subsequently dried in a SpeedVac concentrator (Savant, Barnstable, MA, USA) until complete dryness.	Bio-Fed	Yes	No				Yes		
Psychrobacter cryohalolentis	330922	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Litter	Arctic shore	Norway	No		
Pseudomonas lini	163011	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Litter	Arctic shore	Norway	No		
Kribbella albertanoniae	1266829	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Litter	Arctic shore	Norway	No		
Collimonas arenae	279058	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Switzerland	No		
Collimonas pratensis	279113	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Switzerland	No		
Streptomyces hypolithicus	479410	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Greenland	No		
Rhodococcus sovatensis	1805840	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Switzerland	No		
Amycolatopsis sp.	37632	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Switzerland	No		
Thelebolus globosus	319062	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Litter	Arctic shore	Norway	No		
Samsoniella hepiali	797268	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Litter	Arctic shore	Norway	No		
Linnemannia gamsii	64522	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Switzerland	No		
Penicillium stoloniferum	1343417	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Switzerland	No		
Pseudogymnoascus pannorum	79858	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Switzerland	No		
Lachnellula sp.	2040839	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Switzerland	No		
Pseudogymnoascus verrucosus	342668	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Switzerland	No		
Pseudogymnoascus verrucosus	342668	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Greenland	No		
Pseudogymnoascus pannorum	79858	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Greenland	No		
Pseudogymnoascus pannorum	79858	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Switzerland	No		
Verticillium leptobactrum	93594	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Clear zone	Impranil	CSC Jäklechemie GmbH & Co. KG.	No	No	Soil	Soil	Switzerland	No		
Pseudogymnoascus pannorum	79858	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	ecovio	Petroplast Vinora AG	No	No	Soil	Soil	Switzerland	No		
Lachnellula sp.	2040839	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	ecovio	Petroplast Vinora AG	No	No	Soil	Soil	Switzerland	No		
Lachnellula sp.	2040839	PLA	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	ecovio	Petroplast Vinora AG	No	No	Soil	Soil	Switzerland	No		
Pseudogymnoascus verrucosus	342668	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	ecovio, with 4-MLU assay peroformed on a polymeric matrix of pure PBAT	Petroplast Vinora AG (ecovio)	No	No	Soil	Soil	Switzerland	No		
Pseudogymnoascus verrucosus	342668	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	ecovio, with 4-MLU assay peroformed on a polymeric matrix of pure PBAT	Petroplast Vinora AG (ecovio)	No	No	Soil	Soil	Greenland	No		
Pseudogymnoascus pannorum	79858	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	ecovio	Petroplast Vinora AG	No	No	Soil	Soil	Greenland	No		
Pseudogymnoascus verrucosus	342668	PLA	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	ecovio	Petroplast Vinora AG	No	No	Soil	Soil	Greenland	No		
Neodevriesia sp.	2011839	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	ecovio, with 4-MLU assay peroformed on a polymeric matrix of pure PBAT	Petroplast Vinora AG	No	No	Litter	Arctic shore	Norway	No		
Lachnellula sp.	2040839	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	BI-OPL, with 4-MLU assay perfomred on a polymeric matrix of pure PBAT	Oerlemans Plastics BV (BI-OPL)	No	No	Soil	Soil	Switzerland	No		
Lachnellula sp.	2040839	PLA	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	BI-OPL	Oerlemans Plastics BV	No	No	Soil	Soil	Switzerland	No		
Neodevriesia sp.	2011839	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	BI-OPL	Oerlemans Plastics BV	No	No	Litter	Arctic shore	Norway	No		
Neodevriesia sp.	2011839	PLA	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	BI-OPL	Oerlemans Plastics BV	No	No	Litter	Arctic shore	Norway	No		
Amycolatopsis sp.	37632	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR;4-MUL florescent assay	BI-OPL, with 4-MLU assay perfomred on a polymeric matrix of pure PBAT	Oerlemans Plastics BV	No	No	Soil	Soil	Switzerland	No		
Amycolatopsis sp.	37632	PLA	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR;4-MUL florescent assay	BI-OPL, with 4-MLU assay perfomred on a polymeric matrix of pure PBAT	Oerlemans Plastics BV (BI-OPL)	No	No	Soil	Soil	Switzerland	No		
Thelebolus globosus	319062	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	Weight loss;NMR	BI-OPL	Oerlemans Plastics BV (BI-OPL)	No	No	Litter	Arctic shore	Norway	No		
Streptomyces avidinii	1895	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	4-MUL florescent assay	Polymeric matrix of pure PBAT		No	No	Soil	Soil	Greenland	No		
Streptomyces avidinii	1895	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	4-MUL florescent assay	Polymeric matrix of pure PBAT		No	No	Soil	Soil	Greenland	No		
Verticillium leptobactrum	93594	PBAT	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	4-MUL florescent assay	Polymeric matrix of pure PBAT		No	No	Soil	Soil	Switzerland	No		
Penicillium stoloniferum	1343417	PU	Rüthi, J., Cerri, M., Brunner, I., Stierli, B., Sander, M., & Frey, B. (2023). Discovery of plastic-degrading microbial strains isolated from the alpine and Arctic terrestrial plastisphere. Frontiers in Microbiology, 14, 1178474.				No			2023.0	4-MUL florescent assay	Polymeric matrix of pure PBAT		No	No	Soil	Soil	Switzerland	No		
Halomonas maura	117606	LDPE	Bitalac, J. M. S., Lantican, N. B., Gomez, N. C. F., & Onda, D. F. L. (2023). Attachment of potential cultivable primo-colonizing bacteria and its implications on the fate of low-density polyethylene (LDPE) plastics in the marine environment. Journal of Hazardous Materials, 451, 131124.				No			2023.0	CLSM;SEM;FTIR	LDPE powder was made from LDPE plastic bags purchased from a local supermarket, which were cut into 1.5 cm × 1.5 cm squares, disinfected by soaking in 70% ethanol for 30 min, and air dried in a sterile laminar airflow chamber. To increase the available surface area for attachment and growth of bacterial cells, the LDPE squares were afterwards soaked in liquid nitrogen to increase polymer fragility and shredded into fine powder using an electric stainless-steel grinder (Yisino, Philippines). To make the particle sizes uniform, the ground LDPE particles were sieved through a 250 μm metal mesh, and the sieved powder was stored in a sterile lidded container until further use. These were all conducted under a sterile laminar airflow chamber to maintain an aseptic environment.	New Hi-Zex Plastic Manufacturing	No	No	Sediment		Philippines	No		
Halomonas denitrificans	370769	LDPE	Bitalac, J. M. S., Lantican, N. B., Gomez, N. C. F., & Onda, D. F. L. (2023). Attachment of potential cultivable primo-colonizing bacteria and its implications on the fate of low-density polyethylene (LDPE) plastics in the marine environment. Journal of Hazardous Materials, 451, 131124.				No			2023.0	CLSM;SEM;FTIR	LDPE powder was made from LDPE plastic bags purchased from a local supermarket, which were cut into 1.5 cm × 1.5 cm squares, disinfected by soaking in 70% ethanol for 30 min, and air dried in a sterile laminar airflow chamber. To increase the available surface area for attachment and growth of bacterial cells, the LDPE squares were afterwards soaked in liquid nitrogen to increase polymer fragility and shredded into fine powder using an electric stainless-steel grinder (Yisino, Philippines). To make the particle sizes uniform, the ground LDPE particles were sieved through a 250 μm metal mesh, and the sieved powder was stored in a sterile lidded container until further use. These were all conducted under a sterile laminar airflow chamber to maintain an aseptic environment.	New Hi-Zex Plastic Manufacturing	No	No	Sediment		Philippines	No		
Halomonas pacifica	77098	LDPE	Bitalac, J. M. S., Lantican, N. B., Gomez, N. C. F., & Onda, D. F. L. (2023). Attachment of potential cultivable primo-colonizing bacteria and its implications on the fate of low-density polyethylene (LDPE) plastics in the marine environment. Journal of Hazardous Materials, 451, 131124.				No			2023.0	CLSM;SEM;FTIR	LDPE powder was made from LDPE plastic bags purchased from a local supermarket, which were cut into 1.5 cm × 1.5 cm squares, disinfected by soaking in 70% ethanol for 30 min, and air dried in a sterile laminar airflow chamber. To increase the available surface area for attachment and growth of bacterial cells, the LDPE squares were afterwards soaked in liquid nitrogen to increase polymer fragility and shredded into fine powder using an electric stainless-steel grinder (Yisino, Philippines). To make the particle sizes uniform, the ground LDPE particles were sieved through a 250 μm metal mesh, and the sieved powder was stored in a sterile lidded container until further use. These were all conducted under a sterile laminar airflow chamber to maintain an aseptic environment.	New Hi-Zex Plastic Manufacturing	No	No	Sediment		Philippines	No		
Bacillus megaterium	1404	LDPE	Bitalac, J. M. S., Lantican, N. B., Gomez, N. C. F., & Onda, D. F. L. (2023). Attachment of potential cultivable primo-colonizing bacteria and its implications on the fate of low-density polyethylene (LDPE) plastics in the marine environment. Journal of Hazardous Materials, 451, 131124.				No			2023.0	CLSM;SEM;FTIR	LDPE powder was made from LDPE plastic bags purchased from a local supermarket, which were cut into 1.5 cm × 1.5 cm squares, disinfected by soaking in 70% ethanol for 30 min, and air dried in a sterile laminar airflow chamber. To increase the available surface area for attachment and growth of bacterial cells, the LDPE squares were afterwards soaked in liquid nitrogen to increase polymer fragility and shredded into fine powder using an electric stainless-steel grinder (Yisino, Philippines). To make the particle sizes uniform, the ground LDPE particles were sieved through a 250 μm metal mesh, and the sieved powder was stored in a sterile lidded container until further use. These were all conducted under a sterile laminar airflow chamber to maintain an aseptic environment.	New Hi-Zex Plastic Manufacturing	No	No	Sediment		Philippines	No		
Alteromonas oceani	2071609	LDPE	Bitalac, J. M. S., Lantican, N. B., Gomez, N. C. F., & Onda, D. F. L. (2023). Attachment of potential cultivable primo-colonizing bacteria and its implications on the fate of low-density polyethylene (LDPE) plastics in the marine environment. Journal of Hazardous Materials, 451, 131124.				No			2023.0	CLSM;SEM;FTIR	LDPE powder was made from LDPE plastic bags purchased from a local supermarket, which were cut into 1.5 cm × 1.5 cm squares, disinfected by soaking in 70% ethanol for 30 min, and air dried in a sterile laminar airflow chamber. To increase the available surface area for attachment and growth of bacterial cells, the LDPE squares were afterwards soaked in liquid nitrogen to increase polymer fragility and shredded into fine powder using an electric stainless-steel grinder (Yisino, Philippines). To make the particle sizes uniform, the ground LDPE particles were sieved through a 250 μm metal mesh, and the sieved powder was stored in a sterile lidded container until further use. These were all conducted under a sterile laminar airflow chamber to maintain an aseptic environment.	New Hi-Zex Plastic Manufacturing	No	No	Sediment		Philippines	No		
Photobacterium ganghwense	320778	LDPE	Bitalac, J. M. S., Lantican, N. B., Gomez, N. C. F., & Onda, D. F. L. (2023). Attachment of potential cultivable primo-colonizing bacteria and its implications on the fate of low-density polyethylene (LDPE) plastics in the marine environment. Journal of Hazardous Materials, 451, 131124.				No			2023.0	CLSM;SEM;FTIR	LDPE powder was made from LDPE plastic bags purchased from a local supermarket, which were cut into 1.5 cm × 1.5 cm squares, disinfected by soaking in 70% ethanol for 30 min, and air dried in a sterile laminar airflow chamber. To increase the available surface area for attachment and growth of bacterial cells, the LDPE squares were afterwards soaked in liquid nitrogen to increase polymer fragility and shredded into fine powder using an electric stainless-steel grinder (Yisino, Philippines). To make the particle sizes uniform, the ground LDPE particles were sieved through a 250 μm metal mesh, and the sieved powder was stored in a sterile lidded container until further use. These were all conducted under a sterile laminar airflow chamber to maintain an aseptic environment.	New Hi-Zex Plastic Manufacturing	No	No	Sediment		Philippines	No		
Aliishimia ponticola	2499833	LDPE	Bitalac, J. M. S., Lantican, N. B., Gomez, N. C. F., & Onda, D. F. L. (2023). Attachment of potential cultivable primo-colonizing bacteria and its implications on the fate of low-density polyethylene (LDPE) plastics in the marine environment. Journal of Hazardous Materials, 451, 131124.				No			2023.0	CLSM;SEM;FTIR	LDPE powder was made from LDPE plastic bags purchased from a local supermarket, which were cut into 1.5 cm × 1.5 cm squares, disinfected by soaking in 70% ethanol for 30 min, and air dried in a sterile laminar airflow chamber. To increase the available surface area for attachment and growth of bacterial cells, the LDPE squares were afterwards soaked in liquid nitrogen to increase polymer fragility and shredded into fine powder using an electric stainless-steel grinder (Yisino, Philippines). To make the particle sizes uniform, the ground LDPE particles were sieved through a 250 μm metal mesh, and the sieved powder was stored in a sterile lidded container until further use. These were all conducted under a sterile laminar airflow chamber to maintain an aseptic environment.	New Hi-Zex Plastic Manufacturing	No	No	Sediment		Philippines	No		
Halomonas cerina	447424	LDPE	Bitalac, J. M. S., Lantican, N. B., Gomez, N. C. F., & Onda, D. F. L. (2023). Attachment of potential cultivable primo-colonizing bacteria and its implications on the fate of low-density polyethylene (LDPE) plastics in the marine environment. Journal of Hazardous Materials, 451, 131124.				No			2023.0	CLSM;SEM;FTIR	LDPE powder was made from LDPE plastic bags purchased from a local supermarket, which were cut into 1.5 cm × 1.5 cm squares, disinfected by soaking in 70% ethanol for 30 min, and air dried in a sterile laminar airflow chamber. To increase the available surface area for attachment and growth of bacterial cells, the LDPE squares were afterwards soaked in liquid nitrogen to increase polymer fragility and shredded into fine powder using an electric stainless-steel grinder (Yisino, Philippines). To make the particle sizes uniform, the ground LDPE particles were sieved through a 250 μm metal mesh, and the sieved powder was stored in a sterile lidded container until further use. These were all conducted under a sterile laminar airflow chamber to maintain an aseptic environment.	New Hi-Zex Plastic Manufacturing	No	No	Sediment		Philippines	No		
Bacillus vietnamensis	218284	LDPE	Bitalac, J. M. S., Lantican, N. B., Gomez, N. C. F., & Onda, D. F. L. (2023). Attachment of potential cultivable primo-colonizing bacteria and its implications on the fate of low-density polyethylene (LDPE) plastics in the marine environment. Journal of Hazardous Materials, 451, 131124.				No			2023.0	CLSM;SEM;FTIR	LDPE powder was made from LDPE plastic bags purchased from a local supermarket, which were cut into 1.5 cm × 1.5 cm squares, disinfected by soaking in 70% ethanol for 30 min, and air dried in a sterile laminar airflow chamber. To increase the available surface area for attachment and growth of bacterial cells, the LDPE squares were afterwards soaked in liquid nitrogen to increase polymer fragility and shredded into fine powder using an electric stainless-steel grinder (Yisino, Philippines). To make the particle sizes uniform, the ground LDPE particles were sieved through a 250 μm metal mesh, and the sieved powder was stored in a sterile lidded container until further use. These were all conducted under a sterile laminar airflow chamber to maintain an aseptic environment.	New Hi-Zex Plastic Manufacturing	No	No	Sediment		Philippines	No		
Halomonas gudaonensis	376427	LDPE	Bitalac, J. M. S., Lantican, N. B., Gomez, N. C. F., & Onda, D. F. L. (2023). Attachment of potential cultivable primo-colonizing bacteria and its implications on the fate of low-density polyethylene (LDPE) plastics in the marine environment. Journal of Hazardous Materials, 451, 131124.				No			2023.0	CLSM;SEM;FTIR	LDPE powder was made from LDPE plastic bags purchased from a local supermarket, which were cut into 1.5 cm × 1.5 cm squares, disinfected by soaking in 70% ethanol for 30 min, and air dried in a sterile laminar airflow chamber. To increase the available surface area for attachment and growth of bacterial cells, the LDPE squares were afterwards soaked in liquid nitrogen to increase polymer fragility and shredded into fine powder using an electric stainless-steel grinder (Yisino, Philippines). To make the particle sizes uniform, the ground LDPE particles were sieved through a 250 μm metal mesh, and the sieved powder was stored in a sterile lidded container until further use. These were all conducted under a sterile laminar airflow chamber to maintain an aseptic environment.	New Hi-Zex Plastic Manufacturing	No	No	Sediment		Philippines	No		
Citrobacter freundii	546	LDPE	Ali, S. S., Elsamahy, T., Zhu, D., & Sun, J. (2023). Biodegradability of polyethylene by efficient bacteria from the guts of plastic-eating waxworms and investigation of its degradation mechanism. Journal of Hazardous Materials, 443, 130287.				No			2023.0	XRD;SEM;FTIR;Tenslie strength	LDPE plastic film with a thickness of 15 m (Shandong Kangye Plastic Products Co., Ltd, China) was cut into square sheets measuring 50 mm × 50 mm in order to be incubated on an agar medium plate. Additionally, the film was cut into small pieces measuring 3 mm × 3 mm in order to be incubated in a liquid medium. Before being used, the PE components were first measured and weighted, then disinfected with 70% ethanol, and finally air-dried on a clean bench equipped with laminar flow for 15 min.	Shangdong Kangye Plastic Products Co., Ltd, China	No	No	Waxworm gut	Animal associated		No		
Bacillus sp.	1409	LDPE	Ali, S. S., Elsamahy, T., Zhu, D., & Sun, J. (2023). Biodegradability of polyethylene by efficient bacteria from the guts of plastic-eating waxworms and investigation of its degradation mechanism. Journal of Hazardous Materials, 443, 130287.				No			2023.0	XRD;SEM;FTIR;Tenslie strength	LDPE plastic film with a thickness of 15 m (Shandong Kangye Plastic Products Co., Ltd, China) was cut into square sheets measuring 50 mm × 50 mm in order to be incubated on an agar medium plate. Additionally, the film was cut into small pieces measuring 3 mm × 3 mm in order to be incubated in a liquid medium. Before being used, the PE components were first measured and weighted, then disinfected with 70% ethanol, and finally air-dried on a clean bench equipped with laminar flow for 15 min.	Shangdong Kangye Plastic Products Co., Ltd, China	No	No	Waxworm gut	Animal associated		No		
Bacillus sp.	1409	HDPE	Wu, H., Liu, Q., Sun, W., Lu, Y., Qi, Y., & Zhang, H. (2023). Biodegradability of polyethylene mulch film by Bacillus paramycoides. Chemosphere, 311, 136978.				No			2023.0	Weight loss;FTIR;XRD;XPS;GPC	The high-density polyethylene (HDPE, DFDA-7042) film was provided by Jindi Plastic Products Co., Ltd., Gansu, China, with a density of 0.91–0.92 g/cm3, an average molecular weight of 140,000, and a thickness of approximately 2 mm. The cutting experiment required a 4 × 4 cm rectangular diaphragm, ultrasonicated in 75% ethanol for 20 min, and then transferred to sterile water for 2 h. The sterile filter paper absorbs the surface moisture, the ultraclean typhoon is air-dried, and the UV lamp is irradiated for 0.5 h.	Jindi Plastci Products Co., Ltd., Gansu, China	No	No	Recyling plant	Soil	China	No		
Clostridium sp.	1506	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;Weight loss;SEM;GPC;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 2 g of PBA-PU was dissolved in 20 mL of dichloromethane and then poured into Petri dishes and kept for 12 h to form solid PBA-PU films. The films were then cut into pieces of 2 × 4 cm2. 		No	No	Soil	Soil		No		
Bacillus sp.	1409	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Burkholderia sp.	36773	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Brevibacillus sp.	1882945	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Arthrinium sp.	1756131	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Thelypteris sp.	29617	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Cladosporium sp.	1707700	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Burkholderia sp.	36773	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Lysinibacillus sp.	1869345	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Brevibacillus sp.	1882945	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Streptomyces sp.	1931	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Bacillus sp.	1409	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Aspergillus sp.	5065	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Pseudomonas sp.	306	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Burkholderia sp.	36773	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Burkholderia sp.	36773	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Cladosporium sp.	1707700	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Cladosporium sp.	1707700	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Verticillium sp.	2047679	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Verticillium sp.	2047679	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Clear zone;NMR;FTIR	The synthesis of PBA-PU was performed in a jacketed reactor, heated at 80 ◦C, and equipped with a mechanic stirrer under a nitrogen gas flow. Stoi- chiometric conditions were also used with a NCO/OH ratio of 1. PBA (Mw=2000) was dissolved in dimethyl sulfoxide (DMSO) in the reactor followed by adding MDI dissolved in DMSO. Subsequently, the reaction solution was stirred and slowly heated to 80 ◦ C, kept for 12 h, and finally freeze-dried. 		No	No	Soil	Soil		No		
Clostridium sp.	1506	PU	Liu, J., Zeng, Q., Lei, H., Xin, K., Xu, A., Wei, R., Li, D., Zhou, J., Dong, W., & Jiang, M. (2023). Biodegradation of polyester polyurethane by Cladosporium sp. P7: Evaluating its degradation capacity and metabolic pathways. Journal of Hazardous Materials, 448, 130776.				No			2023.0	Weight loss;SEM;XPS;TGA;FTIR;Spectrophotometry	Impranil, TDI-based PU foam, PU monomers (1000 mg/L BDO, 1000 mg/L AA and 100 mg/L MDA)	Covestro AG (Impranil);Dagong foam Co., Ltd (PU foam);Sigma Aldrich (PU monomers)	No	No	Soil	Soil		No		
Bacillus safensis	561879	PLA	Wang, Y., Hu, T., Zhang, W., Lin, J., Wang, Z., Lyu, S., & Tong, H. (2023). Biodegradation of polylactic acid by a mesophilic bacteria Bacillus safensis. Chemosphere, 318, 137991.				No			2023.0	Clear zone;Weight loss;SEM;FTIR;WCA;MS	Polyester films with a thickness of 0.3 mm were prepared using the hot-press method. In brief, polyester particles were pressed for 2 min to release any exhaust gasses and then hotpressed for 5 min at 180 ◦C on a plate vulcanizer. The films were subsequently cold-pressed for 5 min at room temperature	NatureWorks	No	No	Soil	Soil	China	No		
Aspergillus terreus	33178	PP	Samat, A. F., Carter, D., & Abbas, A. (2023). Biodeterioration of pre-treated polypropylene by Aspergillus terreus and Engyodontium album. npj Materials Degradation, 7(1), 28.				No			2023.0	Weight loss;FTIR;SEM	Three types of PP samples used in this research were PP granule (GPP), PP film (FPP) and PP metallised film (MFPP). PP granule is an isotactic PP (white, pelleted) with an average molecular weight of ~250,000Da, average Mn of ~67,000, density of 0.9 g/ml at 25 °C, and CAS number 9003-07-0 was purchased from Sigma-Aldrich®. PP film is in biaxially oriented condition (transparent), with a thickness of 0.05 mm, 600 × 600 mm in size and product number GF00254944 was manufactured by Goodfellow Corp., USA, purchased through Sigma-Aldrich®. PP metallised film has an aluminium-coated surface on one side (metallic), a thickness of 0.008mm, 0.5 m × 75 mm in size and product number GF80085922 was manufactured by Goodfellow Corp., USA, purchased through Sigma-Aldrich®.	Sigma-Aldrich (GPP);Goodfellow Corp. (FPP & MFPP	Yes	No	Culture collection	Culture collection		No		
Engyodontium album	37998	PP	Samat, A. F., Carter, D., & Abbas, A. (2023). Biodeterioration of pre-treated polypropylene by Aspergillus terreus and Engyodontium album. npj Materials Degradation, 7(1), 28.				No			2023.0	Weight loss;FTIR;SEM	Three types of PP samples used in this research were PP granule (GPP), PP film (FPP) and PP metallised film (MFPP). PP granule is an isotactic PP (white, pelleted) with an average molecular weight of ~250,000Da, average Mn of ~67,000, density of 0.9 g/ml at 25 °C, and CAS number 9003-07-0 was purchased from Sigma-Aldrich®. PP film is in biaxially oriented condition (transparent), with a thickness of 0.05 mm, 600 × 600 mm in size and product number GF00254944 was manufactured by Goodfellow Corp., USA, purchased through Sigma-Aldrich®. PP metallised film has an aluminium-coated surface on one side (metallic), a thickness of 0.008mm, 0.5 m × 75 mm in size and product number GF80085922 was manufactured by Goodfellow Corp., USA, purchased through Sigma-Aldrich®.	Sigma-Aldrich (GPP);Goodfellow Corp. (FPP & MFPP	Yes	No	Culture collection	Culture collection		No		
Bacillus subtilis	1423	LDPE	Pathak, V. M. (2023). Exploitation of bacterial strains for microplastics (LDPE) biodegradation. Chemosphere, 316, 137845.				No			2023.0	Weight loss;FTIR;SEM;Electrical properties	LDPE (low-density polyethylene) pellets were procured from Sigma- Aldrich Chemical Corporation, USA having a density 0.925 g/ml at temperature of 25 ◦C and melting index of 25 g/10 min at 190 ◦C/2.16 kg. LDPE was used in the form of strips and powder with a particle size of 110 μm as microplastic for the isolation of microorganisms. These polymer films (strips) were prepared from LDPE pellets, boiled in xylene and washed with 70% ethanol at room temperature. 	Sigma-Aldrich	Yes	No	Soil	Soil	India	No		
Paracoccus aminophilus	34003	LDPE	Pathak, V. M. (2023). Exploitation of bacterial strains for microplastics (LDPE) biodegradation. Chemosphere, 316, 137845.				No			2023.0	Weight loss;FTIR;SEM;Electrical properties	LDPE (low-density polyethylene) pellets were procured from Sigma- Aldrich Chemical Corporation, USA having a density 0.925 g/ml at temperature of 25 ◦C and melting index of 25 g/10 min at 190 ◦C/2.16 kg. LDPE was used in the form of strips and powder with a particle size of 110 μm as microplastic for the isolation of microorganisms. These polymer films (strips) were prepared from LDPE pellets, boiled in xylene and washed with 70% ethanol at room temperature. 	Sigma-Aldrich	Yes	No	Soil	Soil	India	No		
Pseudomonas putida	303	LDPE	Pathak, V. M. (2023). Exploitation of bacterial strains for microplastics (LDPE) biodegradation. Chemosphere, 316, 137845.				No			2023.0	Weight loss;FTIR;SEM;Electrical properties	LDPE (low-density polyethylene) pellets were procured from Sigma- Aldrich Chemical Corporation, USA having a density 0.925 g/ml at temperature of 25 ◦C and melting index of 25 g/10 min at 190 ◦C/2.16 kg. LDPE was used in the form of strips and powder with a particle size of 110 μm as microplastic for the isolation of microorganisms. These polymer films (strips) were prepared from LDPE pellets, boiled in xylene and washed with 70% ethanol at room temperature. 	Sigma-Aldrich	Yes	No	Soil	Soil	India	No		
Pseudomonas aeruginosa	287	LDPE	Pathak, V. M. (2023). Exploitation of bacterial strains for microplastics (LDPE) biodegradation. Chemosphere, 316, 137845.				No			2023.0	Weight loss;FTIR;SEM;Electrical properties	LDPE (low-density polyethylene) pellets were procured from Sigma- Aldrich Chemical Corporation, USA having a density 0.925 g/ml at temperature of 25 ◦C and melting index of 25 g/10 min at 190 ◦C/2.16 kg. LDPE was used in the form of strips and powder with a particle size of 110 μm as microplastic for the isolation of microorganisms. These polymer films (strips) were prepared from LDPE pellets, boiled in xylene and washed with 70% ethanol at room temperature. 	Sigma-Aldrich	Yes	No	Soil	Soil	India	No		
Acinetobacter calcoaceticus	471	LDPE	Pathak, V. M. (2023). Exploitation of bacterial strains for microplastics (LDPE) biodegradation. Chemosphere, 316, 137845.				No			2023.0	Weight loss;FTIR;SEM;Electrical properties	LDPE (low-density polyethylene) pellets were procured from Sigma- Aldrich Chemical Corporation, USA having a density 0.925 g/ml at temperature of 25 ◦C and melting index of 25 g/10 min at 190 ◦C/2.16 kg. LDPE was used in the form of strips and powder with a particle size of 110 μm as microplastic for the isolation of microorganisms. These polymer films (strips) were prepared from LDPE pellets, boiled in xylene and washed with 70% ethanol at room temperature. 	Sigma-Aldrich	Yes	No	Soil	Soil	India	No		
Achromobacter denitrificans	32002	PP	Shirazi, S., Mafigholami, R., Moghimi, H., & Borghei, S. M. (2023). Feasibility study of microplastic biodegradation in effluents from South Tehran WWTP after quantitative and qualitative measurement of the particles. Applied Water Science, 13(3), 80.				No			2023.0	Weight loss;FTIR;SEM;TGA	In order to prepare microplastics, pellet-type plastics with a diameter of 3–4 mm were prepared. Then, in order to crush them, first using nitrogen, their temperature reached 196 degrees Celsius, and then it was ground using a centrifugal grinder. Before photographing with SEM, a layer of gold was sputtered on the samples to establish the conductivity of the samples.		No	No	Water treatment effluent	Water	Iran	No		
Pseudomonas aestusnigri	857252	PP	Shirazi, S., Mafigholami, R., Moghimi, H., & Borghei, S. M. (2023). Feasibility study of microplastic biodegradation in effluents from South Tehran WWTP after quantitative and qualitative measurement of the particles. Applied Water Science, 13(3), 80.				No			2023.0	Weight loss;FTIR;SEM;TGA	In order to prepare microplastics, pellet-type plastics with a diameter of 3–4 mm were prepared. Then, in order to crush them, first using nitrogen, their temperature reached 196 degrees Celsius, and then it was ground using a centrifugal grinder. Before photographing with SEM, a layer of gold was sputtered on the samples to establish the conductivity of the samples.		No	No	Water treatment effluent	Water	Iran	No		
Bacillus amyloliquefaciens	1390	PE	Shirazi, S., Mafigholami, R., Moghimi, H., & Borghei, S. M. (2023). Feasibility study of microplastic biodegradation in effluents from South Tehran WWTP after quantitative and qualitative measurement of the particles. Applied Water Science, 13(3), 80.				No			2023.0	Weight loss;FTIR;SEM;TGA	In order to prepare microplastics, pellet-type plastics with a diameter of 3–4 mm were prepared. Then, in order to crush them, first using nitrogen, their temperature reached 196 degrees Celsius, and then it was ground using a centrifugal grinder. Before photographing with SEM, a layer of gold was sputtered on the samples to establish the conductivity of the samples.		No	No	Water treatment effluent	Water	Iran	No		
Cladosporium halotolerans	1052096	HDPE	Di Napoli, M., Silvestri, B., Castagliuolo, G., Carpentieri, A., Luciani, G., Di Maro, A., Sorbo, S., Pezzella, R., & Varcamonti, M. (2023). High density polyethylene (HDPE) biodegradation by the fungus Cladosporium halotolerans. FEMS Microbiology Ecology, 99(2), fiac148.	Oxidoreductase			No			2023.0	Weight loss;FTIR;SEM;LCMS	HDPE powder		No	No	Larve gut	Animal associated		No		
Phanerochaete chrysosporium	2822231	PLA	Wu, F., Guo, Z., Cui, K., Dong, D., Yang, X., Li, J., ... & Pan, T. (2023). Insights into characteristics of white rot fungus during environmental plastics adhesion and degradation mechanism of plastics. Journal of Hazardous Materials, 448, 130878.				No			2023.0	FTIR;GPC;WCA;GCMS	PS membranes prepared in the lab. Micrometer caliper was used to select PS films with thickness range of 0.019–0.025 cm.		No	No	Culture collection	Culture collection		No		
Phanerochaete chrysosporium	2822231	PS	Wu, F., Guo, Z., Cui, K., Dong, D., Yang, X., Li, J., ... & Pan, T. (2023). Insights into characteristics of white rot fungus during environmental plastics adhesion and degradation mechanism of plastics. Journal of Hazardous Materials, 448, 130878.				No			2023.0	FTIR;GPC;WCA;GCMS	PLA plastic film was prepared by dissolving PLA feedstock in dichloroethane. Micrometer caliper was used to select PLA films with thickness range of 0.021–0.029 cm.		No	No	Culture collection	Culture collection		No		
Abortiporus biennis	137743	PS	Zerva, A., Siaperas, R., Taxeidis, G., Kyriakidi, M., Vouyiouka, S., Zervakis, G. I., & Topakas, E. (2023). Investigation of abortiporus biennis lignocellulolytic toolbox, and the role of laccases in polystyrene degradation. Chemosphere, 312, 137338.	Laccase			No			2023.0	FTIR;LCMS	PS in the form of pellets (PS Crystal 154) was purchased from Total Petrochemicals and cryomilled into powder (particle diameter <500 μm) in a Pulverisette 14 (Fritsch Corp., Idar-Oberstein, Germany).	Total Petrochemcials	No	No	Culture collection	Culture collection		No		
Methylobacterium radiotolerans	31998	LDPE	Nademo, Z. M., Shibeshi, N. T., & Gemeda, M. T. (2023). Isolation and screening of low-density polyethylene (LDPE) bags degrading bacteria from Addis Ababa municipal solid waste disposal site “Koshe”. Annals of Microbiology, 73(1), 6.				No			2023.0	Clear zone;Weight loss;FTIR;SEM	LDPE granules were collected from Ethiopia Plastic Factory and used for enriching LDPE-degrader bacterial isolates after being prepared in powder form. The powder was prepared by immersing LDPE granules in xylene and boiling them for 15 min (Bhatia et al. 2014). The powder was washed with 95% ethanol, dried overnight in a hot air oven at 50 °C, and stored at room temperature for further use. Low-density polyethylene films required for the biodegradation study were purchased from a local market and prepared by cutting into 1.5 cm × 1.5 cm size pieces.	Ethiopia Plastic Factory (LDPE granules)	No	No	Soil	Solid waste disposal area	Ethiopia	No		
Methylobacterium fujisawaense	107400	LDPE	Nademo, Z. M., Shibeshi, N. T., & Gemeda, M. T. (2023). Isolation and screening of low-density polyethylene (LDPE) bags degrading bacteria from Addis Ababa municipal solid waste disposal site “Koshe”. Annals of Microbiology, 73(1), 6.				No			2023.0	Clear zone;Weight loss;FTIR;SEM	LDPE granules were collected from Ethiopia Plastic Factory and used for enriching LDPE-degrader bacterial isolates after being prepared in powder form. The powder was prepared by immersing LDPE granules in xylene and boiling them for 15 min (Bhatia et al. 2014). The powder was washed with 95% ethanol, dried overnight in a hot air oven at 50 °C, and stored at room temperature for further use. Low-density polyethylene films required for the biodegradation study were purchased from a local market and prepared by cutting into 1.5 cm × 1.5 cm size pieces.	Ethiopia Plastic Factory (LDPE granules)	No	No	Soil	Solid waste disposal area	Ethiopia	No		
Lysinibacillus fusiformis	28031	LDPE	Nademo, Z. M., Shibeshi, N. T., & Gemeda, M. T. (2023). Isolation and screening of low-density polyethylene (LDPE) bags degrading bacteria from Addis Ababa municipal solid waste disposal site “Koshe”. Annals of Microbiology, 73(1), 6.				No			2023.0	Clear zone;Weight loss;FTIR;SEM	LDPE granules were collected from Ethiopia Plastic Factory and used for enriching LDPE-degrader bacterial isolates after being prepared in powder form. The powder was prepared by immersing LDPE granules in xylene and boiling them for 15 min (Bhatia et al. 2014). The powder was washed with 95% ethanol, dried overnight in a hot air oven at 50 °C, and stored at room temperature for further use. Low-density polyethylene films required for the biodegradation study were purchased from a local market and prepared by cutting into 1.5 cm × 1.5 cm size pieces.	Ethiopia Plastic Factory (LDPE granules)	No	No	Soil	Solid waste disposal area	Ethiopia	No		
Rhizopus oryzae	64495	PU	Wu, K. Y., Yang, T. X., Yang, M., Wu, J. Q., Li, X., Chen, X. D., ... & Yang, X. Y. (2023). Preliminary identification of soil fungi for the degradation of polyurethane film. Archives of Microbiology, 205(4), 145.				No			2023.0	Weight loss;SEM	A polyester PU film with a thickness of 0.1 mm was acquired from Jiaxin Plastic Materials Co., Ltd. The film was pre- pared using poly(ethylene–glycol–adipate) diols and tolu- ene diisocyanate (TDI). Waterborne PU was purchased from Nanning Shuoheng Technology Co., Ltd.	Jiaxin Plastic Materials Co., Ltd. (PU film);Nanning Shuoheng Technology Co., Ltd. (Waterbourne PU)	No	No	Soil	Waste transfer station	China	No		
Alternaria alternata	5599	PU	Wu, K. Y., Yang, T. X., Yang, M., Wu, J. Q., Li, X., Chen, X. D., ... & Yang, X. Y. (2023). Preliminary identification of soil fungi for the degradation of polyurethane film. Archives of Microbiology, 205(4), 145.				No			2023.0	Weight loss;SEM	A polyester PU film with a thickness of 0.1 mm was acquired from Jiaxin Plastic Materials Co., Ltd. The film was pre- pared using poly(ethylene–glycol–adipate) diols and tolu- ene diisocyanate (TDI). Waterborne PU was purchased from Nanning Shuoheng Technology Co., Ltd.	Jiaxin Plastic Materials Co., Ltd. (PU film);Nanning Shuoheng Technology Co., Ltd. (Waterbourne PU)	No	No	Soil	Waste transfer station	China	No		
Pseudideonella sakaiensis	1547922	PET	Poulsen, J. S., & Nielsen, J. L. (2023). Proteomic characterisation of polyethylene terephthalate and monomer degradation by Ideonella sakaiensis. Journal of Proteomics, 279, 104888.	PET hydrolase			No			2023.0	Protemoic anaylsis;Quantitative spectrometry	Amorphus and cryo-milled PET	AIM-PLAS	No	No	Culture collection	Culture collection		No		
Pseudideonella sakaiensis	1547922	PET	Poulsen, J. S., & Nielsen, J. L. (2023). Proteomic characterisation of polyethylene terephthalate and monomer degradation by Ideonella sakaiensis. Journal of Proteomics, 279, 104888.	MHET hydrolase			No			2023.0	Protemoic anaylsis;Quantitative spectrometry	Amorphus and cryo-milled PET	AIM-PLAS	No	No	Culture collection	Culture collection		No		
Brucella cytisi	407152	LDPE	Alamer, N. J., Aldayel, M. F., & Khalifa, A. (2023). Isolation and Characterization of Brucella spp., Low-Density Polyethylene (LDPE) Plastic Degrading Bacteria in Al-Ahsa Region, Saudi Arabia. Applied Sciences, 13(7), 4629.				No			2023.0	Weight loss;FTIR;GCMS	LDPE powder			No	Water	Industrial plastic facility	Saudi Arabia	No		
Brucella tritici	94626	LDPE	Alamer, N. J., Aldayel, M. F., & Khalifa, A. (2023). Isolation and Characterization of Brucella spp., Low-Density Polyethylene (LDPE) Plastic Degrading Bacteria in Al-Ahsa Region, Saudi Arabia. Applied Sciences, 13(7), 4629.				No			2023.0	Weight loss;FTIR;GCMS	LDPE powder			No	Water	Industrial plastic facility	Saudi Arabia	No		
Stenotrophomonas maltophilia	40324	PET	Din, S. U., Kalsoom, Satti, S. M., Uddin, S., Mankar, S. V., Ceylan, E., Hasan, F., Khan, S., Badshah, M., Belduz, A. O., Canakci, S., Zhang, B., Linares-Pasten, J. A., & Shah, A. A. (2023). The Purification and Characterization of a Cutinase-like Enzyme with Activity on Polyethylene Terephthalate (PET) from a Newly Isolated Bacterium Stenotrophomonas maltophilia PRS8 at a Mesophilic Temperature. Applied Sciences, 13(6), 3686.	Cutinase			No			2023.0	Weight loss;FTIR;SEM	PET flakes from mineral water bottles and PET beads	Nestle (flakes); Indorama (beads)	No	No	Soil	Garbage Dump		No		
Enterobacter sp.	42895	PS	Jiménez-Perez, C., Gómez-Ruiz, L., González-Olivares, L., Fernández, F. J., & Cruz-Guerrero, A. E. (2023). Biodegradation of polystyrene with laccase-producing enterobacteria isolated from a municipal waste dump. Revista Mexicana de Ingeniería Química, 22(1), Bio2971-Bio2971.	Laccase			No			2023.0	Weight loss	Two different PS samples were used. The first one was a 1 g commercially available crystal PS (PM 192,000; Sigma- Aldrich, EUA). The second sample comprised a commercial cup made of expanded PS that was cut into pieces of 2 x 3 cm, which weighed approximately 0.5 g in total.	Sigma-Aldrich (crystal)	No	No	Plastic waste	Garbage Dump	Mexico	No		
Enterobacter sp.	42895	PS	Jiménez-Perez, C., Gómez-Ruiz, L., González-Olivares, L., Fernández, F. J., & Cruz-Guerrero, A. E. (2023). Biodegradation of polystyrene with laccase-producing enterobacteria isolated from a municipal waste dump. Revista Mexicana de Ingeniería Química, 22(1), Bio2971-Bio2971.	Laccase			No			2023.0	Weight loss	Two different PS samples were used. The first one was a 1 g commercially available crystal PS (PM 192,000; Sigma- Aldrich, EUA). The second sample comprised a commercial cup made of expanded PS that was cut into pieces of 2 x 3 cm, which weighed approximately 0.5 g in total.	Sigma-Aldrich (crystal)	No	No	Plastic waste	Garbage Dump	Mexico	No		
Enterobacter sp.	42895	PS	Jiménez-Perez, C., Gómez-Ruiz, L., González-Olivares, L., Fernández, F. J., & Cruz-Guerrero, A. E. (2023). Biodegradation of polystyrene with laccase-producing enterobacteria isolated from a municipal waste dump. Revista Mexicana de Ingeniería Química, 22(1), Bio2971-Bio2971.	Laccase			No			2023.0	Weight loss	Two different PS samples were used. The first one was a 1 g commercially available crystal PS (PM 192,000; Sigma- Aldrich, EUA). The second sample comprised a commercial cup made of expanded PS that was cut into pieces of 2 x 3 cm, which weighed approximately 0.5 g in total.	Sigma-Aldrich (crystal)	No	No	Plastic waste	Garbage Dump	Mexico	No		
Priestia megaterium	1404	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Priestia megaterium	1404	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Priestia megaterium	1404	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Klebsiella pneumoniae	573	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Pseudomonas fluorescens	294	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Enterobacter ludwigii	299767	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Chryseobacterium sp.	1871047	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Fusarium solani	169388	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Fusarium solani	169388	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Fusarium oxysporum	5507	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Fusarium oxysporum	5507	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Lecanicillium araneicola	501694	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Lecanicillium araneicola	501694	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Trichoderma lixii	1491472	PE	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Serratia marcescens	615	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Serratia marcescens	615	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Serratia marcescens	615	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Serratia marcescens	615	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Serratia marcescens	615	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Enterobacter hormaechei subsp. Xiangfangensis	1296536	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Enterobacter sp.	42895	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Aspergillus flavus	5059	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Aspergillus flavus	5059	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Aspergillus fumigatus	746128	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Aspergillus fumigatus	746128	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Fusarium oxysporum	5507	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Penicillium granulatum	395885	PP	Wróbel, M., Szymańska, S., Kowalkowski, T., & Hrynkiewicz, K. (2023). Selection of microorganisms capable of polyethylene (PE) and polypropylene (PP) degradation. Microbiological Research, 267, 127251.				No			2023.0	SEM;FTIR	Granular polymers were obtained from Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University in Torun ́. Thirty uniformly sized granules (1350 – 1800 μm) of each polymer were placed in 100 ml conical flasks containing 20 ml 0.85 % NaCl.	Department of Physical Chemistry and Physicochemistry of Polymers, Nicolaus Copernicus University	No	No	Soil	Landfill	Poland	No		
Pseudomonas aeruginosa	287	PE	Mehmood, S., Ilyas, N., Akhtar, N., Chia, W. Y., Shati, A. A., Alfaifi, M. Y., Sayyed, R. Z., Pusparizkita, Y. M., Munawaroh, H. S. H., Quan, P. M., & Show, P. L. (2023). Structural breakdown and phytotoxic assessments of PE degradation through acid hydrolysis, starch addition and Pseudomonas aeruginosa bioremediation. Environmental Research, 217, 114784				No			2023.0	Weight loss;FTIR	PE bags were collected from a stationery shop in Rawalpindi, Punjab, Pakistan.		No	No	Soil	Soil	Pakistan	No		
Penicillium citrinum	5077	PU	Taxeidis, G., Nikolaivits, E., Siaperas, R., Gkountela, C., Vouyiouka, S., Pantelic, B., Nikodinovic-Runic, J., & Topakas, E. (2023). Triggering and identifying the polyurethane and polyethylene-degrading machinery of filamentous fungi secretomes. Environmental Pollution, 325, 121460.				No			2023.0	Clear zone	The culture supernatants obtained after inducing putative depoly- merizing enzymes using Impranil® DLN-SD or lcAlk, were tested for their ability to degrade ether-based PU or LDPE powder, respectively. In detail, 50 mg of PU or LDPE powder were incubated with 50 mL of the culture supernatant at 30 ◦C under continuous stirring at 160 rpm for 4 days. Regarding control samples, PU powder was incubated with an equal amount of culture supernatant that had been previously inacti- vated by boiling for 15 min, while for LDPE degradation, MM/hex- adecane supernatant was used. After incubation, plastic powders were separated by centrifugation at 20,000×g for 10 min, resuspended in 10 mL of sodium dodecyl sulfate solution (SDS) (2% w/v), and kept under stirring for 10 min to remove potentially attached proteins. After discarding the SDS solution, poly- meric powders were rinsed twice with 40 mL ultrapure water followed Environmental Pollution 325 (2023) 121460 by centrifugation, and finally separated and dried before their properties were determined.			No	Dead isopods			No		
Aspergillus sp.	5065	PU	Taxeidis, G., Nikolaivits, E., Siaperas, R., Gkountela, C., Vouyiouka, S., Pantelic, B., Nikodinovic-Runic, J., & Topakas, E. (2023). Triggering and identifying the polyurethane and polyethylene-degrading machinery of filamentous fungi secretomes. Environmental Pollution, 325, 121460.	Esterase			No			2023.0	Clear zone;weight loss	The culture supernatants obtained after inducing putative depoly- merizing enzymes using Impranil® DLN-SD or lcAlk, were tested for their ability to degrade ether-based PU or LDPE powder, respectively. In detail, 50 mg of PU or LDPE powder were incubated with 50 mL of the culture supernatant at 30 ◦C under continuous stirring at 160 rpm for 4 days. Regarding control samples, PU powder was incubated with an equal amount of culture supernatant that had been previously inacti- vated by boiling for 15 min, while for LDPE degradation, MM/hex- adecane supernatant was used. After incubation, plastic powders were separated by centrifugation at 20,000×g for 10 min, resuspended in 10 mL of sodium dodecyl sulfate solution (SDS) (2% w/v), and kept under stirring for 10 min to remove potentially attached proteins. After discarding the SDS solution, poly- meric powders were rinsed twice with 40 mL ultrapure water followed Environmental Pollution 325 (2023) 121460 by centrifugation, and finally separated and dried before their properties were determined.			No	Dead isopods			No		
Aspergillus sp.	5065	LDPE	Taxeidis, G., Nikolaivits, E., Siaperas, R., Gkountela, C., Vouyiouka, S., Pantelic, B., Nikodinovic-Runic, J., & Topakas, E. (2023). Triggering and identifying the polyurethane and polyethylene-degrading machinery of filamentous fungi secretomes. Environmental Pollution, 325, 121460.				No			2023.0	FTIR	The culture supernatants obtained after inducing putative depoly- merizing enzymes using Impranil® DLN-SD or lcAlk, were tested for their ability to degrade ether-based PU or LDPE powder, respectively. In detail, 50 mg of PU or LDPE powder were incubated with 50 mL of the culture supernatant at 30 ◦C under continuous stirring at 160 rpm for 4 days. Regarding control samples, PU powder was incubated with an equal amount of culture supernatant that had been previously inacti- vated by boiling for 15 min, while for LDPE degradation, MM/hex- adecane supernatant was used. After incubation, plastic powders were separated by centrifugation at 20,000×g for 10 min, resuspended in 10 mL of sodium dodecyl sulfate solution (SDS) (2% w/v), and kept under stirring for 10 min to remove potentially attached proteins. After discarding the SDS solution, poly- meric powders were rinsed twice with 40 mL ultrapure water followed Environmental Pollution 325 (2023) 121460 by centrifugation, and finally separated and dried before their properties were determined.			No	Dead isopods			No		
Fusarium oxysporum	5507	PU	Taxeidis, G., Nikolaivits, E., Siaperas, R., Gkountela, C., Vouyiouka, S., Pantelic, B., Nikodinovic-Runic, J., & Topakas, E. (2023). Triggering and identifying the polyurethane and polyethylene-degrading machinery of filamentous fungi secretomes. Environmental Pollution, 325, 121460.	Esterase			No			2023.0	Clear zone;weight loss	The culture supernatants obtained after inducing putative depoly- merizing enzymes using Impranil® DLN-SD or lcAlk, were tested for their ability to degrade ether-based PU or LDPE powder, respectively. In detail, 50 mg of PU or LDPE powder were incubated with 50 mL of the culture supernatant at 30 ◦C under continuous stirring at 160 rpm for 4 days. Regarding control samples, PU powder was incubated with an equal amount of culture supernatant that had been previously inacti- vated by boiling for 15 min, while for LDPE degradation, MM/hex- adecane supernatant was used. After incubation, plastic powders were separated by centrifugation at 20,000×g for 10 min, resuspended in 10 mL of sodium dodecyl sulfate solution (SDS) (2% w/v), and kept under stirring for 10 min to remove potentially attached proteins. After discarding the SDS solution, poly- meric powders were rinsed twice with 40 mL ultrapure water followed Environmental Pollution 325 (2023) 121460 by centrifugation, and finally separated and dried before their properties were determined.			No	Sediment	River	Ireland	No		
Fusarium oxysporum	5507	PU	Taxeidis, G., Nikolaivits, E., Siaperas, R., Gkountela, C., Vouyiouka, S., Pantelic, B., Nikodinovic-Runic, J., & Topakas, E. (2023). Triggering and identifying the polyurethane and polyethylene-degrading machinery of filamentous fungi secretomes. Environmental Pollution, 325, 121460.	Esterase			No			2023.0	Clear zone;weight loss	The culture supernatants obtained after inducing putative depoly- merizing enzymes using Impranil® DLN-SD or lcAlk, were tested for their ability to degrade ether-based PU or LDPE powder, respectively. In detail, 50 mg of PU or LDPE powder were incubated with 50 mL of the culture supernatant at 30 ◦C under continuous stirring at 160 rpm for 4 days. Regarding control samples, PU powder was incubated with an equal amount of culture supernatant that had been previously inacti- vated by boiling for 15 min, while for LDPE degradation, MM/hex- adecane supernatant was used. After incubation, plastic powders were separated by centrifugation at 20,000×g for 10 min, resuspended in 10 mL of sodium dodecyl sulfate solution (SDS) (2% w/v), and kept under stirring for 10 min to remove potentially attached proteins. After discarding the SDS solution, poly- meric powders were rinsed twice with 40 mL ultrapure water followed Environmental Pollution 325 (2023) 121460 by centrifugation, and finally separated and dried before their properties were determined.			No	Soil	Garbage Dump	Serbia	No		
Alcanivorax sp.	1872427	LDPE	Zadjelovic, V., Erni-Cassola, G., Obrador-Viel, T., Lester, D., Eley, Y., Gibson, M. I., Dorador, C., Golyshin, P. N., Black, S., Wellington, E. M. H., & Christie-Oleza, J. A. (2022). A mechanistic understanding of polyethylene biodegradation by the marine bacterium Alcanivorax. Journal of Hazardous Materials, 436, 129278.				No			2022.0	FTIR:ATR-FTRI;GCP/SEC;TOC;ROS	pristine and weathered LDPE pellets (~2–3 mm, Sigma-Aldrich®) and films (IAEA-CH-7, International Atomic Energy Agency, IAEA 	Pellets from Sigma-Aldrich, films from International Atomic Energy Agency	Yes	Yes	Plastic debris	Marine		No		
Terribacillus sp.	1925026	PBS	Kim, S. H., Cho, J. Y., Cho, D. H., Jung, H. J., Kim, B. C., Bhatia, S. K., Park, S. H., Park, K., & Yang, Y. H. (2022). Acceleration of Polybutylene Succinate Biodegradation by Terribacillus sp. JY49 Isolated from a Marine Environment. Polymers, 14(19), 3978.				No			2022.0	SEM;GPC;FTIR;HPLC	Pellets	Gio Soltech Co.	Yes	No	Soil	Marine	Korea	No		
Terribacillus sp.	1925026	PBAT	Kim, S. H., Cho, J. Y., Cho, D. H., Jung, H. J., Kim, B. C., Bhatia, S. K., Park, S. H., Park, K., & Yang, Y. H. (2022). Acceleration of Polybutylene Succinate Biodegradation by Terribacillus sp. JY49 Isolated from a Marine Environment. Polymers, 14(19), 3978.				No			2022.0	Clear zone	MB agar medium containing plastic sourced from pellets	Gio Soltech Co.	Yes	No	Soil	Marine	Korea	No		
Terribacillus sp.	1925026	PCL	Kim, S. H., Cho, J. Y., Cho, D. H., Jung, H. J., Kim, B. C., Bhatia, S. K., Park, S. H., Park, K., & Yang, Y. H. (2022). Acceleration of Polybutylene Succinate Biodegradation by Terribacillus sp. JY49 Isolated from a Marine Environment. Polymers, 14(19), 3978.				No			2022.0	Clear zone	MB agar medium containing plastic sourced from pellets		Yes	No	Soil	Marine	Korea	No		
Terribacillus sp.	1925026	P(3HB-co-3HV)	Kim, S. H., Cho, J. Y., Cho, D. H., Jung, H. J., Kim, B. C., Bhatia, S. K., Park, S. H., Park, K., & Yang, Y. H. (2022). Acceleration of Polybutylene Succinate Biodegradation by Terribacillus sp. JY49 Isolated from a Marine Environment. Polymers, 14(19), 3978.				No			2022.0	Clear zone	MB agar medium containing plastic sourced from pellets	Sigma Aldrich	Yes	No	Soil	Marine	Korea	No		
Terribacillus sp.	1925026	P(3HV-co-4HB)	Kim, S. H., Cho, J. Y., Cho, D. H., Jung, H. J., Kim, B. C., Bhatia, S. K., Park, S. H., Park, K., & Yang, Y. H. (2022). Acceleration of Polybutylene Succinate Biodegradation by Terribacillus sp. JY49 Isolated from a Marine Environment. Polymers, 14(19), 3978.				No			2022.0	Clear zone	MB agar medium containing plastic sourced from pellets	CJ	Yes	No	Soil	Marine	Korea	No		
Moraxella sp.	479	PET	Blázquez-Sánchez, P., Engelberger, F., Cifuentes-Anticevic, J., Sonnendecker, C., Griñén, A., Reyes, J., Díez, B., Guixé, V., Richter, P. K., Zimmermann, W., & Ramírez-Sarmiento, C. A. (2022). Antarctic polyester hydrolases degrade aliphatic and aromatic polyesters at moderate temperatures. Applied and Environmental Microbiology, 88(1), e01842-21.	Lipase	00213	00213 | Lipase | Moraxella sp. | PET	Yes	P19833	MNKSILKKLSFGTSVLLVSMNALSWTPSPTPNPDPIPDPTPCQDDCDFTRGPNPTPSSLEASTGPYSVATRSVASSVSGFGGGTLHYPTNTTGTMGAIAVVPGFLLQESSIDFWGPKLASHGFVVITISANSGFDQPASRATQLGRALDYVINQSNGSNSPISGMVDTTRLGVVGWSMGGGGALQLASGDRLSAAIPIAPWNQGGNRFDQIETPTLVIACENDVVASVNSHASPFYNRIPSTTDKAYLEINGGSHFCANDGGSIGGLLGKYGVSWMKRFIDNDLRYDAFLCGPDHAANRSVSEYRDTCNY	2022.0	Clear zone;SEM;HPLC	PET nanoparticles suspended in agar, PET films			No				Yes		
Oleispira antarctica	188908	PET	Blázquez-Sánchez, P., Engelberger, F., Cifuentes-Anticevic, J., Sonnendecker, C., Griñén, A., Reyes, J., Díez, B., Guixé, V., Richter, P. K., Zimmermann, W., & Ramírez-Sarmiento, C. A. (2022). Antarctic polyester hydrolases degrade aliphatic and aromatic polyesters at moderate temperatures. Applied and Environmental Microbiology, 88(1), e01842-21.	Lipase	00214	00214 | Lipase | Olespira antarctica | PET	Yes	R4YKL9	MFIMIKKSELAKAIIVTGALVFSIPTLAEVTLSETTVSSIKSEATVSSTKKALPATPSDCIADSKITAVALSDTRDNGPFSIRTKRISRQSAKGFGGGTIHYPTNASGCGLLGAIAVVPGYVSYENSIKWWGPRLASWGFVVITINTNSIYDDPDSRAAQLNAALDNMIADDTVGSMIDPKRLGAIGWSMGGGGALKLATERSTVRAIMPLAPYHDKSYGEVKTPTLVIACEDDRIAETKKYANAFYKNAIGPKMKVEVNNGSHFCPSYRFNEILLSKPGIAWMQRYINNDTRFDKFLCANENYSKSPRISAYDYKDCP	2022.0	Clear zone;SEM;HPLC	PET nanoparticles suspended in agar, PET films			No				Yes		
Aspergillus terreus	33178	LDPE	Eldin, A. M., Al-Sharnouby, S. F. S., ElGabry, K. I. M., & Ramadan, A. I. (2022). Aspergillus terreus, Penicillium sp. and Bacillus sp. isolated from mangrove soil having laccase and peroxidase role in depolymerization of polyethylene bags. Process Biochemistry, 118, 215-226.	Laccase			No			2022.0	Weight loss;ATR-FTIR;SEM	Plastic bags		No	No	Soil	Mangrove forest at Red Sea shore	Egypt	No		
Aspergillus terreus	33178	LDPE	Eldin, A. M., Al-Sharnouby, S. F. S., ElGabry, K. I. M., & Ramadan, A. I. (2022). Aspergillus terreus, Penicillium sp. and Bacillus sp. isolated from mangrove soil having laccase and peroxidase role in depolymerization of polyethylene bags. Process Biochemistry, 118, 215-226.	Peroxidase			No			2022.0	Weight loss;ATR-FTIR;SEM	Plastic bags		No	No	Soil	Mangrove forest at Red Sea shore	Egypt	No		
Penicillium sp.	5081	LDPE	Eldin, A. M., Al-Sharnouby, S. F. S., ElGabry, K. I. M., & Ramadan, A. I. (2022). Aspergillus terreus, Penicillium sp. and Bacillus sp. isolated from mangrove soil having laccase and peroxidase role in depolymerization of polyethylene bags. Process Biochemistry, 118, 215-226.	Laccase			No			2022.0	Weight loss;ATR-FTIR;SEM	Plastic bags		No	No	Soil	Mangrove forest at Red Sea shore	Egypt	No		
Penicillium sp.	5081	LDPE	Eldin, A. M., Al-Sharnouby, S. F. S., ElGabry, K. I. M., & Ramadan, A. I. (2022). Aspergillus terreus, Penicillium sp. and Bacillus sp. isolated from mangrove soil having laccase and peroxidase role in depolymerization of polyethylene bags. Process Biochemistry, 118, 215-226.	Peroxidase			No			2022.0	Weight loss;ATR-FTIR;SEM	Plastic bags		No	No	Soil	Mangrove forest at Red Sea shore	Egypt	No		
Bacillus sp.	1409	LDPE	Eldin, A. M., Al-Sharnouby, S. F. S., ElGabry, K. I. M., & Ramadan, A. I. (2022). Aspergillus terreus, Penicillium sp. and Bacillus sp. isolated from mangrove soil having laccase and peroxidase role in depolymerization of polyethylene bags. Process Biochemistry, 118, 215-226.	Laccase			No			2022.0	Weight loss;ATR-FTIR;SEM	Plastic bags		No	No	Soil	Mangrove forest at Red Sea shore	Egypt	No		
Bacillus sp.	1409	LDPE	Eldin, A. M., Al-Sharnouby, S. F. S., ElGabry, K. I. M., & Ramadan, A. I. (2022). Aspergillus terreus, Penicillium sp. and Bacillus sp. isolated from mangrove soil having laccase and peroxidase role in depolymerization of polyethylene bags. Process Biochemistry, 118, 215-226.	Peroxidase			No			2022.0	Weight loss;ATR-FTIR;SEM	Plastic bags		No	No	Soil	Mangrove forest at Red Sea shore	Egypt	No		
Agrocybe aegerita	1973307	PE	Bertolacci, L., Goldoni, L., Zych, A., & Athanassiou, A. (2022). Biocatalytic oxidation of polyethylene by Agrocybe aegerita mycelium. Polymer Degradation and Stability, 199, 109911				No			2022.0	SEM;ATR-FTIR;Tensilometer;NMR	LDPE sheets	Goodfellow	No	No	Culture collection	Culture collection	Germany	No		
Penicillium citrinum	5077	LDPE	Khan, S., Ali, S. A., & Ali, A. S. (2023). Biodegradation of low density polyethylene (LDPE) by mesophilic fungus ‘Penicillium citrinum’isolated from soils of plastic waste dump yard, Bhopal, India. Environmental Technology, 44(15), 2300-2314.	Lipase			No			2022.0	Clear zone;weight loss;FE-SEM;FTIR:TGA	LDPE film	B.N. polymers Ltd	No	No	Soil	Landfill	India	No		
Penicillium citrinum	5077	LDPE	Khan, S., Ali, S. A., & Ali, A. S. (2023). Biodegradation of low density polyethylene (LDPE) by mesophilic fungus ‘Penicillium citrinum’isolated from soils of plastic waste dump yard, Bhopal, India. Environmental Technology, 44(15), 2300-2314.	Esterase			No			2022.0	Clear zone;weight loss;FE-SEM;FTIR:TGA	LDPE film	B.N. polymers Ltd	No	No	Soil	Landfill	India	No		
Penicillium citrinum	5077	LDPE	Khan, S., Ali, S. A., & Ali, A. S. (2023). Biodegradation of low density polyethylene (LDPE) by mesophilic fungus ‘Penicillium citrinum’isolated from soils of plastic waste dump yard, Bhopal, India. Environmental Technology, 44(15), 2300-2314.	Laccase			No			2022.0	Clear zone;weight loss;FE-SEM;FTIR:TGA	LDPE film	B.N. polymers Ltd	No	No	Soil	Landfill	India	No		
Penicillium citrinum	5077	LDPE	Khan, S., Ali, S. A., & Ali, A. S. (2023). Biodegradation of low density polyethylene (LDPE) by mesophilic fungus ‘Penicillium citrinum’isolated from soils of plastic waste dump yard, Bhopal, India. Environmental Technology, 44(15), 2300-2314.	Manganase peroxidase			No			2022.0	Clear zone;weight loss;FE-SEM;FTIR:TGA	LDPE film	B.N. polymers Ltd	No	No	Soil	Landfill	India	No		
Aspergillus niger	5061	LDPE	Maroof, L., Iqbal, M., Farman, S., & Faisal, S. (2022). Biodegradation of Low-Density Polyethylene (LDPE) Bags by Fungi Isolated from Waste Disposal Soil. Applied and Environmental Soil Science, 2022.				No	MA		2022.0	Weight loss;FTIR	For making the plastics hydrophobic, pretreatment was performed by using UV (360 nm) and heat treatment (70°C) [26].			No	Soil	Landfill	Pakistan	No		
Aspergillus flavus	5059	LDPE	Maroof, L., Iqbal, M., Farman, S., & Faisal, S. (2022). Biodegradation of Low-Density Polyethylene (LDPE) Bags by Fungi Isolated from Waste Disposal Soil. Applied and Environmental Soil Science, 2022.				No			2022.0	Weight loss;FTIR	For making the plastics hydrophobic, pretreatment was performed by using UV (360 nm) and heat treatment (70°C) [26].			No	Soil	Landfill	Pakistan	No		
Aspergillus fumigatus	746128	PBSA	Chien, H. L., Tsai, Y. T., Tseng, W. S., Wu, J. A., Kuo, S. L., Chang, S. L., Huang, S. L., & Liu, C. T. (2022). Biodegradation of PBSA films by elite aspergillus isolates and farmland soil. Polymers, 14(7), 1320.	Lipase			No			2022.0	Clear zone;weight loss;SEM;NMR	PBSA (number average molecular weight, Mn = 51,899 Daltons; weight average molecular weight, Mw = 77,951 Daltons) particles and films (thickness: 50 μm) were provided by the Industrial Technology Research Institute (ITRI). The constituent ratios of SA, AA, and BDO for the PBSA film were 37%, 13%, and 49.9%, respectively.	Industrial Technology Research Institute	No	No	Soil	Soil	Taiwan	No		
Aspergillus fumigatus	746128	PBSA	Chien, H. L., Tsai, Y. T., Tseng, W. S., Wu, J. A., Kuo, S. L., Chang, S. L., Huang, S. L., & Liu, C. T. (2022). Biodegradation of PBSA films by elite aspergillus isolates and farmland soil. Polymers, 14(7), 1320.	Esterase			No			2022.0	Clear zone;weight loss;SEM;NMR	PBSA (number average molecular weight, Mn = 51,899 Daltons; weight average molecular weight, Mw = 77,951 Daltons) particles and films (thickness: 50 μm) were provided by the Industrial Technology Research Institute (ITRI). The constituent ratios of SA, AA, and BDO for the PBSA film were 37%, 13%, and 49.9%, respectively.	Industrial Technology Research Institute	No	No	Soil	Soil	Taiwan	No		
Aspergillus terreus	33178	PBSA	Chien, H. L., Tsai, Y. T., Tseng, W. S., Wu, J. A., Kuo, S. L., Chang, S. L., Huang, S. L., & Liu, C. T. (2022). Biodegradation of PBSA films by elite aspergillus isolates and farmland soil. Polymers, 14(7), 1320.	Lipase			No			2022.0	Clear zone;weight loss;SEM;NMR	PBSA (number average molecular weight, Mn = 51,899 Daltons; weight average molecular weight, Mw = 77,951 Daltons) particles and films (thickness: 50 μm) were provided by the Industrial Technology Research Institute (ITRI). The constituent ratios of SA, AA, and BDO for the PBSA film were 37%, 13%, and 49.9%, respectively.	Industrial Technology Research Institute	No	No	Soil	Soil	Taiwan	No		
Aspergillus terreus	33178	PBSA	Chien, H. L., Tsai, Y. T., Tseng, W. S., Wu, J. A., Kuo, S. L., Chang, S. L., Huang, S. L., & Liu, C. T. (2022). Biodegradation of PBSA films by elite aspergillus isolates and farmland soil. Polymers, 14(7), 1320.	Esterase			No			2022.0	Clear zone;weight loss;SEM;NMR	PBSA (number average molecular weight, Mn = 51,899 Daltons; weight average molecular weight, Mw = 77,951 Daltons) particles and films (thickness: 50 μm) were provided by the Industrial Technology Research Institute (ITRI). The constituent ratios of SA, AA, and BDO for the PBSA film were 37%, 13%, and 49.9%, respectively.	Industrial Technology Research Institute	No	No	Soil	Soil	Taiwan	No		
Didymella pinodella	749633	PVA	Mohamed, H., Shah, A. M., Nazir, Y., Naz, T., Nosheen, S., & Song, Y. (2022). Biodegradation of poly (vinyl alcohol) by an orychophragmus rhizosphere-associated fungus Penicillium brevicompactum OVR-5, and its proposed PVA biodegradation pathway. World Journal of Microbiology and Biotechnology, 38, 1-18.				No			2022.0	Clear zone	Commercial PVA (Table 1) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, China, and had a 1750 ± 50 polymerisation degree and 99.0% saponification degree.	Sinopharm Chemical Reagent Co., Ltd.	No	No	Papaver rhoeas	Plant associated	China	No		
Penicillium polonicum	60169	PVA	Mohamed, H., Shah, A. M., Nazir, Y., Naz, T., Nosheen, S., & Song, Y. (2022). Biodegradation of poly (vinyl alcohol) by an orychophragmus rhizosphere-associated fungus Penicillium brevicompactum OVR-5, and its proposed PVA biodegradation pathway. World Journal of Microbiology and Biotechnology, 38, 1-18.				No			2022.0	Clear zone;SEM;FTIR	Commercial PVA (Table 1) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, China, and had a 1750 ± 50 polymerisation degree and 99.0% saponification degree.	Sinopharm Chemical Reagent Co., Ltd.	No	No	Brassica juncea	Plant associated	China	No		
Aspergillus keveii	714993	PVA	Mohamed, H., Shah, A. M., Nazir, Y., Naz, T., Nosheen, S., & Song, Y. (2022). Biodegradation of poly (vinyl alcohol) by an orychophragmus rhizosphere-associated fungus Penicillium brevicompactum OVR-5, and its proposed PVA biodegradation pathway. World Journal of Microbiology and Biotechnology, 38, 1-18.				No			2022.0	Clear zone	Commercial PVA (Table 1) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, China, and had a 1750 ± 50 polymerisation degree and 99.0% saponification degree.	Sinopharm Chemical Reagent Co., Ltd.	No	No	Brassica juncea	Plant associated	China	No		
Aspergillus tubingensis	5068	PVA	Mohamed, H., Shah, A. M., Nazir, Y., Naz, T., Nosheen, S., & Song, Y. (2022). Biodegradation of poly (vinyl alcohol) by an orychophragmus rhizosphere-associated fungus Penicillium brevicompactum OVR-5, and its proposed PVA biodegradation pathway. World Journal of Microbiology and Biotechnology, 38, 1-18.				No			2022.0	Clear zone	Commercial PVA (Table 1) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, China, and had a 1750 ± 50 polymerisation degree and 99.0% saponification degree.	Sinopharm Chemical Reagent Co., Ltd.	No	No	Brassica juncea	Plant associated	China	No		
Cladosporium sp.	1707700	PVA	Mohamed, H., Shah, A. M., Nazir, Y., Naz, T., Nosheen, S., & Song, Y. (2022). Biodegradation of poly (vinyl alcohol) by an orychophragmus rhizosphere-associated fungus Penicillium brevicompactum OVR-5, and its proposed PVA biodegradation pathway. World Journal of Microbiology and Biotechnology, 38, 1-18.				No			2022.0	Clear zone	Commercial PVA (Table 1) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, China, and had a 1750 ± 50 polymerisation degree and 99.0% saponification degree.	Sinopharm Chemical Reagent Co., Ltd.	No	No	Orychophragmus violaceus	Plant associated	China	No		
Alternaria tenuissima	119927	PVA	Mohamed, H., Shah, A. M., Nazir, Y., Naz, T., Nosheen, S., & Song, Y. (2022). Biodegradation of poly (vinyl alcohol) by an orychophragmus rhizosphere-associated fungus Penicillium brevicompactum OVR-5, and its proposed PVA biodegradation pathway. World Journal of Microbiology and Biotechnology, 38, 1-18.				No			2022.0	Clear zone	Commercial PVA (Table 1) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, China, and had a 1750 ± 50 polymerisation degree and 99.0% saponification degree.	Sinopharm Chemical Reagent Co., Ltd.	No	No	Brassica juncea	Plant associated	China	No		
Penicillium brevicompactum	5074	PVA	Mohamed, H., Shah, A. M., Nazir, Y., Naz, T., Nosheen, S., & Song, Y. (2022). Biodegradation of poly (vinyl alcohol) by an orychophragmus rhizosphere-associated fungus Penicillium brevicompactum OVR-5, and its proposed PVA biodegradation pathway. World Journal of Microbiology and Biotechnology, 38, 1-18.	Lipase			No			2022.0	Clear zone;SEM:FTIR;GCMS	Commercial PVA (Table 1) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, China, and had a 1750 ± 50 polymerisation degree and 99.0% saponification degree.	Sinopharm Chemical Reagent Co., Ltd.	No	No	Orychophragmus violaceus	Plant associated	China	No		
Penicillium brevicompactum	5074	PVA	Mohamed, H., Shah, A. M., Nazir, Y., Naz, T., Nosheen, S., & Song, Y. (2022). Biodegradation of poly (vinyl alcohol) by an orychophragmus rhizosphere-associated fungus Penicillium brevicompactum OVR-5, and its proposed PVA biodegradation pathway. World Journal of Microbiology and Biotechnology, 38, 1-18.	Laccase			No			2022.0	Clear zone;SEM:FTIR;GCMS	Commercial PVA (Table 1) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, China, and had a 1750 ± 50 polymerisation degree and 99.0% saponification degree.	Sinopharm Chemical Reagent Co., Ltd.	No	No	Orychophragmus violaceus	Plant associated	China	No		
Penicillium brevicompactum	5074	PVA	Mohamed, H., Shah, A. M., Nazir, Y., Naz, T., Nosheen, S., & Song, Y. (2022). Biodegradation of poly (vinyl alcohol) by an orychophragmus rhizosphere-associated fungus Penicillium brevicompactum OVR-5, and its proposed PVA biodegradation pathway. World Journal of Microbiology and Biotechnology, 38, 1-18.	Manganase peroxidase			No			2022.0	Clear zone;SEM:FTIR;GCMS	Commercial PVA (Table 1) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, China, and had a 1750 ± 50 polymerisation degree and 99.0% saponification degree.	Sinopharm Chemical Reagent Co., Ltd.	No	No	Orychophragmus violaceus	Plant associated	China	No		
Aspergillus niger	5061	PVA	Mohamed, H., Shah, A. M., Nazir, Y., Naz, T., Nosheen, S., & Song, Y. (2022). Biodegradation of poly (vinyl alcohol) by an orychophragmus rhizosphere-associated fungus Penicillium brevicompactum OVR-5, and its proposed PVA biodegradation pathway. World Journal of Microbiology and Biotechnology, 38, 1-18.				No			2022.0	Clear zone;SEM;FTIR	Commercial PVA (Table 1) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, China, and had a 1750 ± 50 polymerisation degree and 99.0% saponification degree.	Sinopharm Chemical Reagent Co., Ltd.	No	No	Brassica juncea	Plant associated	China	No		
Plectosphaerella cucumerina	40658	PVA	Mohamed, H., Shah, A. M., Nazir, Y., Naz, T., Nosheen, S., & Song, Y. (2022). Biodegradation of poly (vinyl alcohol) by an orychophragmus rhizosphere-associated fungus Penicillium brevicompactum OVR-5, and its proposed PVA biodegradation pathway. World Journal of Microbiology and Biotechnology, 38, 1-18.				No			2022.0	Clear zone	Commercial PVA (Table 1) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, China, and had a 1750 ± 50 polymerisation degree and 99.0% saponification degree.	Sinopharm Chemical Reagent Co., Ltd.	No	No	Papaver rhoeas	Plant associated	China	No		
Talaromyces verruculosus	198730	PVA	Mohamed, H., Shah, A. M., Nazir, Y., Naz, T., Nosheen, S., & Song, Y. (2022). Biodegradation of poly (vinyl alcohol) by an orychophragmus rhizosphere-associated fungus Penicillium brevicompactum OVR-5, and its proposed PVA biodegradation pathway. World Journal of Microbiology and Biotechnology, 38, 1-18.				No			2022.0	Clear zone;SEM;FTIR	Commercial PVA (Table 1) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, China, and had a 1750 ± 50 polymerisation degree and 99.0% saponification degree.	Sinopharm Chemical Reagent Co., Ltd.	No	No	Papaver rhoeas	Plant associated	China	No		
Embarria clematidis	2134052	PU	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Biodegradation of polyester polyurethane by Embarria clematidis. Frontiers in Microbiology, 13, 874842.	Esterase			No			2022.0	Clear zone;FTIR;GCMS;CO2	Impranil		No	No	Culture collection	Culture collection	Thailand	No		
Pseudophaeosphaeria rubi	1911196	PU	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Biodegradation of polyester polyurethane by Embarria clematidis. Frontiers in Microbiology, 13, 874842.				No			2022.0	Clear zone	Impranil		No	No	Culture collection	Culture collection	Thailand	No		
Ophiosimulans tanaceti	1890457	PU	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Biodegradation of polyester polyurethane by Embarria clematidis. Frontiers in Microbiology, 13, 874842.				No			2022.0	Clear zone	Impranil		No	No	Culture collection	Culture collection	Thailand	No		
Murilentithecium clematidis	1573945	PU	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Biodegradation of polyester polyurethane by Embarria clematidis. Frontiers in Microbiology, 13, 874842.				No			2022.0	Clear zone	Impranil		No	No	Culture collection	Culture collection	Thailand	No		
Roussoella scabrispora	1538321	PU	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Biodegradation of polyester polyurethane by Embarria clematidis. Frontiers in Microbiology, 13, 874842.				No			2022.0	Clear zone	Impranil		No	No	Culture collection	Culture collection	Thailand	No		
Sclerostagonospora lathyri	2134017	PU	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Biodegradation of polyester polyurethane by Embarria clematidis. Frontiers in Microbiology, 13, 874842.				No			2022.0	Clear zone	Impranil		No	No	Culture collection	Culture collection	Thailand	No		
Pseudomassariosphaeria bromicola	1764975	PU	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Biodegradation of polyester polyurethane by Embarria clematidis. Frontiers in Microbiology, 13, 874842.				No			2022.0	Clear zone	Impranil		No	No	Culture collection	Culture collection	Thailand	No		
Nodulosphaeria multiseptata	2024370	PU	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Biodegradation of polyester polyurethane by Embarria clematidis. Frontiers in Microbiology, 13, 874842.				No			2022.0	Clear zone	Impranil		No	No	Culture collection	Culture collection	Thailand	No		
Vagicola chlamydospora	1842666	PU	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Biodegradation of polyester polyurethane by Embarria clematidis. Frontiers in Microbiology, 13, 874842.				No			2022.0	Clear zone	Impranil		No	No	Culture collection	Culture collection	Thailand	No		
Halobyssothecium obiones	2203068	PU	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Biodegradation of polyester polyurethane by Embarria clematidis. Frontiers in Microbiology, 13, 874842.				No			2022.0	Clear zone	Impranil		No	No	Culture collection	Culture collection	Thailand	No		
Colletotrichum fructicola	690256	PU	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Biodegradation of polyester polyurethane by Embarria clematidis. Frontiers in Microbiology, 13, 874842.				No			2022.0	Clear zone	Impranil		No	No	Culture collection	Culture collection	Thailand	No		
Aspergillus niger	5061	PU	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Biodegradation of polyester polyurethane by Embarria clematidis. Frontiers in Microbiology, 13, 874842.	Esterase			No			2022.0	Clear zone;GCMS;CO2	Impranil		No	No			Thailand	No		
Meyerozyma guilliermondii	4929	PE	Lou, H., Fu, R., Long, T., Fan, B., Guo, C., Li, L., Zhang, J., & Zhang, G. (2022). Biodegradation of polyethylene by Meyerozyma guilliermondii and Serratia marcescens isolated from the gut of waxworms (larvae of Plodia interpunctella). Science of The Total Environment, 853, 158604.				No			2022.0	WCA;FTIR;SEM;GPC	PE film	SINOPEC Beijing Yanshan Company	No	No	Waxworm gut	Animal associated	China	No		
Serratia marcescens	615	PE	Lou, H., Fu, R., Long, T., Fan, B., Guo, C., Li, L., Zhang, J., & Zhang, G. (2022). Biodegradation of polyethylene by Meyerozyma guilliermondii and Serratia marcescens isolated from the gut of waxworms (larvae of Plodia interpunctella). Science of The Total Environment, 853, 158604.				No			2022.0	WCA;FTIR;SEM;GPC	PE film	SINOPEC Beijing Yanshan Company	No	No	Waxworm gut	Animal associated	China	No		
Gordonia sp.	84139	PS	Liu, R., Zhao, S., Zhang, B., Li, G., Fu, X., Yan, P., & Shao, Z. (2023). Biodegradation of polystyrene (PS) by marine bacteria in mangrove ecosystem. Journal of Hazardous Materials, 442, 130056.				No			2022.0	Weight loss;SEM;WCA;ATR-FTIR	 PS film	Sigma	Yes	No	Waste in soil	Near mangroves	China	No		
Gordonia sp.	84139	PS	Liu, R., Zhao, S., Zhang, B., Li, G., Fu, X., Yan, P., & Shao, Z. (2023). Biodegradation of polystyrene (PS) by marine bacteria in mangrove ecosystem. Journal of Hazardous Materials, 442, 130056.				No			2022.0	Weight loss;SEM;WCA;ATR-FTIR	 PS film	Sigma	Yes	No	Waste in soil	Near mangroves	China	No		
Gordonia sp.	84139	PS	Liu, R., Zhao, S., Zhang, B., Li, G., Fu, X., Yan, P., & Shao, Z. (2023). Biodegradation of polystyrene (PS) by marine bacteria in mangrove ecosystem. Journal of Hazardous Materials, 442, 130056.				No			2022.0	Weight loss;SEM;WCA;ATR-FTIR	 PS film	Sigma	Yes	No	Waste in soil	Near mangroves	China	No		
Novosphingobium sp.	1874826	PS	Liu, R., Zhao, S., Zhang, B., Li, G., Fu, X., Yan, P., & Shao, Z. (2023). Biodegradation of polystyrene (PS) by marine bacteria in mangrove ecosystem. Journal of Hazardous Materials, 442, 130056.				No			2022.0	Weight loss;SEM;WCA;ATR-FTIR	 PS film	Sigma	Yes	No	Waste in soil	Near mangroves	China	No		
Pseudomonas sp.	306	PS	Arunrattiyakorn, P., Ponprateep, S., Kaennonsang, N., Charapok, Y., Punphuet, Y., Krajangsang, S., ... & Limtrakul, A. (2022). Biodegradation of polystyrene by three bacterial strains isolated from the gut of Superworms (Zophobas atratus larvae). Journal of Applied Microbiology, 132(4), 2823-2831.				No			2022.0	SEM;FTIR;WCA	The Styrofoam (expanded polystyrene foam) feedstock was prepared by breaking down the commercial Styrofoam	A.T. Con Insulation	No	No	Waxworm gut	Animal associated	Thailand	No		
Bacillus sp.	1409	PS	Arunrattiyakorn, P., Ponprateep, S., Kaennonsang, N., Charapok, Y., Punphuet, Y., Krajangsang, S., ... & Limtrakul, A. (2022). Biodegradation of polystyrene by three bacterial strains isolated from the gut of Superworms (Zophobas atratus larvae). Journal of Applied Microbiology, 132(4), 2823-2831.				No			2022.0	SEM;FTIR;WCA	The Styrofoam (expanded polystyrene foam) feedstock was prepared by breaking down the commercial Styrofoam	A.T. Con Insulation	No	No	Waxworm gut	Animal associated	Thailand	No		
Brevibacterium sp.	1701	PS	Arunrattiyakorn, P., Ponprateep, S., Kaennonsang, N., Charapok, Y., Punphuet, Y., Krajangsang, S., ... & Limtrakul, A. (2022). Biodegradation of polystyrene by three bacterial strains isolated from the gut of Superworms (Zophobas atratus larvae). Journal of Applied Microbiology, 132(4), 2823-2831.				No			2022.0	SEM;FTIR;WCA	The Styrofoam (expanded polystyrene foam) feedstock was prepared by breaking down the commercial Styrofoam	A.T. Con Insulation	No	No	Waxworm gut	Animal associated	Thailand	No		
Xanthomonas sp.	29446	PU	Kim, J. H., Choi, S. H., Park, M. G., Park, D. H., Son, K. H., & Park, H. Y. (2022). Biodegradation of polyurethane by Japanese carpenter bee gut-associated symbionts Xanthomonas sp. HY-71, and its potential application on bioconversion. Environmental Technology & Innovation, 28, 102822.				No			2022.0	Clear zone;weight loss;SEM;FTIR	A commercial water polyacrylic urethane acryl PU-Siegel (Düfa, Bad Kreuznach, Germany) containing polyacrylic urethane and the xenobiotic additives benzisothiazolinone, methylisothiazolinone, and methylchloroisothiazolinone was used to evaluate the biodegradation of PU by the isolated strain. PS and PU based foams were also used	Düfa, KPX Chemical Co. (foams)	No	No	Bee gut	Animal associated	Thailand	No		
Xanthomonas sp.	29446	PU	Kim, J. H., Choi, S. H., Park, M. G., Park, D. H., Son, K. H., & Park, H. Y. (2022). Biodegradation of polyurethane by Japanese carpenter bee gut-associated symbionts Xanthomonas sp. HY-71, and its potential application on bioconversion. Environmental Technology & Innovation, 28, 102822.				No			2022.0	Clear zone;weight loss;SEM;FTIR	A commercial water polyacrylic urethane acryl PU-Siegel (Düfa, Bad Kreuznach, Germany) containing polyacrylic urethane and the xenobiotic additives benzisothiazolinone, methylisothiazolinone, and methylchloroisothiazolinone was used to evaluate the biodegradation of PU by the isolated strain. PS and PU based foams were also used	Düfa, KPX Chemical Co. (foams)	No	No	Bee gut	Animal associated	Thailand	No		
Alteromonas sp.	232	PU	Gunawan, N. R., Tessman, M., Zhen, D., Johnson, L., Evans, P., Clements, S. M., Pomeroy, R. S., Burkart, M. D., Simkovsky, R., & Mayfield, S. P. (2022). Biodegradation of renewable polyurethane foams in marine environments occurs through depolymerization by marine microorganisms. Science of The Total Environment, 850, 158761.				No			2022.0	SEM;FTIR;GCMS	PU foam composed of 4,4′-methylene diphenyl diisocyanate (MDI) and linear polyester polyols generated from two aliphatic diols and an aliphatic diacid was prepared in a 2 cm × 20 cm × 20 cm mold, as previously re- ported		No	No	Water/marine sediment	Marine	USA	No		
Pseudomonas sp.	306	PU	Gunawan, N. R., Tessman, M., Zhen, D., Johnson, L., Evans, P., Clements, S. M., Pomeroy, R. S., Burkart, M. D., Simkovsky, R., & Mayfield, S. P. (2022). Biodegradation of renewable polyurethane foams in marine environments occurs through depolymerization by marine microorganisms. Science of The Total Environment, 850, 158761.				No			2022.0	SEM;FTIR;GCMS	PU foam composed of 4,4′-methylene diphenyl diisocyanate (MDI) and linear polyester polyols generated from two aliphatic diols and an aliphatic diacid was prepared in a 2 cm × 20 cm × 20 cm mold, as previously re- ported		No	No	Water/marine sediment	Marine	USA	No		
Alteromonas sp.	232	PU	Gunawan, N. R., Tessman, M., Zhen, D., Johnson, L., Evans, P., Clements, S. M., Pomeroy, R. S., Burkart, M. D., Simkovsky, R., & Mayfield, S. P. (2022). Biodegradation of renewable polyurethane foams in marine environments occurs through depolymerization by marine microorganisms. Science of The Total Environment, 850, 158761.				No			2022.0	SEM;FTIR;GCMS	PU foam composed of 4,4′-methylene diphenyl diisocyanate (MDI) and linear polyester polyols generated from two aliphatic diols and an aliphatic diacid was prepared in a 2 cm × 20 cm × 20 cm mold, as previously re- ported		No	No	Water/marine sediment	Marine	USA	No		
Penicillium chrysogenum	5076	PU	Gunawan, N. R., Tessman, M., Zhen, D., Johnson, L., Evans, P., Clements, S. M., Pomeroy, R. S., Burkart, M. D., Simkovsky, R., & Mayfield, S. P. (2022). Biodegradation of renewable polyurethane foams in marine environments occurs through depolymerization by marine microorganisms. Science of The Total Environment, 850, 158761.				No			2022.0	SEM;FTIR;GCMS	PU foam composed of 4,4′-methylene diphenyl diisocyanate (MDI) and linear polyester polyols generated from two aliphatic diols and an aliphatic diacid was prepared in a 2 cm × 20 cm × 20 cm mold, as previously re- ported		No	No	Water/marine sediment	Marine	USA	No		
Alcaligenes faecalis	511	LLDPE	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Clear zone;weight loss;CO2;FTIR	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Alcaligenes faecalis	511	HDPE	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Weight loss;CO2;FTIR;SEM	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Alcaligenes faecalis	511	PES	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Clear zone;weight loss;CO2;FTIR	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Bacillus sp. SB14	403160	LLDPE	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Clear zone;weight loss;CO2;FTIR;SEM	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Bacillus sp. SB14	403160	PES	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Clear zone;weight loss;CO2;FTIR	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Bacillus cereus	1396	LLDPE	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Clear zone;weight loss;CO2;SEM	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Bacillus cereus	1396	HDPE	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Clear zone;weight loss;CO2	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Bacillus cereus	1396	PES	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Weight loss;CO2	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Bacillus sp. SC9	361480	HDPE	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Clear zone;weight loss;CO2	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Bacillus sp. SC9	361480	LLDPE	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Clear zone;weight loss;CO2;SEM	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Bacillus sp. SC9	361480	PES	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Weight loss;CO2	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Streptococcus sp.	1306	LLDPE	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Clear zone;weight loss;CO2;FTIR	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Streptococcus sp.	1306	HDPE	Tareen, A., Saeed, S., Iqbal, A., Batool, R., & Jamil, N. (2022). Biodeterioration of microplastics: A promising step towards plastics waste management. Polymers, 14(11), 2275.				No			2022.0	Clear zone;weight loss;CO2;FTIR;SEM	Plastic beads and powders	Mehran Plastic Industries Pvt Limited	No	No	Soil	Garbage dump	Pakistan	No		
Priestia aryabhattai	412384	PET	Dhaka, V., Singh, S., Ramamurthy, P. C., Samuel, J., Swamy Sunil Kumar Naik, T., Khasnabis, S., Prasad, R., & Singh, J. (2022). Biological degradation of polyethylene terephthalate by rhizobacteria. Environmental Science and Pollution Research, 1-10.				No			2022.0	Weight loss;HPLC;SEM;FTIR-ATR	PET granules and bottles	Sigma Aldrich (grandules)	No	No	Rhizosphere soil	Garbage dump	India	No		
Bacillus pseudomycoides	64104	PET	Dhaka, V., Singh, S., Ramamurthy, P. C., Samuel, J., Swamy Sunil Kumar Naik, T., Khasnabis, S., Prasad, R., & Singh, J. (2022). Biological degradation of polyethylene terephthalate by rhizobacteria. Environmental Science and Pollution Research, 1-10.				No			2022.0	Weight loss;HPLC;SEM;FTIR-ATR	PET granules and bottles	Sigma Aldrich (grandules)	No	No	Rhizosphere soil	Garbage dump	India	No		
Bacillus pumilus	1408	PET	Dhaka, V., Singh, S., Ramamurthy, P. C., Samuel, J., Swamy Sunil Kumar Naik, T., Khasnabis, S., Prasad, R., & Singh, J. (2022). Biological degradation of polyethylene terephthalate by rhizobacteria. Environmental Science and Pollution Research, 1-10.				No			2022.0	Weight loss;HPLC;SEM;FTIR-ATR	PET granules and bottles	Sigma Aldrich (grandules)	No	No	Rhizosphere soil	Garbage dump	India	No		
Lihuaxuella thermophila	1173111	PHB	Thomas, G. M., Quirk, S., Huard, D. J., & Lieberman, R. L. (2022). Bioplastic degradation by a polyhydroxybutyrate depolymerase from a thermophilic soil bacterium. Protein Science, 31(11), e4470.	PHB depolymerase	00215	00215 | PHB depolymerase | Lihuaxuella thermophila | PHB PHA PHBH PHBVH PLA PCL	Yes	WP_089972404.1	MFLLALVTSLIGTGMFTTPVHAAGQFIRDTAPDGRVYKLYIPSGYNGSTPLPLVVMLHGCTQNPDDFAAGTEMNVYAEQNNFLVAYPEQPSSANLNKCWNWFDSNHQSRGRGEPASIAGVVEDVKRNYSVDSRRVYAAGLSAGGAMSVIMGATYPDVFAAIGVGSGLEYKAATSMTSAYMAMINGGPDPVQQGNLAYQAMGSHARVVPVIVFHGTSDYTVYPVNGHQVISQWAQTNDRAGDGVDNNHIDDQADVTMNGSVPNGRTYTRYLYKDQNGNVVMEKIMVNGMGHAWSGGSTAGTYTDPAGPEASSMMWSFFVNHPK	2022.0	Turbidity;CD	Granules	Millipore-Sigma	No	Yes				Yes		
Lihuaxuella thermophila	1173111	PHA	Thomas, G. M., Quirk, S., Huard, D. J., & Lieberman, R. L. (2022). Bioplastic degradation by a polyhydroxybutyrate depolymerase from a thermophilic soil bacterium. Protein Science, 31(11), e4470.	PHB depolymerase	00215	00215 | PHB depolymerase | Lihuaxuella thermophila | PHB PHA PHBH PHBVH PLA PCL	Yes	WP_089972404.1	MFLLALVTSLIGTGMFTTPVHAAGQFIRDTAPDGRVYKLYIPSGYNGSTPLPLVVMLHGCTQNPDDFAAGTEMNVYAEQNNFLVAYPEQPSSANLNKCWNWFDSNHQSRGRGEPASIAGVVEDVKRNYSVDSRRVYAAGLSAGGAMSVIMGATYPDVFAAIGVGSGLEYKAATSMTSAYMAMINGGPDPVQQGNLAYQAMGSHARVVPVIVFHGTSDYTVYPVNGHQVISQWAQTNDRAGDGVDNNHIDDQADVTMNGSVPNGRTYTRYLYKDQNGNVVMEKIMVNGMGHAWSGGSTAGTYTDPAGPEASSMMWSFFVNHPK	2022.0	Turbidity;CD	Granules	Millipore-Sigma	No	Yes				Yes		
Lihuaxuella thermophila	1173111	PHBH	Thomas, G. M., Quirk, S., Huard, D. J., & Lieberman, R. L. (2022). Bioplastic degradation by a polyhydroxybutyrate depolymerase from a thermophilic soil bacterium. Protein Science, 31(11), e4470.	PHB depolymerase	00215	00215 | PHB depolymerase | Lihuaxuella thermophila | PHB PHA PHBH PHBVH PLA PCL	Yes	WP_089972404.1	MFLLALVTSLIGTGMFTTPVHAAGQFIRDTAPDGRVYKLYIPSGYNGSTPLPLVVMLHGCTQNPDDFAAGTEMNVYAEQNNFLVAYPEQPSSANLNKCWNWFDSNHQSRGRGEPASIAGVVEDVKRNYSVDSRRVYAAGLSAGGAMSVIMGATYPDVFAAIGVGSGLEYKAATSMTSAYMAMINGGPDPVQQGNLAYQAMGSHARVVPVIVFHGTSDYTVYPVNGHQVISQWAQTNDRAGDGVDNNHIDDQADVTMNGSVPNGRTYTRYLYKDQNGNVVMEKIMVNGMGHAWSGGSTAGTYTDPAGPEASSMMWSFFVNHPK	2022.0	Turbidity;CD	Granules	Millipore-Sigma	No	Yes				Yes		
Lihuaxuella thermophila	1173111	PHBVH	Thomas, G. M., Quirk, S., Huard, D. J., & Lieberman, R. L. (2022). Bioplastic degradation by a polyhydroxybutyrate depolymerase from a thermophilic soil bacterium. Protein Science, 31(11), e4470.	PHB depolymerase	00215	00215 | PHB depolymerase | Lihuaxuella thermophila | PHB PHA PHBH PHBVH PLA PCL	Yes	WP_089972404.1	MFLLALVTSLIGTGMFTTPVHAAGQFIRDTAPDGRVYKLYIPSGYNGSTPLPLVVMLHGCTQNPDDFAAGTEMNVYAEQNNFLVAYPEQPSSANLNKCWNWFDSNHQSRGRGEPASIAGVVEDVKRNYSVDSRRVYAAGLSAGGAMSVIMGATYPDVFAAIGVGSGLEYKAATSMTSAYMAMINGGPDPVQQGNLAYQAMGSHARVVPVIVFHGTSDYTVYPVNGHQVISQWAQTNDRAGDGVDNNHIDDQADVTMNGSVPNGRTYTRYLYKDQNGNVVMEKIMVNGMGHAWSGGSTAGTYTDPAGPEASSMMWSFFVNHPK	2022.0	Turbidity;CD	Granules	Millipore-Sigma	No	Yes				Yes		
Lihuaxuella thermophila	1173111	PLA	Thomas, G. M., Quirk, S., Huard, D. J., & Lieberman, R. L. (2022). Bioplastic degradation by a polyhydroxybutyrate depolymerase from a thermophilic soil bacterium. Protein Science, 31(11), e4470.	PHB depolymerase	00215	00215 | PHB depolymerase | Lihuaxuella thermophila | PHB PHA PHBH PHBVH PLA PCL	Yes	WP_089972404.1	MFLLALVTSLIGTGMFTTPVHAAGQFIRDTAPDGRVYKLYIPSGYNGSTPLPLVVMLHGCTQNPDDFAAGTEMNVYAEQNNFLVAYPEQPSSANLNKCWNWFDSNHQSRGRGEPASIAGVVEDVKRNYSVDSRRVYAAGLSAGGAMSVIMGATYPDVFAAIGVGSGLEYKAATSMTSAYMAMINGGPDPVQQGNLAYQAMGSHARVVPVIVFHGTSDYTVYPVNGHQVISQWAQTNDRAGDGVDNNHIDDQADVTMNGSVPNGRTYTRYLYKDQNGNVVMEKIMVNGMGHAWSGGSTAGTYTDPAGPEASSMMWSFFVNHPK	2022.0	Turbidity;CD	Granules	Millipore-Sigma	No	Yes				Yes		
Lihuaxuella thermophila	1173111	PCL	Thomas, G. M., Quirk, S., Huard, D. J., & Lieberman, R. L. (2022). Bioplastic degradation by a polyhydroxybutyrate depolymerase from a thermophilic soil bacterium. Protein Science, 31(11), e4470.	PHB depolymerase	00215	00215 | PHB depolymerase | Lihuaxuella thermophila | PHB PHA PHBH PHBVH PLA PCL	Yes	WP_089972404.1	MFLLALVTSLIGTGMFTTPVHAAGQFIRDTAPDGRVYKLYIPSGYNGSTPLPLVVMLHGCTQNPDDFAAGTEMNVYAEQNNFLVAYPEQPSSANLNKCWNWFDSNHQSRGRGEPASIAGVVEDVKRNYSVDSRRVYAAGLSAGGAMSVIMGATYPDVFAAIGVGSGLEYKAATSMTSAYMAMINGGPDPVQQGNLAYQAMGSHARVVPVIVFHGTSDYTVYPVNGHQVISQWAQTNDRAGDGVDNNHIDDQADVTMNGSVPNGRTYTRYLYKDQNGNVVMEKIMVNGMGHAWSGGSTAGTYTDPAGPEASSMMWSFFVNHPK	2022.0	Turbidity;CD	Granules	Millipore-Sigma	No	Yes				Yes		
Marinactinospora thermotolerans	531310	PET	Liu, Y., Liu, C., Liu, H., Zeng, Q., Tian, X., Long, L., & Yang, J. (2022). Catalytic features and thermal adaptation mechanisms of a deep sea bacterial cutinase-type poly (ethylene terephthalate) hydrolase. Frontiers in Bioengineering and Biotechnology, 10, 865787.	Cutinase	00216	00216 | Cutinase | Marinactinospora thermotolerans | PET	Yes	SJZ42839	MLTHSISPEETDGGRRTPLSRMSRLAARVGVTLSLAAGLTAGVTAPAHASNPYERGPAPTESSVTAVRGYFDTDTDTVSSLVSGFGGGTIYYPTDTSEGTFGGVVIAPGYTASQSSMAWMGHRIASQGFVVFTIDTITRYDQPDSRGRQIEAALDYLVEDSDVADRVDGNRLAVMGHSMGGGGTLAAAENRPELRAAIPLTPWHLQKNWSDVEVPTMIIGAENDTVASVRTHSIPFYESLDEDLERAYLELDGASHFAPNISNTVIAKYSISWLKRFVDEDERYEQFLCPPPDTGLFSDFSDYRDSCPHTT	2022.0	HPLC	High crystallinity PET microparticles			No				Yes		
Bacillus amyloliquefaciens	1390	PLA	Yu, J., Kim, P. D., Jang, Y., Kim, S. K., Han, J., & Min, J. (2022). Comparison of polylactic acid biodegradation ability of Brevibacillus brevis and Bacillus amyloliquefaciens and promotion of PLA biodegradation by soytone. Biodegradation, 33(5), 477-487.				No			2022.0	Weight loss;GPC;FTIR;DSC	Polylactic acid films were formed by solvent casting method. 0.5 g PLA was dissolved in 10 mL chloro- form. The solution was stirred at room temperature for 24 h and transferred onto a silicon mold with a size of 8×8 cm. Then, it was dried overnight in a fume hood. After drying, the PLA films were dried in a vacuum oven at 40 °C for 2 days. The PLA films were cut into 1 × 3 cm for the biodegradation test. The thickness of the film was approximately 100 μm.	NatureWorks	No	No	Culture collection	Culture collection	Korea	No		
Brevibacillus brevis	1393	PLA	Yu, J., Kim, P. D., Jang, Y., Kim, S. K., Han, J., & Min, J. (2022). Comparison of polylactic acid biodegradation ability of Brevibacillus brevis and Bacillus amyloliquefaciens and promotion of PLA biodegradation by soytone. Biodegradation, 33(5), 477-487.				No			2022.0	Weight loss;GPC;FTIR;DSC	Polylactic acid films were formed by solvent casting method. 0.5 g PLA was dissolved in 10 mL chloro- form. The solution was stirred at room temperature for 24 h and transferred onto a silicon mold with a size of 8×8 cm. Then, it was dried overnight in a fume hood. After drying, the PLA films were dried in a vacuum oven at 40 °C for 2 days. The PLA films were cut into 1 × 3 cm for the biodegradation test. The thickness of the film was approximately 100 μm.	NatureWorks	No	No	Culture collection	Culture collection	Korea	No		
Bacillus cereus	1396	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Sinomonas sp.	1914986	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Sinomonas sp.	1914986	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Cellulosimicrobium sp.	1871614	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Streptomyces werraensis	68284	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Streptomyces rochei	1928	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Aspergillus terreus	33178	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Talaromyces islandicus	28573	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Aspergillus sp.	5065	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Aspergillus sp.	5065	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Eupenicillium rubidurum	70093	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Phoma sp.	1707701	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Neosartorya fischeri	36630	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Aspergillus terreus	33178	PE	Nakei, M. D., Misinzo, G., Tindwa, H., & Semu, E. (2022). Degradation of polyethylene plastic bags and bottles using microorganisms isolated from soils of Morogoro, Tanzania. Frontiers in Microbiology, 13, 1077588.				No			2022.0	Clear zone	The PE powder was obtained from ground plastics sieved through a 0.6-mm sieve. After sieving, 1 g of PE powder was added to 1,000 ml (0.1% w/v) of this mineral salt medium and mixed for 1 h at 120 rpm using a shaker. The pH of the medium was adjusted to 7.0 ± 0.2 and autoclaved at 1.05 Kg/cm2 at 121◦C for 15 min. The medium was left to cool to 50◦C and dispensed into Petri dishes until the solidification of the media			No	Soil	Soil	Tanzania	No		
Acinetobacter sp.	472	LDPE	Zhang, H., Lu, Y., Wu, H., Liu, Q., & Sun, W. (2023). Effect of an Acinetobacter pittobacter on low-density polyethylene. Environmental Science and Pollution Research, 30(4), 10495-10504.				No			2023.0	Weight loss;SEM;AFM;XPS;FTIR;WCA;tensile strength	PE powder and film	Lanzhou Jianxing Trading Co., Ltd (powder), Lanzhou Petrochemical Co. (film)		No	Wastewater sediment	Recycling plant	No	No		
Penicillium chrysogenum	5076	LDPE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Rhizopus nigricans	4846	LDPE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Chaetomium murorum	1934362	LDPE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Memnoniella echinata	80383	LDPE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Aspergillus fumigatus	746128	LDPE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Stachybotrys chartarum	74722	LDPE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Aspergillus niger	5061	LDPE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Chaetomium globosum	38033	LDPE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Aspergillus flavus	5059	LDPE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Fusarium oxysporum	5507	LDPE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Penicillium chrysogenum	5076	PE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Rhizopus nigricans	4846	PE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Chaetomium murorum	1934362	PE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Memnoniella echinata	80383	PE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Aspergillus fumigatus	746128	PE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Stachybotrys chartarum	74722	PE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Aspergillus niger	5061	PE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Chaetomium globosum	38033	PE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Aspergillus flavus	5059	PE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Fusarium oxysporum	5507	PE	Saxena, A., Jain, S., & Pareek, A. (2022). Estimation of possible biodegradation of polythene by fungal isolates growing on polythene debris. Pollution, 8(2), 567-577.				No			2022.0	Weight loss;SEM	Plastic segments			No	Decaying sites near water bodies	Dumping site	India	No		
Pseudomonas capeferrum	1495066	PU	Puiggené, Ò., Espinosa, M. J. C., Schlosser, D., Thies, S., Jehmlich, N., Kappelmeyer, U., Schreiber, S., Wibberg, D., Kalinowski, J., Harms, H., Heipieper, H. J., & Eberlein, C. (2022). Extracellular degradation of a polyurethane oligomer involving outer membrane vesicles and further insights on the degradation of 2, 4-diaminotoluene in Pseudomonas capeferrum TDA1. Scientific Reports, 12(1), 2666.	Esterase			No			2022.0	LCMS	For growth assessement, 3 g/l PU oligomer (Sigma-Aldrich, dihydroxy-functional oligomer, aliphatic urethane of proprietary composition, average Mn~320 Dalton) or 2 mM 2,4-TDA or 2 mM 2,4-TDA+succinate were added34. 	Sigma-Aldrich	Yes	No	Soil	Dumping site	Germany	No		
Alternaria alternata	5599	PE	Gao, R., Liu, R., & Sun, C. (2022). A marine fungus Alternaria alternata FB1 efficiently degrades polyethylene. Journal of Hazardous Materials, 431, 128617.	Glutathione peroxidase			No			2022.0	SEM;FTIR;XRD;GPC;GCMS	Three kinds of PE plastic were used in this study, including com- mercial PE bags (additive-containing), type ET311350 PE plastic (0.25 mm in thickness; additive-free) and type ET311126 PE plastic (0.025 mm in thickness; additive-free), the latter two were purchased from the Good Fellow Company (UK). All PE films were treated with 75% ethanol and air-dried in a laminar-flow clean bench prior to use. 	Plastic bags sourced commercially, other plastics from Good Fellow Company (UK)		No	Plastic debris	Intertidal	China	No		
Alternaria alternata	5599	PE	Gao, R., Liu, R., & Sun, C. (2022). A marine fungus Alternaria alternata FB1 efficiently degrades polyethylene. Journal of Hazardous Materials, 431, 128617.	Laccase			No			2022.0	SEM;FTIR;XRD;GPC;GCMS	Three kinds of PE plastic were used in this study, including com- mercial PE bags (additive-containing), type ET311350 PE plastic (0.25 mm in thickness; additive-free) and type ET311126 PE plastic (0.025 mm in thickness; additive-free), the latter two were purchased from the Good Fellow Company (UK). All PE films were treated with 75% ethanol and air-dried in a laminar-flow clean bench prior to use. 	Plastic bags sourced commercially, other plastics from Good Fellow Company (UK)		No	Plastic debris	Intertidal	China	No		
Acinetobacter seifertii	1530123	PCL	Budkum, J., Thammasittirong, S. N. R., & Thammasittirong, A. (2022). High poly ε-caprolactone biodegradation activity by a new Acinetobacter seifertii isolate. Folia Microbiologica, 67(4), 659-669.	PCL depolymerase			No			2022.0	Clear zone;weight loss;spectrophotometry	PCL in agar medium and PCL films	Sigma Aldrich	Yes	No	Soil	Garbage dump	Thailand	No		
Geomyces sp.	1715258	PBS	Urbanek, A. K., Arroyo, M., de la Mata, I., & Mirończuk, A. M. (2022). Identification of novel extracellular putative chitinase and hydrolase from Geomyces sp. B10I with the biodegradation activity towards polyesters. AMB Express, 12(1), 1-11.	Hydrolase	00217	00217 | Hydrolase | Geomyces sp. | PBS PBSA PCL	Yes	KFY49210.1	MSSENIFQKALSKDAPPSMIASRPDHPVKRLGIAPQEGRPISTNKFYANFFLGGQNHATWTHPYSMLWSKGGGSSKSWGLAVTHIEAKQQVFGPDPKASPAEYFVNPGGIQHVILSAAELEKSTVLTTDNLTSSSVNVNILASAGGKPAITFPLVQGMGFITGIYNESTPILQSGVFFRSITQAKTAPKEGVIKYTIVLEDSSKWLVYAHSTSGQPLELSIANNSLIKATSKFQGTLQIAKSPIDAAEAVYDAASGAYATGSALSGTAKGPAGTYTMTFSKGGLKDATLVMFALPHLVESFSSTTKAAATEVKLQTTTKGVATGVVADSWTMEEKDMPVGMGFAPWSPSLGNIGTLSPSAISSIQKVAASDLKQDMMAQSNGDSFYFSGKALAKFAQIIYASKDLVKDEALAKDGLTKLKAAFEVWTTNKNKYPLVYEKAWGGIVSTGGYVTGDSGTDFGNTNYNDHHFHFAYFILAASYIGYLDPGWLASHKDYINTMVRDTANPSSEDPYFPVNRGFDWYNGHSWAKGLFESADGKDQESSAEDACFAYSLKMWGKTIGDANLEARGNLQLSVVARSISKYFLYTSDNTVQPKNFIGNKVSGILFENKIHHTTYFGANIEYIQGIHMIPLLPSSSLTRTKKFVQEEWDTFFSDDRAKKVEGGWRGILFANLALIDPKQSYSFFSQESFDNAWLDGGASRTWYMAQAAGLGGA	2022.0	Clear zone;turbidity;mass spec	Wells were aseptically cut in solid MM medium supple- mented with 0.1% bioplastic emulsions. 	Showa Denko K.K. (Japan)	No	No	Culture collection	Culture collection	Poland	No		
Geomyces sp.	1715258	PBS	Urbanek, A. K., Arroyo, M., de la Mata, I., & Mirończuk, A. M. (2022). Identification of novel extracellular putative chitinase and hydrolase from Geomyces sp. B10I with the biodegradation activity towards polyesters. AMB Express, 12(1), 1-11.	Chitinase	00218	00218 | Chitinase | Geomyces sp. | PBS PBSA PCL	Yes	KFY57494.1	MTIGGSFKAAWAAVTGWRGKKTEGAAEGKADAAAAAPAAVAYKNAGYFVNWAIYGRNFQPAQLQAAQLTHVLYAFANLRPDGSVFLSDTYADLEKHYPEDSWNEPGTNLFGCAKQIYLLKKKHRSMKVLLSIGGWTYSSNFAAAASTPTTRALFVSTAVEIVKDLGFDGLDIDWEYPTNETEAKNYVLLLKACREGLDAYANANAKGYKFQLTIAAPAGPDKYNILKMKEMDAYLDAWHLMAYDYAGSWSTVAGHDANLYPSKTVPEGTPYSTDKAVVDYIKAGVPAAKIIIGVPLYGRSFQATEGMGKKFSGIGEGSWENGVWDYKVLPKAGATVKIDNDAKARYSYDPATKELISFDTVEDAKTKAEYVKTKGLGGAMYWETSADRAGDKSLIGTFAGSFATLDKSQNLLSYPKSKYANMVAGMPS	2022.0	Clear zone;turbidity;mass spec	Wells were aseptically cut in solid MM medium supple- mented with 0.1% bioplastic emulsions. 	Showa Denko K.K. (Japan)	No	No	Culture collection	Culture collection	Poland	No		
Actinomucor elegans	64647	PHB-Blend	Carboué, Q., Fadlallah, S., Werghi, Y., Longé, L., Gallos, A., Allais, F., & Lopez, M. (2022). Impact of Bis-O-dihydroferuloyl-1, 4-butanediol Content on the Chemical, Enzymatic and Fungal Degradation Processes of Poly (3-hydroxybutyrate). Polymers, 14(8), 1564.				No			2022.0	FTIR;DSC;NMR	The PHB films were formed using solvent casting: specimens of PHB/BDF blends were dissolved in chloroform (VWR Chemicals BDH©, Radnor, PA, USA) and the solution was then poured into stainless steel rectangular molds (11 × 6 cm). The solvent was then slowly evaporated under the fume hood at room temperature to obtain uniform films of around 0.1 μm thickness as measured by an electronic digital caliper.	BIOMER	No	No	Soil	Soil	France	No		
Rhizopus oryzae	64495	LDPE	Seenivasagan, R., Karthika, A., & Poonkuzhali, K. (2022). In Vitro and In Silico Study of the Efficacy of Fungi in Low-Density Polyethylene Degradation in a Disposal Paper Cup. Water, Air, & Soil Pollution, 233(3), 77.	Chitin deacetylase	00219	00219 | Chitin deacetylase | Rhizopus oryzae | LDPE	Yes	AAP57213	MYIKTSAIAIALLQVACFAEAAKKTSKSSKSSKLDKPQDYWRNFKSLVDPNNITIADIPQTTSTNPSDECKWYEPPSNFVYNTKEWPNLWEIATSNGMTKTSEFQALNKSIDWTKAPKIPVRKAGSDGGLDMTSYSDSDPDCWWSSSTCTKPKHKDINEDIYACPEPETWGLTYDDGPNCSHNAFYDYLEQNKIKASMFYIGSNVVNWPYGAQRGVKAGHHIADHTWSHQLMTTLTNDEVLAELYYTQKAIKMVTGVTPLHWRPAFGDVDDRVRWIATQLYLTTVLWNLDTDDWAAGSSKTLDEVKATYDSYVEMGSNGTFATSGQIVLTHEIDNTTMSLAMEYLPKIKAAYKNVVDVATCMNITYPYQEHNVSFAPFGSAADESTATFTDATASSASASAAGTSDEPGTTVIPLAANKAQIASAGIQVNPNSLVFAAFVAAAYFF	2022.0	Weight loss;FTIR;SEM	A paper cup; The LDPE was collected, washed with distilled water and ethanol, and dried overnight at 37 °C		No	No	Soil	Dumping site	India	No		
Sarcina aurantiaca	64495	PET	Maheswaran, B., Al-Ansari, M., Al-Humaid, L., Raj, J. S., Kim, W., Karmegam, N., & Rafi, K. M. (2023). In vivo degradation of polyethylene terephthalate using microbial isolates from plastic polluted environment. Chemosphere, 310, 136757.				No			2022.0	Weight loss;FTIR;SEM	PET plastic packaging		No	No	Sediment	River	India	No		
Bacillus subtilis	1423	PET	Maheswaran, B., Al-Ansari, M., Al-Humaid, L., Raj, J. S., Kim, W., Karmegam, N., & Rafi, K. M. (2023). In vivo degradation of polyethylene terephthalate using microbial isolates from plastic polluted environment. Chemosphere, 310, 136757.				No			2022.0	Weight loss;FTIR;SEM	PET plastic packaging		No	No	Sediment	River	India	No		
Aspergillus flavus	5059	PET	Maheswaran, B., Al-Ansari, M., Al-Humaid, L., Raj, J. S., Kim, W., Karmegam, N., & Rafi, K. M. (2023). In vivo degradation of polyethylene terephthalate using microbial isolates from plastic polluted environment. Chemosphere, 310, 136757.				No			2022.0	Weight loss;FTIR;SEM	PET plastic packaging		No	No	Sediment	River	India	No		
Aspergillus niger	5061	PET	Maheswaran, B., Al-Ansari, M., Al-Humaid, L., Raj, J. S., Kim, W., Karmegam, N., & Rafi, K. M. (2023). In vivo degradation of polyethylene terephthalate using microbial isolates from plastic polluted environment. Chemosphere, 310, 136757.				No			2022.0	Weight loss;FTIR;SEM	PET plastic packaging		No	No	Sediment	River	India	No		
Anoxybacillus flavithermus	33934	PE	Investigation of two different size microplastic degradation ability of thermophilic bacteria using polyethylene polymers				No			2022.0	FTIR;SEM	Commercial polyethylene (PE) powder with an average size of 50 μm (Aldrich-434272) and 150μm (Goodfellow-9002884) were used as plastic sources	Sigma Aldrich, Goodfellow	Yes	No	Soil	Hot spring	Turkey	No		
Bacillus firmus	1399	PE	Investigation of two different size microplastic degradation ability of thermophilic bacteria using polyethylene polymers				No			2022.0	FTIR;SEM	Commercial polyethylene (PE) powder with an average size of 50 μm (Aldrich-434272) and 150μm (Goodfellow-9002884) were used as plastic sources	Sigma Aldrich, Goodfellow	Yes	No	Soil	Hot spring	Turkey	No		
Anoxybacillus flavithermus	33934	PE	Özdemir, S., Akarsu, C., Acer, Ö., Fouillaud, M., Dufossé, L., & Dizge, N. (2022). Isolation of thermophilic bacteria and investigation of their microplastic degradation ability using polyethylene polymers. Microorganisms, 10(12), 2441.				No			2022.0	FTIR;SEM	Commercial polyethylene (PE) powder with an average size of 50 μm (Aldrich-434272) and 150μm (Goodfellow-9002884) were used as plastic sources	Sigma Aldrich, Goodfellow	Yes	Yes	Water/muddy soil	Hot spring	Turkey	No		
Anoxybacillus sp.	1872573	PE	Özdemir, S., Akarsu, C., Acer, Ö., Fouillaud, M., Dufossé, L., & Dizge, N. (2022). Isolation of thermophilic bacteria and investigation of their microplastic degradation ability using polyethylene polymers. Microorganisms, 10(12), 2441.				No			2022.0	FTIR;SEM	Commercial polyethylene (PE) powder with an average size of 50 μm (Aldrich-434272) and 150μm (Goodfellow-9002884) were used as plastic sources	Sigma Aldrich, Goodfellow	Yes	Yes	Water/muddy soil	Hot spring	Turkey	No		
Marinobacter sp.	50741	LDPE	Marine bacterial based enzymatic degradation of low-density polyethylene (LDPE) plastic	Esterase			No			2022.0	Weight loss;FE-SEM;AFM;ATR-FTIR;GCMS;tensile strength;TGA	LDPE film	Good Fellow	Yes	No	Plastic litter/seawater/sediment	Seawater	India	No		
Marinobacter sp.	50741	LDPE	Marine bacterial based enzymatic degradation of low-density polyethylene (LDPE) plastic	Esterase			No			2022.0	Weight loss;FE-SEM;AFM;ATR-FTIR;GCMS;tensile strength;TGA	LDPE film	Good Fellow	Yes	No	Plastic litter/seawater/sediment	Seawater	India	No		
Bacillus subtilis	1423	LDPE	Marine bacterial based enzymatic degradation of low-density polyethylene (LDPE) plastic	Esterase			No			2022.0	Weight loss;FE-SEM;AFM;ATR-FTIR;GCMS;tensile strength;TGA	LDPE film	Good Fellow	Yes	No	Plastic litter/seawater/sediment	Seawater	India	No		
Streptomyces gougerotti	1423	LDPE	Oliveira, J., Almeida, P. L., Sobral, R. G., Lourenço, N. D., & Gaudêncio, S. P. (2022). Marine-Derived Actinomycetes: Biodegradation of Plastics and Formation of PHA Bioplastics—A Circular Bioeconomy Approach. Marine Drugs, 20(12), 760.				No			2022.0	Clear zone;weight loss;FTIR;tensile strength	LDPE film			No	Marine sediment	Marine	Portugal	No		
Streptomyces gougerotti	1423	PS	Oliveira, J., Almeida, P. L., Sobral, R. G., Lourenço, N. D., & Gaudêncio, S. P. (2022). Marine-Derived Actinomycetes: Biodegradation of Plastics and Formation of PHA Bioplastics—A Circular Bioeconomy Approach. Marine Drugs, 20(12), 760.				No			2022.0	Clear zone;weight loss;FTIR;tensile strength	PS film			No	Marine sediment	Marine	Portugal	No		
Streptomyces gougerotti	1423	PLA	Oliveira, J., Almeida, P. L., Sobral, R. G., Lourenço, N. D., & Gaudêncio, S. P. (2022). Marine-Derived Actinomycetes: Biodegradation of Plastics and Formation of PHA Bioplastics—A Circular Bioeconomy Approach. Marine Drugs, 20(12), 760.				No			2022.0	Clear zone;weight loss;FTIR;tensile strength	PLA film			No	Marine sediment	Marine	Portugal	No		
Micromonospora matsumotoense	121616	LDPE	Oliveira, J., Almeida, P. L., Sobral, R. G., Lourenço, N. D., & Gaudêncio, S. P. (2022). Marine-Derived Actinomycetes: Biodegradation of Plastics and Formation of PHA Bioplastics—A Circular Bioeconomy Approach. Marine Drugs, 20(12), 760.				No			2022.0	Clear zone;weight loss;FTIR;tensile strength	LDPE film			No	Marine sediment	Marine	Portugal	No		
Micromonospora matsumotoense	121616	PS	Oliveira, J., Almeida, P. L., Sobral, R. G., Lourenço, N. D., & Gaudêncio, S. P. (2022). Marine-Derived Actinomycetes: Biodegradation of Plastics and Formation of PHA Bioplastics—A Circular Bioeconomy Approach. Marine Drugs, 20(12), 760.				No			2022.0	Clear zone;weight loss;FTIR;tensile strength	PS film			No	Marine sediment	Marine	Portugal	No		
Micromonospora matsumotoense	121616	PLA	Oliveira, J., Almeida, P. L., Sobral, R. G., Lourenço, N. D., & Gaudêncio, S. P. (2022). Marine-Derived Actinomycetes: Biodegradation of Plastics and Formation of PHA Bioplastics—A Circular Bioeconomy Approach. Marine Drugs, 20(12), 760.				No			2022.0	Clear zone;weight loss;FTIR;tensile strength	PLA film			No	Marine sediment	Marine	Portugal	No		
Nocardiopsis prasina	2015	LDPE	Oliveira, J., Almeida, P. L., Sobral, R. G., Lourenço, N. D., & Gaudêncio, S. P. (2022). Marine-Derived Actinomycetes: Biodegradation of Plastics and Formation of PHA Bioplastics—A Circular Bioeconomy Approach. Marine Drugs, 20(12), 760.				No			2022.0	Clear zone;weight loss;FTIR;tensile strength	LDPE film			No	Marine sediment	Marine	Portugal	No		
Nocardiopsis prasina	2015	PS	Oliveira, J., Almeida, P. L., Sobral, R. G., Lourenço, N. D., & Gaudêncio, S. P. (2022). Marine-Derived Actinomycetes: Biodegradation of Plastics and Formation of PHA Bioplastics—A Circular Bioeconomy Approach. Marine Drugs, 20(12), 760.				No			2022.0	Clear zone;weight loss;FTIR;tensile strength	PS film			No	Marine sediment	Marine	Portugal	No		
Nocardiopsis prasina	2015	PLA	Oliveira, J., Almeida, P. L., Sobral, R. G., Lourenço, N. D., & Gaudêncio, S. P. (2022). Marine-Derived Actinomycetes: Biodegradation of Plastics and Formation of PHA Bioplastics—A Circular Bioeconomy Approach. Marine Drugs, 20(12), 760.				No			2022.0	Clear zone;weight loss;FTIR;tensile strength	PLA film			No	Marine sediment	Marine	Portugal	No		
Shewanella putrefaciens	24	PS	Yang, Y., Chen, J., Chen, Z., Yu, Z., Xue, J., Luan, T., Chen, S., & Zhou, S. (2022). Mechanisms of polystyrene microplastic degradation by the microbially driven Fenton reaction. Water Research, 223, 118979.				No			2022.0	GPC;XPS;ATR-FTIR;GPC	PS film			No	Culture collection	Culture collection	USA	No		
Exiguobacterium sp.	44751	LDPE	Maroof, L., Khan, I., Hassan, H., Azam, S., & Khan, W. (2022). Microbial degradation of low density polyethylene by Exiguobacterium sp. strain LM-IK2 isolated from plastic dumped soil. World Journal of Microbiology and Biotechnology, 38(11), 197.				No			2022.0	FE-SEM;FTIR;XRD	LDPE film	Good Fellow	No	No	Soil	Dumping site	Pakistan	No		
Neopestalotiopsis phangngaensis	2485531	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Microbial degradation of low-density polyethylene by Neopestalotiopsis phangngaensis. The Journal of General and Applied Microbiology, 68(6), 287-294.	Laccase			No			2022.0	Weight loss;tensile strength;CO2;SEM	Five millimeters nominal size of white amorphous LDPE microplastic granules were used for biodegradability assessment. Each LDPE sheet (1.0 cm × 4.0 cm) with a thickness of 0.11 mm was pre- pared according to a modified method (Khruengsai et al., 2021). They were washed with water, sterilized with 70 % ethanol, and air-drying. The dry sheets were kept inside the desiccator until use.			No	Culture collection	Culture collection	Thailand	No		
Neopestalotiopsis phangngaensis	2485531	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Microbial degradation of low-density polyethylene by Neopestalotiopsis phangngaensis. The Journal of General and Applied Microbiology, 68(6), 287-294.	Manganase peroxidase			No			2022.0	Weight loss;tensile strength;CO2;SEM	Five millimeters nominal size of white amorphous LDPE microplastic granules were used for biodegradability assessment. Each LDPE sheet (1.0 cm × 4.0 cm) with a thickness of 0.11 mm was pre- pared according to a modified method (Khruengsai et al., 2021). They were washed with water, sterilized with 70 % ethanol, and air-drying. The dry sheets were kept inside the desiccator until use.			No	Culture collection	Culture collection	Thailand	No		
Neopestalotiopsis phangngaensis	2485531	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Microbial degradation of low-density polyethylene by Neopestalotiopsis phangngaensis. The Journal of General and Applied Microbiology, 68(6), 287-294.	Lignin peroxidase			No			2022.0	Weight loss;tensile strength;CO2;SEM	Five millimeters nominal size of white amorphous LDPE microplastic granules were used for biodegradability assessment. Each LDPE sheet (1.0 cm × 4.0 cm) with a thickness of 0.11 mm was pre- pared according to a modified method (Khruengsai et al., 2021). They were washed with water, sterilized with 70 % ethanol, and air-drying. The dry sheets were kept inside the desiccator until use.			No	Culture collection	Culture collection	Thailand	No		
Alternaria burnsii	1187904	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Microbial degradation of low-density polyethylene by Neopestalotiopsis phangngaensis. The Journal of General and Applied Microbiology, 68(6), 287-294.				No			2022.0	Weight loss;tensile strength	Five millimeters nominal size of white amorphous LDPE microplastic granules were used for biodegradability assessment. Each LDPE sheet (1.0 cm × 4.0 cm) with a thickness of 0.11 mm was pre- pared according to a modified method (Khruengsai et al., 2021). They were washed with water, sterilized with 70 % ethanol, and air-drying. The dry sheets were kept inside the desiccator until use.			No	Culture collection	Culture collection	Thailand	No		
Alternaria pseudoeichhorniae	2507055	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Microbial degradation of low-density polyethylene by Neopestalotiopsis phangngaensis. The Journal of General and Applied Microbiology, 68(6), 287-294.				No			2022.0	Weight loss;tensile strength	Five millimeters nominal size of white amorphous LDPE microplastic granules were used for biodegradability assessment. Each LDPE sheet (1.0 cm × 4.0 cm) with a thickness of 0.11 mm was pre- pared according to a modified method (Khruengsai et al., 2021). They were washed with water, sterilized with 70 % ethanol, and air-drying. The dry sheets were kept inside the desiccator until use.			No	Culture collection	Culture collection	Thailand	No		
Arthrinium sacchari	166626	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Microbial degradation of low-density polyethylene by Neopestalotiopsis phangngaensis. The Journal of General and Applied Microbiology, 68(6), 287-294.				No			2022.0	Weight loss;tensile strength	Five millimeters nominal size of white amorphous LDPE microplastic granules were used for biodegradability assessment. Each LDPE sheet (1.0 cm × 4.0 cm) with a thickness of 0.11 mm was pre- pared according to a modified method (Khruengsai et al., 2021). They were washed with water, sterilized with 70 % ethanol, and air-drying. The dry sheets were kept inside the desiccator until use.			No	Culture collection	Culture collection	Thailand	No		
Bacillus cereus	1396	PS	Yuan, J., Cao, J., Yu, F., & Ma, J. (2022). Microbial degradation of polystyrene microplastics by a novel isolated bacterium in aquatic ecosystem. Sustainable Chemistry and Pharmacy, 30, 100873.				No			2022.0	Weight loss;FTIR;SEM;WCA;TGA;SSA	PS powder	Dongguan Jing Tian Raw Materials of Plastics Co. Ltd.	No	No	Lake sediment	Lake		No		
Micrococcus luteus	1270	HDPE	Kopecká, R., Kubínová, I., Sovová, K., Mravcová, L., Vítěz, T., & Vítězová, M. (2022). Microbial degradation of virgin polyethylene by bacteria isolated from a landfill site. SN Applied Sciences, 4(11), 302.				No			2022.0	Clear zone;weight loss;FTIR;FE-SEM;EDX	HDPE film			No	Cow dung	Animal associated	India	No		
Bacillus cereus	1396	HDPE	Kopecká, R., Kubínová, I., Sovová, K., Mravcová, L., Vítěz, T., & Vítězová, M. (2022). Microbial degradation of virgin polyethylene by bacteria isolated from a landfill site. SN Applied Sciences, 4(11), 302.				No			2022.0	Weight loss;GCMS	HDPE film	Belt Plast Brno s.r.o.	No	No	Plastic waste	Landfill	Czech Republic	No		
Enterobacter hormaechei	158836	HDPE	Kopecká, R., Kubínová, I., Sovová, K., Mravcová, L., Vítěz, T., & Vítězová, M. (2022). Microbial degradation of virgin polyethylene by bacteria isolated from a landfill site. SN Applied Sciences, 4(11), 302.				No			2022.0	Weight loss;GCMS	HDPE film	Belt Plast Brno s.r.o.	No	No	Plastic waste	Landfill	Czech Republic	No		
Proteus vulgaris	585	HDPE	Kopecká, R., Kubínová, I., Sovová, K., Mravcová, L., Vítěz, T., & Vítězová, M. (2022). Microbial degradation of virgin polyethylene by bacteria isolated from a landfill site. SN Applied Sciences, 4(11), 302.				No			2022.0	Weight loss;GCMS	HDPE film	Belt Plast Brno s.r.o.	No	No	Plastic waste	Landfill	Czech Republic	No		
Citrobacter koseri	545	HDPE	Kopecká, R., Kubínová, I., Sovová, K., Mravcová, L., Vítěz, T., & Vítězová, M. (2022). Microbial degradation of virgin polyethylene by bacteria isolated from a landfill site. SN Applied Sciences, 4(11), 302.				No			2022.0	Weight loss;GCMS	HDPE film	Belt Plast Brno s.r.o.	No	No	Plastic waste	Landfill	Czech Republic	No		
Pseudomonas stutzeri	545	HDPE	Kopecká, R., Kubínová, I., Sovová, K., Mravcová, L., Vítěz, T., & Vítězová, M. (2022). Microbial degradation of virgin polyethylene by bacteria isolated from a landfill site. SN Applied Sciences, 4(11), 302.				No			2022.0	Weight loss;GCMS	HDPE film	Belt Plast Brno s.r.o.	No	No	Plastic waste	Landfill	Czech Republic	No		
Pseudomonas tuomurensis	545	HDPE	Kopecká, R., Kubínová, I., Sovová, K., Mravcová, L., Vítěz, T., & Vítězová, M. (2022). Microbial degradation of virgin polyethylene by bacteria isolated from a landfill site. SN Applied Sciences, 4(11), 302.				No			2022.0	Weight loss;GCMS	HDPE film	Belt Plast Brno s.r.o.	No	No	Plastic waste	Landfill	Czech Republic	No		
Jonesia denitrificans	43674	HDPE	Kopecká, R., Kubínová, I., Sovová, K., Mravcová, L., Vítěz, T., & Vítězová, M. (2022). Microbial degradation of virgin polyethylene by bacteria isolated from a landfill site. SN Applied Sciences, 4(11), 302.				No			2022.0	Weight loss;GCMS	HDPE film	Belt Plast Brno s.r.o.	No	No	Plastic waste	Landfill	Czech Republic	No		
Microbulbifer sp.	1908541	PHB	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Clear zone;weight loss;SEM;FTIR;GPC;HPLC;GCMS	PHB pellets	Goodfellow	Yes	No	Soil	Sea shore	South Korea	No		
Microbulbifer sp.	1908541	P(3HB-co-4HB)	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Clear zone	P(3HB-co-4HB) pellets	Sigma Aldrich	Yes	No	Soil	Sea shore	South Korea	No		
Microbulbifer sp.	1908541	P(3HB-co-HV)	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Clear zone	P(3HB-co-HV) pellets	Sigma Aldrich	Yes	No	Soil	Sea shore	South Korea	No		
Microbulbifer sp.	1908541	PCL	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Clear zone	PCL pellets	Sigma Aldrich	Yes	No	Soil	Sea shore	South Korea	No		
Bacillus thioparans	370439	PHB	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Weight loss	PHB pellets	Goodfellow	Yes	No	Soil	Sea shore	South Korea	No		
Bacillus infantis	324767	PHB	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Weight loss	PHB pellets	Goodfellow	Yes	No	Soil	Sea shore	South Korea	No		
Bacillus aquimaris	189382	PHB	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Weight loss	PHB pellets	Goodfellow	Yes	No	Soil	Sea shore	South Korea	No		
Bacillus pakistanensis	992288	PHB	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Weight loss	PHB pellets	Goodfellow	Yes	No	Soil	Sea shore	South Korea	No		
Bacillus aryabhattai	412384	PHB	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Weight loss	PHB pellets	Goodfellow	Yes	No	Soil	Sea shore	South Korea	No		
Bacillus subterraneus	285983	PHB	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Weight loss	PHB pellets	Goodfellow	Yes	No	Soil	Sea shore	South Korea	No		
Bacillus zanthoxyli	2663026	PHB	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Weight loss	PHB pellets	Goodfellow	Yes	No	Soil	Sea shore	South Korea	No		
Bacillus hwajinpoensis	208199	PHB	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Weight loss	PHB pellets	Goodfellow	Yes	No	Soil	Sea shore	South Korea	No		
Bacillus megaterium	208199	PHB	Park, S. L., Cho, J. Y., Kim, S. H., Lee, H. J., Kim, S. H., Suh, M. J., Ham, S., Bhatia, S. K., Gurav, R., Park, S., Park, K., Kim, Y., & Yang, Y. H. (2022). Novel Polyhydroxybutyrate-degrading activity of the Microbulbifer genus as confirmed by Microbulbifer sp. SOL03 from the marine environment.				No			2022.0	Weight loss	PHB pellets	Goodfellow	Yes	No	Soil	Sea shore	South Korea	No		
Bacillus cereus	1396	PS	Miloloža, M., Ukić, Š., Cvetnić, M., Bolanča, T., & Kučić Grgić, D. (2022). Optimization of Polystyrene Biodegradation by Bacillus cereus and Pseudomonas alcaligenes Using Full Factorial Design. Polymers, 14(20), 4299.				No			2022.0	TOC;FTIR-ATR	MP were obtained by grinding plastic disposable accessories such as spoons for PS. First, these materials were cut into smaller pieces with scissors and then ground in a cryo-mill (Retsch, Haan, Germany) with liquid nitrogen and dried in the air for 48 h at room temperature. Next, obtained particles were sieved on stainless steel screens (RX-86-1 Sieve shaker, W.S. Tyler, Mentor, OH, USA) to obtain particles in size ranges: 500–700 μm, 300–500 μm, and 100–300 μm. 		No	No	 NA		Croatia	No		
Pseudomonas alcaligenes	43263	PS	Miloloža, M., Ukić, Š., Cvetnić, M., Bolanča, T., & Kučić Grgić, D. (2022). Optimization of Polystyrene Biodegradation by Bacillus cereus and Pseudomonas alcaligenes Using Full Factorial Design. Polymers, 14(20), 4299.				No			2022.0	TOC;FTIR-ATR	MP were obtained by grinding plastic disposable accessories such as spoons for PS. First, these materials were cut into smaller pieces with scissors and then ground in a cryo-mill (Retsch, Haan, Germany) with liquid nitrogen and dried in the air for 48 h at room temperature. Next, obtained particles were sieved on stainless steel screens (RX-86-1 Sieve shaker, W.S. Tyler, Mentor, OH, USA) to obtain particles in size ranges: 500–700 μm, 300–500 μm, and 100–300 μm. 		No	No	 NA		Croatia	No		
Staphylococcus sp.	29387	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Microbacterium radiodurans	661398	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Bacillus sp.	1409	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Neisseria sp.	192066	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Streptococcus equi	1336	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Escherichia coli	562	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Streptococcus mitior	562	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Lactobacillus sp.	1591	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Streptococcus sp.	1306	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Bacillus sp.	1409	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Staphylococcus sp.	29387	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Micrococcus mucilaginosus	43675	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Staphylocuccus aureus	43675	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Proteus sp.	43675	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Streptococcus sp.	1306	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Streptococcus sp.	1306	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Micrococcus sp.	1271	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Pseudomonas sp.	306	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Streptococcus sp.	1306	PVC	Emmanuel-Akerele, H. A., & Akinyemi, P. O. (2022). Physico-chemical and microbiological assessment of soils from dumpsites for plastic degrading microorganisms. Pollution, 8(2), 501-512.				No			2022.0	Weight loss	PVC strips			No	Soil	Landfill	Nigeria	No		
Morinia sp.	1306	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Pestalotiopsis sp.	36460	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Pestalotiopsis sp.	36460	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Pestalotiopsis sp.	36460	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Pestalotiopsis thailandica	2594163	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Botryosphaeria dothidea	55169	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Sphaeropsis sapinea	66738	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Neodevriesia sp.	2011839	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium allicinum	1338630	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium antropophilum	1338630	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium sp.	1707700	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium sp.	1707700	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium funiculosum	241845	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium halotolerans	1052096	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium perangustum	887098	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium pseudocladosporioides	887100	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium ramotenellum	470174	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium rectoides	887101	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium tenuissimum	70808	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium xanthochromaticum	1970641	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cladosporium xylophilum	887106	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Diaporthe sp.	1756133	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Diaporthe sp.	1756133	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Diaporthe sp.	1756133	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Diaporthe sp.	1756133	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Cytospora ceratosperma	1928361	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Aureobasidium melanogenum	46634	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Aureobasidium namibiae	559561	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Aureobasidium pullulans	5580	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Aspergillus ochraceus	40380	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Aspergillus oryzae	5062	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Aspergillus tritici	2932460	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Penicillium echinulatum	60174	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Penicillium roqueforti	5082	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Talaromyces rugulosus	121627	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Plectosphaerella cucumerina	40658	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Botrytis cinerea	40559	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Fusarium equiseti	61235	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Fusarium fujikuroi	5127	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Hypocreales sp.	1715234	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Parasarocladium sp.	2712021	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Sarocladium strictum	5046	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Trichoderma harzianum	5544	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Trichoderma fomiticola	692669	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Phaeophleospora eucalypticola	1871380	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Alternaria alternata	5599	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Alternaria sp.	1715220	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Alternaria chlamydospora	1187911	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Didymella sp.	1881153	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Didymosphaeriaceae sp.	1881152	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Didymosphaeriaceae sp.	1881152	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Epicoccum sp.	1859956	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Epicoccum sp.	1859956	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Epicoccum dendrobii	2021033	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Epicoccum duchesneae	2021034	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Epicoccum sorghinum	749593	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Epicoccum sp.	1859956	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Epicoccum tritici	2709053	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Neocamarosporium solicola	1986066	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Neocamarosporium sp.	1979426	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Neodidymelliopsis sp.	1899356	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Neodidymelliopsis longicolla	1770225	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Neosetophoma sp.	1756113	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Neosetophoma poaceicola	2709063	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Neosetophoma rosigena	2133997	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Nothophoma quercina	749835	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Paradendryphiella arenariae	156293	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Paraphoma radicina	437017	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Parathyridaria sp.	2107950	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Phaeosphaeria spartinicola	174302	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Phaeosphaeria oryzae	129864	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Plesporaceae sp.	129864	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Plesporaceae sp.	129864	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Pleosporales sp.	1755443	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Pleosporales sp.	1755443	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Pleosporales sp.	1755443	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Pyrenochaetopsis microspora	798153	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Pyrenochaetopsis paucisetosa	2301484	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Remotididymella sp.	2765348	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Remotididymella sp.	2765348	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Stemphylium lycopersici	183478	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Stemphylium vesicarium	119933	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Chaetomium globosum	38033	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Pseudogymnoascus pannorum	79858	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Eutypella sp.	1715228	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Apiospora marii	335849	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Apiospora rasikravindrae	990691	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Sedecimiella taiwanensis	937808	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Septoriella sp.	2006379	PCL	Kim, S. H., Lee, J. W., Kim, J. S., Lee, W., Park, M. S., & Lim, Y. W. (2022). Plastic-inhabiting fungi in marine environments and PCL degradation activity. Antonie Van Leeuwenhoek, 115(12), 1379-1392.				No			2022.0	Clear zone	PCL in agar medium			No	Plastic waste	Coastline	South Korea	No		
Exiguobacterium sp.	44751	PS	Parthasarathy, A., Miranda, R. R., Eddingsaas, N. C., Chu, J., Freezman, I. M., Tyler, A. C., & Hudson, A. O. (2022). Polystyrene degradation by Exiguobacterium sp. RIT 594: Preliminary evidence for a pathway containing an atypical oxygenase. Microorganisms, 10(8), 1619.				No			2022.0	ATR-FTIR;SEM	PS sheets	Goodfellow	Yes	No	Soil	Soil	USA	No		
Serratia sp.	44751	PU	Kim, J. H., Choi, S. H., Park, M. G., Park, D. H., Son, K. H., & Park, H. Y. (2022). Polyurethane biodegradation by Serratia sp. HY-72 isolated from the intestine of the Asian mantis Hierodula patellifera. Frontiers in Microbiology, 13, 1005415.	Lipase			No			2022.0	Clear zone;turbidity;SEM;weight loss	Impranil, PS-PU foam, PE-PU foam	Bayer Materials Science (Impranil), KPX Chemical Co. (foams)	No	No	Mantis gut	Animal associated	South Korea	No		
Serratia sp.	44751	PU	Kim, J. H., Choi, S. H., Park, M. G., Park, D. H., Son, K. H., & Park, H. Y. (2022). Polyurethane biodegradation by Serratia sp. HY-72 isolated from the intestine of the Asian mantis Hierodula patellifera. Frontiers in Microbiology, 13, 1005415.	Protease			No			2022.0	Clear zone;turbidity;SEM;weight loss	Impranil, PS-PU foam, PE-PU foam	Bayer Materials Science (Impranil), KPX Chemical Co. (foams)	No	No	Mantis gut	Animal associated	South Korea	No		
Brevibacillus parabrevis	54914	PET	Babazadeh, F., Gharavi, S., Soudi, M. R., Zarrabi, M., & Talebpour, Z. (2023). Potential for polyethylene terephthalate (PET) degradation revealed by metabarcoding and bacterial isolates from soil around a bitumen source in Southwestern Iran. Journal of Polymers and the Environment, 31(4), 1279-1291.				No			2022.0	FE-SEM;GCMS;XRD;ATR-FTIR	PET powder and PET film was made by using post-consumer mineral water bottles. 		No	No	Soil	Petroleum seeps	Iran	No		
Pseudomonas aeruginosa	287	PET	Babazadeh, F., Gharavi, S., Soudi, M. R., Zarrabi, M., & Talebpour, Z. (2023). Potential for polyethylene terephthalate (PET) degradation revealed by metabarcoding and bacterial isolates from soil around a bitumen source in Southwestern Iran. Journal of Polymers and the Environment, 31(4), 1279-1291.				No			2022.0	FE-SEM;GCMS;XRD;ATR-FTIR	PET powder and PET film was made by using post-consumer mineral water bottles. 		No	No	Soil	Petroleum seeps	Iran	No		
Pseudomonas aeruginosa	287	PET	Babazadeh, F., Gharavi, S., Soudi, M. R., Zarrabi, M., & Talebpour, Z. (2023). Potential for polyethylene terephthalate (PET) degradation revealed by metabarcoding and bacterial isolates from soil around a bitumen source in Southwestern Iran. Journal of Polymers and the Environment, 31(4), 1279-1291.				No			2022.0	FE-SEM;GCMS;XRD;ATR-FTIR	PET powder and PET film was made by using post-consumer mineral water bottles. 		No	No	Soil	Petroleum seeps	Iran	No		
Bacillus thuringiensis	1428	PBAT	Kanwal, A., Zhang, M., Sharaf, F., & Chengtao, L. (2022). Screening and characterization of novel lipase producing Bacillus species from agricultural soil with high hydrolytic activity against PBAT poly (butylene adipate co terephthalate) co-polyesters. Polymer Bulletin, 79(11), 10053-10076.	Lipase			No			2022.0	Weight loss;SEM;XRD;FTIR;TGA	Raw PBAT granules and chlo- roform were mixed in a three-necked flask and shaken at 600 rpm for 24 h until completely dissolved followed by subsequent purification using industrial alcohol. Then weighed amount of purified PBAT and chloroform were added in a 3-necked flask and shaken for 4–6 h to let it dissolve completely. After that, it was poured on smooth petri plates to make the films of desired thickness. A screw gauge was then used to measure the thickness of all films 	Zhuhai Wantong Chemical Co., Ltd	No	No	Soil	Soil	China	No		
Bacillus cereus	1396	PBAT	Kanwal, A., Zhang, M., Sharaf, F., & Chengtao, L. (2022). Screening and characterization of novel lipase producing Bacillus species from agricultural soil with high hydrolytic activity against PBAT poly (butylene adipate co terephthalate) co-polyesters. Polymer Bulletin, 79(11), 10053-10076.	Lipase			No			2022.0	Weight loss;SEM;XRD;FTIR;TGA	Raw PBAT granules and chlo- roform were mixed in a three-necked flask and shaken at 600 rpm for 24 h until completely dissolved followed by subsequent purification using industrial alcohol. Then weighed amount of purified PBAT and chloroform were added in a 3-necked flask and shaken for 4–6 h to let it dissolve completely. After that, it was poured on smooth petri plates to make the films of desired thickness. A screw gauge was then used to measure the thickness of all films 	Zhuhai Wantong Chemical Co., Ltd	No	No	Soil	Soil	China	No		
Bacillus paramycoides	2026194	PBAT	Kanwal, A., Zhang, M., Sharaf, F., & Chengtao, L. (2022). Screening and characterization of novel lipase producing Bacillus species from agricultural soil with high hydrolytic activity against PBAT poly (butylene adipate co terephthalate) co-polyesters. Polymer Bulletin, 79(11), 10053-10076.	Lipase			No			2022.0	Weight loss;SEM;XRD;FTIR;TGA	Raw PBAT granules and chlo- roform were mixed in a three-necked flask and shaken at 600 rpm for 24 h until completely dissolved followed by subsequent purification using industrial alcohol. Then weighed amount of purified PBAT and chloroform were added in a 3-necked flask and shaken for 4–6 h to let it dissolve completely. After that, it was poured on smooth petri plates to make the films of desired thickness. A screw gauge was then used to measure the thickness of all films 	Zhuhai Wantong Chemical Co., Ltd	No	No	Soil	Soil	China	No		
Acinetobacter baumannii	470	LDPE	Zhang, Y., Lin, Y., Gou, H., Feng, X., Zhang, X., & Yang, L. (2022). Screening of polyethylene-degrading bacteria from rhyzopertha dominica and evaluation of its key enzymes degrading polyethylene. Polymers, 14(23), 5127.	Laccase			No			2022.0	Weight loss;SEM;ATR-FTIR;WCA;GPC	The PE film is a conventional food fresh-keeping bag film, with a weight-average molecular weight (Mw) greater than 130,000, belonging to low-density polyethylene (LDPE), and the weight-average molecular weight (Mw) of PE powder is greater than 80,000. The PE films were cut into 4.0 cm × 4.0 cm, 1.0 cm × 1.0 cm pieces. They were soaked in 0.5% potassium chloride for 1 h. The remaining potassium chloride was rinsed off with ethanol and then rinsed with sterile water. The PE films were dried at 50 ◦C, and finally the PE films were put under a UV lamp for 4 h for sterilization.		No	No	Worm tissue	Animal associated		No		
Comamonas sp.	34028	PE	Peixoto, J., Vizzotto, C., Ramos, A., Alves, G., Steindorff, A., & Krüger, R. (2022). The role of nitrogen metabolism on polyethylene biodegradation. Journal of Hazardous Materials, 432, 128682.				No			2022.0	ATR-FTIR	LDPE films	Carmel Olefins Ltd.	No	No	Soil	Soil	Brazil	No		
Delftia sp.	1886637	PE	Peixoto, J., Vizzotto, C., Ramos, A., Alves, G., Steindorff, A., & Krüger, R. (2022). The role of nitrogen metabolism on polyethylene biodegradation. Journal of Hazardous Materials, 432, 128682.				No			2022.0	ATR-FTIR	LDPE films	Carmel Olefins Ltd.	No	No	Soil	Soil	Brazil	No		
Stenotrophomonas sp.	69392	PE	Peixoto, J., Vizzotto, C., Ramos, A., Alves, G., Steindorff, A., & Krüger, R. (2022). The role of nitrogen metabolism on polyethylene biodegradation. Journal of Hazardous Materials, 432, 128682.				No			2022.0	ATR-FTIR	LDPE films	Carmel Olefins Ltd.	No	No	Soil	Soil	Brazil	No		
Lichtheimia ramosa	688394	PSS	Bhanot, V., & Panwar, J. (2023). Unveiling the potential of Lichtheimia ramosa AJP11 for myco-transformation of polystyrene sulfonate and its driving molecular mechanism. Journal of Environmental Management, 325, 116579.				No			2022.0	GCMS	Poly(sodium 4-styrenesulfonate) (PSS; Mw ~70,000 Da) was used as the source of PS. 			No	Soil	Soil	India	No		
Aspergillus tamarii	41984	PET	Anbalagan, S., Venkatakrishnan, H. R. R., Ravindran, J., Sathyamoorthy, J., Rangabashyam, K. A., Ragini, Y. P., & Sureshbabu, K. (2021). Hydrolytic degradation of polyethylene terephthalate by cutinase enzyme derived from fungal biomass–molecular characterization. BioInterface Res. Appl. Chem, 12, 653-667.	Lipase			No			2021.0	FTIR;SEM;HPLC	An empty non-carbonated water bottle was taken. It is washed using sterile doubledistilled water to remove any impurities. The bottle is then cut into dimensions of about 2×2cm2. The films were again washed and dried to store in a clean desiccator.		No	No	Soil	Soil	India	No		
Penicillium crustosum	36656	PET	Anbalagan, S., Venkatakrishnan, H. R. R., Ravindran, J., Sathyamoorthy, J., Rangabashyam, K. A., Ragini, Y. P., & Sureshbabu, K. (2021). Hydrolytic degradation of polyethylene terephthalate by cutinase enzyme derived from fungal biomass–molecular characterization. BioInterface Res. Appl. Chem, 12, 653-667.	Cutinase			No			2021.0	FTIR;SEM;HPLC	An empty non-carbonated water bottle was taken. It is washed using sterile doubledistilled water to remove any impurities. The bottle is then cut into dimensions of about 2×2cm2. The films were again washed and dried to store in a clean desiccator.		No	No	Soil	Soil	India	No		
Bifidobacterium infantis	36656	PP	Bozkurt, H. S., Yörüklü, H. C., Bozkurt, K., Denktaş, C., Bozdoğan, A., Özdemir, O., & Özkaya, B. (2022). Biodegradation of microplastic by probiotic bifidobacterium. International Journal of Global Warming, 26(4), 429-443.				No			2022.0	FTIR;SEM	To produce microplastic samples, pellets of PP were grinded with a grinder. Grinded microplastic samples were sieved with two sieves having 75 and 100 μm sieve size to obtain MPs of known size range.			No				No		
Exiguobacterium marinum	273528	PP	Sun, Y., Zhang, Y., Hao, X., Zhang, X., Ma, Y., & Niu, Z. (2023). A novel marine bacterium Exiguobacterium marinum a-1 isolated from in situ plastisphere for degradation of additive-free polypropylene. Environmental Pollution, 336, 122390.				No			2023.0	Weight loss;FTIR;SEM	Additive-free PP film	Good Fellow	Yes	No	Plastic waste	Marine	China	No		
Bacillus thermoruber	33942	PCL	Atanasova, N., Paunova-Krasteva, T., Kambourova, M., & Boyadzhieva, I. (2023). A Thermostable Lipase Isolated from Brevibacillus thermoruber Strain 7 Degrades Ɛ-Polycaprolactone. BioTech, 12(1), 23.	Lipase			No			2023.0	GPC;SEM	PCL pearls with a diameter ranging from 2.9 to 4.8 mm and an average MW 80,000enhanced its activity. The monomer Ɛ-caprolactone was a main product of the enzyme(Sigma-Aldrich, Steincheim am Albuch, Germany) were used as the only carbon source.	Sigma Aldrich	Yes	Yes		Hot spring	Germany	No		
Exophilia sp.	33942	PU	Giyahchi, M., & Moghimi, H. (2023). Aerobic biodegradation of untreated polyester–polyether urethanes by newly isolated yeast strains Exophilia sp. NS-7 and Rhodotorula sp. NS-12. Scientific Reports, 13(1), 5016.				No			2023.0	FTIR;SEM;NMR;CO2	Polyurethane films were prepared by dissolving 0.25 g of Poly [4,4’-methylenebis (phenyl isocyanate)-aH-1,4-butanediol/di (propylene glycol)/polycarbonate], in 25 mL Tet- rahydrofuran (THF) solvent. The prepared solution was poured into glass Petri dishes and allowed to evaporate under a fume hood. After 24 h, polyurethane films were cut into quadratic pieces of 2 × 2 cm.			No			Iran	No		
Exophilia sp.	33942	PU	Giyahchi, M., & Moghimi, H. (2023). Aerobic biodegradation of untreated polyester–polyether urethanes by newly isolated yeast strains Exophilia sp. NS-7 and Rhodotorula sp. NS-12. Scientific Reports, 13(1), 5016.				No			2023.0	Clear zone	Impranil	Bayer Company		No	Yes		Iran	No		
Rhodotorula sp.	1853554	PU	Giyahchi, M., & Moghimi, H. (2023). Aerobic biodegradation of untreated polyester–polyether urethanes by newly isolated yeast strains Exophilia sp. NS-7 and Rhodotorula sp. NS-12. Scientific Reports, 13(1), 5016.				No			2023.0	FTIR;SEM;NMR;CO2	Polyurethane films were prepared by dissolving 0.25 g of Poly [4,4’-methylenebis (phenyl isocyanate)-aH-1,4-butanediol/di (propylene glycol)/polycarbonate], in 25 mL Tet- rahydrofuran (THF) solvent. The prepared solution was poured into glass Petri dishes and allowed to evaporate under a fume hood. After 24 h, polyurethane films were cut into quadratic pieces of 2 × 2 cm.			No			Iran	No		
Rhodotorula sp.	1853554	PU	Giyahchi, M., & Moghimi, H. (2023). Aerobic biodegradation of untreated polyester–polyether urethanes by newly isolated yeast strains Exophilia sp. NS-7 and Rhodotorula sp. NS-12. Scientific Reports, 13(1), 5016.				No			2023.0	Clear zone	Impranil	Bayer Company		No	Yes		Iran	No		
Bacillus sp.	1409	PCL	Kim, S. H., Shin, N., Jeon, J. M., Yoon, J. J., Joo, J. C., Kim, H. T., Bhatia, S. K., & Yang, Y. H. (2024). Application of liquid-based colorimetric method for high throughput screening of bioplastic-degrading strains using esterase assay. Analytical Biochemistry, 685, 115390.	Esterase			No			2023.0	Clear zone	For preparing a plastic emulsion, 1 g of plastic pellets were dissolved in 40 mL of DCM in a water bath at 60◦C. Then, 100 ml of distilled water was added, and 2 ml of 2% Sarkosyl NL was added to the boundary between the water and DCM [28]. The mixture was sonicated for 10 min with a 15 s pulse using a Vibra Cell VCX500 (Sonics & Materials, Inc., Newtown, CT, USA). The amplitude was set to 30% to mix the content uniformly [36] After sonication, the solvent was evaporated completely using a stirrer. Next, 1 g/L of the emulsion was added to the marine broth (MB, Difco Laboratories, Detroit, MI, USA) and 2% agarose. All mixtures were autoclaved for 15 min at 121 ◦C.	Sigma-Aldrich	Yes	No				No		
Bacillus sp.	1409	PBAT	Kim, S. H., Shin, N., Jeon, J. M., Yoon, J. J., Joo, J. C., Kim, H. T., Bhatia, S. K., & Yang, Y. H. (2024). Application of liquid-based colorimetric method for high throughput screening of bioplastic-degrading strains using esterase assay. Analytical Biochemistry, 685, 115390.	Esterase			No			2023.0	Clear zone	For preparing a plastic emulsion, 1 g of plastic pellets were dissolved in 40 mL of DCM in a water bath at 60◦C. Then, 100 ml of distilled water was added, and 2 ml of 2% Sarkosyl NL was added to the boundary between the water and DCM [28]. The mixture was sonicated for 10 min with a 15 s pulse using a Vibra Cell VCX500 (Sonics & Materials, Inc., Newtown, CT, USA). The amplitude was set to 30% to mix the content uniformly [36] After sonication, the solvent was evaporated completely using a stirrer. Next, 1 g/L of the emulsion was added to the marine broth (MB, Difco Laboratories, Detroit, MI, USA) and 2% agarose. All mixtures were autoclaved for 15 min at 121 ◦C.	BASF SE	Yes	No				No		
Bacillus sp.	1409	PBS	Kim, S. H., Shin, N., Jeon, J. M., Yoon, J. J., Joo, J. C., Kim, H. T., Bhatia, S. K., & Yang, Y. H. (2024). Application of liquid-based colorimetric method for high throughput screening of bioplastic-degrading strains using esterase assay. Analytical Biochemistry, 685, 115390.	Esterase			No			2023.0	Clear zone	For preparing a plastic emulsion, 1 g of plastic pellets were dissolved in 40 mL of DCM in a water bath at 60◦C. Then, 100 ml of distilled water was added, and 2 ml of 2% Sarkosyl NL was added to the boundary between the water and DCM [28]. The mixture was sonicated for 10 min with a 15 s pulse using a Vibra Cell VCX500 (Sonics & Materials, Inc., Newtown, CT, USA). The amplitude was set to 30% to mix the content uniformly [36] After sonication, the solvent was evaporated completely using a stirrer. Next, 1 g/L of the emulsion was added to the marine broth (MB, Difco Laboratories, Detroit, MI, USA) and 2% agarose. All mixtures were autoclaved for 15 min at 121 ◦C.	ANKOR Bioplastics Co., Ltd	Yes	No				No		
Pseudomonas aeruginosa	287	LDPE	Association of Laccase from Bacillus cereus O2-B and Pseudomonas aeruginosa O1-P with the bio-degradation of polymers an in vitro to in silico approach	Laccase			No			2023.0	SEM;FTIR;XRD;GCMS	1x1 cm LDPE plastic sheets	Apollo Plastics		No	Soil	Garbage dump	India	No		
Bacillus cereus	1396	LDPE	Association of Laccase from Bacillus cereus O2-B and Pseudomonas aeruginosa O1-P with the bio-degradation of polymers an in vitro to in silico approach				No			2023.0	SEM;FTIR;XRD;GCMS	1x1 cm LDPE plastic sheets	Apollo Plastics		No	Soil	Garbage dump	India	No		
Chloroidium saccharophilum	3082	LDPE	Gowthami, A., Marjuk, M. S., Raju, P., Devi, K. N., Santhanam, P., Kumar, S. D., & Perumal, P. (2023). Biodegradation efficacy of selected marine microalgae against Low-Density Polyethylene (LDPE): An environment friendly green approach. Marine Pollution Bulletin, 190, 114889.				No			2023.0	Weight loss;SEM:ATR-FTIR;TGA	LDPE sheets were purchased from a local plastic company (Trichy)that possess a thickness of 20 μm and they were cut down into small pieces (2 cm ×2 cm), sterilized with 70 % ethanol, followed by rinsedwith Milli-Q water and overnight dried at 60 ◦C, using hot air oven.	Trichy		No	Culture collection	Culture collection	India	No		
Picochlorum maculatum	133488	LDPE	Gowthami, A., Marjuk, M. S., Raju, P., Devi, K. N., Santhanam, P., Kumar, S. D., & Perumal, P. (2023). Biodegradation efficacy of selected marine microalgae against Low-Density Polyethylene (LDPE): An environment friendly green approach. Marine Pollution Bulletin, 190, 114889.				No			2023.0	Weight loss;SEM:ATR-FTIR;TGA	LDPE sheets were purchased from a local plastic company (Trichy)that possess a thickness of 20 μm and they were cut down into small pieces (2 cm ×2 cm), sterilized with 70 % ethanol, followed by rinsedwith Milli-Q water and overnight dried at 60 ◦C, using hot air oven.	Trichy		No	Culture collection	Culture collection	India	No		
Amphora sp.	1715697	LDPE	Gowthami, A., Marjuk, M. S., Raju, P., Devi, K. N., Santhanam, P., Kumar, S. D., & Perumal, P. (2023). Biodegradation efficacy of selected marine microalgae against Low-Density Polyethylene (LDPE): An environment friendly green approach. Marine Pollution Bulletin, 190, 114889.				No			2023.0	Weight loss;SEM:ATR-FTIR;TGA	LDPE sheets were purchased from a local plastic company (Trichy)that possess a thickness of 20 μm and they were cut down into small pieces (2 cm ×2 cm), sterilized with 70 % ethanol, followed by rinsedwith Milli-Q water and overnight dried at 60 ◦C, using hot air oven.	Trichy		No	Culture collection	Culture collection	India	No		
Hymenomonas globosa	418938	LDPE	Gowthami, A., Marjuk, M. S., Raju, P., Devi, K. N., Santhanam, P., Kumar, S. D., & Perumal, P. (2023). Biodegradation efficacy of selected marine microalgae against Low-Density Polyethylene (LDPE): An environment friendly green approach. Marine Pollution Bulletin, 190, 114889.				No			2023.0	Weight loss;SEM:ATR-FTIR;TGA	LDPE sheets were purchased from a local plastic company (Trichy)that possess a thickness of 20 μm and they were cut down into small pieces (2 cm ×2 cm), sterilized with 70 % ethanol, followed by rinsedwith Milli-Q water and overnight dried at 60 ◦C, using hot air oven.	Trichy		No	Culture collection	Culture collection	India	No		
Limnospira indica	147322	LDPE	Gowthami, A., Marjuk, M. S., Raju, P., Devi, K. N., Santhanam, P., Kumar, S. D., & Perumal, P. (2023). Biodegradation efficacy of selected marine microalgae against Low-Density Polyethylene (LDPE): An environment friendly green approach. Marine Pollution Bulletin, 190, 114889.				No			2023.0	Weight loss;SEM:ATR-FTIR;TGA	LDPE sheets were purchased from a local plastic company (Trichy)that possess a thickness of 20 μm and they were cut down into small pieces (2 cm ×2 cm), sterilized with 70 % ethanol, followed by rinsedwith Milli-Q water and overnight dried at 60 ◦C, using hot air oven.	Trichy		No	Culture collection	Culture collection	India	No		
Cladosporium basi-inflatum	887087	LDPE	Gong, Z., Jin, L., Yu, X., Wang, B., Hu, S., Ruan, H., Sung, Y.-J., Lee, H.-G., & Jin, F. (2023). Biodegradation of Low Density Polyethylene by the Fungus Cladosporium sp. Recovered from a Landfill Site. Journal of Fungi, 9(6), 605.				No			2023.0	Weight loss;SEM;FTIR	LDPE microplastic granules (Shanghai Macklin Biochemical, Shanghai, China) were employed with a melting index of 20–30 g/10 min and a particle size of ~1000 mesh. The LDPE microplastic granules were weighed, put into Petri dishes, and exposed to UV irradiation for 12 h in the ultra-clean bench. LDPE Clear Open End Bags (Aladdln Industrial Corporation, Shanghai, China) with a thickness of 0.038 mm were cut into 3 cm × 3 cm pieces, weighed, recorded, and placed separately in sterile Petri dishes for further use. The untreated sheets (U-LDPE) were soaked and sterilized with 75% ethanol for 3 h in the ultra-clean bench and rinsed several times with sterile water. Subsequently, the sheets were air dried in the ultra-clean bench and sterilized with UV for 12 h.	Shanghai Macklin Biochemical		No	Soil	Soil		No		
Alcaligenes faecalis	511	LDPE	Devi, D., Gupta, K. K., Chandra, H., Sharma, K. K., Sagar, K., Mori, E., de Farias, P. A. M., Coutinho, H. D. M., & Mishra, A. P. (2023). Biodegradation of low-density polyethylene (LDPE) through application of indigenous strain Alcaligenes faecalis ISJ128. Environmental Geochemistry and Health, 1-19.				No			2023.0	Clear zone;weight loss;SEM;FTIR	Transparent low-density polyethylene (LDPE) sheets generally used for packaging were purchased from VSPN packaging industries, Bhagwanpur, Harid- war (Uttarakhand), India. LDPE sheets were cut into minor sections and sterilized with 70% ethanol, fol- lowed by heating with xylene at 60 °C for 5–15 min until the polyethylene dissolved completely. The resulting slurry was cooled by immersing the beaker in an ice bath. The solvent was extracted from the slurry using sterilized muslin cloth. The residue was further washed with ethanol for 2–3 times to remove the residual xylene. The resulting polyethylene pow- der was kept as such to evaporate remaining ethanol and then dried overnight in hot air oven at 60 °C.	VSPN packaging industries	No	No	Plastic debris	Garbage dump	India	No		
Pseudomonas aeruginosa	287	LDPE	Shilpa, Basak, N., & Meena, S. S. (2023). Biodegradation of low-density polythene (LDPE) by a novel strain of Pseudomonas aeruginosa WD4 isolated from plastic dumpsite. Biodegradation, 1-15.				No			2023.0	Weight loss;FTIR;SEM;XRD;GCMS	For the biodegradation study, 2*2 cm pieces of LDPE film were cut and sanitised using 70% ethanol and autoclaved with distilled water. The plastic films were dried in a hot air oven for 1 to 2 h after sterilisation, followed by 1 h of UV sterilisation in laminar airflow. 	Local market	No	No	Soil	Garbage dump	India	No		
Bacillus sp.	1409	Impranil	de Witt, J., Molitor, R., Gätgens, J., Ortmann de Percin Northumberland, C., Kruse, L., Polen, T., Wynands, B., Goethem, K., Thies, S., Jaeger, K.-E.,  & Wierckx, N. (2023). Biodegradation of poly (ester‐urethane) coatings by Halopseudomonas formosensis. Microbial Biotechnology.				No			2023.0	Clear zone	Impranil	Covestro AG		Yes		Compost heap	Germany	No		
Bacillus sp.	1409	HDPE	Zhang, H., Liu, Q., Wu, H., Sun, W., Yang, F., Ma, Y., & Qi, Y. (2023). Biodegradation of polyethylene film by the Bacillus sp. PELW2042 from the guts of Tenebrio molitor (Mealworm Larvae). Process Biochemistry, 130, 236-244.				No			2023.0	Weight loss;WCA;SEM;FTIR;XPS;XRD;HT-GPC	High purity HDPE film	Lanzhou Petrochemical Co.	Yes	No	Mealworm intestine	Animal associated	China	No		
Marinobacter sediminum	256323	PET	Zhao, S., Liu, R., Wang, J., Lv, S., Zhang, B., Dong, C., & Shao, Z. (2023). Biodegradation of polyethylene terephthalate (PET) by diverse marine bacteria in deep‐sea sediments. Environmental Microbiology, 25(12), 2719-2731.				No			2023.0	Weight loss;SEM	PET film	Sigma Aldrich	Yes	No	Sediment	Marine	Pacific Ocean	No		
Marinobacter gudaonensis	375760	PET	Zhao, S., Liu, R., Wang, J., Lv, S., Zhang, B., Dong, C., & Shao, Z. (2023). Biodegradation of polyethylene terephthalate (PET) by diverse marine bacteria in deep‐sea sediments. Environmental Microbiology, 25(12), 2719-2731.				No			2023.0	Weight loss;SEM	PET film	Sigma Aldrich	Yes	No	Sediment	Marine	Pacific Ocean	No		
Thalassospira xiamenensis	220697	PET	Zhao, S., Liu, R., Wang, J., Lv, S., Zhang, B., Dong, C., & Shao, Z. (2023). Biodegradation of polyethylene terephthalate (PET) by diverse marine bacteria in deep‐sea sediments. Environmental Microbiology, 25(12), 2719-2731.				No			2023.0	Weight loss;SEM	PET film	Sigma Aldrich	Yes	No	Sediment	Marine	Pacific Ocean	No		
Nocardioides marinus	374514	PET	Zhao, S., Liu, R., Wang, J., Lv, S., Zhang, B., Dong, C., & Shao, Z. (2023). Biodegradation of polyethylene terephthalate (PET) by diverse marine bacteria in deep‐sea sediments. Environmental Microbiology, 25(12), 2719-2731.				No			2023.0	Weight loss;SEM	PET film	Sigma Aldrich	Yes	No	Sediment	Marine	Pacific Ocean	No		
Yokenella regensburgei	158877	PS	Park, J. W., Kim, M., Kim, S. Y., Bae, J., & Kim, T. J. (2023). Biodegradation of polystyrene by intestinal symbiotic bacteria isolated from mealworms, the larvae of Tenebrio molitor. Heliyon.				No			2023.0	Optical microscopy;SEM	Polystyrene powder (catalog number: HI-LENE PSP-30, Sinwon Industrial Co., Ltd., Pyeongtaek, Korea) consisted of 95–100% ethenylbenzene homopolymer (CAS No. 9003-53-6), 0–5% general plastic lubricant was provided from Sinwon Industrial Co., Ltd. (Pyeongtaek, Korea). Polystyrene film (catalog number: ST31-FM-000150, GoodFellow, Seoul, Korea) was an additive-free styrene polymer with athickness of 0.05 mm. EPS was sterilized for 10 min at 80 ◦C and cooled at room temperature before feeding. Polystyrene powder wasimmersed in 75% ethanol for 5 min, separated from ethanol using an aspirator and filter paper, and dried sufficiently with UV light on aclean bench before use.	Sinwon Industrial Co., Ltd (powder), GoodFellow (film)		No	Mealworm intestine	Animal associated	Korea	No		
Acinetobacter septicus	465797	PS	Park, J. W., Kim, M., Kim, S. Y., Bae, J., & Kim, T. J. (2023). Biodegradation of polystyrene by intestinal symbiotic bacteria isolated from mealworms, the larvae of Tenebrio molitor. Heliyon.				No			2023.0	Optical microscopy;SEM	Polystyrene powder (catalog number: HI-LENE PSP-30, Sinwon Industrial Co., Ltd., Pyeongtaek, Korea) consisted of 95–100% ethenylbenzene homopolymer (CAS No. 9003-53-6), 0–5% general plastic lubricant was provided from Sinwon Industrial Co., Ltd. (Pyeongtaek, Korea). Polystyrene film (catalog number: ST31-FM-000150, GoodFellow, Seoul, Korea) was an additive-free styrene polymer with athickness of 0.05 mm. EPS was sterilized for 10 min at 80 ◦C and cooled at room temperature before feeding. Polystyrene powder wasimmersed in 75% ethanol for 5 min, separated from ethanol using an aspirator and filter paper, and dried sufficiently with UV light on aclean bench before use.	Sinwon Industrial Co., Ltd (powder), GoodFellow (film)		No	Mealworm intestine	Animal associated	Korea	No		
Acinetobacter septicus	465797	PS	Park, J. W., Kim, M., Kim, S. Y., Bae, J., & Kim, T. J. (2023). Biodegradation of polystyrene by intestinal symbiotic bacteria isolated from mealworms, the larvae of Tenebrio molitor. Heliyon.				No			2023.0	Optical microscopy;SEM	Polystyrene powder (catalog number: HI-LENE PSP-30, Sinwon Industrial Co., Ltd., Pyeongtaek, Korea) consisted of 95–100% ethenylbenzene homopolymer (CAS No. 9003-53-6), 0–5% general plastic lubricant was provided from Sinwon Industrial Co., Ltd. (Pyeongtaek, Korea). Polystyrene film (catalog number: ST31-FM-000150, GoodFellow, Seoul, Korea) was an additive-free styrene polymer with athickness of 0.05 mm. EPS was sterilized for 10 min at 80 ◦C and cooled at room temperature before feeding. Polystyrene powder wasimmersed in 75% ethanol for 5 min, separated from ethanol using an aspirator and filter paper, and dried sufficiently with UV light on aclean bench before use.	Sinwon Industrial Co., Ltd (powder), GoodFellow (film)		No	Mealworm intestine	Animal associated	Korea	No		
Acinetobacter septicus	465797	PS	Park, J. W., Kim, M., Kim, S. Y., Bae, J., & Kim, T. J. (2023). Biodegradation of polystyrene by intestinal symbiotic bacteria isolated from mealworms, the larvae of Tenebrio molitor. Heliyon.				No			2023.0	Optical microscopy;SEM	Polystyrene powder (catalog number: HI-LENE PSP-30, Sinwon Industrial Co., Ltd., Pyeongtaek, Korea) consisted of 95–100% ethenylbenzene homopolymer (CAS No. 9003-53-6), 0–5% general plastic lubricant was provided from Sinwon Industrial Co., Ltd. (Pyeongtaek, Korea). Polystyrene film (catalog number: ST31-FM-000150, GoodFellow, Seoul, Korea) was an additive-free styrene polymer with athickness of 0.05 mm. EPS was sterilized for 10 min at 80 ◦C and cooled at room temperature before feeding. Polystyrene powder wasimmersed in 75% ethanol for 5 min, separated from ethanol using an aspirator and filter paper, and dried sufficiently with UV light on aclean bench before use.	Sinwon Industrial Co., Ltd (powder), GoodFellow (film)		No	Mealworm intestine	Animal associated	Korea	No		
Klebsiella grimontii	2058152	PS	Park, J. W., Kim, M., Kim, S. Y., Bae, J., & Kim, T. J. (2023). Biodegradation of polystyrene by intestinal symbiotic bacteria isolated from mealworms, the larvae of Tenebrio molitor. Heliyon.				No			2023.0	Optical microscopy;SEM	Polystyrene powder (catalog number: HI-LENE PSP-30, Sinwon Industrial Co., Ltd., Pyeongtaek, Korea) consisted of 95–100% ethenylbenzene homopolymer (CAS No. 9003-53-6), 0–5% general plastic lubricant was provided from Sinwon Industrial Co., Ltd. (Pyeongtaek, Korea). Polystyrene film (catalog number: ST31-FM-000150, GoodFellow, Seoul, Korea) was an additive-free styrene polymer with athickness of 0.05 mm. EPS was sterilized for 10 min at 80 ◦C and cooled at room temperature before feeding. Polystyrene powder wasimmersed in 75% ethanol for 5 min, separated from ethanol using an aspirator and filter paper, and dried sufficiently with UV light on aclean bench before use.	Sinwon Industrial Co., Ltd (powder), GoodFellow (film)		No	Mealworm intestine	Animal associated	Korea	No		
Pseudomonas nitroreducens	46680	PS	Park, J. W., Kim, M., Kim, S. Y., Bae, J., & Kim, T. J. (2023). Biodegradation of polystyrene by intestinal symbiotic bacteria isolated from mealworms, the larvae of Tenebrio molitor. Heliyon.				No			2023.0	Optical microscopy;SEM	Polystyrene powder (catalog number: HI-LENE PSP-30, Sinwon Industrial Co., Ltd., Pyeongtaek, Korea) consisted of 95–100% ethenylbenzene homopolymer (CAS No. 9003-53-6), 0–5% general plastic lubricant was provided from Sinwon Industrial Co., Ltd. (Pyeongtaek, Korea). Polystyrene film (catalog number: ST31-FM-000150, GoodFellow, Seoul, Korea) was an additive-free styrene polymer with athickness of 0.05 mm. EPS was sterilized for 10 min at 80 ◦C and cooled at room temperature before feeding. Polystyrene powder wasimmersed in 75% ethanol for 5 min, separated from ethanol using an aspirator and filter paper, and dried sufficiently with UV light on aclean bench before use.	Sinwon Industrial Co., Ltd (powder), GoodFellow (film)		No	Mealworm intestine	Animal associated	Korea	No		
Agrobacterium tumefaciens	358	PS	Park, J. W., Kim, M., Kim, S. Y., Bae, J., & Kim, T. J. (2023). Biodegradation of polystyrene by intestinal symbiotic bacteria isolated from mealworms, the larvae of Tenebrio molitor. Heliyon.				No			2023.0	SEM	Polystyrene powder (catalog number: HI-LENE PSP-30, Sinwon Industrial Co., Ltd., Pyeongtaek, Korea) consisted of 95–100% ethenylbenzene homopolymer (CAS No. 9003-53-6), 0–5% general plastic lubricant was provided from Sinwon Industrial Co., Ltd. (Pyeongtaek, Korea). Polystyrene film (catalog number: ST31-FM-000150, GoodFellow, Seoul, Korea) was an additive-free styrene polymer with athickness of 0.05 mm. EPS was sterilized for 10 min at 80 ◦C and cooled at room temperature before feeding. Polystyrene powder wasimmersed in 75% ethanol for 5 min, separated from ethanol using an aspirator and filter paper, and dried sufficiently with UV light on aclean bench before use.	Sinwon Industrial Co., Ltd (powder), GoodFellow (film)		No	Mealworm intestine	Animal associated	Korea	No		
Pseudomonas plecoglossicida	70775	PS	Park, J. W., Kim, M., Kim, S. Y., Bae, J., & Kim, T. J. (2023). Biodegradation of polystyrene by intestinal symbiotic bacteria isolated from mealworms, the larvae of Tenebrio molitor. Heliyon.				No			2023.0	SEM	Polystyrene powder (catalog number: HI-LENE PSP-30, Sinwon Industrial Co., Ltd., Pyeongtaek, Korea) consisted of 95–100% ethenylbenzene homopolymer (CAS No. 9003-53-6), 0–5% general plastic lubricant was provided from Sinwon Industrial Co., Ltd. (Pyeongtaek, Korea). Polystyrene film (catalog number: ST31-FM-000150, GoodFellow, Seoul, Korea) was an additive-free styrene polymer with athickness of 0.05 mm. EPS was sterilized for 10 min at 80 ◦C and cooled at room temperature before feeding. Polystyrene powder wasimmersed in 75% ethanol for 5 min, separated from ethanol using an aspirator and filter paper, and dried sufficiently with UV light on aclean bench before use.	Sinwon Industrial Co., Ltd (powder), GoodFellow (film)		No	Mealworm intestine	Animal associated	Korea	No		
Serratia marcescens	615	PS	Park, J. W., Kim, M., Kim, S. Y., Bae, J., & Kim, T. J. (2023). Biodegradation of polystyrene by intestinal symbiotic bacteria isolated from mealworms, the larvae of Tenebrio molitor. Heliyon.				No			2023.0	SEM	Polystyrene powder (catalog number: HI-LENE PSP-30, Sinwon Industrial Co., Ltd., Pyeongtaek, Korea) consisted of 95–100% ethenylbenzene homopolymer (CAS No. 9003-53-6), 0–5% general plastic lubricant was provided from Sinwon Industrial Co., Ltd. (Pyeongtaek, Korea). Polystyrene film (catalog number: ST31-FM-000150, GoodFellow, Seoul, Korea) was an additive-free styrene polymer with athickness of 0.05 mm. EPS was sterilized for 10 min at 80 ◦C and cooled at room temperature before feeding. Polystyrene powder wasimmersed in 75% ethanol for 5 min, separated from ethanol using an aspirator and filter paper, and dried sufficiently with UV light on aclean bench before use.	Sinwon Industrial Co., Ltd (powder), GoodFellow (film)		No	Mealworm intestine	Animal associated	Korea	No		
Pseudomonas multiresinivorans	95301	PS	Park, J. W., Kim, M., Kim, S. Y., Bae, J., & Kim, T. J. (2023). Biodegradation of polystyrene by intestinal symbiotic bacteria isolated from mealworms, the larvae of Tenebrio molitor. Heliyon.				No			2023.0	SEM	Polystyrene powder (catalog number: HI-LENE PSP-30, Sinwon Industrial Co., Ltd., Pyeongtaek, Korea) consisted of 95–100% ethenylbenzene homopolymer (CAS No. 9003-53-6), 0–5% general plastic lubricant was provided from Sinwon Industrial Co., Ltd. (Pyeongtaek, Korea). Polystyrene film (catalog number: ST31-FM-000150, GoodFellow, Seoul, Korea) was an additive-free styrene polymer with athickness of 0.05 mm. EPS was sterilized for 10 min at 80 ◦C and cooled at room temperature before feeding. Polystyrene powder wasimmersed in 75% ethanol for 5 min, separated from ethanol using an aspirator and filter paper, and dried sufficiently with UV light on aclean bench before use.	Sinwon Industrial Co., Ltd (powder), GoodFellow (film)		No	Mealworm intestine	Animal associated	Korea	No		
Citrobacter koseri	545	PVC	Nyamjav, I., Jang, Y., Lee, Y. E., & Lee, S. (2023). Biodegradation of polyvinyl chloride by Citrobacter koseri isolated from superworms (Zophobas atratus larvae). Frontiers in Microbiology, 14, 1175249.				No			2023.0	Weight loss;FE-SEM;FTIR;NMR;TGA;HT-GPC	PVC sheets	Goodfellow	Yes	No	Superworm intestine	Animal associated	Korea	No		
Xanthomonas sp.	29446	PET	Kim, J. H., Lee, S. H., Lee, B. M., Son, K. H., & Park, H. Y. (2023). Biodegradation Potential of Polyethylene Terephthalate by the Two Insect Gut Symbionts Xanthomonas sp. HY-74 and Bacillus sp. HY-75. Polymers, 15(17), 3546.				No			2023.0	Clear zone;weight loss;SEM;FTIR;HPLC	PET film cut into 20mm x 10mm x 0.25mm pieces, PET powder	Goodfellow	Yes	No	Bee gut	Animal associated	Korea	No		
Bacillus sp.	1409	PET	Kim, J. H., Lee, S. H., Lee, B. M., Son, K. H., & Park, H. Y. (2023). Biodegradation Potential of Polyethylene Terephthalate by the Two Insect Gut Symbionts Xanthomonas sp. HY-74 and Bacillus sp. HY-75. Polymers, 15(17), 3546.				No			2023.0	Clear zone;weight loss;SEM;FTIR;HPLC	PET film cut into 20mm x 10mm x 0.25mm pieces, PET powder	Goodfellow	Yes	No	Bee gut	Animal associated	Korea	No		
Aspergillus terreus	33178	PP	Samat, A. F., Carter, D., & Abbas, A. (2023). Biodeterioration of pre-treated polypropylene by Aspergillus terreus and Engyodontium album. npj Materials Degradation, 7(1), 28.				No			2023.0	Weight loss;FTIR;SEM	Polypropylene grandules, film, and metalised film	Goodfellow (supplied by Sigma-Aldrich)	Yes	No	Culture collection	Culture collection	Australia	No		
Engyodontium album	37998	PP	Samat, A. F., Carter, D., & Abbas, A. (2023). Biodeterioration of pre-treated polypropylene by Aspergillus terreus and Engyodontium album. npj Materials Degradation, 7(1), 28.				No			2023.0	Weight loss;FTIR;SEM	Polypropylene grandules, film, and metalised film	Goodfellow (supplied by Sigma-Aldrich)	Yes	No	Culture collection	Culture collection	Australia	No		
Pseudoalteromonas sp.	53249	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Pseudoalteromonas sp.	53249	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Pseudoalteromonas sp.	53249	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Pseudoalteromonas sp.	53249	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Pseudoalteromonas sp.	53249	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Pseudoalteromonas sp.	53249	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Pseudoalteromonas sp.	53249	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Photorhabdus luminescens	29488	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Vibrio coralliilyticus	190893	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Enterovibrio sp.	1902814	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Pseudoalteromonas sp.	53249	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
VIbrio sp.	678	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Pseudoalteromonas sp.	53249	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Pseudoalteromonas sp.	53249	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Pseudoalteromonas sp.	53249	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Paraglaciecola sp.	1920173	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
VIbrio sp.	678	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
VIbrio sp.	678	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Shewanella sp.	50422	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
VIbrio sp.	678	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
VIbrio sp.	678	PCL	Galarza–Verkovitch, D., Turak, O., Wiese, J., Rahn, T., Hentschel, U., & Borchert, E. (2023). Bioprospecting for polyesterase activity relevant for PET degradation in marine Enterobacterales isolates. AIMS Microbiology, 9(3), 518-539.				No	 NA		2023.0	Clear zone	PCL-supplemented MB agar plates			No	Culture collection	Culture collection		No		
Stenotrophomonas sp.	69392	PU	Šaraba, V., Milovanovic, J., Nikodinovic-Runic, J., Budin, C., de Boer, T., & Ciric, M. (2023). Brackish groundwaters Contain Plastic-and cellulose-degrading Bacteria. Microbial Ecology, 86(4), 2747-2755.				No			2023.0	Clear zone	A dispersion of impranil  was added directly to MSM plates			No	Groundwater and pellet	Groundwaters	Serbia	No		
Flavobacterium sp.	239	PU	Šaraba, V., Milovanovic, J., Nikodinovic-Runic, J., Budin, C., de Boer, T., & Ciric, M. (2023). Brackish groundwaters Contain Plastic-and cellulose-degrading Bacteria. Microbial Ecology, 86(4), 2747-2755.				No			2023.0	Clear zone	A dispersion of impranil  was added directly to MSM plates			No	Groundwater and pellet	Groundwaters	Serbia	No		
Pantoea sp.	69393	PU	Šaraba, V., Milovanovic, J., Nikodinovic-Runic, J., Budin, C., de Boer, T., & Ciric, M. (2023). Brackish groundwaters Contain Plastic-and cellulose-degrading Bacteria. Microbial Ecology, 86(4), 2747-2755.				No			2023.0	Clear zone	A dispersion of impranil  was added directly to MSM plates			No	Groundwater and pellet	Groundwaters	Serbia	No		
Enterobacter sp.	42895	PU	Šaraba, V., Milovanovic, J., Nikodinovic-Runic, J., Budin, C., de Boer, T., & Ciric, M. (2023). Brackish groundwaters Contain Plastic-and cellulose-degrading Bacteria. Microbial Ecology, 86(4), 2747-2755.				No			2023.0	Clear zone	A dispersion of impranil  was added directly to MSM plates			No	Groundwater and pellet	Groundwaters	Serbia	No		
Pseudomonas sp.	306	PU	Šaraba, V., Milovanovic, J., Nikodinovic-Runic, J., Budin, C., de Boer, T., & Ciric, M. (2023). Brackish groundwaters Contain Plastic-and cellulose-degrading Bacteria. Microbial Ecology, 86(4), 2747-2755.				No			2023.0	Clear zone	A dispersion of impranil  was added directly to MSM plates			No	Groundwater and pellet	Groundwaters	Serbia	No		
Serratia sp.	306	PU	Šaraba, V., Milovanovic, J., Nikodinovic-Runic, J., Budin, C., de Boer, T., & Ciric, M. (2023). Brackish groundwaters Contain Plastic-and cellulose-degrading Bacteria. Microbial Ecology, 86(4), 2747-2755.				No			2023.0	Clear zone	A dispersion of impranil  was added directly to MSM plates			No	Groundwater and pellet	Groundwaters	Serbia	No		
Acinetobacter sp.	472	PU	Šaraba, V., Milovanovic, J., Nikodinovic-Runic, J., Budin, C., de Boer, T., & Ciric, M. (2023). Brackish groundwaters Contain Plastic-and cellulose-degrading Bacteria. Microbial Ecology, 86(4), 2747-2755.				No			2023.0	Clear zone	A dispersion of impranil  was added directly to MSM plates			No	Groundwater and pellet	Groundwaters	Serbia	No		
Proteus sp.	472	PU	Šaraba, V., Milovanovic, J., Nikodinovic-Runic, J., Budin, C., de Boer, T., & Ciric, M. (2023). Brackish groundwaters Contain Plastic-and cellulose-degrading Bacteria. Microbial Ecology, 86(4), 2747-2755.				No			2023.0	Clear zone	A dispersion of impranil  was added directly to MSM plates			No	Groundwater and pellet	Groundwaters	Serbia	No		
Proteus mirabilis	584	LDPE	Akhigbe, G. E., EnochOghene, A. E., Olumurewa, K. O., Koleoso, O. B., & Ogbonna, N. D. (2023). Characterization of low-density polyethylene (LDPE) films degraded using bacteria strains isolated from oil-contaminated soil. Environmental Technology, 1-7.				No			2023.0	Weight loss;FE-SEM;EDX	Commercial grade LDPE 'ziploc bags' 		No	No	Soil	Oil spillage site	Nigeria	No		
Proteus mirabilis	584	LDPE	Akhigbe, G. E., EnochOghene, A. E., Olumurewa, K. O., Koleoso, O. B., & Ogbonna, N. D. (2023). Characterization of low-density polyethylene (LDPE) films degraded using bacteria strains isolated from oil-contaminated soil. Environmental Technology, 1-7.				No			2023.0	Weight loss;FE-SEM;EDX	Commercial grade LDPE 'ziploc bags' 		No	No	Soil	Oil spillage site	Nigeria	No		
Cladosporium cladosporioides	29917	LDPE	Puliga, F., Zuffi, V., Baldo, D., Cavatorta, D., Zambonelli, A., Francioso, O., & Sanchez-Cortes, S. (2023). Cladosporium cladosporioides (strain Clc/1): a candidate for low-density polyethylene degradation. Chemical and Biological Technologies in Agriculture, 10(1), 1-11.				No			2023.0	SEM;ATR-FTIR;Raman;SERS	an LDPE film (6 μm thick, 6 g/m2) was cut into discs about 5.5 cm in diameter and sterilized at 121 °C for 20 min. After sterilization, the LDPE discs were inserted inside ster- ile Petri dishes 6 cm in diameter. 			No	Plastic debris	Soil	Italy	No		
Brevibacillus parabrevis	54914	HDPE	Gupta, K. K., Chandra, H., Sagar, K., Sharma, K. K., & Devi, D. (2023). Degradation of high density polyethylene (HDPE) through bacterial strain from Cow faeces. Biocatalysis and Agricultural Biotechnology, 48, 102646.				No			2023.0	Weight loss;FE-SEM;EDX;FTIR;GCMS	Films were cut into small pieces (dimension 1 × 1 cm), immersed in xylene, and boiled for 5–15 min to dissolve completely. The resulting residue was crushed followed by washing with ethanol 2–3 times to eliminate residual xylene. The polyethylene powder thus ob- tained was kept for ethanol evaporation and then dried at 60 °C overnight in a hot air oven	Uttarakhand Packaging Industries Haridwar 	No	No	Cow dung		India	No		
Rhodococcus sp.	54914	LDPE	Rong, Z., Ding, Z. H., Wu, Y. H., & Xu, X. W. (2024). Degradation of low-density polyethylene by the bacterium Rhodococcus sp. C-2 isolated from seawater. Science of The Total Environment, 907, 167993.	Glutathione peroxidase			No			2023.0	SEM;AFM;Weight loss;HT-GPC;Tensile strength;ATR-FTIR;GCMS	LDPE films	Good Fellow Company	Yes	No	Seawater and sediment	Marine	China	No		
Rhodococcus sp.	54914	LDPE	Rong, Z., Ding, Z. H., Wu, Y. H., & Xu, X. W. (2024). Degradation of low-density polyethylene by the bacterium Rhodococcus sp. C-2 isolated from seawater. Science of The Total Environment, 907, 167993.	Non-heme chloroperoxidase			No			2023.0	SEM;AFM;Weight loss;HT-GPC;Tensile strength;ATR-FTIR;GCMS	LDPE films	Good Fellow Company	Yes	No	Seawater and sediment	Marine	China	No		
Rhodococcus sp.	54914	LDPE	Rong, Z., Ding, Z. H., Wu, Y. H., & Xu, X. W. (2024). Degradation of low-density polyethylene by the bacterium Rhodococcus sp. C-2 isolated from seawater. Science of The Total Environment, 907, 167993.	Alkane hydroxylase			No			2023.0	SEM;AFM;Weight loss;HT-GPC;Tensile strength;ATR-FTIR;GCMS	LDPE films	Good Fellow Company	Yes	No	Seawater and sediment	Marine	China	No		
Rhodococcus sp.	54914	LDPE	Rong, Z., Ding, Z. H., Wu, Y. H., & Xu, X. W. (2024). Degradation of low-density polyethylene by the bacterium Rhodococcus sp. C-2 isolated from seawater. Science of The Total Environment, 907, 167993.	Alcohol dehydrogenase			No			2023.0	SEM;AFM;Weight loss;HT-GPC;Tensile strength;ATR-FTIR;GCMS	LDPE films	Good Fellow Company	Yes	No	Seawater and sediment	Marine	China	No		
Rhodococcus sp.	54914	LDPE	Rong, Z., Ding, Z. H., Wu, Y. H., & Xu, X. W. (2024). Degradation of low-density polyethylene by the bacterium Rhodococcus sp. C-2 isolated from seawater. Science of The Total Environment, 907, 167993.	Aldehyde dehydrogenase			No			2023.0	SEM;AFM;Weight loss;HT-GPC;Tensile strength;ATR-FTIR;GCMS	LDPE films	Good Fellow Company	Yes	No	Seawater and sediment	Marine	China	No		
Brevibacillus brevis	1393	PE	Tiwari, N., Santhiya, D., & Sharma, J. G. (2023). Degradation of polyethylene microplastics through microbial action by a soil isolate of Brevibacillus brevis. Polymer Degradation and Stability, 215, 110436.	Laccase			No			2023.0	Weight loss;HPLC;SEM;DSC;TGA;XRD;FTIR	Polyethylene (ultra-high molecular weight) 40–48 µm particle size		Yes	No	Soil	Soil	India	No		
Trichoderma harzianum	5544	PE	Ruan, Y., Hu, F., Zhao, J., Li, Y., Ling, J., Cao, J., & Zhang, L. (2023). Degradation of polyethylene particles by Trichoderma harzianum and recombinant laccase cloned from the strain. Journal of Applied Polymer Science, 140(43), e54599.	Laccase			No			2023.0	Weight loss;SEM;FTIR;GCMS	Polyethylene film (60 μm thick, white, high density) and PE particles (355 μm and 160 μm in diameter, white, density 0.918 g/cm2, melting rate 2 g/10 min, tensile yield strength 100kg/cm2, and tensile breaking strength 260 kg/cm2) PE particles (355 μm and 160 μm in diameter, white, den- sity 0.918 g/cm2, melting rate 2 g/10 min, tensile yield strength 100kg/cm2, and tensile breaking strength 260 kg/cm2)	Feihong Plastic		No	Soil	Plastic-waste contaminated soil	China	No		
Coniochaeta hoffmannii	91930	PP	Porter, R., Černoša, A., Fernández-Sanmartín, P., Cortizas, A. M., Aranda, E., Luo, Y., ... & Gostinčar, C. (2023). Degradation of polypropylene by fungi Coniochaeta hoffmannii and Pleurostoma richardsiae. Microbiological research, 277, 127507.				No			2023.0	SEM;NMR;FTIR-ATR	Pure polymer PP films (thickness of 0.012 mm; GoodFellow, United Kingdom) were cut into 1 cm2 pieces and then sterilized in 96% ethanol for 15 min. After sterilization, the remaining ethanol was removed, and the films were dried at 37 ◦C. The PP film pieces were placed on M9 medium without any carbon source.	Good Fellow	Yes	No	Cotton swabs	Hydrocarbon-contaminated environments	Slovenia	No		
Pleurostoma richardsiae	41990	PP	Porter, R., Černoša, A., Fernández-Sanmartín, P., Cortizas, A. M., Aranda, E., Luo, Y., ... & Gostinčar, C. (2023). Degradation of polypropylene by fungi Coniochaeta hoffmannii and Pleurostoma richardsiae. Microbiological research, 277, 127507.				No			2023.0	SEM;NMR;FTIR-ATR	Pure polymer PP films (thickness of 0.012 mm; GoodFellow, United Kingdom) were cut into 1 cm2 pieces and then sterilized in 96% ethanol for 15 min. After sterilization, the remaining ethanol was removed, and the films were dried at 37 ◦C. The PP film pieces were placed on M9 medium without any carbon source.	Good Fellow	Yes	No	Cotton swabs	Hydrocarbon-contaminated environments	Slovenia	No		
Clonostachys sp.	1756104	PU	Bhavsar, P., Bhave, M., & Webb, H. K. (2024). Effective multi-stage biodegradation of commercial bulk polyurethane by Clonostachys and Purpureocillium spp. Science of The Total Environment, 908, 168329.				No			2023.0	Weight loss:FTIR;XPS;LCMS	Two different types of PU were used in this study. Impranil® DLN W 50, an anionic aliphatic polyester-polyurethane dispersion, was obtained from Connell Brothers, Australia. Solid polyester-polyurethane sheet (40a shore hardness) was purchased from Elastomers Queensland, Australia. This solid PU came as a 300 ×300 ×3 mm sheet. Small pieces weighing 30 to 80 mg were cut from the larger sheet, sterilized with 70 % ethanol for 20 min and dried before use.	Connell Brothers (Impranil), Elastomers Queensland (PU sheet)		No	Soil	Landfill	Australia	No		
Purpureocillium sp.	1926681	PU	Bhavsar, P., Bhave, M., & Webb, H. K. (2024). Effective multi-stage biodegradation of commercial bulk polyurethane by Clonostachys and Purpureocillium spp. Science of The Total Environment, 908, 168329.				No			2023.0	Weight loss:FTIR;XPS;LCMS	Two different types of PU were used in this study. Impranil® DLN W 50, an anionic aliphatic polyester-polyurethane dispersion, was obtained from Connell Brothers, Australia. Solid polyester-polyurethane sheet (40a shore hardness) was purchased from Elastomers Queensland, Australia. This solid PU came as a 300 ×300 ×3 mm sheet. Small pieces weighing 30 to 80 mg were cut from the larger sheet, sterilized with 70 % ethanol for 20 min and dried before use.	Connell Brothers (Impranil), Elastomers Queensland (PU sheet)		No	Soil	Landfill	Australia	No		
Brevundimonas sp.	1871086	PS	Tang, P. M., Habib, S., Shukor, M. Y. A., Alias, S. A., Smykla, J., & Yasid, N. A. (2023). Evaluation of the deterioration of untreated commercial polystyrene by Psychrotrophic Antarctic Bacterium. Polymers, 15(8), 1841.				No			2023.0	Weight loss;FTIR;SEM	PS microplastics were prepared by grating the commercial PS product (Greiner Bio-One GmbH, Frickenhausen, Germany; Lot No: E10090MX) obtained from the plastic-producing industry using a steel file. The grated plastics were then filtered through a sieve with a mesh size of 0.3 mm.	Greiner Bio-One GmbH	No	No	Soil	Soil	Antarctica	No		
Dermacpccis sp.	1871086	PS	Tang, P. M., Habib, S., Shukor, M. Y. A., Alias, S. A., Smykla, J., & Yasid, N. A. (2023). Evaluation of the deterioration of untreated commercial polystyrene by Psychrotrophic Antarctic Bacterium. Polymers, 15(8), 1841.				No			2023.0	Weight loss	PS microplastics were prepared by grating the commercial PS product (Greiner Bio-One GmbH, Frickenhausen, Germany; Lot No: E10090MX) obtained from the plastic-producing industry using a steel file. The grated plastics were then filtered through a sieve with a mesh size of 0.3 mm.		No	No	Soil	Soil	Antarctica	No		
Enterobacter hormaechei	158836	LLDPE	Sun, W., Zhang, Y., Zhang, H., Wu, H., Liu, Q., Yang, F., Hou, M., Qi, Y., & Zhang, W. (2024). Exploitation of Enterobacter hormaechei for biodegradation of multiple plastics. Science of The Total Environment, 907, 167708.				No			2023.0	Weight loss;SEM;FTIR;XPS;WCA;XRD	The plastics were cut into rectangular pieces of 3.0 cm ×2.0 cm to perform cultivation experiments. All films were rinsed 3–5 times with ultrapure water, then immersed in 75 % ethanol before being transferred to ethanol to sonicate for 30 min. Then they were flushed 3 times with deionized water to remove ethanol and final UV irradiation for 4 h after blotting the surface with sterile gauze. 	Lanzhou Jindi Plastic Products Co., Ltd		No	Soil	Plastic-waste contaminated soil	China	No		
Enterobacter hormaechei	158836	HDPE	Sun, W., Zhang, Y., Zhang, H., Wu, H., Liu, Q., Yang, F., Hou, M., Qi, Y., & Zhang, W. (2024). Exploitation of Enterobacter hormaechei for biodegradation of multiple plastics. Science of The Total Environment, 907, 167708.				No			2023.0	Weight loss;SEM;FTIR;XPS;WCA;XRD	The plastics were cut into rectangular pieces of 3.0 cm ×2.0 cm to perform cultivation experiments. All films were rinsed 3–5 times with ultrapure water, then immersed in 75 % ethanol before being transferred to ethanol to sonicate for 30 min. Then they were flushed 3 times with deionized water to remove ethanol and final UV irradiation for 4 h after blotting the surface with sterile gauze.	PetroChina Lanzhou Petrochemical Company		No	Soil	Plastic-waste contaminated soil	China	No		
Enterobacter hormaechei	158836	PVC	Sun, W., Zhang, Y., Zhang, H., Wu, H., Liu, Q., Yang, F., Hou, M., Qi, Y., & Zhang, W. (2024). Exploitation of Enterobacter hormaechei for biodegradation of multiple plastics. Science of The Total Environment, 907, 167708.				No			2023.0	Weight loss;SEM;FTIR;XPS;WCA;XRD	Commercial PVC - The plastics were cut into rectangular pieces of 3.0 cm ×2.0 cm to perform cultivation experiments. All films were rinsed 3–5 times with ultrapure water, then immersed in 75 % ethanol before being transferred to ethanol to sonicate for 30 min. Then they were flushed 3 times with deionized water to remove ethanol and final UV irradiation for 4 h after blotting the surface with sterile gauze.		No	No	Soil	Plastic-waste contaminated soil	China	No		
Enterobacter hormaechei	158836	PP	Sun, W., Zhang, Y., Zhang, H., Wu, H., Liu, Q., Yang, F., Hou, M., Qi, Y., & Zhang, W. (2024). Exploitation of Enterobacter hormaechei for biodegradation of multiple plastics. Science of The Total Environment, 907, 167708.				No			2023.0	Weight loss;SEM;FTIR;XPS;WCA;XRD	Commercial PP - The plastics were cut into rectangular pieces of 3.0 cm ×2.0 cm to perform cultivation experiments. All films were rinsed 3–5 times with ultrapure water, then immersed in 75 % ethanol before being transferred to ethanol to sonicate for 30 min. Then they were flushed 3 times with deionized water to remove ethanol and final UV irradiation for 4 h after blotting the surface with sterile gauze.		No	No	Soil	Plastic-waste contaminated soil	China	No		
Enterobacter hormaechei	158836	PBAT	Sun, W., Zhang, Y., Zhang, H., Wu, H., Liu, Q., Yang, F., Hou, M., Qi, Y., & Zhang, W. (2024). Exploitation of Enterobacter hormaechei for biodegradation of multiple plastics. Science of The Total Environment, 907, 167708.				No			2023.0	Weight loss;SEM;FTIR;XPS;WCA;XRD	Commercial PBAT - The plastics were cut into rectangular pieces of 3.0 cm ×2.0 cm to perform cultivation experiments. All films were rinsed 3–5 times with ultrapure water, then immersed in 75 % ethanol before being transferred to ethanol to sonicate for 30 min. Then they were flushed 3 times with deionized water to remove ethanol and final UV irradiation for 4 h after blotting the surface with sterile gauze.		No	No	Soil	Plastic-waste contaminated soil	China	No		
Bacillus thuringiensis	1428	PE	Yun, S. D., Lee, C. O., Kim, H. W., An, S. J., Kim, S., Seo, M. J., Park, C., Yun, C.-H., Chi, W. S., & Yeom, S. J. (2023). Exploring a new biocatalyst from Bacillus thuringiensis JNU01 for polyethylene biodegradation. Environmental Science & Technology Letters, 10(6), 485-492.				No			2023.0	DO;GCMS;FTIR;NMR;XPS	PE  was  re-precipitated  to  increase  the  external  surface  area  by  using  the  following method: PE (20 g) and chloroform (300 mL) were mixed in a 500 mL round bottom flask. The solution mixture in the flask was vigorously stirred at 55 °C overnight to completely dissolve the  PE  powder.  Then,  the  PE  solution  was  poured  into  a  beaker  containing  methanol  to  re-precipitate PE samples by forming fine powders. The resultant PE product was filtered using vacuum filtration and dried in a vacuum oven at 60 °C for 24 h to remove the residual solvent, and then we used it as sole carbon source and control. The  PE  film  was  fabricated  using  a  solvent  evaporation  method  as  follows:  Re-precipitated PE (0.3 g) sample was dissolved in heptane (6 mL) at 70 °C overnight to form a homogeneous solution. The PE solution was poured into Teflon dishes, which were covered using aluminum foils. Of note, the aluminum foil had a few small holes to allow slow solvent evaporation. The Teflon dishes, covered by aluminum foil, were placed horizontally in an oven at 70 °C overnight to produce a uniform PE film. The PE films were detached from the Teflon dishes and further dried in a vacuum oven at 70 °C for 24 h to completely remove the residual solvent	Sigma-Aldrich	Yes	No	Soil	Landfill		No		
Bacillus pumilus	1408	PCL	Shin, N., Kim, S. H., Cho, J. Y., Hwang, J. H., Kim, H. J., Oh, S. J., Park, S. -H., Park, K., Bhatia, S. H.,  & Yang, Y. H. (2023). Fast Degradation of Polycaprolactone/Poly (Butylene Adipate-Co-Terephthalate) Blends by Novel Bacillus Strain NR4 with Broad Degrading Activity. Journal of Polymers and the Environment, 1-15.	Esterase			No			2023.0	Clear zone;GCMS;GPC;SEM;FTIR	1 g of bioplastic pellets was dissolved in 40 mL dichloromethane (DCM) in a water bath at 60 °C for 1 h. The pellets were diluted in 100 mL water; then, 2 mL of 2% Sarkosyl NL was added to the boundary between water and DCM. The mixture was sonicated using a Vibra-Cell VCX500 (Sonics & Materials, Inc., Newtown, CT, USA) with 15 s of pulsing at an amplitude of 40% for 10 min. Next, 1 g/L of plastic emulsion, uniformly dissolved in the aqueous phase of the solvent, was added to the marine broth (MB; Difco Laboratories, Detroit, MI, USA) contain- ing peptone (5.0 g/L), yeast extract (1.0 g/L), ferric citrate (0.1 g/L), sodium chloride (19.45 g/L), magnesium chloride (5.9 g/L), magnesium sulfate (3.24 g/L), calcium chloride (1.8 g/L), potassium chloride (0.55 g/L), sodium bicarbonate (0.16 g/L), potassium bromide (0.08 g/L), strontium chlo- ride (34.0 mg/L), boric acid (22.0 mg/L), sodium silicate (4.0 mg/L), sodium fluoride (2.4 mg/L), ammonium nitrate (1.6 mg/L), disodium phosphate (8.0 mg/L), and 2% agarose. All mixtures were then autoclaved for 15 min at 121 °C.	Sigma-Aldrich	Yes	Yes	Soil	Mairne	South Korea	No		
Terribacillus saccharophilus	361277	PCL	Shin, N., Kim, S. H., Cho, J. Y., Hwang, J. H., Kim, H. J., Oh, S. J., Park, S. -H., Park, K., Bhatia, S. H.,  & Yang, Y. H. (2023). Fast Degradation of Polycaprolactone/Poly (Butylene Adipate-Co-Terephthalate) Blends by Novel Bacillus Strain NR4 with Broad Degrading Activity. Journal of Polymers and the Environment, 1-15.	Esterase			No			2023.0	Clear zone;GCMS	1 g of bioplastic pellets was dissolved in 40 mL dichloromethane (DCM) in a water bath at 60 °C for 1 h. The pellets were diluted in 100 mL water; then, 2 mL of 2% Sarkosyl NL was added to the boundary between water and DCM. The mixture was sonicated using a Vibra-Cell VCX500 (Sonics & Materials, Inc., Newtown, CT, USA) with 15 s of pulsing at an amplitude of 40% for 10 min. Next, 1 g/L of plastic emulsion, uniformly dissolved in the aqueous phase of the solvent, was added to the marine broth (MB; Difco Laboratories, Detroit, MI, USA) contain- ing peptone (5.0 g/L), yeast extract (1.0 g/L), ferric citrate (0.1 g/L), sodium chloride (19.45 g/L), magnesium chloride (5.9 g/L), magnesium sulfate (3.24 g/L), calcium chloride (1.8 g/L), potassium chloride (0.55 g/L), sodium bicarbonate (0.16 g/L), potassium bromide (0.08 g/L), strontium chlo- ride (34.0 mg/L), boric acid (22.0 mg/L), sodium silicate (4.0 mg/L), sodium fluoride (2.4 mg/L), ammonium nitrate (1.6 mg/L), disodium phosphate (8.0 mg/L), and 2% agarose. All mixtures were then autoclaved for 15 min at 121 °C.	Sigma-Aldrich	Yes	No	Soil	Mairne	South Korea	No		
Bacillus subtilis	1423	PCL	Shin, N., Kim, S. H., Cho, J. Y., Hwang, J. H., Kim, H. J., Oh, S. J., Park, S. -H., Park, K., Bhatia, S. H.,  & Yang, Y. H. (2023). Fast Degradation of Polycaprolactone/Poly (Butylene Adipate-Co-Terephthalate) Blends by Novel Bacillus Strain NR4 with Broad Degrading Activity. Journal of Polymers and the Environment, 1-15.				No			2023.0	Clear zone;GCMS	1 g of bioplastic pellets was dissolved in 40 mL dichloromethane (DCM) in a water bath at 60 °C for 1 h. The pellets were diluted in 100 mL water; then, 2 mL of 2% Sarkosyl NL was added to the boundary between water and DCM. The mixture was sonicated using a Vibra-Cell VCX500 (Sonics & Materials, Inc., Newtown, CT, USA) with 15 s of pulsing at an amplitude of 40% for 10 min. Next, 1 g/L of plastic emulsion, uniformly dissolved in the aqueous phase of the solvent, was added to the marine broth (MB; Difco Laboratories, Detroit, MI, USA) contain- ing peptone (5.0 g/L), yeast extract (1.0 g/L), ferric citrate (0.1 g/L), sodium chloride (19.45 g/L), magnesium chloride (5.9 g/L), magnesium sulfate (3.24 g/L), calcium chloride (1.8 g/L), potassium chloride (0.55 g/L), sodium bicarbonate (0.16 g/L), potassium bromide (0.08 g/L), strontium chlo- ride (34.0 mg/L), boric acid (22.0 mg/L), sodium silicate (4.0 mg/L), sodium fluoride (2.4 mg/L), ammonium nitrate (1.6 mg/L), disodium phosphate (8.0 mg/L), and 2% agarose. All mixtures were then autoclaved for 15 min at 121 °C.	Sigma-Aldrich	Yes	No	Soil	Mairne	South Korea	No		
Lactobacillus paracasei	1597	PCL	Shin, N., Kim, S. H., Cho, J. Y., Hwang, J. H., Kim, H. J., Oh, S. J., Park, S. -H., Park, K., Bhatia, S. H.,  & Yang, Y. H. (2023). Fast Degradation of Polycaprolactone/Poly (Butylene Adipate-Co-Terephthalate) Blends by Novel Bacillus Strain NR4 with Broad Degrading Activity. Journal of Polymers and the Environment, 1-15.				No			2023.0	Clear zone;GCMS	1 g of bioplastic pellets was dissolved in 40 mL dichloromethane (DCM) in a water bath at 60 °C for 1 h. The pellets were diluted in 100 mL water; then, 2 mL of 2% Sarkosyl NL was added to the boundary between water and DCM. The mixture was sonicated using a Vibra-Cell VCX500 (Sonics & Materials, Inc., Newtown, CT, USA) with 15 s of pulsing at an amplitude of 40% for 10 min. Next, 1 g/L of plastic emulsion, uniformly dissolved in the aqueous phase of the solvent, was added to the marine broth (MB; Difco Laboratories, Detroit, MI, USA) contain- ing peptone (5.0 g/L), yeast extract (1.0 g/L), ferric citrate (0.1 g/L), sodium chloride (19.45 g/L), magnesium chloride (5.9 g/L), magnesium sulfate (3.24 g/L), calcium chloride (1.8 g/L), potassium chloride (0.55 g/L), sodium bicarbonate (0.16 g/L), potassium bromide (0.08 g/L), strontium chlo- ride (34.0 mg/L), boric acid (22.0 mg/L), sodium silicate (4.0 mg/L), sodium fluoride (2.4 mg/L), ammonium nitrate (1.6 mg/L), disodium phosphate (8.0 mg/L), and 2% agarose. All mixtures were then autoclaved for 15 min at 121 °C.	Sigma-Aldrich	Yes	No	Soil	Mairne	South Korea	No		
Bacillus pumilus	1408	P(3HB-co-4HB)	Shin, N., Kim, S. H., Cho, J. Y., Hwang, J. H., Kim, H. J., Oh, S. J., Park, S. -H., Park, K., Bhatia, S. H.,  & Yang, Y. H. (2023). Fast Degradation of Polycaprolactone/Poly (Butylene Adipate-Co-Terephthalate) Blends by Novel Bacillus Strain NR4 with Broad Degrading Activity. Journal of Polymers and the Environment, 1-15.	Esterase			No			2023.0	Clear zone	1 g of bioplastic pellets was dissolved in 40 mL dichloromethane (DCM) in a water bath at 60 °C for 1 h. The pellets were diluted in 100 mL water; then, 2 mL of 2% Sarkosyl NL was added to the boundary between water and DCM. The mixture was sonicated using a Vibra-Cell VCX500 (Sonics & Materials, Inc., Newtown, CT, USA) with 15 s of pulsing at an amplitude of 40% for 10 min. Next, 1 g/L of plastic emulsion, uniformly dissolved in the aqueous phase of the solvent, was added to the marine broth (MB; Difco Laboratories, Detroit, MI, USA) contain- ing peptone (5.0 g/L), yeast extract (1.0 g/L), ferric citrate (0.1 g/L), sodium chloride (19.45 g/L), magnesium chloride (5.9 g/L), magnesium sulfate (3.24 g/L), calcium chloride (1.8 g/L), potassium chloride (0.55 g/L), sodium bicarbonate (0.16 g/L), potassium bromide (0.08 g/L), strontium chlo- ride (34.0 mg/L), boric acid (22.0 mg/L), sodium silicate (4.0 mg/L), sodium fluoride (2.4 mg/L), ammonium nitrate (1.6 mg/L), disodium phosphate (8.0 mg/L), and 2% agarose. All mixtures were then autoclaved for 15 min at 121 °C.	CJ	Yes	Yes	Soil	Mairne	South Korea	No		
Bacillus pumilus	1408	PBAT	Shin, N., Kim, S. H., Cho, J. Y., Hwang, J. H., Kim, H. J., Oh, S. J., Park, S. -H., Park, K., Bhatia, S. H.,  & Yang, Y. H. (2023). Fast Degradation of Polycaprolactone/Poly (Butylene Adipate-Co-Terephthalate) Blends by Novel Bacillus Strain NR4 with Broad Degrading Activity. Journal of Polymers and the Environment, 1-15.	Esterase			No			2023.0	Clear zone	1 g of bioplastic pellets was dissolved in 40 mL dichloromethane (DCM) in a water bath at 60 °C for 1 h. The pellets were diluted in 100 mL water; then, 2 mL of 2% Sarkosyl NL was added to the boundary between water and DCM. The mixture was sonicated using a Vibra-Cell VCX500 (Sonics & Materials, Inc., Newtown, CT, USA) with 15 s of pulsing at an amplitude of 40% for 10 min. Next, 1 g/L of plastic emulsion, uniformly dissolved in the aqueous phase of the solvent, was added to the marine broth (MB; Difco Laboratories, Detroit, MI, USA) contain- ing peptone (5.0 g/L), yeast extract (1.0 g/L), ferric citrate (0.1 g/L), sodium chloride (19.45 g/L), magnesium chloride (5.9 g/L), magnesium sulfate (3.24 g/L), calcium chloride (1.8 g/L), potassium chloride (0.55 g/L), sodium bicarbonate (0.16 g/L), potassium bromide (0.08 g/L), strontium chlo- ride (34.0 mg/L), boric acid (22.0 mg/L), sodium silicate (4.0 mg/L), sodium fluoride (2.4 mg/L), ammonium nitrate (1.6 mg/L), disodium phosphate (8.0 mg/L), and 2% agarose. All mixtures were then autoclaved for 15 min at 121 °C.	ANKOR Bioplastics Co., Ltd	Yes	Yes	Soil	Mairne	South Korea	No		
Pseudomonas putida	303	LDPE	Ji, S. H., Seok, D. C., & Yoo, S. (2023). Improved biodegradability of low-density polyethylene using plasma pretreatment and plastic-degrading bacteria. Environmental Technology & Innovation, 32, 103449.				No			2023.0	AFM;SEM;FTIR;XPS;TGA	The LDPE film used in this study was a 0.02-mm mulching film treated with chemical coating (Ace Agricultural Materials, Korea).Before use, the LDPE film was washed with 70% ethanol and sterile water and then air-dried on a clean bench. LDPE films were cut into50 mm ×50 mm pieces and placed in MSM inoculated with bacteria.	Ace Agricultural Materials	No	No	Culture collection	Culture collection	South Korea	No		
Klebsiella pneumonia	303	PET	 Mukhaifi, E. A., Al-Atbi, H. S., & Ali, S. F. (2023). Isolation and Identification of Polyethylene Terephthalate Degrading Bacteria from Shatt Al-Arab and Sewage Water of Basrah City. Baghdad Science Journal, 20(5 (Suppl.)).				No			2023.0	Weight loss	Drinking water bottles		No	No	Water/sewage	Sewage	Iraq	No		
Acinetobacter guillouiae	106649	PE	Riabi, H. R. A., Mohammadzadeh, A., Mirzahosseini, S. A. H., Chahak, A. F., & Imani, J. (2023). Isolation of the Gut Microbiome of Galleria mellonella Sp.(Lepidoptera: Pyralidae) Larvae and Its Role in the Digestion of Polyethylene Plastic. Water, Air, & Soil Pollution, 234(8), 523.				No			2023.0	DCPIP;weight loss;SEM;XPS;ATR-FTIR;WCA	To screen for plastic-degrading bacteria, candidates were selected based on bacterial cultivation in liquid carbon free basal medium (LCFBM) as minimal medium with 8 g/L of PE (Mw ~4,000 and Mn ~1,700, Sigma-Aldrich, Burlington, MA, USA) and 10 mg/L of DCPIP (Sigma-Aldrich, Burlington, MA, USA) as the sole carbon source and electron acceptor, respectively. The medium (pH 6.8) consisted of 0.7 g KH2PO4, 0.7 g K2HPO4, 0.7 g MgSO4⋅7H2O, 1 g NH4NO3, 0.005 g NaCl, and 0.002 g FeSO4⋅7H2O per 1 L, as described previously [10], with 1 mL of 100-fold trace mineral stock solution (0.3 g H3BO3, 0.2 g CoCl2⋅6H2O, 0.1 g ZnSO4⋅7H2O, 0.03 g MnCl2⋅4H2O, 0.03 NaMoO4⋅2H2O, 0.02 g NiCl2⋅6H2O, and 0.01 g CuSO4⋅5H2O per 1 L). The medium and PE were sterilized in an autoclave and UV-C sterilizer, respectively, before use. Each bacterial cell was precultured in LB broth for 24 h under aerobic conditions until a cell density with optical density (OD)600 =1 (approximately 108− 9 cells/mL) was reached. Cell pellets were collected by centrifugation (13,000 rpm and 4 ◦C) and washed twice with 0.9% sterile saline solution to remove nutrients retained from the LB broth for inoculum preparation. Finally, the washed pellets were resuspended in 1 mL of LCFBM broth. 	Sigma Aldrich	Yes	No	Superworm intestine	Animal associated	South Korea	No		
Acinetobacter guillouiae	106649	PE	Riabi, H. R. A., Mohammadzadeh, A., Mirzahosseini, S. A. H., Chahak, A. F., & Imani, J. (2023). Isolation of the Gut Microbiome of Galleria mellonella Sp.(Lepidoptera: Pyralidae) Larvae and Its Role in the Digestion of Polyethylene Plastic. Water, Air, & Soil Pollution, 234(8), 523.				No			2023.0	DCPIP	To screen for plastic-degrading bacteria, candidates were selected based on bacterial cultivation in liquid carbon free basal medium (LCFBM) as minimal medium with 8 g/L of PE (Mw ~4,000 and Mn ~1,700, Sigma-Aldrich, Burlington, MA, USA) and 10 mg/L of DCPIP (Sigma-Aldrich, Burlington, MA, USA) as the sole carbon source and electron acceptor, respectively. The medium (pH 6.8) consisted of 0.7 g KH2PO4, 0.7 g K2HPO4, 0.7 g MgSO4⋅7H2O, 1 g NH4NO3, 0.005 g NaCl, and 0.002 g FeSO4⋅7H2O per 1 L, as described previously [10], with 1 mL of 100-fold trace mineral stock solution (0.3 g H3BO3, 0.2 g CoCl2⋅6H2O, 0.1 g ZnSO4⋅7H2O, 0.03 g MnCl2⋅4H2O, 0.03 NaMoO4⋅2H2O, 0.02 g NiCl2⋅6H2O, and 0.01 g CuSO4⋅5H2O per 1 L). The medium and PE were sterilized in an autoclave and UV-C sterilizer, respectively, before use. Each bacterial cell was precultured in LB broth for 24 h under aerobic conditions until a cell density with optical density (OD)600 =1 (approximately 108− 9 cells/mL) was reached. Cell pellets were collected by centrifugation (13,000 rpm and 4 ◦C) and washed twice with 0.9% sterile saline solution to remove nutrients retained from the LB broth for inoculum preparation. Finally, the washed pellets were resuspended in 1 mL of LCFBM broth. 	Sigma Aldrich	Yes	No	Superworm intestine	Animal associated	South Korea	No		
Pseudoalteromonas sp.	53249	Nylon	Saito, Y., Honda, M., Yamashita, T., Furuno, Y., Kato, D. I., Abe, H., & Yamada, M. (2023). Marine bacterial enzyme degrades polyamide 4 into gamma-aminobutyric acid oligomers. Polymer Degradation and Stability, 215, 110446.				No			2023.0	Clear zone;LCMS	PA4 was synthesized as previously reported [26]. Ring-opening polymerization of 2PRN was carried out using isophthaloyl dichloride and sodium as the initiator and catalyst, respectively. The molecular mass of the polymerized PA4 was estimated to be Mn =12,000, with Mw/Mn =1.4, using analytical gel permeation chromatography	NA (lab synthesised)	Yes	No	Plastic surface	Mairne	Japan	No		
Alternaria burnsii	1187904	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Microbial degradation of low-density polyethylene by Neopestalotiopsis phangngaensis. The Journal of General and Applied Microbiology, 68(6), 287-294.				No			2023.0	Weight loss;tensile strength	Five millimeters nominal size of white amorphous LDPE microplastic granules were used for biodegradability assessment. Each LDPE sheet 1.0 cm × 4.0 cm) with a thickness of 0.11 mm was pre- pared according to a modified method (Khruengsai et al., 2021). They were washed with water, sterilized with 70 % ethanol, and air-drying. The dry sheets were kept inside the desiccator until use. The weight of the dried LDPE sheet was recorded as the initial weight.			No	Culture collection	Culture collection	Thailand	No		
Alternaria pseudoeichhorniae	2507055	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Microbial degradation of low-density polyethylene by Neopestalotiopsis phangngaensis. The Journal of General and Applied Microbiology, 68(6), 287-294.				No			2023.0	Weight loss;tensile strength	Five millimeters nominal size of white amorphous LDPE microplastic granules were used for biodegradability assessment. Each LDPE sheet 1.0 cm × 4.0 cm) with a thickness of 0.11 mm was pre- pared according to a modified method (Khruengsai et al., 2021). They were washed with water, sterilized with 70 % ethanol, and air-drying. The dry sheets were kept inside the desiccator until use. The weight of the dried LDPE sheet was recorded as the initial weight.			No	Culture collection	Culture collection	Thailand	No		
Arthrinium sacchari	166626	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Microbial degradation of low-density polyethylene by Neopestalotiopsis phangngaensis. The Journal of General and Applied Microbiology, 68(6), 287-294.				No			2023.0	Weight loss;tensile strength	Five millimeters nominal size of white amorphous LDPE microplastic granules were used for biodegradability assessment. Each LDPE sheet 1.0 cm × 4.0 cm) with a thickness of 0.11 mm was pre- pared according to a modified method (Khruengsai et al., 2021). They were washed with water, sterilized with 70 % ethanol, and air-drying. The dry sheets were kept inside the desiccator until use. The weight of the dried LDPE sheet was recorded as the initial weight.			No	Culture collection	Culture collection	Thailand	No		
Neopestalotiopsis phangngaensis	2485531	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Microbial degradation of low-density polyethylene by Neopestalotiopsis phangngaensis. The Journal of General and Applied Microbiology, 68(6), 287-294.	Laccase			No			2023.0	Weight loss;tensile strength;SEM;CO2	Five millimeters nominal size of white amorphous LDPE microplastic granules were used for biodegradability assessment. Each LDPE sheet 1.0 cm × 4.0 cm) with a thickness of 0.11 mm was pre- pared according to a modified method (Khruengsai et al., 2021). They were washed with water, sterilized with 70 % ethanol, and air-drying. The dry sheets were kept inside the desiccator until use. The weight of the dried LDPE sheet was recorded as the initial weight.			No	Culture collection	Culture collection	Thailand	No		
Neopestalotiopsis phangngaensis	2485531	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Microbial degradation of low-density polyethylene by Neopestalotiopsis phangngaensis. The Journal of General and Applied Microbiology, 68(6), 287-294.	Manganase peroxidase			No			2023.0	Weight loss;tensile strength;SEM;CO2	Five millimeters nominal size of white amorphous LDPE microplastic granules were used for biodegradability assessment. Each LDPE sheet 1.0 cm × 4.0 cm) with a thickness of 0.11 mm was pre- pared according to a modified method (Khruengsai et al., 2021). They were washed with water, sterilized with 70 % ethanol, and air-drying. The dry sheets were kept inside the desiccator until use. The weight of the dried LDPE sheet was recorded as the initial weight.			No	Culture collection	Culture collection	Thailand	No		
Neopestalotiopsis phangngaensis	2485531	LDPE	Khruengsai, S., Sripahco, T., & Pripdeevech, P. (2022). Microbial degradation of low-density polyethylene by Neopestalotiopsis phangngaensis. The Journal of General and Applied Microbiology, 68(6), 287-294.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;SEM;CO2	Five millimeters nominal size of white amorphous LDPE microplastic granules were used for biodegradability assessment. Each LDPE sheet 1.0 cm × 4.0 cm) with a thickness of 0.11 mm was pre- pared according to a modified method (Khruengsai et al., 2021). They were washed with water, sterilized with 70 % ethanol, and air-drying. The dry sheets were kept inside the desiccator until use. The weight of the dried LDPE sheet was recorded as the initial weight.			No	Culture collection	Culture collection	Thailand	No		
Aspergillus fumigatus	746128	PVC	El-Dash, H. A., Yousef, N. E., Aboelazm, A. A., Awan, Z. A., Yahya, G., & El-Ganiny, A. M. (2023). Optimizing Eco-Friendly Degradation of Polyvinyl Chloride (PVC) Plastic Using Environmental Strains of Malassezia Species and Aspergillus fumigatus. International Journal of Molecular Sciences, 24(20), 15452.	Depolymerase enzyme			No			2023.0	Clear zone;weight loss	The PVC polymer was an industrial-grade polymer supplied by Elreda Company (Gharbya, Egypt) in the form of powder. Polymer emulsion was prepared as described previously with some modifications [57]. Briefly, 1 g of PVC was suspended in 20 mL of dichloromethane and 30 mL of distilled water. This mixture was sonicated for 10 min. Then, dichloromethane was evaporated by stirring at 80 ◦C in water bath for 2 h, then the pH was adjusted to 7 with KOH. The obtained suspension was added to 1 L of culture media to obtain a final concentration of 0.1% PVC. For weight reduction and SEM analysis, colourless PVC plastic strips from Polysolutions Co., Ltd were cut into small pieces.	Elreda Company (clear zone); Polysolutions Co., Ltd. (weight loss and SEM)		Yes	Soil	Landfill	Egypt	No		
Malassezia sp.	2011732	PVC	El-Dash, H. A., Yousef, N. E., Aboelazm, A. A., Awan, Z. A., Yahya, G., & El-Ganiny, A. M. (2023). Optimizing Eco-Friendly Degradation of Polyvinyl Chloride (PVC) Plastic Using Environmental Strains of Malassezia Species and Aspergillus fumigatus. International Journal of Molecular Sciences, 24(20), 15452.	Depolymerase enzyme			No			2023.0	Clear zone;weight loss;SEM	The PVC polymer was an industrial-grade polymer supplied by Elreda Company (Gharbya, Egypt) in the form of powder. Polymer emulsion was prepared as described previously with some modifications [57]. Briefly, 1 g of PVC was suspended in 20 mL of dichloromethane and 30 mL of distilled water. This mixture was sonicated for 10 min. Then, dichloromethane was evaporated by stirring at 80 ◦C in water bath for 2 h, then the pH was adjusted to 7 with KOH. The obtained suspension was added to 1 L of culture media to obtain a final concentration of 0.1% PVC.	Elreda Company (clear zone); Polysolutions Co., Ltd. (weight loss and SEM)		Yes	Soil	Landfill	Egypt	No		
Aspergillus fumigatus	746128	PVC	El-Dash, H. A., Yousef, N. E., Aboelazm, A. A., Awan, Z. A., Yahya, G., & El-Ganiny, A. M. (2023). Optimizing Eco-Friendly Degradation of Polyvinyl Chloride (PVC) Plastic Using Environmental Strains of Malassezia Species and Aspergillus fumigatus. International Journal of Molecular Sciences, 24(20), 15452.	Depolymerase enzyme			No			2023.0	Clear zone;weight loss;SEM	The PVC polymer was an industrial-grade polymer supplied by Elreda Company (Gharbya, Egypt) in the form of powder. Polymer emulsion was prepared as described previously with some modifications [57]. Briefly, 1 g of PVC was suspended in 20 mL of dichloromethane and 30 mL of distilled water. This mixture was sonicated for 10 min. Then, dichloromethane was evaporated by stirring at 80 ◦C in water bath for 2 h, then the pH was adjusted to 7 with KOH. The obtained suspension was added to 1 L of culture media to obtain a final concentration of 0.1% PVC.	Elreda Company (clear zone); Polysolutions Co., Ltd. (weight loss and SEM)		No	Soil	Landfill	Egypt	No		
Aspergillus fumigatus	746128	PVC	El-Dash, H. A., Yousef, N. E., Aboelazm, A. A., Awan, Z. A., Yahya, G., & El-Ganiny, A. M. (2023). Optimizing Eco-Friendly Degradation of Polyvinyl Chloride (PVC) Plastic Using Environmental Strains of Malassezia Species and Aspergillus fumigatus. International Journal of Molecular Sciences, 24(20), 15452.	Depolymerase enzyme			No			2023.0	Clear zone;weight loss;SEM	The PVC polymer was an industrial-grade polymer supplied by Elreda Company (Gharbya, Egypt) in the form of powder. Polymer emulsion was prepared as described previously with some modifications [57]. Briefly, 1 g of PVC was suspended in 20 mL of dichloromethane and 30 mL of distilled water. This mixture was sonicated for 10 min. Then, dichloromethane was evaporated by stirring at 80 ◦C in water bath for 2 h, then the pH was adjusted to 7 with KOH. The obtained suspension was added to 1 L of culture media to obtain a final concentration of 0.1% PVC.	Elreda Company (clear zone); Polysolutions Co., Ltd. (weight loss and SEM)		Yes	Soil	Landfill	Egypt	No		
Aspergillus fumigatus	746128	PVC	El-Dash, H. A., Yousef, N. E., Aboelazm, A. A., Awan, Z. A., Yahya, G., & El-Ganiny, A. M. (2023). Optimizing Eco-Friendly Degradation of Polyvinyl Chloride (PVC) Plastic Using Environmental Strains of Malassezia Species and Aspergillus fumigatus. International Journal of Molecular Sciences, 24(20), 15452.	Lipase			No			2023.0	Clear zone;weight loss	The PVC polymer was an industrial-grade polymer supplied by Elreda Company (Gharbya, Egypt) in the form of powder. Polymer emulsion was prepared as described previously with some modifications [57]. Briefly, 1 g of PVC was suspended in 20 mL of dichloromethane and 30 mL of distilled water. This mixture was sonicated for 10 min. Then, dichloromethane was evaporated by stirring at 80 ◦C in water bath for 2 h, then the pH was adjusted to 7 with KOH. The obtained suspension was added to 1 L of culture media to obtain a final concentration of 0.1% PVC. For weight reduction and SEM analysis, colourless PVC plastic strips from Polysolutions Co., Ltd were cut into small pieces.	Elreda Company (clear zone); Polysolutions Co., Ltd. (weight loss and SEM)		Yes	Soil	Landfill	Egypt	No		
Aspergillus fumigatus	746128	PVC	El-Dash, H. A., Yousef, N. E., Aboelazm, A. A., Awan, Z. A., Yahya, G., & El-Ganiny, A. M. (2023). Optimizing Eco-Friendly Degradation of Polyvinyl Chloride (PVC) Plastic Using Environmental Strains of Malassezia Species and Aspergillus fumigatus. International Journal of Molecular Sciences, 24(20), 15452.	Lipase			No			2023.0	Clear zone;weight loss	The PVC polymer was an industrial-grade polymer supplied by Elreda Company (Gharbya, Egypt) in the form of powder. Polymer emulsion was prepared as described previously with some modifications [57]. Briefly, 1 g of PVC was suspended in 20 mL of dichloromethane and 30 mL of distilled water. This mixture was sonicated for 10 min. Then, dichloromethane was evaporated by stirring at 80 ◦C in water bath for 2 h, then the pH was adjusted to 7 with KOH. The obtained suspension was added to 1 L of culture media to obtain a final concentration of 0.1% PVC. For weight reduction and SEM analysis, colourless PVC plastic strips from Polysolutions Co., Ltd were cut into small pieces.	Elreda Company (clear zone); Polysolutions Co., Ltd. (weight loss and SEM)		Yes	Soil	Landfill	Egypt	No		
Exiguobacterium profundum	307643	LDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Exiguobacterium profundum	307643	HDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Exiguobacterium profundum	307643	PP	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Exiguobacterium profundum	307643	PET	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas mendocina	300	LDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2;SEM	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas mendocina	300	HDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2;SEM	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas mendocina	300	PP	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2;SEM	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas mendocina	300	PET	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2;SEM	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Halomonas aquamarina	77097	LDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Halomonas aquamarina	77097	HDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Halomonas aquamarina	77097	PP	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Halomonas aquamarina	77097	PET	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Halomonas sp.	1486246	HDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Halomonas sp.	1486246	PP	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Halomonas sp.	1486246	PET	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Exiguobacterium sp.	44751	LDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Exiguobacterium sp.	44751	HDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Exiguobacterium sp.	44751	PP	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Exiguobacterium sp.	44751	PET	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas sp.	306	LDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas sp.	306	HDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas sp.	306	PP	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas sp.	306	PET	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas sp.	306	LDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas sp.	306	HDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas sp.	306	PP	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas sp.	306	PET	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas oryzihabitans	47885	LDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas oryzihabitans	47885	HDPE	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas oryzihabitans	47885	PP	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Pseudomonas oryzihabitans	47885	PET	Jadhav, H. S., Fulke, A. B., Dasari, L. N., Dalai, A., & Haridevi, C. K. (2024). Plastic bio-mitigation by Pseudomonas mendocina ABF786 and simultaneous conversion of its CO2 byproduct to microalgal biodiesel. Bioresource Technology, 391, 129952.				No			2023.0	CO2	Granules (2–4 mm in diameter) of different grades of all the four plastic types were acquired from MicroMaster Industries Private Limited, India. These plastic granules were further ground into a fine powder of particle size <500 µm using a cryogenic grinder Retsch ultra centrifugal mill model ZM300 (Retsch, Germany) from Verder ScientificPrivate Limited, India. The quality of all the types of plastics acquired were reconfirmed using FTIR in our laboratory	MicroMaster Industries Private Limited		No	Sediment	Polluted intertidal region	India	No		
Purpureocillium lilacinum	33203	PBAT	Tseng, W. S., Lee, M. J., Wu, J. A., Kuo, S. L., Chang, S. L., Huang, S. J., & Liu, C. T. (2023). Poly (butylene adipate-co-terephthalate) biodegradation by Purpureocillium lilacinum strain BA1S. Applied Microbiology and Biotechnology, 107(19), 6057-6070.	Cutinase			No			2023.0	Clear zone;weight loss;SEM;FTIR;LCMS	Poly(butylene adipate-co-terephthalate) (PBAT) parti- cles and films were provided by the Material and Chemi- cal Research Laboratories of the Industrial Technology Research Institute (ITRI). The number-average molecular weight (Mn) and the average molecular weight (Mw) of the PBAT films were 7732 and 58919 g/mol, respectively. The molar ratio of the butylene adipate (BA) unit to the butylene terephthalate (BT) unit in the copolymer PBAT was 0.52/0.48 molBA/molBT, which was determined by 1H NMR spectroscopy in CDCl.	The Material and Chemical Research Laboratories of the Industrial Technology Research Institute	Yes	No	Soil	Soil	Taiwan	No		
Purpureocillium lilacinum	33203	PBAT	Tseng, W. S., Lee, M. J., Wu, J. A., Kuo, S. L., Chang, S. L., Huang, S. J., & Liu, C. T. (2023). Poly (butylene adipate-co-terephthalate) biodegradation by Purpureocillium lilacinum strain BA1S. Applied Microbiology and Biotechnology, 107(19), 6057-6070.	Cytochrome P450			No			2023.0	Clear zone;weight loss;SEM;FTIR;LCMS	Poly(butylene adipate-co-terephthalate) (PBAT) parti- cles and films were provided by the Material and Chemi- cal Research Laboratories of the Industrial Technology Research Institute (ITRI). The number-average molecular weight (Mn) and the average molecular weight (Mw) of the PBAT films were 7732 and 58919 g/mol, respectively. The molar ratio of the butylene adipate (BA) unit to the butylene terephthalate (BT) unit in the copolymer PBAT was 0.52/0.48 molBA/molBT, which was determined by 1H NMR spectroscopy in CDCl.	The Material and Chemical Research Laboratories of the Industrial Technology Research Institute	Yes	No	Soil	Soil	Taiwan	No		
Penicillium citrinum	5077	PBAT	Tseng, W. S., Lee, M. J., Wu, J. A., Kuo, S. L., Chang, S. L., Huang, S. J., & Liu, C. T. (2023). Poly (butylene adipate-co-terephthalate) biodegradation by Purpureocillium lilacinum strain BA1S. Applied Microbiology and Biotechnology, 107(19), 6057-6070.				No			2023.0	Clear zone	Poly(butylene adipate-co-terephthalate) (PBAT) parti- cles and films were provided by the Material and Chemi- cal Research Laboratories of the Industrial Technology Research Institute (ITRI). The number-average molecular weight (Mn) and the average molecular weight (Mw) of the PBAT films were 7732 and 58919 g/mol, respectively. The molar ratio of the butylene adipate (BA) unit to the butylene terephthalate (BT) unit in the copolymer PBAT was 0.52/0.48 molBA/molBT, which was determined by 1H NMR spectroscopy in CDCl.	The Material and Chemical Research Laboratories of the Industrial Technology Research Institute	Yes	No	Soil	Soil	Taiwan	No		
Aspergillus fumigatus	746128	PBAT	Tseng, W. S., Lee, M. J., Wu, J. A., Kuo, S. L., Chang, S. L., Huang, S. J., & Liu, C. T. (2023). Poly (butylene adipate-co-terephthalate) biodegradation by Purpureocillium lilacinum strain BA1S. Applied Microbiology and Biotechnology, 107(19), 6057-6070.				No			2023.0	Clear zone	Poly(butylene adipate-co-terephthalate) (PBAT) parti- cles and films were provided by the Material and Chemi- cal Research Laboratories of the Industrial Technology Research Institute (ITRI). The number-average molecular weight (Mn) and the average molecular weight (Mw) of the PBAT films were 7732 and 58919 g/mol, respectively. The molar ratio of the butylene adipate (BA) unit to the butylene terephthalate (BT) unit in the copolymer PBAT was 0.52/0.48 molBA/molBT, which was determined by 1H NMR spectroscopy in CDCl.	The Material and Chemical Research Laboratories of the Industrial Technology Research Institute	Yes	No	Soil	Soil	Taiwan	No		
Westerdykella dispersa	45154	PBAT	Tseng, W. S., Lee, M. J., Wu, J. A., Kuo, S. L., Chang, S. L., Huang, S. J., & Liu, C. T. (2023). Poly (butylene adipate-co-terephthalate) biodegradation by Purpureocillium lilacinum strain BA1S. Applied Microbiology and Biotechnology, 107(19), 6057-6070.				No			2023.0	Clear zone	Poly(butylene adipate-co-terephthalate) (PBAT) parti- cles and films were provided by the Material and Chemi- cal Research Laboratories of the Industrial Technology Research Institute (ITRI). The number-average molecular weight (Mn) and the average molecular weight (Mw) of the PBAT films were 7732 and 58919 g/mol, respectively. The molar ratio of the butylene adipate (BA) unit to the butylene terephthalate (BT) unit in the copolymer PBAT was 0.52/0.48 molBA/molBT, which was determined by 1H NMR spectroscopy in CDCl.	The Material and Chemical Research Laboratories of the Industrial Technology Research Institute	Yes	No	Soil	Soil	Taiwan	No		
Rhodotorula mucilaginosa	5537	PE	Vaksmaa, A., Polerecky, L., Dombrowski, N., Kienhuis, M. V., Posthuma, I., Gerritse, J., Boekhout, T., & Niemann, H. (2023). Polyethylene degradation and assimilation by the marine yeast Rhodotorula mucilaginosa. ISME communications, 3(1), 68.				No			2023.0	Radiolabeling		Sigma-Aldrich	Yes	No	Seawater	Marine	North Sea	No		
Pleurotus ostreatus	5322	PET	Odigbo, C., Adenipekun, C., Oladosu, I., & Ogunjobi, A. (2022). Polyethylene Terephthalate (PET) Biodegradation by Pleurotus ostreatus and Pleurotus pulmonarius.				No			2023.0	FTIR;GCMS	The pre- viously used and discarded PET bottles were sourced from the suburbs of the University of Ibadan (Agbowo region). The PET bottles were cut into 0.5 mm × 1.0 mm flakes. 		No	No	Culture collection	Culture collection	Namibia	No		
Pleurotus pulmonarius	28995	PET	Odigbo, C., Adenipekun, C., Oladosu, I., & Ogunjobi, A. (2022). Polyethylene Terephthalate (PET) Biodegradation by Pleurotus ostreatus and Pleurotus pulmonarius.				No			2023.0	FTIR;GCMS	Th+G2323e pre- viously used and discarded PET bottles were sourced from the suburbs of the University of Ibadan (Agbowo region). The PET bottles were cut into 0.5 mm × 1.0 mm flakes. 		No	No	Culture collection	Culture collection	Namibia	No		
Enterobacter hormaechei	158836	PS	Kang, M. G., Kwak, M. J., & Kim, Y. (2023). Polystyrene microplastics biodegradation by gut bacterial Enterobacter hormaechei from mealworms under anaerobic conditions: Anaerobic oxidation and depolymerization. Journal of Hazardous Materials, 459, 132045.	Thiol peroxidase			No			2023.0	Weight loss;FE-SEM;FTIR;SPME/GCMS;GC	PS foams were source from commercially available products. PS films were purchased from the Goodfellow company (Huntingdon, UK). Microspheres PS (Mi-PS) with a diameter of 1 µm were obtained as beads from the Polysciences company (Warrington, USA). Mi-PS are internally PC Red dyed using dye entrapment. The dyes remain trapped in the beads in aqueous environments. The PS materials (0.1 g) dissolved in tetrahydrofuran (THF). The weight average molecular weight (Mw), number average molecular weight (Mn), and z-average molecular weight (Mz) of THF-dissolved PS materials were analyzed using gel permeation chromatography (GPC, Ultimate 3000, Thermo) [96]. The Mw values of PS foams, PS films, Mi-PS, PS emulsion were 247,800 Da, 314,700 Da, 276,700 Da, and 284,800 Da, respectively (Supplementary Table 1).	NA (foams), Goodfellow (films), Polysciences company (microbeads)		No	Mealworm intestine	Animal associated	South Korea	No		
Enterobacter hormaechei	158836	PS	Kang, M. G., Kwak, M. J., & Kim, Y. (2023). Polystyrene microplastics biodegradation by gut bacterial Enterobacter hormaechei from mealworms under anaerobic conditions: Anaerobic oxidation and depolymerization. Journal of Hazardous Materials, 459, 132045.	Alkyl hydroperoxide reductase C			No			2023.0	Weight loss;FE-SEM;FTIR;SPME/GCMS;GC	PS foams were source from commercially available products. PS films were purchased from the Goodfellow company (Huntingdon, UK). Microspheres PS (Mi-PS) with a diameter of 1 µm were obtained as beads from the Polysciences company (Warrington, USA). Mi-PS are internally PC Red dyed using dye entrapment. The dyes remain trapped in the beads in aqueous environments. The PS materials (0.1 g) dissolved in tetrahydrofuran (THF). The weight average molecular weight (Mw), number average molecular weight (Mn), and z-average molecular weight (Mz) of THF-dissolved PS materials were analyzed using gel permeation chromatography (GPC, Ultimate 3000, Thermo) [96]. The Mw values of PS foams, PS films, Mi-PS, PS emulsion were 247,800 Da, 314,700 Da, 276,700 Da, and 284,800 Da, respectively (Supplementary Table 1).	NA (foams), Goodfellow (films), Polysciences company (microbeads)		No	Mealworm intestine	Animal associated	South Korea	No		
Enterobacter hormaechei	158836	PS	Kang, M. G., Kwak, M. J., & Kim, Y. (2023). Polystyrene microplastics biodegradation by gut bacterial Enterobacter hormaechei from mealworms under anaerobic conditions: Anaerobic oxidation and depolymerization. Journal of Hazardous Materials, 459, 132045.	Bacterioferritin comigratory protien			No			2023.0	Weight loss;FE-SEM;FTIR;SPME/GCMS;GC	PS foams were source from commercially available products. PS films were purchased from the Goodfellow company (Huntingdon, UK). Microspheres PS (Mi-PS) with a diameter of 1 µm were obtained as beads from the Polysciences company (Warrington, USA). Mi-PS are internally PC Red dyed using dye entrapment. The dyes remain trapped in the beads in aqueous environments. The PS materials (0.1 g) dissolved in tetrahydrofuran (THF). The weight average molecular weight (Mw), number average molecular weight (Mn), and z-average molecular weight (Mz) of THF-dissolved PS materials were analyzed using gel permeation chromatography (GPC, Ultimate 3000, Thermo) [96]. The Mw values of PS foams, PS films, Mi-PS, PS emulsion were 247,800 Da, 314,700 Da, 276,700 Da, and 284,800 Da, respectively (Supplementary Table 1).	NA (foams), Goodfellow (films), Polysciences company (microbeads)		No	Mealworm intestine	Animal associated	South Korea	No		
Bacillus amyloliquefaciens	1390	PS	Kang, M. G., Kwak, M. J., & Kim, Y. (2023). Polystyrene microplastics biodegradation by gut bacterial Enterobacter hormaechei from mealworms under anaerobic conditions: Anaerobic oxidation and depolymerization. Journal of Hazardous Materials, 459, 132045.				No			2023.0	Weight loss;FE-SEM;FTIR;SPME/GCMS;GC	PS foams were source from commercially available products. PS films were purchased from the Goodfellow company (Huntingdon, UK). Microspheres PS (Mi-PS) with a diameter of 1 µm were obtained as beads from the Polysciences company (Warrington, USA). Mi-PS are internally PC Red dyed using dye entrapment. The dyes remain trapped in the beads in aqueous environments. The PS materials (0.1 g) dissolved in tetrahydrofuran (THF). The weight average molecular weight (Mw), number average molecular weight (Mn), and z-average molecular weight (Mz) of THF-dissolved PS materials were analyzed using gel permeation chromatography (GPC, Ultimate 3000, Thermo) [96]. The Mw values of PS foams, PS films, Mi-PS, PS emulsion were 247,800 Da, 314,700 Da, 276,700 Da, and 284,800 Da, respectively (Supplementary Table 1).	NA (foams), Goodfellow (films), Polysciences company (microbeads)		No		Soybean fermented foods	South Korea	No		
Burkholderia cepacia	292	LDPE	Lin, Z., Jin, T., Xu, X., Yin, X., Zhang, D., Geng, M., Pang, C., Luo, G., Xiong, L., Peng, J., & Fei, J. (2024). Screening and degradation characteristics of plastic-degrading microorganisms in film-mulched vegetable soil. International Biodeterioration & Biodegradation, 186, 105686.				No			2023.0	Weight loss;WCA	The mulch film used in this study is purchased from Xuanhan Hualong plastic products Co., Ltd., its thickness is 10 μm, and the composition is LDPE. The weight-average molecular weight (Mw) and number-average molecular weight (Mn) detected by gel permeation chromatography (GPC, PL220, Agilent, USA) was 153,637 Da and 62,705 Da, respectively. The LDPE mulch film is cut into sizes 2 ×2 cm and 5 ×5 cm, respectively, it is soaked in sodium dodecyl sulfate (SDS) for 4 h, then cleaned, washed, dried and weighted. The film is then exposed to UV light for 4 h, soaked in 75% ethanol for 4 h and rinsed with sterile water for 3 times. Sterile blotting paper is used to dry the film surface on super clean workbench, then place the film in the sterilized Petri dish. After the water is air-dried, the sterilized with UV lamp for 30 min. on	Xuanhan Hualong plastic products Co., Ltd.	No	No	Soil	Plastic contaminated vegetable field	China	No		
Burkholderia ambifaria	152480	LDPE	Lin, Z., Jin, T., Xu, X., Yin, X., Zhang, D., Geng, M., Pang, C., Luo, G., Xiong, L., Peng, J., & Fei, J. (2024). Screening and degradation characteristics of plastic-degrading microorganisms in film-mulched vegetable soil. International Biodeterioration & Biodegradation, 186, 105686.				No			2023.0	Weight loss;WCA	The mulch film used in this study is purchased from Xuanhan Hualong plastic products Co., Ltd., its thickness is 10 μm, and the composition is LDPE. The weight-average molecular weight (Mw) and number-average molecular weight (Mn) detected by gel permeation chromatography (GPC, PL220, Agilent, USA) was 153,637 Da and 62,705 Da, respectively. The LDPE mulch film is cut into sizes 2 ×2 cm and 5 ×5 cm, respectively, it is soaked in sodium dodecyl sulfate (SDS) for 4 h, then cleaned, washed, dried and weighted. The film is then exposed to UV light for 4 h, soaked in 75% ethanol for 4 h and rinsed with sterile water for 3 times. Sterile blotting paper is used to dry the film surface on super clean workbench, then place the film in the sterilized Petri dish. After the water is air-dried, the sterilized with UV lamp for 30 min. on	Xuanhan Hualong plastic products Co., Ltd.	No	No	Soil	Plastic contaminated vegetable field	China	No		
Burkholderia aenigmatica	2015348	LDPE	Lin, Z., Jin, T., Xu, X., Yin, X., Zhang, D., Geng, M., Pang, C., Luo, G., Xiong, L., Peng, J., & Fei, J. (2024). Screening and degradation characteristics of plastic-degrading microorganisms in film-mulched vegetable soil. International Biodeterioration & Biodegradation, 186, 105686.				No			2023.0	Weight loss;WCA;SEM;ATR-FTIR	The mulch film used in this study is purchased from Xuanhan Hualong plastic products Co., Ltd., its thickness is 10 μm, and the composition is LDPE. The weight-average molecular weight (Mw) and number-average molecular weight (Mn) detected by gel permeation chromatography (GPC, PL220, Agilent, USA) was 153,637 Da and 62,705 Da, respectively. The LDPE mulch film is cut into sizes 2 ×2 cm and 5 ×5 cm, respectively, it is soaked in sodium dodecyl sulfate (SDS) for 4 h, then cleaned, washed, dried and weighted. The film is then exposed to UV light for 4 h, soaked in 75% ethanol for 4 h and rinsed with sterile water for 3 times. Sterile blotting paper is used to dry the film surface on super clean workbench, then place the film in the sterilized Petri dish. After the water is air-dried, the sterilized with UV lamp for 30 min. on	Xuanhan Hualong plastic products Co., Ltd.	No	No	Soil	Plastic contaminated vegetable field	China	No		
Chrysebacterium nepalense	2015348	LDPE	Lin, Z., Jin, T., Xu, X., Yin, X., Zhang, D., Geng, M., Pang, C., Luo, G., Xiong, L., Peng, J., & Fei, J. (2024). Screening and degradation characteristics of plastic-degrading microorganisms in film-mulched vegetable soil. International Biodeterioration & Biodegradation, 186, 105686.				No			2023.0	Weight loss;WCA	The mulch film used in this study is purchased from Xuanhan Hualong plastic products Co., Ltd., its thickness is 10 μm, and the composition is LDPE. The weight-average molecular weight (Mw) and number-average molecular weight (Mn) detected by gel permeation chromatography (GPC, PL220, Agilent, USA) was 153,637 Da and 62,705 Da, respectively. The LDPE mulch film is cut into sizes 2 ×2 cm and 5 ×5 cm, respectively, it is soaked in sodium dodecyl sulfate (SDS) for 4 h, then cleaned, washed, dried and weighted. The film is then exposed to UV light for 4 h, soaked in 75% ethanol for 4 h and rinsed with sterile water for 3 times. Sterile blotting paper is used to dry the film surface on super clean workbench, then place the film in the sterilized Petri dish. After the water is air-dried, the sterilized with UV lamp for 30 min. on	Xuanhan Hualong plastic products Co., Ltd.	No	No	Soil	Plastic contaminated vegetable field	China	No		
Geotrichum candidum	1173061	LDPE	Lin, Z., Jin, T., Xu, X., Yin, X., Zhang, D., Geng, M., Pang, C., Luo, G., Xiong, L., Peng, J., & Fei, J. (2024). Screening and degradation characteristics of plastic-degrading microorganisms in film-mulched vegetable soil. International Biodeterioration & Biodegradation, 186, 105686.				No			2023.0	Weight loss;WCA	The mulch film used in this study is purchased from Xuanhan Hualong plastic products Co., Ltd., its thickness is 10 μm, and the composition is LDPE. The weight-average molecular weight (Mw) and number-average molecular weight (Mn) detected by gel permeation chromatography (GPC, PL220, Agilent, USA) was 153,637 Da and 62,705 Da, respectively. The LDPE mulch film is cut into sizes 2 ×2 cm and 5 ×5 cm, respectively, it is soaked in sodium dodecyl sulfate (SDS) for 4 h, then cleaned, washed, dried and weighted. The film is then exposed to UV light for 4 h, soaked in 75% ethanol for 4 h and rinsed with sterile water for 3 times. Sterile blotting paper is used to dry the film surface on super clean workbench, then place the film in the sterilized Petri dish. After the water is air-dried, the sterilized with UV lamp for 30 min. on	Xuanhan Hualong plastic products Co., Ltd.	No	No	Soil	Plastic contaminated vegetable field	China	No		
Fusarium oxysporum	5507	LDPE	Lin, Z., Jin, T., Xu, X., Yin, X., Zhang, D., Geng, M., Pang, C., Luo, G., Xiong, L., Peng, J., & Fei, J. (2024). Screening and degradation characteristics of plastic-degrading microorganisms in film-mulched vegetable soil. International Biodeterioration & Biodegradation, 186, 105686.				No			2023.0	Weight loss;WCA	The mulch film used in this study is purchased from Xuanhan Hualong plastic products Co., Ltd., its thickness is 10 μm, and the composition is LDPE. The weight-average molecular weight (Mw) and number-average molecular weight (Mn) detected by gel permeation chromatography (GPC, PL220, Agilent, USA) was 153,637 Da and 62,705 Da, respectively. The LDPE mulch film is cut into sizes 2 ×2 cm and 5 ×5 cm, respectively, it is soaked in sodium dodecyl sulfate (SDS) for 4 h, then cleaned, washed, dried and weighted. The film is then exposed to UV light for 4 h, soaked in 75% ethanol for 4 h and rinsed with sterile water for 3 times. Sterile blotting paper is used to dry the film surface on super clean workbench, then place the film in the sterilized Petri dish. After the water is air-dried, the sterilized with UV lamp for 30 min. on	Xuanhan Hualong plastic products Co., Ltd.	No	No	Soil	Plastic contaminated vegetable field	China	No		
Trichoderma sp.	1715253	LDPE	Lin, Z., Jin, T., Xu, X., Yin, X., Zhang, D., Geng, M., Pang, C., Luo, G., Xiong, L., Peng, J., & Fei, J. (2024). Screening and degradation characteristics of plastic-degrading microorganisms in film-mulched vegetable soil. International Biodeterioration & Biodegradation, 186, 105686.				No			2023.0	Weight loss;WCA	The mulch film used in this study is purchased from Xuanhan Hualong plastic products Co., Ltd., its thickness is 10 μm, and the composition is LDPE. The weight-average molecular weight (Mw) and number-average molecular weight (Mn) detected by gel permeation chromatography (GPC, PL220, Agilent, USA) was 153,637 Da and 62,705 Da, respectively. The LDPE mulch film is cut into sizes 2 ×2 cm and 5 ×5 cm, respectively, it is soaked in sodium dodecyl sulfate (SDS) for 4 h, then cleaned, washed, dried and weighted. The film is then exposed to UV light for 4 h, soaked in 75% ethanol for 4 h and rinsed with sterile water for 3 times. Sterile blotting paper is used to dry the film surface on super clean workbench, then place the film in the sterilized Petri dish. After the water is air-dried, the sterilized with UV lamp for 30 min. on	Xuanhan Hualong plastic products Co., Ltd.	No	No	Soil	Plastic contaminated vegetable field	China	No		
Achromobacter xylosoxidans	85698	Nylon	Tiwari, N., Santhiya, D., & Sharma, J. G. (2024). Significance of landfill microbial communities in biodegradation of polyethylene and nylon 6, 6 microplastics. Journal of Hazardous Materials, 462, 132786.	Laccase			No			2023.0	Weight loss;UP-HPLC;GCMS;DSC;TGA;FTIR;SEM;TEM	Lab synthesised			No	Soil	Landfill	India	No		
Achromobacter xylosoxidans	85698	Nylon	Tiwari, N., Santhiya, D., & Sharma, J. G. (2024). Significance of landfill microbial communities in biodegradation of polyethylene and nylon 6, 6 microplastics. Journal of Hazardous Materials, 462, 132786.	Peroxidase			No			2023.0	Weight loss;UP-HPLC;GCMS;DSC;TGA;FTIR;SEM;TEM	Lab synthesised			No	Soil	Landfill	India	No		
Achromobacter xylosoxidans	85698	HDPE	Tiwari, N., Santhiya, D., & Sharma, J. G. (2024). Significance of landfill microbial communities in biodegradation of polyethylene and nylon 6, 6 microplastics. Journal of Hazardous Materials, 462, 132786.	Laccase			No			2023.0	Weight loss;UP-HPLC;GCMS;DSC;TGA;FTIR;SEM;TEM	The PE microplastics used in this study were composed of ultra-high molecular weight with a particle size of 42–48 µm.			No	Soil	Landfill	India	No		
Achromobacter xylosoxidans	85698	HDPE	Tiwari, N., Santhiya, D., & Sharma, J. G. (2024). Significance of landfill microbial communities in biodegradation of polyethylene and nylon 6, 6 microplastics. Journal of Hazardous Materials, 462, 132786.	Peroxidase			No			2023.0	Weight loss;UP-HPLC;GCMS;DSC;TGA;FTIR;SEM;TEM	The PE microplastics used in this study were composed of ultra-high molecular weight with a particle size of 42–48 µm.			No	Soil	Landfill	India	No		
Aspergillus terreus	33178	LDPE	Kuswytasari, N. D., Kurniawati, A. R., Aunurohim, A., Alami, N. H., Zulaika, E., Shovitri, M., Kumari, N., & Luqman, A. (2023). Plastic Biodegradation Potential of Soil Mangrove Mold Isolated from Wonorejo, Indonesia. Advancements in Life Sciences, 10(2), 228-238.	Lipase			No			2023.0	Weight loss;FTIR;SEM;AFM	Plastic cut into small sizes measuring 20X20mm squares	Aldrich	Yes	No	Plastic waste	Mangrove soil	India	No		
Perenniporia sp.	1881144	LDPE	Kuswytasari, N. D., Kurniawati, A. R., Aunurohim, A., Alami, N. H., Zulaika, E., Shovitri, M., Kumari, N., & Luqman, A. (2023). Plastic Biodegradation Potential of Soil Mangrove Mold Isolated from Wonorejo, Indonesia. Advancements in Life Sciences, 10(2), 228-238.	Lipase			No			2023.0	Weight loss;FTIR;SEM;AFM	Plastic cut into small sizes measuring 20X20mm squares	Aldrich	Yes	No	Plastic waste	Mangrove soil	India	No		
Trametes polyzona	239206	LDPE	Kuswytasari, N. D., Kurniawati, A. R., Aunurohim, A., Alami, N. H., Zulaika, E., Shovitri, M., Kumari, N., & Luqman, A. (2023). Plastic Biodegradation Potential of Soil Mangrove Mold Isolated from Wonorejo, Indonesia. Advancements in Life Sciences, 10(2), 228-238.				No			2023.0	Weight loss;FTIR;SEM;AFM	Plastic cut into small sizes measuring 20X20mm squares	Aldrich	Yes	No	Plastic waste	Mangrove soil	India	No		
Candidatus bathyarchaeota	928852	PET	Perez-Garcia, P., Chow, J., Costanzi, E., Gurschke, M., Dittrich, J., Dierkes, R. F., Molitor, R., Applegate, V., Feuerriegel, G., Tete, P., Danso, D., Thies, S., Schumacher, J., Pfleger, C., Jaeger, K.-E., Gohlke, H., Smits, S. H. J., Schmitz, R. A.,  & Streit, W. R. (2023). An archaeal lid-containing feruloyl esterase degrades polyethylene terephthalate. Communications chemistry, 6(1), 193.	Esterase	00220	00220 | Esterase | Candidatus bathyarchaeota | PET	Yes	RLI42440.1	MIKPVTFMSEGEQIIGVLHVPDDLRGDKRAPAIAMFHGFTGNKSEAHRLFVHVARSLCNDGFVVLRFDFRGSGDSDGEFEDMTVPGEVCDASRSIDFLSELNFVDSERIGVLGLSMGGRVAAILASKDRRIKFVILYSAALTPLRRKFLEGLEKESIRRLEMGEAVHVGNGWYLKKGFFETVDSIVPLDVLDRIRVPVLIIHGDSDSVIPLDGALKGYEIIRDLNDKNELYIVRGGDHVFTRREHTIEVIERTLDWLRSLNL	2023.0	HPLC	Respectively, 3 μM PET46 WT (roughly 0.1mgmL−1), the generated variants, IsPETase or LCC were incubated with 50 μM ethylene terephthalate linear trimer (3PET, Toronto Research Chemicals, Ontario, Canada), 150 μM bis-(2- hydroxyethyl) terephthalate (BHET), 150μM mono-(2-hydro- xyethyl) terephthalate (MHET; Merck, Darmstadt, Germany), 7mg amorphous PET foil platelet (product no. ES301445; a = 5 mm2, 33.6 μmol or 168 mM TPA eq.; GoodFellow GmbH, Hamburg, Germany), 2 mg semi-crystalline PET powder (product no. ES306000; >40% crystallinity, d ≈ 300 μm; 9.6 μmol or 48 mM TPA eq.; GoodFellow GmbH, Hamburg, Germany), unless indi- cated otherwise	Goodfellow	Yes	No				Yes		
Pseudomonas sp.	306	PE	Ali, S., Rehman, A., Hussain, S. Z., & Bukhari, D. A. (2023). Characterization of plastic degrading bacteria isolated from sewage wastewater. Saudi Journal of Biological Sciences, 30(5), 103628.				No			2023.0	Weight loss;GCMS;FTIR	As the principal carbon source, polyethylene was used to cultivate the samples in carbon-depleted minimum media (MSM).			No	Water/sewage	Sewage canal	Pakistan	No		
Pseudomonas aeruginosa	287	PE	Ali, S., Rehman, A., Hussain, S. Z., & Bukhari, D. A. (2023). Characterization of plastic degrading bacteria isolated from sewage wastewater. Saudi Journal of Biological Sciences, 30(5), 103628.				No			2023.0	Weight loss;GCMS;FTIR	As the principal carbon source, polyethylene was used to cultivate the samples in carbon-depleted minimum media (MSM).			No	Water/sewage	Sewage canal	Pakistan	No		
Thermobacillus composti	377615	PBAT	Wu, P., Li, Z., Gao, J., Zhao, Y., Wang, H., Qin, H., Gu, Q., Wei, R., Liu, W., & Han, X. (2023). Characterization of a PBAT Degradation Carboxylesterase from Thermobacillus composti KWC4. Catalysts, 13(2), 340.	Carboxylesterase	00221	00221 | Carboxylesterase | Thermobacillus composti | PBAT	Yes	WP_015255658.1	MVSLRIAKTENGYVQGLPAADPRITSFKGIPFAAPPVGENRWRAPQPAKNWDGVLKAYEFSPIPLQVRQEIDVNNIYTREWAVDPDIAMSEDCLYLNIWTPAKSPDEKLPVFVWYFGGGLQVGHASEMEFDGERIARRGIVVVTINYRLNVFGFLCHPEITAESPDAPANFGHLDQQFATQWVKRNIAAFGGDPDNITIGGQSAGGGSVLAQLTSPQNEGLFNKAIIMSGIFSPVYPGQRGPGVRETLAEAEQEGIKFFEYLGVSSLAEARKLDAVYIRDKMVEYKRFWGAVVDNKFCVGHPFERFLRNERWNVPILWGNTTDEFISRPQVGSIEELRQMAEGVFGEDADRFLALCGADSGDLEQALKAASVNTIEYAIRVASRANAAAGAGTPLYYYKFDAEIPGWDNPGTFHSVDLWFFFETLAKCWRPFVGKHYDLARQMCNYWAHFIRSGDPNGPDSTGEDLPRWEPYTEEAPYAMVFGDKSEFVREQPGEMIRFLVEQYFKRK	2023.0	SEM	PBAT film with a size of 8mm x 8mm			No				Yes		
Rhodococcus opacus	37919	PE	Zampolli, J., Mangiagalli, M., Vezzini, D., Lasagni, M., Ami, D., Natalello, A., Arrigoni, F., Bertini, L., Lotti, M., & Di Gennaro, P. (2023). Oxidative degradation of polyethylene by two novel laccase-like multicopper oxidases from Rhodococcus opacus R7. Environmental Technology & Innovation, 32, 103273.	Copper oxidase	00222	00222 | Copper oxidase | Rhodococcus opacus | PE	Yes	AII11185.1	MIEQFPTAGARLSRRNFLVLAGLGAAATVAGCGNTGDTGPATTVIGPDSAAVKAAEQTRRANIGTGKTVTSSLQARPTRIDLGGVQVDTWAYNDRVPGREVRLRRGDLLRAELTNDLPAESTIHWHGIALRNDMDGVPGLTQSAIAPNTPFTYEFLAPDAGTHWLHPHVGMQFDRGLYAPVIVEDPAEGGDYDLEAVLVLDDWLDGVTGRTPDQQLDTLRQGGMPMSGMGMDHGGMSGMGMGAVTDPANPLGADTGDVEYPYYLINGTLAADPFSVRARPGQRIRLRIINAGADTAFRIAVGGHELTVTHTDGYPVEPVTGSSLLIGMGERFDAVVTLGDGVFPIVASAEGKQGQGFALIRTGAGRTPEPTIRPTELDAPPITGLGLRAREEVRLGSRDPDRVHELMLGMDMSGYRWTINGATYDQHTPLDVAEGQRVRLRFVNQTMMFHPMHLHGHTFQLVDGQGAGPRKDTTLVLPNQTVEVDLDADNPGQWLVHCHNLYHGEAGMMTTLSYTE	2023.0	ATR-FTIR;GC-MSD	Standard PE  powder			No				Yes		
Rhodococcus opacus	37919	PE	Zampolli, J., Mangiagalli, M., Vezzini, D., Lasagni, M., Ami, D., Natalello, A., Arrigoni, F., Bertini, L., Lotti, M., & Di Gennaro, P. (2023). Oxidative degradation of polyethylene by two novel laccase-like multicopper oxidases from Rhodococcus opacus R7. Environmental Technology & Innovation, 32, 103273.	Copper oxidase	00223	00223 | Copper oxidase | Rhodococcus opacus | PE	Yes	AII11221	MAESRRQFLLGSALLGTAGAAALGARAASAAPSAAPPATETGGVHSGGHGGGVAGPTFRKGAVVDHAANGFDPTALLRDFDYGRVSQLPDGRVLREWVVAAADLDLEIAPGVRYPAWTFNGRIPGPTLRCQEGDLLRVQFVNTSAHPHTMHFHGIHPAEMDGIPDTGPGVIPSGGSFVYEFDAQPFGVHLYHCHVGPLAEHIARGLYGTFIVDPPEPRPPADEMVMVMHGYNTTFDGEGNQLYAVNGIPFHYMHEPVRVKRGELVRIYLVNALEYDPINTFHLHGNFFDYYPTGTRLEPSEYTDTIMQAQGQRGICEVRFPYPGRYMFHAHKTEFAELGWMGFFEVTD	2023.0	ATR-FTIR;GC-MSD	Standard PE  powder			No				Yes		
Aquabacterium parvum	70584	PET	Ho, N. H. E., Effendi, S. S. W., Ting, W. W., Yi, Y. C., Yu, J. Y., Chang, J. S., & Ng, I. S. (2023). Heterologous expression and characterization of Aquabacterium parvum lipase, a close relative of Ideonella sakaiensis PETase in Escherichia coli. Biochemical Engineering Journal, 197, 108985.	Lipase			No			2023.0	HPLC;SEM	Evaluation of PET degradation was carried out using a commercial beverage container labelled as PET with a modified process [4]. Circular PET film pieces of 5 mm diameter were sterilized using SDS and ethanol, each PET film was immersed in purified ApLip-Ec solution (approximately 5.5 µM) and 100 mM Na2HPO4 at pH 8.5, and then incubated at 30 ◦C for 48 h. 		No	No				Yes		
Halopseudomonas formosensis	1002526	PU	de Witt, J., Molitor, R., Gätgens, J., Ortmann de Percin Northumberland, C., Kruse, L., Polen, T., Wynands, B., Goethem, K., Thies, S., Jaeger, K.-E.,  & Wierckx, N. (2023). Biodegradation of poly (ester‐urethane) coatings by Halopseudomonas formosensis. Microbial Biotechnology.	Hydrolase	00224	00224 | Hydrolase | Halopseudomonas formosensis | PU	Yes	WP_090538641.1	MINNIFPKSLLSMIAAGALLMSASAFATNPPADPPPGGDSPYARGPDPTVSFLEASSGPYSTRTSRVSGLVSGFGGGTIHYPTGVEGTMAAIVVIPGFVSAESSIDWWGPKLASHGFVVMTIDTNTGFDQPPSRARQINNALDYLISQNSSRTSPVRGMIDTDRLGVIGWSMGGGGTLRVASEGRIKAAIPLAPWDTVSTYAGRSQAPTLIFACQADIIAPVAAHASPFYNRLPNGIEKAFVEINNGTHYCANGGGLNNDVLSRFGVSWMKRFLDEDTRYSQFLCGPNHTSDRKISEYRGNCPY	2023.0	Clear zone;light microscopy;GC-ToF-MS	Impranil	Covestro AG		Yes				No		
Rhodococcus sp.	1002526	PCL	Won, S. J., Yim, J. H., & Kim, H. K. (2022). Functional production, characterization, and immobilization of a cold-adapted cutinase from Antarctic Rhodococcus sp. Protein Expression and Purification, 195, 106077.	Cutinase	00225	00225 | Cutinase | Rhodococcus sp. | PCL PET	Yes	UNZ22463.1	MKRRLIAYSIAALAISATAVALPTGVASAAPCSDVDVSFARGTGELPGLGITGTPFVNSVKSQLSDRSVSTYAVNYAADFTQASAGPGSRDLVAHLNSVAASCPSTKFVIGGYSQGATVVTNAVGLRTPSSFTGAVIPAAIADRIEAVVVFGNPFGLTGRKIETASSTYGSRTNSFCNFGDPVCQIGGFNTFAHLTYGTNGSTTQGASFAAAQVRS	2022.0	Weight loss;SEM;HPLC	Polycaprolactone (PCL) was dissolved in dichloromethane (DCM) at a concentration of 10% (v/v), respectively. The DCM solvent was evaporated at room temperature for 1 day to make PCL and PLA films.	Sigma-Aldrich	Yes	No				Yes		
Rhodococcus sp.	1002526	PET	Won, S. J., Yim, J. H., & Kim, H. K. (2022). Functional production, characterization, and immobilization of a cold-adapted cutinase from Antarctic Rhodococcus sp. Protein Expression and Purification, 195, 106077.	Cutinase	00225	00225 | Cutinase | Rhodococcus sp. | PCL PET	Yes	UNZ22463.1	MKRRLIAYSIAALAISATAVALPTGVASAAPCSDVDVSFARGTGELPGLGITGTPFVNSVKSQLSDRSVSTYAVNYAADFTQASAGPGSRDLVAHLNSVAASCPSTKFVIGGYSQGATVVTNAVGLRTPSSFTGAVIPAAIADRIEAVVVFGNPFGLTGRKIETASSTYGSRTNSFCNFGDPVCQIGGFNTFAHLTYGTNGSTTQGASFAAAQVRS	2022.0	Weight loss;SEM;HPLC	PET film	Goodfellow	Yes	No				Yes		
Streptomyces sp.	1931	PET	Carr, C. M., Keller, M. B., Paul, B., Schubert, S. W., Clausen, K. S., Jensen, K., Clarke, D. J., Westh, P., & Dobson, A. D. (2023). Purification and biochemical characterization of SM14est, a PET-hydrolyzing enzyme from the marine sponge-derived Streptomyces sp. SM14. Frontiers in Microbiology, 14, 1170880.	Polyesterase	00226	00226 | Polyesterase | Streptomyces sp. | PET	Yes	DAC80635	MFQRVWALTAALMLMLSLGATSSHAAQNPHERGPDPSNSYIEQARGSYSVSQRSISRLGSDGFRDGTMYYPTSTADGRFGVVAISPGYTASESTIAWLGPRLASFGFVVVTINTDSRYDQPRQRATQLHAALDHAIGDSVVGPRIDTSRQAVMGHSMGGGGALQAAEERDEIRAAVPLTPWNLKKGWSGVDAATLVIGAENDAIAPVRSHSIPFYESLTNAERRAYLELRREGHFAPNSSNTLIAKYSVSWLKRYVDNDLRYDQFIDPGPRTGITTGVSDYRLG	2023.0	HPLC	PET powder reported to have >40% crystallinity with a particle size of <300µm	Goodfellow	Yes	No				Yes		
Thermoanaerobacter sp.	1755	PET	Sonnendecker, C., Oeser, J., Richter, P. K., Hille, P., Zhao, Z., Fischer, C., Lippold, H., Blázquez-Sánchez, P., Engelberger, F., Ramírez-Sarmiento, C. A., Oeser, T., Lihanova, Y., Frank, R., Jahnke, H.-J., Billig, S., Abel, B., Sträter, N., Matysik, J., & Zimmermann, W. (2022). Low carbon footprint recycling of post‐consumer PET plastic with a metagenomic polyester hydrolase. ChemSusChem, 15(9), e202101062.	Polyester hydrolase	00227	00227 | Polyester hydrolase | Thermoanaerobacter sp. | PET	Yes	7NEI_A	MANPYERGPDPTESSIEAVRGPFAVAQTTVSRLQADGFGGGTIYYPTDTSQGTFGAVAISPGFTAGQESIAWLGPRIASQGFVVITIDTITRLDQPDSRGRQLQAALDHLRTNSVVRNRIDPNRMAVMGHSMGGGGALSAAANNTSLEAAIPLQGWHTRKNWSSVRTPTLVVGAQLDTIAPVSSHSEAFYNSLPSDLDKAYMELRGASHLVSNTPDTTTAKYSIAWLKRFVDDDLRYEQFLCPAPDDFAISEYRSTCPFLEHHHHHH	2022.0	Weight loss;HPLC;VSI;SEM	The purified TPA was used for PET synthesis. A two-step polymer- ization of PET with the purified TPA and EG was performed.[60] The first step was an esterification reaction with TPA and EG to obtain BHET followed by a polycondensation reaction of BHET. The weight ratio of EG:TPA was 1.5Zinc acetate (150ppm), sodium acetate (150 ppm) and antimony oxide (500 ppm) were added as catalysts in the polycondensation reaction. TPA, EG and catalysts were added to a reactor and mixed overnight. The esterification was performed at 190 °C for 8 h under stirring. The reactor was then heated up to 220°C for 2h and the reaction mixture became transparent. The temperature was increased to 270–280 °C and a 3 mbar vacuum was applied for 3 h to remove the EG. The synthesized PET was of white and light-yellow color and was further characterized by FT IR and 1H NMR.Amorphous G-PET films (9cm2, about 150mg) were added to reaction vials containing 0.11 mg g of the partially purified enzyme preparation and enzyme PET 1 m potassium phosphate buffer (pH 8.0) in a total volume of 1.8mL. The vials were incubated at 40°C to 85°C on a thermoshaker (1000 rpm) for 1 h. 	NA (lab synthesised)		No				Yes		
Amycolatopsis sp.	37632	PCL	Zhang, H., Dierkes, R. F., Perez‐Garcia, P., Costanzi, E., Dittrich, J., Cea, P. A., Gurschke, M., Applegate, V., Partus, K., Schmeisser, C., Pfleger, C., Gohlke, H., Smits, S. H. J., Chow, J., & Streit, W. R. (2023). The metagenome‐derived esterase PET40 is highly promiscuous and hydrolyses polyethylene terephthalate (PET). The FEBS Journal, 291(1), 70-91.	Hydrolase	00228	00228 | Hydrolase | Amycolatopsis sp. | PCL PET PU	Yes	WAU86704	MAENPYERGPAPTTSSIEASRGSFATSTVTVSRLAVSGFGGGTIYYPTSTTAGTFGAISIAPGFTALQSSIAWLGPRLASQGFVVFTIDTLTTSDQPDSRGRQLLAALDYLTQQSSVRSRIDSSRLGVVGHSMGGGGTLEAARSRPSLQAAIPLTGWNLTKTWSTVRVPTLVVGAQADTVAPVASHSIPFYNSLPSSLDKAYLELRGASHFAPNSSNTTIAKYTLSWLKRFIDNDTRYEQFLCPIPSTSLSISDYRGNCPHNG	2023.0	Clear zone				No				Yes		
Amycolatopsis sp.	37632	PU	Zhang, H., Dierkes, R. F., Perez‐Garcia, P., Costanzi, E., Dittrich, J., Cea, P. A., Gurschke, M., Applegate, V., Partus, K., Schmeisser, C., Pfleger, C., Gohlke, H., Smits, S. H. J., Chow, J., & Streit, W. R. (2023). The metagenome‐derived esterase PET40 is highly promiscuous and hydrolyses polyethylene terephthalate (PET). The FEBS Journal, 291(1), 70-91.	Hydrolase	00228	00228 | Hydrolase | Amycolatopsis sp. | PCL PET PU	Yes	WAU86704	MAENPYERGPAPTTSSIEASRGSFATSTVTVSRLAVSGFGGGTIYYPTSTTAGTFGAISIAPGFTALQSSIAWLGPRLASQGFVVFTIDTLTTSDQPDSRGRQLLAALDYLTQQSSVRSRIDSSRLGVVGHSMGGGGTLEAARSRPSLQAAIPLTGWNLTKTWSTVRVPTLVVGAQADTVAPVASHSIPFYNSLPSSLDKAYLELRGASHFAPNSSNTTIAKYTLSWLKRFIDNDTRYEQFLCPIPSTSLSISDYRGNCPHNG	2023.0	HPLC	Impranil	Covestro AG		No				Yes		
Amycolatopsis sp.	37632	PET	Zhang, H., Dierkes, R. F., Perez‐Garcia, P., Costanzi, E., Dittrich, J., Cea, P. A., Gurschke, M., Applegate, V., Partus, K., Schmeisser, C., Pfleger, C., Gohlke, H., Smits, S. H. J., Chow, J., & Streit, W. R. (2023). The metagenome‐derived esterase PET40 is highly promiscuous and hydrolyses polyethylene terephthalate (PET). The FEBS Journal, 291(1), 70-91.	Hydrolase	00228	00228 | Hydrolase | Amycolatopsis sp. | PCL PET PU	Yes	WAU86704	MAENPYERGPAPTTSSIEASRGSFATSTVTVSRLAVSGFGGGTIYYPTSTTAGTFGAISIAPGFTALQSSIAWLGPRLASQGFVVFTIDTLTTSDQPDSRGRQLLAALDYLTQQSSVRSRIDSSRLGVVGHSMGGGGTLEAARSRPSLQAAIPLTGWNLTKTWSTVRVPTLVVGAQADTVAPVASHSIPFYNSLPSSLDKAYLELRGASHFAPNSSNTTIAKYTLSWLKRFIDNDTRYEQFLCPIPSTSLSISDYRGNCPHNG	2023.0	HPLC	PET powder	Goodfellow	Yes	No				Yes		
Humicola insolens	34413	PET	Brackmann, R., de Oliveira Veloso, C., de Castro, A. M., & Langone, M. A. P. (2023). Enzymatic post-consumer poly (ethylene terephthalate)(PET) depolymerization using commercial enzymes. 3 Biotech, 13(5), 135.	Cutinase			No			2023.0	HPLC	PET samples were obtained from post-consumer non-carbonated mineral water bottles (Crystal® brand). The post-consumer PET (PC-PET) presents an intrinsic viscosity of 0.7453 ± 0.0032 dl g−1, molar mass equal to 42,737±288 g mol−1, a polymerization degree of 222.4 ± 1.5, and crystallinity of 36.6 ± 0.5% (Castro et al. 2017). Before the hydrolysis reaction, PET squares of approximately 0.5 cm with 0.1 mm thickness were washed with detergent, subsequently with distilled water, and finally with a mixture of water and ethanol (1:1 volume ratio) for 10 min using orbital stirring (200 rpm) and then dried using the Moisture analyzer (Mettler HB43-S) at 105 °C.		No	Yes				Yes		
Candida antarctica	84753	PET	Brackmann, R., de Oliveira Veloso, C., de Castro, A. M., & Langone, M. A. P. (2023). Enzymatic post-consumer poly (ethylene terephthalate)(PET) depolymerization using commercial enzymes. 3 Biotech, 13(5), 135.	Lipase			No			2023.0	HPLC	PET samples were obtained from post-consumer non-carbonated mineral water bottles (Crystal® brand). The post-consumer PET (PC-PET) presents an intrinsic viscosity of 0.7453 ± 0.0032 dl g−1, molar mass equal to 42,737±288 g mol−1, a polymerization degree of 222.4 ± 1.5, and crystallinity of 36.6 ± 0.5% (Castro et al. 2017). Before the hydrolysis reaction, PET squares of approximately 0.5 cm with 0.1 mm thickness were washed with detergent, subsequently with distilled water, and finally with a mixture of water and ethanol (1:1 volume ratio) for 10 min using orbital stirring (200 rpm) and then dried using the Moisture analyzer (Mettler HB43-S) at 105 °C.		No	No				Yes		
Rhizomucor miehei	4839	PET	Brackmann, R., de Oliveira Veloso, C., de Castro, A. M., & Langone, M. A. P. (2023). Enzymatic post-consumer poly (ethylene terephthalate)(PET) depolymerization using commercial enzymes. 3 Biotech, 13(5), 135.	Lipase			No			2023.0	HPLC	PET samples were obtained from post-consumer non-carbonated mineral water bottles (Crystal® brand). The post-consumer PET (PC-PET) presents an intrinsic viscosity of 0.7453 ± 0.0032 dl g−1, molar mass equal to 42,737±288 g mol−1, a polymerization degree of 222.4 ± 1.5, and crystallinity of 36.6 ± 0.5% (Castro et al. 2017). Before the hydrolysis reaction, PET squares of approximately 0.5 cm with 0.1 mm thickness were washed with detergent, subsequently with distilled water, and finally with a mixture of water and ethanol (1:1 volume ratio) for 10 min using orbital stirring (200 rpm) and then dried using the Moisture analyzer (Mettler HB43-S) at 105 °C.		No	No				Yes		
Nigrospora oryzae	335854	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Nigrospora oryzae	335854	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Nigrospora oryzae	335854	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phanerochaete chrysosporium	2822231	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phanerochaete chrysosporium	2822231	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phanerochaete chrysosporium	2822231	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Schizophyllum commune	5334	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Schizophyllum commune	5334	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Schizophyllum commune	5334	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Fusarium decemcellulare	57161	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Fusarium decemcellulare	57161	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Fusarium decemcellulare	57161	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Coprinellus bipellis	2726693	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Coprinellus bipellis	2726693	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Aspergillus fischeri	36630	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Aspergillus fischeri	36630	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Aspergillus fischeri	36630	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Schizophyllum commune	5334	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Schizophyllum commune	5334	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Schizophyllum commune	5334	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Fusarium pseudensiforme	986114	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Fusarium pseudensiforme	986114	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Fusarium pseudensiforme	986114	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Hypoxylon sp.	1896109	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Hypoxylon sp.	1896109	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Hypoxylon sp.	1896109	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Curvularia lunata	5503	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Curvularia lunata	5503	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Curvularia lunata	5503	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Coprinellus aureogranulatus	752674	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Coprinellus aureogranulatus	752674	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Coprinellus aureogranulatus	752674	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Xylaria sp.	1715255	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Xylaria sp.	1715255	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Xylaria sp.	1715255	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phlebiopsis flavidoalba	467968	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM;CO2	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phlebiopsis flavidoalba	467968	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM;CO2	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phlebiopsis flavidoalba	467968	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM;CO2	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Prerenniporia tephropora	467968	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Prerenniporia tephropora	467968	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Prerenniporia tephropora	467968	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Flavodon ambrosius	1958834	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Flavodon ambrosius	1958834	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Flavodon ambrosius	1958834	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Prerenniporia tephropora	1958834	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Prerenniporia tephropora	1958834	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Prerenniporia tephropora	1958834	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phlebiopsis sp.	1968779	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phlebiopsis sp.	1968779	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phlebiopsis sp.	1968779	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phanerochaete pseudomagnolia	1968779	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phanerochaete pseudomagnolia	1968779	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phanerochaete pseudomagnolia	1968779	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Arcopilus aureus	79815	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Arcopilus aureus	79815	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Arcopilus aureus	79815	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Prerenniporia tephropora	79815	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Prerenniporia tephropora	79815	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Prerenniporia tephropora	79815	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Xylaria sp.	1715255	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Xylaria sp.	1715255	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Xylaria sp.	1715255	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Xylaria feejeensis	498163	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Xylaria feejeensis	498163	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Xylaria feejeensis	498163	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phlebiopsis sp.	1968779	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Laccase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phlebiopsis sp.	1968779	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Lignin peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Phlebiopsis sp.	1968779	LDPE	Perera, P., Herath, H., Paranagama, P. A., Wijesinghe, P., & Attanayake, R. N. (2023). Wood decay fungi show enhanced biodeterioration of low-density polyethylene in the absence of wood in culture media. Plos one, 18(7), e0288133.	Manganese peroxidase			No			2023.0	Weight loss;tensile strength;WCA;FTIR;SEM	Transparent 37.5 μm LDPE sheets were purchased from a local polyethylene vender (Southern Lions Poly Print Pvt., Ltd., Sri Lanka). As per the producer of LDPE sheets, no specific additives were used during the production procedure using pellets (Personal communication, Southern Lions Poly Print Pvt., Ltd., Sri Lanka). Polyethylene sheets were surface sterilized with 70% ethanol for 2 min. followed by three serial washings with sterilized distilled water. A preliminary study confirmed that surface sterilization with 70% ethanol was sufficient for the complete removal of microbial contaminants in LDPE sheets [12]. Surface sterilized three LDPE sheets (2 cm x 10 cm x 37.5 μm) were added to each flask.	Southern Lions Poly Pvt.		No	Decayed hardwood	Dry zone forest reserve	Sri Lanka	No		
Clonostachys rosea	29856	PCL	Gambarini, V.; Pavlov, N.; Young, P.; Dawes, S.; Auffret, A.; Kingsbury, J.M.; Donaldson, L.A.; Smith, D.A.; Weaver, L.; Pantos, O.; Handley, K.M.; Lear, G. (2025). Molecular mechanisms of plastic biodegradation by the flar Mechanisms of Plastic Biodegradation by the Fungus Clonostachys Rosea. Mbio.	PETase	00229	00229 | PETase | Clonostachys rosea | PCL PET	Yes		MKFFTAITLFTALVAGAPLGMEELETRQSSTSTDLERGSSSNCPSAILIFARGSTEIGNMGSSVGPALSGALSQKVRGIWVQGVGGPYDAALGDNALPRGSSSSAIAEGVRLFKLAKSKCPNASVVAGGYSQGAALIAAAISDLDSSTRDQVKGAALFGYTQNKQNNGRIPNYPADRTKVYCAVGDLVCEGLLIVAPPHLTYNDEARGEAADFLASKV	2025.0	Clear zone;weight loss	PCL acquired from Sigma Aldrich (New Zealand; product 440752).  Pellet form and average molecular weights of 14,000 g/mol	Sigma Aldrich	Yes	No	Soil	Soil	New Zealand	No	g9562.t1	
Clonostachys rosea	29856	PET	Gambarini, V.; Pavlov, N.; Young, P.; Dawes, S.; Auffret, A.; Kingsbury, J.M.; Donaldson, L.A.; Smith, D.A.; Weaver, L.; Pantos, O.; Handley, K.M.; Lear, G. (2025). Molecular mechanisms of plastic biodegradation by the flar Mechanisms of Plastic Biodegradation by the Fungus Clonostachys Rosea. Mbio.	PETase	00229	00229 | PETase | Clonostachys rosea | PCL PET	Yes		MKFFTAITLFTALVAGAPLGMEELETRQSSTSTDLERGSSSNCPSAILIFARGSTEIGNMGSSVGPALSGALSQKVRGIWVQGVGGPYDAALGDNALPRGSSSSAIAEGVRLFKLAKSKCPNASVVAGGYSQGAALIAAAISDLDSSTRDQVKGAALFGYTQNKQNNGRIPNYPADRTKVYCAVGDLVCEGLLIVAPPHLTYNDEARGEAADFLASKV	2025.0	Clear zone;weight loss	5 mg of PET powder and films were incubated in 2.5 ml of PBS buffer with different enzyme concentrations		Yes	No	Soil	Soil	New Zealand	No	g9562.t1	
Clonostachys rosea	29856	PCL	Gambarini, V.; Pavlov, N.; Young, P.; Dawes, S.; Auffret, A.; Kingsbury, J.M.; Donaldson, L.A.; Smith, D.A.; Weaver, L.; Pantos, O.; Handley, K.M.; Lear, G. (2025). Molecular mechanisms of plastic biodegradation by the flar Mechanisms of Plastic Biodegradation by the Fungus Clonostachys Rosea. Mbio.	PETase	00230	00230 | PETase | Clonostachys rosea | PCL	Yes		MPSLIVMAGLARLLVSGTLAAGLGAYNVDPNSVSVSGLSAGGFMAAQLGVAYSDTFKTGFGIFAGGPYDCARNQLYSSCMNNQNPSITKPVANMQSWSGNQIDPLANLQSRQIYMQVGSADRTVGPKPMNQLKAQLANFDDSSRVSFVTTVGAAHVFPTDFDGSGNNACGETRSPYISNCGYDGAGAVLKWMYGDLVPRNNGQLSGTLLSFSQTGTYGASGMDSTGYIYVPQACQGGSSVCKLHVALHGCAQSYGQIGAKFINNSGYNKWADTNNIIIHYPQAKTDYSVHPVWGGLILNNPNACFDWVGWYGSNADQKGGVQVQALVNQVNQITSGYTG	2025.0	Clear zone;weight loss	PCL acquired from Sigma Aldrich (New Zealand; product 440752).  Pellet form and average molecular weights of 14,000 g/mol	Sigma Aldrich	Yes	No	Soil	Soil	New Zealand	No	g16887.t1	
Rhizobacter sp.	1909292	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00231	00231 | PETase | Rhizobacter sp.  | PET	Yes	MBX3624429.1	MARFTQASVLAAAALFAGVASAQYQKGPDPTVAGLERDGTFAIRTTTVSRLSASGFGGGTIYYPTATGSYGVVAVSPGFTAYQSSISWIGSRLASHGFVVITIDTNTTSDQPDSRARQLKAALDKVVSLASSRTNVLYGKVDSSRLAVAGHSMGGGGSLAAARDYPSLKASVPLAPWHTTKSFSTVRVPTLIVGADGDTVASVTSHSIPFYTSIPSSTPKGYLELNNEDHFFPQDSGEYGLVGKYMISWFKRFVDSDTRYSPFLCGAPHQTQIANTLRVSDSRTNCPY	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Piscinibacter gummiphilus	946333	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00232	00232 | PETase | Piscinibacter gummiphilus | PET	Yes	MBX3624429.1	MARFTQASVLAAAALFAGVASAQYQKGPDPTVAGLERDGTFAIRTTTVSRLSASGFGGGTIYYPTATGSYGVVAVSPGFTAYQSSISWIGSRLASHGFVVITIDTNTTSDQPDSRARQLKAALDKVVSLASSRTNVLYGKVDSSRLAVAGHSMGGGGSLAAARDYPSLKASVPLAPWHTTKSFSTVRVPTLIVGADGDTVASVTSHSIPFYTSIPSSTPKGYLELNNEDHFFPQDSGEYGLVGKYMISWFKRFVDSDTRYSPFLCGAPHQTQIANTLRVSDSRTNCPY	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Pseudomonas fluvialis	1793966	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00233	00233 | PETase | Pseudomonas fluvialis | PET	Yes	WP_184682765.1	MNAKLSLGKTLLLAASLLVSATAFSATGPSSPCSNCTRGPDPTVASLKSATGPYTTAKFSVSGYLKGFGDSTVYYPTNASGKMGAIAVIPGYVSYEDSIKWWGPRLASHGFVVMTMNTSTIYDQPDSRATQLSKALDYMIAQSGSSSSPIYNKVDSTRLGVIGWSMGGGGTLKLSTQRSINAIIPQAPYYAGSNSFNTIKTPALILACGADAVAPVGVHASPFYNRIPGTTPKAYLEIYGGSHFCANSGYPNEDLLGMYGIAWMKRFIDFDSRYSKFLCGPNHTADLNISEYRQNCNY	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Rhizobacter sp.	1909292	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00234	00234 | PETase | Rhizobacter sp. | PET	Yes	MBX3621832.1	MKIQQFLKAALLVGAGLITASASAVQIGPNPTKSSLEASRGPFSTSQFTVSRPSGYGAGTVYYPTNAGAKVGAIAIVPGFLSYQSSINWWGPRLASHGFVVITIDTYTTGDQPDSRSRQQLAALDQVIALGNTSSSPIYGKVDGSRTGVMGWSMGGGGSLISAKNRPSIKAAAPQAPWNTSTNFSSVTVPTLIFACQSDIVAPVISHAIPFYNSMTRNPKQYLEKTLGDHFCFNNANATVGLKGVAWMKRFVDGDTRYTSFACSNPNAFGFSDFRTARCS	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Pseudomonas subflava	2952933	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00235	00235 | PETase | Pseudomonas subflava | PET	Yes	WP_252275389.1	MKASLATAALFVASLLVSSHVLSAPGPSAPCSNCTRGPNPTEASLKSDRGPFTTARFSVSGFLKGFGDSTVYYPTNTTGRMGAIAVIPGYLSYESSIEWWGPRLASHGFVVMTMNTSTIYDQPDSRATQLSKALDYLIAQSNTSSSPIYNKIDSTRLGAIGWSMGGGGSLKLSTQRSLNAIIPQAPWYSGSNSFNTIKTPALILACSADTVAPVSVHASPFYNRIPGSTPKAFLEIYGGSHFCANSGYPNEDLLGLYGIAWMKRFIDFDNRYSQFLCGPNHEGDFAISDYRQNCPY	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Rhizobacter sp.	1909292	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00236	00236 | PETase | Rhizobacter sp. | PET	Yes	MBT9528079.1	MKITAHNTARGVANFAKASLFVAALTVSALANAQYQKGPDPTVSALERTGSFATRTTTVSRTSASGFGGGTIYYPTASGSYGAIAISPGFTAYQSSISWMGTRLASHGFVVITIDTITTSDQPDSRGRQLKAALDKVVSLSRSSSSPIYNKVDTTRLAVAGHSMGGGGTLAAARDYPSLKAAVPLAPWHTTKSWSRVTVPTLIIGGSTDTIASVGLHSIPFYTSLPSSTNKAYMELSGEGHFFPQTSSNYPLVGRYMISWFKRFVDGDSRYSPFLCGAQHQADLGLFSDISDYRENCPY	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Halopseudomonas yangmingensis	1720063	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00237	00237 | PETase | Halopseudomonas yangmingensis | PET	Yes	WP_093473685.1	MKHNMHKLALSLLATGALMFSSAALASNPAPDTGSGDGSSSQYQIGPDPTVSFLEASSGPFSVRTSNVSSLVSGFGGGTIHYPTGVNRPMAAIVVIPGFVSAESSIDWWGPKLASYGFVVMTIGTNSGFDQPPSRARQINNALDYLVAQNTNSRSPVNGMIDTNRLGAMGWSMGGGGTLRVAEEGRIKAAIPLAPWDTTSFRSNRTPTLIFACGSDSIAPVRTHASPFYNQIPTSTPKIFIEINRGNHYCANGGNSNNATLGRLGVAWMKRFLDEDRRYSQFLCGPRHTSDRNISESRDTCNF	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Jonesia denitrificans	43674	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00238	00238 | PETase | Jonesia denitrificans | PET	Yes	ACV09511	MPIVRHRFFLHYVRTHKSGVIVRLRVLPTPIRKDTHVRRILALCVTLALLVIPTGSVAHAADTPYERGPNPSESLIEQRRGNYDIAQRSISRFSSDGFRNGTIYYPTDTSDGKFGVIAISPGYTAGESSIAWLGSRIASFGFVVVTINTTTRYDQPRQRSTQLLAALDHAMNDSVVGPLIDPERQAVMGHSMGGGGALQAAESRPEIDAVVALTPWNLKKNWDGVDAATLIIGAERDTVASVRTHSIPFYESLTQAEQRGYLELRGASHFAPNVSNTTIAKYSIAWMKRYLDNDDRYDQFLNPGPAVGYASGVSDYRLQ	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinokineospora alba	504798	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00239	00239 | PETase | Actinokineospora alba | PET	Yes	TDP67440.1	MRMSLIRKLAAIPAALLLFGAAATVASPAGAAIEHRRGPAPSEQSVLAANGPFSHSTFAVSDAASAKFGKGTIYYPNDTSQGTFGGVAISPGYTSTEPHIAWLGTRLAAHGFVTITITTNSLYDNPTERGQQLLAALDYLANNAPLAIRQRLDTSRMGVVGHSMGGGGSLYAVWNRPALKAAVPLAPYHTIKNWSGIKTPTMIIGGSADGVAPVEEHSERFYSSMTYARERAYAELEGANHSGSFLFEDHPIIGKFTVAWLKRFIDGDTRYDQFLCPPPTGAYLTEYRASCPHA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinokineospora spheciospongiae	909613	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00240	00240 | PETase | Actinokineospora spheciospongiae | PET	Yes	WP_035284691	MRISKKIAVAIPAALAIAGAGVVVAIPDAGAAQTSQVVTANPHQRGPDPTPETVRAPQGTFAFSTYSVPASVTGFGQGTIYYPDDTTQGTFAGVAISPGYTGPEASVAWLGPRLASRGFVVITITTNSRYDQPTSRGKQLLAALDYLTKQSPTEVRQRLDATRLGVMGHSMGGGGALYAAYKRPSLKAAVPLAPWNLIKNWSGIRVPTLVVAGTADKTASAGAHSLPFYSSMTGARERAFADVTGADHLTFVREDPVIGALAVSWLKRFLDDDTRYAPFITEPVGLSRFLCSCPYAG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Herbihabitans rhizosphaerae	1872711	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00241	00241 | PETase | Herbihabitans rhizosphaerae | PET	Yes	WP_130342639	MRRRPRIVVGILSVLTLILATIAGIAGASFATAAPDTVVGNPFARGPDPTKESIEAERGPFAVATEKVPGGKGFGGGTIHYPTDTSQGTFGAIAVAPGFTESESAIAWYGPRLASQGFVVITISTNGLWDLPASRADQLLAALRHVTDASQIKSRVDRDRLAVMGHSMGGGGSLIAARNNPALKATIPLTGWNPNTSFSDLKVPTFVVSAQNDFIAPDGSHSRPFYQSLPASLNKAYMRLAGVGHMAPVNPNVTIAKYSISWLKRFVDNDTRYSQFLCPLPTGDPKIAAYEGTCPLS	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinomadura physcomitrii	2650748	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00242	00242 | PETase | Actinomadura physcomitrii | PET	Yes	WP_151597653.1	MHRNLAHSFRLLSVAAVLASGAALAPSASAATPARPASVAAAPAAVQRAADNPYQRGPAPTEASITAEKGPFAVETIPVPAGSGTGFNKGTVYAPTDTSEGTFGAIVVSPGFVSPEAWISWYGPRLASQGFVVMTLETNSLVDVPASRGDQLLAALDWLTGKSSVKNRIDASRTAVMGHSMGGGGTLEAANKRPSLKADIPLAPWDTNYNFPNIKTPTLIMGADNDLIAPASSMAESYYNNITTAPEKAYLLLKNAGHMTFVSPNTTIAKYSIAWMKRFVDNDTRYDQFLCPAPKPDANIAKYLDTCPNG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinokineospora xionganensis	2684470	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00243	00243 | PETase | Actinokineospora xionganensis | PET	Yes	WP_187224800.1	MPTLSRRLAVAAAAVAVVFVSVDASAAENPHQRGPNPTVAALEAAAGPFAVAKVSVPGGHGFGGGTITYPTDTSQGTFGAVAVSPGFIESEGAIAWFGPRLASHGFVVITISTNGLFDQPDARGAQLLAALDYVTKSSAVRDRVDPARLAVMGHSMGGGGALYATAQRPALKASIPLLAWSNTKSWGSVRVPTMVIGAENDFIASVGSHSEPFYQSLGGEKAYLEMNDADHFVTNSPTPTVGKLTVSWLKRFMDNDTRYDQFLCPAPPVGGPISEYRDTCPYI	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Dactylosporangium sp.	60453	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00244	00244 | PETase | Dactylosporangium sp. | PET	Yes	MBT8227529.1	MPRPPSEPAPSPTSGVPAPHHRLRHPARGPRGLPLAGAAVGLLLLGSAVAARSALAADNPYQRGPAPTAASISADTGPFATATTVAEGTGFGGATIYYPTDTSQGTFGAIGMLPGWTAPWSAYAWLGPRLASQGFVVIGVDTNDPNDYPAARATQVLAALDHLTESSAVRDRVDPDRLAVAGHSMGGGGSLEAALSRPSLKAVYGIEPYDDITSDFSNLTVPTFIQAGQDDTLVTPSYLESLYATLPSTSEHAYLEIAGADHMFVGSPNVILARTLISWMKIFVDDDTRYTQFLCPLSDDSGVSQYRNTCPLTPGGSTGSPTATAPSPPASSSNPPGTPSSPAPTDGTCRVTYTTNAWDSGLTASVTIANTGTTASTGWSLAFTLPDGQTITSGWNATYSPSSGQVTATGVSHNATIPAGESINIGFQATHTGDTGAPTTFALNGQTCTIT	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinokineospora spheciospongiae	909613	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00245	00245 | PETase | Actinokineospora spheciospongiae | PET	Yes	WP_233427406.1	MRREIVKRSAVLTAALAVGASAFLGPQAFAGQAAVPVAVAGTSAFAKGPDPTEQSIQAQRGPFATAQRTVPSEAGRAFNRGTVHYPTDTSHGTYGAVVVSPGFFGPEFSVAWYGSTLASHGFVVLTLETNFLFDQPDARATQLLAGLDWLAARSPVKDRVDPNRLAVMGHSMGGGGTLIAASRNPALKAAIPLTPWNTSPDFSTVTVPTLVLGTDNDTVAPVARHADPMYASLRDKPDEGYVKLRGDHFTPIRYTAAATRFIVPWLKRYVDEDTRYSRFLCPLPAPDATLVSFELRCPV	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinoplanes sp. DH11	2857011	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00246	00246 | PETase | Actinoplanes sp. | PET	Yes	WP_229068674.1	MSDENRMPSASRRSSITLVRRALTAIALTAGLAATSAAQPASAAANPYQRGPAPTAASVAAVTGPFATASVSVPRGNGFGGGVIYYPTDTSQGTFGGLAISPGLNGTWPGIAWLGSRLASQGFIVFGIETNNLNDSPTSRGTQLLAALDYLAQRSSVRSRLDPGRLAVAGHSMGGGGALDAALRRPSLKAAIGNAPYLPSNTLAGNRVPTLIYAMQNDTLVPPSRLTSLYNTIPATTERAYLEITGAGHNYIGQPSTTLARTMIPWLKIFIDNDTRFSQFLCPLADQSGIRQYRSSCPLVPATTRALTAAAG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinomadura rayongensis	1429076	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00247	00247 | PETase | Actinomadura rayongensis | PET	Yes	WP_161104454.1	MPLWSHARPKTALTAVAAFAALTSVTAVGAPAHADTNPFQRGPAPTEASVSAQKGPFATAQVNVPANSGEGFNDGTIYYPTDTSQGTFGAIAVMPGFLSPQDWIRWYGPTLASQGFVVMTLDSKGFIDSPTARGNQLLAALDYLTTKSKVVDRIDTSRLGVVGWSMGGGGALESTYNRPSLKADVALAPWHVGLDQSKITVPSLILADDNDWLAPTGSFAKPFYAGIPESTNKAFIELKNANHFTFTGYNKNIAKYAVSWLKRFVDDDTRYDQFLCPKPATNNEISQSEETCPLH	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinomycetes bacterium	1883427	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00248	00248 | PETase | Actinomycetes bacterium | PET	Yes	MGYP001489421514	MRGMRKPGGLRRRVRTAIVGATAVALCLTGASLTTSAAQAQSSNPYQRGPAPTERSIEASRGPFAVAQTTVSRLSATGFGGGTIYYPTDTSQGRFGGVAISPGFTALQSSIAWLGPRIASQGFIVFTIDTITTLDQPAQRGDQLLAALDYLVQRSPAAVRDRLDPTRLAVMGHSMGGGGTLEAAKKRPSLKAAIPLTGWNLDTIWNDLRVPTLVVGAQLDLIAPILTFSLPFYNTIPASTEKVYLELAGASHFAPNLPDTNIAKYSIAWLKRWVDNDTRYTQFLCPGPRFELAISNYMSSCPM	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Acidimicrobiales bacterium	2201156	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00249	00249 | PETase | Acidimicrobiales bacterium | PET	Yes	MBN2622270.1	MLTSVARGRGRLAKIALAASLVGGSLVSGATSAGAQSNPYERGPAPTESSIEATRGSFSVSDKNVSSFSASGFGGGTIYYPTDTSQGTFGGVAISPGFTAGESSIAWLGPRIASQGFVVITIDTNSRYDQPNSRADQLQAALDHIVADSTVGSRIDPNRLAVMGHSMGGGGSLKAAEDNADLQAAVPLQPWHTQKNWSDVEVPTLIIGAENDSVASVTTHSKPFYTSLPDDLDKAYLELDGASHFVSNTPDTTTAKYSISWLKRFVDDDTRYEQFLCPAPDDRTISEYRDTCPHSGGGGTTPTTTPTTLPPDDDCAWWQWWC	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonosporales bacterium	2201156	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00250	00250 | PETase | Micromonosporales bacterium | PET	Yes	MGYP001121581011	MRRDTRHHPPSVGTEVGRGSPGPGRRLITLAATGAALTLGTVTALVATGSASMADNPYQRGPDPTPALVASVNGPFATASVSVPAGYGFGGGMIYYPTDTSQGTFGGIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNNRNDFDEARGTQLLAALDYLTQQSPVRNRVDPNRLAVAGHSMGGGGALNAAIRRPSLKAAVGLAPFSPSSNLANDRVPTMVFSGQQDTVVTPSYVTGLYNSLPSTTQSAYLEIAGGDHGFPVGRPNQVMIRTMLPFVKIFVDYDTRYSPFLCPLSDTSGVVTYRSTCPLTPPGLPTTPPTTPPTTVPTSPPTGGPTTPPTTPSQPGGACTATYRTVNSWPGGFQGEVTVTAGNSAINGWTVRWTLDSGQAITQVWNGEVSTSGSTVSVRNAPYNGSLPPSGSTTFGFLSSGSPSSPSLTCTSP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Paractinoplanes polyasparticus	2201156	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00251	00251 | PETase | Paractinoplanes polyasparticus | PET	Yes	WP_221382552.1	MRGHRHHPSLSRNTHADRASRGFRGRLFRIVTAGVAAAVGLFAIALTAGTASAADNPFQRGPDPTRASVAAQTGPFANASVSVPTGYGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRVDPNRLAVSGHSMGGGGALSAASRRSSLKAAVGITPYSPSSNLANDRVPTMIISGQADTVVTPSYALGLYNSLPATTESVYLEVAGGDHGFMVGRSNPVMIRTMLPFVKMFIDNDTRYSQFLCPLADSSGVVTYRSTCPLLPGAPTTPPTTPPTDSPGSAGEIVGTQSGRCIDVPNAARDNGTRVQLYDCNKQPNQSWTYTSNKQLQVYGDRCLDAAGSGNGAAVQIYSCHSQTNQQWNLNSNGTISNVQSGRCLDVWSTANGAQVQLYDCHGQTNQQFRLASRTR	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonosporales bacterium	2201156	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00252	00252 | PETase | Micromonosporales bacterium | PET	Yes	MGYP000271253724	MAAGPAAVAADNPYQRGPDPTPASVAAPNGPFATAQVSVPPGYGFNGGMIYYPTDTSQGTFGAIAISPGYTALFSVELAWMGPRLASQGFVVIGIETNDRNDFDTARGTQLLAALDYLTGQSSVRSRVDPNRLAVAGHSMGGGGAFSAALRRPALKAAVGFTPFSPSQNLTNMQVPALLYSGQYDTVTTPSSVSNLYNGLPSTTEGAYIEAAGLDHSFPTRPNTLLMRTMIPWVKIFLDNDLRYTQFLCPLMDSSGVLQYRNTCPLVPPGLPSPSPTTAPPTTAPPTTAPPPTTAPPPTTAPPPTTAPPPTTNPPAGACSVSYTTNQWPGGFTRDVRITNTGGSVSSWTLAFTAGSNVSLSNGWNGDWSQSGSQITVRNAAWNGSLASGATVSIGFQGTFSGSTLPPLSNITLNGAACAS	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Thermoleophilaceae bacterium	2732252	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00253	00253 | PETase | Thermoleophilaceae bacterium | PET	Yes	MBJ7347705.1	MTNQTRTTRPTRLWIVAALSACLLLIGAASAFAANPYERGPDPTLASVEATSGTFAYASLSVSSGNGFGGGTIYYPTSTTDGTFAGIVTCPGFTNSGSSMAWFGKVLASQGFVTLVMNPKSNLDFPDARATQMLAALDWLTNSSSVKTRIDATRLGVLGQSMGGGATLKASKTRPSLKASFATAPYNSDKDWSTNTVPQFLFGMQNDTTAAVTNHALKFYNSLPATTPKIYAELRGAGHSTATSPNTSIRRYAVSFMKRNLDNDTRYSQFLCPGPTITSSSPLSAFMSNCLF	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonosporales bacterium	2732252	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00254	00254 | PETase | Micromonosporales bacterium | PET	Yes	MGYP000221121644	LFDNNGNKKQAYDATLSALNAGGTPVSPSPSVSPTAGPSPSTSPSPSPPPGDNPYQRGPDPTRDSVAANRGTFATAEMSVSPGNGFNGGSIYYPTDTSQGTFGAVAIVPGYTARFADEEAWMGHWLASFGFVVIGVETNSTNDFDTARGTQLLAALDWLTQSSPVRDRIDASRQSVIGHSMGGGGALHAAGNRSSLKAAVGLTPFMPSGTPANNQVPTLMIAGTNDTVVAPSYVTDLYNALPSSTERAYMEFVGADHLFPTRPNNLEMRILIPWLKTFVDSDSRYTQFLCPLMDSSGIAGYRNSCPLLPDQPTPPPTPTPSPTTPTPDPTTPGPGTCTATMSTGQVWGDRYNTSVTVTGTSNWTVVVAITPPQRISATWNGNPTWDSSGNVMTIRANGNGNVFGFTTMFNGNSWARPQIRSCTAG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Paractinoplanes durhamensis	2732252	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00255	00255 | PETase | Paractinoplanes durhamensis | PET	Yes	WP_203733135.1	MSTPTRRNRGTVRNALIAVFAMILAFVAAPTAPALAANPYERGPAPTKASIEATTGYFATAKVTVAKSSVSGFGGGTIYYPTSTTSGTFGAIALVPGFTNVQSAVAWLGPRVASQGFVVFIIDTNSVYDSPDSRGTQLLAALDYLTNTSTVKSRVDATRLGVMGYSMGGGGALSATKTRTSIKASVPMAPYHSTKTWTTVKTPTLIVTGQSDTTAPPASHGLAFYNSLSTSIDKAYMELKGAGHSAPTSANTTIAKYSISWFKRFIDDDTRYDQFLCPNPTDTTISSYKSTCNYS	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Hamadaea sp.	2024425	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00256	00256 | PETase | Hamadaea sp. | PET	Yes	NUT34383.1	MQPRRLRLPAVLAAALTLALALGAPAHAASPYERGPNPTTAILEASSGPYSVSSVSVSSLVTGFGGGRIYYPTTTADGTFGGIAISPGFTARWSSLEWLGPRIASHGFVVIGIETNSIYDQPTSRGQQLLAALDYLVNSSSARTRVDRNRLAVAGHSMGGGGTLYAANARPSLQAAVPIAPWNTDKTWGGVQVPTMIIGGESDSVAPVATHAIPFYTSIPASSEKAYLELNNASHFFPQTVNTTMAKSMVSWLKRYVDDDTRYDPWLCPAPSGLSISDYRDTCPA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Promicromonospora panici	2219658	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00257	00257 | PETase | Promicromonospora panici | PET	Yes	WP_129786244.1	MQSFSRVFRAALAATALTVGTFGAVPAAVADDGYQRGPDPTEESIEAPRGTFEIGMAVVTRASADGFGGGTVYYPTDTSEGTFGAVAVSPGYSSSQAAIAWLGPRLASQGFVVFTIDTLSTSDSPTRRGDQVLAALSFLGRTELADRIDPDRLAVMGHSMGGGGSLEAAKDYPALQAIVPMTPWSVDKTFPEVTAPTLVIGAEDDVVARPRSHAEPIYESLPADGDKAYLELRDASHSAPSAPNTLIARYSLSWLKRYVDDDERYQQFLCPPPAVDDEISEYRSTCA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Streptomyces sp.	1931	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00258	00258 | PETase | Streptomyces sp. | PET	Yes	WP_233872418.1	MEPHSNEAERTTGRHKRTSRRRILSLGVAALFAIGGAGVAVPAAMAGETAQTTDVSAQSQFQRGPNPTVSSIEARTGHYRTSTTRVSSFASGFGGGTIYYPTTTSDGTFGGVAVAPGYTASSSTMDWLGPRIASQGFVVFVIDTNTRLDQPSSRGRQLLAALDYLTERSSERHRVDSNRLAVMGHSMGGGGALEATISRPSLKASIPLTPWNLTKNWSRVTTPTLIVGAENDSVASVRSHSIPFYTSLSSSTDRMYVELDGASHFAPNVSNTTIAKYSISWLKRFVDDDTRYDQFLCPLPNERAISDIRGNCPR	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Microbispora catharanthi	1712871	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00259	00259 | PETase | Microbispora catharanthi | PET	Yes	WP_139580723.1	MRPPRPRTRILAWIVAALLVIAGLAAGPSAASAAGNPYERGPSPTAASIAADRGPFATAQVTVPRGNGFGGGVIYYPTDTSQGTFGAIAIAPGFNTAWSYYAWQGPRLASFGFVVIGIETNTLNDYADARATQLLAALDYLVNSSPVRDRVDRDRLAVGGHSMGGGGALLAATQRPSLLTAVGQAPYVPNGNLSGIKSPTIIFAGQADGTVTPQYAQNAYNTIPADVERAYVEIANEGHGFPAGGGGGNSGAFARTMMVWLKLFIDKDTRYAPFLCPTLSNANGISKYMASCPLDPPGGGPTASPTASPTATPSSTPTGPPPATSALKGVASGRCLDVNGASQANGAQAQIWDCNGQNNQQWTTTSAGELRVYGNKCLDVNGGSTADGTSVIIWDCNGQNNQKWRLNSDGTITAVGANKCLDVSGAGTANGTKTQIWTCHGGTNQKWTRV	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Saccharothrix sp.	1873460	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00260	00260 | PETase | Saccharothrix sp. | PET	Yes	WP_267938240.1	MLGALAIVGGTRPATGADNPYQRGPDPTPASVSAGRGTFATAQVSVGAGNGFGGGVIYYPTDTSQGTFGAIAVVPGYTATWAAEGAWMGHWLASYGFVVIGIDTNTRNDWDTARGTQLLAALDYLTQRSSVRDRVDATRTAVMGHSMGGGGAAYASLQRPSLKTSVGLAPFSPSQNLTTTRVPTMLLSGQNDGTVTPSSVQNLYNGIPAGVEKAYLELTGAGHGFPTSNNPTMMRTVIPWFKIFVDSDTRYTQFLCPLADSNGIRTYQSTCPLVPSTPPTTTTTPTSTTTTSTTSTTPTTTTTTPQPGGACSATYRTVNSWSGGYQGEVTVTAGTSAVTGWTVRWSLGSGQTISQVWNGTLTVDGPTASVRNVSYNGSLGANASTTFGFIGGGTPPTSTLSCTSP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Microbispora	2005	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00261	00261 | PETase | Microbispora | PET	Yes	WP_167521412.1	MSPPQAPEPASRRAVSAYDTGPRRFAAAVLAGIVAVLLATAGAAGWPSAVSAADNPYQRGPAPTAASIAADRGPFATAQVTVPRGNGFGGGVIYYPTDTSQGTFGAIAIAPGFGTAWSYYAWQGPRLASFGFVVIGIETNTLNDYADARAAQLLAALDYLVNSSSVRDRVDRNRLAVGGHSMGGGGAILAANQRPSLLTAVGQAPYVPDGSLSGIKSPTIIFAGQADGTVTPQYAQNAYNTIPGSVERAYVEIANEGHGFPAGGGGGNSGAFARTMMVWLKLFVDKDTRYAPFLCPSLTNANGISKYMASCPLDPPGGGPTASPTSTPTSTPTSTPTSTPTGTPPAGGTSALRGVASGRCLDVNGASQANGATVLIWDCNGQNNQKWTSTSAGELRVYGNKCLDVNGGGTADGSAVIIWDCNGQSNQKWRLNSDGSITAVGANKCLDVSGNGTANGTRVQIWSCTGGTNQKWTRV	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Solwaraspora sp.	1912063	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00262	00262 | PETase | Solwaraspora sp. | PET	Yes	WBC00352.1	MAAGIVATSPAAVAADNPYERGPDPTPASVAAPNGPFATAQVSVPPGYGFNGGMIYYPTDTSQGTFGAIAISPGYTALFSVELAWMGPRLASQGFVVIGIETNDRNDFDTARGTQLLAALDYLTGQSSVRSRVDPNRLAVAGHSMGGGGAFSAALRRPALKAAVGFTPFSPSQNLTNMQVPALLYSGQNDTVTTPSSVSNLYNGLPSTTEGAYLEAAGLDHSFPTRPNTLLMRTMIPWVKIFLDNDLRYTQFLCPLMDSSGVLQYRNTCPLVPPGLPSPSPTTAPPTTAPPTTAPPTTAPPTTAPPTTAPPTTAPPAGACTATYQTIGSWPGGFQGEVTVRAGNSAINGWTVGWSLGSGQSITQIWNGTLSTSGSSVSVRNVSYNGSLPAAGTVTFGFLGSGSPSTPSTVTCTSP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Microbispora oryzae	2806554	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00263	00263 | PETase | Microbispora oryzae | PET	Yes	WP_210157342.1	MSSAETPGTIPRRVPDPHRAGVRSPRRPRTGFLAGIVAALLVLVGSVTMSTASAATNPYERGPAPTGTSVAADRGPFATAQLTVAKGNGFGGGVVYYPTDTSQGTFGAIAIAPGYGTEWRWYAWLGPRLASFGFVVLGIETNSLDDYADARGAQLLSALDWLVDSSPVRDRVDRTRLAVGGHSMGGGGALTAAIQRPSLMTAIGMAPYVPDGILRTIKIPTVLFGGQTDTTVTPSYLASAYATIPATVQRAYPEIANEGHGFAAGGGGGNSGAFARTMMIWMKVFIDKDTRYTGFLCPTLSNMSGISKYQASCPLGPTSGPSQSPSSSPSSTPSSSPSSTPSVSPSSTPSASPPGGPCRATYRTVNSWSGGYQGEVTVTAGGSAVNGWTVKWALSGGQSVTQVWNGTLSASGSNVSVSNASYNGSLGAGASTTFGFLANGTPSTPSPTCTSP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Microbispora triticiradicis	2200763	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00264	00264 | PETase | Microbispora triticiradicis | PET	Yes	MBO4274871.1	MAGAAGWPSTASAADNPYQRGPAPTAASIAADRGPFATAQVTVPRGNGFGGGVIYYPTDTSQGTFGAIAIAPGFSTAWSYYAWQGPRLASFGFVVIGIETNTLNDYADARAAQLLAALDYLVNSSSVRDRVDRNRLAVGGHSMGGGGAILAANQRPSLLTAVGQAPYVPDGSLSGIKSPTIIFAGQTDGTVTPQYAQNAYNTIPGSVERAYVEIANEGHGFPAGGGGGNSGAFARTMMIWLKLFVDKDTRYAPFLCPALTNANGISKYMASCPLDPPGGGPTASPTSTPTSTPTSTPTGSPPTGSTSSLRGVASGRCLDVNGASQSNGATVLIWDCNGQSNQKWTSTSASELRVYGGKCLDVNGGGTADGTAVIIWDCNGQNNQKWRFNSDSSITAVGANKCLDVSANGTANGTRVQIWSCTGGGNQKWTRV	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Microbispora sp.	1898321	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00265	00265 | PETase | Microbispora sp. | PET	Yes	WP_232326807.1	MTLLLVFAGAAALSPTASADVNPFQRGPDPTAAGVAAARGPFATAQVTVPAGNGFGGGVVYYPTDTSQGTFGAIAIAPGYGTAWSYYAWQGPRLASFGFVVIGIETNTLNDYADARAAQLLAALDWLVTSSPVRDRVDRNRLAVGGHSMGGGGALLAAIQRPSLMTAIGMAPYVPGGDLSGIRIPTVLFAGQTDGTVTPSYALSAYTTIPGSVERAYVEIANEGHGFPAGGGGGNSGAFARTEMIWMKLFIDKDTRYAPFLCPSLSNMNGISRYQASCPLDPPGGTTPTPSATPTSSPTSTPTSTPSATSALRGAGSSRCLDVPGASQTNGTQLQIWDCNGQANQRWTSTSAGELRVYGGKCLDVNGAGTADGTSVIIWDCNGQNNQKWRLNSDGSITAVGANKCLDVSGAGTANGTKVQIWTCNGQANQRWTRT	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Phytohabitans rumicis	1076125	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00266	00266 | PETase | Phytohabitans rumicis | PET	Yes	GFJ87714.1	MAVIAVVLGLVAVTVAAQSASAADNPYQRGPDPTLASVSAQRGTFATAQVAVPAGDGFGGGMIYYPTDTSQGTFGAVAIVPGYTARFSVEEAWMGHWLASFGFVVIGVETNSTNDFDTARGTQLLAALDYLTQRSSVRDRVDASRQSVVGHSMGGGGALYAAGQRASLKAAVGLAPYKPSGNPTNVRVPTMIISGQNDTVVTPSYATGLYNTLPATTESAYMEFTGADHLFPTRANTLEMRILIPWLKIFVDSDNRYSQFLCPLQDSTGIRGYRSTCPFLPNPTTSPSTTAPTTPPTTPPTTPPTGACSATYRTVNSWPGGFQGEVTVSAGSTPVDGWAVRWTLASGQAVTQVWNGALSVSGSAVTVRNTTYNGSLGANASTTFGFLASGSPTPVSLTCTSP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Saccharothrix deserti	2593674	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00267	00267 | PETase | Saccharothrix deserti | PET	Yes	WP_158852571.1	MLGTLLIAAAVSPASGADNPYQRGPDPTPASVSANRGTFATAQISVPAGNGFGGGVIYHPTDTSQGTFGAIAVVPGYTATWAAEGAWMGHWLASFGFVVIGIDTNSRNDWDTARGTQLLAALDYLTQRSPVRDRVDANRTAVMGHSMGGGGAMHAALQRPSLKAAIGLAPFSPSQNLTTTRVPTMLLAGQSDTTTTPASILNLYNGIPAATEKAYLELTGAGHGFPTSNNPTMMRNVIPWLKIFVDSDTRYTQFLCSLSNWDGIRAYQSTCPLVPSPVPTTTSTTSTTTTISTTTTTPAPGDACSATYRTTNSWPGGYQAEVTVTAGNTAVNGWNVQWTLGSGQTVTQVWNGTLNVSGSTASVRNASYNGSLQANTSTTFGFIGGGTPPTSSLSCTSP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Microbispora sp.	1898321	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00268	00268 | PETase | Microbispora sp. | PET	Yes	WP_182904095.1	MRPRRPRTGFLTGVVAVLLVIAGLAAGPSAASAADNPYERGPAPTAASIAADRGPFATAQVTVPRGNGFGGGVIYYPTDTSQGTFGAIAIAPGFGTAWSYYAWQGPRLASFGFVVIGIETNTLNDYADARATQLLAALDYLVNSSPVRDRVDRNRLAVGGHSMGGGGAILAANQRPSLLTAVGQAPYVPDGSLATIKSPTIIFAGQADGTVTPQYAQNAYNTIPSSVERAYVEIANEGHGFPAGGGGGNSGAFARTMMIWMKLFIDKDTRYAPFLCPSLSNANGISKYMASCPLDPPGGGPTASPTASPTVSPTVSPSGTPPATSAIRGVGSGRCLDVNGASQANGAQAQIWDCNGQNNQKWTTTSAGELRVYGNKCLDVNGGGTADGTSVIIWDCNGQNNQKWRLNTDGTITAVGANKCLDVSGAGTANGTKVQIWTCNGQNNQKWTRT	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Streptomyces sp.	1931	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00269	00269 | PETase | Streptomyces sp. | PET	Yes	WP_031525917.1	MVVAALVAVAGLLAAMLAFQPAAAADNPYQRGPDPTPAGVAASRGPFATAQTTVAPGNGFNGGTIYYPTDTSAGTWGAVAIVPGYTALFADEEAWMGPWLSSFGFVVIGIETNSRTDFDVARGTQLLAALDYLTQQSPVRDRVDTSRLSVIGHSMGGGGVVYATEHRPSLKAAVALAPFSPSQDMSTDRVPTMVMAGQNDTVVTPSYLDGLYATMPAATQSDFVQIAGADHVYYTHPQSTEMRILIPWLKIFVDNDTRYTQFLCPSLSDSSGISIYRSKCPYVPPGTSTTGGTTSGTTSGGTTTGGTTSGGTTTGGTTSGGTTSGGTSGSACTASYATVNTWSGGFQGEVTVTAGGKPVNGWTVRWTLAGGQGISQVWNGTVSTSGSDVSVRNVSYNGSLQPSTSTTFGFLGTGTPSDVSLSCTSP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Acidimicrobiales bacterium	2201156	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00270	00270 | PETase | Acidimicrobiales bacterium | PET	Yes	GIU85367.1	MSIVSVIESLTGRDRVGKAGVFMVGVALLVSACVTPAPPPAPDVATVTVGAGNGFGGGTIYYPQGATGRLPVVAASPGFTENQNAVGWYGPLLAREGNIVITIDTNSPFDSPTSRADQLLAAIDYVVNRSSVASIADGSRTAVMGHSMGGGGSLEAALKRPGLKAIIPLAPWNTTTNFSGVRVPTLIVGCQNDAIAPVGSHAEPFYQSIPATTPKAYLEIAGGDHFCTNSENPTIANYVVAWTDRFLQGDTSASSRLCPPPPAGGSISEYRANCPY	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Paractinoplanes deccanensis	2201156	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00271	00271 | PETase | Paractinoplanes deccanensis | PET	Yes	WP_203777396.1	MNAVGPTTPPTTTPPTTPAGDNPYQRGPDPTVASVAAQYGPFATAQITVPPGNGFNGGFIYYPTDSSHTYGAVAIVPGYTALFADEEAWMGPRLASFGFVVIGVETNSRTDYDTARGTQLLAALDYLTNSSAVRDRVDRNRLAVIGHSMGGGGALYAATQRPSLKAAIGLAPFKPSGNLASDTVPTMIIGGINDTTVTPSYLDGLYPTLPAATPGAYLQLANADHLYFTRPNDIEMRSQIEWLKIFVDNDTRYTPFLCPSIKDTTGIVRSNVKCSTIPGGGSTSPPTTTPPPAGSNRIVGAQSGRCVDVPGASQTNGTRVQLYDCNGQPNQAWTLTASKQLTVYGSRCLDAAGSGNGSAVQIYSCNGQANQQWNVNANGTITGVQSGRCLDVWGTGNGQQVQIYDCNGQANQRFGLS	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Phytohabitans houttuyneae	1076126	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00272	00272 | PETase | Phytohabitans houttuyneae | PET	Yes	WP_173061649.1	MFLGLRGRLLKLAVAGVAVTLGLFTMAVTTGSASAADNPYQRGPDPTRTSVAAVNGPFANTSVSVPTGYGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRVDPNRLAVSGHSMGGGGALSAAIRRSSLKAVVGIAPYSPSSNLANDRVPTMVFSGQADTVVTPSYATGLYNSLPATTESVYLEVAGADHGFMVGRSNPVMIRTMLPFVKMFIDNDTRYSQFLCPLLDSSGVVTYRSTCPLLPPAPTPSNTGTTPPTTPPVTPTTPPSSASEIVGVQSGRCIDVPNASRNNGTRVQLYDCNRQANQSWTYTSGKQLQVYGNMCLDAAGSGNGAAVQIYSCHSQTNQQWNVNSNGTISGVQSGRCLDVWSTANGAQIQLYDCHGGANQRFNLVPRT	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora craterilacus	1655439	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00273	00273 | PETase | Micromonospora craterilacus | PET	Yes	WP_111214096.1	MRPHAHHPPSSEESPADRVSPGIRGRLFKLAAAGIAAAVGLFTMTVATGSASAADNPYQRGPDPTRTSVTAVNGPFANTSVSVPTGYGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRVDPNRLAVSGHSMGGGGALSAAMRRSSLKAVVGITPYSPSSNLANDRVPTMIISGQADTVVTPSYALGLYNSIPTTTKSVYLEVAGGDHGFMVGRSNPVMVRTMLPFVKMFIDNDARYSQFLCPLLDNSGVVTYRSTCPLLPTTPPTGTPTPTPTNSPTTPPPGSASGIVGAQSGRCIDVPNASRSNGTRVQLYDCNRQSNQSWTYTANKQLRVYGDMCLDAAGSGNGAAVQIYSCHNQTNQQWNVNSNGTITGVQSGRCLDVWSTSNGAQVQLYDCHGQANQQFRLAPLA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Paractinoplanes rishiriensis	1655439	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00274	00274 | PETase | Paractinoplanes rishiriensis | PET	Yes	WP_203790592.1	MSRVRKFLAATTIGLGLLAGSVAVSPASAADNPYQRGPDPTAASIAAVTGPFATASVTVPRGNGFGGGVIYYPTDTSQGTFGGIAISPGLNGTWPGIAWLGPRLASQGFVVFGIETNNLNDSPTSRGTQLLAALDYLTGSSSVRTRVDAGRLAVAGHSMGGGGALDAALRRPSLRATIGNAPHLPSGSLANDRVPTLIYAMQNDTLVPPSRLTSLYNTVPATTERGYLEITGAGHNYIGQPSTILARTMIPWLKIFVDDDARYSQFLCPLTDRSGISQYQSSCPLITTSPTTGPTAQPTTAAPTTTPTTPPVGGPCEATHRTVNSWSGGYQGEVTVRAGSAAINGWTVSWTLGSGQTINQVWGGALTASGTAATVRNETWNGPVAAGASTTFGYIATGNAPTQPLACSAR	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Plantactinospora alkalitolerans	2789879	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00275	00275 | PETase | Plantactinospora alkalitolerans | PET	Yes	MBF9135495.1	MRGHTPHPTPSGDTHADRRSPGFRGGLFKLAAAGIAAAVGLFAMAVTTGSASAADNPYQRGPDPTRTSVAAVNGPFANTSVSVPTGYGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRVDPNRLAVSGHSMGGGGALSAAIRRSSLKAVVGIAPYSPSSNLANDRVPTMIFSGQADTVVTPSYATGLYNSLPATTESVYLEVAGADHGFMVGRSNPVMIRTMLPFVKMFIDNDTRYSQFLCPLLDSSGVVTYRSTCPLLPPAPTTPPPTGTPTPTPSSNPTTPPTTPPSTPTA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora taraxaci	1316803	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00276	00276 | PETase | Micromonospora taraxaci | PET	Yes	TWG17167.1	MRGPADHLPPTGNTQADRVSTGLRGRLFKLAAAGIAAAVGLLTITVATGSASAADNPYQRGPDPTRTSVTAVNGPFANTSVSVPTGYGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRVDPTRLAVAGHSMGGGGALSAAIRRSSLKAVVGIAPYSPSSNLANDRVPTMIFSGQADTVVTPSYATGLYNSLPSTTESVYLEVAGADHGFMVGRSNPVMVRTMLPFVKMFVDNDARYSQFLCPLLDNSGVVTYRSTCPLLPSTPTTPTPTPTDPTTPTPTPTVPPGSASQIVGTQSGRCIDVPNASRTNGTRVQLYDCNRQTNQAWTYTSGKQLQVYGNMCLDAAGTGNGAAVQIYSCHSQTNQQWNVNSNGTISNVQSGRCLDVWSTANGAQIQLYDCHSQTNQQFRVTPLA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Phytohabitans aurantiacus	1316803	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00277	00277 | PETase | Phytohabitans aurantiacus | PET	Yes	GLI01021.1	MKRLWTIGSVAALLCGASVAVALEAAAADNPYQRGPDPTPQSISATTGPFATASVTVPRQGNFGGGVIYYPTDTSQGTFGAVAISPGLNGTWPGIAWLGPRLSSQGFVVFGIDTLGLNDSTASRGSQLLAALDYLTQTSSVRTRVDASRLAVAGHSMGGGGAFEAVLRRPTLKASIPNAPFFPGSAANVRVPTLITAMQNDSLVGQNRNAYNGIPAGVEKAYIELAGAGHNQIGQPTTAIARNWIPWLKIFVDNDARYHQFFCPTTNMSGLSQYLNTCPLTSATPPTSSPSAGPTTPGPTGPPPGGACAATYQTVNTWSGGYQGEMTVRAGNSAINGWTVRWTMGGGQISQVWNGTLVTGSGAAAVRNAPYNGALAAGATTTFGFISSGTPSATSLTCATP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora qiuiae	502268	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00278	00278 | PETase | Micromonospora qiuiae | PET	Yes	WP_204038550.1	MREHPHHPPPSGSTRADRSSPGIRRRLFKLATAGIAAAVGLFTVTVATGSASAADNPYQRGPDPTRTSVATERGPFANTSVSVPSGYGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRIDPNRLAVSGHSMGGGGALSAAMRRSSLKAVVGIAPYSPSSNLANDRVPTMIFSGQADTVVTPSYAMGLYNSIPAGTKSAYLEVAGGDHGFMVGRSNPVLIRTMLPFLKIFIDNDARYSQFLCPLLDNSGVVTYRSTCPFLPTTPTTPPPTG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora saelicesensis	285676	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00279	00279 | PETase | Micromonospora saelicesensis | PET	Yes	WP_181548579.1	MAPRFRGRLFKLAAAGIAAAVGLFTITVATGSASAADNPYQRGPDPTRTSVTAVNGPFANTSVSVPTGYGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRVDPNRLAVAGHSMGGGGALSAATRRPSLKAVVGIAPYSPSSNLANDRVPTMIFAGQADTVVTPSYATGLYNSLPATTESVYVEVAGADHGFMVGRSNPVMVRTMLPFVKMFIDNDTRYSQFLCPLLDSSGVVTYRSTCPLLPSTPTPTDPPTPTDPPTVPPGSANEIVGTQSGRCVDVPNASRTNGTRVQLYGCNKQTNQAWTYTSSKQLQVYGNMCLDAAGTGNGAAVQIYSCHNQTNQQWNVNSNGTISNVQSGRCLDAWSTANGAQIQLYDCHGQTNQQFRLAALAG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora sp.	1876	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00280	00280 | PETase | Micromonospora sp. | PET	Yes	GHJ08786.1	MAGGAAALLGVAMAGAAVVGSSPSAAAASYQRGPDPTVQSVAANRGTFPTAEITVPRGYGFNGGKIYYPTDTSQGTWGAIAAVPGYTASWAAEGAWMGPWLASFGFVVIGIDTNSPTDFDTARGTQLLAALDYLTGQSAVRDRVDPNRLAVLGHSMGGGGAISAAMRRPTLKAAIPLAPASFSQNLSTVRVPTLIMGARDDGTVTPSSINSLWATKPATTKGAYVELTGGGHGFPTWGNSQVTRREIPWLKIFLDNDNRYTQFLCPSLADNTGVSRYLSECPYGSTGQPTSPPSTPPPTSGGPVRAVGAGKCLDVPNASQTNDTQLAIWDCNGGTNQRWTRTAGKQLTVYGNKCLDAAGQGTTNGTRVIIWDCTGTANQQWNVNANGTITGVQSGLCLDVSGGSTANGALTQLWACNNGSNQQWRLG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora rifamycinica	291594	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00281	00281 | PETase | Micromonospora rifamycinica | PET	Yes	WP_084261341.1	MRGQAYHPPPPERTHAATAHPGRRGRLVKLAAAGVAAAVAGLLTMTVASGSASAADNPYQRGPDPTRSSVAAVNGPFANTSVAVPTGYGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSVELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRVDPNRLAVSGHSMGGGGALSAAIRRSSLKAVVGIAPYSPSSNLANDRVPTMVFAGQADTVVTPSYATGLYNSLPATTESAYLEVAGADHGFMVGRSNPVLIRTMLPFLKMFVDNDARYSQFLCPLADNSGVVSYRSTCPLLPTTPTTPPPTPSDTPPPTPSGTPTTPPTTGPPGTASLVVGAQSGRCLDVPNASRANGTRVQLWDCNRQANQQWTYTSTRQLRVYGDMCLDAAGSGNGAAVQIYGCHGQPNQQWTVNANGTISGVQSGRCLDVWSTANGAQVQLYDCHGQTNQRFTLTPVA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora sp.	1876	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00282	00282 | PETase | Micromonospora sp. | PET	Yes	WP_265247586.1	MRRLWTIASVAALLCGAGVAVALEASAADNPYQRGPDPTPQSISAPTGPFATASVTVPRQGNFGGGVIYYPTDTSQGTFGAVAISPGLNGTWPGIAWLGPRLSSQGFVVFGIDTLGLSDSTASRGSQLLAALDYLTQTSSVRTRVDSSRLAVAGHSMGGGGAFEAALRRPALKAAIPNAPFFPGSASNVRVPTLITAMQNDSLVGQNRNAYNGIPAGVEKAYVELAGAGHNQIGQPTTAIARNWIPWLKIFVDSDARYHQFLCPTTDMSGLSQYLNTCPLISTTPPTSSPSAQPTTPGPTGPPPGGACAATYRTVNSWSDGYQGEMTVQAGSSAINGWTVRWTMSGGQTISQVWNGTLVAGSGAAAVRNVAYNGSLAAGASTTFGFISSGTPSATSITCGSP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Dactylosporangium vinaceum	53362	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00283	00283 | PETase | Dactylosporangium vinaceum | PET	Yes	UAC02078.1	MLSLVGGSLAVTTAPAHADQIGQAPTASNITGNGSFATTSASISSTVSGFGGGRVYYPTAAGTYPVIAISPGFTATWSSLAWIGPRLSSWGFVVVGIETNSIYDQPASRGNQLLAALNWAVNSSPTAVRSHVDGSRRGVAGHSMGGGGTLEALAADTTGLVKAGVPLAPWNTDKTWNNVSEPVLIVGGQADTVAPVASHSIPFYNTLAGPKTYVELTGQSHFFPQTTNATASRALVAWFKRWVSQDSRFTPFTCGFSGVAVSDFRSNAC	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinoallomurus spadix	79912	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00284	00284 | PETase | Actinoallomurus spadix | PET	Yes	WP_252811421.1	MAERTTRPQAAGAATRSGLLTRPLRWAVAAVTALAAAIALTVATWPASAAGNPYQRGPDPTLASVAASRGTFATAQVSVPPGNGFNGGTIYYPTDTTQGTWGAVAIVPGYTALFANEEAWMGPWLASFGFVVIGIETNSRNDFDTARGTQLLAALDYLTQKSPVRDRVDSARLGVIGHSMGGGGVVYATEHRPSLKAAVALAPFSPSQDMSTDHVPTMVMAGQNDTVVTPSYLDGLYATMPASAQSDFVQLAGADHVAYTHPNTTEMRLLIPWLKIFLDDDTRYTQFLCPLKDSTGVSMYRAKCPYVPPGGPTTSPTPTTTPTPPDGGACSATYRTVNSWSGGYQGEITVTAGGAAIDGWTVRWSLGGGQTVTQVWNGTLSTSGSTASVANASYNGSLQASASTTFGFLANGTPSTPALTCSSP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Dactylosporangium sucinum	1424081	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00285	00285 | PETase | Dactylosporangium sucinum | PET	Yes	WP_229836555.1	MQRQHPAIRFLVRAAMVFALMGAGITAAAAPAVADEIGQAPTAGNITGNGSFTTTSESISSLVSGFGGGRVYYPTTAGKYPVVAISPGFTATWSSLSWIGPRLSSWGFVVVGIETNSIYDQPASRGSQLLAALNWAVNSSSSAVRARVDGSRRGVAGHSMGGGGTLEALAADTTGLVKAGVPIAPWNSDKTWNNVSEPVMIVGGQSDTVAPVASHSIPFYNTLAGPKGYVELTGASHFFPQSTNATLSRALVAWFKRWLNQDSRFTPYTCGFSGLAVSDFRSNAC	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Dactylosporangium siamense	685454	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00286	00286 | PETase | Dactylosporangium siamense | PET	Yes	WP_239135698.1	MRTILLRLAVVLTLMGGGVAAVATPALADEIGQAPTASNITGNGSFATTSASISSTVAGFGGGRVYYPTATGTYPVIAISPGFTATWSSLSWIGPRLSSWGFVVVGIETNSIYDQPGSRGSQLLAALNWAVSSSPTAVRSRVDGSRRGVAGHSMGGGGTLEALAADTSGLVKAGVPLAPWNSDKTWNNVSEPVLIVGGQSDTIAPVSSHSVPFYNTLAGPKTYVELTGASHFFPQSSNATTSRALVSWFKRWLNQDSRFTPFTCGFSGAAVSSFRTNAC	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Dactylosporangium matsuzakiense	53360	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00287	00287 | PETase | Dactylosporangium matsuzakiense | PET	Yes	WP_271190254.1	MAAAAAALLADSPSALAASYQRGPDPTVQSVAANRGTFATAELTVPRGFGFNGGKIYYPTDTSQGTWGAIAAVPGYTASWAAEGAWMGPWLASFGFVVIGIDTNSPTDYDTARGTQLLAALDYLTGQSAVRDRVDPNRLAVLGHSMGGGGAISAAMRRPSLKAAVPLAPASFSQNLSNVRVPTLIMGARDDGTITPSSIDGLWSSKPATTQGARVELASGGHGFPTWGNSQVTRREIPWLKIFLDNDNRYAQFLCPSLADSTGVSRYISQCPYGSTGQPSSPPVSSPPAAGGPVRAVGAGKCLDVPNASQTNDTQLAIWDCNGGSNQQWTYTSGKQLRVYGGKCLDASGHGMSNGTRVIIWDCGGGANQQWNVNANGTITGVESGLCLDVTGAATANGALVDLWACNNGGNQQWRLG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora sp.	1876	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00288	00288 | PETase | Micromonospora sp. | PET	Yes	MBW4703769.1	MRGHVPHSPPPEQPHPARVSPRRRGRLFTLVTAGIAAAVAGLFTMTVATGTASAADNPYQRGPDPTRSSVAAVNGPFANTSVAVPTGYGFNGGRIYYPTDTSQGTFGAVAISPGYTALFSVELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLVQQSPVRDRIDPNRLAVSGHSMGGGGALSAALRRPALKAAVGIAPYSPSSNLANDRVPTMVFAGQADTVVTPSYATGLYNSLPTTTESAYLEVAGADHGFMVGRSNPVLIRTMLPFLKMFVDNDARYSQFLCPLADNSGVVSYRSTCPLLPPTSTTPPPIPSDTPPPIPTTPPQTTPPPSNPPGAASLIVGAQSNRCLDVPNASRANGTRVQLWDCNRGTNQSWTYTTNKQLRVYGDMCLDAAGSGNGAAVQIYGCHSQTNQQWNVNANGTISSVQSGRCLDVWSTANGAQVQLYDCHGQTNQRFTLTPLT	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora sp.	1876	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00289	00289 | PETase | Micromonospora sp. | PET	Yes	WP_247684544.1	MLTITVATGSASAADNPYQRGPDPTRTSVTAVNGPFANTSVSVPTGYGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRVDPNRLAVAGHSMGGGGALSAATRRSSLKAVVGIAPYSPSSNLANDRVPTMIFAGQADTVVTPSYATGLYNSLPTTTESAYLEVAGADHGFMVGRSNPVMVRTMLPFVKMFIDNDARYSQFLCPLLDSSGVVTYRSTCPLLPSTPPTSTPTPTDPPTPTPTPTVPPGSASEIVGTQSSRCIDVPNASRNNGTRVQLYDCNKQTNQA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Verrucosispora sp.	1871626	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00290	00290 | PETase | Verrucosispora sp. | PET	Yes	WP_269740835.1	MSNEETELAPRQPRPSPIRRALGGVAIVLGLLAATTVASPATAASPYQRGPNPTAASIAATTGPFAIASITVPRGNGFGGGVIYYPTSTSQGTFGGIAISPGLNGTWSGISWLGPRLASQGFVVFGIETNNLNDSPTSRGTQLLAALDYLTQRSSVRSRLDANRLAVMGHSMGGGGALDAALRRPTLKATIGNAPHLPSGSLANDRVPTLIYAMQNDTLVTPARLTSLYNTIPAATERAYIEVTGAGHNYIGQPSTTLARTMIPWLKIFIDSDTRYAPFLCPLNDRSGIRQYRNSCPLI	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora sp.	1876	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00291	00291 | PETase | Micromonospora sp. | PET	Yes	MCF0091346.1	MRGPADHPPPPGDTHADRPSPRSRGRLLKLAAAGIAAAVGLLTIAVATGSASAADNPYQRGPDPTAASVTAVNGPFANTSVSVPTGYGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRVDPNRLAVAGHSMGGGGALSAATRRPSLKAVVGIAPYSPSSNLANDRVPTMIFAGQADTVVTPSYATGLYNSLPTTTESTYLEVAGADHGFMVGRSNPVLVRTMLPFVKMFLDNDARYSQFLCPLLDNSGVVTYRSTCPLLPSTPTSPTPTTTPTSTPTPTPTVTPTTPPGSASQIVGTQSGRCVDVPNASRTNGTRVHLWDCNRQANQAWTYTANKQLQVYGTMCLDAAGTGNGAAVQIYSCHGQTNQQWNVNSNGTISSVQSGRCLDVWSTANGAQVQLYDCHGQTNQQFRLTALN	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinoplanes ianthinogenes	122358	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00292	00292 | PETase | Actinoplanes ianthinogenes | PET	Yes	GGR16917.1	MVAGRRRSWGMRTVVGAAITAAAVAVGMIASSPASPSPGTPGGDNPYQRGPDPTVASVAAQYGPFATAQITVPPGNGFNGGFIYYPTDTSHTYGAVAIVPGYTALFADEEAWMGPRLASFGFVVIGVETNSRTDYDTARGTQLLAALDYLTNSSAVRDRVDRNRLSVIGHSMGGGGSLYAATQRPSLKAAIGLAPFKPSGNLASDTVPTMIIGGINDTTVTPSYLDGLYPTLPAATPGAYLQLANADHLYFTRPNDIELRSQIEWLKIFVDNDTRYTPFLCPSVKDTTGIVRSSVKCSTVPGGGSTPSSSRILGTQSGRCVDVPGATHNNGTRVQLYDCNGQANQQWTYTSSKQLTVYGTVCLDAAGSGNGSAVQIYSCNGQANQQWNVNANGTITGVQSGRCLDVWGTGNGQQIQIYDCNGQANQKFSLN	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Amycolatopsis sp.	37632	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00293	00293 | PETase | Amycolatopsis sp. | PET	Yes	WP_199199185.1	MWRRFRGALAVLGVVLGLAPVSSAVAADNPYQRGPDPTPASIAADHGPFATAQTTIPKGNGLGGGIVYYPTDTSQGTFGAIAIAPGYGTEWRWYGWLGPRLASFGFVVVGIETNSLSDYADARADQLLAALDWLVTSSPVRDRVDRTRLAVGGHSMGGGGALVAATRRPSLRSAVGMAPYVPDGILRGTSVPTILFGGQADTTVTPAYLASAYATIPATVPRAYPEIAGEGHGFAAGGGGGNSGAFARVMMVWLKVFVDADTRYPPFLCPTLSNTSGISKYQASCPLGPGGTIPPPDTSRLANANAGRCLDASGAGTANGTKVILWTCNHGANQQWNRT	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Amycolatopsis sp.	37632	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00294	00294 | PETase | Amycolatopsis sp. | PET	Yes	WP_247056560.1	MSVLTSPPTSSGSGEKTRRLGWRSKTAGVVVAALALTTGVVAPAPAAANPYERGPAPTTSSIEASRGSFATSTTTVSRLAVSGFGGGTIYYPTSTASGTFGAVSIAPGFTATQSSMAWLGPRLASQGFVVFTIDTITTSDQPDSRGRQLLSSLDYLTQQSSVRSRIDSSRLGVVGHSMGGGGTLEAARSRPSLQAAVPLTGWNLTKSWSTVRVPTLVVGAQADTVAPVASHSIPFYTSLPSSLDKAYLELRGASHFAPNSANTTIAKYTLSWLKRFIDDDTRYEQFLCPIPGTSTTISDYRGNCPHAG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Catellatospora bangladeshensis	310355	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00295	00295 | PETase | Catellatospora bangladeshensis | PET	Yes	WP_239125827.1	MPQVSVRRRLTRLVATAFVATALAGGTALGAAAPAYADEIGQAPTSSNITGNGSFSVATYNISSLVSGFGGGVAYYPTTSGRYPVIAVSPGFTARWSSISWIGPRLASWGFVVVGIETNSIYDQPGSRGSQLLAALNWAVNSAPSSVRDRVDGSRRGVAGHSMGGGGTLEALAADTTGLVKAGVPIAPWNTDTTWGGLNEAVQIVGGESDTIAPVSSHSIPFYSTLGGPKSYVELNGASHFFPQTSNSTLSRALVSWFKRYLNNDARFTPFTCGYSGLSISDFRSNNC	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Paractinoplanes tereljensis	310355	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00296	00296 | PETase | Paractinoplanes tereljensis | PET	Yes	WP_203812622.1	MKVFRARNMAGVLAAVALTAAGITLVPSANAATTSFQRGPAPTTASIQATSGPFATSQTTVSRISVTGFGGGDIYYPTSTSSGTFGAVAIAPGYTALRSSMAWLAPRIASQGFVVFNIDTLTTSDQPATRGTELLAALDYLTTRSTVRTRIDTTRLAVMGHSMGGGGTLEAAKSRPSLQAAIPLTPWDLNKSFAGLAVPTLIIGAQADTVAPVSQHAKPFFTSLPSGLDKAYLELAGASHFAPNTSNTTIASISIAWLKRFVDDDTRYDQFLCPGPTVGTAVSQFTTNCPHIS	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora acroterricola	2202421	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00297	00297 | PETase | Micromonospora acroterricola | PET	Yes	PWR09075.1	MAFAAVAATAVAGPASAAANPYERGPAPTAASIAATTGPFAVASVSVPRGNGFGGGVIYYPTSTSQGTFGGVAISPGLNGTWAGIAWLGPRLASQGFVIFGIETNNLNDSPASRGTQLLAALDFLTRSSSVRTRVDASRLAVAGHSMGGGGALSAALQRPSLQAAIGNAPHLPSGSLATDRVPTLIYAMQNDTLVTPSRLTSLYNSMPATTERAYIEVAGAGHNYIGQPSTTLARTMIPWLKIFVDNDARYSQFLCPLSNQSGISQYRNSCPLISTTTLSTGVDSTSGLAVR	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Rhizocola hellebori	1392758	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00298	00298 | PETase | Rhizocola hellebori | PET	Yes	WP_203906211.1	MSQHESTALASRPARAWLARKAVAGTAVVLGLVAGMAAPQPALAADNPYQRGPNPTAASIAATTGPFAIASVSVARGNGFGGGVIYYPTDTSQGTFGAIAISPGLNGTWPGIAWLGPRLASQGFVVFGIETNNLNDSPTSRGTQLLAALDYLTQRSSVRTRVDATRLAVAGHSMGGGGALDAALRRPSLQAAIGNAPYLPSGNLSTDRVPTLIYAMQNDTLVPPSRLTTMYNTIPATTERGYIQITGAGHNYIGQPSTNLARTMIPWFKIFIDNDTRFSQFLCPLSNMSGISQYRNSCPLI	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Asanoa hainanensis	560556	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00299	00299 | PETase | Asanoa hainanensis | PET	Yes	WP_144022925.1	MTRHQQPTLARPPRLRAALLGIATMLGVLAPAALSGPALAASPYERGPNPTAASVSATTGPFAIASVSVARGNGFGGGVIYYPTATNQGTFGGIAISPGLNGTWAGIAWLGPRLASQGFVVFGIETNNLNDSPTSRGTQLLAALDYLTQRSTVRTRVDAGRLAVMGHSMGGGGALDAALRRPSLQAAIGNAPHLPSGTLSNDRVPTMIYAMQNDTLVPPSRLTTLYNSIPATTERGYILVTGAGHNYIGQPSTTLARTMIPWFKIFIDDDTRYSQFLCPMSNQSGISQYRNSCPLS	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Amycolatopsis tolypomycina	208445	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00300	00300 | PETase | Amycolatopsis tolypomycina | PET	Yes	WP_091317053.1	MSALTSPPTTSGSREKISRRRGWRAKTAGVVLAALALTTAVAAPAPAAANPYERGPDPTTASIEASRGSFATSTVTVSRLAVSGFGGGTIYYPTTTTAGTFGAISIAPGFTATQSSMAWLGPRLASQGFVVFTIDTITTSDQPDSRGRQLLASLDYLTQQSSVRSRIDSSRLGVVGHSMGGGGTLEAARSRPSLQAAVPLTGWNLTKNWSTLRVPTLVVGAQSDTIAPVASHSIPFYTSLPSTLDRAYLELRGASHFAPNTSNTTIAKYTLSWLKRFIDNDTRYEQFLCPIPSSSLSISDYRGNCPHNG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora sp.	1876	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00301	00301 | PETase | Micromonospora sp. | PET	Yes	MTK05241.1	MPAKVRGRLFKLATAGIAAAVGLFTMTVATSSASAADNPYERGPDPTRTSVATERGPFANTSVSVPSGHGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSVELAWMGPWLASHGFVVIGIETNSTNDFDTARGTQLLAALDYLTQQSPVRDRIDPSRLAVSGHSMGGGGALSAAMRRSSLKAVVGITPFSPSSNLASNQVPTMVISGQADTVVTPSYALDLYNSLPASTESVYLEVAGGDHGFMVGRSNPVLIRTMLPFLKMFVDNDTRYSQFLCPLMDNSGVVTYRSTCPLLPTPPTTPPPTGDPTSPPPSTDPTTPPPSGSTGQIVGTQSNRCIDVPNSSRNNGTRVQLYDCHGQANQTWTYNSTTKQLRVYGDMCLDAAGSGNGAAVQIYNCHGQTNQQWNLNSNGTISGVQSNRCLDVWSTNNGAQIQLYDCHGQTNQQFRIRS	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Catellatospora methionotrophica	121620	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00302	00302 | PETase | Catellatospora methionotrophica | PET	Yes	WP_239086781.1	MQQTISSPRRRLTRLIATTFVATALAAGTALGTGTPAYADEIGQAPTSSNITGNGSFSVSTYNISSLVTGFGGGVAYYPSTAGRYPVVAVSPGFTARWSSISWIGPRLASWGFVVVGIETNSVYDQPASRGSQLLAALNWAVNSAPSAITSRADGSRRGVAGHSMGGGGTLEALAADTTGNVKAGVPLAPWNSDKTWNNVNEPVQIIGGESDTVAGVSSHSIPFYNSLGGSKSYVELNGASHFFPQTTNATTSRALVSWFKRWLNQDARFTPFTCGYGGTAVSDFRTNAC	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Verrucosispora sioxanthis	2499994	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00303	00303 | PETase | Verrucosispora sioxanthis | PET	Yes	WP_164449727.1	MFTVTVATGSASAADNPYQRGPDPTRASVAAVNGPFANTSVSVPTGYGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRVDPNRLAVSGHSMGGGGALSAAIRRSSLKAAVGITPYSPSQNLANDRVPTMVISGQADTVVTPSYALNLYNSLPASTESVYLEVAGGDHGFMVGRSNPVLIRTMLPFLKMFVDNDSRYSQFLCPLLDSSGVVTYRSTCPLLPTDPTTPPTGTPTPTPTTPPTPTPTPTTPPPSGSANEIIGTQSGRCVDVPNASRNNGTRVQLYDCNKQTNQSWTYTTNKQLRVYDNMCLDAAGSGNGAAVQIYTCHSGTNQQWNVNSNGTITGVQSGRCLDVWSSNNGAQIQLYDCHGQPNQQFRLAALA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Thermobifida cellulosilytica	144786	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00304	00304 | PETase | Thermobifida cellulosilytica | PET	Yes	MGYP001477358452	ANPYERGPNPTQALLEARSGPFSVSSERAWRLGSDGFGGGTIYYPRENNTYGAVAISPGYTGTQASVAWLGERIASHGFVVITIDTNTTLDQPDSRADQLEAALDHMVDGASSTVRSRIDRNRLAVMGHSMGGGGTLRLASQRPDLKAAIPLTPWHLNKSWSNVQVPTLIIGADLDTIAPVLTHAEPFYNSIPTSTRKAYLELDGATHFAPNITNSTIGMYSVAWLKRFVDEDTRYTQFLCPGPRTGLFSDVEEYRSTCPF	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Streptomyces sp.	1931	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00305	00305 | PETase | Streptomyces sp. | PET	Yes	WP_264933993.1	MHPSVTDVPVSEDTRATRTRRRWTDRTVRLRAAVVAAVTGLITALVAIQPASARPASAQDNPYERGPAPTVSSVAAQRGTFATAELTVPPGNGFNGGKIYYPTDTSLGTWGAVAAVPGYTAKWAAEGAWMGPWLASFGFVVIGIDTNSPNDYDTARGTQLLAALDYLTQKSAVRDRVDPNRLGVIGHSMGGGGAISAAVRRPSLKAALPLAPFSPSQNLSTLRVPTVIMGARDDGTVTPSYLDGLYGGMPAGTQSAFIELSSGGHGFPTWGNSNVTRRMIPWLKIFLDNDTRYTQFLCPSLADTSGVSRSKLKCPYVPPGGTTPPPPSGGPIVGAASGRCLEVPNSSQTNGTQVQLWDCLDRAGQKWTRTAAGELRVYGTKCLDAEASGTSPGTRVVIWDCHGGQNQQWNVNSNGTITSARSGLCLDAYNAGTGNGTQGVLWNCNGGANQRWALG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinomycetes bacterium	1883427	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00306	00306 | PETase | Actinomycetes bacterium | PET	Yes	MGYP000321434903	AETTTQHGPDPTEGSITAPTGPFQTDQKTVPRSSVQGFGGGTIYYPTETSQGTFGAVTIAPGYTAGKESLAWLGPRLASQGFVVFTIDTITTSDQPDSRAKQLMASLDYLTGDSDVRDRIDTSRLAVMGHSMGGGGTLEAARDNRNLKAAIPMTPWDTTKDFSGVQTPTLIIGAQNDTIAPVAQHAKPFYGSLPDDPGKAYLELAGASHFAPNQDNTTIAKSSIAWLKRFVDDDTRYDQFLCPPPQDAEISDYQSTCPY	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Crossiella sp.	1911417	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00307	00307 | PETase | Crossiella sp. | PET	Yes	WP_256510026.1	MAADNPYQRGPNPTSASVAASRGTFATAELSVPRGNGFGGGKIYYPTDTTQGTFGAIAIVPGYTATWAAEGAWMGHWLASFGFVVIGIDTNSRNDNDTARGTQLLAALDYLTQRSSVRGRVDAKRLAVMGHSMGGGGALVAARQRPSLKAAVGLAPFKPSGPPSADRVPTMVIAGQRDGTVTPSYVDGLYRAIPAGTEKAYLEFAGAGHAFPTRPNPLQMRLVIPWLKSFTDHDTRYHQFLCPLKDRTGVTAYRSTCPLVAPGARD	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Dactylosporangium aurantiacum	35754	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00308	00308 | PETase | Dactylosporangium aurantiacum | PET	Yes	WP_260709492.1	MTAGVVGVVAVAVAAVMMPSADAASTLADNPYQRGPDPTVASVAAAYGTFATAQLTVPPGNGFNGGSIYYPTDTSQTYGAVAIVPGYTARFADEEAWMGPRLASFGFVVIGVETNSRNDFDTARGTQLLAALDYLTNSSAVRDRVDRNRLAVIGHSMGGGGALVAADQRPSLKAAIGLAPYKPSGNLANNRVPTLILSGQNDTVVTPSYLDGLYPTLPAATPGAYILLSGADHLFFTRPNDIEMRSQIPWLKTFVDNDTRYSQFLCPTLKDTTSVARSTAKCSLIPSGGNPSTPPSSSSPSPSSPASSSPPPSGAKHIVGAQSGRCVDVPNSSRTNGTRVQLYDCHSGTNQQWTYTSSRQLTVYGSMCLDAAGSGNGAAVQIYSCNGQANQQWNVNSNGTISGVQSGRCLDVWGTNNGQQIQLYDCHGQANQRFSLS	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Microbispora rosea subsp. Aerata	147065	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00309	00309 | PETase | Microbispora rosea | PET	Yes	GGO06455.1	MPTHPPTSPLRRVFSVVTTLASAVVLALSGGLLTAPAAHAAVHGPDPTDALLEASRGPYATAQIDVSALAVSGFGGGTIYYPTTTSEGTFGGVAIAPGYTADKSSLAWLAARLASHGFVVFNIDTLTRLDQPDSRGRQLLAALDYLTQRSSVRSRVDASRLGVMGHSMGGGGTLEAAVSRPSLRAAVPLTPWNLDKTWPEVRTPTLIIGADLDTIAPVLTHAEPFYASLPSTLDKAYLELNNATHFAPNITDTTIGKYAVAWMKRFIDDDTRYNRFLCPGPSWSLSVEEYRSTCPF	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinomadura sp.	1989	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00310	00310 | PETase | Actinomadura sp. | PET	Yes	WP_149259982.1	MYRHLTHALRVLPATVALAAGAALAPAAQAAAPAGPAALPARPLAAAPADSPYERGPAPTEASITAERGPFAIEKIDVPAGSGTGFNRGTIYAPTDTSQGTFGAIAVSPGFMSPQSVIDWYGPRLASQGFVVMTLETKSLLDAPAARGDQLLAALDYMTGKSKAKDRIDASRLAVMGHSMGGGGTLEAANKRASLQAAVPLAPWDTNYDWKNVQAPTMIMGADNDTIAPADSMAERYYGTLTAVPEKAYLELRNAGHTTFNAPNTTIAKYAIAWMKRFVDDDARYEQFLCPEPSPSTTIAQYEGTCPTG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonosporaceae bacterium	1873464	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00311	00311 | PETase | Micromonosporaceae bacterium | PET	Yes	MBN1171866.1	MVPRSRTRFLRPAAAAVTVLLGLAGVTLAREARAADNPYQRGPDPTVASVAATNGPFATAQLNVPSGNGFNGGTIYYPTDTSLGTWGAVAIVPGYTARFANEEAWMGPRLASFGFVVIGVETNSTTDWDTARGTQLLAALDYLTQKSSVRDRVDASRLAVIGHSMGGGGVVYAASQRPSLKAAIGLAPYAPSGNLSNVKVPMLIQGGQNDTVVTPSYLDGLYPTLPSSTPGAYVQYSGADHLFWTKANNIELRTQIPWLKIFLDNDTRYTQFMCPTLKDTASVAKYSAKCSLIPSAGSTTAPTTQPATSAPATTSPTTQPPSQPG	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Cellulomonas iranensis	76862	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00312	00312 | PETase | Cellulomonas iranensis | PET	Yes	MBO9569276.1	MTARTTRRPLAAVILGLALTLTGSLPAQAADQRGPDPTVQSIEAARGPFATSTSRVSSLVSGFGGGTIYYPTDTSQGRFGGVVIAPGYTAGESSIAWLGPRLASQGFVVFTIDTLTRVDQPASRGRQLLAAADYLTQRSDVADRVDPARLAVMGHSMGGGGTLEAAKSRPGLKAIIPLTPWNLDKTWPEITTPTLIFGAQADSVASVVTHARPFYQTLPATTPRSYLELRGASHFAPNLSNTTIAKYSIAWLKRFVDDDQRYTQFLCPAPADTALSDVRTSCPF	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Plantactinospora endophytica	673535	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00313	00313 | PETase | Plantactinospora endophytica | PET	Yes	GIG90696.1	MRRHTPHPPPPEDSHADRVPPGVRGRLLTLVTAGIAAAGIAAAVGLFTVTAATGPASAADNPYQRGPDPSRTSVATETGPFANASVSVPTGYGFNGGRIYYPTDSSQGTFGAIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRVDPNRLAVAGHSMGGGGALSAAVRRSSLKAAVGIAPYSPSSNLANDRVPTMVFSGQADTVVTPSYAIGLYNSLPTTTESVYLEVAGADHGFMVGRSNPVMIRTMLPFVKMFIDNDTRYSQFLCPLLDSSGVVTYRSTCPLLPTTPTTPPVNPTTPPVNPTVSPTGAPGSASEIVGVQSGRCVDVPNASRTNGTRVQLYDCNRQSQQSWTYTSGRQLRVYGDMCLDAAGSGNGAAVQIYACHSQTNQQWNVNSNGTISGVQSGRCLDVWSTANGAQVQLYDCHGQTNQRFNVMPLAR	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Streptomyces swartbergensis	487165	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00314	00314 | PETase | Streptomyces swartbergensis | PET	Yes	WP_086599340.1	MHPSVTDVPVSEDIRATRTGLRRTGRTVRLRAAVVAAVTGLITALVAIQPASARPASAQDNPYERGPDPTVSSVAAQRGTFATAEVTVPPGNGFNGGKIYYPTDTSKGTWGAVAAVPGYTAKWAAEGAWMGPWLASFGFVVIGIDTNSPNDYDTARGTQLLAALDYLTQKSPVRDRVDPNRLGVIGHSMGGGGAISAAERRPSLKAALPLAPFSPSQNLSSLRVPTMIMGARDDGTVTPSYLNGLYAGMPAATPSAYIELTSGGHGFPTWGNSNVTRRTIPWLKIFLDNDTRYTQLLCPSPADRTGVSRSQVKCAYVPGGGTTPPPPSSGQIVGAASARCLDVPNSSQTNGTQLQLWDCLDQTSQKWARTDAGELRVYGNKCLDAEASGTSAGTRAIIWDCHGGQNQRWNVNANGTITSARSGLCLDANNAGTANGTQAILWTCNGGSNQRWTLR	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinomadura atramentaria	1990	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00315	00315 | PETase | Actinomadura atramentaria | PET	Yes	WP_019633337.1	MRTIVRRSLAVLPAALTLAAAAVAVPAAAAPPARVAALATTAYQRGPAPTLSGVRAALGPFSYSTASVSAAATGYTFGGGTVYYPDDTSQGTFGGIAVTPGYTGTEGSIAWLGPRLASQGFVVITIATKSLYDQPTARGQQLLAALDYLKTYSPAAVRQRLDPQRLAVSGHSMGGGGALYAVWSRPSLKAAVPLAPYHTIKNWSAITVPTLIEAGTADTVTPVGTFAEPIYQSLTGASERAYAEVAGANHLTFTAENPLIGGLEVAWMKRFVDDDARYDQFLCPAPTDPGLTEYRDSCPTS	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Streptomyces sp.	1931	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00316	00316 | PETase | Streptomyces sp. | PET	Yes	WP_109361459.1	MHPSTRLRAAVVAAVTGLIAALLATQPASARPAAPADSPYQRGPDPTVSSVAAQRGTFATAELTVPPGNGFNGGKIYYPTDTSQGTWAAVAAVPGYTAKWAAEGAWMGPWLASFGFVVIGIDTDSPNDYDTARGTQLLAALDYLTQRSPVRDRVDPGRLGVIGHSMGGGGAINAAERRPSLKAALPLAPFSPSQNLSTLRVPTMIMGARDDGTVTPSYLNGLYGGMPATTPSASIELTSGGHGFPTWGNSNVTRRTIPWLKIFLDEDTRYTQFLCPSLPDRTGISRSQVTCGSVPGDGSTPPPATGRQVVGAASGRCLDVPGSSQANGTQLQLWDCLDQAGQKWARTDAGELRVLGGKCLDAEASGTAPGTRAVVWDCHGGPNQRWNVTPDGTITSAQSGLCLDAYNAGTANGTRTVLWTCNGGSNQRWTWR	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Kutzneria sp.	1930788	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00317	00317 | PETase | Kutzneria sp. | PET	Yes	WP_211769896.1	MQAQHSARAERRRPWRRFSGPLAALGIVLALTAGGLATAATPAFADQVGQAPTADNITGNGSFATTSAAITNQTGFGGGTVYYPTADGTYPVVAIVPGFAATWSQISWLGPRVASWGFVVVGVDTTSVFDSPQQRGDEFLAALNWAANSAPASTRGKVDGTRRGVAGWSMGGGGTLEAMAKDTTLKAGVPLAPWDTTQDWSKIGKPVFIVGAQNDLIAPPASHAIPFYNSLAGPKSYLELAGADHFFPISANPTVSRAVVSWFKRFVSADDRFAPFTCGFAGAAVSAFRTTAC	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Saccharopolyspora hirsuta	1837	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00318	00318 | PETase | Saccharopolyspora hirsuta | PET	Yes	WP_150070118.1	MFATRAPARPSPLRRSLIVSTAVLGLLVGNTALAQSAEASPPHGPDPTEESITAPRGPFEIDQKTVSRASVRGFGGGTIYYPTDTSEGTFSAVAIAPGYTAGQESLAWLGPRLASQGFVVFTIDTLTRYDQPDSRSRQLLAALDHLTDDSDVADRVDPARRGVMGHSMGGGGSLQAALDDPDLKAAIPMTPWHTTKDFSGVRTPTLIIGAQNDTVAPVSQHAKPFYESLPDDPGKAYLELAGASHFAPNVDNTTIARYSIAWLKRFLDDDTRYEQFLCPPPPDPAISDHQSTCPY	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Kibdelosporangium banguiense	1365924	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00319	00319 | PETase | Kibdelosporangium banguiense | PET	Yes	MBP2328848.1	MRHVIKSRAPAGAEPPIPRRRLLKQAVTAAAVVLGILAPAVSPQSALAAANPYQRGPDPTLASVAATNGPFATAQMTVPPGNGFNGGYIYYPTDTSLGTWGAVAIVPGYTALFKNEEAWMGPRLASFGFVVIGIETNSRTDFDTARGTQLLAALDYLTQKSAVRNRVDPGRLGVIGHSMGGGGALVAATQRPSLKAAVGLAPFKPSGNLANDRVPTMFIAGNRDTVVTPSYLDGLYGSLPAATKKAYVQINGADHLFATKPNTVEMRTLIPWLKIFLDNDTRYSQFLCPTLLDKTGVSMYRGTCPLI	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora carbonacea	47853	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00320	00320 | PETase | Micromonospora carbonacea | PET	Yes	WP_260422593.1	MFTIAVATGSASAADNPYQRGPDPTRASVASENGPFANTSVAVPTGYGFNGGRIYYPTDTSQGTFGAIAISPGYTALFSVELAWMGPWLASHGFVVIGIETNSRNDFDTARGTQLLAALDYLTQQSPVRDRVDASRLAVAGHSMGGGGALSAAMRRSSLKAAVGIAPYSPSSNLATDRVPTMVFSGQADTVVTPSYATGLYNSLPTTTESAYLEVAGADHGFMVGRSNPVLIRTMLPFLKIFIDNDARYSQFLCPLLDSSGVVTYRSTCPLLPTPPTSPTATPTTTPTTPPPTSPPGAASQIVGAQSGRCVDVPNASRANGTRVQLYDCNRQSNQSWTYTSTKQLRVYGDMCLDAAGSGNGAAVQIYGCHSQTNQQWNVNSNGTISSVQSGRCLDVWSTANGAQIQLYDCHGQTNQRFSLTPLA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinoallomurus spadix	79912	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00321	00321 | PETase | Actinoallomurus spadix | PET	Yes	WP_252811421.1	MAERTTRPQAAGAATRSGLLTRPLRWAVAAVTALAAAIALTVATWPASAAGNPYQRGPDPTLASVAASRGTFATAQVSVPPGNGFNGGTIYYPTDTTQGTWGAVAIVPGYTALFANEEAWMGPWLASFGFVVIGIETNSRNDFDTARGTQLLAALDYLTQKSPVRDRVDSARLGVIGHSMGGGGVVYATEHRPSLKAAVALAPFSPSQDMSTDHVPTMVMAGQNDTVVTPSYLDGLYATMPASAQSDFVQLAGADHVAYTHPNTTEMRLLIPWLKIFLDDDTRYTQFLCPLKDSTGVSMYRAKCPYVPPGGPTTSPTPTTTPTPPDGGACSATYRTVNSWSGGYQGEITVTAGGAAIDGWTVRWSLGGGQTVTQVWNGTLSTSGSTASVANASYNGSLQASASTTFGFLANGTPSTPALTCSSP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Streptomyces sp.	1931	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00322	00322 | PETase | Streptomyces sp. | PET	Yes	WP_218517662.1	MVKRIGFAAAIGLVILAVVAPGSAPAAESPYQRGPDPTRESVAASRGTFATAEVSVPAGNGFGGGVIYYPTDTSQGTFGGVAIVPGYTATWAAEGAWMGHWLASFGFVVIGIDTINRNDWDTARGTQLLAALDYLTQRSSVRNRVDANRLAVMGHSMGGGGAMHAALQRPSLKAAIGLAPFSPSQNLTNMRVPTLLVAGQNDTTTTPTSILNLYNGIPATTEKAYLELTGAGHGFPTSANSVMTRKVIPWLKIFVDHDTRYHQFLCPLLDWTGITAYRSSCPLNPPGGPTGSTFSLVGADSGKCVDVPGASRTNGTGLITYTCNGASNQRWTQTAANELRIYDNSKCMEAGTSAGSRAVITSCTGGNGQKWTFNANGTITHAQSGLCLYVNGGSTANQAAVIVWTCHGGSNQVWTRQP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Crossiella sp.	1911417	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00323	00323 | PETase | Crossiella sp. | PET	Yes	WP_256510519.1	MASIVVPGSAAAADNPYQRGPNPTQASVAANRGTFATAETSVGGGNGFGGAKIYYPTDTSQGTFGAIAVVPGYTATWAAEGAWMGHWLSSFGFVVIGIDTNSRNDNDTARGTQLLAALDYLTQRSSVRARVDPNRLAVMGHSMGGGGAISAALRRPTLKAAIGNAPFSPSQNLSTMRVPTALLAGQRDGTVTPSLVSGYYNQIPASTEKMYLELTGAGHGFPTSNNSVATRKWVPWMKIFLDQDTRYQQFLCPLLDNTGISAYRSTCPLIPGDPAPGTTFSLAGSASGKCVDVPGGTQTNGAGLIIWPCRGVTNQRWAQTAAGELRIYDNAKCMDANASGQGARVTINSCHGGASQKWTVNTNGTVTNSASGRCLEAVGTADDAPVVVNTCNGGSGQTWAKRA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora sp.	1876	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00324	00324 | PETase | Micromonospora sp. | PET	Yes	WP_233604767.1	MRPDVQHLPPPGGTDRIVPGSRRRLLALAAAGIALVLGLLTTVVTTGSASAADNPYQRGPDPTPASVAAVNGPFATASVSVPAGYGFGGGMIYYPTDTSQGTFGGIAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSRNDFDEARGTQLLAALDYLTQQSPVRTRVDPNRLAVSGHSMGGGGALNAAIRRPSLKAAVGLAPFLPSSNLANDRVPTMVFAGQQDTVVSPSYVTNLYNSLPATTESAYLEIAGGDHGFPVGRPNQVMIRTMLPFVKIFLDNDTRYSQFLCPLMDSTGVVTYRSTCPLLPPGLPTTPPTSTSSNPTVGPTTPSTTAPTTTPAPGGACTATYRTTNSWPGGFQGEVTITAGSSAINGWTVRWTLGSGQTISQVWNGEVSITGSTVSVRNAPYNGSLPASGSTTFGFLGGGSPSSPSLTCTSP	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Micromonospora lutea	419825	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00325	00325 | PETase | Micromonospora lutea | PET	Yes	WP_239095870.1	MPASVRGRLFKLATAGIAAAVGLFTMTVATSSASAADNPYQRGPDPTRTSVTAVNGPFANTSVSVPTGQGFNGGRIYYPTDTSQGTFGAVAISPGYTALFSAELAWMGPWLASHGFVVIGIETNSTNDFDTARGTQLLAALDYLTQRSSVRDRVDPNRLAVSGHSMGGGGALSAAARRSSLKAVVGITPYSPSSNLANVRVPTMVVSGQADTVVTPSYALNLYNSLPSTTESVYLEVAGGDHGFMVGRSNPVLVRTMLPFLKMFVDNDTRYSQFLCPLMDNSGVVTYRSTCPLLPTPTTPPPTTGPTTPPPTTPPTTTPPPSGSTGQIVGTQSNRCIDVPNSSRNNGTRVQLYDCHGQANQTWTYDSSTKQLRVYGDMCLDASGSGNGAAVQIYSCHNQTNQQWNINSNGTISGVQSNRCLDAWSTNNGAQIQLYDCHGQTNQQFRIRA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Hamadaea flava	1742688	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00326	00326 | PETase | Hamadaea flava | PET	Yes	WP_253762837.1	MHLRRSRLLAMLSLALTLAVGAAVASPAHALNPYQRGPNPTDAILEASSGPYATSSISVPSIVSGFGGGRIYYPTTTADGTFGGIAISPGFTATWSSLSWLGPRLASHGFVVIGIETNTIYDQPTSRGQQLLAALDYLVNTSSVRTRVDSSRLAVAGHSMGGGGTLWAANSRPSLQAAIPLAPWNTDKSWSGVRVPTLIVGGQSDTVAPVATHSIPFYTSIPAASEKAYLELRSASHFFPQTVNTTVAVSMVSWLKRYVDDDTRYDPWLCPGPSGLSVSDYRDTCPA	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Actinoplanes ianthinogenes	122358	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00327	00327 | PETase | Actinoplanes ianthinogenes | PET	Yes	WP_212846608.1	MRTVVGAAITAAAVAVGMIASSPASPSPGTPGGDNPYQRGPDPTVASVAAQYGPFATAQITVPPGNGFNGGFIYYPTDTSHTYGAVAIVPGYTALFADEEAWMGPRLASFGFVVIGVETNSRTDYDTARGTQLLAALDYLTNSSAVRDRVDRNRLSVIGHSMGGGGSLYAATQRPSLKAAIGLAPFKPSGNLASDTVPTMIIGGINDTTVTPSYLDGLYPTLPAATPGAYLQLANADHLYFTRPNDIELRSQIEWLKIFVDNDTRYTPFLCPSVKDTTGIVRSSVKCSTVPGGGSTPSSSRILGTQSGRCVDVPGATHNNGTRVQLYDCNGQANQQWTYTSSKQLTVYGTVCLDAAGSGNGSAVQIYSCNGQANQQWNVNANGTITGVQSGRCLDVWGTGNGQQIQIYDCNGQANQKFSLN	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Acidimicrobiales bacterium	2201156	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00328	00328 | PETase | Acidimicrobiales bacterium | PET	Yes	GIU85371.1	MPPPPPPPPPVQTVTVEPGYGFGGGTIYYPQESTGRLPVVAAVPGFTETQEAVAWYGPLLARRGNIVITIDTISPTNAPKTRADQALAAIDYVVTQSAVSDIADASRTAVMGHSMGGGASLFAALKRPTLKAIVPLAPWARTTDFSGVAVPTLIVGCENDGIAAVGTYAEPFYESIPATTPKAYLEMAGGNHYCTNSEDPVIAGYVSAWTDRFLKGDTTASSRLCPPSPVGPISEYRSNCPY	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460
Sphaerisporangium fuscum	2835868	PET	Norton-Baker, B., Komp, E., Gado, J. E., Denton, M. C., Mathews, I. I., Murphy, N. P., ... & Beckham, G. T. (2025). Machine learning-guided identification of PET hydrolases from natural diversity. ACS catalysis, 15(18), 16070-16083.	PETase	00329	00329 | PETase | Sphaerisporangium fuscum | PET	Yes	WP_250563816.1	MAVVLAGVAAAPAAHAAANPYERGPDPTDAILEAARGPFETSRTEVPALSVTGFGGGTIYYPATTSAGTFGGVAVAPGYTADRTSLAWLAERLASHGFVVFNIDTLTRLDQPDSRGRQLLAALDYLTQRSSVRGRLDAGRLGVMGHSMGGGGTLEAARDRPSLQAAVPLTPWDLTKIWSGVRVPTMIVGAEADTIAPVASHAEPFYQSLPSSPGKAYLELNNATHFAPNVPDTTIGKYVVAWMKRFVDDDTRYTRFLCPGPSGGLTVEEYRSTCPFS	2025.0	Spectrophotometry	amorphous film (Goodfellow ES30-FM-000145) or crystalline powder (Goodfellow ES30-PD-006031)	Goodfellow	Yes	No				Yes		doi.org/10.1021/acscatal.5c03460