合成生物学 ›› 2022, Vol. 3 ›› Issue (4): 763-780.DOI: 10.12211/2096-8280.2021-089
李磊1,2, 高鑫2, 齐宏斌2, 李超2, 路福平1,2,3, 毛淑红1,2,3, 秦慧民1,2,3
收稿日期:
2021-09-01
修回日期:
2022-02-17
出版日期:
2022-08-31
发布日期:
2022-09-08
通讯作者:
毛淑红,秦慧民
作者简介:
基金资助:
LI Lei1,2, GAO Xin2, QI Hongbin2, LI Chao2, LU Fuping1,2,3, MAO Shuhong1,2,3, QIN Huimin1,2,3
Received:
2021-09-01
Revised:
2022-02-17
Online:
2022-08-31
Published:
2022-09-08
Contact:
MAO Shuhong, QIN Huimin
摘要:
聚对苯二甲酸乙二酯(PET)因其耐用、可塑性强、安全性好等特点而广泛应用于食品包装和服装产业等领域,同时由于疏水性强、结晶度高等原因难以被微生物或酶降解利用,造成PET废弃物的不断积累,带来严重的环境和社会问题。部分高质量的PET净片可以再用到食品包装中,但绝大多数废弃PET通过常规的机械回收方法被降级利用,不能做到绿色高效回收。因此,解决“白色污染”,探索安全高效的生物降解方法成为急需攻克的重大研究课题。本文以石油基塑料的现状为背景,以PET的生物降解为切入点,综述了PET的生物降解研究现状,以宏基因组学、蛋白质组学为基础,重点总结了微生物和新酶基因的挖掘方法,并通过结构分析,以追溯不同来源的PET降解酶特性,利用定向改造和智能计算策略提高酶特性以及PET的降解效率。在改造降解酶的同时,探索对PET原材料的可降解性改良,提出了“双向改造”的思想。塑料降解酶新酶挖掘与工程改造、多酶催化体系开发以及塑料的可持续性能的改良等领域将成为塑料绿色降解的主流趋势,其为探索PET高效生物降解提供了新思路。
中图分类号:
李磊, 高鑫, 齐宏斌, 李超, 路福平, 毛淑红, 秦慧民. 现代生物技术推动塑料中聚对苯二甲酸乙二酯绿色降解的研究进展[J]. 合成生物学, 2022, 3(4): 763-780.
LI Lei, GAO Xin, QI Hongbin, LI Chao, LU Fuping, MAO Shuhong, QIN Huimin. Research progress of modern biotechnology-promoted green degradation of polyethylene terephthalate in plastics[J]. Synthetic Biology Journal, 2022, 3(4): 763-780.
图1 2020年中国塑料生产及处理情况(The data in the figure come from the National Bureau of Statistics. In 2020, the output of plastic products in China was 76.032 million tons, and the consumption of plastics was 90.877 million tons. Compared with 2019, this was a 12.2% increase. Plastic waste was 38.4 million tons. Green recycling accounts for 17.6% of the total waste)
Fig. 1 Plastic production and processing in China in 2020
降解塑料类型 | 降解酶来源 | 降解酶名称 | 最佳降解温度/℃ | 文献 |
---|---|---|---|---|
PET | Fosmid基因文库 | LCC | 50 | [ |
Sphagnummagellanicum | EstC7 | 50 | [ | |
Thermobifida alba AHK119 | Est119 | 45~55 | [ | |
T.alba DSM43185 | Tha_Cut1 | 88.7 | [ | |
T.cellulosilytica DSM44535 | Tc_Cut1 | 50 | [ | |
Humicola insolens | HiC | 70 | [ | |
Sminthurusviridis AHK190 | Cut190 | 65 | [ | |
T. fusca DSM43793 | TfH | 55 | [ | |
T. halotolerans DSM44931 | Thh_Est | 50 | [ | |
T.insolens | pulA | 80 | [ | |
Thermomyces lanuginosus | TLL | 37 | [ | |
Acidovorax delafieldii BS-3 | PETase | 30 | [ | |
Ideonella sakaiensis 201-F6 | IsPETase | 30 | [ | |
T.fusca KW3 | TfCut2 | 70 | [ |
表1 PET降解酶研究进展
Tab. 1 Research progress of PET degrading enzymes
降解塑料类型 | 降解酶来源 | 降解酶名称 | 最佳降解温度/℃ | 文献 |
---|---|---|---|---|
PET | Fosmid基因文库 | LCC | 50 | [ |
Sphagnummagellanicum | EstC7 | 50 | [ | |
Thermobifida alba AHK119 | Est119 | 45~55 | [ | |
T.alba DSM43185 | Tha_Cut1 | 88.7 | [ | |
T.cellulosilytica DSM44535 | Tc_Cut1 | 50 | [ | |
Humicola insolens | HiC | 70 | [ | |
Sminthurusviridis AHK190 | Cut190 | 65 | [ | |
T. fusca DSM43793 | TfH | 55 | [ | |
T. halotolerans DSM44931 | Thh_Est | 50 | [ | |
T.insolens | pulA | 80 | [ | |
Thermomyces lanuginosus | TLL | 37 | [ | |
Acidovorax delafieldii BS-3 | PETase | 30 | [ | |
Ideonella sakaiensis 201-F6 | IsPETase | 30 | [ | |
T.fusca KW3 | TfCut2 | 70 | [ |
降解塑料类型 | 微生物名称 | 最适降解温度/℃ | 文献 |
---|---|---|---|
PET | Aspergillusoryzae CCUG33812 | 30 | [ |
Clostridium botulinum ATCC3502 | 50 | [ | |
Pseudomonas aestusnigri VGXO14T | 30 | [ | |
Fusarium oxysporum | 30 | [ | |
Fusarium solani | 30 | [ | |
Streptomyces scabies | 37 | [ | |
Penicillium citrinum | 30 | [ | |
Trichoderma reesei | 37 | [ | |
Burkholderiacepacia | 37 | [ | |
Candida antarctica | 60 | [ |
表2 PET降解微生物研究进展
Tab. 2 Research progress of microorganisms in PET degradation
降解塑料类型 | 微生物名称 | 最适降解温度/℃ | 文献 |
---|---|---|---|
PET | Aspergillusoryzae CCUG33812 | 30 | [ |
Clostridium botulinum ATCC3502 | 50 | [ | |
Pseudomonas aestusnigri VGXO14T | 30 | [ | |
Fusarium oxysporum | 30 | [ | |
Fusarium solani | 30 | [ | |
Streptomyces scabies | 37 | [ | |
Penicillium citrinum | 30 | [ | |
Trichoderma reesei | 37 | [ | |
Burkholderiacepacia | 37 | [ | |
Candida antarctica | 60 | [ |
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