Mohanan Nisha, Montazer Zahra, Sharma Parveen K, Levin David B
Department of Biosystems Engineering, University of Manitoba, Winnipeg, MB, Canada.
Faculty of Food Engineering, The Educational Complex of Agriculture and Animal Science, Torbat-e-jam, Iran.
Front Microbiol. 2020 Nov 26;11:580709. doi: 10.3389/fmicb.2020.580709. eCollection 2020.
Synthetic plastics are pivotal in our current lifestyle and therefore, its accumulation is a major concern for environment and human health. Petroleum-derived (petro-)polymers such as polyethylene (PE), polyethylene terephthalate (PET), polyurethane (PU), polystyrene (PS), polypropylene (PP), and polyvinyl chloride (PVC) are extremely recalcitrant to natural biodegradation pathways. Some microorganisms with the ability to degrade petro-polymers under conditions have been isolated and characterized. In some cases, the enzymes expressed by these microbes have been cloned and sequenced. The rate of polymer biodegradation depends on several factors including chemical structures, molecular weights, and degrees of crystallinity. Polymers are large molecules having both regular crystals (crystalline region) and irregular groups (amorphous region), where the latter provides polymers with flexibility. Highly crystalline polymers like polyethylene (95%), are rigid with a low capacity to resist impacts. PET-based plastics possess a high degree of crystallinity (30-50%), which is one of the principal reasons for their low rate of microbial degradation, which is projected to take more than 50 years for complete degraded in the natural environment, and hundreds of years if discarded into the oceans, due to their lower temperature and oxygen availability. The enzymatic degradation occurs in two stages: adsorption of enzymes on the polymer surface, followed by hydro-peroxidation/hydrolysis of the bonds. The sources of plastic-degrading enzymes can be found in microorganisms from various environments as well as digestive intestine of some invertebrates. Microbial and enzymatic degradation of waste petro-plastics is a promising strategy for depolymerization of waste petro-plastics into polymer monomers for recycling, or to covert waste plastics into higher value bioproducts, such as biodegradable polymers via mineralization. The objective of this review is to outline the advances made in the microbial degradation of synthetic plastics and, overview the enzymes involved in biodegradation.
合成塑料在我们当前的生活方式中至关重要,因此,其积累是环境和人类健康的一个主要问题。石油衍生的(石化)聚合物,如聚乙烯(PE)、聚对苯二甲酸乙二酯(PET)、聚氨酯(PU)、聚苯乙烯(PS)、聚丙烯(PP)和聚氯乙烯(PVC),对自然生物降解途径具有极强的抗性。一些能够在特定条件下降解石化聚合物的微生物已被分离和鉴定。在某些情况下,这些微生物表达的酶已被克隆和测序。聚合物的生物降解速率取决于几个因素,包括化学结构、分子量和结晶度。聚合物是具有规则晶体(结晶区域)和不规则基团(无定形区域)的大分子,后者赋予聚合物柔韧性。高度结晶的聚合物,如聚乙烯(95%),质地坚硬,抗冲击能力低。基于PET的塑料具有高度的结晶度(30 - 50%),这是其微生物降解速率低的主要原因之一,预计在自然环境中完全降解需要50多年,如果丢弃到海洋中则需要数百年,因为海洋中的温度和氧气供应较低。酶促降解分两个阶段进行:酶吸附在聚合物表面,随后是键的氢过氧化/水解。塑料降解酶的来源可以在各种环境中的微生物以及一些无脊椎动物的消化道中找到。废弃石化塑料的微生物和酶促降解是一种很有前景的策略,可将废弃石化塑料解聚为聚合物单体进行回收,或将废弃塑料转化为更高价值的生物产品,如通过矿化转化为可生物降解的聚合物。本综述的目的是概述合成塑料微生物降解方面取得的进展,并概述参与生物降解的酶。