Laboratory of Biotechnology, Research Centre for Biological Sciences, Autonomous University of Tlaxcala, Ixtacuixtla, Tlaxcala, 90120, Mexico.
MSc Program in Environmental Engineering, Technological Institute of Aguascalientes, Aguascalientes, 20256, Mexico.
World J Microbiol Biotechnol. 2024 Aug 24;40(10):309. doi: 10.1007/s11274-024-04116-6.
Polyethylene, one of the most used petroleum-derived polymers, causes serious environmental pollution. The ability of Pleurotus ostreatus to degrade UV-treated and untreated recycled and unused (new) low-density polyethylene (LDPE) films was studied. We determined the fungal biomass production, enzyme production, and enzyme yield. Changes in the chemical structure and surface morphology of the LDPE after fungal growth were analyzed using FTIR spectroscopy and SEM. Functional group indices and contact angles were also evaluated. In general, the highest Lac (6013 U/L), LiP (2432 U/L), MnP (995 U/L) and UP (6671 U/L) activities were observed in irradiated recycled LDPE (IrRPE). The contact angle of all samples was negatively correlated with fermentation time; the smaller the contact angle, the longer the fermentation time, indicating effective biodegradation. The IrRPE samples exhibited the smallest contact angle (49°) at 4 weeks, and the samples were fragmented (into two pieces) at 5 weeks. This fungus could degrade unused (new) LDPE significantly within 6 weeks. The biodegradation of LDPE proceeded faster in recycled than in unused samples, which can be enhanced by exposing LDPE to UV radiation. Enzymatic production during fungal growth suggest that LDPE degradation is initiated by laccase (Lac) followed by lignin peroxidase (LiP), whereas manganese peroxidase (MnP) and unspecific peroxygenase (UP) are involved in the final degradation process. This is the first experimental study on the fungal growth and its main enzymes involved in LDPE biodegradation. This fungus has great promise as a safe, efficient, and environmentally friendly organism capable of degrading LDPE.
聚乙烯是最常用的石油衍生聚合物之一,会造成严重的环境污染。本研究考察了糙皮侧耳对经紫外光处理和未经处理的再循环和未使用(新)低密度聚乙烯(LDPE)薄膜的降解能力。我们测定了真菌生物量的产生、酶的产生和酶的产率。利用傅里叶变换红外光谱和扫描电子显微镜分析了 LDPE 化学结构和表面形貌的变化。还评估了功能基团指数和接触角。总的来说,在辐照再循环 LDPE(IrRPE)中观察到最高的 Lac(6013 U/L)、LiP(2432 U/L)、MnP(995 U/L)和 UP(6671 U/L)活性。所有样品的接触角均与发酵时间呈负相关;接触角越小,发酵时间越长,表明有效生物降解。IrRPE 样品在第 4 周时接触角最小(49°),第 5 周时样品破碎(分成两块)。该真菌可以在 6 周内显著降解未使用(新)LDPE。在再循环样品中,LDPE 的生物降解速度快于未使用的样品,而将 LDPE 暴露于紫外线下可以增强生物降解。真菌生长过程中的酶产生表明,LDPE 的降解是由漆酶(Lac)引发的,随后是木质素过氧化物酶(LiP),而锰过氧化物酶(MnP)和非特异性过氧化物酶(UP)则参与最终的降解过程。这是关于真菌生长及其参与 LDPE 生物降解的主要酶的首次实验研究。该真菌作为一种安全、高效、环保的生物,具有降解 LDPE 的巨大潜力。