National Engineering Research Center for Efficient Utilization of Soil and Fertilizer Resources, College of Recourses and Environment, Shandong Agricultural University, Taian, Shandong 271018, China.
National Engineering Research Center for Efficient Utilization of Soil and Fertilizer Resources, College of Recourses and Environment, Shandong Agricultural University, Taian, Shandong 271018, China.
Water Res. 2024 Aug 1;259:121856. doi: 10.1016/j.watres.2024.121856. Epub 2024 May 30.
The accumulation of polyurethane plastics (PU-PS) in the environment is on the rise, posing potential risks to the health and function of ecosystems. However, little is known about the degradation behavior of PU-PS in the environment, especially water environment. To address this knowledge gap, we investigated and isolated a degrading strain of Streptomyces sp. B2 from the surface of polyurethane coatings. Subsequently, a photoreactor was employed to simulate the degradation process of bio-based polyurethane (BPU) and petroleum-based polyurethane (PPU) under three conditions, including single microorganism (SM), single light exposure (SL), and combined light exposure/microorganism action (ML) in aqueous solution. The results indicated that PU-PS mainly relies on biodegradation, with the highest degradation rate observed after 28 d under SM condition (BPU 5.69 %; PPU 5.25 %). SL inhibited microbial growth and degradation, with the least impact on plastic degradation. Microorganisms colonized the plastic surface, secreting relevant hydrolytic enzymes and organic acids into the culture medium, providing a negative charge. The carbon chains were broken and aged through hydrogen peroxide induction or attack by oxygen free radicals. This process promoted the formation of oxidized functional groups such as OH and CO, disrupting the polymer's structure. Consequently, localized fragmentation and erosion of the microstructure occurred, resulting in the generation of secondary microplastic (MPs) particles, weight loss of the original plastic, increased surface roughness, and enhanced hydrophilicity. Additionally, BPU exhibited greater degradability than PPU, as microorganisms could utilize the produced fatty acids, which promoted their reproduction. In contrast, PPU degradation generated a large amount of isocyanate, potentially toxic to cells and inhibiting biodegradation. This study unveils the significant role of microorganisms in plastic degradation and the underlying degradation mechanisms of BPU, providing a novel strategy for polyurethane degradation and valuable information for comprehensive assessment of the behavior and fate of MPs in the environment.
聚氨酯塑料(PU-PS)在环境中的积累呈上升趋势,对生态系统的健康和功能构成潜在风险。然而,对于 PU-PS 在环境中的降解行为,特别是水环境中的降解行为,知之甚少。为了填补这一知识空白,我们从聚氨酯涂料表面分离出一株降解菌 Streptomyces sp. B2。随后,我们采用光反应器模拟了生物基聚氨酯(BPU)和石油基聚氨酯(PPU)在三种条件下(单一微生物(SM)、单一光照(SL)和光照/微生物联合作用(ML))在水溶液中的降解过程。结果表明,PU-PS 主要依赖于生物降解,在 SM 条件下 28 天后观察到最高降解率(BPU 为 5.69%;PPU 为 5.25%)。SL 抑制微生物生长和降解,对塑料降解的影响最小。微生物在塑料表面定殖,分泌相关的水解酶和有机酸进入培养基,提供负电荷。碳链通过过氧化氢诱导或氧自由基攻击而断裂和老化。这一过程促进了氧化官能团如 OH 和 CO 的形成,破坏了聚合物的结构。因此,微结构发生局部破碎和侵蚀,导致二次微塑料(MPs)颗粒的生成、原始塑料的重量损失、表面粗糙度增加和亲水性增强。此外,BPU 比 PPU 更具可降解性,因为微生物可以利用产生的脂肪酸,促进它们的繁殖。相比之下,PPU 降解产生了大量异氰酸酯,对细胞有毒,抑制了生物降解。本研究揭示了微生物在塑料降解中的重要作用和 BPU 的潜在降解机制,为聚氨酯降解提供了新的策略,为 MPs 在环境中的行为和归宿的综合评估提供了有价值的信息。