Marine College, Shandong University, Weihai, Shandong 264209, China.
Environment Research Institute, Shandong University, Qingdao 266237, China.
J Hazard Mater. 2024 Dec 5;480:136236. doi: 10.1016/j.jhazmat.2024.136236. Epub 2024 Oct 21.
Biomolecules, prevalent in the marine environment, can readily adsorb onto the surface of micro(nano)plastics (MNPs), forming eco-corona. This study indicated that 50 nm polystyrene nanoplastics (NP50), whether wrapped with eco-corona or not, can passively enter embryos, whereas 5 µm polystyrene microplastics (MP5) cannot. Additionally, translocation of MP5 from the intestine to the liver was observed in larvae, a process facilitated by eco-corona. Notably, eco-corona prolonged the retention time of MNPs in larvae. However, NP50 was more challenging to purify than MP5, irrespective of the presence of eco-corona. Interestingly, eco-corona degraded in the intestine during the uptake of MNPs, and the hard coronae that readily formed on NP50 may restrict the degradation rate. Although NP50 significantly disrupted larval microbiota homeostasis compared with MP5, eco-corona was more likely to exacerbate MP5's damage to the intestine and liver by disrupting microbiota homeostasis. Additionally, NP50 caused more significant damage to immunity and energy metabolism compared with MP5, regardless of the presence of eco-corona. This study revealed that previously overlooked biomolecules in the marine environment can enhance the translocation of MNPs and subsequently exacerbate their toxic effects, providing theoretical support for assessing the ecological risks of MNPs in real environments.
生物分子在海洋环境中很常见,它们可以很容易地吸附在微(纳)塑料(MNPs)的表面,形成生态冠。本研究表明,50nm 的聚苯乙烯纳米塑料(NP50),无论是否包裹生态冠,都可以被动进入胚胎,而 5μm 的聚苯乙烯微塑料(MP5)则不能。此外,研究还观察到 MP5 从肠道转移到肝脏,这一过程是由生态冠促进的。值得注意的是,生态冠延长了 MNPs 在幼虫体内的滞留时间。然而,NP50 比 MP5 更难被清除,无论是否存在生态冠。有趣的是,生态冠在吸收 MNPs 的过程中会在肠道中降解,而 NP50 上易于形成的硬冠可能会限制降解速率。尽管 NP50 与 MP5 相比显著破坏了幼虫的微生物组稳态,但生态冠更有可能通过破坏微生物组稳态来加剧 MP5 对肠道和肝脏的损伤。此外,NP50 引起的免疫和能量代谢损伤比 MP5 更显著,无论是否存在生态冠。本研究揭示了海洋环境中以前被忽视的生物分子可以增强 MNPs 的迁移,并随后加剧其毒性作用,为评估 MNPs 在真实环境中的生态风险提供了理论支持。