Institute of Marine Research (IIM), National Research Council (CSIC), Eduardo Cabello 6, 36208, Vigo, Spain.
Department of Material Science, Metallurgical Engineering and Inorganic Chemistry, University of Cádiz, Spain.
Environ Pollut. 2021 Jan 1;268(Pt A):115769. doi: 10.1016/j.envpol.2020.115769. Epub 2020 Oct 1.
The contamination of the aquatic environment by plastic nanoparticles is becoming a major concern due to their potential adverse effects in aquatic biota. Therefore, in-depth knowledge of their uptake, trafficking and effects at cellular and systemic levels is essential to understand their potential impacts for aquatic species. In this work, zebrafish (Danio rerio) was used as a model and our aims were: i) to determine the distribution, uptake, trafficking, degradation and genotoxicity of polystyrene (PS) NPs of different sizes in a zebrafish cell line; ii) to study PS NPs accumulation, migration of immune cells and genotoxicity in larvae exposed to PS NPs; and iii) to assess how PS NPs condition the survival of zebrafish larvae exposed to a pathogen and/or how they impact the resistance of an immunodeficient zebrafish. Our results revealed that the cellular distribution differed depending on the particle size: the 50 nm PS NPs were more homogeneously distributed in the cytoplasm and the 1 μM PS NPs more agglomerated. The main endocytic mechanisms for the uptake of NPs were dynamin-dependent internalization for the 50 nm NPs and phagocytosis for the 1 μm nanoparticles. In both cases, degradation in lysosomes was the main fate of the PS NPs, which generated alkalinisation and modified cathepsin genes expression. These effects at cellular level agree with the results in vivo, since lysosomal alkalization increases oxidative stress and vice versa. Nanoparticles mainly accumulated in the gut, where they triggered reactive oxygen species, decreased expression of the antioxidant gene catalase and induced migration of immune cells. Finally, although PS NPs did not induce mortality in wild-type larvae, immunodeficient and infected larvae had decreased survival upon exposure to PS NPs. This fact could be explained by the mechanical disruption and/or the oxidative damage caused by these NPs that increase their susceptibility to pathogens.
由于塑料纳米颗粒对水生生物群具有潜在的不利影响,因此其对水生环境的污染正成为一个主要关注点。因此,深入了解它们在细胞和系统水平上的摄取、转运和作用对于了解它们对水生物种的潜在影响至关重要。在这项工作中,斑马鱼(Danio rerio)被用作模型,我们的目的是:i)确定不同大小的聚苯乙烯(PS)纳米颗粒在斑马鱼细胞系中的分布、摄取、转运、降解和遗传毒性;ii)研究暴露于 PS NPs 的幼虫中 PS NPs 的积累、免疫细胞迁移和遗传毒性;iii)评估 PS NPs 如何影响暴露于病原体的斑马鱼幼虫的存活,以及它们如何影响免疫缺陷斑马鱼的抵抗力。我们的结果表明,细胞内分布取决于颗粒大小:50nm PS NPs 在细胞质中分布更均匀,而 1μm PS NPs 聚集更多。纳米颗粒摄取的主要内吞机制是 50nm PS NPs 的网格蛋白依赖内化和 1μm 纳米颗粒的吞噬作用。在这两种情况下,溶酶体降解是 PS NPs 的主要归宿,这导致溶酶体碱化并改变组织蛋白酶基因的表达。这些细胞水平上的效应与体内结果一致,因为溶酶体碱化增加氧化应激,反之亦然。纳米颗粒主要积聚在肠道中,在肠道中它们引发活性氧,降低抗氧化基因过氧化氢酶的表达并诱导免疫细胞迁移。最后,尽管 PS NPs 没有在野生型幼虫中引起死亡率,但免疫缺陷和感染的幼虫在暴露于 PS NPs 时存活率降低。这一事实可以用这些 NPs 引起的机械破坏和/或氧化损伤来解释,这增加了它们对病原体的易感性。