Environment Research Institute, Shandong University, Qingdao 266237, China.
School of Environmental Sciences and Engineering, Shandong University, Qingdao 266237, China.
Sci Total Environ. 2021 Jul 20;779:146523. doi: 10.1016/j.scitotenv.2021.146523. Epub 2021 Mar 18.
Microplastics and nanoplastics can accumulate in organisms after being ingested, be transported in the food web, and ultimately threaten human health. An understanding of the cellular internalization and release of micro(nano)plastics is important to predict their cytotoxicity. In this study, 50 nm, 500 nm and 5 μm polystyrene particles (PS50, PS500 and PS5000) were exposed to both model cell membranes and rat basophilic leukemia (RBL-2H3) cells. PS50 and PS500 absorb on the model membrane due to hydrophobic interactions and Van der Waals' forces, and may also penetrate the model membrane. PS50 and PS500 are internalized into living cells via both passive membrane penetration and active endocytosis. The passive membrane penetration is due to the partition of polystyrene particles in the water-phospholipid system. The endocytosis of PS50 occurs through the clathrin-mediated pathway, the caveolin-mediated pathway and macropinocytosis, but endocytosis of PS500 is mainly via the macropinocytosis. PS5000 cannot adhere to the cell membrane or be internalized into cells due to its large size and weak Brownian motion. The endocytosed PS50 and PS500 mainly accumulate in the lysosomes. The passively internalized PS50 and PS500 initially distribute in the cytoplasm not in lysosomes, but are transported to lysosomes with energy supply. PS50 and PS500 are excreted from cells via energy-free penetration and energy-dependent lysosomal exocytosis. The masses of the internalized PS50 inside the cells and the excreted PS50 outside the cells were both higher than the masses of PS500, indicating that the smaller particles are more easily enter or leave cells than do their larger counterparts. Our findings will contribute to the risk assessment of micro(nano)plastics and their safe application.
微塑料和纳米塑料在被摄入后会在生物体内积累,在食物网中运输,并最终威胁人类健康。了解微(纳)塑料的细胞内化和释放对于预测其细胞毒性非常重要。在这项研究中,将 50nm、500nm 和 5μm 的聚苯乙烯颗粒(PS50、PS500 和 PS5000)分别暴露于模型细胞膜和大鼠嗜碱性白血病(RBL-2H3)细胞。PS50 和 PS500 由于疏水相互作用和范德华力而吸附在模型膜上,并且可能还会穿透模型膜。PS50 和 PS500 通过被动膜穿透和主动内吞作用被内化到活细胞中。被动膜穿透是由于聚苯乙烯颗粒在水-磷脂体系中的分配。PS50 的内吞作用通过网格蛋白介导途径、小窝蛋白介导途径和胞吞作用发生,而 PS500 的内吞作用主要通过胞吞作用发生。由于尺寸较大且布朗运动较弱,PS5000 不能附着在细胞膜上或被内化到细胞内。内吞的 PS50 和 PS500 主要积聚在溶酶体中。被动内化的 PS50 和 PS500 最初分布在细胞质中而不是溶酶体中,但在提供能量的情况下被转运到溶酶体中。PS50 和 PS500 通过无能量渗透和能量依赖的溶酶体胞吐作用从细胞中排出。细胞内 PS50 的内化量和细胞外 PS50 的排泄量均高于 PS500,这表明较小的颗粒比其较大的颗粒更容易进入或离开细胞。我们的研究结果将有助于评估微(纳)塑料的风险及其安全应用。