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Tissue distribution of polystyrene nanoplastics in mice and their entry, transport, and cytotoxicity to GES-1 cells

Environmental Pollution 2021 154 citations ? Citation count from OpenAlex, updated daily. May differ slightly from the publisher's own count. Score: 60 ? 0–100 AI score estimating relevance to the microplastics field. Papers below 30 are filtered from public browse.
Yunfei Ding, Xiaohan Tong, Xiaohan Tong, Yunfei Ding, Boqing Li, Ruiqing Zhang, Xiaohan Tong, Ruiqing Zhang, Xiaohan Tong, Yunfei Ding, Boqing Li, Jing Li Jing Li Jing Li Ruiqing Zhang, Jing Li Jing Li Yunfei Ding, Ruiqing Zhang, Boqing Li, Ruiqing Zhang, Xiaohan Tong, Jing Li Ruiqing Zhang, Xiaohan Tong, Yunqiu Du, Boqing Li, Jing Li Yunqiu Du, Jing Li Boqing Li, Ruiqing Zhang, Jing Li Jing Li Jing Li Ruiqing Zhang, Jing Li Jing Li Yunqiu Du, Yunqiu Du, Jing Li Xiaohan Tong, Xiaohan Tong, Ying Zhang, Yulong Wu, Jing Li Jing Li Jing Li Boqing Li, Yulong Wu, Jing Li Xiaofei Ji, Ruiqing Zhang, Ruiqing Zhang, Ying Zhang, Xiaofei Ji, Jing Li

Summary

Scientists tracked polystyrene nanoplastics in mice after oral exposure and found the particles accumulated in the stomach, intestines, and liver tissues. In human gastric cells, the nanoplastics entered through multiple pathways and were transported through the cell's internal trafficking system, ultimately reducing cell growth and increasing cell death. The study provides detailed evidence of how nanoplastics can cross biological barriers and cause cellular damage in mammalian systems.

Polymers
Models

With the widespread use of plastics and nanotechnology products, nanoplastics (NPs) have become a potential threat to human health. It is of great practical significance to study and evaluate the distribution of NPs in mice as mammal models and their entry, transport, and cytotoxicity in human cell lines. In this study, we detected the tissue distribution of fluorescent polystyrene nanoplastics (PS-NPs) in mice and assessed their endocytosis, transport pathways, and cytotoxic effects in GES-1 cells. We found that PS-NPs were clearly visible in gastric, intestine, and liver tissues of mice and in GES-1 cells treated with PS-NPs. Entry of PS-NPs into GES-1 cells decreased with the inhibition of caveolae-mediated endocytosis (nystatin), clathrin-mediated endocytosis (chlorpromazine HCl), micropinocytosis (ethyl-isopropyl amiloride), RhoA (CCG-1423), and F-actin polymerization (lantrunculin A). Rac1 inhibitors (NSC 23766) had no significant effect on PS-NPs entering GES-1 cells. F-actin levels significantly decreased in CCG-1423-pretreated GES-1 cells exposed to PS-NPs. GES-1 cell ultrastructural features indicated that internalized PS-NPs can be encapsulated in vesicles, autophagosomes, lysosomes, and lysosomal residues. RhoA, F-actin, RAB7, and LAMP1 levels in PS-NPs-treated GES-1 cells were remarkably up-regulated and the Rab5 level was significantly down-regulated compared to levels in untreated cells. PS-NPs treatment decreased cell proliferation rates and increased cell apoptosis. The formation of autophagosomes and autolysosomes and levels of LC3II increased with the length of PS-NPs treatment. The results indicated that cells regulated endocytosis in response to PS-NPs through the RhoA/F-actin signaling pathway and internalized PS-NPs in the cytoplasm, autophagosomes, or lysosomes produced cytotoxicity. These results illustrate the potential threat of NPs pollution to human health.

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