Combined effects of different-sized microplastics and fluindapyr on earthworm: Bioaccumulation, oxidative stress, histopathological responses and gut microbiota
文献类型: 外文期刊
第一作者: Wang, Jingjing
作者: Wang, Jingjing;Lv, Lu;An, Xuehua;Zhang, Chunrong;Tang, Tao;Wang, Feidi;Sun, Yangying
作者机构:
关键词: Polymethylmethacrylate; Polystyrene; Fluindapyr; Earthworms; Toxic effects
期刊名称:ENVIRONMENTAL POLLUTION ( 影响因子:7.3; 五年影响因子:8.1 )
ISSN: 0269-7491
年卷期: 2025 年 366 卷
页码:
收录情况: SCI
摘要: Soil is an important sink for microplastics (MPs) and pesticides. MPs can act as carriers for pesticides, thus induce direct and indirect effects on soil organisms. Fluindapyr (FIP), a novel succinate dehydrogenase inhibitors fungicides (SDHIs), may pose a serious threat to earthworms. However, few studies have evaluated the effects of joint exposure to MPs and FIP. Here, earthworms (Eisenia fetida) were jointly exposed to PMMA (polymethylmethacrylate) and PS (polystyrene) MPs of different sizes (0.1, 1 and 10 mu m) along with FIP for 28-day to investigate the toxic effects of single and joint exposure of FIP and MPs on earthworms. The results showed that joint exposure to 0.1 and 1 mu m MP promoted the accumulation of FIP in earthworms at the beginning of the experiment compared to the sole group, but the elimination of FIP from earthworms accelerated after 14 d. In addition, the joint exposure caused more serious damages to the epidermis and intestine of earthworms and increased the severity of oxidative stress. The effects of joint exposure to FIP and MPs depended on the size of the MPs, and the strongest effects were observed in the treatment with the smallest size. The 16S rRNA sequencing results showed that the joint exposure to MPs and FIP didn't cause gut microbiota dysbiosis. However, the sole 0.1 mu m PS significantly altered the community diversity and richness of earthworm gut bacteria, and the relative abundance of Proteobacteria, Actinobacteria and Firmicutes was significantly changed. The obtained results inferred that MPs could influence environmental and toxicological behaviors of FIP and may provide data support for the risk assessments of MPs and FIP on soil ecosystems.
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