Microplastics mulch film affects the environmental behavior of adsorption and degradation of pesticide residues in soil

杀虫剂 农药降解 护根物 环境化学 吸附 化学 微塑料 益达胺 降级(电信) 农药残留 土壤污染物 土壤水分 土壤污染 环境工程 环境科学 农学 土壤科学 生物 有机化学 电信 计算机科学
作者
Changcai Wu,Shaodong Pan,Yongpan Shan,Yajie Ma,Dan Wang,Xianpeng Song,Hongyan Hu,Xiangliang Ren,Xiaoyan Ma,Jinjie Cui,Yan Ma
出处
期刊:Environmental Research [Elsevier BV]
卷期号:214: 114133-114133 被引量:39
标识
DOI:10.1016/j.envres.2022.114133
摘要

Plastic pollution in the soil ecosystem is currently receiving worldwide attention. However, little is known whether the presence of microplastics (MPs) in soil will affect the environmental behavior of pesticide residues in soil. Here, the effect of the addition of new mulch MPs (New-MPs), aged mulch MPs (Aged-MPs) and biodegradable mulch MPs (BioD-MPs) on the adsorption and degradation behaviors of two pesticides (imidacloprid and flumioxazin) in soil was investigated. Three MPs slowed down rapid adsorption stage of pesticides in soil and delayed the time to reach adsorption equilibrium. Adsorption rates: Soil > Soil + New-MPs > Soil + Aged-MPs > Soil + BioD-MPs. Three MPs enhanced the adsorption strength of the soil system for the two pesticides, and the aging treatment of the MPs enhanced this effect. Three MPs affected the degradation process of the two pesticides. New-MPs promoted the degradation of two pesticides imidacloprid and flumioxazin, and the degradation half-lives were shortened to 0.93 and 0.85 times, respectively; while Aged-Mps and BioD-MPs delayed the degradation process of two pesticides, and the degradation half-lives were extended to 1.64 times and 1.21 times, respectively. The effect was more significant with the increase of MPs and pesticides concentration. Pesticide polarity, surface structure and functional groups of MPs are potentially important reasons for the differences in adsorption and degradation of MPs-soil systems. Our findings provide a deep insight into understanding the mechanism of interaction between MPs and pesticide residues in soil environment.
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