Conventional and Biodegradable Microplastics Both Impair Soil Phosphorus Cycling and Availability via Microbial Suppression

微塑料 环境化学 化学 生物地球化学循环 自行车 磷酸酶 矿化(土壤科学) 肥料 TCEP 碱性磷酸酶 孵化 磷酸盐 土壤生态学 土壤pH值 农学 微生物种群生物学 土壤健康 土壤酸化 微生物 生态学 污染物 土壤有机质 生物量(生态学) 土壤质量 土壤微生物学 环境科学 丰度(生态学) 生态毒性 土工试验 土壤化学 土壤水分
作者
Chengming Zhang,Ziyi Zhao,Fengwu Zhou,Changzhi Shi,Xiangmei Zhai,Zhimin Sha,Qingnan Chu,Hongling Liu,Songqin Liu,Zezhen Pan,Xiaofei Wang,Xiangcheng Pan,Mingliang Fang,Matthias C. Rillig,Zimeng Wang
出处
期刊:Environmental Science & Technology [American Chemical Society]
卷期号:60 (1): 1229-1240 被引量:8
标识
DOI:10.1021/acs.est.5c11806
摘要

Microplastics (MPs) are emerging soil pollutants that can disrupt essential biogeochemical processes, yet their effects on phosphorus (P) cycling remain underexplored. Here, we conducted a 150-day incubation experiment using agricultural soil amended with either polyethylene (PE, conventional) or polylactic acid (PLA, biodegradable) MPs to investigate their impact on microbially mediated P cycling. MPs altered soil P cycling and decreased available phosphorus (AP) by ∼15% after 90 days. Fourier transform infrared spectroscopy revealed weakened AP-associated functional groups (P–O–P, P–O, and P═O), most pronounced under PLA treatment. These shifts were accompanied by reduced abundances of key P-cycling taxa ( Bacillus, Paenibacillus, and Sphingomonas ) and downregulation of phosphatase gene abundance ( phoA/D/X: −65.4% in PE, −59.8% in PLA). Correspondingly, the activities of acid, neutral, and alkaline phosphatases were all suppressed, with alkaline phosphatase in PE-treated soil reduced by 34.1%. Together, these results demonstrate that MPs disturb biotic transformation pathways, leading to subsequent alterations in the chemical speciation of soil P and decreased AP content. Notably, significant disruption was observed for both conventional and biodegradable types. Our findings challenge the prevailing assumption of environmental benignity for biodegradable plastics and underscore the urgent need for mechanistic assessments of their byproducts. Such disruption may hinder microbial P mobilization and decrease fertilizer use efficiency, ultimately threatening soil health and agricultural sustainability.
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