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Microplastic pollution drives soil bacterial community shifts and alters phosphorus cycling across land use gradients
Summary
Researchers conducted a landscape-scale field study across urban, mining, agricultural, and rural land-use types to measure accumulated microplastic levels and their effects on soil bacterial communities and phosphorus cycling. Microplastic contamination shifted bacterial community composition and impaired phosphorus mineralization, with effects scaling with land-use intensity and microplastic abundance.
Microplastics (MPs) pollution is increasingly recognized as a pervasive threat to terrestrial ecosystems, yet its functional impacts on soil processes remain poorly understood under field conditions. Here, we conducted a landscape-scale study across four land-use types, urban, mining, agricultural, and rural, to quantify environmentally accumulated MP and assess their effects on phosphorus (P) cycling and microbial communities. High-resolution spectroscopy revealed that urban and mining soils contained the highest MP loads (600-1000 particles/kg), with distinct polymer types linked to anthropogenic activities. MP abundance was negatively correlated with P solubilization (R = -0.59, p < 0.01) and soil enzymatic activity, and positively with P immobilization (R = 0.53, p < 0.05), indicating impaired nutrient availability. Amplicon sequencing showed that MP-rich soils were enriched in certain taxa within Firmicutes and Actinobacteria often associated with stress tolerance, while low-MP soils supported functionally important groups, including specific Acidobacteria and nitrifying archaea (e.g., Candidatus Nitrososphaera). Co-occurrence network analysis revealed simplified and cooperative microbial structures in MP-polluted soils. Multivariate analyses confirmed that MP are independent drivers of microbial beta-diversity beyond land use. Overall, our findings provide in situ evidence that MP, even at moderate levels, alter microbial ecology and disrupt soil nutrient cycling, posing a potential risk to biogeochemical resilience in human-impacted landscapes.
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