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Article ? AI-assigned paper type based on the abstract. Classification may not be perfect — flag errors using the feedback button. Tier 2 ? Original research — experimental, observational, or case-control study. Direct primary evidence. Environmental Sources Marine & Wildlife Sign in to save

Effects of microplastics on nitrogen and phosphorus cycles and microbial communities in sediments

Environmental Pollution 2022 107 citations ? Citation count from OpenAlex, updated daily. May differ slightly from the publisher's own count. Score: 50 ? 0–100 AI score estimating relevance to the microplastics field. Papers below 30 are filtered from public browse.
Maoyun Yin, Xiang Wang, Maoyun Yin, Jueqiao Wang, Jueqiao Wang, Yuting Liu, Bin Yan, Zhihao Zhu, Bin Yan, Huan Wang, Xiang Wang, Yan Wu, Yuting Liu, Yan Wu, Xiang Wang, Yan Wu, Huan Wang, Yan Wu, Huan Wang, Yuting Liu, Yan Wu, Huan Wang, Xiang Wang, Xiang Wang, Huan Wang, Jueqiao Wang, Yan Wu, Jueqiao Wang, Huan Wang, Zhihao Zhu, Maoyun Yin, Maoyun Yin, Zhihao Zhu, Yan Wu, Xixi Yan, Yuting Liu, Xixi Yan, Chuan Fu Meijun Liu, Yan Wu, Chuan Fu Chuan Fu

Summary

Researchers found that PVC, PLA, and polypropylene microplastics altered nitrogen and phosphorus cycling in freshwater sediments by shifting microbial community composition, with effects varying by polymer type and biodegradability.

Study Type Environmental

Sediments are the long-term sinks of microplastics (MPs) and nutrients in freshwater ecosystems. Therefore, understanding the effect of MPs on sediment nutrients is crucial. However, few studies have discussed the effects of MPs on nitrogen and phosphorus cycles in freshwater sediments. Herein, 0.5% (w/w) polyvinyl chloride (PVC), polylactic acid (PLA), and polypropylene (PP) MPs were added to freshwater sediments to evaluate their effects on microbial communities and nitrogen and phosphorus release. The potential biochemical functions of the bacterial communities in the sediments were predicted and assessed via 16S rRNA gene sequencing. The results showed that MPs significantly affected the microbial community composition and nutrient cycling in the sediments. PVC and PP MPs can promote microbial nitrification and nitrite oxidation, while PP can significantly promote alkaline phosphatase (ALP) activity and the abundance of the phosphorus-regulation (phoR) gene. PLA MPs had the potential to promote the abundance of microbial phosphorus transporter (ugpB), nitrogen fixation (nifD, nifH, and nifX), and denitrification (nirS, napA, and norB) genes and inhibit nitrification, resulting in massive accumulation and release of ammonia nitrogen. Although PLA MPs inhibited the activity of ALP and the abundance of the organophosphorus mineralization (phoD) gene, it could enhance dissimilatory iron and sulfite reduction, which may promote the release of sedimentary phosphorus. Our findings may help understand the mechanisms of nitrogen and phosphorus cycles and microbial communities driven by MPs in sediments and provide a basis for future assessments of the environmental behavior of MPs in freshwater ecosystems.

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