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Metagenomic and metabolomic insight into microplastic-derived inhibition of tetracycline degradation in sediments
Summary
Microplastics in aquatic sediments don't just sit there — this study found they actively interfere with the natural microbial processes that break down antibiotic compounds like tetracycline. By combining field sampling with lab experiments, researchers showed that microplastics disrupt the microbial communities responsible for tetracycline degradation, potentially allowing antibiotics to persist longer in the environment. This interaction between microplastics and antibiotic persistence is a concern for both ecosystem health and the spread of antibiotic resistance.
Microplastics (MPs) have been extensively reported to affect organic compound metabolism and nutrient cycling in the ecosystem, particularly in aquatic sediments. However, the specific microbial pathways and underlying mechanisms governing these impacts remain incompletely understood. Herein, this study integrates field investigations and simulation experiments to demonstrate the inhibitory effects of MP contamination on tetracycline (TC) biodegradation in sediments. Our findings reveal three distinct TC biotransformation pathways in sediments, with monooxygenase-mediated hydroxylation emerging as the predominant pathway. Comparative analysis revealed significant reductions in monooxygenase abundance (56.6 %), host bacterial populations (38.5 %), and TC biodegradation efficiency (23.8 %) in MP-amended sediments compared with the control after 28 days (p < 0.05). MPs reduce microbial metabolic activity and cooperative relationships among microorganisms, which inhibit cooperative metabolism of complex organic compounds (including tetracycline). Ultimately, MPs occupy interstitial spaces within sediment matrices, thereby altering redox conditions and promoting microbial succession toward taxa less efficient in TC metabolism. Moreover, the plastisphere exhibits significantly reduced metabolic capacity for TC transformation compared with inorganic mineral-associated biofilms, thereby impeding TC biotransformation within sediments. This finding further implies that continuous MP accumulation may exacerbate interference with biogeochemical cycles.
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