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Bioelectrochemistry promotes microbial activity and accelerates wastewater methanogenesis in anaerobic digestion under combined exposure to antibiotics and microplastics

Journal of Hazardous Materials 2025 7 citations ? Citation count from OpenAlex, updated daily. May differ slightly from the publisher's own count.
Hui Wang, Qixing Zhou

Summary

Researchers tested a bioelectrochemical system for treating wastewater contaminated with both antibiotics and microplastics, achieving 14% better treatment efficiency and methane recovery than standard methods. The electrical stimulation helped beneficial microbes thrive despite the pollutants, though it also increased some antibiotic resistance genes. This study is relevant because it addresses a real-world challenge of treating water containing multiple contaminants, including microplastics, before it reaches the environment.

Study Type Environmental

Antibiotics and microplastics (MPs), as pervasive environmental pollutants, coexist in wastewater and pose significant threats to public health. Bioelectrochemical systems (BES), which integrate microbial metabolism and electrochemical redox reactions, exhibit considerable potential for treating recalcitrant pollutants and recovering bioenergy from wastewater. This study represents the first comprehensive investigation into the application of BES for treating wastewater contaminated with multiple antibiotics and MPs, focusing on the synergistic effects of composite pollutants rather than isolated toxicological impacts. Compared to conventional anaerobic digestion, BES demonstrated enhanced wastewater treatment efficiency (14.39 %) and methane recovery (14.32 %). Under pollutant exposure and electrical stimulation, significant alterations in microbial cell viability and enzyme activities were observed. While pollutants reduced microbial species abundance, BES increased microbial diversity. The microbial community was predominantly composed of methanogens (Methanothrix), whereas fermentative bacteria (Proteiniphilum) dominated the cathode compartment. Although the addition of antibiotics did not significantly alter the overall abundance of antibiotic class and antibiotic resistance genes (ARGs), the cathode exhibited the potential to reduce their abundance. Functional gene abundance related to methane synthesis (EC:6.2.1.1) increased at the anode, while the cathode exacerbated inhibitory effects, primarily mediating acetate generation (EC:1.2.4.1, EC:2.3.1.12). These findings provide novel insights into the application of BES for treating co-contaminated wastewater, highlighting its capacity to mitigate emerging environmental challenges.

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