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Sulfamethoxazole (SMX) residues in river water may disturb microbial nitrogen (N) transformation and compromise N-removal stability. Bypass constructed wetlands (CWs) divert polluted water through off-channel wetland units and return treated water to the river, providing an off-line treatment approach without directly modifying the main river channel. However, the N-removal and microbial N-transformation responses of bypass CWs to SMX under alternating runoff and lake-water conditions, particularly differences between planted and unplanted systems, remain poorly understood. In this study, laboratory-scale bypass CWs receiving alternating simulated rainwater runoff and natural lake water were established, including an unplanted CW (U-CW) and a planted CW (P-CW) with mature Canna indica and Phragmites australis , to evaluate N removal, microbial communities, and predicted functional shifts under SMX stress. Under SMX exposure, TN and NO 3 − -N removal increased in U-CW, while NH 4 + -N and NO 2 − -N remained stable. Surface NO 3 − -N accumulation (89.89 mg/kg) suggested that apparent nitrate removal did not reflect net N reduction. In contrast, P-CW maintained stable N removal with high NH 4 + -N removal efficiency (84.24%). SMX stress decreased microbial diversity in U-CW but increased diversity and unique taxa in P-CW. Anaeromyxobacter increased in both systems and was positively correlated with TN and NO 2 − -N removal, while Nitrospira showed opposite responses. PICRUSt2 predictions indicated reduced nitrate-reduction potential in U-CW but maintained nitrate/nitrite reduction and N-assimilation potential in P-CW. Overall, SMX disrupted N-transformation balance in U-CW, whereas P-CW showed greater buffering capacity against SMX stress. These findings highlight the potential of planted bypass CWs for stable treatment of antibiotic-impacted rivers.
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Huang et al. (2026) studied this question.
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