4.7 Article

Removal of tetracycline in nitrification membrane bioreactors with different ammonia loading rates: Performance, metabolic pathway, and key contributors

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ENVIRONMENTAL POLLUTION
卷 332, 期 -, 页码 -

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ELSEVIER SCI LTD
DOI: 10.1016/j.envpol.2023.121922

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Tetracycline; Ammonia loading rate; MBR; Biodegradation; Cometabolism

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This study investigated the removal of tetracycline (TC) in three parallel lab-scale nitrification MBRs with different ammonium loading rates (ALRs) at four different concentrations. The results showed that high TC removal efficiency (90.46%) was achieved in the MBR with the highest ALR (AN1000) at an influent TC concentration of 50 mg/L. Higher ALRs promoted TC removal at lower influent TC concentrations, while no significant difference was observed at higher influent TC concentrations, suggesting that heterotrophic degradation could be strengthened after long-term exposure to high TC concentration.
Membrane bioreactors (MBRs) have been widely applied for the treatment of wastewater that contains high concentrations of both ammonium and antibiotics. Nonetheless, information about tetracycline (TC) removal in nitrification MBRs with high ammonium loading rates (ALRs) is still very limited. Herein, the fate of TC at four different concentrations of 1, 5, 20, and 50 mg/L in three parallel lab-scale nitrification MBRs with different ALRs (named AN50, AN500, and AN1000) were investigated in this study. Excellent nitrification performance and high TC removal efficiency (90.46%) were achieved in AN1000 at infiuent TC concentration of 50 mg/L. Higher ALRs promoted the removal of TC at lower infiuent TC concentration (& LE;5 mg/L), while no significant difference was observed in TC removal efficiencies among different ALRs MBRs at higher infiuent TC concentration (& GE;20 mg/L), implying that the heterotrophic degradation could be strengthened after long-term exposure to high concentration of TC. Batch tests demonstrated that adsorption and biodegradation were the primary TC removal routes by nitrification sludge, of which both autotrophic ammonia oxidizers and heterotrophic microorganisms played an important role in the biodegradation of TC. FT-IR spectroscopy confirmed that amide groups on the sludge biomass contributed to the adsorption of TC. Mass balance analyses indicated that biodegradation (63.4-88.6% for AN50, 74.5-88.4% for AN500 and 74.4-91.4% for AN1000) was the major mechanism responsible for the removal of TC in nitrification MBRs, and its contribution increased with infiuent TC concentration, while only 1.1%-15.0% of TC removal was due to biosorption. TC was progressively degraded to small molecules and the presence of TC had no notable effect on membrane permeability. These jointly confirmed TC could be effectively removed via initial adsorption and subsequent biodegradation, while biodegradation was the primary mechanism in this study.

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