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通过宏基因组学和宏转录组学分析揭示硫介导自养反硝化中诺氟沙星去除机制和抗生素耐药基因(ARGs)的命运。

Unraveling the mechanism of norfloxacin removal and fate of antibiotics resistance genes (ARGs) in the sulfur-mediated autotrophic denitrification via metagenomic and metatranscriptomic analyses.

机构信息

Xi'an TPRI Water-Management & Environmental Protection Co. Ltd., State Key Laboratory of High-Efficiency Flexible Coal Power Generation and Carbon Capture Utilization and Storage, PR China.

Research & Development Institute in Shenzhen, School of Chemistry and Chemical Engineering, Northwestern Polytechnical University, PR China.

出版信息

Sci Total Environ. 2024 Apr 20;922:171328. doi: 10.1016/j.scitotenv.2024.171328. Epub 2024 Feb 28.

Abstract

The co-contamination of antibiotics and nitrogen has attracted widespread concerns due to its potential harm to ecological safety and human health. Sulfur-driven autotrophic denitrification (SAD) with low sludge production rate was adopted to treat antibiotics laden-organic deficient wastewater. Herein, a lab-scale sequencing batch reactor (SBR) was established to explore the simultaneous removal of nitrate and antibiotics, i.e. Norfloxacin (NOR), as well as microbial response mechanism of SAD sludge system towards NOR exposure. About 80.78 % of NOR was removed by SAD sludge when the influent NOR level was 0.5 mg/L, in which biodegradation was dominant removal route. The nitrate removal efficiency decreased slightly from 98.37 ± 0.58 % to 96.58 ± 1.03 % in the presence of NOR. Thiobacillus and Sulfurimonas were the most abundant sulfur-oxidizing bacteria (SOB) in SAD system, but Thiobacillus was more sensitive to NOR. The up-regulated genes related to Xenobiotics biodegradation and metabolism and CYP450 indicated the occurrence of NOR biotransformation in SAD system. The resistance of SAD sludge to the exposure of NOR was mainly ascribed to antibiotic efflux. And the effect of antibiotic inactivation was enhanced after long-term fed with NOR. The NOR exposure resulted in the increased level of antibiotics resistance genes (ARGs) and mobile genetic elements (MGEs). Besides, the enhanced ARG-MGE co-existence patterns further reveals the higher horizontal mobility potential of ARGs under NOR exposure pressures. The most enriched sulfur oxidizing bacterium Thiobacillus was a potential host for most of ARGs. This study provides a new insight for the treatment of NOR-laden wastewater with low C/N ratio based on the sulfur-mediated biological process.

摘要

抗生素和氮的共污染由于其对生态安全和人类健康的潜在危害而引起了广泛关注。采用产硫自养反硝化(SAD)工艺,污泥产量低,处理抗生素负荷有机缺乏废水。本文采用实验室规模序批式反应器(SBR),探索硝酸盐和抗生素(如诺氟沙星,NOR)的同时去除,以及 SAD 污泥系统对 NOR 暴露的微生物响应机制。当进水 NOR 浓度为 0.5mg/L 时,SAD 污泥去除了约 80.78%的 NOR,其中生物降解是主要的去除途径。在存在 NOR 的情况下,硝酸盐去除效率从 98.37%±0.58%略有下降至 96.58%±1.03%。硫杆菌和硫单胞菌是 SAD 系统中最丰富的硫氧化菌(SOB),但硫杆菌对 NOR 更敏感。与 Xenobiotics 生物降解和代谢以及 CYP450 相关的上调基因表明 NOR 在 SAD 系统中发生了生物转化。SAD 污泥对 NOR 暴露的抗性主要归因于抗生素外排。并且,长期喂食 NOR 后会增强抗生素失活的效果。NOR 暴露导致抗生素抗性基因(ARGs)和移动遗传元件(MGEs)的水平升高。此外,增强的 ARG-MGE 共存模式进一步揭示了在 NOR 暴露压力下 ARGs 具有更高的水平转移潜力。最丰富的硫氧化菌硫杆菌是大多数 ARGs 的潜在宿主。该研究为基于硫介导的生物过程处理低 C/N 比的 NOR 污染废水提供了新的见解。

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