ISSN 1000-3665 CN 11-2202/P
    刘菲,黄福杨. 地下水系统中的抗生素对反硝化的影响研究进展[J]. 水文地质工程地质,2024,51(2): 3-12. DOI: 10.16030/j.cnki.issn.1000-3665.202312009
    引用本文: 刘菲,黄福杨. 地下水系统中的抗生素对反硝化的影响研究进展[J]. 水文地质工程地质,2024,51(2): 3-12. DOI: 10.16030/j.cnki.issn.1000-3665.202312009
    LIU Fei, HUANG Fuyang. Research progress on the impact of antibiotics in groundwater systems on denitrification[J]. Hydrogeology & Engineering Geology, 2024, 51(2): 3-12. DOI: 10.16030/j.cnki.issn.1000-3665.202312009
    Citation: LIU Fei, HUANG Fuyang. Research progress on the impact of antibiotics in groundwater systems on denitrification[J]. Hydrogeology & Engineering Geology, 2024, 51(2): 3-12. DOI: 10.16030/j.cnki.issn.1000-3665.202312009

    地下水系统中的抗生素对反硝化的影响研究进展

    Research progress on the impact of antibiotics in groundwater systems on denitrification

    • 摘要: 微生物反硝化过程是地下水中硝酸盐最重要的脱氮形式。再生水利用和养殖业引起的抗生素污染常与硝酸盐共存。因此,需深入研究抗生素及其存在形式对地下水中硝酸盐反硝化过程及抗生素抗性基因(ARGs)产生、富集和传播的影响,以综合解析地下水硝酸盐浓度升高的原因。近年来的研究识别了地下水系统中抗生素的解离/络合形态、吸附形式(层间吸附/表面吸附)、水解与微生物降解产物等存在形式,并从反硝化微生物群落、功能酶的种类与活性、功能基因丰度以及ARGs产生与传播途径阐释了抗生素对反硝化过程的抑制机制。主要结论为:(1)地下水系统中,抗生素以多种形式存在,而不同形式的抗生素对微生物的毒性有显著差异;(2)在每升纳克至微克水平的抗生素存在下,地下水反硝化过程受到抑制,抗生素改变了微生物群落结构,抑制了功能酶活性,增加了ARGs的丰度,在这些作用的协同影响下,硝酸盐降解动力学由零级向一级转变;(3)在抗生素抑制反硝化过程中,还增加了温室气体N2O的释放量,抗生素影响了功能基因nosZ表达,N2O浓度与nosZ丰度呈负指数关系。在综述相关文献的基础上,对未来研究提出了展望:(1)定量识别典型抗生素进入地下水系统后的存在形式;(2)厘清不同存在形式的抗生素对反硝化微生物群落、功能酶种类与活性、功能基因丰度和多样性的影响;(3)探索反硝化功能基因在抗生素不同存在形式和不同输入方式下的变化过程,并建立ARGs产生、富集与传播模式;(4)结合野外观测和室内实验从分子生物学、环境化学和水文地质学多尺度研究复合污染下地下水系统的反硝化过程,可为日益复杂的地下水污染防治和饮用水安全保障提供理论依据。

       

      Abstract: The microbial denitrification process is the most important form of nitrate-nitrogen removal in groundwater. The reclaimed water reuse and livestock breeding caused antibiotic pollution usually co-occurs with nitrate. Therefore, it is necessary to conduct in-depth research on the effects of denitrification and the generation, accumulation, and dissemination of antibiotic resistance genes (ARGs) by antibiotics and their forms to comprehensively analyze the reasons for the increased concentration of nitrate in groundwater. Many studies in recent years have identified the dissociation/complexation, adsorption forms (interlayer adsorption/surface adsorption), and the products of hydrolysis and microbial degradation of antibiotics in groundwater systems; and have elucidated the inhibitory mechanism of antibiotics on the denitrification process from the perspectives of denitrifying microbial communities, the types and activities of functional enzymes, abundance of functional genes, as well as the production and transmission pathways of ARGs. The main conclusions are as follows: (1) In groundwater systems, antibiotics exist in various forms, and different forms of antibiotics exhibit significant differences in toxicity to microorganisms. (2) In the presence of antibiotics at levels ranging from nanograms to micrograms per liter, the denitrification process in groundwater is inhibited. Antibiotics alter the microbial community structure, suppress enzymatic activity, and increase the abundance of ARGs. Under the synergistic effects of these actions, the kinetics of nitrate degradation shift from zero-order to first-order. (3) During the antibiotic-induced inhibition of denitrification, there is also an increase in the emission of the greenhouse gas N2O. Antibiotics primarily affect the expression of the functional gene nosZ, and the concentration of N2O shows a negative exponential relationship with nosZ abundance. Based on the review of relevant literature, the prospects for future research are put forward: (1) quantitatively identifying the existence forms of typical antibiotics after entering groundwater systems; (2) elucidating the impact of antibiotics in different existence forms on denitrifying microbial communities, the types and activities of functional enzymes, and the abundance and diversity of functional genes; (3) exploring the dynamic process of denitrification functional genes under different existence forms and input modes of antibiotics, and establishing models for the production, enrichment, and transmission of ARGs; (4) combining field observations and laboratory experiments to study the denitrification process in groundwater systems under complex pollution from molecular biology, environmental chemistry, and hydrogeology perspectives. This research can provide a theoretical basis for addressing the increasingly complex groundwater pollution prevention and drinking water safety assurance.

       

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