Yin Guoyu, Hou Lijun, Liu Min, Zheng Yanling, Li Xiaofei, Lin Xianbiao, Gao Juan, Jiang Xiaofen, Wang Rong, Yu Chendi
Key Laboratory of Geographic Information Science (Ministry of Education), East China Normal University, Shanghai, 200241, China; School of Geographic Sciences, East China Normal University, Shanghai, 200241, China.
State Key Laboratory of Estuarine and Coastal Research, East China Normal University, Shanghai, 200062, China.
Chemosphere. 2017 Mar;171:118-125. doi: 10.1016/j.chemosphere.2016.12.068. Epub 2016 Dec 18.
Denitrification is a dominant reactive nitrogen removal pathway in most estuarine and coastal ecosystems, and plays a significant role in regulating NO release. Although multiple antibiotics residues are widely detected in aquatic environment, combined effects of antibiotics on denitrification remain indistinct. In this work, 5 classes of antibiotics (sulfonamides, chloramphenicols, tetracyclines, macrolides, and fluoroquinolones) were selected to conduct orthogonal experiments in order to explore their combined effects on denitrification. N-based denitrification and NO release rates were determined in the orthogonal experiments, while denitrifying functional genes were examined to illustrate the microbial mechanism of the combined antibiotics effect. Denitrification rates were inhibited by antibiotics treatments, and synergistic inhibition effect was observed for multiple antibiotics exposure. Different classes of antibiotics had different influence on NO release rates, but multiple antibiotics exposure mostly led to stimulatory effect. Abundances of denitrifying functional genes were inhibited by multiple antibiotics exposure due to the antimicrobial properties, and different inhibition on denitrifiers may be the major mechanism for the variations of NO release rates. Combined effects of antibiotics on denitrification may lead to nitrate retention and NO release in estuarine and coastal ecosystems, and consequently cause cascading environmental problems, such as greenhouse effects and hyper-eutrophication.
反硝化作用是大多数河口和沿海生态系统中主要的活性氮去除途径,在调节一氧化氮(NO)释放方面发挥着重要作用。尽管在水生环境中广泛检测到多种抗生素残留,但抗生素对反硝化作用的联合影响仍不明确。在这项工作中,选择了5类抗生素(磺胺类、氯霉素类、四环素类、大环内酯类和氟喹诺酮类)进行正交试验,以探讨它们对反硝化作用的联合影响。在正交试验中测定了基于氮的反硝化作用和NO释放速率,同时检测了反硝化功能基因以阐明抗生素联合作用的微生物机制。抗生素处理抑制了反硝化速率,并且观察到多种抗生素暴露具有协同抑制作用。不同类别的抗生素对NO释放速率有不同影响,但多种抗生素暴露大多导致刺激作用。由于抗菌特性,多种抗生素暴露抑制了反硝化功能基因的丰度,对反硝化菌的不同抑制作用可能是NO释放速率变化的主要机制。抗生素对反硝化作用的联合影响可能导致河口和沿海生态系统中的硝酸盐滞留和NO释放,进而引发一系列环境问题,如温室效应和富营养化加剧。