Key Laboratory of Drinking Water Science and Technology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing, China.
Key Laboratory of Drinking Water Science and Technology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing, China.
Water Res. 2020 Apr 15;173:115539. doi: 10.1016/j.watres.2020.115539. Epub 2020 Jan 30.
Dissimilatory nitrate reduction to ammonium (DNRA), an important intermediate process in the N-cycle, links N-compound oxidation and reduction processes. Hence, the oxic-anoxic interface would be the hotspot of the DNRA process. In freshwater ecosystems, the riparian zone is the most typical carrier of the oxic-anoxic interface. Here we report spatio-temporal evidence of a higher abundance and rate of DNRA in the riparian zone than in the open water sediments based on molecular and N isotopic-tracing technologies, hence signifying a hotspot for the DNRA process. These abudance and rates were significantly higher than those in open water sediments. N isotopic paring technology revealed that the DNRA hotspot promoted higher rates of N-compound oxidation (NO), reduction (NO and DNRA), and N production (anammox and denitrification) in the riparian zone than those in open water sediment. However, high-through sequencing analysis showed that the DNRA bacteria in the riparian zone and openwater sediments were insignificantly different. Network and correlation analysis showed that the DNRA abundance and rates were significantly positively correlated with TOM, TC/NH, and TC/NO, but not with the dominant genera (Anaeromyxobacter, Lacunisphaera, and Sorangium), which played different roles on the connection in the respective community networks. The DNRA process in the riparian zone could be driven mainly by the related environmental biogeochemical characteristics induced by anthropogenic changes, followed by microbial processes. This result provides valuable information for the management of riparian zones because anthropogenic changes in the riparian water table are expected to increase, inducing consequent changes in the reduction from NO to NH.
异化硝酸盐还原为铵(DNRA)是氮循环中的一个重要中间过程,将氮化合物的氧化和还原过程联系起来。因此,好氧-缺氧界面将是 DNRA 过程的热点。在淡水生态系统中,河岸带是好氧-缺氧界面最典型的载体。本研究基于分子和氮同位素示踪技术,报道了河岸带中 DNRA 丰度和速率高于开阔水域沉积物的时空证据,表明该区域是 DNRA 过程的热点。这些丰度和速率明显高于开阔水域沉积物。氮同位素配对技术表明,DNRA 热点促进了河岸带中氮化合物的氧化(NO)、还原(NO 和 DNRA)和氮的产生(厌氧氨氧化和反硝化)速率高于开阔水域沉积物。然而,高通量测序分析表明,河岸带和开阔水域沉积物中的 DNRA 细菌没有显著差异。网络和相关性分析表明,DNRA 的丰度和速率与 TOM、TC/NH 和 TC/NO 呈显著正相关,但与优势属(Anaeromyxobacter、Lacunisphaera 和 Sorangium)无关,它们在各自的群落网络连接中发挥着不同的作用。河岸带的 DNRA 过程可能主要由人为变化引起的相关环境生物地球化学特征驱动,其次是微生物过程。该结果为河岸带的管理提供了有价值的信息,因为预计河岸带地下水位的人为变化会增加,从而导致从 NO 到 NH 的还原发生相应变化。