Ye Fei, Duan Lei, Sun Yaqiao, Yang Fan, Liu Rui, Gao Fan, Wang Yike, Xu Yirong
School of Water and Environment, Chang'an University, Xi'an, China.
Key Laboratory of Subsurface Hydrology and Ecological Effects in Arid Region, Ministry of Education, Chang'an University, Xi'an, China.
Front Microbiol. 2023 Aug 17;14:1239055. doi: 10.3389/fmicb.2023.1239055. eCollection 2023.
The riparian zone is an important location of nitrogen removal in the terrestrial and aquatic ecosystems. Many studies have focused on the nitrogen removal efficiency and one or two nitrogen removal processes in the riparian zone, and less attention has been paid to the interaction of different nitrogen transformation processes and the impact of environmental conditions. The molecular biotechnology, microcosm culture experiments and N stable isotope tracing techniques were used in this research at the riparian zone in Weinan section of the Wei River, to reveal the nitrogen removal mechanism of riparian zone with multi-layer lithologic structure. The results showed that the nitrogen removal rate in the riparian zone was 4.14-35.19 μmol·N·kg·h. Denitrification, dissimilatory reduction to ammonium (DNRA) and anaerobic ammonium oxidation (anammox) jointly achieved the natural attenuation process of nitrogen in the riparian zone, and denitrification was the dominant process (accounting for 59.6%). High dissolved organic nitrogen and nitrate ratio (DOC:NO) would promote denitrification, but when the NO content was less than 0.06 mg/kg, DNRA would occur in preference to denitrification. Furthermore, the abundances of functional genes () and anammox bacterial 16S rRNA gene showed similar distribution patterns with the corresponding nitrogen transformation rates. Sedimentary NO, Fe(II), dissolved organic carbon (DOC) and the nitrogen transformation functional microbial abundance were the main factors affecting nitrogen removal in the riparian zone. Fe (II) promoted NO attenuation through nitrate dependent ferrous oxidation process under microbial mediation, and DOC promotes NO attenuation through enhancing DNRA effect. The results of this study can be used for the management of the riparian zone and the prevention and control of global nitrogen pollution.
河岸带是陆地和水生生态系统中氮去除的重要场所。许多研究聚焦于河岸带的氮去除效率以及一两种氮去除过程,而对不同氮转化过程的相互作用和环境条件的影响关注较少。本研究在渭河渭南段河岸带运用分子生物技术、微观培养实验和氮稳定同位素示踪技术,以揭示具有多层岩性结构的河岸带的氮去除机制。结果表明,河岸带的氮去除率为4.14 - 35.19 μmol·N·kg·h。反硝化作用、异化还原为铵(DNRA)和厌氧氨氧化(anammox)共同实现了河岸带氮的自然衰减过程,且反硝化作用是主导过程(占59.6%)。高溶解有机氮与硝酸盐比率(DOC:NO)会促进反硝化作用,但当NO含量低于0.06 mg/kg时,DNRA会优先于反硝化作用发生。此外,功能基因()和厌氧氨氧化细菌16S rRNA基因的丰度与相应的氮转化速率呈现相似的分布模式。沉积物中的NO、Fe(II)、溶解有机碳(DOC)和氮转化功能微生物丰度是影响河岸带氮去除的主要因素。Fe(II)在微生物介导下通过硝酸盐依赖的亚铁氧化过程促进NO衰减,DOC则通过增强DNRA效应促进NO衰减。本研究结果可用于河岸带的管理以及全球氮污染的防治。