Post Doctoral Research Station of Hydraulic Engineering of Three Gorges University, Hubei Field Observation and Scientific Research Stations for Water Ecosystem in Three Gorges Reservoir, China Three Gorges University, Yichang 443002, China; Hubei Key Laboratory of Wetland Evolution & Ecological Restoration, Wuhan Botanical Garden, Chinese Academy of Sciences, Wuhan 430074, China.
Post Doctoral Research Station of Hydraulic Engineering of Three Gorges University, Hubei Field Observation and Scientific Research Stations for Water Ecosystem in Three Gorges Reservoir, China Three Gorges University, Yichang 443002, China.
Water Res. 2024 Nov 1;265:122229. doi: 10.1016/j.watres.2024.122229. Epub 2024 Aug 8.
Nitrogen (N) pollution is a major threat to river ecosystems worldwide. Elucidating the community structure of N-cycling microorganisms in rivers is essential to understanding how ecosystem processes and functions will respond to increasing N inputs. However, previous studies generally focus on limited functional genes through amplicon sequencing or quantitative PCR techniques and cannot cover all N-cycling microorganisms. Here, metagenomic sequencing and genome binning were used to determine N-cycling genes in water, channel sediments, and riparian soils of the Yangtze River, which has been heavily polluted by N. Additionally, the denitrification and anaerobic ammonium oxidation (anammox) rates that reflect N removal potential were measured using N isotope pairing technique. Results showed that functional genes involved in organic N metabolism (i.e., organic degradation and synthesis) and nitrate reduction pathways (i.e., dissimilatory and assimilatory nitrate reduction to ammonium and denitrification) were more abundant and diverse than other N-cycling genes. A total of 121 metagenome-assembled genomes (MAGs) were identified to be involved in N-cycling processes, and the key MAGs were mainly taxonomically classified as Alphaproteobacteria and Gammaproteobacteria. The abundance and diversity of most N-cycling genes were higher in soils and sediments than in water, as well as higher in downstream and midstream than in upstream sites. These spatial variations were explained not only by local environment and vegetation but also by geographical and climatic factors. N removal process (i.e., denitrification and anammox) rates were significantly related to the abundance or diversity of several N-cycling genes, and climate and edaphic factors could regulate denitrification and anammox rates directly and indirectly through their effects on functional genes. Overall, these results provide a new avenue for further understanding the biogeographic patterns and environmental drivers of N-cycling microorganisms in rivers from the metagenomic perspective.
氮(N)污染是全球河流生态系统的主要威胁。阐明河流中 N 循环微生物的群落结构对于理解生态系统过程和功能将如何应对不断增加的 N 输入至关重要。然而,以前的研究通常侧重于通过扩增子测序或定量 PCR 技术研究有限的功能基因,而不能涵盖所有的 N 循环微生物。在这里,宏基因组测序和基因组 binning 用于确定长江受 N 严重污染的水体、河道沉积物和河岸土壤中的 N 循环基因,同时使用 N 同位素配对技术测量反映 N 去除潜力的反硝化和厌氧氨氧化(anammox)速率。结果表明,参与有机 N 代谢(即有机降解和合成)和硝酸盐还原途径(即异化和同化硝酸盐还原为铵和反硝化)的功能基因比其他 N 循环基因更丰富和多样。总共鉴定出 121 个参与 N 循环过程的宏基因组组装基因组(MAG),关键的 MAG 主要在分类学上归类为α变形菌和γ变形菌。大多数 N 循环基因的丰度和多样性在土壤和沉积物中高于水,在下游和中游高于上游。这些空间变化不仅由当地环境和植被解释,还由地理和气候因素解释。N 去除过程(即反硝化和 anammox)速率与几种 N 循环基因的丰度或多样性显著相关,气候和土壤因素可以通过直接和间接影响功能基因来调节反硝化和 anammox 速率。总体而言,这些结果从宏基因组的角度为进一步了解河流中 N 循环微生物的生物地理格局和环境驱动因素提供了新的途径。