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氮、硫、铁和微生物群落共同塑造了与河流相关的沿海潮滩湿地中砷和锑的季节性生物地球化学行为。

Nitrogen, sulfur, iron, and microbial communities co-shape the seasonal biogeochemical behaviors of As and Sb in coastal tidal flat wetlands associated with rivers.

作者信息

Kong Shen, Luo Ting, Xue Lili, Zou Yang, Dai Shijing, He Dongmei

机构信息

School of Environmental Science and Engineering, Yancheng Institute of Technology, Yancheng 224051, China; Jiangsu Province Ecology and Environment Protection Key Laboratory of Ecology and Pollution Control of Coastal Wetlands, Yancheng 224051, China.

School of Environmental Science and Engineering, Yancheng Institute of Technology, Yancheng 224051, China; Jiangsu Province Ecology and Environment Protection Key Laboratory of Ecology and Pollution Control of Coastal Wetlands, Yancheng 224051, China.

出版信息

J Hazard Mater. 2025 Feb 15;484:136730. doi: 10.1016/j.jhazmat.2024.136730. Epub 2024 Dec 1.

Abstract

Arsenic (As) and antimony (Sb) are affected by complex biogeochemical processes in coastal ecosystems. However, the influence of N, S, Fe, and microbial communities on the biogeochemistry of As and Sb in coastal tidal flat wetlands remain uncertain, particularly when rivers flow into these areas. This study combined diffusive gradients in the thin-film technique with high-throughput sequencing to investigate the release and vertical distribution of As and Sb in river and coastal tidal flat wetland sediments. The results indicated a distinct stratification phenomenon in the As release at depths ranging from 20 mm to -150 mm. At river sites, the release of As occurred in the upper layer (above -40 mm), with peak values of 4.3 and 9.3 μg/L at HS and SY sites in summer, respectively, likely due to anaerobic ammonium oxidation. In the lower layer (below -40 mm), both As and Sb were released, and this was possibly due to Fe reduction. However, at the coastal tidal flat sites, the release of As and Sb may have been driven by anaerobic ammonium oxidation, dissimilatory nitrate reduction to ammonium, sulfate reduction, and Fe reduction. At the river sites, As exhibited increased activity during the summer, and the residual forms were converted more easily into mobile forms. Sb remained relatively stable during both winter and summer. Conversely, both As and Sb primarily existed in residual forms and exhibited higher stability during summer in the coastal tidal flat sites. The microbial phyla Nitrospirota (3.6-7.0 %) and Acidobacteriota (9.5-10.2 %) were more prevalent at the river sites, whereas Desulfobacterota (8.8-12.0 %) and Firmicutes (0.13-27.9 %) were more prevalent at the coastal tidal flat sites. The bacterial genera involved in the N, S, and Fe transformation processes differed between the two sites, and they were primarily Thiobacillus, Limnobacter, and Sulfurovum at the river sites and Sva1033, Anaeromyxobacter, and Sva0485 at the coastal tidal flat sites. In this study, the microorganisms that mediated N, S, and Fe complex processes at various depths in the sediment-water interface were decoupled to elucidate the effect of these processes on the biogeochemical behavior of As and Sb as they move from rivers to coastal tidal flat wetlands.

摘要

砷(As)和锑(Sb)受沿海生态系统中复杂生物地球化学过程的影响。然而,氮、硫、铁和微生物群落对沿海潮滩湿地中砷和锑生物地球化学的影响仍不确定,尤其是当河流流入这些区域时。本研究将薄膜扩散梯度技术与高通量测序相结合,以研究河流和沿海潮滩湿地沉积物中砷和锑的释放及垂直分布。结果表明,在20毫米至-150毫米深度范围内,砷的释放存在明显的分层现象。在河流站点,砷的释放在上层(-40毫米以上)发生,夏季HS和SY站点的峰值分别为4.3和9.3微克/升,这可能是由于厌氧氨氧化作用。在下层(-40毫米以下),砷和锑均有释放,这可能是由于铁还原作用。然而,在沿海潮滩站点,砷和锑的释放可能是由厌氧氨氧化、异化硝酸盐还原为铵、硫酸盐还原和铁还原驱动的。在河流站点,夏季砷的活性增加,其残留形态更容易转化为可移动形态。冬季和夏季锑均相对稳定。相反,在沿海潮滩站点,砷和锑主要以残留形态存在,夏季表现出更高的稳定性。在河流站点,硝化螺旋菌门(3.6-7.0%)和酸杆菌门(9.5-10.2%)更为普遍,而在沿海潮滩站点,脱硫杆菌门(8.8-12.0%)和厚壁菌门(0.13-27.9%)更为普遍。参与氮、硫和铁转化过程的细菌属在两个站点之间有所不同,河流站点主要是硫杆菌属、湖杆菌属和硫卵菌属,沿海潮滩站点主要是Sva1033、厌氧粘细菌属和Sva0485。在本研究中,沉积物-水界面不同深度介导氮、硫和铁复杂过程的微生物被解耦,以阐明这些过程对砷和锑从河流向沿海潮滩湿地迁移过程中生物地球化学行为的影响。

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