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Effects of elevated sulfate concentration on the mobility of arsenic in the sediment-water interface

机译:硫酸盐浓度升高对沉积物-水界面中砷迁移率的影响

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摘要

The adsorption/desorption of arsenic (As) at the sediment-water interface in lakes is the key to understanding whether As can enter the ecosystem and participate in material circulation. In this study, the concentrations of As(III), total arsenic [As(T)], sulfide, iron (Fe), and dissolved organic carbon (DOC) in overlying water were observed after the initial sulfate (SO42-) concentrations were increased by four gradients in the presence and absence of microbial systems. The results indicate that increased SO42- concentrations in overlying water triggered As desorption from sediments. Approximately 10% of the desorbed As was desorbed directly as arsenite or arsenate by competitive adsorption sites on the iron salt surface; 21% was due to the reduction of iron (hydr)oxides; and 69% was due to microbial activity, as compared with a system with no microbial activity. The intensity of microbial activity was controlled by the SO42- and DOC concentrations in the overlying water. In anaerobic systems, which had SO42- and DOC concentrations higher than 47 and 7 mg/L, respectively, microbial activity was promoted by SO42- and DOC; As(III) was desorbed under these indoor simulation conditions. When either the SO42- or DOC concentration was lower than its respective threshold of 47 or 7 mg/L, or when either of these indices was below its concentration limit, it was difficult for microorganisms to use SO42- and DOC to enhance their own activities. Therefore, conditions were insufficient for As desorption. The migration of As in lake sediments was dominated by microbial activity, which was co-limited by SO42- and DOC. The concentrations of SO42- and DOC in the overlying water are thus important for the prevention and control of As pollution in lakes. We recommend controlling SO42- and DOC concentrations as a method for controlling As inner-source pollution in lake water.
机译:湖泊沉积物-水界面处砷的吸附/解吸是了解砷能否进入生态系统并参与物质循环的关键。在这项研究中,在初始硫酸盐(SO42-)浓度为10%后,观察了上覆水中的As(III),总砷[As(T)],硫化物,铁(Fe)和溶解的有机碳(DOC)的浓度。在存在和不存在微生物系统的情况下,通过四个梯度增加。结果表明,上覆水中SO42-浓度的增加触发了As从沉积物中的解吸。大约10%的被解吸的As通过铁盐表面上的竞争性吸附位点被直接解吸为亚砷酸盐或砷酸盐。 21%是由于氧化铁(氢氧根)的减少;与没有微生物活性的系统相比,有69%是由于微生物活性。微生物活性强度由上层水中的SO42和DOC浓度控制。在SO42和DOC浓度分别高于47和7 mg / L的厌氧系统中,SO42和DOC促进了微生物活性。在这些室内模拟条件下,As(III)被解吸。当SO42-或DOC的浓度低于其各自的阈值47或7 mg / L时,或者当这些指数中的任何一个低于其浓度极限时,微生物都很难使用SO42-和DOC来增强自身的活性。因此,条件不足以进行As的解吸。砷在湖泊沉积物中的迁移以微生物活动为主导,而微生物活动受SO42和DOC共同限制。因此,上层水中SO42和DOC的浓度对于预防和控制湖泊中的As污染非常重要。我们建议控制SO42和DOC的浓度,作为控制湖水中As内源污染的一种方法。

著录项

  • 来源
    《Ecotoxicology and Environmental Safety》 |2018年第6期|311-320|共10页
  • 作者单位

    Yunnan Univ, Sch Ecol & Environm Sci, Kunming 650091, Yunnan, Peoples R China;

    Yunnan Univ, Sch Ecol & Environm Sci, Kunming 650091, Yunnan, Peoples R China;

    Yunnan Univ, Yunnan Key Lab Plateau Mt Ecol & Restorat Degrade, Kunming 650091, Yunnan, Peoples R China;

    Yunnan Univ, Yunnan Key Lab Plateau Mt Ecol & Restorat Degrade, Kunming 650091, Yunnan, Peoples R China;

    Yunnan Univ, Sch Ecol & Environm Sci, Kunming 650091, Yunnan, Peoples R China;

    Yunnan Univ, Inst Int Rivers & Ecosecur, Kunming 650091, Yunnan, Peoples R China;

    Yunnan Univ, Inst Int Rivers & Ecosecur, Kunming 650091, Yunnan, Peoples R China;

    Yunnan Univ, Inst Int Rivers & Ecosecur, Kunming 650091, Yunnan, Peoples R China;

    Yunnan Univ, Inst Int Rivers & Ecosecur, Kunming 650091, Yunnan, Peoples R China;

  • 收录信息 美国《科学引文索引》(SCI);美国《生物学医学文摘》(MEDLINE);美国《化学文摘》(CA);
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    Arsenic contamination; Lake sediment; Sediment-water interface; Water pollution;

    机译:砷污染;湖泊沉积物;沉积物-水界面;水污染;
  • 入库时间 2022-08-17 13:22:39

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