Williamson Research Centre for Molecular Environmental Science and School of Earth, Atmospheric and Environmental Sciences, University of Manchester, Manchester, United Kingdom.
Appl Environ Microbiol. 2013 Jul;79(14):4325-35. doi: 10.1128/AEM.00683-13. Epub 2013 May 10.
Microcosms containing sediment from an aquifer in Cambodia with naturally elevated levels of arsenic in the associated groundwater were used to evaluate the effectiveness of microbially mediated production of iron minerals for in situ As remediation. The microcosms were first incubated without amendments for 28 days, and the release of As and other geogenic chemicals from the sediments into the aqueous phase was monitored. Nitrate or a mixture of sulfate and lactate was then added to stimulate biological Fe(II) oxidation or sulfate reduction, respectively. Without treatment, soluble As concentrations reached 3.9 ± 0.9 μM at the end of the 143-day experiment. However, in the nitrate- and sulfate-plus-lactate-amended microcosms, soluble As levels decreased to 0.01 and 0.41 ± 0.13 μM, respectively, by the end of the experiment. Analyses using a range of biogeochemical and mineralogical tools indicated that sorption onto freshly formed hydrous ferric oxide (HFO) and iron sulfide mineral phases are the likely mechanisms for As removal in the respective treatments. Incorporation of the experimental results into a one-dimensional transport-reaction model suggests that, under conditions representative of the Cambodian aquifer, the in situ precipitation of HFO would be effective in bringing groundwater into compliance with the World Health Organization (WHO) provisional guideline value for As (10 ppb or 0.13 μM), although soluble Mn release accompanying microbial Fe(II) oxidation presents a potential health concern. In contrast, production of biogenic iron sulfide minerals would not remediate the groundwater As concentration below the recommended WHO limit.
含有柬埔寨含水层沉积物的微宇宙,其相关地下水中砷含量自然升高,用于评估微生物介导的铁矿物生产对原位砷修复的有效性。首先将微宇宙在没有添加物的情况下孵育 28 天,并监测沉积物中砷和其他地球化学物质向水相的释放情况。然后分别添加硝酸盐或硫酸盐和乳酸盐混合物以刺激生物 Fe(II)氧化或硫酸盐还原。未经处理,可溶性 As 浓度在 143 天实验结束时达到 3.9 ± 0.9 μM。然而,在添加硝酸盐和硫酸盐加乳酸盐的微宇宙中,可溶性 As 水平分别降至 0.01 和 0.41 ± 0.13 μM。使用一系列生物地球化学和矿物学工具的分析表明,吸附到新形成的水合氧化铁(HFO)和铁硫化物矿物相上是去除各自处理中 As 的可能机制。将实验结果纳入一维运移反应模型表明,在柬埔寨含水层的代表性条件下,HFO 的原位沉淀将有效使地下水符合世界卫生组织(WHO)暂定的砷指导值(10 ppb 或 0.13 μM),尽管微生物 Fe(II)氧化伴随的可溶性 Mn 释放带来了潜在的健康风险。相比之下,生物铁硫化物矿物的产生不会将地下水的砷浓度降低到建议的 WHO 限值以下。