Soil Chemistry Group, Institute of Biogeochemistry and Pollutant Dynamics, Department of Environmental Systems Science, CHN, ETH Zurich , 8092 Zurich, Switzerland.
Section for Environmental Chemistry and Physics, Department of Plant and Environmental Sciences, University of Copenhagen , DK-1871 Frederiksberg C, Denmark.
Environ Sci Technol. 2016 Sep 6;50(17):9251-61. doi: 10.1021/acs.est.6b01767. Epub 2016 Aug 10.
Reductive release of the potentially toxic metalloid As from Fe(III) (oxyhydr)oxides has been identified as an important process leading to elevated As porewater concentrations in soils and sediments. Despite the ubiquitous presence of Mn oxides in soils and their oxidizing power toward As(III), their impact on interrelated As, Fe, and Mn speciation under microbially reducing conditions remains largely unknown. For this reason, we employed a column setup and X-ray absorption spectroscopy to investigate the influence of increasing birnessite concentrations (molar soil Fe-to-Mn ratios: 4.8, 10.2, and 24.7) on As speciation and release from an As-contaminated floodplain soil (214 mg As/kg) under anoxic conditions. Our results show that birnessite additions significantly decreased As leaching. The reduction of both As and Fe was delayed, and As(III) accumulated in birnessite-rich column parts, indicating the passivation of birnessite and its transformation products toward As(III) oxidation and the precipitation of Fe(III)(oxyhydr)oxides. Microbial Mn reduction resulted in elevated soil pH values, which in turn lowered the microbial activity in the birnessite-enriched soil. We conclude that in Mn-oxide-rich soil environments undergoing redox fluctuations, the enhanced As adsorption to newly formed Fe(III) (oxyhydr)oxides under reducing conditions leads to a transient stabilization of As.
从 Fe(III)(氧氢)氧化物中还原释放出潜在有毒的类金属砷已被确定为导致土壤和沉积物中砷孔隙水浓度升高的重要过程。尽管锰氧化物在土壤中普遍存在,并且对 As(III) 具有氧化能力,但在微生物还原条件下,它们对相互关联的 As、Fe 和 Mn 形态的影响在很大程度上仍不清楚。出于这个原因,我们采用了柱装置和 X 射线吸收光谱法来研究增加锰矿浓度(土壤中 Fe 与 Mn 的摩尔比:4.8、10.2 和 24.7)对缺氧条件下受砷污染的冲积平原土壤(214mg As/kg)中砷形态和释放的影响。我们的结果表明,锰矿的添加显著降低了砷的浸出。砷和铁的还原都被延迟,并且 As(III) 在富含锰矿的柱部分积累,这表明锰矿及其转化产物对 As(III)氧化的钝化和 Fe(III)(氧氢)氧化物的沉淀。微生物 Mn 的还原导致土壤 pH 值升高,进而降低了富含锰矿土壤中的微生物活性。我们得出结论,在经历氧化还原波动的富含 Mn 氧化物的土壤环境中,还原条件下新形成的 Fe(III)(氧氢)氧化物对砷的吸附增强导致砷的短暂稳定。