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首页> 外文期刊>Applied Geochemistry: Journal of the International Association of Geochemistry and Cosmochemistry >Characterization of Fe(III) (hydr)oxides in arsenic contaminated soil under various redox conditions by XAFS and Mossbauer spectroscopies
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Characterization of Fe(III) (hydr)oxides in arsenic contaminated soil under various redox conditions by XAFS and Mossbauer spectroscopies

机译:XAFS和Mossbauer光谱法在各种氧化还原条件下表征砷污染土壤中的Fe(III)(OH)氧化物

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Characterization of Fe(III) (hydr)oxides in soils near the Ichinokawa mine was conducted using X-ray absorption fine structure (XAFS) and Mossbauer spectroscopies, and the structural changes were correlated with the release of As into pore-water. The Eh values decreased monotonically with depth. Iron is mainly present as poorly-ordered Fe(III) (hydr)oxides, such as ferrihydrite, over a wide redox range (from Eh = 360 to -140 mV). Structural details of the short-range order of these Fe(III) (hydr)oxides were examined using Mossbauer spectroscopy by comparing the soil phases with synthesized ferrihydrite samples having varying crystallinities. The crystallinity of the soil Fe (hydr)oxides decreased slightly with depth and Eh. Thus, within the redox range of this soil profile, ferrihydrite dominated, even under very reducing conditions, but the crystalline domain size, and, potentially, particle size, changed with the variation in Eh. In the soil-water system examined here, where As concentration and the As(III)/As(V) ratio in soil water increased with depth, ferrihydrite persisted and maintained or even enhanced its capacity for As retention with increased reducing conditions. Therefore, it is concluded that As release from these soils largely depends on the transformation of As(V) to As(III) rather than reductive dissolution of Fe(Ill) (hydr)oxide. (C) 2008 Published by Elsevier Ltd.
机译:使用X射线吸收精细结构(XAFS)和Mossbauer光谱仪对一之川矿区附近土壤中的Fe(III)(氢氧化)氧化物进行了表征,其结构变化与As释放到孔隙水中有关。 Eh值随深度单调降低。铁主要在较宽的氧化还原范围内(从Eh = 360到-140 mV)以无序的Fe(III)(氢氧化)氧化物(如亚铁酸盐)形式存在。这些Fe(III)(氢氧化)氧化物的短程有序结构细节通过Mossbauer光谱法进行了研究,方法是将土壤相与具有不同结晶度的合成三水铁矿样品进行比较。土壤Fe(氢)氧化物的结晶度随深度和Eh略有降低。因此,即使在非常还原的条件下,在该土壤剖面的氧化还原范围内,亚铁水合物仍占主导地位,但随着Eh的变化,晶畴尺寸以及潜在的颗粒尺寸也会发生变化。在这里研究的土壤-水系统中,土壤水中的As浓度和As(III)/ As(V)之比随深度增加而增加,水铁矿持续存在并保持,甚至随着还原条件的增加,其保留As的能力甚至增强。因此,可以得出结论,砷从这些土壤中的释放在很大程度上取决于As(V)向As(III)的转化,而不是还原性的Fe(III)(氢氧化)氧化物的溶解。 (C)2008由Elsevier Ltd.发布

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