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首页> 外文期刊>Environmental Science: Processes & Impacts >Cr(VI) uptake and reduction by biogenic iron (oxyhydr)oxides
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Cr(VI) uptake and reduction by biogenic iron (oxyhydr)oxides

机译:Br(vi)通过生物铁(氧水)氧化物的吸收和减少

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The mobility and toxicity of chromium (Cr) in soil and water systems are largely controlled by its oxidation state and interactions with solid phases. Relative to abiotic minerals, biogenic iron (Fe) (oxyhydr)oxides (BIOS) may enhance Cr(vi) adsorption and reduction due to their poorly ordered structures, large surface areas, and incorporation of cell derived organic matter. To determine the extent and mechanisms of the reaction between Cr(vi) and BIOS, sorption isotherm and kinetic studies were conducted using two-line ferrihydrite, BIOS, and BIOS amended with 0.135 M ferrozine (an Fe(ii) chelator). X-ray absorption near edge structure (XANES) spectroscopy of BIOS reacted with Cr(vi) showed approximately 50% reduction of the total sorbed Cr from Cr(vi) to Cr(iii) after 14 days of exposure. Sorbed Cr(iii) was best fit with an organic carboxylate complex after 1 d of reaction, but after 7 d mineral-associated Cr(iii) was the predominant form. In the presence of ferrozine, Cr(vi) reduction by BIOS was inhibited, confirming a key role for Fe(ii) as the Cr(vi) reductant. However, the lack of a 3:1 reaction stoichiometry between Fe(ii) and Cr(iii) produced suggests roles for reaction with organic matter and Cr(v) autoreduction in Cr(iii) production. This study thus elucidates an unrecognized mechanism of Cr sequestration by ubiquitous natural Fe (oxyhydr)oxide deposits. Furthermore, the redox transformation of mobile Cr(vi) to less soluble Cr(iii) species observed in our study implies that biogenic Fe (oxyhydr)oxides in soils and natural waters may naturally attenuate Cr(vi) concentrations through sorption and reduction processes, thus limiting its transport to downstream environments.
机译:土壤和水系统中铬(Cr)的迁移率和毒性主要由其氧化状态和与固相的相互作用控制。相对于非生物矿物质,生物铸铁(Fe)(氧水)氧化物(BIOS)可以增强Cr(VI)吸附和减少由于其有序的结构,大表面积,细胞衍生的有机物质的掺入。为了确定Cr(VI)和BIOS之间的反应的程度和机制,使用双线Ferrihydrite,BIOS和BIOS进行用0.135M铁嗪(Fe(II)螯合剂)进行吸附等温线和动力学研究。与Cr(VI)反应的BIOS的边缘结构附近的X射线吸收(XANES)光谱显示在接触14天后,在CR(VI)至Cr(III)中的总吸附Cr减少约50%。在1 d反应后的有机羧酸酯复合物最合适,但在7d矿物相关的Cr(III)之后是主要的形式。在铁嗪的存在下,抑制BIOS的Cr(VI)减少,证实Fe(II)作为Cr(VI)还原剂的关键作用。然而,在Fe(II)和Cr(III)之间缺乏3:1反应化学计量表明在Cr(III)生产中的有机物质和Cr(v)自动化的作用表明作用。因此,该研究阐明了普遍存在的天然Fe(Oxyhydr)氧化物沉积物的Cr封存的未识别机制。此外,在我们的研究中观察到的移动Cr(VI)的氧化还原转化较低的可溶性Cr(III)物种意味着土壤和天然水中的生物氧化氢(氧水)氧化物可以通过吸附和还原过程自然衰减Cr(VI)浓度,因此将其运输到下游环境限制。

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