首页> 外文期刊>Journal of Hazardous Materials >Dual diffusive gradients in the thin films (DGT) probes provide insights into speciation and mobility of sediment chromium (Cr) from the Xizhi River basin, South China
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Dual diffusive gradients in the thin films (DGT) probes provide insights into speciation and mobility of sediment chromium (Cr) from the Xizhi River basin, South China

机译:薄膜中的双扩散梯度 (DGT) 探针提供了对华南汐止河流域沉积物铬 (Cr) 的形态和迁移的见解

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摘要

Investigation of the speciation and remobilization mechanisms of chromium (Cr) in sediment is essential for accurate estimation of its ecological risks in aquatic systems. In this work, a three-step chemical extraction procedure and diffusive gradient in thin films (DGT) technique were combined to investigate the geochemical speciation, mobility potentials, and release characteristics of sediment Cr. The geochemical speciation of sediment Cr decreased in the following order: oxidizable > reducible > residual > acid-soluble fraction. Dissociation of OM-bound Cr(III) and oxidation by Mn oxides contributed to higher labile Cr(III) and Cr(VI) levels in winter, with the labile Cr(III) being the dominant species and accounting for 48.1-65.5 of the total concentration of labile Cr; whereas, reductive dissolution of Mn oxides was responsible for the remobilization of labile Cr(VI) in summer, leading to a shift in dominant Cr species to Cr(VI) (48.9-65.7) due to rapid precipitation of Cr(III). Sediment acted as a major sink for labile Cr(VI) in two sampling campaigns. For labile Cr(III), sediment converted from source in winter to sink in summer. The diffusive release of labile Cr(III) deserves preferential concern due to its potential to be re-oxidized to more toxic Cr(VI) under the oxic conditions of river water in winter.
机译:研究沉积物中铬(Cr)的形态和再动员机制对于准确评估其在水生系统中的生态风险至关重要。本工作采用三步化学提取法和薄膜扩散梯度(DGT)技术相结合,研究了沉积物Cr的地球化学形态、迁移势和释放特征。沉积物Cr的地球化学形态按以下顺序降低:可氧化>可还原>残留>酸溶性部分。OM结合的Cr(III)解离和Mn氧化物的氧化导致冬季Cr(III)和Cr(VI)水平升高,其中不稳定的Cr(III)为优势物种,占不稳定Cr总浓度的48.1%-65.5%;而Mn氧化物的还原溶解是夏季不稳定Cr(VI)再动员的原因,由于Cr(III)的快速沉淀,导致优势Cr物种向Cr(VI)转变(48.9%-65.7%)。沉积物在两次采样活动中充当了不稳定的Cr(VI)的主要汇。对于不稳定的Cr(III),沉积物在冬季从源头转化为夏季的汇。不稳定的Cr(III)的扩散释放值得关注,因为它有可能在冬季河水的含氧条件下被重新氧化成毒性更大的Cr(VI)。

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