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薄膜双扩散梯度(DGT)探针揭示了来自中国南方西枝河流域沉积物铬(Cr)的形态和迁移特性。

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.

机构信息

Guangdong Provincial Key Laboratory of Applied Botany, Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Guangzhou 510650, China.

School of Geography and Planning, Sun Yat-Sen University, Guangzhou 510275, China.

出版信息

J Hazard Mater. 2022 Aug 15;436:129229. doi: 10.1016/j.jhazmat.2022.129229. Epub 2022 May 23.

DOI:10.1016/j.jhazmat.2022.129229
PMID:35739749
Abstract

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.

摘要

研究沉积物中铬(Cr)的形态和再迁移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程序和扩散梯度薄膜(DGT)技术相结合,研究了沉积物 Cr 的地球化学形态、迁移潜力和释放特征。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 > 酸可溶部分。OM 结合态 Cr(III)的解吸和 Mn 氧化物的氧化作用导致冬季可迁移 Cr(III)和 Cr(VI)水平较高,其中可迁移 Cr(III)是主要形态,占可迁移 Cr 总浓度的 48.1%65.5%;而 Mn 氧化物的还原溶解导致夏季可迁移 Cr(VI)的再迁移,由于 Cr(III)的快速沉淀,主导 Cr 形态向 Cr(VI)转变(48.9%65.7%)。在两次采样期间,沉积物是可迁移 Cr(VI)的主要汇。对于可迁移 Cr(III),冬季沉积物从源转变为夏季的汇。由于冬季河水处于氧化条件下,可迁移 Cr(III)有被重新氧化为更具毒性的 Cr(VI)的潜力,因此其扩散释放值得优先关注。

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