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缺氧河口沉积物中六价铬的还原速率:pH 值的影响及酸可挥发性硫化物的作用。

Rates of hexavalent chromium reduction in anoxic estuarine sediments: pH effects and the role of acid volatile sulfides.

机构信息

Department of Geography and Environmental Engineering, Johns Hopkins University, 3400 North Charles Street, Ames Hall 313, Baltimore, Maryland 21218, USA.

出版信息

Environ Sci Technol. 2010 Jan 1;44(1):136-42. doi: 10.1021/es9013882.

DOI:10.1021/es9013882
PMID:20039744
Abstract

Rates of Cr(VI) reduction were assessed in batch kinetic experiments using dilute suspensions of anoxic sediments collected from the Baltimore Harbor. Rapid and complete Cr(VI) reduction occurred on the time scale of minutes (pseudo-first-order rate constants ranged from 0.01 to 0.40 min(-1) for 1.0 g/L sediment suspensions at pH 7.0) via reaction with mineral surfaces. The reaction rate was first-order with respect to Cr(VI) concentration and proportional to the concentration of sediment acid volatile sulfides (AVS). AVS-normalized rates of Cr(VI) reduction decreased by approximately 2 orders of magnitude as the suspension pH increased from 5.0 to 8.2. The AVS-normalized rate constant was linearly correlated with the fraction of total dissolved Cr(VI) in the protonated HCrO(4)(-) form at a given pH (f(HCrO(4))((-))). The following rate law was found to describe all the experimental data: d[Cr(VI)]/dt = -k[AVS]f(HCrO(4))((-))Cr(VI), where the AVS- and pH-independent rate constant k = 3.14(+/-0.75) x 10(4) M(-1) min(-1). The results of this study suggest the importance of reactions between Cr(VI) and solid phase AVS constituents in controlling Cr(VI) fate in anoxic estuarine sediments, and indicate that Cr(VI) is unlikely to be a toxicological stressor in AVS-containing sediments.

摘要

采用来自巴尔的摩港缺氧沉积物的稀悬浮液,在批量动力学实验中评估了 Cr(VI)的还原速率。在分钟时间尺度内,通过与矿物表面反应,快速且完全地还原 Cr(VI)(在 pH 值为 7.0 时,对于 1.0 g/L 沉积物悬浮液,假一级速率常数范围为 0.01 至 0.40 min(-1))。该反应对 Cr(VI)浓度呈一级反应,与沉积物酸可挥发硫化物(AVS)的浓度成正比。随着悬浮液 pH 值从 5.0 增加到 8.2,AVS 归一化的 Cr(VI)还原速率降低了约 2 个数量级。在给定 pH 值下,AVS 归一化的速率常数与总溶解 Cr(VI)中质子化 HCrO(4)(-)形式的分数(f(HCrO(4))((-)))呈线性相关。发现以下速率定律可以描述所有实验数据:d[Cr(VI)]/dt = -k[AVS]f(HCrO(4))((-))Cr(VI),其中 AVS 和 pH 无关的速率常数 k = 3.14(+/-0.75) x 10(4) M(-1) min(-1)。本研究的结果表明,Cr(VI)与固相 AVS 成分之间的反应对于控制缺氧河口沉积物中 Cr(VI)的命运非常重要,并且表明在含有 AVS 的沉积物中,Cr(VI)不太可能成为毒理学胁迫物。

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