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与来源值相比,受地质/工业铬污染的中欧水域中 δ53Cr 偏移呈阳性的情况较为常见。

Common occurrence of a positive δ53Cr shift in Central European waters contaminated by geogenic/industrial chromium relative to source values.

机构信息

Division of Geochemistry and Laboratories, Czech Geological Survey , Geologicka 6, 152 00 Prague 5, Czech Republic.

出版信息

Environ Sci Technol. 2014 Jun 3;48(11):6089-96. doi: 10.1021/es405615h. Epub 2014 May 13.

DOI:10.1021/es405615h
PMID:24779992
Abstract

Carcinogenic effects of hexavalent chromium in waters are of concern in many countries worldwide. We explored Cr isotope systematics at 11 sites in the Czech Republic and Poland. Geogenic Cr pollution was associated with serpentinite bodies at former convergent plate margins, while anthropogenic Cr pollution resulted from electroplating, tanning, and the chemical industry. Cr(VI) concentration in geogenic waters was less than 40 ppb. Anthropogenic waters contained up to 127,000 ppb Cr(VI). At both geogenic and anthropogenic sites, where known, the source of pollution had a low δ53Cr (<1‰). δ53Cr of geogenic and anthropogenic waters was up to 3.9 and 5.8‰, respectively. At both serpentinite-dominated and industrial sites, δ53Cr(VI)aq was shifted toward higher values, compared to the pollution source. At the industrial sites, this positive δ53Cr shift was related to Cr(VI) reduction, a process known to fractionate Cr isotopes. At geogenic sites, the origin of high δ53Cr(VI)aq is tentatively ascribed to preferential release of 53Cr during oxidation of soil Cr(III) and its mobilization to water. δ53Cr(VI) of industrially contaminated waters was significantly higher (p<0.001) compared to δ53Cr of waters carrying geogenic Cr(VI), implying that either the effective fractionation factor or process extent was greater for Cr(VI) reduction than for Cr(III) oxidation.

摘要

六价铬在水中的致癌作用引起了世界上许多国家的关注。我们在捷克共和国和波兰的 11 个地点探索了铬同位素系统。原生铬污染与前汇聚板块边缘的蛇纹岩有关,而人为铬污染则来自电镀、鞣制和化学工业。原生水中的 Cr(VI)浓度小于 40ppb。人为水中含有高达 127000ppb 的 Cr(VI)。在原生和人为污染的地方,如果已知,污染的来源具有较低的 δ53Cr(<1‰)。原生和人为水中的 δ53Cr 分别高达 3.9 和 5.8‰。在蛇纹岩占主导地位的和工业的地方,δ53Cr(VI)aq 与污染源相比向更高的值偏移。在工业地点,这种正的 δ53Cr 偏移与 Cr(VI)还原有关,这是一种已知的分馏 Cr 同位素的过程。在原生地,高 δ53Cr(VI)aq 的起源暂归因于土壤 Cr(III)氧化过程中 53Cr 的优先释放及其向水中的迁移。工业污染水中的 δ53Cr(VI)显著高于携带原生 Cr(VI)的水(p<0.001),这意味着 Cr(VI)还原的有效分馏因子或过程程度大于 Cr(III)氧化。

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