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饮用水分配系统中六价铬的释放:铁腐蚀层中零价铬的新见解。

Hexavalent Chromium Release in Drinking Water Distribution Systems: New Insights into Zerovalent Chromium in Iron Corrosion Scales.

机构信息

Department of Chemical and Environmental Engineering, University of California at Riverside, Riverside, California 92521, United States.

出版信息

Environ Sci Technol. 2020 Oct 20;54(20):13036-13045. doi: 10.1021/acs.est.0c03922. Epub 2020 Sep 30.

Abstract

Upon cast iron corrosion in contact with residual disinfectants, drinking water distribution systems have become potential geogenic sources for hexavalent chromium Cr(VI) release. This study investigated mechanisms of Cr(VI) release from cast iron corrosion scales. The oxidation of the corrosion scales by residual disinfectant chlorine released Cr(VI) and exhibited a three-phase kinetics behavior: an initial 2 h fast reaction phase, a subsequent 2-to-12 h transitional phase, and a final 7-day slow reaction phase approximately 2 orders of magnitude slower than the initial phase. X-ray absorption spectroscopy analysis discovered that zerovalent Cr(0) coexisted with trivalent Cr(III) solids in the corrosion scales. Electrochemical corrosion analyses strongly suggested that Cr(0) in the corrosion scales originated from Cr(0) in the cast iron alloy. Cr(0) exhibited a much higher reactivity than Cr(III) in the formation of Cr(VI) by chlorine. The presence of bromide in drinking water significantly accelerated Cr(VI) release because of its catalytic effect. Meanwhile, chlorine consumption was mainly attributed to the oxidation of organic matter and ferrous iron. Findings from this study point to a previously unknown but important pathway of Cr(VI) formation in drinking water, that is, direct oxidation of Cr(0) by chlorine, and suggest new strategies to control Cr(VI) in drinking water by inhibiting Cr(0) reactivity.

摘要

当铸铁与残留消毒剂接触而发生腐蚀时,饮用水分配系统就成为六价铬 Cr(VI) 释放的潜在地球成因源。本研究调查了从铸铁腐蚀层释放 Cr(VI) 的机制。残留消毒剂氯对腐蚀层的氧化释放出 Cr(VI),并表现出三相动力学行为:最初 2 小时的快速反应阶段,随后 2 至 12 小时的过渡阶段,以及最终 7 天的缓慢反应阶段,其反应速度比初始阶段慢约 2 个数量级。X 射线吸收光谱分析发现,零价 Cr(0)与腐蚀层中的三价 Cr(III)固体共存。电化学腐蚀分析强烈表明,腐蚀层中的 Cr(0)源自铸铁合金中的 Cr(0)。Cr(0)在氯气作用下形成 Cr(VI)的反应活性远高于 Cr(III)。饮用水中溴化物的存在由于其催化作用显著加速了 Cr(VI)的释放。同时,氯的消耗主要归因于有机物和亚铁的氧化。本研究的结果指出了饮用水中 Cr(VI)形成的一个以前未知但很重要的途径,即氯气直接氧化 Cr(0),并提出了通过抑制 Cr(0)反应性来控制饮用水中 Cr(VI)的新策略。

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