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Identification and Distribution of Vanadinite (Pb_5(V~(5+) O_4)_3CI) in Lead Pipe Corrosion By-Products

机译:铅管腐蚀副产物中钒铅矿(Pb_5(V〜(5+)O_4)_3CI)的鉴定与分布

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摘要

This study presents the first detailed look at vanadium (V) speciation in drinking water pipe corrosion scales. A pool of 34 scale layers from 15 lead or lead-lined pipes representing eight different municipal drinking water distribution systems in the Northeastern and Midwestern portions of the United States were examined. Diverse synchrotron-based techniques, including bulkXANES (X-ray absorption near edge spectroscopy), μ-XANES, μ-XRD (X-ray diffraction), and μ-XRF (X-ray fluorescence) mapping were employed along with traditional powder XRD, SEM-EDXA (scanning electron microscopy-energy dispersive X-ray analysis), and ICP-OES (inductively coupled plasma-optical emission spectrometry) to evaluate vanadium speciation and distribution in these deposits. Vanadinite (Pb_5(VO_4)_3CI) was positively identified, and occurred most frequently in the surface layers. Low V_(tot) in these waters is likely the limiting factor in the abundance of vanadinite in the pipe scales, along with the existence of divalent lead. The occurrence of V in these samples as a discrete mineral is important because it is formed in the presence of very low concentrations of V in the finished water, it provides a mechanism to concentrate μg·L~(-1) amounts of V from the water to near-percent levels in the pipe scales, and the robustness of V accumulation and release in response to water chemistry changes is likely different than it would be with a sorption accumulation mechanism. Extrapolation from limited existing water chemistry data in this study provides an estimate of △G_f° for vanadinite as approximately -3443 kJ·mol~(-1), or less, leading to a log K_(s0) value of approximately -86 for the reactionrnin which denotes activity.
机译:这项研究首次详细介绍了饮用水管腐蚀水垢中的钒(V)形态。对来自15个铅或衬里管道的34层水垢池进行了分析,这些管道代表了美国东北部和中西部地区的8种不同的市政饮用水分配系统。基于多元同步加速器的技术,包括bulkXANES(近边缘光谱的X射线吸收),μ-XANES,μ-XRD(X射线衍射)和μ-XRF(X射线荧光)作图,以及传统的粉末XRD ,SEM-EDXA(扫描电子显微镜-能量色散X射线分析)和ICP-OES(电感耦合等离子体发射光谱法)来评估这些沉积物中的钒形态和分布。钒铅矿(Pb_5(VO_4)_3CI)得到了肯定鉴定,并且最常出现在表层。这些水域中较低的V_(tot)可能是管垢中钒铁矿丰度的限制因素,同时也存在二价铅。这些样品中的V以离散矿物的形式存在很重要,因为它是在最终水中存在非常低浓度的V的情况下形成的,它提供了一种机制,可以从水中浓缩出μg·L〜(-1)量的V。到水垢达到接近百分数的水平,响应水化学变化的V积累和释放的稳健性可能与吸附积累机制不同。本研究从有限的现有水化学数据中推算得出,钒铁矿的△G_f°约为-3443 kJ·mol〜(-1)或更小,导致对数对数K_(s0)的对数K_(s0)值约为-86。表示活性的反应。

著录项

  • 来源
    《Environmental Science & Technology》 |2009年第12期|4412-4418|共7页
  • 作者单位

    Department of Geology, University of Cincinnati, Cincinnati, Ohio 45221-0013;

    U.S. Environmental Protection Agency, National Risk Management Research Laboratory, 26 West Martin Luther King Drive, Cincinnati, Ohio 45268;

    U.S. Environmental Protection Agency, National Risk Management Research Laboratory, 26 West Martin Luther King Drive, Cincinnati, Ohio 45268;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);美国《生物学医学文摘》(MEDLINE);美国《化学文摘》(CA);
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

  • 入库时间 2022-08-17 14:04:43

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