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浊点萃取分光光度法测定环境样品中痕量汞形态。

Cloud point extraction and spectrophotometric determination of mercury species at trace levels in environmental samples.

机构信息

University of Cumhuriyet, Faculty of Sciences, Department of Chemistry, TR-58140, Sivas, Turkey.

出版信息

Talanta. 2012 Jan 15;88:516-23. doi: 10.1016/j.talanta.2011.11.026. Epub 2011 Nov 12.

Abstract

A new micelle-mediated separation and preconcentration method was developed for ultra-trace quantities of mercury ions prior to spectrophotometric determination. The method is based on cloud point extraction (CPE) of Hg(II) ions with polyethylene glycol tert-octylphenyl ether (Triton X-114) in the presence of chelating agents such as 1-(2-pyridylazo)-2-naphthol (PAN) and 4-(2-thiazolylazo) resorcinol (TAR). Hg(II) ions react with both PAN and TAR in a surfactant solution yielding a hydrophobic complex at pH 9.0 and 8.0, respectively. The phase separation was accomplished by centrifugation for 5 min at 3500 rpm. The calibration graphs obtained from Hg(II)-PAN and Hg(II)-TAR complexes were linear in the concentration ranges of 10-1000 μg L(-1) and 50-2500 μg L(-1) with detection limits of 1.65 and 14.5 μg L(-1), respectively. The relative standard deviations (RSDs) were 1.85% and 2.35% in determinations of 25 and 250 μg L(-1) Hg(II), respectively. The interference effect of several ions were studied and seen commonly present ions in water samples had no significantly effect on determination of Hg(II). The developed methods were successfully applied to determine mercury concentrations in environmental water samples. The accuracy and validity of the proposed methods were tested by means of five replicate analyses of the certified standard materials such as QC Metal LL3 (VWR, drinking water) and IAEA W-4 (NIST, simulated fresh water).

摘要

一种新的胶束介导分离和预浓缩方法被开发用于超痕量汞离子的分光光度测定前。该方法基于浊点萃取(CPE)与聚乙二醇叔辛基苯基醚(Triton X-114)存在螯合剂如 1-(2-吡啶偶氮)-2-萘酚(PAN)和 4-(2-噻唑偶氮)间苯二酚(TAR)的汞(II)离子。Hg(II)离子在表面活性剂溶液中与 PAN 和 TAR 反应,分别在 pH 9.0 和 8.0 下生成疏水性络合物。通过在 3500 rpm 下离心 5 分钟完成相分离。从 Hg(II)-PAN 和 Hg(II)-TAR 络合物获得的校准曲线在 10-1000 μg L(-1)和 50-2500 μg L(-1)浓度范围内呈线性,检测限分别为 1.65 和 14.5 μg L(-1)。在测定 25 和 250 μg L(-1)Hg(II)时,相对标准偏差(RSD)分别为 1.85%和 2.35%。研究了几种离子的干扰效应,发现水样中常见的共存离子对 Hg(II)的测定没有显著影响。该方法成功应用于环境水样中汞浓度的测定。通过对 QC Metal LL3(VWR,饮用水)和 IAEA W-4(NIST,模拟淡水)等认证标准物质的五次重复分析,验证了所提出方法的准确性和有效性。

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