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Quantification of Trace Mercury in Water: Solving the Problem of Adsorption Sample Preservation and Cross‐Contamination

机译:水中痕量汞的定量:解决吸附样品保存和交叉污染的问题

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摘要

Adsorption, sample preservation, and cross‐contamination are the major impediments to the accurate and sensitive analysis of low‐level mercury samples. Common measures to deal with this issue are to use Teflon, quartz, or borosilicate glass bottles for sampling, standard solution and sample preservation with oxidative chemicals, to prepare standard solutions daily and to use dedicated glassware. This paper demonstrates that these measures are neither efficient nor effective. Two common laboratory sample containers (borosilicate volumetric glass flasks and polypropylene tubes) are investigated for the preparation and preservation of water samples and standard solutions of 0.2–1 µg L with 2% HNO . Mercury adsorption rates of 6–22% are observed within 30 min and after 48 days, the adsorption is greater than 98%. In stark contrast, no adsorption is found during a testing period of 560 days when the solutions are subject to potassium permanganate‐persulfate digestion. New glass flasks and polypropylene bottles are free of mercury contamination but reused flasks are a major source of mercury cross‐contamination. To minimize adsorption and cross‐contamination, standard solutions are treated by potassium permanganate‐persulfate or BrCl digestion, and each individual sample and standard solution should be stored and prepared in single‐use polypropylene bottle, without transference.
机译:吸附,样品保存和交叉污染是对低含量汞样品进行准确和灵敏分析的主要障碍。解决此问题的常用措施是使用聚四氟乙烯,石英或硼硅酸盐玻璃瓶进行采样,标准溶液和使用氧化性化学物质保存的样品,每天准备标准溶液并使用专用玻璃器皿。本文证明了这些措施既无效又无效。研究了两个常用的实验室样品容器(硼硅酸盐容量瓶和聚丙烯管),用于制备和保存水样品和0.2–1 µg L和2%HNO的标准溶液。 30分钟内汞吸附率为6–22%,48天后,汞吸附率大于98%。与之形成鲜明对比的是,当溶液经过高锰酸钾-过硫酸盐消化时,在560天的测试时间内未发现吸附。新型玻璃烧瓶和聚丙烯瓶没有汞污染,但重复使用的烧瓶是汞交叉污染的主要来源。为了最大程度地减少吸附和交叉污染,用高锰酸钾-过硫酸钾或BrCl消解法处理标准溶液,每个单独的样品和标准溶液应在一次性聚丙烯瓶中储存和制备,不得转移。

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