首页> 外文期刊>Journal of Environmental Science and Health >Electrothermal atomic absorption spectrometric determination of cadmium and lead in traces in aquatic systems following flotation by two chromium(III) collectors
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Electrothermal atomic absorption spectrometric determination of cadmium and lead in traces in aquatic systems following flotation by two chromium(III) collectors

机译:电热原子吸收光谱法测定两个铬(III)捕集剂浮选后水体系统中的痕量镉和铅

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摘要

A fast notation method for determination of cadmium and lead in aquatic systems by two chromium(III) collectors is described. The first collector is a colloid precipitate of hydrated chromium(III) oxide, Cr_2O_3. XH_2O, while the second is a bulk chromium(III) pentamethylenedithiocarbamate, Cr(PMDTC)_3. Cadmium and lead present in water are incorporated into the collector mass at pH 7.5 by addition of 20 mg of Cr(III) and 0.4 mmol of pentamethyleneammonium pentamethylenedithiocarbamate, PMA-PMDTC, to 0.5 L water sample. A solid precipitate was separated from the processed water system by air bubbles. After dissolving with strong acid, the solution is tested by electrothermal atomic absorption spectrometry (ETAAS). The limit of detection for Cd by flotation/ETAAS method is 0.002 μg L~(-1), while for Pb is 0.04 μg L~(-1). The precision of the method is expressed as relative standard deviations ranging of 5.0% for Cd (concentration range from 0.1 to 0.5 μg L~(-1)) and 4.25% for Pb (concentration range from 0.5 to 5 μg L~(-1)). The characteristic mass (mass that gives an integrated absorbance of 0.0044 s) of 1.06 pg for Cd and 16.7 pg for Pb were obtained. The method was validated by the standard additions and by its application to the reference materials (Surface water-SPS-SW-1, River Thames Water-LGC-6019).
机译:描述了一种通过两种铬(III)捕集剂测定水体系统中镉和铅的快速标记方法。第一收集器是水合氧化铬(III)Cr_2O_3的胶体沉淀。 XH_2O,而第二个是块状五亚甲基二硫代氨基甲酸铬(III)Cr(PMDTC)_3。通过向0.5 L水样品中添加20 mg Cr(III)和0.4 mmol五亚甲基五亚甲基二硫代氨基甲酸酯PMA-PMDTC,将水中存在的镉和铅掺入pH 7.5的收集器物料中。通过气泡将固体沉淀物从处理后的水系统中分离出来。用强酸溶解后,通过电热原子吸收光谱法(ETAAS)测试溶液。浮选/ ETAAS法检测镉的下限为0.002μgL〜(-1),而铅的检测限为0.04μgL〜(-1)。该方法的精密度表示为相对标准偏差,镉的相对标准偏差为5.0%(浓度范围为0.1至0.5μgL〜(-1)),铅含量的相对标准偏差为4.25%(浓度范围为0.5至5μgL〜(-1) ))。获得的Cd的特征质量(积分吸光度为0.0044 s的质量)为1.06 pg,Pb的特征质量为16.7 pg。该方法已通过标准添加及其在参考材料(表面水-SPS-SW-1,泰晤士河水-LGC-6019)中的应用进行了验证。

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