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首页> 外文期刊>Talanta: The International Journal of Pure and Applied Analytical Chemistry >Development of methodologies to determine aluminum,cadmium,chromium and lead in drinking waterby ET AAS using permanent modifiers
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Development of methodologies to determine aluminum,cadmium,chromium and lead in drinking waterby ET AAS using permanent modifiers

机译:开发使用永久性修饰剂通过ET AAS测定饮用水中铝,镉,铬和铅的方法

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In this work,methodologies were developed to determine aluminum (Al),cadmium chromium and lead in drinking water by electrothermal atomic absorption spectrometry using permanent modifiers.No use of modifier,iridium,ruthenium,rhodium and zirconium (independently,500 mug) were tested to each one analyte through the pyrolysis and atomization temperatures curves.As the matrix is very simple,did not had occurred problems with the background for all metals.The best results obtained for cadmium and chromium was with the use of rhodium permanent modifier.For lead and aluminum,the best choice was the use of zirconium.The selection for the modifier took into account the sensitivity,form of the absorption pulse and low atomization temperature (what contributes to elevate the useful life of the graphite tube).For aluminum using zirconium permanent,the best pyrolysis and atomization temperatures were respectively,of 1000 and 2500 deg C with a characteristic mass (1% of absorbance,m_0) of 19 pg (recommended of 20 pg).For cadmium,with use of rhodium the best temperatures for the pyrolysis and atomization were respectively of 400 and 1100 deg C,with a symmetrical peak and with a m_0 of 1.0 pg (recommended of 1.0 pg).For chromium with rhodium permanent,the best temperatures for pyrolysis and atomization were respectively of 1000 and 2200 deg C,with symmetrical peak and m_0 of 5.3 pg (recommended of 5.5 pg).For lead with zirconium permanent,the best temperatures for pyrolysis and atomization were of 700 and 2400 deg C,with symmetrical peak and with m_0 of 30 pg (recommended of 20 pg).Water samples spiked with each one of the metals in four different levels inside of the acceptable values presented recoveries always close to 100%.The detection limits were of 0.1 mug1~(-1) for cadmium0.2mug1~(-1) for chromium0.5 (xgl~(-1) for lead and l.4mugl~(-1) for aluminum.
机译:在这项工作中,开发了使用永久性改性剂通过电热原子吸收光谱法测定饮用水中铝(Al),镉铬和铅的方法。未测试使用改性剂,铱,钌,铑和锆(独立地为500杯)由于基质非常简单,所有金属的背景都没有出现问题。镉和铬的最佳结果是使用铑永久性改性剂。对于铝,最好的选择是使用锆。改性剂的选择要考虑到灵敏度,吸收脉冲的形式和低雾化温度(这有助于提高石墨管的使用寿命)。对于使用锆的铝永久的最佳热解温度和雾化温度分别为1000和2500℃,特征质量(吸光度的1%,m_0)为19 pg(rec)对于镉,使用铑,热解和雾化的最佳温度分别为400和1100℃,对称峰,m_0为1.0 pg(建议为1.0 pg)。铬含铑永久物的最佳热解和雾化温度分别为1000和2200℃,对称峰和m_0为5.3 pg(推荐为5.5 pg)。 700和2400摄氏度,具有对称峰且m_0为30 pg(建议为20 pg)。加水样品中每种金属以四种不同的含量加标到可接受的值范围内,回收率始终接近100%。镉的限制为0.1 Cug1〜(-1),铬0.5的范围为(-1)铬0.5(铅的xgl〜(-1)和铝为1.4mugl〜(-1)。

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