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首页> 外文期刊>Atomic Spectroscopy >An Evolved GFAAS Method for Trace and Ultratrace Determination of Cr(III) and Cr(VI) in Water and Wastewater: Speciation of Chromium
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An Evolved GFAAS Method for Trace and Ultratrace Determination of Cr(III) and Cr(VI) in Water and Wastewater: Speciation of Chromium

机译:水和废水中Cr(III)和Cr(VI)的痕量和超速度测定的演进GFAAS方法:铬的形态

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摘要

A highly evolved method for the determination of Cr(III) and Cr(VI) at the ppm to ppb level in water and wastewater samples has been developed. For the ppm level determination of chromium, Cr(III) is separated from Cr(VI) by its R2O3 precipitation along with Fe(OH)(3), then both Cr(III) and Cr(VI) are separately determined by GFAAS in a smaller aliquot of sample solution after removal of associated interfering elements by a novel solvent extraction system involving 2,Adihydroxynaphthalene as an extractant. However, for ppb level determination of Gr(III) and Cr(I), a pre-concentration technique needs to be combined with a solvent extraction system. Here, Cr(III) is separated and preconcentrated by R2O3 precipitation as above, however, from a large volume of water sample, i.e., about 400-500 mL. The analyte Cr(III) is further separated from iron and other interfering elements by selective solvent extraction using the same extractant (2,3-dihydroxynaphthalene) and was then determined selectively by GFAAS. Total chromium [Cr(III)+Cr(VI)] from a 400.500 mL separate water sample is preconcentrated as R2O3 ppt of Cr(III) [after reducing Cr(VI) with Rap] along with R2O3 ppt of Fe(III) generated in situ by way of oxidation of residual Fe(H) by HNO: t . Iron and other interfering elements are similarly removed by solvent extraction using the same extractant (2,34I,ND) as in the determination of Cr(III), and total Cr as Cr(III) is similarly determined by GFAAS. The content of Cr(VI) was deduced by subtracting the value of Cr(III) from the content of total chromium determined as Cr(III). The method developed is highly effective and reliable. While the detection limit (36) and %RSD of the method for ppm level chromium (without further preconcentration) was 0.4 mu g L-1 and 5-10%, respectively, at the 4.0 mu g L-1 level, the corresponding values of the method for ppb to ppt level chromium determination were 0.01 mu g L-1 and 3 to 5%, respectively, at the 0.1 mu g level. The pre-c
机译:已经开发了一种高度进化的方法,用于测定PPM在水和废水样品中PPM至PPB水平的Cr(III)和Cr(VI)。对于PPM水平测定铬,Cr(III)通过其R 2 O 3沉淀与Fe(OH)(3)分离Cr(III),然后通过GFAAs分别确定Cr(III)和Cr(VI)。通过涉及2,Adihydroxynaphonalena作为萃取剂的新型溶剂萃取系统除去相关的干扰元件后,较少等份的样品溶液。然而,对于GR(III)和Cr(I)的PPB水平测定,预浓缩技术需要与溶剂萃取系统结合。这里,如上所述,通过R2O3沉淀分离并预先浓缩,但是,从大量的水样,即约400-500ml。通过使用相同的萃取剂(2,3-二羟基萘)选择性溶剂萃取,通过选择性溶剂萃取进一步与铁和其他干扰元件分离出分析物Cr(III),然后通过GFAAs选择性地测定。来自400.500ml单独的水样品的总铬[Cr(III)+ Cr(VI)]作为Cr(III)的R2O3 PPT预浓缩,与RAP]和RAP]的R2O3 PPT一起以及产生的Fe(III)的R2O3 PPT通过HNO:T通过氧化残留Fe(H)的方式原位原位。通过使用相同的萃取剂(2,34i,Nd)在Cr(III)的测定中,通过溶剂萃取类似地除去铁和其他干扰元件,并且作为Cr(III)的总Cr类似地通过GFAAs确定。通过从作为Cr(III)的总铬的含量中减去Cr(III)的值来推导Cr(VI)的含量。该方法开发的方法非常有效可靠。虽然PPM水平铬(无需进一步前浓度的方法的检测极限(36)和%RSD分别为0.4μg1-1和5-10%,在4.0μgl-1水平,相应的值在0.1μg水平下,PPB对PPT水平铬测定的方法分别为0.01μmg1-1和3至5%。预先c

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