Precision and Bias of Graphite Furnace Analysis of Environmental Samples

G. L. Mckinney
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Abstract

* Determination of Cr(lIl)+Cr(VI). To 25 mL of sample, add 0.3 mL of 8% PHP, adjust pH to 3.5, and add 3 mL of 10% APDC and 5 mL of PHP-saturated MIBK. Extract for 20 min. Determine Cr(lll)+Cr(VI) in the MIBK layer. * Determination of Cr(VI). Proceed as above except for the addition of 3 mL of 8% PHP and 3 mL of 2% APDC and for the extraction time of 10 mm. * Determination of Cr(III). The value of Cr(III) is obtained as the difference between Cr(Ill) +Cr(VI) and Cr(VI). The concentration of Cr(111) is also determined by the SM-7 ion exchange procedure [1]. In all the above cases, the Cr atomic absorption signal was measured by using the dry/atomize program of 900 'C-30 s (ramp)-30 s (hold)/2500 0 C-O s (ramp)-6 s (hold).
环境样品石墨炉分析的精度和偏差
* Cr(lIl)+Cr(VI)测定。取25ml样品,加入0.3 mL 8%的PHP,调整pH至3.5,加入3ml 10%的APDC和5ml PHP饱和的MIBK。提取20分钟,测定MIBK层中Cr(ll)+Cr(VI)含量。* Cr(VI)的测定。除加入3ml 8%的PHP和3ml 2%的APDC,提取时间为10mm外,按上述步骤进行。Cr(III)的值由Cr(Ill) +Cr(VI)与Cr(VI)之差得到。Cr(111)的浓度也可用SM-7离子交换法测定。在上述所有情况下,采用900 'C-30 s(斜坡)-30 s(保持)/2500 ' C-O s(斜坡)-6 s(保持)的干燥/雾化程序测量Cr原子吸收信号。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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