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    铬(Ⅵ)-二乙基二硫代甲酸钠共沉淀-原子吸收光谱法测定环境水样中铁、锰、锌、镉

    AAS Determination of Iron,Manganese,Zinc,Cadmium in Environmental Water Samples After Enrichment by Coprecipitaion with Cr(Ⅵ)-DDTC

    • 摘要: 提出了以二乙基二硫代甲酸钠螯合铬(Ⅵ)作为载体共沉淀富集水体中铁、锰、锌和镉的方法.沉淀经离心分离,甲基异丁酮溶解后,以微量进样300 μL火焰原子吸收光谱法测定铁、锰、锌,以石墨炉原子吸收光谱法测定镉.用水样10.0 mL,在pH 4.6的邻苯二甲酸氢钾缓冲介质中加入20 g·L-1重铬酸钾溶液150 μL,20 g·L-1 DDTC溶液1.0 mL可达到完全共沉淀分离,所得沉淀经离心分离后用甲基异丁酮2.0 mL溶解,并用于AAS分析.在优化的条件下,铁、锰、锌和镉的检出限(3σ)分别为9.0,6.8,1.8,0.03 μg·L-1,相对标准偏差(n=6)在1.8%~3.8%之间.方法用于实际水样的测定,用标准加入法测得回收率在93.7%~105.0%之间.

       

      Abstract: Trace amounts of Fe(Ⅲ),Zn(Ⅱ),Mn(Ⅱ) and Cd(Ⅱ) in environmental water sample was enriched by coprecipitation by DDTC-Cr precipitate.The sample solution (10.0 mL) was adjusted to pH 4.6 with phosphate buffer solution and 150 μL of 20 g·L-1 K2Cr2O7 solution were added to form DDTC-Cr precipitate.One mL of 20 g·L-1 DDTC solution was necessary for complete to precipitation of the 4 elements.The precipitates were separated by centrifugation and dissolved in 2.0 mL of MIBK,which was used for AAS determination.The volume of the MIBK solution introduced for AAS analysis was 300 μL,and Fe(Ⅲ),Zn(Ⅱ),Mn(Ⅱ) and Cd(Ⅱ) were determined by FAAS,while Cd(Ⅱ) was determined by GFFAAS.Under the optimum conditions,values of detection limit (3s/k) found were (μg·L-1) 9.0 (for Fe),6.8 (for Mn),1.8 (for Zn) and 0.03 (for Cd).Values of RSD′s (n=6) found were in the range of 1.8%-3.8% respectively.Recovery was tested on the base of samples of sea water and river water by standard addition method,giving results in the range of 93.7%-105.0%

       

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