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Ultrasound-assisted supramolecular solvent microextraction coupled with graphite furnace atomic absorption spectrometry for speciation analysis of inorganic arsenic

机译:超声辅助超分子溶剂微萃取与石墨炉原子吸收光谱法,用于无机砷的形态分析

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摘要

A novel ultrasonic-assisted supramolecular solvent microextraction (USASS-ME) method was proposed for the selective microextraction of As(III, V) prior to its determination via graphite furnace atomic absorption spectrometry. Supramolecular solvent (SUPRAS) was prepared from the solution of reverse micelles of decanoic acid (DeA) in tetrahydrofuran (THF) that was immediately injected into water, where water acted as the coacervating agent. Then, As(III) was complexed with ammonium pyrrolidinedithiocarbamate (APDC) and directly extracted by reverse micelle coacervates. Sonication increased the speed of homogenization and mass transfer of the target analyte into the SUPRAS. The effects of the above mentioned parameters on the recovery of As(III) were investigated. Total inorganic As(III, V) was similarly extracted after the reduction of As(V) to As(III) with the mixture of potassium iodide and sodium thiosulfate, and As(V) concentration was calculated by the difference. Under the optimized conditions, the proposed method was validated with satisfactory results. Good linearity with the coefficient of determination greater than 0.99 was obtained. The limit of detection and quantification was 0.2 and 0.7 ng mL(-1). Intra-day (n = 3) and inter-day (n = 3) relative standard deviations were 3.8% and 6.9%, respectively, and the enrichment factor was equal to 60-fold. The method was also successfully applied to the speciation of As in different environmental water samples and soil.
机译:提出了一种新型超声波辅助超分子溶剂微萃取(USAS-ME)方法,用于在通过石墨炉原子吸收光谱法测定之前选择性微萃取作为(III,V)的选择性微萃取。由癸酸(DEA)的反向胶束溶液中的超分子溶剂(SUPRAS)在立即注射到水中的癸酸(DEA)的溶液中制备,其中水用作凝聚剂。然后,如(III)用吡咯烷二硫代氨基甲酸铵(APDC)复合,并通过反转胶束凝聚体直接萃取。超声处理提高了靶分析物的均质化和传质转移到上普拉斯的速度。研究了上述参数对恢复(III)的影响。在将As(v)还原为(iii)与碘化钾和硫代硫酸钠的混合物的情况下类似地提取无机作为(III,V),并且通过差异计算(v)浓度。在优化条件下,验证了所提出的方法,结果验证。获得了大于0.99的测定系数的良好线性。检测和定量的极限为0.2和0.7 ng ml(-1)。白天(n = 3)和白天(n = 3)相对标准偏差分别为3.8%和6.9%,富集因子等于60倍。该方法还成功地应用于不同环境水样和土壤中的形态。

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