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采用在线固相萃取-流动注射氢化物发生原子吸收光谱法测定水样中的 As(III)和总无机砷。

Determination of As(III) and total inorganic As in water samples using an on-line solid phase extraction and flow injection hydride generation atomic absorption spectrometry.

机构信息

Laboratorio Central, Facultad de Ingeniería Química, Universidad Nacional del Litoral, Santiago del Estero 2654-Piso 6, 3000 Santa Fe, Argentina.

出版信息

J Hazard Mater. 2011 Apr 15;188(1-3):311-8. doi: 10.1016/j.jhazmat.2011.01.126. Epub 2011 Feb 4.

Abstract

A simple and robust on-line sequential injection system based on solid phase extraction (SPE) coupled to a flow injection hydride generation atomic absorption spectrometer (FI-HGAAS) with a heated quartz tube atomizer (QTA) was developed and optimized for the determination of As(III) in groundwater without any kind of sample pretreatment. The method was based on the selective retention of inorganic As(V) that was carried out by passing the filtered original sample through a cartridge containing a chloride-form strong anion exchanger. Thus the most toxic form, inorganic As(III), was determined fast and directly by AsH(3) generation using 3.5 mol L(-1) HCl as carrier solution and 0.35% (m/v) NaBH(4) in 0.025% NaOH as the reductant. Since the uptake of As(V) should be interfered by several anions of natural occurrence in waters, the effect of Cl(-), SO(4)(2-), NO(3)(-), HPO(4)(2-), HCO(3)(-) on retention was evaluated and discussed. The total soluble inorganic arsenic concentration was determined on aliquots of filtered samples acidified with concentrated HCl and pre-reduced with 5% KI-5% C(6)H(8)O(6) solution. The concentration of As(V) was calculated by difference between the total soluble inorganic arsenic and As(III) concentrations. Detection limits (LODs) of 0.5 μg L(-1) and 0.6 μg L(-1) for As(III) and inorganic total As, respectively, were obtained for a 500 μL sample volume. The obtained limits of detection allowed testing the water quality according to the national and international regulations. The analytical recovery for water samples spiked with As(III) ranged between 98% and 106%. The sampling throughput for As(III) determination was 60 samplesh(-1). The device for groundwater sampling was especially designed for the authors. Metallic components were avoided and the contact between the sample and the atmospheric oxygen was carried to a minimum. On-field arsenic species separation was performed through the employ of a serial connection of membrane filters and anion-exchange cartridges. Advantages derived from this approach were evaluated. HPLC-ICPMS was employed to study the consistency of the analytical results.

摘要

开发并优化了一种基于固相萃取(SPE)的简单、稳健的在线顺序注射系统,该系统与带有加热石英管原子化器(QTA)的流动注射氢化物发生原子吸收光谱法(FI-HGAAS)联用,无需任何样品预处理即可测定地下水样品中的砷(III)。该方法基于将过滤后的原始样品通过装有氯化物形式强阴离子交换剂的小柱,选择性保留无机砷(V)。因此,最有毒的形式无机砷(III)可以通过使用 3.5mol/L HCl 作为载流溶液和 0.35%(m/v)NaBH₄在 0.025%NaOH 中作为还原剂来快速直接地通过生成 AsH₃进行测定。由于水样中天然存在的几种阴离子会干扰砷(V)的吸收,因此评估并讨论了 Cl-、SO₄²-、NO₃-、HPO₄²-、HCO₃-对保留的影响。通过在酸化的过滤样品中加入浓 HCl,并使用 5%KI-5%C₆H₈O₆溶液预先还原,测定总可溶性无机砷浓度。砷(V)的浓度通过总可溶性无机砷和砷(III)浓度的差值计算。对于 500μL 样品体积,分别获得了 0.5μg/L 和 0.6μg/L 的砷(III)和无机总砷的检测限(LOD)。获得的检测限允许根据国家和国际法规测试水质。用砷(III)对水样进行加标回收的范围为 98%-106%。砷(III)测定的采样通量为 60 个样品/h。地下水采样装置是作者专门设计的。避免使用金属部件,并将样品与大气氧气的接触降至最低。通过串联使用膜过滤器和阴离子交换柱来进行现场砷形态分离。评估了这种方法的优点。使用高效液相色谱-电感耦合等离子体质谱法(HPLC-ICPMS)研究分析结果的一致性。

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