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.

J Hazard Mater

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

Published: April 2011

AI Article Synopsis

  • A straightforward online sequential injection system was developed that uses solid-phase extraction coupled with flow injection hydride generation atomic absorption spectrometry (FI-HGAAS) to detect As(III) in groundwater without sample pretreatment.
  • The method selectively retains the less toxic form of arsenic (As(V)) and directly measures As(III) by generating arsine (AsH3) using specific reagents, while evaluating potential interferences from common anions found in natural water.
  • The system achieved low detection limits and high analytical recovery rates, enabling efficient water quality testing in compliance with regulations, and was designed to minimize contact with atmospheric oxygen during sampling.

Article 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.

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http://dx.doi.org/10.1016/j.jhazmat.2011.01.126DOI Listing

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