Speciation of eight arsenic compounds in human urine by high-performance liquid chromatography with inductively coupled plasma mass spectrometric detection using antimonate for internal chromatographic standardization

Four anionic and four cationic arsenic compounds in urine were separated by anion- and cation-exchange high-performance liquid chromatography and detected by inductively coupled plasma mass spectrometry (ICP-MS) at m/z 75. The species were the anions arsenite, arsenate, monomethylarsonate and dimethylarsinate and the cations arsenobetaine, trimethylarsine oxide, arsenocholine and the tetramethylarsonium ion. Hexahydroxyantimonate(III) was co-chromatographed with the arsenic anions but detected at m/z 121 and used as an internal standard for their qualitative analysis. Arsenite was prone to oxidation to arsenate in urine but was stable after at least 4-fold dilution of the urine with water. Arsenite was unstable in both urine samples and standard mixtures when diluted with the basic (pH 10.3) mobile phase used for anion chromatography. This could not be prevented by adding ascorbic acid as antioxidant. The argon chloride interference at m/z 75 was eliminated by chromatographic separation of the chloride present in the sample from the arsenic analytes. The ClO+ ion detected at m/z 51 and 53 was used to monitor the retention time of chloride in the anion-exchange system. The chloride eluted about 100 s after the last analyte peak and the intensity of ArCl+ was negligible even after injection of a 1% NaCl solution (less than 200 ions s–1). The recovery of all arsenic species in urine was close to 100%. The chromatographic peaks were evaluated by their peak heights and calibration was carried out by the method of standard additions. The calibration graphs were linear for all species (r > 0.999). The limits of detection were 3–6 ng cm–3 for the cations and 7–10 ng cm–3 for the anions in urine.

[1]  J. Caruso,et al.  Elimination of the chloride interference on the determination of arsenic using hydride generation inductively coupled plasma mass spectrometry. , 1992, Journal of chromatographic science.

[2]  H. Roels,et al.  Relation between airborne arsenic trioxide and urinary excretion of inorganic arsenic and its methylated metabolites. , 1992, British journal of industrial medicine.

[3]  J. M. Christensen,et al.  Estimation of the method evaluation function for the determination of hydride-generating arsenic compounds in urine by flow-injection atomic-absorption spectrometry. , 1992, Talanta.

[4]  K. Wolnik,et al.  Arsenic speciation by ion chromatography with inductively coupled plasma mass spectrometric detection. , 1992, The Analyst.

[5]  G. van Belle,et al.  The effect of variable environmental arsenic contamination on urinary concentrations of arsenic species. , 1990, Environmental health perspectives.

[6]  K. Reimer,et al.  Arsenic speciation in the environment , 1989 .

[7]  N. J. Smith,et al.  Urinary arsenic speciation by high-performance liquid chromatography/atomic absorption spectrometry for monitoring occupational exposure to inorganic arsenic , 1987 .

[8]  G. Calzaferri,et al.  The speciation of the chemical forms of arsenic in the biological monitoring of exposure to inorganic arsenic. , 1984, The Science of the total environment.

[9]  E. Marafante,et al.  Metabolism of arsenobetaine in mice, rats and rabbits. , 1983, The Science of the total environment.

[10]  E. Crecelius Changes in the chemical speciation of arsenic following ingestion by man. , 1977, Environmental health perspectives.