Estimation of arsenobetaine in the NIES candidate certified reference material no. 18 human urine by HPLC-ICP-MS using different chromatographic conditions

HPLC-ICP-MS, employing a silica-based LC-SCX cation-exchange column, styrene-divinylbenzene copolymer-based PRP-X100 anion exchange column, an ODS reversed-phase and gel-permeation (polyvinyl alcohol-based resin) GS-220 columns, has been used for the separation, identification, and quantification of arsenic compounds, particularly arsenobetaine (AB), present in NIES candidate certified reference material (CRM) no. 18 human urine. AB is the predominant arsenic species, followed by dimethylarsinic acid, methylarsonic acid and arsenic acid. The peak of each arsenic compound has been validated by spiking of the authentic standard solution to the urine sample and by using the above chromatographic systems. The high concentration of chloride that co-elutes with the arsenic acid from the LC-SCX and with the AB from the GS-220 columns has interfered with the ion signals of arsenic acid and AB, by forming the molecular ions 40 Ar 35 Cl and 38 Ar 37 Cl + in the plasma. Thus, the concentration of AB has been carefully estimated on the GS-220 after extracting the chloride interference ( 37 Cl: 35 Cl = 1:3.1271) by measuring the 40 Ar 37 Cl + . The peak of AB overlapped with the peak of arsenous acid and hindered the estimation of AB on the ODS and PRP-X100 columns. But AB has been baseline separated from the other arsenic compounds and also from the chloride with 20 mM pyridine at pH 2.60 on the LC-SCX. So, the LC-SCX column has been proven and used for the determination of AB in NIES candidate CRM no. 18 human urine. The concentrations of AB, estimated by the standard addition method and found using the LC-SCX and GS-220 columns, are 70.5 ± 5.5 (n = 20) and 71.5 ± 4 μgl -1 (n = 9). The concentration of AB thus found has been applied as the baseline value for the collaborative study to certify the AB in the NIES candidate CRM no. 18 human urine.

[1]  A. Chatterjee Determination of total cationic and total anionic arsenic species in oyster tissue using microwave-assisted extraction followed by HPLC-ICP-MS. , 2000, Talanta.

[2]  W. Kosmus,et al.  Arsenic speciation in human urine reference materials using high-performance liquid chromatography with inductively coupled plasma mass spectrometric detection. , 1999, Journal of trace elements in medicine and biology : organ of the Society for Minerals and Trace Elements.

[3]  F. Bressolle,et al.  Arsenic speciation in humans and food products: a review. , 1999, Journal of chromatographic science.

[4]  M. Astruc,et al.  Speciation of arsenic and selenium compounds by HPLC hyphenated to specific detectors: a review of the main separation techniques. , 1999, Talanta.

[5]  C. Sarzanini Liquid chromatography: a tool for the analysis of metal species. , 1999, Journal of chromatography. A.

[6]  J. Blum,et al.  Trace analyses of arsenic in drinking water by inductively coupled plasma mass spectrometry: high resolution versus hydride generation. , 1999, Analytical chemistry.

[7]  X. Le,et al.  Effect of arsenosugar ingestion on urinary arsenic speciation. , 1998, Clinical chemistry.

[8]  J. M. Christensen,et al.  Speciation measurements by HPLC-HGAAS of dimethylarsinic acid and arsenobetaine in three candidate lyophilized urine reference materials. , 1998, The Analyst.

[9]  M. Moore,et al.  Speciation of arsenic metabolites in the urine of occupational workers and experimental rats using an optimised hydride cold-trapping method. , 1998, The Analyst.

[10]  W. Buchberger,et al.  Advances in detection techniques for ion chromatography , 1997 .

[11]  M. Accominotti,et al.  Arsenic Speciation by Ion-Pair Reversed-Phase Liquid Chromatography with Coupled Amperometric and Ultraviolet Detection , 1996 .

[12]  R. Cornelis,et al.  Arsenic speciation in serum of uraemic patients based on liquid chromatography with hydride generation atomic absorption spectrometry and on-line UV photo-oxidation digestion , 1996 .

[13]  M. Magnuson,et al.  Speciation of arsenic compounds by ion chromatography with inductively coupled plasma mass spectrometry detection utilizing hydride generation with a membrane separator , 1996 .

[14]  J. Edmonds,et al.  Arsenic and Marine Organisms , 1996 .

[15]  J. Gailer,et al.  Metabolism of arsenic compounds by the blue mussel mytilus edulis after accumulation from seawater spiked with arsenic compounds , 1995 .

[16]  P. C. Meier,et al.  Statistical Methods in Analytical Chemistry , 2005 .

[17]  M. Vahter What are the chemical forms of arsenic in urine, and what can they tell us about exposure? , 1994, Clinical chemistry.

[18]  K. Irgolic,et al.  The lon‐chromatographic behavior of arsenite, arsenate, methylarsonic acid and dimethylarsinic acid on the hamilton PRP‐X100 anion‐exchange column , 1994 .

[19]  X. Le,et al.  Human urinary arsenic excretion after one-time ingestion of seaweed, crab, and shrimp. , 1994, Clinical chemistry.

[20]  S. Hansen,et al.  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 , 1993 .

[21]  K. Reimer,et al.  Decomposition of organoarsenic compounds by using a microwave oven and subsequent determination by flow injection‐hydride generation‐atomic absorption spectrometry , 1992 .

[22]  M. Morita,et al.  Determination of arsenic species in biological and environmental samples (Technical Report) , 1992 .

[23]  S. Hansen,et al.  Separation of seven arsenic compounds by high-performance liquid chromatography with on-line detection by hydrogen–argon flame atomic absorption spectrometry and inductively coupled plasma mass spectrometry , 1992 .

[24]  K. Fuwa,et al.  Selenium and arsenic in biology: their chemical forms and biological functions. , 1992, Advances in biophysics.

[25]  J. M. Christensen,et al.  Effect of seafood consumption on the urinary level of total hydride-generating arsenic compounds. Instability of arsenobetaine and arsenocholine. , 1992, The Analyst.

[26]  M. Morita,et al.  Speciation of Arsenic by Reversed-Phase High Performance Liquid Chromatography-Inductively Coupled Plasma Mass Spectrometry , 1989 .

[27]  M. Morita,et al.  Speciation of Arsenic Compounds in Marine Life by High Performance Liquid Chromatography Combined with Inductively Coupled Argon Plasma Atomic Emission Spectrometry , 1987 .

[28]  G. Horlick,et al.  Background Spectral Features in Inductively Coupled Plasma/Mass Spectrometry , 1986 .

[29]  T. Kaise,et al.  The acute toxicity of arsenobetaine , 1985 .

[30]  M. Vahter,et al.  A rapid method for the selective analysis of total urinary metabolites of inorganic arsenic. , 1981, Scandinavian journal of work, environment & health.

[31]  K. Yasuda,et al.  Identification of Arsenobetaine, a Water Soluble Organo-arsenic Compound in Muscle and Liver of a Shark, Prionace glaucus , 1980 .

[32]  G. Lunde Water Soluble Arseno-organic Compounds in Marine Fishes , 1969, Nature.

[33]  G. Kortüm,et al.  Disssociation constants of organic acids in aqueous solution , 1960 .

[34]  A. Chapman On the presence of compounds of arsenic in marine crustaceans and shell fish , 1926 .