Accurate quantification and transformation of arsenic compounds during wet ashing with nitric acid and microwave assisted heating.

Arsenous acid, dimethylarsinic acid (DMA), methylarsonic acid (MA), arsenic acid, arsenobetaine bromide (AB), trimethylarsine oxide (TMAO), arsenocholine iodide (AC), and tetramethylarsonium iodide (TETRA) were heated in a microwave autoclave with nitric acid to 100-300 degrees C. The arsenic compounds in the digests were separated with anion- and cation-exchange chromatography and determined with an inductively coupled plasma mass spectrometer as arsenic-specific detector. Arsenous acid was completely oxidized to arsenic acid at 100 degrees C. For a complete oxidation of MA and DMA to arsenic acid temperatures > 220 degrees C and > 280 degrees C were necessary. AB decomposed to arsenic acid via TMAO. Complete conversion was only obtained after heating the sample for 90 min to 300 degrees C. For a complete conversion of TMAO similar harsh conditions were necessary. AC was already substantially degraded to TMAO, TETRA and two unknown compounds at 100 degrees C. The unknown arsenic compounds were found only in the digests up to 160 degrees C. Quantitative conversion of AC to arsenic acid went also via TMAO. At temperatures above 220 degrees C TETRA started to convert to TMAO, which then was further converted to arsenic acid. To investigate whether the results obtained for the arsenic standards are transferable to real samples, the certified reference material DORM-2 was also heated in nitric acid with variable digestion temperatures and times. For an almost complete conversion of the AB present in DORM-2 90 min at 300 degrees C were necessary. Total organic carbon (TOC) was less < 0.2% when DORM-2 was heated at temperatures > or = 260 degrees C for 60 min. UV photo-oxidation of DORM-2 was investigated as an alternative sample decomposition. Only 6% of AB was converted to arsenic acid when DORM-2 was irradiated for 2 h at 1000 W. In contrast to microwave heating substantial amounts of MA were observed as degradation product.

[1]  W. Goessler,et al.  Efficiency of oxidation in wet digestion procedures and influence from the residual organic carbon content on selected techniques for determination of trace elementsPresented at the 2002 Winter Conference on Plasma Spectrochemistry, Scottsdale, AZ, USA, January 6???12, 2002. , 2002 .

[2]  J. T. Elteren,et al.  Underestimation of the total arsenic concentration by hydride generation techniques as a consequence of the incomplete mineralization of arsenobetaine in acid digestion procedures , 2001 .

[3]  D. Vélez,et al.  Kinetic study of transformations of arsenic species during heat treatment. , 2001, Journal of agricultural and food chemistry.

[4]  M. Hoenig,et al.  Revisitation of mineralization modes for arsenic and selenium determinations in environmental samples. , 2001, Talanta.

[5]  W. Goessler,et al.  Formation of toxic arsenical in roasted muscles of marine animals , 2001 .

[6]  W. Goessler,et al.  Arsenic compounds in terrestrial organisms. IV. Green plants and lichens from an old arsenic smelter site in Austria , 2000 .

[7]  A. Chatterjee Behaviour of cationic arsenic compounds in a microwave system with nitric acid and hydrogen peroxide , 2000 .

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

[9]  A. Chatterjee Behaviour of anionic arsenic compounds in microwave system with nitric acid and hydrogen peroxide — preliminary laboratory study , 1999 .

[10]  P. Fecher,et al.  Determination of arsenic and selenium in foodstuffs : methods and errors , 1998 .

[11]  W. Goessler,et al.  Arsenobetaine and other arsenic compounds in the National Research Council of Canada Certified Reference Materials DORM 1 and DORM 2 , 1998 .

[12]  A. R. Byrne,et al.  Arsenic Compounds in Higher Fungi , 1997 .

[13]  M. Grote,et al.  Comparison of sample digestion procedures for the determination of arsenic in certified marine samples using the FI-HG-AAS-technique , 1997 .

[14]  H. Matusiewicz,et al.  Comparison of the efficiencies of on-line and high-pressure closed vessel approaches to microwave heated sample decomposition , 1994 .

[15]  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.

[16]  P. Schramel,et al.  Determination of arsenic, antimony, bismuth, selenium and tin in biological and environmental samples by continuous flow hydride generation ICP-AES without gas-liquid separator , 1991 .