Underestimation of the total arsenic concentration by hydride generation techniques as a consequence of the incomplete mineralization of arsenobetaine in acid digestion procedures

被引:49
作者
Slejkovec, Z
van Elteren, JT
Woroniecka, UD
机构
[1] Delft Univ Technol, Interfac Reactor Inst, NL-2629 JB Delft, Netherlands
[2] Jozef Stefan Inst, Dept Environm Sci, Ljubljana, Slovenia
关键词
arsenobetaine; stability; digestion; hydride generation; speciation;
D O I
10.1016/S0003-2670(01)01223-5
中图分类号
O65 [分析化学];
学科分类号
070302 ; 081704 ;
摘要
Individual arsenobetaine (AsB) decomposition products obtained with five different acid digestion procedures (nitric acid/200 degreesC/10 or 30 min, nitric acid/sulphuric acid/300 degreesC/10 or 30 min and nitric acid/sulphuric acid/hydrogen peroxide/300 degreesC/30 min) were determined by high-performance liquid chromatography-(ultraviolet digestion)-hydride generation atomic fluorescence spectrometry (HPLC-(UV)-HGAFS). It was found that AsB was converted to mainly inorganic arsenic, trimethylarsine oxide (TMAO) and dimethylarsinic acid (DMAA), depending on acid digestion procedure; the "stronger" the digestion procedure the more mineralization occurred. The sensitivity of the flow injection-hydride generation atomic fluorescence spectrometry (FI-HGAFS) for each of the decomposition products was also measured which allowed us to calculate the FI-HGAFS response, and thus the total arsenic concentration using arsenate as a quantification standard. Total arsenic concentrations calculated were between 56 and 100% of the initially present AsB, depending on acid digestion procedure. This was completely in accordance with total arsenic concentrations measured so that underestimation of the total arsenic concentration in AsB digests measured by the FI-HGAFS can be fully explained in terms of incomplete mineralization and the lower response of the partly degraded products. (C) 2001 Elsevier Science B.V. All rights reserved.
引用
收藏
页码:277 / 282
页数:6
相关论文
共 8 条
[1]   THE DETERMINATION OF SELENIUM WITH HYDRIDE GENERATION AAS .4. APPLICATION TO COAL ANALYSIS [J].
AGTERDENBOS, J ;
VANELTEREN, JT ;
BAX, D ;
TERHEEGE, JP .
SPECTROCHIMICA ACTA PART B-ATOMIC SPECTROSCOPY, 1986, 41 (04) :303-316
[2]   Analytical methodology for speciation of arsenic in environmental and biological samples [J].
Burguera, M ;
Burguera, JL .
TALANTA, 1997, 44 (09) :1581-1604
[3]  
BYRNE AR, 1974, CROAT CHEM ACTA, V46, P225
[4]   ARSENIC SPECIATION IN THE ENVIRONMENT [J].
CULLEN, WR ;
REIMER, KJ .
CHEMICAL REVIEWS, 1989, 89 (04) :713-764
[5]   Comparison of sample digestion procedures for the determination of arsenic in certified marine samples using the FI-HG-AAS technique [J].
Damkroger, G ;
Grote, M ;
Janssen, E .
FRESENIUS JOURNAL OF ANALYTICAL CHEMISTRY, 1997, 357 (07) :817-821
[6]  
Fecher P, 1998, ATOM SPECTROSC, V19, P204
[7]   Determination of traces of arsenic(III) by anodic stripping voltammetry in solutions, natural waters and biological material [J].
Kopanica, M ;
Novotny, L .
ANALYTICA CHIMICA ACTA, 1998, 368 (03) :211-218
[8]   DETERMINATION OF ARSENIC(III/V) IN AQUEOUS SAMPLES BY NEUTRON-ACTIVATION ANALYSIS AFTER SEQUENTIAL COPRECIPITATION WITH DIBENZYLDITIOCARBAMATE [J].
VANELTEREN, JT ;
DAS, HA ;
DELIGNY, CL ;
AGTERDENBOS, J .
ANALYTICA CHIMICA ACTA, 1989, 222 (01) :159-167