Determination of inorganic selenium species in rain and sea waters by anion exchange chromatography-hydride generation-inductively-coupled plasma-dynamic reaction cell-mass spectrometry (AEC-HG-ICP-DRC-MS)

被引:46
作者
Wallschläger, D [1 ]
London, J [1 ]
机构
[1] Trent Univ, Environm & Resource Studies Program, Peterborough, ON K9J 7B8, Canada
关键词
D O I
10.1039/b401616e
中图分类号
O65 [分析化学];
学科分类号
070302 ; 081704 ;
摘要
The inorganic selenium ( Se) species selenite, selenate and selenocyanate in waters are determined by anion exchange chromatography-hydride generation-inductively-coupled plasma-dynamic reaction cell-mass spectrometry (AEC-HG-ICP-DRC-MS) with instrumental detection limits of 0.15, 0.27 and 0.19 ng Se L-1, respectively. Sea water has to be diluted ten-fold prior to analysis to overcome chromatographic interferences, so practical method detection limits for this matrix are around 2 - 3 ng Se L-1. The species are separated by gradient elution with NaOH and converted to SeH2 by prereduction with iodide in HCl at 100 degreesC, followed by subsequent reaction with KBH4, before the SeH2 is introduced into the plasma after aerosol and water vapor removal. Quantification using the main Se isotope 80 Se was possible by employing, for the first time, a mixture of two reaction gases: methane for eliminating the Ar-40(2)+ dimer, and ammonia for eliminating a significant interference from HBr+ caused by bromine present in the employed reagents. Oxidation of Se+ to SeO+ using O-2 as the reaction gas was also attempted, but yielded incomplete ( 10 - 25%) conversion. In addition, the HBr+ interference was not eliminated by this approach, because the interfering molecular ion was also oxidized to HBrO+. The optimized method was successfully applied to the determination of Se speciation in uncontaminated sea water and in rain water. In rain water, an unidentified Se species was detected, which we believe to be a monomethylated Se species.
引用
收藏
页码:1119 / 1127
页数:9
相关论文
共 23 条
[1]   ARSENIC AND SELENIUM SPECIES IN THE OXIC AND ANOXIC WATERS OF THE OSLOFJORD, NORWAY [J].
ABDULLAH, MI ;
SHIYU, Z ;
MOSGREN, K .
MARINE POLLUTION BULLETIN, 1995, 31 (1-3) :116-126
[2]   Evasion of selenium to the atmosphere via biomethylation processes in the Gironde estuary, France [J].
Amouroux, D ;
Donard, OFX .
MARINE CHEMISTRY, 1997, 58 (1-2) :173-188
[3]   Reaction chemistry and collisional processes in multipole devices for resolving isobaric interferences in ICP-MS [J].
Bandura, DR ;
Baranov, VI ;
Tanner, SD .
FRESENIUS JOURNAL OF ANALYTICAL CHEMISTRY, 2001, 370 (05) :454-470
[4]   Detection of metals in proteins by means of polyacrylamide gel electrophoresis and laser ablation-inductively coupled plasma-mass spectrometry:: Application to selenium [J].
Chéry, CC ;
Günther, D ;
Cornelis, R ;
Vanhaecke, F ;
Moens, L .
ELECTROPHORESIS, 2003, 24 (19-20) :3305-3313
[5]   Metalloids in the high latitude north Atlantic Ocean: Sources and internal cycling [J].
Cutter, GA ;
Cutter, LS .
MARINE CHEMISTRY, 1998, 61 (1-2) :25-36
[6]   THE ESTUARINE BEHAVIOR OF SELENIUM IN SAN-FRANCISCO BAY [J].
CUTTER, GA .
ESTUARINE COASTAL AND SHELF SCIENCE, 1989, 28 (01) :13-34
[7]   SPECIES DETERMINATION OF SELENIUM IN NATURAL-WATERS [J].
CUTTER, GA .
ANALYTICA CHIMICA ACTA, 1978, 98 (01) :59-66
[8]   SELENIUM IN WESTERN ATLANTIC PRECIPITATION [J].
CUTTER, GA ;
CHURCH, TM .
NATURE, 1986, 322 (6081) :720-722
[9]   Selenium and its redox speciation in rainwater from sites of Valparaiso region in Chile, impacted by mining activities of copper ores [J].
De Gregori, I ;
Lobos, MG ;
Pinochet, H .
WATER RESEARCH, 2002, 36 (01) :115-122
[10]  
Donat J.R., 1994, TRACE ELEMENTS NATUR, V1st