Heitland Peter, Köster Helmut D
Medical Laboratory Bremen, Haferwende 12, D-28357 Bremen, Germany.
J Anal Toxicol. 2008 May;32(4):308-14. doi: 10.1093/jat/32.4.308.
A fast and reliable high-pressure liquid chromatography (HPLC)-inductively coupled plasma-mass spectrometry (ICP-MS) routine method was developed for the determination of inorganic arsenic [As(III) and As(V)], organic monomethylarsonate [MMA(V)], dimethylarsinate [DMA(V)], and arsenobetaine (As-B) in human urine. The complete method validation is described, including internal and external quality assurance. Limits of quantification for the As species are 0.1 microg/L, which is sufficient to determine background concentrations of the arsenic species in human urine. Additionally, total As in all urine samples was determined by conventional ICP-MS. Mean concentrations for 82 non-exposed inhabitants from northern Germany are 12.7, 5.9, 4.0, 0.23, 0.52, and 0.17 microg/L for total As, As-B, DMA(V), As(III), MMA(V), and As(V), respectively. Approximately 15% of the total As was not identified by the anion exchange HPLC-ICP-MS method, and could be other As metabolites in urine. Two case studies underline the need for As speciation, especially when total urinary arsenic concentrations are elevated. In the first case, we investigated the effect of seafood consumption on the concentration of different arsenic species in urine for different persons. A maximum enhancement of total As from 1 up to 2,200 microg/L (2,000 microg/L for As-B) was observed after a normal fish meal. The second case describes the exposure of a 7-year-old child to As(III) by inhalation of calcium arsenite powder. Five hours after exposure, the concentrations in the child's urine for As-B, DMA(V), As(III), MMA(V), and As(V) were < 0.1, 189, 304, 229, and 27 microg/L, respectively, and these concentrations were reduced to normal background values after 4 days.
建立了一种快速可靠的高压液相色谱(HPLC)-电感耦合等离子体质谱(ICP-MS)常规方法,用于测定人尿中的无机砷[As(III)和As(V)]、有机一甲基胂酸[MMA(V)]、二甲基胂酸[DMA(V)]和砷甜菜碱(As-B)。描述了完整的方法验证,包括内部和外部质量保证。各种砷形态的定量限为0.1μg/L,足以测定人尿中砷形态的背景浓度。此外,通过常规ICP-MS测定所有尿样中的总砷。来自德国北部的82名未接触者的总砷、As-B、DMA(V)、As(III)、MMA(V)和As(V)的平均浓度分别为12.7、5.9、4.0、0.23、0.52和0.17μg/L。阴离子交换HPLC-ICP-MS方法未鉴定出约15%的总砷,可能是尿中的其他砷代谢物。两个案例研究强调了砷形态分析的必要性,尤其是当尿中总砷浓度升高时。在第一个案例中,我们研究了食用海鲜对不同人群尿中不同砷形态浓度的影响。正常食用鱼餐后,观察到总砷最大增幅从1μg/L增至2200μg/L(As-B为2000μg/L)。第二个案例描述了一名7岁儿童因吸入亚砷酸钙粉末而接触As(III)的情况。接触5小时后,儿童尿中As-B、DMA(V)、As(III)、MMA(V)和As(V)的浓度分别<0.1、189、304、229和27μg/L,4天后这些浓度降至正常背景值。