Vereda Alonso E, Siles Cordero M T, García de Torres A, Cañada Rudner P, Cano Pavón J M
Department of Analytical Chemistry, Faculty of Sciences, University of Málaga, E-29071 Málaga, Spain.
Talanta. 2008 Oct 19;77(1):53-9. doi: 10.1016/j.talanta.2008.05.053. Epub 2008 Jun 8.
An on-line inorganic and organomercury species separation, preconcentration and determination system consisting of cold vapor atomic absorption spectrometry (CV-AAS or CV-ETAAS) coupled to a flow injection (FI) method was studied. The inorganic mercury species was retained on a column (i.d., 3 mm; length 3 cm) packed to a height of 0.7 cm with a chelating resin aminopropyl-controlled pore glass (550 A) functionalized with [1,5-bis (2 pyridyl)-3-sulphophenyl methylene thiocarbonohydrazyde] placed in the injection valve of a simple flow manifold. Methylmercury is not directly determined. Previous oxidation of the organomercurial species permitted the determination of total mercury. The separation of mercury species was obtained by the selective retention of inorganic mercury on the chelating resin. The difference between total and inorganic mercury determined the organomercury content in the sample. The inorganic mercury was removed on-line from the microcolumn with 6% (m/v) thiourea. The mercury cold vapor generation was performed on-line with 0.2% (m/v) sodium tethrahydroborate and 0.05% (m/v) sodium hydroxide as reducing solution. The determination was performed using CV-AAS and CV-ETAAS, both approaches have been used and compared for the speciation of mercury in sea food. A detection limit of 10 and 6 ng l(-1) was achieved for CV-AAS and CV-ETAAS, respectively. The precision for 10 replicate determinations at the 1 microg l(-1) Hg level was 3.5% relative standard deviation (R.S.D.), calculated from the peak heights obtained. Both approaches were validated with the use of two certified reference materials and by spiking experiments. By analyzing the two biological certified materials, it was evident that the difference between the total mercury and inorganic mercury corresponds to methylmercury. The concentrations obtained by both techniques were in agreement with the certified values or with differences of the certified values for total Hg(2+) and CH(3)Hg(+), according to the t-test for a 95% confidence level. It is amazing how this very simple method is able to provide very important information on mercury speciation.
研究了一种在线无机和有机汞物种分离、预富集和测定系统,该系统由与流动注射(FI)方法联用的冷蒸气原子吸收光谱法(CV-AAS或CV-ETAAS)组成。无机汞物种保留在一根内径3 mm、长度3 cm、填充高度0.7 cm的柱中,该柱填充有经[1,5-双(2-吡啶基)-3-磺苯基亚甲基硫代碳酰肼]官能化的螯合树脂氨丙基可控孔径玻璃(550 Å),放置在简单流动歧管的进样阀中。甲基汞不直接测定。有机汞物种预先氧化后可测定总汞。汞物种的分离是通过无机汞在螯合树脂上的选择性保留实现的。总汞与无机汞的差值决定了样品中有机汞的含量。用6%(m/v)硫脲在线从微柱上除去无机汞。用0.2%(m/v)硼氢化四钠和0.05%(m/v)氢氧化钠作为还原溶液在线进行汞冷蒸气发生。使用CV-AAS和CV-ETAAS进行测定,两种方法都已用于海产品中汞形态分析并进行了比较。CV-AAS和CV-ETAAS的检测限分别为10和6 ng l⁻¹。在1 μg l⁻¹汞水平下进行10次重复测定的精密度为相对标准偏差(R.S.D.)3.5%,由获得的峰高计算得出。两种方法都通过使用两种有证标准物质和加标实验进行了验证。通过分析两种生物有证物质,很明显总汞与无机汞的差值对应于甲基汞。根据95%置信水平的t检验,两种技术获得的浓度与总Hg²⁺和CH₃Hg⁺的有证值或有证值的差值一致。令人惊讶的是,这种非常简单的方法能够提供关于汞形态的非常重要的信息。