Delgado Alejandra, Prieto Ailette, Zuloaga Olatz, de Diego Alberto, Madariaga Juan Manuel
Kimika Analitikoa Saila, Euskal Herriko Unibertsitatea, 644 P.K., E-48080 Bilbao, Spain.
Anal Chim Acta. 2007 Jan 16;582(1):109-15. doi: 10.1016/j.aca.2006.08.051. Epub 2006 Sep 1.
Production of artifact methylmercury (MeHg(+)) during the analysis of two certified reference sediments, CRM-580 and IAEA-405, was investigated. Leaching of the analyte from the solid sample was achieved by ultrasound assisted acidic extraction. The aqueous leachate was either ethylated (NaBEt(4)) or phenylated (NaBPh(4)) using acetic/acetate or citric/citrate to buffer the solution. Preconcentration of the volatile compounds was carried out by extraction with an organic solvent (n-hexane) or solid phase microextraction (SPME). MeHg(+) was finally separated and detected by gas chromatography with atomic emission or mass spectrometry detection (GC-MIP-AED or GC-MS). In all the cases the concentrations obtained for MeHg(+) in the CRM-580 were significantly higher than the certified value. For the IAEA-405, however, the MeHg(+) concentration found was always statistically indistinguishable from the certified value. Experiments were also conducted with synthetic samples, such as aqueous mixtures of MeHg(+) and inorganic mercury (Hg(2+)) or silica-gel spiked with both compounds. The methylation rates found (defined as the percentage of Hg(2+) present in the sample which methylates to give artifact MeHg(+)) ranged from not observable (in certain synthetic aqueous mixtures) to 0.57% (analysis of CRM-580 under certain conditions). As the amount of Hg(2+) available in the sample seems to be the main factor controlling the magnitude of the artifact, several experiments were conducted using an ionic exchange resin (Dowex M-41) in order to minimise the concentration of this chemical in the reaction medium. First, a hydrochloric leachate of the sample was passed through a microcolumn packed with the exchanger. Second, the resin was mixed with the sample prior to extraction with HCl. In both cases, the predominant Hg(2+) species, HgCl(4)(2-), was adsorbed on the resin, whereas MeHg(+), mainly as MeHgCl, remained in solution. Following the second option, a new method to analyse MeHg(+) in conflictive matrices like certain sediments was proposed. This approach produced better results for the CRM-580, but a MeHg(+) concentration slightly, but statistically significant, higher than the reference value was still obtained.
研究了在分析两种标准参考沉积物CRM - 580和IAEA - 405过程中人为甲基汞(MeHg(+))的产生情况。通过超声辅助酸性萃取实现固体样品中分析物的浸出。使用乙酸/乙酸盐或柠檬酸/柠檬酸盐缓冲溶液,对水相浸出液进行乙基化(NaBEt(4))或苯基化(NaBPh(4))。通过用有机溶剂(正己烷)萃取或固相微萃取(SPME)对挥发性化合物进行预浓缩。MeHg(+)最终通过气相色谱与原子发射或质谱检测(GC - MIP - AED或GC - MS)进行分离和检测。在所有情况下,CRM - 580中获得的MeHg(+)浓度均显著高于认证值。然而,对于IAEA - 405,所发现的MeHg(+)浓度在统计学上与认证值始终无显著差异。还对合成样品进行了实验,例如MeHg(+)和无机汞(Hg(2+))的水相混合物或同时添加这两种化合物的硅胶。所发现的甲基化率(定义为样品中甲基化生成人为MeHg(+)的Hg(2+)所占的百分比)范围从不可观察到(在某些合成水相混合物中)到0.57%(在某些条件下对CRM - 580的分析)。由于样品中可用的Hg(2+)量似乎是控制人为产物量的主要因素,为了使反应介质中这种化学物质的浓度最小化,使用离子交换树脂(Dowex M - 41)进行了若干实验。首先,将样品的盐酸浸出液通过填充有该交换剂的微柱。其次,在使用HCl萃取之前,将树脂与样品混合。在这两种情况下,主要的Hg(2+)物种HgCl(4)(2-)被吸附在树脂上,而MeHg(+)主要以MeHgCl的形式留在溶液中。遵循第二种方法,提出了一种分析某些沉积物等复杂基质中MeHg(+)的新方法。这种方法对CRM - 580产生了更好的结果,但仍获得了略高于参考值但在统计学上显著的MeHg(+)浓度。