Leopold Kerstin, Foulkes Michael, Worsfold Paul J
Biogeochemistry and Environmental Analytical Chemistry Group, School of Earth, Ocean and Environmental Sciences, University of Plymouth, Portland Square, Plymouth PL4 8AA, United Kingdom.
Anal Chem. 2009 May 1;81(9):3421-8. doi: 10.1021/ac802685s.
A novel solid-phase preconcentration method is reported, using in-house gold-coated silica adsorbent packed in a microcolumn, for the determination of dissolved mercury in natural waters by atomic fluorescence spectrometry (AFS). The adsorbent was prepared by chemical reduction of a Au(III) solution with hydroxylamine in the presence of suspended silica particles. The resulting Au nanoparticles on the silica surface were highly efficient for adsorbing different mercury species from acidified waters without additional reagents. The acidified aqueous samples were passed over the microcolumn, either incorporated in a fully automated flow injection (FI) system directly coupled to the AFS or as part of a portable FI system for in situ preconcentration. After rinsing and drying of the column, Hg(0) was released by heating and directed to the AFS cell for quantification. The method offers significant advantages because no reagents are needed for species conversion, preconcentration, sample storage, or desorption and therefore the risk of contamination is minimized and blank values are lowered. This results in a low detection limit of 180 pg L(-1) using a sample volume of only 7 mL and good reproducibility, with relative standard deviations <3.2% (n = 10, [Hg] = 5 ng L(-1)). Recoveries were all >90% in spiked river waters (spiked [Hg] = 0, 1, 5, 10 ng L(-1)), and the experimental value for the certified reference material ORMS-4 (elevated mercury in river water) was 22.3 +/- 2.6 ng Hg L(-1) which was in good agreement with the certified value of 22.0 +/- 1.6 ng Hg L(-1) (recovery = 101%). The method was successfully applied to seven different natural waters and wastewaters ([Hg] 0.5-4.6 ng L(-1)) from south west England.
本文报道了一种新型固相预富集方法,该方法使用填充在微柱中的自制金包覆硅胶吸附剂,通过原子荧光光谱法(AFS)测定天然水中的溶解汞。吸附剂是在悬浮硅胶颗粒存在下,用羟胺化学还原Au(III)溶液制备而成。硅胶表面生成的金纳米颗粒无需额外试剂就能高效吸附酸化水中的不同汞形态。酸化后的水样通过微柱,微柱可直接集成到与AFS直接联用的全自动流动注射(FI)系统中,也可作为便携式FI系统的一部分用于现场预富集。柱冲洗和干燥后,通过加热释放Hg(0)并导入AFS池进行定量分析。该方法具有显著优势,因为在形态转换、预富集、样品储存或解吸过程中无需试剂,因此污染风险降至最低,空白值降低。这使得仅使用7 mL样品体积时检测限低至180 pg L(-1),且重现性良好,相对标准偏差<3.2%(n = 10,[Hg] = 5 ng L(-1))。加标河水(加标[Hg] = 0、1、5、10 ng L(-1))中的回收率均>90%,认证参考物质ORMS-4(河水中汞含量升高)的实验值为22.3±2.6 ng Hg L(-1),与认证值22.0±1.6 ng Hg L(-1)(回收率 = 101%)高度吻合。该方法成功应用于英格兰西南部的七种不同天然水和废水([Hg] 0.5 - 4.6 ng L(-1))。