Facultad de Química, Pontificia Universidad Católica de Chile, Vicuña Mackenna 4860, Santiago-7820436, Chile.
Talanta. 2012 Sep 15;99:119-24. doi: 10.1016/j.talanta.2012.05.028. Epub 2012 Jun 4.
An adsorptive stripping voltammetric (AdSV) method is presented for the simultaneous determination of Pb(II) and Cd(II) at trace levels in natural waters, based on metal complexation with pyrogallol red (PR) and subsequent adsorptive deposition on a Nafion-mercury coated glassy carbon electrode (NHgFE). Pyrogallol red forms complexes with a metal:ligand stoichiometry of 1:1 with Pb(II) and of 1:2 with Cd(II). Optimal analytical conditions were pH 4.0 (acetate buffer); C(PR)=2.8 μmol L(-1); E(ads)=-0.40 V vs. Ag/AgCl; t(ads)=100 s. The linear calibration curves ranged from 1.0 μg L(-1) to 16.0 μg L(-1) for Pb(II) and from 1.0 μg L(-1) to 13.0 μg L(-1) for Cd(II). The detection limits (S/N=3) were 0.05 μg L(-1) for Pb(II) and 0.01 μg L(-1) for Cd(II). The relative standard deviation was 1.0% and 2.0% (n=7), respectively, for a solution containing 5.0 μg L(-1) Pb(II) and Cd(II). The method was validated by determining Pb(II) and Cd(II) in certified reference waste water (SPS-WW1). Finally, the method was applied to the determination of Pb(II) and Cd(II) in commercial mineral water samples after UV digestion.
一种基于与没食子酸红(PR)金属络合随后在 Nafion-汞涂覆玻碳电极(NHgFE)上吸附沉积的吸附溶出伏安法(AdSV),用于同时测定天然水中痕量水平的 Pb(II) 和 Cd(II)。没食子酸红与 Pb(II) 形成 1:1 的金属-配体络合物,与 Cd(II) 形成 1:2 的络合物。最佳分析条件为 pH 4.0(醋酸盐缓冲液);C(PR)=2.8 μmol L(-1);E(ads)=-0.40 V vs. Ag/AgCl;t(ads)=100 s。对于 Pb(II),线性校准曲线的范围从 1.0 μg L(-1) 到 16.0 μg L(-1);对于 Cd(II),线性校准曲线的范围从 1.0 μg L(-1) 到 13.0 μg L(-1)。Pb(II) 和 Cd(II) 的检测限(S/N=3)分别为 0.05 μg L(-1) 和 0.01 μg L(-1)。对于含有 5.0 μg L(-1) Pb(II) 和 Cd(II)的溶液,相对标准偏差分别为 1.0%和 2.0%(n=7)。该方法通过测定认证参考废水(SPS-WW1)中的 Pb(II) 和 Cd(II) 得到验证。最后,该方法应用于 UV 消解后商业矿泉水样品中 Pb(II) 和 Cd(II) 的测定。