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使用丝网印刷碳和改性碳糊电极对来自 Eerste-Kuils 河流系统的河水进行痕量金属离子的剥离伏安法测量。

Stripping voltammetric measurement of trace metal ions using screen-printed carbon and modified carbon paste electrodes on river water from the Eerste-Kuils River System.

机构信息

NRE, Council for Scientific and Industrial Research (CSIR), Stellenbosch, South Africa.

出版信息

J Environ Sci Health A Tox Hazard Subst Environ Eng. 2011;46(1):17-32. doi: 10.1080/10934529.2011.526075.

Abstract

Screen-printed carbon electrodes (SPCEs) and carbon paste electrodes (CPEs) were prepared as "mercury-free" electrochemical sensors for the determination of trace metal ions in aqueous solutions. SPCEs were coated with conducting polymer layers of either polyaniline (PANI), or polyaniline-poly(2,2'-dithiodianiline) (PANI-PDTDA). Furthermore, CPEs containing electroactive compounds with reactivity towards metal ions were employed to obtain enhanced selectivity. Optimised experimental conditions for Hg(2+), Pb(2+), Ni(2+) and Cd(2+) determination included the supporting electrolyte concentration, deposition potential (E(d)) and accumulation time (t(acc)). For the modified carbon paste sensors (MCPEs) it was found that -400 mV is an adequate deposition potential and an accumulation time of 120 s was adequate for the determination using the different constructed electrodes. Initial results showed linearity in the examined concentration range between 1 × 10(-9) M and 1 × 10(-6) M using the SPCE/PANI-PDTDA sensor on laboratory prepared standard solutions, while good selectivity for the different metal ions were obtained. Furthermore, the limit of detection (LOD) was determined for each of the sensors and for the SPCE/PANI-PDTDA sensor it was found to be 2.2 × 10(-13) M, while for the SPCE/PANI sensor the LOD was determined to be 8.4 × 10(-11) M. The MCPE sensors also showed good linearity between the concentration range of 1 × 10(-3) to 1 × 10(-9) M. The LOD values for the various MCPE sensors, were found to be Hg(II) - 1.3 × 10(-7) M; Cd(II) - 2.9 × 10(-7) M; Ni(II) - 3.2 × 10(-7) M; and Pb(II) - 1.7 × 10(-7) M for the CPE/PANI-PDTDA sensor. For the CPE/PANI sensor the LOD values were Hg(II) - 1.5 × 10(-5) M; Cd(II) - 8.6 × 10(-7) M; Ni(II) - 9.5 × 10(-7) M; and Pb(II) - 1.3 × 10(-6) M. For the CPE/MBT sensor the LOD values were Hg(II) - 3.8 × 10(-5) M; Cd(II) - 1.4 × 10(-6) M; Ni(II) - 1 × 10(-6) M; and Pb(II) - 6.3 × 10(-5) M. Very low detection was obtained for the SPCE/PANI-PDTDA sensor in Hg(2+) determination, while the MCPE sensors delivered sensitive simultaneous detection for Hg(2+), Pb(2+), Ni(2+) and Cd(2+) metal ions.

摘要

丝网印刷碳电极(SPCEs)和碳糊电极(CPEs)被制备为“无汞”电化学传感器,用于测定水溶液中的痕量金属离子。SPCEs 涂有导电聚合物层,分别为聚苯胺(PANI)或聚苯胺-聚(2,2'-二硫代二苯胺)(PANI-PDTDA)。此外,含有对金属离子具有反应性的电活性化合物的 CPEs 被用于获得增强的选择性。优化的实验条件对于 Hg(2+),Pb(2+),Ni(2+)和 Cd(2+)的测定包括支持电解质浓度,沉积电位(E(d))和积累时间(t(acc))。对于修饰的碳糊传感器(MCPEs),发现-400 mV 是合适的沉积电位,对于使用不同构建的电极进行测定,120 s 的积累时间是足够的。初步结果表明,使用实验室制备的标准溶液,在 SPCE/PANI-PDTDA 传感器上,在 1×10(-9)M 至 1×10(-6)M 的检测范围内具有线性关系,而对于不同的金属离子获得了良好的选择性。此外,还确定了每个传感器的检测限(LOD),对于 SPCE/PANI-PDTDA 传感器,LOD 为 2.2×10(-13)M,而对于 SPCE/PANI 传感器,LOD 为 8.4×10(-11)M。MCPE 传感器在 1×10(-3)至 1×10(-9)M 的浓度范围内也显示出良好的线性关系。对于各种 MCPE 传感器,LOD 值分别为 Hg(II)-1.3×10(-7)M;Cd(II)-2.9×10(-7)M;Ni(II)-3.2×10(-7)M;Pb(II)-1.7×10(-7)M 对于 CPE/PANI-PDTDA 传感器。对于 CPE/PANI 传感器,LOD 值分别为 Hg(II)-1.5×10(-5)M;Cd(II)-8.6×10(-7)M;Ni(II)-9.5×10(-7)M;Pb(II)-1.3×10(-6)M。对于 CPE/MBT 传感器,LOD 值分别为 Hg(II)-3.8×10(-5)M;Cd(II)-1.4×10(-6)M;Ni(II)-1×10(-6)M;Pb(II)-6.3×10(-5)M。对于 SPCE/PANI-PDTDA 传感器,在 Hg(2+)测定中获得了非常低的检测,而 MCPE 传感器则提供了对 Hg(2+),Pb(2+),Ni(2+)和 Cd(2+)金属离子的灵敏同时检测。

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