聚(azulenedta)类丝网印刷修饰电极上汞离子的伏安检测

G. Buica, Georgiana-Luiza Tatu (Arnold), E. Ungureanu, G. Vasile
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摘要

近年来,水样中不同有毒金属(As、Cd、Cu、Hg、Ni、Pb)的检测得到了广泛的应用。经典的分析方法(ICP-MS、石墨炉AAS、超声雾化器ICP-EOS)不仅需要较长的分析时间(样品的预处理和分析),而且由于昂贵的设备、方法验证过程的相关成本和合格的人员,所涉及的成本也较高。使用改性电极对废水样品中的痕量金属进行分析代表了一种现代方法,可以提供准确,快速的结果,具有选择性和灵敏度。因此,我们在这里介绍了先前获得的基于聚(2,2 ' -(乙烷-1,2-二基双((2-(azulen-2-氨基)-2-氧乙基)azanediyl))二乙酸(polyL)的玻璃碳修饰电极的发展。为了分析水样品中的Hg(II)离子含量,使用了一种由聚l选择性络合聚合物膜修饰的碳丝网印刷修饰电极(spe)与便携式恒电位器耦合组成的组装系统。Hg(II)离子的检测是通过在开路中化学积累,然后使用差分脉冲伏安法技术阳极剥离来完成的。分析方法的校准曲线位于20 ~ 150 ppb范围内(y = 0.0051x + 0.123, R2 = 0.9951),检出限为6 ppb。校准曲线的下限精密度为20%,上限精密度为10.5%。该方法的新颖之处不仅在于分析成本低,而且还在于可以使用小型便携式设备提供有关废水中汞(II)浓度的实时可靠信息。
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Voltammetric Detection of Mercury Ions at Poly(azulene-EDTA)-like Screen Printed Modified Electrodes
In recent years, many applications have been developed for the detection of different toxic metals (As, Cd, Cu, Hg, Ni, Pb) in water samples. The classic analytical methods (ICP-MS, AAS with graphite furnace, ICP-EOS with ultrasonic nebulizer) not only require a longer analysis time (pretreatment of the sample and analysis), but also the costs involved are higher as a result of expensive equipment, costs associated with the method validation process and qualified staff. The use of modified electrodes for trace metals analysi from wastewater samples represents a modern approach which can provide accurate, fast results with selectivity and sensitivity. Thus, here we present the development of the previously obtained glassy carbon-modified electrodes based on poly(2,2′-(ethane-1,2-diylbis((2-(azulen-2-ylamino)-2-oxoethyl)azanediyl))diacetic acid, (polyL) in laboratory-scale studies. In order to analyze Hg(II) ion content from aqueous samples, an assembly system made of carbon screen-printed modified electrodes (SPEs) modified with polyL selective complexing polymeric films coupled with a portable potentiostat was used. The detection of Hg(II) ions was accomplished by chemical accumulation in an open circuit followed by anodic stripping using the differential pulse voltammetry technique. The calibration curve of the analytical method was situated in the range of 20 ppb to 150 ppb (y = 0.0051x + 0.123, R2 = 0.9951), with a detection limit of 6 ppb. The precision value for the lower limit of the calibration curve was 20%, while for the upper limit, the value was 10.5%. The novelty of the method consists not only of the low cost of the analysis, but also of the possibility to provide real-time reliable information about the Hg(II) concentration in wastewater using a small and portable device.
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