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基于电化学聚合的水中毒莠定脂质体免疫传感器

[Liposome immunosensor for picloram in water based on electrochemical polymerization].

作者信息

Li Ting, Zeng Guang-ming, Tang Lin, Zhang Yi, Li Yuan-ping

机构信息

College of Environmental Science and Engineering, Hunan University, Changsha 410082, China.

出版信息

Huan Jing Ke Xue. 2008 Jun;29(6):1660-5.

Abstract

A "sandwich-type" immunosensor for the determination of picloram in water environment was developed based on the immunoliposomes prepared by crosslinking rabbit antibody against picloram (anti-picloram) and potassium ferrocyanide-encapsulated liposomes with glutaraldehyde. The working conditions including modification components on the electrode were optimized. The best performance is obtained using 0.5% of Nafion, 10 mg x mL(-1) of multiwalled carbon nanotubes (MWCNTs) and 50 microg x mL(-1) of anti-picloram. The preparation and detection process of immunosensor was as follows. Cyclic voltammetry was applied to urge the electrochemical polymerization of 3,4-ethylenedioxythiophene (EDOT) and the anti-picloram was immobilized on the modified glassy carbon electrode (GCE). Then the electrode was incubated with the analytes and immunoliposomes sequentially. The bound liposomes were lysed with TritonX-100, and square-wave voltammetry was applied to determine current response of picloram concentration. The whole process was able to be completed in 70 min. The immunosensor has good reproductivity after being soaked in 0.1 mol x L(-1) of H3PO4 in 5 min. The result shows that lower detection limit for picloram is 10(-10) mol x L(-1) with linear range of 10(-10)-10(-4) mol x L(-1), which meets the detection requirement of picloram for the safety of drinking water.

摘要

基于戊二醛交联抗毒莠定兔抗体(抗毒莠定)和包封亚铁氰化钾的脂质体制备的免疫脂质体,开发了一种用于测定水环境中毒莠定的“三明治型”免疫传感器。优化了包括电极修饰成分在内的工作条件。使用0.5%的Nafion、10 mg·mL⁻¹的多壁碳纳米管(MWCNTs)和50 μg·mL⁻¹的抗毒莠定可获得最佳性能。免疫传感器的制备和检测过程如下。采用循环伏安法促使3,4-乙撑二氧噻吩(EDOT)进行电化学聚合,并将抗毒莠定固定在修饰玻碳电极(GCE)上。然后将电极依次与分析物和免疫脂质体孵育。用TritonX-100裂解结合的脂质体,并采用方波伏安法测定毒莠定浓度的电流响应。整个过程可在70分钟内完成。免疫传感器在0.1 mol·L⁻¹的H₃PO₄中浸泡5分钟后具有良好的重现性。结果表明,毒莠定的最低检测限为10⁻¹⁰ mol·L⁻¹,线性范围为10⁻¹⁰ - 10⁻⁴ mol·L⁻¹,满足毒莠定对饮用水安全的检测要求。

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