机构地区: 北京工业大学环境与能源工程学院
出 处: 《分析化学》 2013年第9期1353-1358,共6页
摘 要: 将核壳型Fe3O4@Au磁性纳米粒子修饰在丝网印刷工作电极表面,再通过纳米金和微囊藻毒素-(亮氨酸-精氨酸)抗体(anti-MCLR)之间的吸附作用,将抗体固定于电极表面,以牛血清白蛋白(BSA)封闭非特异性吸附位点,制得了检测MCLR的电流型免疫传感器。该传感器基于直接竞争的免疫分析模式,以辣根过氧化物酶偶联的微囊藻毒素(MCLR-HRP)为标记物,用差分脉冲伏安法检测微囊藻毒素,在优化的实验条件下,此免疫传感器响应的峰电流值与微囊藻毒素浓度在0.79~12.9μg/L范围内呈良好的线性关系,检测限为0.38μg/L。对实际水样进行了微囊藻毒素的加标回收实验,回收率在95%~107%之间。此免疫传感器具有测定速度快、灵敏高、携带方便等优点。 The coreshell Fe3O4@Au magnetic nanoparticles were modified onto the screen-printed working electrode surface,and the antibody of microcystin-(leucine-arginine)(anti-MCLR) was immobilized on the modified electrode surface by the adsorption between Au nanoparticles and the antibody.Subsequently,bovine serum albumin(BSA) was used to block the non-specific adsorption sites of the immunosensor to obtain immunosensor for the detection of MCLR.The immunosensor was based on the direct competitive immunoassay format between the labeled agent of horseradish peroxidase-conjugated MCLR(MCLR-HRP) and the analyte.MCLR was determined by differential pulse voltammetry(DPV).Under the optimal experimental conditions,the peak current response decreased proportionally with the concentration of MCLR in the range of 0.79-12.90 μg/L with a detection limit of 0.38 μg/L.The developed biosensor was used to determine MCLR in real water samples,and the recoveries of standard additions were in the range of 95% to 107%.The proposed immunosensor possesses the properties of fast,sensitive and portable,etc.