北京工业大学环境与能源工程学院 区域大气复合污染防治北京市重点实验室
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王玲, 康天放, 张晶晶, 等. 基于Ru@SiO2的微囊藻毒素电化学发光免疫传感器研究[J]. 分析测试学报, 2015,34(5):552-557.
Study of Electrochemiluminescence Immunosensor for Microcystins Based on Ru@SiO2[J]. 2015,34(5):552-557.
本研究在玻碳电极(GCE)表面电沉积金纳米粒子(AuNPs),通过化学吸附将微囊藻毒素-(亮氨酸-精氨酸)(MC-LR)的单克隆抗体(anti-MC-LR)固定在电沉积了AuNPs的玻碳电极表面,以牛血清白蛋白(BSA) 封闭非特异性吸附位点,制得免疫电极anti-MC-LR/AuNPs/GCE。采用微乳化法制备了掺杂三(2,2’联二吡啶)钌(Ⅱ)配合物离子(Ru(bpy)2+3)的二氧化硅纳米粒子(Ru@SiO2),利用透射电镜和扫描电镜对所制备的纳米粒子进行表征。3-氨基丙基三乙氧基硅烷(APTS)进一步与Ru@SiO2反应,制得氨基功能化的Ru@SiO2,通过1-(3-二甲氨基丙基)-3-乙基碳二亚胺(EDC)和N 羟基琥珀酰亚胺(NHS)活化辣根过氧化物酶标记的MC-LR(HRP-MC-LR),并使其与氨基功能化的Ru@SiO2偶联,制得MC-LR-Ru@SiO2。采用直接竞争模式,在标记物MC-LR-Ru@SiO2存在下,以三丙胺作为共反应物,利用电化学发光法(ECL)测定溶液中的微囊藻毒素,免疫反应完成后,电化学发光强度(I) 随着MC-LR浓度的增大而减小,且在0.100~100 μg/L范围内,电化学发光强度差值(ΔI)与游离的MC-LR浓度的对数呈良好线性关系,检出限为0.007 μg/L。对实际水样进行了加标回收实验,回收率为95.5%~105%。
Gold nanoparticles(AuNPs) were electrodeposited onto the surface of a glassy carbon electrode(GCE).The antibody of microcystin (leucine arginine)(anti-MC-LR) was immobilized on the film surface of AuNPs by the adsorption between Au nanoparticles and antibody.Non specific adsorption sites on the AuNPs were blocked with bovine serum albumin(BSA) to prepare an immunoelectrode anti-MC-LR/AuNPs/GCE.Microemulsion polymerization method was adopted to synthesize silica nanoparticles doped with tris(2,2′-bipyridyl) ruthenium(Ⅱ) complex ions(e.g.Ru@SiO2).Ru@SiO2 nanoparticles and AuNPs on the surface of a GCE were characterized by transmission electron microscopy image(TEM) and scanning electron microscopy(SEM),respectively.The Ru@SiO2 nanoparticles were further modified with amino groups by reacting with 3-aminopropyltriethoxysilane.The amino group modified Ru@SiO2 was then crosslinked with the carboxylic groups of microcystin (leucine-arginine)(MC-LR) by ethyl-3-(dimethyl aminopropyl) carbodiimide(EDC) and N-hydroxysuccinimide(NHS) to prepare Ru@SiO2-conjugated MC-LR(MC-LR-Ru@SiO2).The immunosensor was based on the direct competitive immunoassay format between the labeled agent of MC-LR-Ru@SiO2 and the analyte.In the presence of MC-LR-Ru@SiO2,tripropylamine(TPA) was used as coreactant.MC-LR in solution was determined by electrochemiluminescence(ECL) method.The ECL intensity(I) decreases with the increase of MC-LR concentration after antigen-antibody reaction.A good linear relationship between the change of ECL intensity(ΔI) and the logarithm of MC-LR concentration was obtained in the range of 0.100-100 μg/L with a detection limit of 0.007 μg/L.The developed ECL immunosensor was used to determine MC-LR in real water samples with recoveries of 95.5%-105%.
Ru@SiO2纳米粒子微囊藻毒素免疫传感器电化学发光
Ru@SiO2nanoparticlesmicrocystinsimmunosensorselectrochemiluminescence
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