CN104133070B - Preparation method and application of a label-free immunosensor for environmental estrogen - Google Patents
Preparation method and application of a label-free immunosensor for environmental estrogen Download PDFInfo
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Abstract
本发明公开了一种环境雌激素无标记免疫传感器的制备方法及在环境雌激素的检测中的应用,属于新型纳米功能材料和环境检测技术领域。本发明利用两种新型纳米功能材料修饰工作电极,利用二者的协同催化作用以及对抗体的吸附作用,从而制备了一种灵敏度高、特异性好、检测快速、制备简单的检测环境雌激素的无标记电化学免疫传感器。The invention discloses a preparation method of a label-free immune sensor for environmental estrogen and its application in the detection of environmental estrogen, belonging to the technical field of new nano functional materials and environmental detection. The present invention utilizes two novel nano-functional materials to modify the working electrode, utilizes the synergistic catalytic effect of the two and the adsorption effect on antibodies, thereby preparing a device for detecting environmental estrogen with high sensitivity, good specificity, rapid detection and simple preparation. Label-free electrochemical immunosensor.
Description
技术领域 technical field
本发明涉及一种环境雌激素无标记免疫传感器的制备方法及应用。具体是采用具有协同催化作用的新型纳米复合材料构建的检测环境雌激素的无标记电化学免疫传感器,属于新型纳米功能材料与环境检测技术领域。 The invention relates to a preparation method and application of an environmental estrogen label-free immunosensor. Specifically, it is a label-free electrochemical immunosensor for detecting environmental estrogen constructed by a new nanocomposite material with a synergistic catalytic effect, which belongs to the technical field of new nanometer functional materials and environmental detection.
背景技术 Background technique
环境雌激素是一类存在于环境中的化学物质,具有类似生物体内雌激素的活性,进入人体后具有模拟雌激素的作用,通过扰乱人体内分泌、免疫、神经等系统的正常功能而产生如致癌、损害生殖发育系统、免疫系统、神经系统等多种疾病,是一类严重危害人类健康的环境毒素。常见的环境雌激素来源包括如农药(如有机氯农药)、二手烟、废气(如燃烧塑料垃圾产生的有毒气体)、食品添加剂等。 Environmental estrogen is a kind of chemical substance that exists in the environment. It has the activity similar to that of estrogen in organisms. After entering the human body, it has the effect of simulating estrogen. It is a class of environmental toxins that seriously endanger human health. Common sources of environmental estrogen include pesticides (such as organochlorine pesticides), second-hand smoke, waste gas (such as toxic gases produced by burning plastic waste), food additives, etc.
用于环境雌激素的检测方法主要有高效液相色谱法、气相色谱法、色谱-质谱联用法、酶联免疫法、放射免疫法等。但大多数检测方法仪器贵重、操作复杂,检验人员必须经过严格训练后,方可进行检测。一些简便的方法如电化学分析法,虽操作简单、检测灵敏、快速,但特异性差。因此,可快速、灵敏、高特异性检测环境中的环境雌激素的电化学免疫传感器显得尤为突出。 The detection methods for environmental estrogen mainly include high performance liquid chromatography, gas chromatography, chromatography-mass spectrometry, enzyme-linked immunoassay, radioimmunoassay, etc. However, most of the detection methods have expensive instruments and complicated operations, and the inspectors must undergo strict training before they can carry out the detection. Some simple methods, such as electrochemical analysis, are simple in operation, sensitive and fast in detection, but have poor specificity. Therefore, electrochemical immunosensors that can detect environmental estrogens in the environment quickly, sensitively, and with high specificity are particularly prominent.
电化学免疫传感器由于其灵敏度高、特异性好、操作简便等优点被广泛应用于临床分析和环境检测领域,一般可分为有标记和无标记两种,由于标记物的特性,前者比后者对检测环境要求更严格,操作也相对繁琐,因此其中在检测环境雌激素方面,无标记电化学免疫传感器更有应用前景。构建环境雌激素无标记免疫传感器,关键的技术是提高修饰电极对抗体的固定量和对测试底液的信号响应速度和大小。核壳结构的AuPd纳米棒复合材料是一种新型贵金属纳米复合材料,由于其生物相容性好以及纳米级尺寸,增加了抗体的吸附量;并且核壳结构中Au为核Pd为壳层,减少了Pd的使用量,降低了成本;同时其特殊的棒状形貌赋予Pd暴露出更多的催化晶面,可以更好的提高对作为测试底液的双氧水的催化响应速度和电流响应信号大小。另外,CoFe2O4/rGo一方面增加了电极比表面积,增强电极导电能力,另一方面可以与AuPd产生协同催化作用,更大的增强对双氧水的催化响应速度和电流响应信号大小。因此,将二者联合使用,可成功用于无标记电化学免疫传感器的构建。 Electrochemical immunosensors are widely used in clinical analysis and environmental detection due to their high sensitivity, good specificity, and easy operation. They can generally be divided into two types: labeled and unlabeled. The requirements for the detection environment are stricter and the operation is relatively cumbersome. Therefore, in the detection of environmental estrogen, the label-free electrochemical immunosensor has more application prospects. To construct a label-free immunosensor for environmental estrogen, the key technology is to improve the immobilization amount of the modified electrode to the antibody and the signal response speed and size to the test bottom solution. The AuPd nanorod composite material with core-shell structure is a new type of noble metal nanocomposite material. Due to its good biocompatibility and nano-scale size, the adsorption capacity of antibodies is increased; and in the core-shell structure, Au is the core and Pd is the shell, It reduces the usage of Pd and lowers the cost; at the same time, its special rod-like shape endows Pd with more catalytic crystal faces, which can better improve the catalytic response speed and current response signal size of hydrogen peroxide used as the test bottom liquid . In addition, on the one hand, CoFe 2 O 4 /rGo increases the specific surface area of the electrode and enhances the conductivity of the electrode. On the other hand, it can produce a synergistic catalytic effect with AuPd, and greatly enhance the catalytic response speed and current response signal to hydrogen peroxide. Therefore, the combined use of the two can be successfully used in the construction of label-free electrochemical immunosensors.
本发明先后使用CoFe2O4/rGo和AuPd-Ab对电极进行修饰,然后利用环境雌激素抗原的加入,使得电极对双氧水的电流响应信号降低,从而实现了无标记的电化学免疫传感器的构建,并应用于简单、快速、特异性好和灵敏度高的检测环境雌激素。 The present invention successively uses CoFe 2 O 4 /rGo and AuPd-Ab to modify the electrode, and then utilizes the addition of environmental estrogen antigen to reduce the current response signal of the electrode to hydrogen peroxide, thereby realizing the construction of a label-free electrochemical immunosensor , and applied to the simple, rapid, specific and sensitive detection of environmental estrogen.
发明内容 Contents of the invention
本发明的目的之一在于避免现有检测方法中存在的仪器设备复杂、操作过程繁琐及特异性差等不足,提供一种环境雌激素无标记免疫传感器的制备方法,所制备的传感器具有灵敏度高、特异性强的特点,且制备简单、操作方便,可用于环境雌激素的快速、灵敏检测; One of the purposes of the present invention is to avoid the shortcomings of existing detection methods such as complex equipment, cumbersome operation process, and poor specificity, and provide a method for preparing an environmental estrogen-free immunosensor. The prepared sensor has high sensitivity, With strong specificity, simple preparation and convenient operation, it can be used for rapid and sensitive detection of environmental estrogen;
本发明的目的之二在于将所制备的无标记免疫传感器应用到环境雌激素的检测中,实现对多种环境雌激素的快速、灵敏检测。 The second object of the present invention is to apply the prepared label-free immunosensor to the detection of environmental estrogens, so as to realize rapid and sensitive detection of various environmental estrogens.
本发明采用的技术方案如下: The technical scheme that the present invention adopts is as follows:
1. 一种环境雌激素无标记免疫传感器的制备方法,所述环境雌激素无标记免疫传感器包括:工作电极、参比电极和对电极,所述工作电极的基底电极为玻碳电极,其表面依次修饰CoFe2O4/rGo、戊二醛、AuPdNRs-Ab、牛血清蛋白(BSA),所述参比电极为饱和甘汞电极,所述对电极为铂丝电极,所述CoFe2O4/rGo为铁酸钴/还原石墨烯复合材料,所述AuPtNRs-Ab为金钯核壳纳米棒复合材料孵化的环境雌激素抗体; 1. A preparation method of an environmental estrogen label-free immunosensor, the environmental estrogen label-free immunosensor comprising: a working electrode, a reference electrode and a counter electrode, the base electrode of the working electrode is a glassy carbon electrode, and its surface sequentially modify CoFe 2 O 4 /rGo, glutaraldehyde, AuPdNRs-Ab, and bovine serum albumin (BSA), the reference electrode is a saturated calomel electrode, the counter electrode is a platinum wire electrode, and the CoFe 2 O 4 /rGo is a cobalt ferrite/reduced graphene composite material, and the AuPtNRs-Ab is an environmental estrogen antibody incubated with a gold-palladium core-shell nanorod composite material;
其特征在于,所述制备方法包括以下步骤: It is characterized in that the preparation method comprises the following steps:
a、制备CoFe2O4/rGo; a. Preparation of CoFe 2 O 4 /rGo;
b、制备AuPdNRs-Ab; b. Preparation of AuPdNRs-Ab;
c、制备环境雌激素无标记免疫传感器工作电极; c. Preparation of working electrode for environmental estrogen label-free immunosensor;
其中,步骤a制备CoFe2O4/rGo的具体步骤如下: Wherein, the specific steps for preparing CoFe 2 O 4 /rGo in step a are as follows:
将8~12 mg氧化石墨烯超声分散到25~35 ml无水乙醇中,依次加入0.5~1.5 ml 0.2 mol/mL的 Fe(NO3)3水溶液、0.25~0.75 ml of 0.2 mol/L Co(NO3)2水溶液和2.0~3.0 ml氨水,80℃下搅拌10~14h,然后转移至高压反应釜中,180℃下反应4~6h;冷却至室温后,离心分离,于50℃真空干燥箱中烘干,即得CoFe2O4/rGo; Ultrasonic dispersion of 8-12 mg graphene oxide into 25-35 ml of absolute ethanol, followed by adding 0.5-1.5 ml of 0.2 mol/mL Fe(NO 3 ) 3 aqueous solution, 0.25-0.75 ml of 0.2 mol/L Co( NO 3 ) 2 aqueous solution and 2.0~3.0 ml ammonia water, stirred at 80°C for 10~14h, then transferred to a high-pressure reactor, reacted at 180°C for 4~6h; cooled to room temperature, centrifuged, and placed in a vacuum oven at 50°C Dry in medium to get CoFe 2 O 4 /rGo;
步骤b制备AuPdNRs-Ab的具体步骤如下: Step b The specific steps for preparing AuPdNRs-Ab are as follows:
将20mL金纳米棒溶液和20mL 0.05~0.2 mol/L的十六烷基三甲基溴化铵(CTAB)溶液混合,在30~45℃下搅拌,并顺序加入3~6 mL 0.1 mol/L的 L-抗坏血酸(AA)溶液、0.5~1 mL 0.03 mol/L的氯化钯(PdCl2)溶液和 3~6 mL 0.1 mol/L的氢氧化钠(NaOH)溶液,停止搅拌,静置1~3h,离心分离,加入20mL pH7.4的PBS缓冲溶液,然后再加入环境雌激素抗体(Ab),在4℃下震荡24h,得到AuPdNRs-Ab; Mix 20mL gold nanorod solution and 20mL 0.05~0.2 mol/L cetyltrimethylammonium bromide (CTAB) solution, stir at 30~45℃, and add 3~6 mL 0.1 mol/L L-ascorbic acid (AA) solution, 0.5-1 mL 0.03 mol/L palladium chloride (PdCl 2 ) solution and 3-6 mL 0.1 mol/L sodium hydroxide (NaOH) solution, stop stirring, and let stand for 1 ~3h, centrifuge, add 20mL PBS buffer solution with pH7.4, and then add environmental estrogen antibody (Ab), shake at 4°C for 24h to obtain AuPdNRs-Ab;
步骤c制备环境雌激素无标记免疫传感器工作电极的具体步骤如下: Step c The specific steps for preparing the working electrode of the environmental estrogen label-free immunosensor are as follows:
① 对工作电极进行预处理,使其表面光洁; ① Pretreat the working electrode to make its surface smooth;
② 在①中得到的电极表面滴加5~10 μL 1~5 mg/mL的CoFe2O4/rGo水溶液,室温下自然晾干; ② Add 5~10 μL of 1~5 mg/mL CoFe 2 O 4 /rGo aqueous solution dropwise to the surface of the electrode obtained in ①, and let it dry naturally at room temperature;
③ 在②中得到的电极表面滴加5~10 μL的戊二醛,室温下自然晾干; ③ Add 5-10 μL of glutaraldehyde dropwise to the surface of the electrode obtained in ②, and let it dry naturally at room temperature;
④ 在③中得到的电极表面滴加5~8 μL 10 μg/mL的AuPdNRs-Ab溶液,4 ℃ 冰箱中保存晾干,超纯水清洗,晾干成膜,4 ℃保存; ④ Add 5~8 μL of 10 μg/mL AuPdNRs-Ab solution dropwise to the surface of the electrode obtained in ③, store in a refrigerator at 4 ℃ to dry, wash with ultrapure water, dry to form a film, and store at 4 ℃;
⑤ 在④中得到的电极表面滴加4~6 μL 100 μg/mL的BSA溶液,用以封闭电极上的非特异性活性位点,4 ℃ 冰箱中保存晾干,超纯水清洗,晾干成膜,即得到环境雌激素无标记免疫传感器的工作电极。 ⑤ Add 4~6 μL of 100 μg/mL BSA solution dropwise to the surface of the electrode obtained in ④ to seal the non-specific active sites on the electrode, store it in a refrigerator at 4°C and dry it, wash it with ultrapure water, and dry it in the air. Membrane, that is, the working electrode of the label-free immunosensor for environmental estrogen.
2. 本发明所述的环境雌激素无标记免疫传感器,用于环境雌激素的检测,步骤如下: 2. The environmental estrogen label-free immunosensor of the present invention is used for the detection of environmental estrogen, and the steps are as follows:
1)将已知浓度的环境雌激素抗原标准溶液加入到40~60 μL、pH=7.0~8.0的PBS缓冲溶液中,制得抗原混合溶液,取5~10 μL抗原混合溶液滴涂到所制备的环境雌激素免疫传感器的工作电极上,在4 ℃ 冰箱中保存晾干,pH=7.0~8.0的PBS缓冲溶液清洗后,晾干,4 ℃保存; 1) Add environmental estrogen antigen standard solution of known concentration to 40-60 μL PBS buffer solution with pH=7.0-8.0 to prepare antigen mixed solution, take 5-10 μL antigen mixed solution and drop-spray on the prepared On the working electrode of the environmental estrogen immunosensor, store and dry in the refrigerator at 4 ℃, wash with PBS buffer solution with pH=7.0~8.0, dry in the air, and store at 4 ℃;
2)将作为参比电极得甘汞电极、作为对电极得铂丝电极,与1)中组装的工作电极组成三电极系统,连接到电化学工作站上;在电解槽中先后加入10~25mL pH=7.0~8.0的PBS缓冲溶液和1mL 3~6 mmol/L的过氧化氢(H2O2)溶液;通过计时电流法检测组装的工作电极对H2O2的响应;根据所得的电流响应与环境雌激素抗原标准溶液浓度之间的关系,绘制工作曲线; 2) Use the calomel electrode as the reference electrode, the platinum wire electrode as the counter electrode, and the working electrode assembled in 1) to form a three-electrode system, and connect it to the electrochemical workstation; add 10~25mL pH =7.0~8.0 PBS buffer solution and 1mL 3~6 mmol/L hydrogen peroxide (H 2 O 2 ) solution; detect the response of the assembled working electrode to H 2 O 2 by chronoamperometry; according to the obtained current response The relationship between the concentration of the environmental estrogen antigen standard solution and the working curve are drawn;
3)将待测样品溶液代替环境雌激素抗原的标准溶液,按照所述环境雌激素抗原的工作曲线的绘制方法进行检测。 3) Replace the standard solution of the environmental estrogen antigen with the sample solution to be tested, and perform detection according to the drawing method of the working curve of the environmental estrogen antigen.
3. 本发明所述的环境雌激素无标记免疫传感器的制备方法和应用,其特征在于所述环境雌激素选自下列之一:雌二醇、雌三醇、己烯雌酚、双酚A或壬基酚。 3. The preparation method and application of the environmental estrogen label-free immunosensor of the present invention, characterized in that the environmental estrogen is selected from one of the following: estradiol, estriol, diethylstilbestrol, bisphenol A or nonyl phenol.
本发明的有益成果Beneficial results of the present invention
(1)本发明所述的环境雌激素无标记免疫传感器制备简单,操作方便,实现了对多种环境雌激素的快速、灵敏、高选择性检测,具有市场发展前景。 (1) The environmental estrogen label-free immunosensor of the present invention is simple to prepare, easy to operate, realizes rapid, sensitive, and highly selective detection of various environmental estrogens, and has market development prospects.
(2)本发明首次采用CoFe2O4/rGo和AuPdNRs-Ab共同修饰电极,并利用二者的协同催化效应,显著提高电流相应速度和大小,进一步增强了抗体的吸附量,从而构建了无标记的电化学免疫传感器,具有重要的科学意义和应用价值。 (2) The present invention uses CoFe 2 O 4 /rGo and AuPdNRs-Ab to modify the electrode for the first time, and utilizes the synergistic catalytic effect of the two to significantly increase the corresponding speed and magnitude of the current, and further enhance the adsorption capacity of the antibody, thereby constructing an electrode without The labeled electrochemical immunosensor has important scientific significance and application value.
具体实施方式 Detailed ways
实施例1 CoFe2O4/rGo的制备 Example 1 Preparation of CoFe 2 O 4 /rGo
将8 mg氧化石墨烯超声分散到25 ml无水乙醇中,依次加入0.5 ml 0.2 mol/mL的 Fe(NO3)3水溶液、0.25 ml of 0.2 mol/L Co(NO3)2水溶液和2.0 ml氨水,80℃下搅拌10h,然后转移至高压反应釜中,180℃下反应4h;冷却至室温后,离心分离,于50℃真空干燥箱中烘干,即得CoFe2O4/rGo。 8 mg of graphene oxide was ultrasonically dispersed into 25 ml of absolute ethanol, and 0.5 ml of 0.2 mol/mL Fe(NO 3 ) 3 aqueous solution, 0.25 ml of 0.2 mol/L Co(NO 3 ) 2 aqueous solution and 2.0 ml of Ammonia, stirred at 80°C for 10h, then transferred to an autoclave, reacted at 180°C for 4h; cooled to room temperature, centrifuged, and dried in a vacuum oven at 50°C to obtain CoFe 2 O 4 /rGo.
实施例2 CoFe2O4/rGo的制备 Example 2 Preparation of CoFe 2 O 4 /rGo
将10 mg氧化石墨烯超声分散到30 ml无水乙醇中,依次加入1 ml 0.2 mol/mL的 Fe(NO3)3水溶液、0.5 ml of 0.2 M Co(NO3)2水溶液和2.50 ml氨水,80℃下搅拌12h,然后转移至高压反应釜中,180℃下反应5h;冷却至室温后,离心分离,于50℃真空干燥箱中烘干,即得CoFe2O4/rGo。 Ultrasonic dispersion of 10 mg of graphene oxide into 30 ml of absolute ethanol was followed by adding 1 ml of 0.2 mol/mL Fe(NO 3 ) 3 aqueous solution, 0.5 ml of 0.2 M Co(NO 3 ) 2 aqueous solution and 2.50 ml of ammonia water, Stir at 80°C for 12h, then transfer to an autoclave, react at 180°C for 5h; cool to room temperature, centrifuge and dry in a vacuum oven at 50°C to obtain CoFe 2 O 4 /rGo.
实施例3 CoFe2O4/rGo的制备 Example 3 Preparation of CoFe 2 O 4 /rGo
将12 mg氧化石墨烯超声分散到35 ml无水乙醇中,依次加入1.5 ml 0.2 mol/mL的 Fe(NO3)3水溶液、0.75 ml of 0.2 mol/L Co(NO3)2水溶液和3.0 ml氨水,80℃下搅拌14h,然后转移至高压反应釜中,180℃下反应6h;冷却至室温后,离心分离,于50℃真空干燥箱中烘干,即得CoFe2O4/rGo。 12 mg of graphene oxide was ultrasonically dispersed into 35 ml of absolute ethanol, and 1.5 ml of 0.2 mol/mL Fe(NO 3 ) 3 aqueous solution, 0.75 ml of 0.2 mol/L Co(NO 3 ) 2 aqueous solution and 3.0 ml of Ammonia, stirred at 80°C for 14h, then transferred to an autoclave, reacted at 180°C for 6h; cooled to room temperature, centrifuged, and dried in a vacuum oven at 50°C to obtain CoFe 2 O 4 /rGo.
实施例4 AuPdNRs-Ab的制备 Example 4 Preparation of AuPdNRs-Ab
将20mL金纳米棒溶液和20mL 0.05 mol/L的十六烷基三甲基溴化铵(CTAB)溶液混合,在30℃下搅拌,并顺序加入3 mL 0.1 mol/L的 L-抗坏血酸(AA)溶液、0.5 mL 0.03 mol/L的氯化钯(PdCl2)溶液和 3 mL 0.1 mol/L的氢氧化钠(NaOH)溶液,停止搅拌,静置1h,离心分离,加入20mL pH7.4的PBS缓冲溶液,然后再加入环境雌激素抗体(Ab),在4℃下震荡24h,得到AuPdNRs-Ab。 Mix 20 mL of gold nanorod solution and 20 mL of 0.05 mol/L cetyltrimethylammonium bromide (CTAB) solution, stir at 30 °C, and sequentially add 3 mL of 0.1 mol/L L-ascorbic acid (AA ) solution, 0.5 mL 0.03 mol/L palladium chloride (PdCl 2 ) solution and 3 mL 0.1 mol/L sodium hydroxide (NaOH) solution, stop stirring, let stand for 1 hour, centrifuge, add 20 mL pH7.4 PBS buffer solution, and then add environmental estrogen antibody (Ab), shake at 4°C for 24h to obtain AuPdNRs-Ab.
实施例5 AuPdNRs-Ab的制备 Example 5 Preparation of AuPdNRs-Ab
将20mL金纳米棒溶液和20mL 0.1 mol/L的CTAB溶液混合,在35℃下搅拌,并顺序加入4 mL 0.1 mol/L的AA溶液、0.8 mL 0.03 mol/L的PdCl2溶液和 4 mL 0.1 mol/L的NaOH溶液,停止搅拌,静置2h,离心分离,加入20mL pH7.4的PBS缓冲溶液,然后再加入环境雌激素抗体(Ab),在4℃下震荡24h,得到AuPdNRs-Ab。 Mix 20 mL of gold nanorod solution and 20 mL of 0.1 mol/L CTAB solution, stir at 35 °C, and sequentially add 4 mL of 0.1 mol/L AA solution, 0.8 mL of 0.03 mol/L PdCl solution and 4 mL of 0.1 mol/L NaOH solution, stop stirring, let stand for 2h, centrifuge, add 20mL PBS buffer solution with pH7.4, then add environmental estrogen antibody (Ab), shake at 4°C for 24h, and obtain AuPdNRs-Ab.
实施例6 AuPdNRs-Ab的制备 Example 6 Preparation of AuPdNRs-Ab
将20mL金纳米棒溶液和20mL 0.2 mol/L的CTAB溶液混合,在45℃下搅拌,并顺序加入6 mL 0.1 mol/L的 AA溶液、1 mL 0.03 mol/L的PdCl2溶液和 6 mL 0.1 mol/L的NaOH溶液,停止搅拌,静置3h,离心分离,加入20mL pH7.4的PBS缓冲溶液,然后再加入环境雌激素抗体(Ab),在4℃下震荡24h,得到AuPdNRs-Ab。 Mix 20 mL of gold nanorod solution and 20 mL of 0.2 mol/L CTAB solution, stir at 45 °C, and sequentially add 6 mL of 0.1 mol/L AA solution, 1 mL of 0.03 mol/L PdCl2 solution and 6 mL of 0.1 mol/L NaOH solution, stop stirring, let stand for 3h, centrifuge, add 20mL PBS buffer solution with pH7.4, then add environmental estrogen antibody (Ab), shake at 4°C for 24h, and obtain AuPdNRs-Ab.
实施例7 环境雌激素无标记免疫传感器工作电极的制备方法 Example 7 Preparation method of environmental estrogen label-free immunosensor working electrode
(1)对工作电极进行预处理,使其表面光洁; (1) Pretreat the working electrode to make its surface smooth;
(2)在(1)中得到的电极表面滴加5 μL 1 mg/mL的CoFe2O4/rGo水溶液,室温下自然晾干; (2) Add 5 μL of 1 mg/mL CoFe 2 O 4 /rGo aqueous solution dropwise to the surface of the electrode obtained in (1), and let it dry naturally at room temperature;
(3)在(2)中得到的电极表面滴加5 μL的戊二醛,室温下自然晾干; (3) Add 5 μL of glutaraldehyde dropwise to the surface of the electrode obtained in (2), and let it dry naturally at room temperature;
(4)在(3)中得到的电极表面滴加5 μL 10 μg/mL的AuPdNRs-Ab溶液,4 ℃ 冰箱中保存晾干,超纯水清洗,晾干成膜,4 ℃保存; (4) Add 5 μL of 10 μg/mL AuPdNRs-Ab solution dropwise to the surface of the electrode obtained in (3), store in a refrigerator at 4 °C to dry, wash with ultrapure water, dry to form a film, and store at 4 °C;
(5)在(4)中得到的电极表面滴加4 μL 100 μg/mL的BSA溶液,用以封闭电极上的非特异性活性位点,4 ℃ 冰箱中保存晾干,超纯水清洗,晾干成膜,即得到环境雌激素无标记免疫传感器的工作电极。 (5) Add 4 μL of 100 μg/mL BSA solution dropwise to the surface of the electrode obtained in (4) to seal the non-specific active sites on the electrode, store in a refrigerator at 4°C to dry, wash with ultrapure water, and dry in the air. After drying into a film, the working electrode of the environmental estrogen-free immunosensor can be obtained.
实施例8 环境雌激素无标记免疫传感器工作电极的制备方法 Example 8 Preparation Method of Environmental Estrogen Label-Free Immunosensor Working Electrode
(1)对工作电极进行预处理,使其表面光洁; (1) Pretreat the working electrode to make its surface smooth;
(2)在(1)中得到的电极表面滴加8 μL 3 mg/mL的CoFe2O4/rGo水溶液,室温下自然晾干; (2) Add 8 μL of 3 mg/mL CoFe 2 O 4 /rGo aqueous solution dropwise to the surface of the electrode obtained in (1), and let it dry naturally at room temperature;
(3)在(2)中得到的电极表面滴加8 μL的戊二醛,室温下自然晾干; (3) Add 8 μL of glutaraldehyde dropwise to the surface of the electrode obtained in (2), and let it dry naturally at room temperature;
(4)在(3)中得到的电极表面滴加6 μL 10 μg/mL的AuPdNRs-Ab溶液,4 ℃ 冰箱中保存晾干,超纯水清洗,晾干成膜,4 ℃保存; (4) Add 6 μL of 10 μg/mL AuPdNRs-Ab solution dropwise to the surface of the electrode obtained in (3), store in a refrigerator at 4 °C to dry, wash with ultrapure water, dry to form a film, and store at 4 °C;
(5)在(4)中得到的电极表面滴加5 μL 100 μg/mL的BSA溶液,用以封闭电极上的非特异性活性位点,4 ℃ 冰箱中保存晾干,超纯水清洗,晾干成膜,即得到环境雌激素无标记免疫传感器的工作电极。 (5) Add 5 μL of 100 μg/mL BSA solution dropwise to the surface of the electrode obtained in (4) to seal the non-specific active sites on the electrode, store it in a refrigerator at 4°C and dry it, wash it with ultrapure water, and dry it in the air. After drying into a film, the working electrode of the environmental estrogen-free immunosensor can be obtained.
实施例9 环境雌激素无标记免疫传感器工作电极的制备方法 Example 9 Preparation method of environmental estrogen label-free immunosensor working electrode
(1)对工作电极进行预处理,使其表面光洁; (1) Pretreat the working electrode to make its surface smooth;
(2)在(1)中得到的电极表面滴加10 μL 5 mg/mL的CoFe2O4/rGo水溶液,室温下自然晾干; (2) Add 10 μL of 5 mg/mL CoFe 2 O 4 /rGo aqueous solution dropwise to the surface of the electrode obtained in (1), and let it dry naturally at room temperature;
(3)在(2)中得到的电极表面滴加10 μL的戊二醛,室温下自然晾干; (3) Add 10 μL of glutaraldehyde dropwise to the surface of the electrode obtained in (2), and let it dry naturally at room temperature;
(4)在(3)中得到的电极表面滴加8 μL 10 μg/mL的AuPdNRs-Ab溶液,4 ℃ 冰箱中保存晾干,超纯水清洗,晾干成膜,4 ℃保存; (4) Add 8 μL of 10 μg/mL AuPdNRs-Ab solution dropwise to the surface of the electrode obtained in (3), store in a refrigerator at 4 °C to dry, wash with ultrapure water, dry to form a film, and store at 4 °C;
(5)在(4)中得到的电极表面滴加6 μL 100 μg/mL的BSA溶液,用以封闭电极上的非特异性活性位点,4 ℃ 冰箱中保存晾干,超纯水清洗,晾干成膜,即得到环境雌激素无标记免疫传感器的工作电极。 (5) Add 6 μL of 100 μg/mL BSA solution dropwise to the surface of the electrode obtained in (4) to seal the non-specific active sites on the electrode, store it in a refrigerator at 4°C and dry it, wash it with ultrapure water, and dry it in the air. After drying into a film, the working electrode of the environmental estrogen-free immunosensor can be obtained.
实施例10 实施例1~9制备的环境雌激素无标记免疫传感器,用于环境雌激素的检测,步骤如下 Example 10 The environmental estrogen label-free immunosensor prepared in Examples 1-9 is used for the detection of environmental estrogen, and the steps are as follows
(1)将已知浓度的环境雌激素抗原标准溶液加入到40 μL、pH=7.0的PBS缓冲溶液中,制得抗原混合溶液,取5 μL抗原混合溶液滴涂到所制备的环境雌激素免疫传感器的工作电极上,在4 ℃ 冰箱中保存晾干,pH=7.0的PBS缓冲溶液清洗后,晾干,4 ℃保存; (1) Add the known concentration of environmental estrogen antigen standard solution to 40 μL of PBS buffer solution with pH=7.0 to prepare the antigen mixed solution, and take 5 μL of the antigen mixed solution to drop-spray on the prepared environmental estrogen immunoassay On the working electrode of the sensor, store and dry in the refrigerator at 4 °C, wash with PBS buffer solution with pH=7.0, dry in the air, and store at 4 °C;
(2)将作为参比电极得甘汞电极、作为对电极得铂丝电极,与(1)中组装的工作电极组成三电极系统,连接到电化学工作站上;在电解槽中先后加入10mL pH=7.0的PBS缓冲溶液和1mL 3 mmol/L的H2O2溶液;通过计时电流法检测组装的工作电极对H2O2的响应;根据所得的电流响应与环境雌激素抗原标准溶液浓度之间的关系,绘制工作曲线; (2) Use the calomel electrode as the reference electrode, the platinum wire electrode as the counter electrode, and the working electrode assembled in (1) to form a three-electrode system, and connect it to the electrochemical workstation; add 10mL of pH =7.0 PBS buffer solution and 1mL 3 mmol/L H 2 O 2 solution; detect the response of the assembled working electrode to H 2 O 2 by chronoamperometry; The relationship between, draw the working curve;
(3)将待测样品溶液代替环境雌激素抗原的标准溶液,按照所述环境雌激素抗原的工作曲线的绘制方法进行检测。 (3) Replace the standard solution of the environmental estrogen antigen with the sample solution to be tested, and perform detection according to the drawing method of the working curve of the environmental estrogen antigen.
实施例11 实施例1~9制备的环境雌激素无标记免疫传感器,用于环境雌激素的检测,步骤如下 Example 11 The environmental estrogen label-free immunosensor prepared in Examples 1-9 is used for the detection of environmental estrogen, and the steps are as follows
(1)将已知浓度的环境雌激素抗原标准溶液加入到50 μL、pH=7.4的PBS缓冲溶液中,制得抗原混合溶液,取7 μL抗原混合溶液滴涂到所制备的环境雌激素免疫传感器的工作电极上,在4 ℃ 冰箱中保存晾干,pH=7.4的PBS缓冲溶液清洗后,晾干,4 ℃保存; (1) Add the known concentration of environmental estrogen antigen standard solution to 50 μL of PBS buffer solution with pH=7.4 to prepare the antigen mixed solution, take 7 μL of the antigen mixed solution and drop-spray it on the prepared environmental estrogen immunoassay On the working electrode of the sensor, store and dry in the refrigerator at 4 °C, wash with PBS buffer solution with pH=7.4, dry in the air, and store at 4 °C;
(2)将作为参比电极得甘汞电极、作为对电极得铂丝电极,与(1)中组装的工作电极组成三电极系统,连接到电化学工作站上;在电解槽中先后加入20mL pH=7.4的PBS缓冲溶液和1mL 4 mmol/L的H2O2溶液;通过计时电流法检测组装的工作电极对H2O2的响应;根据所得的电流响应与环境雌激素抗原标准溶液浓度之间的关系,绘制工作曲线; (2) Use the calomel electrode as the reference electrode, the platinum wire electrode as the counter electrode, and the working electrode assembled in (1) to form a three-electrode system, and connect it to the electrochemical workstation; add 20mL of pH =7.4 PBS buffer solution and 1mL 4 mmol/L H 2 O 2 solution; detect the response of the assembled working electrode to H 2 O 2 by chronoamperometry; The relationship between, draw the working curve;
(3)将待测样品溶液代替环境雌激素抗原的标准溶液,按照所述环境雌激素抗原的工作曲线的绘制方法进行检测。 (3) Replace the standard solution of the environmental estrogen antigen with the sample solution to be tested, and perform detection according to the drawing method of the working curve of the environmental estrogen antigen.
实施例12 实施例1~9制备的环境雌激素无标记免疫传感器,用于环境雌激素的检测,步骤如下 Example 12 The environmental estrogen label-free immunosensor prepared in Examples 1-9 is used for the detection of environmental estrogen, and the steps are as follows
(1)将已知浓度的环境雌激素抗原标准溶液加入到60 μL、pH=8.0的PBS缓冲溶液中,制得抗原混合溶液,取10 μL抗原混合溶液滴涂到所制备的环境雌激素免疫传感器的工作电极上,在4 ℃ 冰箱中保存晾干,pH=8.0的PBS缓冲溶液清洗后,晾干,4 ℃保存; (1) Add the known concentration of environmental estrogen antigen standard solution to 60 μL of PBS buffer solution with pH=8.0 to prepare the antigen mixed solution, take 10 μL of the antigen mixed solution and drop-spray it on the prepared environmental estrogen immunoassay On the working electrode of the sensor, store and dry in the refrigerator at 4 °C, wash with PBS buffer solution with pH=8.0, dry in the air, and store at 4 °C;
(2)将作为参比电极得甘汞电极、作为对电极得铂丝电极,与(1)中组装的工作电极组成三电极系统,连接到电化学工作站上;在电解槽中先后加入25mL pH=8.0的PBS缓冲溶液和1mL 6 mmol/L的H2O2溶液;通过计时电流法检测组装的工作电极对H2O2的响应;根据所得的电流响应与环境雌激素抗原标准溶液浓度之间的关系,绘制工作曲线; (2) The calomel electrode used as the reference electrode, the platinum wire electrode used as the counter electrode, and the working electrode assembled in (1) form a three-electrode system, which is connected to the electrochemical workstation; 25mL pH =8.0 PBS buffer solution and 1mL 6 mmol/L H 2 O 2 solution; detect the response of the assembled working electrode to H 2 O 2 by chronoamperometry; The relationship between, draw the working curve;
(3)将待测样品溶液代替环境雌激素抗原的标准溶液,按照所述环境雌激素抗原的工作曲线的绘制方法进行检测。 (3) Replace the standard solution of the environmental estrogen antigen with the sample solution to be tested, and perform detection according to the drawing method of the working curve of the environmental estrogen antigen.
实施例13 环境雌激素:雌二醇、雌三醇、己烯雌酚、双酚A或壬基酚的检测,包括以下步骤 Embodiment 13 environmental estrogen: detection of estradiol, estriol, diethylstilbestrol, bisphenol A or nonylphenol, comprising the following steps
(1)选择一种环境雌激素,按照实施例1~9所述的步骤构建环境雌激素无标记免疫传感器; (1) Select an environmental estrogen, and construct an environmental estrogen label-free immunosensor according to the steps described in Examples 1-9;
(2)按照实施例10~12所述的步骤进行检测,环境雌激素的检测技术指标见表1。 (2) Perform detection according to the steps described in Examples 10-12, and see Table 1 for the technical indicators of environmental estrogen detection.
表1 环境雌激素的检测技术指标 Table 1 Detection technical indicators of environmental estrogen
实施例14 牛奶中环境雌激素的检测 The detection of environmental estrogen in embodiment 14 milk
准确移取牛奶样品,加入一定质量浓度的环境雌激素抗原标准溶液,以未加入环境雌激素抗原的牛奶为空白,进行加标回收实验,按照实施例13的步骤进行检测,测定牛奶样品中环境雌激素的回收率,检测结果见表2。 Accurately pipette the milk sample, add a certain mass concentration of the environmental estrogen antigen standard solution, take the milk without the environmental estrogen antigen as the blank, carry out the standard addition recovery experiment, and perform detection according to the steps in Example 13 to determine the environmental concentration in the milk sample. The recovery rate of estrogen, the test results are shown in Table 2.
表2 牛奶中多种环境雌激素的检测结果 Table 2 Detection results of various environmental estrogens in milk
表2检测结果可知,结果的相对标准偏差(RSD)小于3.0 %,平均回收率为96.0 ~ 102%,表明本发明可用于牛奶中多种环境雌激素的检测,方法的灵敏度高、特异性强,结果准确可靠。 It can be seen from the detection results in Table 2 that the relative standard deviation (RSD) of the results is less than 3.0%, and the average recovery rate is 96.0-102%, which shows that the present invention can be used for the detection of various environmental estrogens in milk, and the method has high sensitivity and strong specificity , the result is accurate and reliable.
实施例15 水样中环境雌激素的检测 The detection of environmental estrogen in embodiment 15 water samples
准确移取一定水样,加入一定质量浓度的环境雌激素抗原标准溶液,以未加入环境雌激素抗原的水样为空白,进行加标回收实验,按照实施例13的步骤进行检测,测定水样中环境雌激素的回收率,检测结果见表3。 Accurately pipette a certain water sample, add a certain mass concentration of environmental estrogen antigen standard solution, take the water sample without environmental estrogen antigen as a blank, carry out the standard addition recovery experiment, and perform detection according to the steps in Example 13, and measure the water sample The recovery rate of estrogen in the environment, the test results are shown in Table 3.
表3 水样中多种环境雌激素的检测结果 Table 3 Detection results of various environmental estrogens in water samples
表3检测结果可知,结果的相对标准偏差(RSD)小于3.3 %,平均回收率为97.2 ~ 102%,表明本发明可用于水样中多种环境雌激素的检测,方法的灵敏度高、特异性强,结果准确可靠。 As can be seen from the test results in Table 3, the relative standard deviation (RSD) of the results is less than 3.3%, and the average recovery rate is 97.2 to 102%, indicating that the present invention can be used for the detection of various environmental estrogens in water samples, and the method has high sensitivity and specificity Strong, accurate and reliable results.
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