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CN109254053A - A kind of preparation method and application of environmental estrogens electro-chemical analyzing sensor - Google Patents

A kind of preparation method and application of environmental estrogens electro-chemical analyzing sensor Download PDF

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CN109254053A
CN109254053A CN201811306544.5A CN201811306544A CN109254053A CN 109254053 A CN109254053 A CN 109254053A CN 201811306544 A CN201811306544 A CN 201811306544A CN 109254053 A CN109254053 A CN 109254053A
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electrode
imprinted polymer
template molecule
molecularly imprinted
environmental
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CN109254053B (en
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刘召壹
张勇
魏琴
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University of Jinan
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    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N27/00Investigating or analysing materials by the use of electric, electrochemical, or magnetic means
    • G01N27/26Investigating or analysing materials by the use of electric, electrochemical, or magnetic means by investigating electrochemical variables; by using electrolysis or electrophoresis
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N27/00Investigating or analysing materials by the use of electric, electrochemical, or magnetic means
    • G01N27/26Investigating or analysing materials by the use of electric, electrochemical, or magnetic means by investigating electrochemical variables; by using electrolysis or electrophoresis
    • G01N27/28Electrolytic cell components
    • G01N27/30Electrodes, e.g. test electrodes; Half-cells
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N27/00Investigating or analysing materials by the use of electric, electrochemical, or magnetic means
    • G01N27/26Investigating or analysing materials by the use of electric, electrochemical, or magnetic means by investigating electrochemical variables; by using electrolysis or electrophoresis
    • G01N27/28Electrolytic cell components
    • G01N27/30Electrodes, e.g. test electrodes; Half-cells
    • G01N27/327Biochemical electrodes, e.g. electrical or mechanical details for in vitro measurements
    • G01N27/3275Sensing specific biomolecules, e.g. nucleic acid strands, based on an electrode surface reaction
    • G01N27/3278Sensing specific biomolecules, e.g. nucleic acid strands, based on an electrode surface reaction involving nanosized elements, e.g. nanogaps or nanoparticles

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Abstract

The invention discloses a kind of preparation methods of environmental estrogens electro-chemical analyzing sensor.Belong to Nano-function thin films and biosensory analysis technology field.The present invention is prepared for cobalt hydroxide nano-chip arrays can disposably throw first on electrode, utilize its big specific surface area and high activity hydroxy functional group, and the amido functional group of poly-dopamine, using the method for growth in situ, directly it is prepared for the poly-dopamine film containing electron mediator in succession and using environmental estrogens as the molecularly imprinted polymer of template molecule on cobalt hydroxide nano-chip arrays in succession, after by template molecule elution, the position of template molecule originally has become hole, that is the molecularly imprinted polymer of eluted template molecule, thus, a kind of environmental estrogens electro-chemical analyzing sensor just prepares completion.

Description

A kind of preparation method and application of environmental estrogens electro-chemical analyzing sensor
Technical field
The present invention relates to a kind of preparation method and applications of electro-chemical analyzing sensor.Belong to Nano-function thin films with Biosensory analysis technology field.
Background technique
Environmental estrogens are a kind of chemical substances existed in the environment, have the activity of similar organism inner estrogen, Have the function of simulating estrogen after into human body, by upsetting the normal function of the systems such as human endocrine, immune, nerve Such as carcinogenic, damage reproductive development system, immune system, a variety of diseases of nervous system are generated, is that a kind of serious harm mankind are strong The environmental toxin of health.Common environmental estrogens source includes if pesticide (such as organo-chlorine pesticide), secondhand smoke, exhaust gas are (as burnt The toxic gas that plastic garbage generates), food additives etc..Detection method for environmental estrogens mainly has high-efficient liquid phase color Spectrometry, gas chromatography, chromatograph-mass spectrometer coupling method, enzyme-linked immunization, radioimmunology etc..But most of detection method instruments It is valuable, complicated for operation, reviewer has to pass through screw up discipline after, can be detected.The method such as electrochemistry of some simplicity Analytic approach, though easy to operate, sensitive, quick, the poor specificity of detection.Therefore, it develops as early as possible a kind of quick, highly selective and clever The method of quick detection environmental estrogens is extremely important to publilc health, and has wide market application prospect.
Molecular imprinting electrochemical sensor has high specific selectivity, excellent stability, excellent reproducibility, wide inspection Survey range and floor detection limit.Due to the sensor prepare simple, easy to detect, high sensitivity, it is at low cost the advantages that it is extensive Applied to the fields such as chromatographic isolation, film point, Solid Phase Extraction, medicine controlled releasing, chemical sensitisation.Molecularly imprinted polymer (MIP), also referred to as It, being capable of specific recognition and the specific target molecule of selective absorption (i.e. template molecule) for " plastics antibody ".Due to molecular engram Technology has many advantages that, such as organic reagent corrosion resistance, good stability, heat-resisting quantity and preparation are simple.Therefore, in mistake In several years gone, electroanalysis is caused based on the MIP electrochemical sensor (MIP-ECS) that MIP is combined with electrochemical sensor The detection of the focus of chemical field, especially small molecule contaminants.However, having in the preparation process of traditional MIP-ECS The elution of template molecule difficulty, the disadvantages of thickness of blotting membrane is difficult to control, reproducibility is poor, limit molecular engram film and passed in electrochemistry Application in sensor.These problems, especially molecular engram film thickness are not easy to control to lead to electrochemical sensor sensitivity decrease And molecular engram film easily falls off from electrode surface the technical problem for causing stability and reproducibility to reduce during elution, limit The application of MIP_ECS has been made, therefore, has found new molecularly imprinted polymer synthetic method, new molecular engram film electrode is repaired The combination method of decorations method and molecular engram film and base material, to solve the preparation of MIP-ECS and have using problem important Research significance and market value.
Summary of the invention
The purpose of the present invention is to provide a kind of high specificity, prepare simple, easy to detect, high sensitivity, at low cost The preparation method of environmental estrogens electro-chemical analyzing sensor, prepared electrochemical sensing electrode prepare simple, reproducibility Well, stability is strong, can be used as quick, Sensitive Detection of the electrochemical sensor for environmental estrogens.Based on this purpose, the present invention It is prepared for cobalt hydroxide nano-chip arrays on electrode can disposably throw first, utilizes its big specific surface area and high activity hydrogen-oxygen The amido functional group of base functional group and poly-dopamine, using the method for growth in situ, in succession in cobalt hydroxide nano-chip arrays It is upper to be directly prepared for the poly-dopamine film containing electron mediator in succession and printed by the molecule of template molecule of environmental estrogens Mark polymer, after by template molecule elution, the position of template molecule originally has become hole, i.e. eluted template molecule Molecularly imprinted polymer, a kind of environmental estrogens electro-chemical analyzing sensor just prepares completion as a result,.Swash when for female to environment When element is detected, environmental estrogens electro-chemical analyzing sensor is inserted into solution to be measured, the environment in solution to be measured is female to swash Element can be adsorbed onto the hole of NIP.Environmental estrogens concentration in solution to be measured is bigger, and it is female to be adsorbed onto environment in the hole of NIP Hormone is more.When carrying out Electrochemical Detection, the intensity for detecting electric current can be with environmental estrogens in the hole for being adsorbed onto NIP Increase and become smaller, thus according to the degree that current strength reduces, is capable of the dense of environmental estrogens in qualitative, quantitative solution to be measured Degree.
The technical solution adopted by the invention is as follows:
1. a kind of preparation method of environmental estrogens electro-chemical analyzing sensor, the environmental estrogens electrochemical analysis is passed Sensor is by growth in situ on cobalt hydroxide nano-chip arrays electrode Co-nanoarray without template molecule molecularly imprinted polymer NIP It obtains;The molecularly imprinted polymer that template molecule is free from without template molecule molecularly imprinted polymer NIP;It is described The molecularly imprinted polymer without containing template molecule be by the MIP of molecularly imprinted polymer containing template molecule by eluted template point What son obtained;The MIP of molecularly imprinted polymer containing template molecule is the molecularly imprinted polymer containing template molecule;It is described Template molecule be environmental estrogens;
2. the preparation method of cobalt hydroxide nano-chip arrays electrode Co-nanoarray described in technical solution 1 includes following Preparation step:
(1) it will can disposably throw electrode and carry out ultrasonic cleaning processing using dilute hydrochloric acid, dehydrated alcohol and deionization respectively, to go Except the oxide layer and surface impurity that can disposably throw electrode;
(2) 1 ~ 3 mmol Co (NO is weighed3)2With 3 ~ 9 mmol urea CO (NH2)2, it is put into 50 mL beakers, is added 30 ML deionized water stirs to clarify, and is then transferred into 50 mL ptfe autoclaves;
(3) in the disposable solution thrown in the reaction kettle that electrode is put into step (2) for handling step (1) well, 100 ~ It is reacted 9 ~ 12 hours at a temperature of 130 DEG C, cobalt hydroxide nano-chip arrays presoma electrode is prepared;
(4) the cobalt hydroxide nano-chip arrays presoma electrode insertion obtained step (3) contains dopamine, Ammonium Persulfate 98.5 and nitre In the phosphate buffer solution PBS of sour cobalt, 20 ~ 40 DEG C at a temperature of reaction 4 ~ 6 hours after, take out simultaneously soaked with deionized water It washes 2 ~ 4 times, cobalt hydroxide nano-chip arrays electrode Co-nanoarray is prepared;
The described disposable electrode of throwing is selected from one of cycle unit: nickel foam, foam copper, pure nickel piece, pure copper sheet, pure cobalt piece, Pure silicon piece, conductive carbon cloth;
In the phosphate buffer solution PBS containing dopamine, Ammonium Persulfate 98.5 and cobalt nitrate: dopamine concentration is 2 ~ 5 Mg/mL, the concentration of Ammonium Persulfate 98.5 are 3 ~ 8 mg/mL, and the concentration of cobalt nitrate is 0.1 ~ 0.5 mg/mL, phosphate buffer solution PBS Concentration be 0.1 mol/L, pH value be 7.2 ~ 8.5;
3. the system of the MIP of molecularly imprinted polymer containing template molecule of Co-nanoarray growth in situ described in technical solution 1 Preparation Method includes following preparation step:
(1) 0.25 ~ 0.45mmol template molecule and 3 ~ 5 mmol 2- methacrylic acid MAA are weighed respectively in peace times bottle, are added Enter 8 ~ 15 mL acetonitriles, 30 min of ultrasound to whole dissolutions;
(2) 15 ~ 25 mmol ethylene glycol dimethacrylate EDMA are added in the solution of step (1), 30 min of ultrasound To being uniformly mixed, precursor mixed solution is obtained;
(3) Co-nanoarray prepared in technical solution 2 is clipped on Stirring device, the forerunner being inserted into step (2) In body mixed solution, in N2At a temperature of environment and 20 ~ 40 DEG C of water-bath, with 5 ~ 200 revolutions per seconds of speed Stirring, while with 1 ~ 20 drops/sec of speed carries out initiation polymerization to 1 mmol azodiisobutyronitrile AIBN of mixed solution and dripping, in Co- The MIP of molecularly imprinted polymer containing template molecule of growth in situ is obtained on nanoarray;
4. the system without template molecule molecularly imprinted polymer NIP of Co-nanoarray growth in situ described in technical solution 1 Standby step are as follows: by the molecular engram containing template molecule of growth in situ polymerize on Co-nanoarray obtained in technical solution 3 Object MIP is immersed in eluant, eluent, and template molecule is carried out 5 ~ 20 min of elution at room temperature, is then taken out, no template is obtained Molecular imprinted polymer NIP;The eluant, eluent is the mixed liquor of formic acid and methanol, wherein the volume ratio of formic acid and methanol For 9:(1 ~ 5);
5. the preparation step of environmental estrogens electro-chemical analyzing sensor described in technical solution 1 are as follows: by technical solution 2 ~ 4 In the obtained growth in situ on Co-nanoarray without template molecule molecularly imprinted polymer NIP, embathe 2 with deionized water It ~ 4 times, dries at room temperature, obtains environmental estrogens electro-chemical analyzing sensor;
6. being applied to using environmental estrogens electro-chemical analyzing sensor prepared by technical solution described in technical solution 1 ~ 5 The detection of environmental estrogens, including following applying step:
(1) standard solution is prepared: preparing the environmental estrogens standard solution of one group of various concentration including blank standard specimen;
(2) working electrode is modified: being working electrode by environmental estrogens electro-chemical analyzing sensor, is prepared in inserting step (1) Various concentration environmental estrogens standard solution, hatch 10 min after take out, embathed 3 times with deionized water;
(3) working curve is drawn: using saturated calomel electrode electrode as reference electrode, platinum electrode is used as to electrode, with step (2) the working electrode composition three-electrode system modified, connects electrochemical workstation, 15 mL is successively added in a cell Phosphate buffer solution PBS;Pass through the current-responsive of the working electrode of Differential Pulse Voltammetry DPV detection assembling;Blank standard specimen Response current intensity be denoted asI 0, the response current intensity of the environmental estrogens standard solution containing various concentration is denoted asI i, response The difference that current strength reduces is ΔI = I 0-I i, ΔIWith the mass concentration of environmental estrogens standard solutionCBetween linear pass Δ is drawn by systemI?CWorking curve;The phosphate buffer solution PBS concentration is 10 mmol/L, pH value 7.4;Described Parameter setting when DPV is detected are as follows: range and direction are 0 ~ 1 V, and stride is 0.05 V, and the burst length is 0.05 s, when sampling Between be 0.016 s, the pulse period be 0.5 s;
(4) in sample to be tested environmental estrogens detection: replace the environmental estrogens standard in step (1) molten with sample to be tested Liquid is detected according to the method in step (2) and (3), the difference DELTA that current strength reduces according to responseIAnd working curve, Obtain the content of environmental estrogens in sample to be tested;
7. environmental estrogens described in technical solution 1 ~ 6 are one of following environmental estrogens: estradiol, estriol, hexene are female Phenol, bisphenol-A, nonyl phenol.
Beneficial achievement of the invention
(1) environmental estrogens electro-chemical analyzing sensor preparation of the present invention is simple, easy to operate, realizes to sample Quickly, sensitive, highly selective detection, and it is at low cost, it can be applied to portable inspectiont, there is market development prospect;
(2) growth in situ molecular engram polymerize the present invention on cobalt hydroxide nano-chip arrays electrode Co-nanoarray for the first time On the one hand object can grow more, molecularly imprinted polymer more evenly using the big specific surface area of Co-nanoarray, and Co-nanoarray has excellent electron transmission ability, to greatly improve detection sensitivity;On the other hand, the present invention will be more When on bar amine in-situ polymerization to cobalt hydroxide nano-chip arrays, creative is doped into cobalt ions as electron mediator, is examining Electrochemical response electric current is directly generated when survey, allows sensor straight in the buffer solution it is not necessary that other media substance is added Capable detection is tapped into, to greatly reduce testing cost simultaneously while further decreasing signal background, improving detection sensitivity It reduces environmental pollution;
(3) present invention is rich in using cobalt hydroxide nano-chip arrays high activity hydroxy functional group and big specific surface area with Dopamine combines, sufficiently thin poly- more being formed so that dopamine is in cobalt hydroxide nano-chip arrays in situ Polymerization While bar amine film, on uniform fold to cobalt hydroxide nano-chip arrays, thus for more better polymerizable moleculars in next step Imprinted polymer carries out place mat;Later using poly-dopamine to the amino being rich on hydroxy functional group and molecularly imprinted polymer Strong connection function, then dexterously use Co-nanoarray as blender, in molecular engram precursor mixed solution Immersion stirring is carried out, by control mixing speed, the rate of addition and polymeric reaction temperature of initiators for polymerization, in Co- The surface nanoarray direct in-situ grows the molecularly imprinted polymer that can control film thickness, on the one hand makes Co- Nanoarray can secured supporting molecular imprinted polymer, to significantly improve the stability of prepared electrochemical sensor And reproducibility;On the other hand molecularly imprinted polymer can effectively be controlled in the film forming thickness of electrode surface, solving can not control Molecular engram film processed is unable to control the technical problem so as to cause poor reproducibility in electrode surface film forming thickness;In addition, more due to Preparation method of the invention can sufficiently improve molecule print to the in-stiu coating of the effective control and electron mediator of film forming thickness The sensitivity of electrochemical sensor based on mark and detection limit have important scientific meaning and application value.
Specific embodiment
The preparation of 1 Co-nanoarray of embodiment
(1) it will can disposably throw electrode and carry out ultrasonic cleaning processing using dilute hydrochloric acid, dehydrated alcohol and deionization respectively, to go Except the oxide layer and surface impurity that can disposably throw electrode;
(2) 1 mmol Co (NO is weighed3)2With 3 mmol urea CO (NH2)2, it is put into 50 mL beakers, 30 mL is added and go Ionized water stirs to clarify, and is then transferred into 50 mL ptfe autoclaves;
(3) in the disposable solution thrown in the reaction kettle that electrode is put into step (2) for handling step (1) well, 100 It is reacted 12 hours at a temperature of DEG C, cobalt hydroxide nano-chip arrays presoma electrode is prepared;
(4) the cobalt hydroxide nano-chip arrays presoma electrode insertion obtained step (3) contains dopamine, Ammonium Persulfate 98.5 and nitre In the phosphate buffer solution PBS of sour cobalt, 20 DEG C at a temperature of reaction 4 hours after, take out simultaneously embathed 2 times with deionized water, Cobalt hydroxide nano-chip arrays electrode Co-nanoarray is prepared;
The electrode therein that can disposably throw is nickel foam;Dopamine concentration is 2 mg/mL, and the concentration of Ammonium Persulfate 98.5 is 3 mg/mL, The concentration of cobalt nitrate is 0.1 mg/mL, and the concentration of phosphate buffer solution PBS is 0.1 mol/L, pH value 7.2.
The preparation of 2 Co-nanoarray of embodiment
(1) it will can disposably throw electrode and carry out ultrasonic cleaning processing using dilute hydrochloric acid, dehydrated alcohol and deionization respectively, to go Except the oxide layer and surface impurity that can disposably throw electrode;
(2) 2 mmol Co (NO are weighed3)2With 6 mmol urea CO (NH2)2, it is put into 50 mL beakers, 30 mL is added and go Ionized water stirs to clarify, and is then transferred into 50 mL ptfe autoclaves;
(3) in the disposable solution thrown in the reaction kettle that electrode is put into step (2) for handling step (1) well, 110 It is reacted 11 hours at a temperature of DEG C, cobalt hydroxide nano-chip arrays presoma electrode is prepared;
(4) the cobalt hydroxide nano-chip arrays presoma electrode insertion obtained step (3) contains dopamine, Ammonium Persulfate 98.5 and nitre In the phosphate buffer solution PBS of sour cobalt, 30 DEG C at a temperature of reaction 5 hours after, take out simultaneously embathed 3 times with deionized water, Cobalt hydroxide nano-chip arrays electrode Co-nanoarray is prepared;
The electrode therein that can disposably throw is pure copper sheet;Dopamine concentration is 3.5 mg/mL, and the concentration of Ammonium Persulfate 98.5 is 6.2 Mg/mL, the concentration of cobalt nitrate are 0.3 mg/mL, and the concentration of phosphate buffer solution PBS is 0.1 mol/L, pH value 8.0.
The preparation of 3 Co-nanoarray of embodiment
(1) it will can disposably throw electrode and carry out ultrasonic cleaning processing using dilute hydrochloric acid, dehydrated alcohol and deionization respectively, to go Except the oxide layer and surface impurity that can disposably throw electrode;
(2) 3 mmol Co (NO are weighed3)2With 9 mmol urea CO (NH2)2, it is put into 50 mL beakers, 30 mL is added and go Ionized water stirs to clarify, and is then transferred into 50 mL ptfe autoclaves;
(3) in the disposable solution thrown in the reaction kettle that electrode is put into step (2) for handling step (1) well, 130 It is reacted 9 hours at a temperature of DEG C, cobalt hydroxide nano-chip arrays presoma electrode is prepared;
(4) the cobalt hydroxide nano-chip arrays presoma electrode insertion obtained step (3) contains dopamine, Ammonium Persulfate 98.5 and nitre In the phosphate buffer solution PBS of sour cobalt, 40 DEG C at a temperature of reaction 6 hours after, take out simultaneously embathed 4 times with deionized water, Cobalt hydroxide nano-chip arrays electrode Co-nanoarray is prepared;
The electrode therein that can disposably throw is conductive carbon cloth;Dopamine concentration is 5 mg/mL, and the concentration of Ammonium Persulfate 98.5 is 8 mg/ ML, the concentration of cobalt nitrate are 0.5 mg/mL, and the concentration of phosphate buffer solution PBS is 0.1 mol/L, pH value 8.5.
The preparation method of 4 environmental estrogens electro-chemical analyzing sensor of embodiment
(1) 0.25 mmol template molecule and 3 mmol 2- methacrylic acid MAA are weighed respectively in peace times bottle, and 8 mL second are added Nitrile, 30 min of ultrasound to whole dissolutions;
(2) 15 mmol ethylene glycol dimethacrylate EDMA are added in the solution of step (1), 30 min of ultrasound are to mixed It closes uniformly, obtains precursor mixed solution;
(3) Co-nanoarray prepared in embodiment 1 is clipped on Stirring device, the presoma being inserted into step (2) In mixed solution, in N2At a temperature of environment and 20 DEG C of water-bath, with 200 revolutions per seconds of speed Stirring, while with 1 drop/sec Speed carry out initiation polymerization to 1 mmol azodiisobutyronitrile AIBN of mixed solution and dripping, obtained on Co-nanoarray The MIP of molecularly imprinted polymer containing template molecule of growth in situ;
(4) MIP of molecularly imprinted polymer containing template molecule of growth in situ on Co-nanoarray for obtaining step (3) soaks Not in eluant, eluent, template molecule is subjected to 5 min of elution at room temperature, is then taken out, obtains no template molecule molecule print Mark polymer NIP;Continue to be embathed 2 times with deionized water, dry at room temperature, obtains environmental estrogens electrochemical analysis sensing Device;
Eluant, eluent therein is the mixed liquor of formic acid and methanol, and wherein the volume ratio of formic acid and methanol is 9:1.
The preparation method of 5 environmental estrogens electro-chemical analyzing sensor of embodiment
(1) 0.35mmol template molecule and 4 mmol 2- methacrylic acid MAA are weighed respectively in peace times bottle, and 12 mL second are added Nitrile, 30 min of ultrasound to whole dissolutions;
(2) 18 mmol ethylene glycol dimethacrylate EDMA are added in the solution of step (1), 30 min of ultrasound are to mixed It closes uniformly, obtains precursor mixed solution;
(3) Co-nanoarray prepared in technical solution 2 is clipped on Stirring device, the forerunner being inserted into step (2) In body mixed solution, in N2At a temperature of environment and 30 DEG C of water-bath, with 60 revolutions per seconds of speed Stirring, while with 10 drops/sec Speed carry out initiation polymerization to 1 mmol azodiisobutyronitrile AIBN of mixed solution and dripping, obtained on Co-nanoarray The MIP of molecularly imprinted polymer containing template molecule of growth in situ;
(4) MIP of molecularly imprinted polymer containing template molecule of growth in situ on Co-nanoarray for obtaining step (3) soaks Not in eluant, eluent, template molecule is subjected to 10 min of elution at room temperature, is then taken out, obtains no template molecule molecule print Mark polymer NIP;Continue to be embathed 3 times with deionized water, dry at room temperature, obtains environmental estrogens electrochemical analysis sensing Device;
Eluant, eluent therein is the mixed liquor of formic acid and methanol, and wherein the volume ratio of formic acid and methanol is 9:3.
The preparation method of 6 environmental estrogens electro-chemical analyzing sensor of embodiment
(1) 0.45mmol template molecule and 5 mmol 2- methacrylic acid MAA are weighed respectively in peace times bottle, and 15 mL second are added Nitrile, 30 min of ultrasound to whole dissolutions;
(2) 25 mmol ethylene glycol dimethacrylate EDMA are added in the solution of step (1), 30 min of ultrasound are to mixed It closes uniformly, obtains precursor mixed solution;
(3) Co-nanoarray prepared in technical solution 2 is clipped on Stirring device, the forerunner being inserted into step (2) In body mixed solution, in N2At a temperature of environment and 40 DEG C of water-bath, with 5 revolutions per seconds of speed Stirring, while with 20 drops/sec Speed carry out initiation polymerization to 1 mmol azodiisobutyronitrile AIBN of mixed solution and dripping, obtained on Co-nanoarray The MIP of molecularly imprinted polymer containing template molecule of growth in situ;
(4) MIP of molecularly imprinted polymer containing template molecule of growth in situ on Co-nanoarray for obtaining step (3) soaks Not in eluant, eluent, template molecule is subjected to 20 min of elution at room temperature, is then taken out, obtains no template molecule molecule print Mark polymer NIP;Continue to be embathed 4 times with deionized water, dry at room temperature, obtains environmental estrogens electrochemical analysis sensing Device;
Eluant, eluent therein is the mixed liquor of formic acid and methanol, and wherein the volume ratio of formic acid and methanol is 9:5.
The environmental estrogens sensor of 7 embodiment 1 ~ 6 of embodiment preparation, applied to the detection of environmental estrogens, step It is as follows:
(1) standard solution is prepared: preparing the environmental estrogens standard solution of one group of various concentration including blank standard specimen;
(2) working electrode is modified: being working electrode by environmental estrogens electro-chemical analyzing sensor, is prepared in inserting step (1) Various concentration environmental estrogens standard solution, hatch 10 min after take out, embathed 3 times with deionized water;
(3) working curve is drawn: using saturated calomel electrode electrode as reference electrode, platinum electrode is used as to electrode, with step (2) the working electrode composition three-electrode system modified, connects electrochemical workstation, 15 mL is successively added in a cell PBS;Pass through the current-responsive of the working electrode of Differential Pulse Voltammetry DPV detection assembling;The response current intensity of blank standard specimen It is denoted asI 0, the response current intensity of the environmental estrogens standard solution containing various concentration is denoted asI i, response current strength reduction Difference is ΔI = I 0-I i, ΔIWith the mass concentration of environmental estrogens standard solutionCBetween it is linear, draw ΔI?C Working curve;The PBS is the phosphate buffer solution of 10 mmol/L, and the pH value of the phosphate buffer solution is 7.4;Parameter setting when the described DPV detection are as follows: range and direction are 0 ~ 1 V, and stride is 0.05 V, burst length 0.05 S, sampling time are 0.016 s, and the pulse period is 0.5 s;
(4) in sample to be tested environmental estrogens detection: replace the environmental estrogens standard in step (1) molten with sample to be tested Liquid is detected according to the method in step (2) and (3), the difference DELTA that current strength reduces according to responseIAnd working curve, Obtain the content of environmental estrogens in sample to be tested.
The environmental estrogens sensor of 8 embodiment 1 ~ 6 of embodiment preparation, is applied to according to the detecting step of embodiment 7 The detection of varying environment estrogen, the range of linearity and detection limit are shown in Table 1:
The detection technique index of 1 environmental estrogens of table
The detection of environmental estrogens in 9 milk of embodiment
Milk sample is accurately pipetted, the environmental estrogens standard solution of certain mass concentration is added, environmental estrogens not to be added Milk be blank, carry out recovery testu, with embodiment 1 ~ 6 prepare environmental estrogens sensor, according to embodiment 7 Step is detected, and the rate of recovery of environmental estrogens in milk sample is measured, and testing result is shown in Table 2:
The testing result of environmental estrogens in 2 milk of table
2 testing result of table it is found that the relative standard deviation (RSD) of result less than 3.0 %, average recovery rate is 98.0 ~ 101.6%, show that the present invention can be used for the detection of a variety of environmental estrogens in milk, the high sensitivity of method, high specificity, knot Fruit is accurate and reliable.
The detection of environmental estrogens in 10 water sample of embodiment
Certain water sample is accurately pipetted, the environmental estrogens standard solution of certain mass concentration is added, environmental estrogens not to be added Water sample be blank, carry out recovery testu, with embodiment 1 ~ 6 prepare environmental estrogens sensor, according to embodiment 7 Step is detected, and the rate of recovery of environmental estrogens in water sample is measured, and testing result is shown in Table 3:
The testing result of environmental estrogens in 3 water sample of table
For 3 testing result of table it is found that the relative standard deviation (RSD) of result is less than 3.0 %, average recovery rate is 98.4 ~ 102%, Show that the present invention can be used for the detection of a variety of environmental estrogens in water sample, as a result the high sensitivity of method, high specificity accurately may be used It leans on.

Claims (7)

1.一种环境雌激素电化学分析传感器的制备方法,其特征在于,所述的环境雌激素电化学分析传感器由氢氧化钴纳米片阵列电极Co-nanoarray上原位生长无模板分子分子印迹聚合物NIP得到的;所述的无模板分子分子印迹聚合物NIP是不含有模板分子的分子印迹聚合物;所述的不含有模板分子的分子印迹聚合物是由含模板分子分子印迹聚合物MIP经过洗脱模板分子得到的;所述的含模板分子分子印迹聚合物MIP是含有模板分子的分子印迹聚合物;所述的模板分子是环境雌激素。1. a preparation method of environmental estrogen electrochemical analysis sensor, is characterized in that, described environmental estrogen electrochemical analysis sensor is by cobalt hydroxide nanosheet array electrode Co-nanoarray in situ growth without template molecular molecular imprinting polymerization The molecularly imprinted polymer NIP without template molecule is a molecularly imprinted polymer without template molecule; the molecularly imprinted polymer without template molecule is obtained by the molecularly imprinted polymer MIP containing template molecule The template molecule is obtained by elution; the template molecule-containing molecularly imprinted polymer MIP is a template molecule-containing molecularly imprinted polymer; the template molecule is environmental estrogen. 2.如权利要求1所述的氢氧化钴纳米片阵列电极Co-nanoarray其特征在于,所述的Co-nanoarray的制备方法包括以下制备步骤:2. The cobalt hydroxide nanosheet array electrode Co-nanoarray as claimed in claim 1 is characterized in that, the preparation method of described Co-nanoarray comprises the following preparation steps: (1)将一次性可抛电极分别使用稀盐酸、无水乙醇和去离子进行超声清洗处理,用以去除一次性可抛电极的氧化层和表面杂质;(1) The disposable disposable electrode is ultrasonically cleaned with dilute hydrochloric acid, anhydrous ethanol and deionization to remove the oxide layer and surface impurities of the disposable disposable electrode; (2)称取1~3 mmol Co(NO3)2和3~9 mmol尿素CO(NH2)2,将其置入50 mL烧杯中,加入30mL去离子水搅拌至澄清,然后转移到50 mL聚四氟乙烯反应釜中;(2) Weigh 1~3 mmol Co(NO 3 ) 2 and 3~9 mmol urea CO(NH 2 ) 2 , put them into a 50 mL beaker, add 30 mL deionized water, stir until clear, and then transfer to 50 mL polytetrafluoroethylene reactor; (3)将步骤(1)处理好的一次性可抛电极放入步骤(2)中的反应釜里的溶液中,在100~130 ℃的温度下反应9~12小时,制备得到氢氧化钴纳米片阵列前驱体电极;(3) Putting the disposable disposable electrode processed in step (1) into the solution in the reaction kettle in step (2), and reacting at a temperature of 100-130 ° C for 9-12 hours to prepare cobalt hydroxide Nanosheet array precursor electrode; (4)将步骤(3)得到的氢氧化钴纳米片阵列前驱体电极插入含有多巴胺、过硫酸胺和硝酸钴的磷酸盐缓冲溶液PBS中,在20~40 ℃的温度下反应4~6小时后,取出并用去离子水浸洗2~4次,制备得到氢氧化钴纳米片阵列电极Co-nanoarray;(4) Insert the cobalt hydroxide nanosheet array precursor electrode obtained in step (3) into a phosphate buffered solution PBS containing dopamine, ammonium persulfate and cobalt nitrate, and react at a temperature of 20-40 °C for 4-6 hours Then, take it out and rinse it with deionized water for 2 to 4 times to prepare the cobalt hydroxide nanosheet array electrode Co-nanoarray; 所述的一次性可抛电极选自下列电极之一:泡沫镍、泡沫铜、纯镍片、纯铜片、纯钴片、纯硅片、导电碳布;The disposable disposable electrode is selected from one of the following electrodes: nickel foam, copper foam, pure nickel sheet, pure copper sheet, pure cobalt sheet, pure silicon sheet, and conductive carbon cloth; 所述的含有多巴胺、过硫酸胺和硝酸钴的磷酸盐缓冲溶液PBS中:多巴胺浓度为2~5mg/mL,过硫酸胺的浓度为3~8 mg/mL,硝酸钴的浓度为0.1~0.5 mg/mL,磷酸盐缓冲溶液PBS的浓度为0.1 mol/L,pH值为7.2~8.5。In the phosphate buffered solution PBS containing dopamine, ammonium persulfate and cobalt nitrate: the concentration of dopamine is 2-5 mg/mL, the concentration of amine persulfate is 3-8 mg/mL, and the concentration of cobalt nitrate is 0.1-0.5 mg/mL, the concentration of phosphate buffer solution PBS is 0.1 mol/L, and the pH value is 7.2~8.5. 3.如权利要求1所述的含模板分子分子印迹聚合物MIP,其特征在于,所述的含模板分子分子印迹聚合物MIP是直接原位生长在Co-nanoarray上的,制备方法包括以下制备步骤:3. The template-containing molecularly imprinted polymer MIP as claimed in claim 1, wherein the template-containing molecularly imprinted polymer MIP is directly grown on Co-nanoarray in situ, and the preparation method comprises the following preparations step: (1)分别称取0.25~ 0.45mmol模板分子和3~5 mmol 2-甲基丙烯酸MAA于安倍瓶中,加入8~15 mL乙腈,超声30 min至全部溶解;(1) Weigh 0.25-0.45 mmol of template molecule and 3-5 mmol of 2-methacrylic acid MAA into an ampoule bottle, add 8-15 mL of acetonitrile, and sonicate for 30 min to dissolve completely; (2)将15~25 mmol 乙二醇二甲基丙烯酸酯EDMA加入到步骤(1)的溶液中,超声30 min至混合均匀,得到前驱体混合溶液;(2) Add 15-25 mmol of ethylene glycol dimethacrylate EDMA to the solution of step (1), ultrasonicate for 30 min to mix uniformly, and obtain a precursor mixed solution; (3)将Co-nanoarray夹到旋转搅拌器上,插入到步骤(2)中的前驱体混合溶液中,在N2环境和水浴20~40℃的温度下,以5~200转/秒的速度旋转搅拌,同时以1~20滴/秒的速度向混合溶液中滴加1 mmol偶氮二异丁腈AIBN进行引发聚合,在Co-nanoarray上得到原位生长的含模板分子分子印迹聚合物MIP。(3) Clamp the Co-nanoarray onto a rotary stirrer, insert it into the precursor mixed solution in step (2), under a N2 environment and a water bath temperature of 20–40 °C, at 5–200 rpm. Rotate and stir at a high speed, and at the same time add 1 mmol azobisisobutyronitrile AIBN to the mixed solution at a rate of 1~20 drops/s to initiate the polymerization, and obtain the in situ growth of the molecularly imprinted polymer containing the template molecule on the Co-nanoarray. MIPs. 4.如权利要求1所述的无模板分子分子印迹聚合物NIP,其特征在于所述的无模板分子分子印迹聚合物NIP的制备步骤为:将权利要求3中得到的在Co-nanoarray上原位生长的含模板分子分子印迹聚合物MIP浸没于洗脱剂中,在室温下将模板分子进行洗脱5~20 min,然后取出,即制得无模板分子分子印迹聚合物NIP;所述的洗脱剂为甲酸和甲醇的混合液,其中甲酸与甲醇的体积比为9:(1~5)。4. the template-free molecularly imprinted polymer NIP as claimed in claim 1, wherein the preparation step of the template-free molecularly imprinted polymer NIP is: The template molecule-containing molecularly imprinted polymer MIP grown in situ is immersed in the eluent, and the template molecule is eluted at room temperature for 5-20 min, and then taken out to obtain the template-free molecularly imprinted polymer NIP; the described The eluent is a mixture of formic acid and methanol, wherein the volume ratio of formic acid to methanol is 9:(1~5). 5.如权利要求1所述的环境雌激素电化学分析传感器的制备步骤为:将权利要求2~4中制得的在Co-nanoarray上原位生长的无模板分子分子印迹聚合物NIP,用去离子水浸洗2~4次,室温下晾干,即制得环境雌激素电化学分析传感器。5. The preparation step of the environmental estrogen electrochemical analysis sensor as claimed in claim 1 is: the molecularly imprinted polymer NIP without template molecules grown in situ on the Co-nanoarray obtained in claims 2 to 4, using Immersion in deionized water for 2 to 4 times and air drying at room temperature to prepare an environmental estrogen electrochemical analysis sensor. 6.采用权利要求1~5所述的制备方法所制备的环境雌激素电化学分析传感器,应用于环境雌激素的检测,其特征在于,所述的检测步骤如下:6. adopt the environmental estrogen electrochemical analysis sensor prepared by the preparation method of claim 1 to 5, be applied to the detection of environmental estrogen, and it is characterized in that, described detection step is as follows: (1)标准溶液配制:配制一组包括空白标样在内的不同浓度的环境雌激素标准溶液;(1) Standard solution preparation: prepare a group of environmental estrogen standard solutions of different concentrations including blank standard samples; (2)工作电极修饰:将环境雌激素电化学分析传感器为工作电极,插入步骤(1)中配制的不同浓度的环境雌激素标准溶液,孵化10 min后取出,用去离子水浸洗3次;(2) Working electrode modification: Take the environmental estrogen electrochemical analysis sensor as the working electrode, insert the environmental estrogen standard solution of different concentrations prepared in step (1), take it out after incubation for 10 min, and rinse it with deionized water 3 times. ; (3)工作曲线绘制:将饱和甘汞电极电极作为参比电极,铂丝电极作为对电极,与步骤(2)所修饰好的工作电极组成三电极系统,连接电化学工作站,在电解槽中先后加入15 mL磷酸盐缓冲溶液PBS;通过微分脉冲伏安法DPV检测组装的工作电极的电流响应;空白标样的响应电流强度记为I 0,含有不同浓度的环境雌激素标准溶液的响应电流强度记作I i,响应电流强度降低的差值为ΔI = I 0-I i,ΔI与环境雌激素标准溶液的质量浓度C之间成线性关系,绘制ΔIC工作曲线;所述的磷酸盐缓冲溶液PBS浓度为10 mmol/L,其pH值为7.4;所述的DPV检测时的参数设置为:范围和方向为0~1 V,步幅为0.05 V,脉冲时间为0.05 s,采样时间为0.016 s,脉冲周期为0.5 s;(3) Drawing of the working curve: the saturated calomel electrode is used as the reference electrode, the platinum wire electrode is used as the counter electrode, and the working electrode modified in step (2) forms a three-electrode system, which is connected to the electrochemical workstation and placed in the electrolytic cell. 15 mL of phosphate buffered solution PBS was added successively; the current response of the assembled working electrode was detected by differential pulse voltammetry DPV; the response current intensity of the blank standard was marked as I 0 , and the response current of the standard solutions containing different concentrations of environmental estrogen The intensity is denoted as I i , the difference in response to the decrease in current intensity is Δ I = I 0 - I i , and there is a linear relationship between Δ I and the mass concentration C of the environmental estrogen standard solution, and the Δ I - C working curve is drawn; The described phosphate buffered solution PBS concentration is 10 mmol/L, and its pH value is 7.4; the parameters during the described DPV detection are set as: range and direction are 0 ~ 1 V, step is 0.05 V, and pulse time is 0.05 s, the sampling time is 0.016 s, and the pulse period is 0.5 s; (4)待测样品中环境雌激素的检测:用待测样品代替步骤(1)中的环境雌激素标准溶液,按照步骤(2)和(3)中的方法进行检测,根据响应电流强度降低的差值ΔI和工作曲线,得到待测样品中环境雌激素的含量。(4) Detection of environmental estrogen in the sample to be tested: replace the standard solution of environmental estrogen in step (1) with the sample to be tested, and perform the detection according to the methods in steps (2) and (3), and decrease according to the response current intensity The difference ΔI and the working curve are obtained to obtain the content of environmental estrogen in the sample to be tested. 7.如权利要求1~6所述的环境雌激素是下列环境雌激素之一:雌二醇、雌三醇、己烯雌酚、双酚A、壬基酚。7. The environmental estrogen of claim 1 to 6 is one of the following environmental estrogens: estradiol, estriol, diethylstilbestrol, bisphenol A, nonylphenol.
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