CN1673732A - Method for measuring density of organic phosphorus insecticide - Google Patents

Method for measuring density of organic phosphorus insecticide Download PDF

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CN1673732A
CN1673732A CN200510038059.0A CN200510038059A CN1673732A CN 1673732 A CN1673732 A CN 1673732A CN 200510038059 A CN200510038059 A CN 200510038059A CN 1673732 A CN1673732 A CN 1673732A
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electrode
insecticide
enzyme
solution
assay method
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CN100348971C (en
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鞠熀先
维卫克·巴布·坎地马拉
陈进
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Nanjing University
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Nanjing University
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Abstract

The present invention discloses the measurement method of organophosphorus pesticide concentration. The method includes mainly preparing biosensor, measurement to obtain oxidation current I0 of choline and suppression factor I% of organophosphorus on enzyme activity, and detecting the concentration of the same kind of organophosphorus pesticide based on the linear relation between the suppression factor I% and the organophosphorus pesticide concentration. The present invention is simple, feasible and low in cost, and has fast detection speed and high efficiency.

Description

The assay method of density of organic phosphorus insecticide
One, technical field
The present invention relates to a kind of assay method of pesticide, relate in particular to a kind of organic phosphorous insecticide assay method.
Two, background technology
Organic phosphorus compound is widely used in agricultural and other field, for example vegetation control, lawn desinsection or the like.This compounds toxicity is very strong, the activity of inhibitory enzyme irreversibly, thus influence the function of human central nervous system, usually cause the respiratory system paralysis, seriously can cause death.Thereby being extensive use of of organic phosphorus compound directly threatening human health, in use influences human health for preventing organic phosphorus compound, need be to it is detected.Therefore, quick, sensitive, the special and stable organic phosphorus detection method of research urgently is important.At present, chromatographic technique has been used for the organic phosphorous insecticide specificity is detected, but this detection method needs the testing staff of specialty to operate, and needs sample is carried out pre-service before detection, and cost is higher, and is unfavorable for open-air the detection.
Three, summary of the invention
1, goal of the invention: the purpose of this invention is to provide a kind of assay method of operating the density of organic phosphorus insecticide fast and convenient, that measuring accuracy is high, cost is low.
2, technical scheme: in order to realize the foregoing invention purpose, organic phosphorous insecticide assay method of the present invention comprises the following steps:
(1) enzyme is dripped be coated in the surface have again on the electrode surface of cross-linked chitosan-multiple-wall carbon nanotube film, obtain biology sensor;
(2) with the working electrode of above-mentioned biology sensor as electrochemical analyser, place reaction tank, flow then and inject substrate, make the enzyme-to-substrate reaction of above-mentioned electrode surface produce choline, obtain the oxidation current value I of choline again with the electrochemical analyser test with electrochemical activity 0
(3) with behind the mobile cleaning electrode of carrier fluid, injecting with this carrier fluid in reaction tank is the organophosphorus insecticide solution of solvent, and organophosphorus insecticide solution is resident in reaction tank, uses the carrier fluid cleaning electrode then;
(4) the mobile again substrate that injects in reaction tank is tested the oxidation current I that obtains choline with electrochemical analyser t
(5) according to following formula:
I % = I 0 - I t I 0 × 100
Calculate the inhibiting value I% of the activity of the irreversible inhibition cholinesterase of organophosphorus, repeating step (2) records corresponding I again to (4) then 0And I t, and calculate I% mean value, the I% logarithm of averaging;
(6) concentration of change organophosphorus insecticide solution, repeat above-mentioned step (2) to (5), obtain the logarithm of above-mentioned inhibiting value I% and the linear relationship between the density of organic phosphorus insecticide, utilize the quantitative measurement of gained linear relationship to go out organic phosphorous insecticide concentration.
Wherein in step (1), the preparation of biology sensor comprises the following steps:
(1) with glutaraldehyde and the mixed stirring of chitosan solution, obtains mixed solution;
(2) multiple-wall carbon nanotube is added above-mentioned solution, obtain the mixed solution of cross-linked chitosan-multiple-wall carbon nanotube;
(3) above-mentioned cross-linked chitosan-multiple-wall carbon nanotube mixed solution is dripped on the electrode that is coated onto surface cleaning, dry back cleaning electrode is removed unnecessary glutaraldehyde, obtains being compounded with at electrode surface the film of cross-linked chitosan-multiple-wall carbon nanotube;
(4) drips of solution of enzyme is coated in the surface of above-mentioned film, obtains biology sensor.
Electrode used therein can be glass-carbon electrode in the preparation process of biology sensor, and described biology sensor can recover the activity of enzyme with multiple enzyme agent, and used enzyme can be acetylcholinesterase.
In the step (2) of the assay method of machine phosphorus insecticide, substrate can be the acetyl chloride thiocholine, and in step (3), carrier fluid can be Klorvess Liquid.
The present invention utilizes organophosphorus composition in the organophosphorus insecticide to the inhibited principle of the biologically active of enzyme, utilize the enzyme on the cross-linked chitosan-multiple-wall carbon nanotube composite membrane that is fixed on electrode surface well to contact with organophosphorus insecticide solution, detect the variation of reacting the active mark of front and back enzyme with the organophosphorus composition, thereby can draw the logarithm of its active inhibiting value, organophosphorus insecticide with variable concentrations carries out the detection that enzymatic activity suppresses mark again, then can obtain the linear relationship between enzymatic activity inhibiting value and the density of organic phosphorus insecticide, so just can utilize this linear relationship to detect the concentration value of the detection sample of a certain organophosphorus pesticide.Cross-linked chitosan-multiple-wall carbon nanotube composite membrane is a kind of bionical interface, have hypotoxicity, water wettability, good chemical stability and bio-compatibility and electronic conductivity, help the fixing of biomolecule, the present invention promptly is these characteristics of utilizing this composite membrane, the enzyme of biologically active is fixed on its surface to detect, and can utilize pralidoxime to remove activated centre--the organophosphorus group of combination on the serine of enzyme, thereby can recover the activity of enzyme, can reuse the electrode that is fixed with enzyme and detect.
3, beneficial effect: the present invention has the following advantages:
(1) used electrochemical apparatus and flowing injection device convenient and flexible operation, reagent consumption are less, cost is lower, analysis speed is fast, are applicable to the organic phosphorous insecticide fast detecting.
(2) utilize this natural macromolecular material of shitosan and CNT composite membrane immobilized enzyme molecule to have result of use preferably, this composite membrane is inexpensive, hypotoxicity, preparation are simple, and has good conduction, chemical stability and bio-compatibility.
(3) composite membrane and enzyme are fixedly combined in an electrode surface, the immobilization technology of enzyme is applied to organic phosphorous insecticide mensuration field, utilize the Flow Injection Analysis device, thereby the consumption of enzyme reagent place requirement and other reagent is few, minute is short, thereby has reduced cost of determination;
(4) this method shows good accuracy, repeatability and stable, and the preparation method is simple, but duplicate detection often, and the more existing organophosphorus insecticide assay method of detectability is much lower as electrochemical detection method.
Four, description of drawings
Accompanying drawing is an assay method synoptic diagram of the present invention.
Five, embodiment
Embodiment 1: as shown in the figure, peristaltic pump 1 is used for importing insecticide solution, substrate, loading and multiple enzyme buffer liquid to reaction tank, working electrode 3 is connected to 7, three electrodes of electrochemical analytical instrument with auxiliary electrode 2 and contrast electrode 4 to be placed in the reaction tank 5 for being combined with the electrode of enzyme; Electrochemical analytical instrument 7 is connected to computing machine 8, is handled the measuring-signal of electrochemical analyser output by Computer Analysis.Present embodiment is a detected object with the sulfotep pesticide, the enzyme that adopts is an acetylcholinesterase, and substrate is the acetyl chloride thiocholine, and carrier fluid is the 0.1M pH7.4 PBS solution that contains 0.1M KCl, multiple enzyme buffer liquid is pralidoxime solution, adopts BAS 100B electrochemical analytical instrument.
For obtaining optimum detection signal and sensitivity, the content of shitosan will satisfy the required amount of immobilized enzyme in the composite membrane, and it is dry and cracked that the film of preparation is difficult for, and helps the electrochemical oxidation of the load of enzyme and enzymatic reaction subsequently and product; Though multiple-wall carbon nanotube helps the conduction of electronics, if too high levels, the composite membrane biological affinity will descend, and therefore will control the content of multiple-wall carbon nanotube; The charge capacity of enzyme directly by crosslinked chitosan film with aldehyde radical quantity determined that so the content of glutaraldehyde and shitosan and multiple-wall carbon nanotube should guarantee best ratio.In addition, concentration by changing the pH value apply current potential, buffer solution, substrate respectively and flow injection speed and sulfotep be in the residence time of flow cell, and the value of correspondence is as the sulfotep optimum determining condition when selecting to reach maximum current and responding.Below be the optimization method of biology sensor preparation and sulfotep flow injection Electrochemical Detection condition:
1, determining of the optimization preparation condition of biology sensor: by changing shitosan in the composite membrane respectively, the content of multiple-wall carbon nanotube and glutaraldehyde, the value of correspondence is as the biology sensor optimum preparating condition when selecting to reach the maximum current response.Its testing process is: adopt BAS 100B electrochemical analytical instrument, three-electrode system carries out electrochemical measurement, and wherein, platinum filament is as auxiliary electrode, and Ag/AgCl is as contrast electrode, and enzyme modification GCE is as working electrode.The 0.1M pH7.4 PBS solution that contains 0.1M KCl is as carrier fluid; At room temperature, in reaction tank, apply with respect to the Ag/AgCl electrode and carry out electrochemical gaging for the potential step of+600mV; After the baseline of current signal is steady, add substrate acetyl chloride thiocholine in the system; Insert three electrodes in the flow system and be connected to BAS 100B (seeing accompanying drawing).The sample injection speed is controlled to be 0.5mL min -1, carrier fluid is PBS.Change shitosan successively, the content of multiple-wall carbon nanotube and glutaraldehyde, the electrochemical response signal of record sensor, can draw: the optimal conditions of preparation biology sensor is a shitosan, the content of multiple-wall carbon nanotube and glutaraldehyde is respectively 0.45 (w/v) %, 0.13 (w/v) % and 1.26 (v/v) %;
2, the optimal conditions of sulfotep flow injection Electrochemical Detection: in Electrochemical Detection, different potentials is influential to the steady-state current signal of enzymatic reaction product, can take potentiostatic method to carry out, and under the current potential that is fit to, the gained current responsing signal has maximal value; Because enzyme just has optimum activity under the normal pH condition of human body, so the pH value of buffer solution should be consistent with the human body normal ph; Substrate A TC1 is injected in the reaction tank continuously, carries out Electrochemical Detection, the gained current signal has maximal value under certain ATC1 concentration; The speed of flow of substrates injection has directly determined the performance of sensor; Sulfotep directly influences inhibition degree to the electrode surface activity of the immobilized enzyme in the residence time in reaction tank pond, according to above principle, apply the pH value of current potential, buffer solution, concentration and the flow injection speed and the residence time of sulfotep in reaction tank of substrate by changing respectively, the value that selection reaches maximum current when response correspondence is as the sulfotep optimum determining condition: current potential is+600mV, the pH of buffer solution is 7.4, the concentration of substrate is 500 μ M, and flow velocity is 0.5mL min -1, sulfotep is 14 minutes in the residence time of flow cell.
Carry out the detection of sulfotep insecticide concentration according to above-mentioned optimized condition below:
1. acetylcholinesterase is fixed:
(1) polishing electrode: 3mm plate-like glass-carbon electrode is used 1.0 respectively, 0.3 and the polishing on chamois leather of the outstanding slurry of the Alpha-alumina of 0.05 μ m is minute surface, secondary water is rinsed well, uses 1: 1 nitric acid, acetone, the ultrasonic cleaning of secondary water more successively, obtains fresh, clean electrode surface.
(2) preparation of composite membrane solution: get an amount of 25% glutaraldehyde and the mixed 10min of stirring of 0.5% chitosan solution.The 1.3mg multiple-wall carbon nanotube adds the above-mentioned mixed solution of 1.0mL then, and is ultrasonic evenly mixed to solution.
(3) formation of cross-linked chitosan-multiple-wall carbon nanotube composite membrane: mixed solution places the good GCE of pre-service among the 3.0 μ L (2), in 25 ℃ down reaction 4 hours obtain cross-linked chitosan-multiple-wall carbon nanotube composite membrane at electrode surface.Modified electrode cleans up to remove unnecessary glutaraldehyde with secondary water.
(4) acetylcholinesterase is fixing: get 2.0 μ L phatidylcholine esterase (10mIU) drips of solution and be applied to the complex film modified electrode surface of above-mentioned cross-linked chitosan-multiple-wall carbon nanotube, 25 ℃ of incubations 30 minutes, by acetylcholinesterase being combined with composite membrane, realize the fixing of acetylcholinesterase with the free aldehyde radical of the glutaraldehyde of shitosan bonding.After moisture drying removed, remove unconjugated acetylcholinesterase with the PBS washing and make required biology sensor sensor and preserve down in-20 ℃.
2, acetylcholinesterase suppresses to measure
At first, with the substrate acetyl chloride thiocholine adding flow duct 6 of 500 μ M, the gained current signal is designated as I 0(volume 250 μ L, flow velocity is 0.5mL min -1), use carrier fluid with 1.0mL min -1Flow velocity cleaning electrode injected 0.5mL sulfotep solution after 2 minutes, stopped 14 minutes in reaction tank, used carrier fluid with 1.0mL min then -1Flow velocity cleaning electrode 2 minutes adds 500 μ M substrate acetyl chloride thiocholine gained current signals again and is designated as I tSuppress mark (I%) and calculate, get its mean value after three measurements by following equation.
I % = I 0 - I t I 0 × 100
3, change the concentration of sulfotep pesticide, the electrochemical response that obtains when measuring variable concentrations according to inhibition mark (I%) logarithm that calculates gained and the linear relationship between sulfotep concentration, can carry out the quantitative measurement of sulfotep concentration.The concentration range that detects sulfotep is 1.5-80nM, and detectability is 1.0nM when I%=10%.
In addition, the regenerant of pralidoxime can be adopted, the organophosphorus group of combination on the acetylcholine esterase active central hair propylhomoserin can be removed by pralidoxime as acetylcholinesterase.When working electrode with after sulfotep agrochemical organophosphorus insecticide contacts, with carrier fluid with 1.0mL min -1Flow velocity cleaning electrode with 5.0mM pralidoxime regeneration 15 minutes, uses carrier fluid with 1.0mL min after 2 minutes again -1Flow velocity cleaned 2 minutes.The current signal I of available substrates rRepresent enzymatic activity.Equation below enzyme regeneration efficiency (R%) is available is represented:
R % = I r - I t I 0 - I t × 100
This method can make the working electrode continuous detecting and regenerate 15 times, and the regeneration efficiency that guarantees enzyme is more than 95%.

Claims (7)

1, a kind of assay method of density of organic phosphorus insecticide is characterized in that: this method comprises the following steps:
(1) enzyme is dripped be coated in the surface have again on the electrode surface of cross-linked chitosan-multiple-wall carbon nanotube film, obtain biology sensor;
(2) with the working electrode of above-mentioned biology sensor as electrochemical analyser, place reaction tank, flow then and inject substrate, make the enzyme-to-substrate reaction of above-mentioned electrode surface produce choline, obtain the oxidation current value I of choline again with the electrochemical analyser test with electrochemical activity 0
(3) with behind the mobile cleaning electrode of carrier fluid, injecting with this carrier fluid in reaction tank is the organophosphorus insecticide solution of solvent, and organophosphorus insecticide solution is resident in reaction tank, uses the carrier fluid cleaning electrode then;
(4) the mobile again substrate that injects in reaction tank is tested the oxidation current I that obtains choline with electrochemical analyser t
(5) according to following formula:
I % = I 0 - I t I 0 100
Calculate the inhibiting value I% of the activity of the irreversible inhibition cholinesterase of organophosphorus, repeating step (2) records corresponding I again to (4) then 0And I t, and calculate the mean value of I%, the logarithm of the I% that averages;
(6) concentration of change organophosphorus insecticide solution, repeat above-mentioned step (2) to (5), obtain the logarithm of above-mentioned inhibiting value I% and the linear relationship between the density of organic phosphorus insecticide, utilize the quantitative measurement of gained linear relationship to go out organic phosphorous insecticide concentration.
2, the assay method of density of organic phosphorus insecticide as claimed in claim 1 is characterized in that: the preparation of biology sensor comprises the following steps: in the step (1)
(1) with glutaraldehyde and the mixed stirring of chitosan solution, obtains mixed solution;
(2) multiple-wall carbon nanotube is added above-mentioned solution, obtain the mixed solution of cross-linked chitosan-multiple-wall carbon nanotube;
(3) above-mentioned cross-linked chitosan-multiple-wall carbon nanotube mixed solution is dripped on the electrode that is coated onto surface cleaning, dry back cleaning electrode is removed unnecessary glutaraldehyde, obtains being compounded with at electrode surface the film of cross-linked chitosan-multiple-wall carbon nanotube;
(4) drips of solution of enzyme is coated in the surface of above-mentioned film, obtains biology sensor.
3, the assay method of density of organic phosphorus insecticide as claimed in claim 2 is characterized in that: the electrode that uses in the step (3) is glass-carbon electrode.
4, the assay method of density of organic phosphorus insecticide as claimed in claim 2 is characterized in that: described biology sensor can recover the activity of enzyme with multiple enzyme agent.
5, the assay method of machine phosphorus insecticide concentration as claimed in claim 2 is characterized in that: the enzyme in the step (4) is an acetylcholinesterase.
6, the assay method of machine phosphorus insecticide concentration as claimed in claim 1 is characterized in that: the substrate in the step (2) is the acetyl chloride thiocholine.
7, the assay method of machine phosphorus insecticide concentration as claimed in claim 1 is characterized in that: the carrier fluid in the step (3) is a Klorvess Liquid.
CNB2005100380590A 2005-03-10 2005-03-10 Method for measuring density of organic phosphorus insecticide Expired - Fee Related CN100348971C (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101082599B (en) * 2006-06-01 2010-10-13 五鼎生物技术股份有限公司 Device for analyzing enzyme inhibitors and method thereof
CN102304558A (en) * 2011-05-25 2012-01-04 青岛大学 Method for analyzing inhibition of immobilized flow injection enzyme
CN102507714A (en) * 2011-11-07 2012-06-20 华中师范大学 Method for detecting biomarker of organophosphorus pesticide
CN104198559A (en) * 2014-09-15 2014-12-10 常熟理工学院 Electrochemical biosensor for organic phosphorus pesticide detection and preparation method of electrochemical biosensor

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
RU2175352C1 (en) * 2000-05-11 2001-10-27 Саратовский государственынй аграрный университет имени Н.И. Вавилова Method of determination of concentration of insecticide metaphos and product of hydrolysis of organophosphorus nitro-aromatic insecticides of para-nitrophenol in aqueous medium
JP3924472B2 (en) * 2002-02-05 2007-06-06 株式会社ジェイテクト Sensors using carbon nanotubes
CN100376890C (en) * 2003-08-18 2008-03-26 中国海洋大学 Detecting method of organic phosphorus pesticide and its device
CN1277116C (en) * 2004-03-22 2006-09-27 南开大学 Biological enzyme electrode for biosensor, and its prepn. method

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101082599B (en) * 2006-06-01 2010-10-13 五鼎生物技术股份有限公司 Device for analyzing enzyme inhibitors and method thereof
CN102304558A (en) * 2011-05-25 2012-01-04 青岛大学 Method for analyzing inhibition of immobilized flow injection enzyme
CN102507714A (en) * 2011-11-07 2012-06-20 华中师范大学 Method for detecting biomarker of organophosphorus pesticide
CN104198559A (en) * 2014-09-15 2014-12-10 常熟理工学院 Electrochemical biosensor for organic phosphorus pesticide detection and preparation method of electrochemical biosensor

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