WO2005064331A1

WO2005064331A1 - Method and kit for pesticide analysis

Info

Publication number: WO2005064331A1
Application number: PCT/IN2003/000446
Authority: WO
Inventors: Munna Singh Thakur; Naikankatte Ganesh Karanth; Mysore Anantharamaiah Kumar; Bangalore Eshwar Amita Rani; Akimal Pasha; Nittiru Gopala Krishna Karanth
Original assignee: Council Of Scientific And Industrial Research
Priority date: 2003-12-31
Filing date: 2003-12-31
Publication date: 2005-07-14
Also published as: JP2007531862A; ATE396397T1; CN1886660A; DE60321244D1; AU2003300703A1; EP1700117B1; EP1700117A1

Abstract

A method for rapid detection of pesticide at ppt level using immunochemiluminescence is diclosed. The method comprises packing immobilized antibodies packed in a glass capillary column, passing a sample solution to be tested for pesticide content through said column so that a pesticide-antibody conjugate is formed, removing said pesticide-antibody conjugate from the column and adding thereto, urea H202 followed by Luminol and K3Fe(CN)6, mixing said solution thoroughly until light is generated, and capturing the light generated by a CCD camera, the intensity of the light produced being directly proportional to the amount of pesticide content in said sample. The present invention also discloses a kit for carrying out the method of the present invention.

Description

METHOD AND KIT FOR PESTICIDE ANALYSIS

Field of the invention The present invention provides a rapid test kit for pesticide analysis based on charge coupled device. The present invention also provides a method for the manufacture of a charge coupled device based test kit for pesticide analysis and to the use thereof for determination of pesticide levels in water, food and environment. Background of the invention Environmental protection in connection with water and agriculture need urgent attention for human health. Major health problems occur due to the use of contaminated water and food. Application of organochlorine and organophosphosporous pesticides in agriculture has been practiced in many countries. As a result of increased use of pesticides in agriculture in the last few decades, ground water, raw food materials and processed food are becoming contaminated with pesticide residues. The pollution monitoring and protection agencies need rapid and sensitive methods for the analysis of pollutants. The commonly used analytical methods for pesticide analysis include Liquid chromatography, Gas chromatography and ELISA methods (Lehotay, S.J., analysis of pesticide residues in mixed fruit and vegetable extracts by direct sample introduction Gas chromatography/tandem mass spectrometry, J. AOAC Int., 2002, 83, 680-697; Sasaki. K., Suzuki.K., and Sito. Y., (1987) 'A simplified cleanup and gas chromatographic determination of organophosphorous pesticides in crops' Journal of the Association of Official analytical Chemists International, 70, 460-464. Fernandez. M., Pico, Y., Girotti, S., Manes, J., 'Analysis of organophosphorous pesticides in honey bee by liquid chromatography-atmospheric pressure chemical ionization- mass spectrometry', J. Agric. Food chem. 2001, 49, 3540-3547). These conventional methods are sensitive upto ppb level, but are time consuming, laborious and require skilled technicians and expensive instrumentation. Biosensor is an alternative instrument method to detect the pesticide rapidly and economically. Literature on the applications of biosensor for rapid qualitative detection of pesticide is scanty. In particular, the qualitative rapid techniques are not available to detect methyl parathion (MP) pesticide residues in water and food materials for field application. Reference is made to US Patent 6,569,384 (Inventors: Greenbaum; Elias (Oak Ridge, TN); Sanders; Charlene A. (Knoxville, TN) May 27, 2003, 'Tissue-based water quality biosensors for detecting chemical warfare agents'). They have described an apparatus for introducing water into the cell and discharging water from the cell adapted for analyzing photosynthetic activity of naturally occurring, free-living, indigenous photosynthetic organisms in water; a fluorometer for measuring photosynthetic activity of these organisms drawn into the cell; and an electronics package that analyzes raw data from the fluorometer and emits a signal indicating the presence of at least one pesticide at μg/ml (ppm level). Limitation of this method is detection of the pesticide up to ppb level only and also time consuming and not specific to any pesticides. This method will respond nonspecifically to many organophosphorous and carbamate pesticides. Reference is made to a dipstick immunoassay method described by Mosiello, L., Cremisini, C, Sergre, L., Chiavarini, S. and Spano, M. (1998) Dipstick Immunoassay format for atrazine and Terbuthylazine analysis in water samples. J. Agric. Food Chem. 46, 3847-3851. In this method antibodies were immobilised on nylon membrane and detection limit was 1.2 to lOμg/L^"1 (ppb level) when they use reflectometer. Detection limit of this method is ppb level. As has been reported, the main problem existing in this method is the poor precision, probably due to problems in the homogeneity of the monoclonal antibody on the nylon membrane or polystyrol transperants and the instability of the coloured TMB charge-transfer complex. Reference may be made to a Test Kit and method for the determination of pesticides by Eliezer,Z , Steven, S. Stanely E.C, Sciences, C in WO93 14222. In this publication, the use of insect brain as the biological sensing agent has been described. The publication, however, does not describe the detection limit for the pesticide or the duration required for the analysis. The prior art methods reported above are time consuming. In addition, most of the known methods are not specific to the analyte and a sound technical knowledge is required for the user. Therefore, there is a need for an improved method and test kit for use in pesticide analysis. Objects of the invention It is therefore, an important object of the present invention to provide a rapid test kit for pesticide detection, which obviates the above drawbacks. It is another object of the present invention to provide a rapid test kit for pesticide detection at high sensitivity (ppt Level) using the immunochemiluminescence principle. Summary of the invention The above and other objects of the present invention are achieved by the present invention by utilizing in a novel manner, chemiluminescence (CL) and biochemical reactions to produce light, which is proportional to pesticides concentration at high sensitivity (ppt level). There is no information available at present on determination of pesticide specially Mehyl /Ethyl Parathion (MP/EP) using chemiluminescence (CL). It is known that CL based test kit is very sensitive to detect the analyte very low concentrations. CL method has numerous advantages such as sensitive rapid assay and possibility of robust and inexpensive instrumentation and hence this test kit has become an attractive analytical tool in pesticide determination. In this connection, reference is made to (J Wang C. Zhang, H. Wang, F. Yang and X. Zhang, 2001, Development of a luminol based chemilumnescence flow injection method for the determination of dichlorvos pesticide, 54, 1185-1193) in which they have detected diclorvos at ppm level (0.2 - 3.1μg/ml). However, this method does not work for detection of methyl parathion. It should be noted that there was no involvement of antibody-antigen reactions in the prior art methods mentioned above. On the contrary, the novelty of the present invention resides in the use of antibody- antigen reactions, which are specific to pesticides coupled with a charge-coupled device (CCD). There are no existing reports to detect pesticides at high sensitivities (upto ppt level) using chemiluminescence and CCD camera. The CL based test kit developed in the present invention enables rapid and sensitive detection of pesticide upto ppt level. Another novelty of the present invention resides in the use of an electron mediator such as potassium ferricayanide, to amplify the very low level of light signals produced, thereby enabling clear distinction of different pesticide concentrations from ppm to ppt levels. Detailed Description The present invention will now be described in detail with reference to the accompanying drawings wherein: Fig 1 shows the HRP enzyme catalysed oxidation of electron donor substrate with hydrogen peroxide; and Fig 2 shows a flow chart of the use of the pesticide test kit in accordance with the present invention. Principle of Immuno-ehemiluminescence ( CL) based pesticide detection: The present invention is based on the finding that in the presence of hydrogen peroxide (H₂O₂), horseradish peroxidase (HRP) catalyzes the oxidation of luminol. Immediately following the oxidation of luminol, it reaches an excited state, which then decays to the ground state by emitting light. Using this method it is possible to detect pesticides such as ethyl parathion (EP) and Methyl parathion, using respective antibodies. HRP enzyme catalyzes oxidation of electronic donor substrates with hydrogen peroxide according to the following scheme.

HRP + H₂O₂ ► Complex 1 + H₂O

Complex (1) + Luminol (LH₂) ► Complex (II) +luminol Radical (LH^")

Complex (II)+ luminol Radical (LH^" ) ► Compound 2 + Luminol (fully oxidized) + LIGHT

Pesticide Detection: MP antibodies are immobilised in excess on the carrier matrix in the immunobioreactor column. Pesticide molecules bind with the immobilized antibodies. During this process some of the antibody sites (epitopes) remain unbound. These unbound sites are available for binding the MP-HRP-conjugate. A fixed amount of MP- HRP-conjugate was passed through the column, thereby the remaining antibody epitope sites are occupied by this conjugate. This antibody column was now washed thoroughly. These immobilised matrix-having pesticide and MP-HRP-Conjugate was taken out and subjected to chemiluminescence reaction as given above. However, in this reaction light produced is of very low intensity. To get enhanced light intensity the electron mediator K₃FeCN₆ is added. At high pesticide concentration having more unreacted H₂O_2j K₃FeCN₆ reacts with this and produces an enhanced light intensity which is directly proportional to the pesticide concentration. As shown in Fig 1, in the presence of hydrogen peroxide (H₂O₂), horseradish peroxidase (HRP) catalyzes the oxidation of luminol. Immediately following the oxidation of luminol, it reaches an excited state, which then decays to the ground state by emitting light. Using this method it is possible to detect pesticide such as ethyl parathion (EP) and Methyl parathion, using respective antibodies. Fig.2 illustrates the method and the kit (or device) in accordance with the present invention. A kit (or device) in accordance with the present invention for rapid detection of pesticide at ppt level using immuno-chemiluminescence comprises a capillary column 6 for packing immobilized antibodies. A source of sample solution 2 to be tested for pesticide content is operatively connected to said column 6. A source of buffer 1 is operatively connected to said column for equilibrating the antibody and washing unbound pesticides. Sources of urea H₂O₂ Luminol and K₃Fe(CN)₆ also operatively connected to said column 6. Preferably, all said sources of reagents are connected to said column 6 through a peristaltic pump 5. The mixing said reagents results in light being generated, which may take place I column 7 connected to said column 6. The light generated is captured by a CCD camera 8 to record the intensity of the light produced which is linked to a computer 9 for effecting comparison with a control sample. A preferred embodiment of the method of detecting the presence of pesticide in water, in accordance with the present invention comprises the following: (1). Methyl parathion (MP) antibodies raised in chickens and purified from egg yolk (IgY- MP) and immobilized on sepharose matrix through reductive animation (Hermanson G.T, A.K Mallia and Smitjh P.K, Immobilized affinity ligand techniques. Academic press, 1992, 69-75) were taken in packed column and flow ELISA was carried out, in which MP at different concentrations and MP-HRP conjugates were used as described below. 2). 150 μl immobilized antibodies were packed in a glass capillary column and equilibrated with cold PBS (pH7.4, 50 mM) using 10 times of the bed volume. 50μl sample of this solution containing pesticide was passed through the column at 50μl/min flow rate. 3). PBS was continuously passed for 5 min. to wash of unbound pesticide. 4). MP-HRP conjugate 25μl, was passed through the column at 50μl/min flow rate. 5). The unbound conjugate was washed-out for 15 min using PBS containing 0.1% BSA. 6). Finally, the conjugate containing matrix was taken out from the column and used for the Chemiluminescence test as follows: To 50 μl conjugate containing matrix obtained from above, 25μl urea H₂O₂ (lOmM in Milli Q) was added and kept at room temp for 2 min. Then 25μl of O.lmM Luminol was added to 25μl of 0.5% K₃Fe (CN)₆, (prepared in Milli Q water) and mixed thoroughly. During this process light is generated which is immediately captured by CCD camera in dark room conditions. Intensity of light in the images were compared with control having no pesticide. It was found that there was less light produced in control whereas more light was produced in pesticide containing samples. It was also observed that more light was produced at higher pesticide concentrations whereas less light was observed with less pesticide containing samples. The following example is given by way of illustration only and therefore should not be constructed to limit the scope of present invention. Example: This example illustrates the present invention, which has been schematically shown in Fig 2. Referring to Fig. 2, 150μl immobilized antibodies were packed in a glass capillary column 6 and equilibrated with cold PBS (pH7.4, 50 mM) using 10 times of the bed volume. 50μl sample of solution containing pesticide 2 was passed through the column 6 at 50μl/min flow rate. PBS 1 was continuously passed for 5 min. to wash of unbound pesticide. MP-HRP conjugate 3 25μl, was passed through the column 6 at 50μl/min flow rate. The unbound conjugate was washed-out for 15 min using PBS 1 containing 0.1% BSA. All the above reagents are preferably passed into the column 6 through a peristaltic pump 5. Finally, the conjugate containing matrix was taken out from the column and used for the Chemiluminescence test conducted as follows: To 50 μl conjugate containing matrix obtained from above, 25μl urea H₂O₂ (lOmM in Milli Q) was added and kept at room temp for 2 min. Then 25μl of O.lmM Luminol was added to 25μl of 0.5% K₃Fe (CN)_6> and mixed thoroughly as shown in 7. During this process, light is generated which is immediately captured by CCD camera 8 in dark room conditions. Intensity of light in the images were compared with control having no pesticide through a computer 9. ICL intensity was monitored at different concentrations of the pesticide (MP) viz., lOOppb, lppb, 500ppt and 10 ppt along with the control, which did not have any pesticide. The clear observable CL intensity can be identified upto lOppt. As can be seen from the bottom of Fig 2, at lower pesticide concentration CL difference between sample and control is not distinguishable. By this test kit device it was possible to detect presence and absence of the pesticide up to 10 ppt. The simple photo detection kit for pesticide analysis of the present invention enables testing for pesticide in water, food and environment even by a common man.

Claims

Claims:

1. A method for rapid detection of pesticide at ppt level using immunochemiluminescence which comprises: packing immobilized antibodies packed in a glass capillary column, passing a sample solution to be tested for pesticide content through said column so that a pesticide- antibody conjugate is formed, removing said pesticide-antibody conjugate from the column and adding thereto, urea H₂O₂ followed by Luminol and K₃Fe(CN)_6, mixing said solution thoroughly until light is generated, and capturing the light generated by a CCD camera, the intensity of the light produced being directly proportional to the amount of pesticide content in said sample.

2. A method as claimed in claim 1 wherein said antibodies comprise methyl parathion (MP) antibodies raised in chicken and purified from egg yolk (IgY- MP) and immobilized on sepharose matrix.

3. A method as claimed in claim 1 or 2 wherein said Urea H₂O₂ is employed in the range of 10-50μl.

4. A method as claimed in any preceding claim wherein said Luminol is employed in the range of 10-50μl.

5. A method as claimed in any preceding claim wherein said K3FeCN6 is employed in the range of 10-150μl.

6. A method as claimed in an preceding claim wherein after the addition of urea H₂O_2j said pesticide-antibody conjugate is maintained at room temperature for about two minutes.

7. A method as claimed in any preceding claim wherein said column is fed with phosphate buffer to wash unbound pesticide.

8. A kit for rapid detection of pesticide at ppt level using immunochemiluminescence which comprises a capillary column for packing immobilized antibodies, a source of sample solution to be tested for pesticide content, said source of sample solution being operatively connected to said column, a source of pesticide operatively connected to said column, a source of buffer operatively connected to said column, a source of urea H₂O₂ operatively connected to said column, a source of Luminol operatively connected to said column, and a source of K₃Fe(CN)₆ operatively connected to said column so that all the reagents are thoroughly mixed until light is generated, and capturing the light generated and a CCD camera to record the intensity of the light produced as a function of level of pesticides present in said sample.

9. A kit as claimed in claim 7 wherein a computer is connected to said CCD camera to compare the light produced by the test sample with a control sample.