Method development for determination of residual Chlorpyrifos in the grapes by Tlc-fid

Chlorpyrifos, (Fig.1) is an organophosphorus insecticide, which is chemically named as thiophosphoric acid O, O′- diethyl ester-O″-(3, 5, 6-trichloro-pyridin-2-yl phosphorothioate) ester (Radišić et al., 2009).

In market it is available under numerous trade names, i.e., Dursban, Lorsban, Pyridane, Pyrinex, Silrifos etc. It is a white or colorless crystal which has a slightly skunky odour, similar to that of rotten eggs or garlic. Chlorpyrifos is insoluble in water but it is soluble in organic solvents like ethyl acetate, acetone, benzene, chloroform, methanol, diethyl ether at room temperature (Radišić et al., 2009).

Chlorpyrifos is the common name for the chemical 0,0-diethyl 0-(3,5,6-trichloro-2-pyridinyl)-phosphorothioate. Chlorpyrifos is used as an insecticide to control many different kinds of pests, including roundworms, termites, mosquitoes etc. Some products which contain chlorpyrifos are especially used in agriculture industry for the treatment of fruits and vegetables (Blakely et al., 2014; Pujeri et al., 2015; Karabasanavar & Singh, 2012). Fruits and vegetables being highly nutritious are produced for local consumption as well as for export purposes. In order to produce higher and better yield, a large amount of insecticide is used by farmers during the entire period of growth (Blakely et al., 2014; Pujeri et al., 2015; Karabasanavar & Singh, 2012). In a study of seven aerobic soils ranging in texture from loamy sand to clay, with soil pH values from 6.0 to 7.4, the soil half life for radiolabeled chlorpyrifos ranged from 11 to 141 days. However, studies have found chlorpyrifos in soils for over one year following application. Since a huge amount of insecticide is used so their irrational and continual use becomes the reason of accumulation of insecticide residues in the primary agriculture products. The continuous use of these insecticides increases the possibility that residues of these compounds could be found in some fruits and vegetables, thus making this matter a public health and sanitary defense issue (Blakely et al., 2014; Pujeri et al., 2015; Karabasanavar & Singh, 2012). Also, being an organophosphorus insecticide, chlorpyrifos acts as poison if it is touched, inhaled, injected or eaten in any manner (Eaton et al., 2008; Watts, 2013). Chlorpyrifos affects the nervous system. On exposure to chlorpyrifos, it moves to all the parts of the body through metabolic pathways and when the body tries to break it down into its metabolites it gets converted to another form which is called chlorpyrifos oxon. This oxon further binds permanently to the enzymes, which controls the messages that travel between the nerve cells (Eaton et al., 2008; Watts, 2013). Nerves and muscles do not respond correctly when this oxon binds with too many of the enzymes. This causes the body to make more enzymes so that normal nerve function can resume. The body can break down and excrete most of the unbound chlorpyrifos in feces and urine within a few days. Chlorpyrifos that finds its way into the nervous system may stay there much longer. Chlorpyrifos is principally excreted in the urine (Eaton et al., 2008; Watts, 2013).

For human beings to remain healthy, it is important to include fruits and vegetables in their diet for most of the actions taking place in our body. Even though these fruits and vegetables are healthy but they are equally prone to pests and diseases which attack them during their time of production as well as storage thus, degrading their yield and quality (Blakely et al., 2014; Pujeri et al., 2015; Karabasanavar & Singh, 2012). So, to prevent these issues farmers use high amount of pesticides and other products. Even though the use of pesticides has increased the quality and quantity of fruits and vegetables but it has also affected the life of its consumers by causing a large number of health issues to the human beings. Although a large amount of pesticides gets removed from the human body in the form of urine and fecal matter but, still some pesticides (especially chlorpyrifos) are very persistent and can remain in human body for a long term (Eaton et al., 2008; Watts, 2013).

Detailed survey of literature for chlorpyrifos revealed that various techniques have been discovered and used for the assay of chlorpyrifos residue in fruits and vegetables samples. These techniques include TLC (Tewari, 1976), HPLC with UV detection (High Performance Liquid Chromatography) (Richard et al., 2006; Sajjad et al., 2009; Cozma et al., 2011; Devendra et al., 2011; Barkat et al., 2012; Paranthaman et al., 2012; Shailendra et al., 2012; Alamgir et al., 2013; Tordzagla et al., 2013), Liquid chromatography-tandem Mass spectrometery (Steven et al., 2005; Rohan et al., 2012), High Performance Thin Layer Chromatography (HPTLC) (Iqbal et al., 2007; YueY et al., 2008; Akkad & Schwack, 2012; RouhollahD et al., 2012), Gas chromatography–Mass spectrometry(GC-MS) (Paranthaman et al., 2012; Steven et al., 2005; Tomas et al., 2012),Gas Chromatography with Electron Capture detection (GC-ECD) (Devendra et al., 2011; Paranthaman et al., 2012; Mohammad et al., 2010; Subhash et al., 2010), Spectrophotometry (Venugopal et al., 2012), Reflectance near-infrared spectroscopy (Umesh et al., 2012), Chemiluminescence assay (Aifang et al., 2008), immunoassay (Gabaldón & Maquieira, 2007) and Capillary electrochromatography, (Weimin et al., 2010) but in present study an attempt has been made to analyze chlorpyrifos by Thin Layer Chromatography-Flame Ionization Detection technique (TLC-FID) and to validate the method. TLC-FID is a technique which combines the advantages of TLC with the possibility of quantitation using FID. (Cebolla et al., 1998; Bharati et al., 1993; Stephens et al., 1998; Jiang et al., 2008; Ranny, 1987) The separation is made with the TLC Method on chromarods instead of TLC plates and the detection of chlorpyrifos is done with a FID. To separate and identify chlorpyrifos poison, standard solution was prepared and spotted on chromarods with micro dispenser and the rods were made to run in the Hexane: Acetone solvent system and was afterwards subjected to TLC-FID instrument/ IATROSCAN MK-6 s, after which the chromatograms were generated. (Cebolla et al., 1998; Bharati et al., 1993; Stephens et al., 1998; Jiang et al., 2008; Ranny, 1987)Only few methods have been reported for the determination of pesticide residue in leafy vegetables. The methods adopted so far include HPLC with UV detection, (Barkat et al., 2012; Paranthaman et al., 2012; Shailendra et al., 2012) Capillary Chromatography (Weimin et al., 2010) and Gas Chromatography with electron capture detector. (Subhash et al., 2010; Hussain & Samia, 2010)

The current “Joint Meeting on Pesticide Residues” (JMPR) that comprises the WHO Core Assessment Group and the FAO Panel of Experts on Pesticide Residues in Food and the Environment is responsible for reviewing pesticide toxicological data and estimating Acceptable Daily Intakes (ADI), acute reference doses (ARfDs). JMPR has fixed the ADI (per day per kg body weight) for Chlorpyrifos as 0.01 mg/kg (Bhushan et al., 2013).

Since the efficiency of both the techniques gas chromatography/ mass spectrometry (GC/MS) and liquid chromatography/tandem mass spectrometry (LC/MS/MS) had been tested extensively in the determination of residues of 446 pesticides in fruits and in the method, fortification recovery tests at high, medium, and low levels were conducted on 6 varieties of fruits and vegetables, i.e., apples, oranges, grapes, cabbage, tomatoes, and celery, with average recoveries falling within the range of 55.0–133.8% for 446 pesticides, among which average recoveries between 60.0–120.0% accounted for 99% of the results (Pang et al., 2006). One can observe the effect of surface on the absorption of compounds studied in this work and thus there was no need to repeat those studies.

In the present work, a novel chromatographic methodology was developed to identify Chlorpyrifos, an organophosphorus insecticide residue in grapes samples by TLC-FID technique. The method developed is an alternative analytical method for the detection and confirmation of chlorpyrifos residue. The sample blank was assayed to verify that there are no significant peaks with similar retention times. The blank chromatogram exhibits no peak beyond normal noise level near the retention time of the analyte of interest. To optimize the method various concentrations of analyte were applied using a Micro dispenser and S-III chromarods were used for performing chromatographic separation. Sensitivity of the proposed TLC- FID method was assessed by examining peak interferences from other substances present in grapes extract. This was done by comparing the chromatograms of blank, grapes extract with the authentic chlorpyrifos standard. It was observed that none of the peak appears at the same retention time of pure standard chlorpyrifos. Pesticide residue (chlorpyrifos) was identified from its retention time appeared in grape extract chromatogram (Fig. 2) and confirmed by comparison with authentic standard.

A linear calibration curve (Fig. 3). was also constructed for chlorpyrifos from the linear regression and concentration. The x-axis of the calibration curve represents the concentration whereas the y-axis of the calibration curve represents the area count. The correlation coefficient (r2) from the plotted area response versus concentration for chlorpyrifos is 0.9996 which is ≥0.99. The average percent recovery for chlorpyrifos is 97.9% -99.8% of the amount prepared for 25–100% level.

The accuracy of the method was proven by using spiked solutions that were prepared by spiking in the appropriate amount of analyte of interest into the sample matrix and assayed using a standard. The recovery was within the acceptance criteria and the %RSD among the accuracy dilutions was ≤2.

Afterwards, for each standard concentration, the standard deviation of the “calculated concentrations” was determined and plotted over the actual concentrations of chlorpyrifos. Limit of Detection (LOD) is defined as three times the expected value of the standard deviation of the calculated concentrations at zero concentration. LOD was determined from standard deviation-concentration relationship.

The %RSD calculated for system precision evaluation ≤2% (Table 2) and that of method precision was also obtained as ≤2% (Table 3). Thus system precision criteria and method precision criteria were met. All acceptance criteria for the linearity of chlorpyrifos were also met.

The method developed can be used to detect chlorpyrifos residues in a concentration as minimum as 0.02 mg/Kg. The method verification elements of linearity, accuracy, specificity, precision and range met each of the respective elements’ acceptance criteria.

The regression data was used to calculate the limit of detection for the method and recovery results were found to be in the range of 97.9% -99.8% The correlation coefficient calculated from the calibration curve and linear relationship was found to be R² = 0.9996.

The method is precise, accurate and fast, with a standard relative error. The recovery and reproducibility was acceptable for chlorpyrifos based on the matrix spiked standards. The impurities and matrix effects from grapes were minimal and did not interfere with the quantization of any target compound.

The proposed novel method used for the determination of residual chlorpyrifos in the grapes is suitable for analyzing for compliance with current MRLs. In contrast to other TLC based methods, this method can be used alone for the determination of residual chlorpyrifos in sample of unknown origin and can produce reliable and valid results. In order to obtain the best reproducibility and separation, it is recommended to always use freshly activated chromarods and equilibrated solvent/ vapour phase in the developing chamber.

The elaborated method can be tested to cover a wide range of pesticides residue including organophosphorus, carbamate insecticide, synthetic pyrethroid and several other pesticides of various chemical classes from different matrix. Chromarods used in this technique can be subjected to multiple elutions in one or several solvent systems. Further chromarods can also be impregnated with silver nitrate or boric acid to improve separation of quite complex mixtures.

This study evidenced that the proposed novel method may be used in routine analysis of grapes, with low LOD value and good analytical precision.