International Journal of Research in Pure and Applied Chemistry

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Available online at http://www.urpjournals.com International Journal of Research in Pure and Applied Chemistry Universal Research Publications. All rights reserved Original Article Simultaneous determination of triazole fungicide residues in papaya followed by a new validated HPLC-UV method ageswara Rao Tentu*., Parvathamma. Tentu and Patrudu.T.B Departmen t of Engineering Ch emistr y, Andhra University, Visakhapatnam, Andhrapradesh, India Email:- r aoau@ r ediffmail.com. Received 09 August 2012; accepted 24 August 2012 Abstract A simple, sensitive and inexpensive method was developed using matrix solid-phase dispersion (MSPD), together with high performance liquid chromatographic method for determination of triazole fungicide residues (Tetraconazole, Tebuconazole, Hexaconazole and Difenconazole) in papaya. The evaluated parameters included the type and amount of sorbent (silica gel, C18 and Florisil) and the nature of eluent (ethyl acetate, dichloromethane and acetonitrile).the best results were obtained using 1.0 g of papaya sample, 1.0 g of C18 as sorbent and 20ml of ethyl acetate-dichloromethane (1:1, (v/v)).the method was validated using in papaya samples spiked with fungicides at different concentration levels (0.03 and 0.3 µg/ml). Average recoveries (using each concentration six replicates) ranged 90-98%, with relative standard deviations less than 2%, calibration solutions concentration in the range 0.01-2.0 µg/ml and limit of detection (LOD) and limit of quantification (LOQ) were 0.01 µg/ml and 0.03 µg/ml respectively. 2011 Universal Research Publications. All rights reserved Keywords: matrix solid-phase dispersion, triazole fungicides, HPLC-UV 1. ITRODUCTIO Fungicides are a group of chemicals which are used primarily to control spoilage of crops through fungal attack. Fungicides can be divided into protectant and specific types.protectants are the older type and includes copper and sulfur based products. They form a protective film on the plant surface and inhibit the germination of fungal spores. Specific type fungicides are so called because they act on one specific chemical reaction in the fungus. Triazole fungicides are one of the Specific type fungicides. Their invention was inspired by a group of fungicidally active natural products. The outstanding benefits they deliver are currently being utilized in a wide range of crops throughout the world. First launched in 1973, the newer triazoles, being intrinsically more active, push the sensitivity curves back to their original ED 50 values. Various methods have been described for the determination of these Fungicides, using solid-phase extraction(spe)[5], solid-phase micro extraction (SPME)[2], supercritical fluid extraction (SFE) and matrix solid-phase dispersion (MSPD), However, none of the published researches to date have reported the simultaneous analysis of chemical classes such as Tetraconazole, Tebuconazole, Hexaconazole and Difenconazole in papaya. The matrix solid-phase dispersion (MSPD) technique was developed by Barker in 1989[1]. It has advantages over conventional techniques because it employs small amounts of sample and solvent, and the extraction procedure consists of only a few experimental steps. MSPD evolved from the solid-phase extraction (SPE) technique, modified for application to solid and semi-solid matrices. The MSPD procedure is based on the use of a sorbent, which acts as an abrasive in order to produce a modified opening of the solid matrix, facilitating the extraction process when using a suitable solvent for eluting the analytes. The use of MSPD for fungicide recovery depends on the solubility of the fungicide in the eluting solvent, as well as the interactions between the matrix components, sorbent and eluent. Due to the lack of literature reports concerning the use of MSPD as an extraction technique[4,6] for fungicides belonging to different chemical classes from plants, this paper presents an MSPD method for determination of residue of fungicides in papaya. So, the present research considered four different chemical classes, namely Tetraconazole, Tebuconazole, Hexaconazole and Difenconazole which analysis by high-performance liquid chromatography with 1

C CH 2OCF2CHF2 CH2 Tetraconazole Tebuconazole OH CH2 CH 2 C C(CH3)3 CH 2 OH C (CH2) 3CH3 CH2 Hexaconazole CH3 O O O CH2 Difenconazole Fig.1. ames and structures of four triazole fungicides evaluated ultraviolet detector (HPLC-UV). 2. EXPERIMETAL 2.1. Standards, Reagents and samples Certificated analytical standards of Tetraconazole (99.2%), Tebuconazole (99.1%), Hexaconazole (99.4%) and Difenconazole (99.2%) were obtained from international institute of biotechnology and toxicology (IIBAT). Common names and structures of the triazole fungicides evaluated here are shown in Fig. 1. Acetonitrile was purchased from Rankem, ew Delhi, Analytical grade solvents, dichloromethane and ethyl acetate, were supplied from Merck Limited, Mumbai, C18-bonded silica (50 µm) from phenomenex (Torrance, CA, USA), Florisil (60-100 mesh) from fluka chemie GmbH CH-9471 Buchs, AR grade sodium sulphate from Merck Limited, Mumbai and papaya were purchased from local market. They were brought to the laboratory and stored in plastic bag at refrigerator condition until they were processed in the laboratory. 2.2. Standard stock solutions The fungicide standard stock solutions were individually prepared in acetonitrile at a concentration level 100 µg/ml and stored in a freezer at -18 C. The stock standard solutions were used for up to 3 months. Suitable concentrations of working standards were prepared from the stock solutions by dilution using acetonitrile, immediately prior to sample preparation. 2.3. Sample preparation Representative 1.0 g portions of papaya fortified with 1000 µl of working standard solution. The mixture was then gently blended in the mortar for 30 min, to assess the homogeneity of the sample. The sample was allowed to stand at room temperature for one hour, before it was kept at refrigerator condition, until analysis. 2.4. Extraction procedure 1.0 g of papaya sample was weighed out and homogenized with 1.0 g of C18 bonded silica for 5 min. The homogenized sample was transferred to an MSPD column consisting of a 20mL capacity polyethylene syringe containing 1.0 g flurosil and 1.0 g of anhydrous sodium sulfate. The elution was performed under vacuum with 20 ml of ethyl acetate-dichloromethane (1:1).The eluent was collected into a round bottom flask and evaporated to near dryness. Finally make up with 5mL of acetonitrile and analysed by HPLC-UV system. 2.5. Chromatographic separation parameters The HPLC-UV system used, consisted shimadzu high performance liquid chromatography with LC- 20AT pump and SPD-20A interfaced with LC solution software, equipped with a reversed Phase C18 analytical column of 250 mm x 4.6 mm and particle size 5 µm (PhenomenexLuna- C18) Column temperature was maintained at 40 C. The injected sample volume was 20µL. Mobile Phases A and B was Acetonitrile and 0.1% formic acid (70:30(v/v)). The flow- rate used was kept at 1.0 ml/min. A detector wavelength was 240nm. The external standard method of Calibration was used for this analysis. 2.6. Method validation Method validation ensures analysis credibility. In this study, the parameters accuracy, precision, linearity and limits of detection (LOD) and quantification (LOQ) were considered. The accuracy of the method was determined by recovery tests, using samples spiked at concentration levels of 0.03 and 0.3 mg/kg. Linearity was determined by different known concentrations (0.01, 0.05, 0.1, 0.5, 1.0 and 2.0 µg/ml) were prepared by diluting the stock solution. The limit of detection (LOD, µg/ml) was determined as the lowest concentration giving a response of 3 times the baseline noise defined from the analysis of control (untreated) sample. The limit of quantification (LOQ, µg/ml) was determined as the lowest concentration of a given fungicide giving a response of 10 times the baseline noise. 3. RESULTS AD DISCUSSIO 3.1. Specificity Specificity was confirmed by injecting the papaya control. There were no matrix peaks in the chromatograms to interfere with the analysis of fungicide residues shown in Fig.2. Furthermore, the retention times of Tetraconazole, Tebuconazole, Hexaconazole and Difenconazole were constant at 5.1±0.2, 5.7±0.2, 6.5±0.2, 8.1±0.2 min 3.2. Linearity Different known concentrations of fungicides (0.01, 0.05, 0.1, 0.5, 1.0, 2.0 µg/ml) were prepared in acetonitrile by diluting the stock solution. Each solution was prepared in triplicate. Injected the standard solutions and measured the 2

Fig.2. Representative Chromatogram at fortification level of 0.05µg/mL peak area. A calibration curve has been plotted of concentration of the standards injected versus area observed and the linearity of method was evaluated by analyzing six solutions. The peak areas obtained from different concentrations of fungicides were used to calculate linear regression equations. These were Y= 121224.3X+33.12, Y= 8241.43X+12.12 and Y=120045.15+41.13, with correlation coefficients of 0.9999, 0.9998, 0.9999 and 0.9998 for Tetraconazole, Tebuconazole, Hexaconazole and Difenconazole respectively. A calibration curve showed in Fig. 3. recoveries (90-95%, RSD<3%) were achieved. This quantitation limit also reflects the fortification level at which an analyte peak is consistently generated at approximately 10 times the baseline noise in the chromatogram. The limit of detection was determined to be 0.01 µg/ml at a level of approximately three times the back ground of control injection around the retention time of the peak of interest. 3.5. Storage Stability A storage stability study was conducted at -20±1 C with papaya samples spiked with 0.1µg/mL of Tetraconazole, Tebuconazole, Hexaconazole and Difenconazole Samples were stored for a period of 30 days at this temperature. Analysed for the content of Tetraconazole, Tebuconazole, Hexaconazole and Difenconazole before storing and at the end of storage period. The percentage dissipation observed for the above storage period was only less than 3% for Tetraconazole, Tebuconazole, Hexaconazole and Difenconazole showing no significant loss of residues on storage. The results are presented in table 2. Fig.3. Representative Calibration curve of triazole fungicides. 3.3. Accuracy and Precision Recovery studies were carried out at 0.03 and 0.3 µg/ml fortification levels for Tetraconazole, Tebuconazole, Hexaconazole and Difenconazol in papaya. The recovery data and relative standard deviation values obtained by this method are summarized in Table 1. These numbers were calculated from four (6) replicate analyses of given sample (Tetraconazole, Tebuconazole, Hexaconazole and Difenconazol) made by a single analyst on one day. The repeatability of method satisfactory (RSDs<3 %). 3.4. Detection and Quantification Limits The limit of quantification was determined to be 0.03 µg/ml. The quantitation limit was defined as the lowest fortification level evaluated at which acceptable average 4. COCLUSIOS This paper describes for the first time a fast, simple sensitive analytical method based on MSPD-HPLC-UV was developed and validated for the simultaneous determination of four triazole fungicide residues in papaya. The MSPD extraction procedure of the described method is very simple and requires no sample preparation or pretreatment, providing adequate clean-up of the matrix. Whole papaya extracts are very clean, with no interfering peaks at the retention time of the target compounds, indicating good selectivity of the proposed method. The mobile phase Acetonitrile and 0.1% formic acid yields good separation and resolution and the analysis time required for the chromatographic determination of the four Triazole fungicides is very short (around 15 min for a chromatographic run). Satisfactory validation parameters such as linearity, recovery, precision and very low limits were obtained and according to the SACO guidelines [7]. For all of the Triazole fungicides the sensitivity of the method was good enough to ensure 3

Table1. Recoveries of the triazole fungicides from fortified papaya control sample (n=6) Fortification Recovery (%) Concentration Replication Tetraconazole Tebuconazole Hexaconazole Difenconazole in µg/ml R1 88 90 89 91 R2 90 91 88 90 R3 91 89 89 94 0.05 R4 89 93 90 93 R5 89 90 91 91 R6 90 90 93 90 Mean 90 91 90 92 RSD 1.17 1.52 1.99 1.80 R1 95 95 93 96 R2 98 93 93 93 R3 96 96 94 92 0.5 R4 95 92 92 95 R5 95 94 93 93 R6 93 92 95 92 Mean 95 94 93 94 RSD 1.71 1.74 1.11 1.76 Table2. Storage stability Details (n=6) Fortified concentration in µg/ml Storage Period in Days Replication Recovery in % Tetraconazole Tebuconazole Hexaconazole Difenconazole R1 92 90 93 96 R2 94 91 92 91 R3 95 93 93 92 0 R4 92 92 95 94 R5 93 91 95 93 R6 92 93 95 93 0.1 Mean 93 92 93 93 RSD 1.36 1.32 1.31 1.85 R1 90 88 90 88 R2 90 91 89 92 R3 92 90 90 91 30 R4 91 90 91 89 R5 89 88 91 88 R6 90 88 92 90 Mean 90 89 91 90 RSD 1.14 1.49 1.08 1.82 reliable determination levels lower than the respective MRLs. Therefore, the proposed analytical procedure could satisfactorily be useful for regular monitoring of Strobilurin fungicide residues on a large number of fruit samples. 5. ACKOWLEDGEMET The authors are thankful to the Management, and Dr. P. Balakrishnamurthy, Director, IIBAT, for providing necessary facility to conduct the experiment. 6. REFERECES 1. Barker S.A, Long A.R, and Short C.R, Isolation of Drug residues from tissues by solid phase dispersion., J. Chromatogr. 475 (1989) 361-363. 2. Ho W and Hsieh S.J, Solid phase micro extraction associated with microwave assisted extraction of organ chlorine pesticides in medicinal plants, Anal. Chim. Acta. 428 (2001) 111. 3. Bicchi C, Cordero C, Rubiolo P, Simultaneous determination of six trizolic pesticide residues in apple, J. AOAC int. 84 (2001) 1543-1550. 4. avickiene S, Aquino A, Bezerra DS, Amatrix solid- 4

phase dispersion for the extraction of seven pesticides from mango and papaya, J Chromatogr Sci. 48 (2010) 750-754. 5. T.K. Choudhury, K.O. Gerhardt and T.P. Mawhinney, Solid-Phase extraction of nitrogen and phosphorus-containing pesticides from water and gas chromatographic analysis, Environ. Sci. Technol. 30 (1996) 3259-3265. 6. Zuin V.G, Yariwake J.H., Langas F.M, Analysis of pesticide residues in Brazilian plants, Braz.Chem.Soc. 14 (2003) 304-309. 7. SACO Guidelines, Method validation and quality control procedures for pesticide residues analysis in food and feed, Document O. SACO/10684/2009. 2009. Source of support: il; Conflict of interest: one declared 5