Application Note: Multi-Residue Pesticides in Fruit and Vegetables (9/16/08)

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Application Note: Multi-Residue Pesticides in Fruit and Vegetables (9/16/08) Product: DPX-Q (5 ml) INTRODUCTION The analysis of pesticides in fruit and vegetables is very important in the field of food safety. To ensure levels of toxic pesticides are below tolerance levels and are safe to ingest, routine and comprehensive testing must be performed. The biggest drawback to this analysis has been sample preparation. Recently, there has been a great amount of interest in QuEChERS 1-2, which stands for quick, easy, cheap, effective, rugged and safe. This method is used to remove fatty acid components rather than to extract and isolate the pesticides. The advantage of this method is that it is comprehensive, providing very high recoveries for almost all pesticides. The disadvantage of this method is that the resultant sample solutions are relatively "dirty", and as a result there have been numerous modifications and variations of the original method. Some of the different methods include the use of dispersive tubes or cartridges, and some use graphite or other additives (like C 18 ) to remove sample matrix interferences. In this study, the QuEChERS concept is used in a relatively new solid-phase extraction method called disposable pipette extraction (DPX). The DPX tip has loosely contained solid-phase sorbent contained inside a pipette tip through the use of a screen and upper barrier. The main advantages of DPX are its speed and ease of use, taking only seconds to mix sample solutions with the solid-phase sorbent. The advantage of the DPX-Q over other QuEChERS products is that the screen of the DPX tip permits dispersive extractions without the need for centrifugation for the clean up. The screen of the DPX tip acts as a filter removing the sorbent and salt particulate matter from the solution, thereby providing a convenient means of conducting the QuEChERS extraction. EXPERIMENTAL Initial Sample Preparation Add 15 g blended sample (s) and 15 ml acetonitrile into 50 ml centrifuge tube Add 1.5 g NaCl and 6.0 g MgSO 4 Cap and shake tube vigorously for a few minutes; let stand app. 10 minutes Centrifuge at 3,000 rpm for 10 minutes Transfer 2.5 ml of the acetonitrile solution (supernatant) for the manual DPX-Q method. Manual DPX-Q extraction steps 1. If using an internal standard, spike the standard into the 2.5 ml of acetonitrile solution 2. Aspirate the acetonitrile solution in and out of the DPX-Q tip using an attached syringe. 3. Repeat this mixing 2-3 times. 4. Dispense the solution following the final DPX-QuEChERS extraction into a GC vial, cap and inject into the GC. 5. Alternatively, dispense the DPX-Q solution into a small vial and concentrate to 0.5 ml of acetonitrile (or another solvent such as toluene) and then transfer to a GC vial and inject.

DPX-Q tips: 5 ml DPX tips containing MgSO 4, PSA and graphitized carbon black (GCB) Instrumentation. The GC/MS was an Agilent Technologies 6890 GC with 5972A MSD (inert XL). This instrument utilized the following conditions: GC column: 30 m DB-1701 (J&W Scientific), 0.25 mm ID, df = 0.25um carrier gas: He at constant flow of 1 ml/min oven: initial temp at 80 C for 1 min, ramp at 20 C /min to 300 C, hold 7 min (19 min run) inlet temperature: 250 C injection: 2 µl using a HP6890 Series Injector Table 1. Parameters for the MS analysis by SIM for OC pesticides. Group Time Dwell pesticides Monitored ions (m/z) # (min) (msec) 1 8.50 Alpha-BHC 181, 219, 111 30 2 9.20 Gamma-BHC, Beta-BHC, Heptachlor 100, 109, 181, 219, 237, 272 30 3 9.90 Delta-BHC, aldrin 66, 181, 109, 219, 293,263 30 4 10.50 Heptachlor epoxide 81, 263, 353 30 5 11.00 Endosulfan I, 4,4'-DDE, Dieldrin 79, 81, 176, 195, 241, 246, 263, 318,339 30 6 11.80 Endrin, 4,4'-DDD 81, 165, 235, 237, 263,345 30 7 12.20 Endosulfan II, 4,4'-DDT 165,170, 195, 199, 235, 237, 30 8 12.60 Endrin aldehyde, Endosulfan sulfate 67, 237, 250, 272, 387, 345 30 9 13.50 Methoxychlor 227, 228, 346 30 Table 2. Parameters for the MS analysis by SIM for OP pesticides. Group Time Dwell Monitored ions (m/z) # (min) pesticides (msec) 1 5.40 Dichlorphos 79, 109, 185 30 2 6.80 Mevinphos 109, 127, 92 30 3 8.00 Ethoprophos 97, 139, 158 30 4 8.55 Phorate, Demeton-S, Diazinon 60, 75, 88, 121, 137, 152, 30 170, 179, 260 5 9.25 Disulfoton 88, 97, 274 30 6 9.80 Ronnel, Methyl parathion, 97, 109, 125, 197, 263, 269, 20 Trichloronat, Chlorpyrifos 285, 287, 297, 314 7 10.50 Fenthion 109, 125, 278 30 8 10.90 Merphos, Tokuthion, Stirofos 57, 109, 113, 162, 169, 267, 30 314, 329, 331 9 12.00 Bolstar, Fensulfothion 139, 141, 156, 293, 322, 308 30 10 16.80 Coumaphos 109, 226, 362, 30 RESULTS AND DISCUSSION The initial sample preparation used the same method that is delineated in QuEChERS 1-2. The sample was "shaken" in a ratio of 1:1 with acetonitrile in order to achieve good sensitivity. The addition of salt is used to separate the acetonitrile layer from the water. The concept of

QuEChERS is to then remove the sample matrix. This is readily accomplished using the DPX-Q tips and an attached disposable syringe (or pipette). The acetonitrile solution is aspirated in and out of the DPX-Q tip a few times, then the solution is transferred into a GC vial and injected. For higher recovery, the solution can be concentrated to a lower volume, or solvent exchanged using a "keeper" solvent such as toluene to stabilize the pesticides ("keeper" solvent such as toluene). It is also possible to concentrate the analytes directly into the GC inlet by using a PTV inlet (such as the GERSTEL CIS), which would reduce time and eliminate solvent evaporation. The DPX-Q method takes only 90 seconds to perform; there are no wash steps or elution steps. The acetonitrile solution is simply mixed with the sorbent a few times to remove fatty acid components, sample matrix components and water. Results from the analysis of organochlorine and organophosphate pesticides are shown in Tables 3 and 4, respectively. The recoveries were very good for all of the pesticides analyzed with only one exception. One of the OC pesticides, endrin aldehyde, had interference with a sample matrix component s, and so it could not be analyzed using the procedure delineated in the experimental section. Changing the type of GC column or ions analyzed may eliminate the interference. It should be noted that the extracts appear "clean" with the use of the graphitized carbon. However, the GC inlet liners still obtain a build up of residue and must be changed routinely. Table 3. Statistical results for organochlorine pesticides extracted from s and s. OC Pesticides α-bhc 87.78 3.93 92.84 2.71 γ-bhc 88.73 3.57 89.42 0.69 β-bhc 88.42 3.67 92.01 2.08 δ-bhc 104.85 12.65 92.39 2.50 Heptachlor 85.68 7.22 89.47 4.32 Aldrin 90.84 5.26 92.10 3.47 Heptachlor epoxide 84.57 5.13 94.26 8.57 Endosulfan I 90.79 4.87 105.23 4.18 p,p'-dde 88.23 3.38 92.59 2.41 Diendrin 91.77 3.79 99.07 3.15 Endrin 94.99 6.11 93.46 0.93 p,p'-ddd 88.67 5.49 95.60 3.82 Endosulfan II 91.88 3.82 94.53 3.90 p,p'-ddt 89.38 4.48 84.78 3.52 Endrin aldehyde 84.53 3.08 Endosulfan sulfate 97.76 6.29 97.97 1.77 Methoxychlor 89.30 5.02 83.01 3.83

Table 4. Statistical results for organophosphate pesticides extracted from s and s. OP Pesticides Dichlorphos 86.98 5.01 93.05 3.05 Mevinphos 91.15 4.15 113.29 2.62 Ethoprophos 88.12 3.93 97.43 1.12 Phorate 89.01 3.28 89.04 2.64 Demeton-S 88.09 7.16 108.60 5.17 Diazinone 81.77 7.48 90.36 2.18 Disulfoton 89.42 4.19 85.71 3.92 Ronnel 90.11 7.06 88.92 3.58 Parathion-methyl 85.50 4.99 104.43 3.48 Trichloronat 85.60 3.08 83.63 1.22 Chlorpyrifos 80.69 2.43 72.64 2.94 Fenthion 86.16 4.00 91.98 2.29 Merphos 88.34 5.41 99.24 4.83 Tokuthion 88.35 3.68 88.57 1.86 Stirofos 94.75 11.08 103.66 10.24 Bolstar 89.09 3.40 85.61 2.12 Fensulfothion 89.64 4.65 106.64 2.88 Coumaphos 76.91 4.52 108.66 2.73 It has been found that the QuEChERS products provide high recoveries of polar pesticides such as acephate and methamidophos. These compounds are difficult to isolate and extract due to their high polarity, but these analytes can be readily detected using QuEChERS because this method does not attempt to bind the compounds of interest. Using the DPX-Q tips, good recoveries of these compounds were obtained s and s (Table 5). Table 5. Statistical results for miscellaneous pesticides, including chlorothalonil and acephate. Misc. Pesticides Methamidophos 66.92 3.53 74.97 1.78 Acephate 71.80 9.97 84.92 2.12 Captan 77.75 8.60 85.39 3.95 Chlorothalonil 79.57 2.77 62.47 8.21 Thiabendazole 88.45 1.48 70.12 2.44 Other compounds that have been difficult to analyze by QuEChERS include chlorothalonil, captan and thiabendazole. These compounds were also extracted with good recoveries using the

DPX-Q tips (Table 5). It is noted that the DPX-RP tips 3 (discussed in a previous application note) appear to provide better recoveries of chlorothalonil and captan, and this product may be used as a complimentary method to DPX-Q. CONCLUSION This method proves to be very reproducible and efficient for analysis of pesticides in fruit and vegetables. This study demonstrates a rapid, convenient and efficient method for comprehensive pesticide screening. DPX-Q provides high recoveries of all pesticides tested, including polar pesticides such as acephate. Further research focuses on "automated" DPX-Q, where the "cleanup" method is performed by a GERSTEL MPS-2 and the resultant eluent is injected into a GERSTEL CIS for large volume injection for improved sensitivity. REFERENCES 1) S. J. Lehotay, J. AOAC Int. (2007), 90, 485. 2) M. Anastassiades, S. J. Lehotay, D. Stajnbaher, and F. J. Schenck (2003), J. AOAC Int. (2003) 86, 412. 3) W. E. Brewer, H. Guan, S. R. Garris, C. Craft, and S. L. Morgan, Disposable pipette extraction of pesticides in fruit and vegetables, manuscript in preparation. Acknowledgements The authors would like to acknowledge the support of the following organizations: Dept. of Chemistry and Biochemistry, University of South Carolina, Columbia, SC. SC Department of Agriculture, Columbia, SC.