In this application note, we describe the development of a multi-residue method for the routine determination of 190 pesticide residues in various fruit and vegetable matrices using UPLC-MS/MS.
Pesticides are widely used in agricultural farming across the world. Pesticide residue levels in food products are regulated and closely monitored. Most countries have established legislation imposing Maximum Residue Limits (MRLs) for pesticide residues in food commodities which require analytical techniques that are sensitive, selective, accurate, and robust. Multiresidue analysis is challenging due to the low limits of detection required to achieve MRL compliance for a diverse range of pesticides in a wide range of food commodities. There are currently in excess of 1000 pesticides commercially available, and laboratories are under increasing pressure to widen the scope of their analytical methods for routine pesticide monitoring.
In this application note, we describe the development of a multiresidue method for the routine determination of 190 pesticide residues in various fruit and vegetable matrices using UPLC-MS/MS. White grapes and green beans were selected for this application due to their relatively increased complexity, since they contain chlorophylls which are known to affect the extraction efficiency of pesticides from food matrices. A generic QuEChERS sample extraction procedure was used to extract the pesticides from the fruit and vegetable samples, followed by rapid and high resolution UPLC separation and trace level detection of pesticides using the Xevo TQ-S micro.
LC system: |
ACQUITY UPLC H-Class |
Column: |
ACQUITY BEH C18 1.7 μm, 2.1 x 100 mm |
Column temp.: |
45 °C |
Injection volume: |
10 μL |
Flow rate: |
0.45 mL/min |
Mobile phase A: |
10 mM Ammonium acetate (pH 5) in water |
Mobile phase B: |
10 mM Ammonium acetate (pH 5) in methanol |
Weak needle wash: |
50/50 Water/methanol (v/v) |
Strong needle wash: |
10/90 Methanol/water (v/v) |
Seal wash: |
90/10 Water/methanol |
Time (min) |
Flow rate (mL/min) |
%A |
%B |
Curve |
---|---|---|---|---|
Initial |
0.45 |
98 |
2 |
6 |
0.25 |
0.45 |
98 |
2 |
6 |
12.25 |
0.45 |
1 |
99 |
6 |
13 |
0.45 |
1 |
99 |
6 |
13.01 |
0.45 |
98 |
2 |
6 |
17 |
0.45 |
98 |
2 |
6 |
MS system: |
Xevo TQ-S micro |
Ionization mode: |
ESI+ |
Capillary voltage: |
1.00 kV |
Desolvation temp.: |
500 °C |
Desolvation gas flow: |
1000 L/Hr |
Source temp.: |
150 °C |
Two MRM transitions for each compound were obtained from the Quanpedia Database1 which contains a compendium of methods, and monitored for all of the pesticides that were studied. The data were acquired and processed using MassLynx MS Software v.4.1 with TargetLynx XS Application Manager.
Restek LC Multiresidue Pesticide Kit (Catalog #31971) was used to make a mix of calibration standards. The stock solution of 10 µg/mL was prepared by combining 100 µL from each ampoule.
The green beans and white grape samples investigated in this study were purchased from a local supermarket.
15 g of homogenized samples were extracted with 15 mL of 1% glacial acetic acid in acetonitrile, followed by the addition of QuEChERS AOAC material (DisQuE Pouches, p/n 186006812). The tube was shaken for 1 minute and centrifuged at 3700 rpm for 5 minutes. Then 100 µL of the extract was taken and diluted to 1 mL with water before LC-MS/MS analysis.
To study linearity, solvent and matrix matched standards (MMS) calibration curves were created by spiking the pesticide mix from 0.01 to 0.50 mg/kg (1 ppb to 500 ppb) in solvent and the matrices, respectively.
All pesticides were analyzed on an ACQUITY UPLC BEH C18 Column. For each pesticide, two MRM transitions were monitored, and AutoDwell was applied. AutoDwell is a feature used in MassLynx Software to ensure that sufficient points across each chromatographic peak are achieved. A user simply enters the average peak width and number of points required, and the software automatically calculates the dwell time required to achieve the minimum number of points across the peak specified. With the rapid acquisition rate of the Xevo TQ-S micro, 380 MRMs were monitored with a 1 minute wide retention time window with at least 12 data points across the peak. False negatives are potentially avoided by extending the acquisition range.
Figure 1 shows an overlay of chromatograms (vertically linked) for all pesticides spiked at 10 ppb (0.01 mg/kg) in the green beans and white grapes.
Linearity was studied with nine different levels of matrix-matched standards calibration. The concentrations of the calibration levels ranged from 1 to 500 ppb (sample equivalent to 0.001 to 0.5 mg/kg). A majority of the compounds (96%) showed a linear response with correlation coefficients >0.990 in both matrices. Example calibration curves of imidacloprid in white grapes and pyraclostrobin in green beans are shown in Figure 2.
Method recovery was evaluated by spiking the reference standards in the samples and quantifying against the matrix-matched calibration curve. Green bean and white grape samples were pre-spiked with all of the pesticides at 10 ppb (0.01 mg/kg) in triplicate. The samples were extracted and quantified against the matrix matched calibration curve. Recoveries were calculated using TargetLynx XS Software. Recoveries for most of the pesticides (97% in white grapes and 96% in green beans) fell within the acceptable tolerance of 70% to 120% range (DG SANTE/11945/2015)2 in both samples. The precision in terms of %RSD for most compounds (93%) in green beans and white grapes were less than 20%. The use of a suitable internal standard will significantly improve repeatability for those analytes. Recoveries for all the pesticides in green beans and white grapes are shown in Appendix A.
To determine incurred residues, the white grape and green bean samples were prepared as described in the Sample preparation section and analyzed. From the obtained results, carbendazim, propamocarb, and pyrimethanil were observed in the green bean sample and quantified below 0.07 mg/kg. Boscalid, cyprodinil, fenhexaid, imidacloprid, methoxyfenozide, pyraclostrobin, and trifloxystrobin were observed in the grape sample and quantified at less than 0.25 mg/kg. For accurate quantification of incurred residues, a standard addition technique can be employed. Figure 3 shows an example of an incurred residue found in the green bean sample.
In order to avoid false identification, it is important to check the retention time tolerance and ion ratios of the incurred residues. TargetLynx automatically calculates ion ratios and provides accurate quantification for all incurred residues. All of the incurred pesticide residues detected in the green bean and white grape samples were identified in accordance with the criteria specified in the European Commission SANTE document 11945/2015,2 [retention time (± 0.1 minute) and ion ratios (<30%)] and compared against the reference.
720006039, Revised December 2020