Screening Method for 30 Pesticides in Green Tea Extract Using Automated Online Sample Preparation with LC-MS/MS

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Application Note: 514 Screening Method for 3 Pesticides in Green Tea Extract Using Automated Online Sample Preparation with LC-MS/MS Yang Shi, Catherine Lafontaine, Thermo Fisher Scientific, Franklin, MA, USA Fangting Ye, Zheng Jiang, Le Ma, Ting Liu, Haijian Wang, Thermo Fisher Scientific, Shanghai, China Key Words Transcend TLX-1 System TurboFlow Technology TSQ Access MAX Food Safety Introduction Analysis of pesticide residues has been one of the most important tasks of food safety laboratories. Mass spectrometers (MS), with liquid chromatography coupled to triple stage quadrupole mass spectrometers (LC-MSMS), have been the main tools used in pesticide residue analysis. There is a consensus that sample preparation is becoming the bottleneck to the entire workflow. Traditional sample preparation methods, usually involving liquid-liquid extraction (LLE) or solid phase extraction (SPE), can be time-consuming and labor-intensive. In addition, low recovery, matrix interference and poor reproducibility are among other major concerns. In recent years, a rapid processing method, QuEChERs, has gained popularity. The QuEChERs method makes it easier and less expensive for analytical chemists to examine pesticide residues in various food matrices 1. However, some reports show matrix interference tends to be severe after QuEChERs, and the mass spectrometer is more vulnerable to contamination by highly complex food matrices 2. In this study, we describe an easy, comprehensive, online screening LC method using a Thermo Scientific Transcend TLX-1 system powered by Thermo Scientific Turbo- Flow technology to analyze multiple pesticide residues in green tea extract. Figure 1 illustrates a typical Transcend TLX-1 system with the Thermo Scientific TSQ Access MAX triple stage quadrupole mass spectrometer. Goal Develop a rapid and sensitive automated online sample preparation LC-MS/MS method to screen for multiple pesticides in green tea extract. Experimental The matrix standard curve One gram of Chinese green tea was extracted using 1 ml HPLC grade acetonitrile followed by 15 minutes of ultra-sonication. The extract was then filtered through a.45 μm membrane filter. The resultant solution was used to prepare the matrix calibrators and QC samples. The matrix calibrant concentrations are 6.25 μg/l, 12.5 μg/l, 25 μg/l, 5 μg/l and 1 μg/l, respectively. The matrix QC sample concentration is 1 μg/l. TurboFlow Method Parameters System: Transcend TLX-1 system controlled by Thermo Scientific Aria OS 1.6.3 software Column: TurboFlow Cyclone.5 x 5 mm Injection Volume: 1 μl Loading Solvent:.1% formic acid in water Loading Flow Rate: 1.5 ml/min Eluting Solvent:.1% formic acid in methanol Figure 1. Typical layout of a Transcend TLX-1 system with a TSQ Access MAX triple stage quadrupole mass spectrometer.

HPLC Method Parameters Analytical Column: Thermo Scientific Hypersil GOLD 2.1 x 1 mm, 3 μm Solvent A:.1% formic acid in water Solvent B:.1% formic acid in methanol Mass Spectrometer Parameters MS: TSQ Quantum Access MAX MS Ionization Source: Heated Electrospray Ionization (H-ESI) Ion Polarity: Positive ion mode Spray Voltage: 2 KV Sheath Gas Pressure (N 2 ): 3 arbitrary units Auxiliary Gas Pressure (N 2 ): 15 arbitrary units Vaporizer Temperature: 3 C Capillary Temperature: 3 C Collision Gas Pressure: 1.5 mtorr Figure 2. TurboFlow method schematic as viewed in the Aria OS software. Results and Discussion The Extraction and Separation of 3 Pesticide Residues In 26, Japan released the most stringent pesticiderelated regulation in history entitled Positive List System for Agricultural Chemical Residues in Foods 3. Since Japan is China s major tea importer, the limits discussed in the current study follow this regulation. As described in the Experimental section, the tea matrix standard samples are 6.25 μg/l, 12.5 μg/l, 25 μg/l, 5 μg/l and 1 μg/l, respectively. The matrix QC samples are 1 μg/l. Figure 3 shows the representative chromatograms at 6.25 μg/l, which has been determined as the lower limit of quantitation (LLOQ). The data demonstrate that 3 pesticides were well separated with good peak shape. The peaks signal to noise ratios are far greater than the required 1:1 at the LLOQ. Table 1 shows the linear curve for these 3 analytes. All R 2 values are between.993-.999. The relative standard deviation (RSD) for 6 consecutive injections of 6.25 μg/l calibrator was in the range of 2.85% -7.48%. Background Reduction Effects using TurboFlow Technology By using the Transcend TLX system with TurboFlow technology, the background noise and interference peaks are reduced significantly. Figure 4 compares chromatograms of Clomazone at 6.25 μg/l in tea extract using standard HPLC (top) and the TurboFlow method (bottom). The left panel (A-1 and B-1) shows the primary transition of m/z 24 > 125. The right panel (A-2 and B-2) shows the secondary transition of m/z 24 > 89. It clearly shows the effectiveness of background reduction using TurboFlow technology while the signal to noise ratio increased by 3 and 4 times for m/z 125 and 89 transitions, respectively. The area responses of both peaks also increase by more than 5% due to the minimization of ion suppression incurred by matrix. We also noticed the mass spectrometry response become more stable across the entire tested concentration range, thus improving the method reliability. A Simple Method Optimization Process During TurboFlow method development, the sample loading condition, elution solvents and many other parameters may need to be optimized. Aria OS 1.6.3 operation software for Transcend systems offers a method variable function. By utilizing this unique tool, different parameters can be easily tried using the same method in a single batch. For example, in this study, one of the critical steps was to find the optimal solvent content in the transfer loop to elute the target analytes completely from the TurboFlow column without introducing unnecessarily high organic solvent into the analytical column. We compared 5 different concentration ratios of.1% formic acid in acetonitrile to.1% formic acid in water (1:9, 3:7, 5:5, 7:3 and 9:1). The results indicated that with the increase of organic content, the target compounds were more completely washed off from TurboFlow column. However, once the organic concentration reached 5%, the elution strength was approaching a balance. Therefore, we chose 5:5 as the optimal elution ratio of organic to aqueous solvent in the transfer loop. Another example of method optimization appears in Figure 5, showing the effects of the loading flow rate on Dimethametryn s elution peak shape. All these tests were done in just one sample batch without writing multiple methods, which simplified the method development process and improved method reliability. The Comparison of TurboFlow Technology with Two of the Most Popular Pesticides Sample Preparation Methods As shown in Figure 6, we compared a TurboFlow method and two currently popular methods for pesticide residue sample preparation, SPE and QuEChERs. A typical SPE method involves equilibrating the cartridge, loading, washing and eluting analytes. It usually takes about 1 week to process 1 samples. Although QuEChERs was designed to simplify sample preparation, it still requires two-step centrifugation and concentration. A few days are typically required to prepare 1 samples with QuEChERs. TurboFlow technology minimizes preparation of 1 samples to less than 3 hours, dramatically improving the efficiency and throughput of this routine lab test.

Table 1: Standard curve linearity and QC results for the 3 pesticides in tea extract. Parent ion Product ion Collision CV% (n = 6) Compound RT (min) (m/z) (m/z) Energy (V) Linear Curve R 2 QC = 1 μg/l Prometon 4.82 226. 184. 2 Y=167343+396533X.999 2.99% 142.1 27 Ametryn 5.7 228. 186. 26 Y=83264.1+194461X.999 2.85% 96. 34 Dimethametryn 5.68 256.1 186.1 21 Y=166875+6555X.999 3.29% 158.1 27 Mefenoxam 5.79 28. 22. 17 Y=4619+27242X.998 4.23% 192. 2 Monolinuron 5.85 215. 126. 17 Y=-1985.6+18335.3X.998 6.51% 99. 36 Isoprocarb 5.94 194. 95. 16 Y=-18662+12428.2X.999 6.43% 137. 11 Dimethachlor 6.1 256. 224. 15 Y=-23531.9+96341.3X.997 5.53% 148. 28 Clomazone 6.5 24. 125. 2 Y=-43447.5+42181.6X.998 6.37% 89. 37 Furalaxyl 6.21 32. 242. 15 Y=35811+267257X.998 4.85% 27. 1 Azoxystrobin 6.33 44. 372. 15 Y=538988+377945X.997 4.% 329. 33 Triadimefon 6.39 294. 197. 19 Y=-2167.4+16685.8X.997 7.31% 225. 19 Ethoprophos 6.41 243. 131. 21 Y=-13814+14313.8X.997 7.48% 97. 33 Iprobenfos 6.52 289. 25. 12 Y=538.6+137376X.999 6.28% 91. 23 Isoprothiolane 6.57 291. 189. 22 Y=12316+87284X.998 6.% 231. 12 Flutolanil 6.6 324. 242. 26 Y=677+47866X.998 6.56% 262. 18 Propiconazole 6.65 342. 159. 3 Y=-17113.2+36428.7X.997 6.74% 69. 31 Benalaxyl 6.78 326. 148. 25 Y=172291+126493X.997 5.92% 28. 2 Pirimiphos-methyl 6.81 36. 164. 22 Y=227752+24491X.994 4.73% 18. 33 Picoxystrobin 6.82 368. 145.1 22 Y=3293+78661.3X.993 4.3% 25. 7 Diazinon 6.9 35. 169. 24 Y=182248+386247X.998 4.96% 153. 26 Thiazopyr 6.95 397. 335. 3 Y=-552.12+18434.8X.997 6.47% 275. 4 Piperophos 7.9 354. 171. 25 Y=142671+143459X.996 4.68% 143. 33 Trifloxystrobin 7.13 49. 186. 21 Y=-18755.2+4315.6X.998 6.22% 26. 16 Tebufenpyrad 7.16 334. 145. 28 Y=-3267.9+939.51X.998 7.1% 117. 36 Piperonyl butoxide 7.25 356. 177. 13 Y=-3922+17566X.996 4.16% 119. 33 Pyriproxyfen 7.34 322. 96. 16 Y=-1916.9+56881.6X.999 4.73% 185.2 27 Tralkoxydim 7.39 33. 284. 15 Y=-8119.47+46536.4X.997 5.1% 138. 2 Fenazaquin 7.55 37. 161. 18 Y=-56587.3+97365.3X.998 2.76% 57. 23 Butralin 7.58 296. 24. 15 Y=-2485.92+25777.9X.998 4.72% 222. 2 DEF 7.85 315. 169. 15 Y=-8658.91+7992.12X.998 3.89% 113. 25

1 RT: 6.8 1 RT: 7.18 5 5 1 RT: 6.81 1 RT: 7.25 5 5 1 RT: 6.84 1 6.69 6.78 7.11 7.67 7.77 8.23 RT: 7.36 5 5 1 RT: 6.92 1 6.47 6.69 6.85 7.16 7.79 7.86 8. 8.22 RT: 7.43 5 1 RT: 6.97 5 1 6.58 6.89 7. 7.14 7.7 7.93 8.3 8.31 RT: 7.57 5 5 1 6.31 6.78 7.13 7.47 7.91 RT: 7.11 1 RT: 7.62 5 5 1 6.35 6.51 6.95 7.47 7.84 RT: 7.15 8.3 1 6.94 7.26 7.5 7.99 8.9 8.39 8.52 RT: 7.91 5 5 6.35 6.79 6.99 7.38 7.55 8.9 6. 6.5 7. 7.5 8. 7.5 7.18 7.54 8. 8.42 8.55 6.5 7. 7.5 8. 8.5 1 RT: 4.82 1 RT: 6.23 5 5 1 RT: 5.7 1 RT: 6.35 5 5 1 RT: 5.66 1 RT: 6.17 RT: 6.41 RT: 6.99 5 5 1 5 1 RT: 5.79 RT: 5.87 1 5 1 RT: 6. RT: 6.99 RT: 6.41 RT: 6.88 RT: 7.23 RT: 6.52 5 1 5.35 RT: 5.96 6.35 6.7 5 1 RT: 6.59 5 5 1 5.33 5.69 6.15 RT: 6.3 6.64 1 5.62 5.91 6.18 RT: 6.62 6.83 7.8 7.3 5 1 RT: 6.7 6.21 6.77 5 1 6.94 5.64 5.91 7.29 6.29 RT: 6.67 5 5.54 5.96 6.37 6.88 4. 4.5 5. 5.5 6. 6.5 7. 5 5.5 6. 6.5 7. Figure 3. Selected ion chromatograms at LLOQ of 6.25 μg/l for all 3 analytes (same as the order in Table 1).

1 RT: 6.7 MA: 15273 SN: 63 RMS 1 RT: 6.7 MA: 11668 SN: 19 9 8 7 6 5 4 3 2 1 9 A-1 8 7 A-2 6 5 4 3 2 1 5.2 5.4 5.6 5.8 6. 6.2 6.4 6.6 6.8 7. 5.2 5.4 5.6 5.8 6. 6.2 6.4 6.6 6.8 7. RT: 6.5 MA: 215337 RT: 6.5 MA: 2577 1 9 8 7 SN: 19 RMS 1 9 B-1 8 B-2 7 SN: 77 RMS 6 5 4 3 6 5 4 3 2 2 1 1 5.2 5.4 5.6 5.8 6. 6.2 6.4 6.6 6.8 7. 5.2 5.4 5.6 5.8 6. 6.2 6.4 6.6 6.8 7. 7.2 Figure 4: Comparison of chromatograms of Clomazone at 6.25 μg/l in tea extract using standard HPLC (top) and the TurboFlow method (bottom). 1 RT: 4.91 8 6 4 2 1 8 6 4 2 1 8 6 4 Loading flow rate:.1 ml/min.28.79 1.14 1.56 2.17 2.84 3.67 5.25 5.7 6.39 6.8 7.21 RT: 5.9 Loading flow rate:.8 ml/min.38.77 1.23 2.37 2.87 3.23 3.56 4.29 5.31 5.77 6.71 7.25 RT: 5.24 Loading flow rate:.7 ml/min 2.86 1.15 1.76 2.53.143.46 4.12 4.51 5.56 6.19 6.55 7.19 1 2 3 4 5 6 7 Figure 5. Effect of the loading flow rate on Dimethametryn s elution peak shape.

SPE Weigh Sample Extraction QuEChERs Weigh Sample Extraction TurboFlow Method Weigh Sample Extraction In addition to these offices, Thermo Fisher Scientific maintains a network of representative organizations throughout the world. SPE Loading Washing Eluting Drying Reconstitution Filtration LC-MS/MS 1 Samples, 1 Week Shake and Centrifuge 5 min Transfer Top Layer to Clean-up Tube Shake and Centrifuge 5 min Drying Reconstitution Filtration LC-MS/MS 1 Samples, 2 Days Figure 6. Comparison of the TurboFlow method to SPE and QuEChERs. Conclusion A quick, automated online sample preparation LC-MS/MS method has been developed that is sensitive enough to screen the tested pesticides in tea extracts. The method detection and quantitation limits are significantly lower than the strictest limits set by the Japanese government. TurboFlow technology eliminates the need for time-consuming sample preparation procedures such as SPE and QuEChERs. By using Aria OS software, the method development and optimization process is greatly simplified. References Filtration LC-MS/MS 1 Samples, 3 Hours 1. Steven J. Lehotay, Quick, Easy, Cheap, Effective, Rugged and Safe (QuEChERs Approach for Determining Pesticide Residues. Methods in Biotechnology, 26, 19, 239-261 2. Steven J. Lehotay, Michelangelo Anastassiades, Ronald E. Majors, QuEChERS, a Sample Preparation Technique that Is Catching On : An Up-to-Date Interview with the Inventors, LCGC North America, July 21 3. The Japanese Positive List System for Agricultural Chemical Residues in Foods (enforcement on May 29, 26) 4. GB/T 19648-25 (466 Pesticides analysis method in Fruit and Vegetable GC-MS and LC-MS-MS) Africa-Other +27 11 57 184 Australia +61 3 9757 43 Austria +43 1 333 5 34 Belgium +32 53 73 42 41 Canada +1 8 53 8447 China +86 1 8419 3588 Denmark +45 7 23 62 6 Europe-Other +43 1 333 5 34 Finland/Norway/ Sweden +46 8 556 468 France +33 1 6 92 48 Germany +49 613 48 114 India +91 22 6742 9434 Italy +39 2 95 591 Japan +81 45 453 91 Latin America +1 561 688 87 Middle East +43 1 333 5 34 Netherlands +31 76 579 55 55 New Zealand +64 9 98 67 Russia/CIS +43 1 333 5 34 South Africa +27 11 57 184 Spain +34 914 845 965 Switzerland +41 61 716 77 UK +44 1442 233555 USA +1 8 532 4752 www.thermoscientific.com Legal Notices: 211 Thermo Fisher Scientific Inc. All rights reserved. All trademarks are the property of Thermo Fisher Scientific Inc. and its subsidiaries. This information is presented as an example of the capabilities of Thermo Fisher Scientific Inc. products. It is not intended to encourage use of these products in any manners that might infringe the intellectual property rights of others. Specifications, terms and pricing are subject to change. Not all products are available in all countries. Please consult your local sales representative for details. Thermo Fisher Scientific, San Jose, CA USA is ISO Certified. AN63386_E 1/11S Part of Thermo Fisher Scientific