Fast Determination of 22 Pesticides in Rice Wine by Dispersive Solid-Phase Extraction in Combination with GC-MS
Nannan Chen, Hongbo Gao, Nengsheng Ye, Qiding Zhong, Zhenghe Xiong, Xuexin Gu
.
DOI: 10.4236/ajac.2012.31006   PDF    HTML     6,239 Downloads   11,929 Views   Citations

Abstract

A rapid method was developed for the determination of 22 pesticides in rice wine. The procedure involved an extraction with acetonitrile and a cleanup step using dispersive solid-phase extraction (d-SPE), and primary-secondary amine (PSA) and octadecylsilane (ODS) were used as sorbents. D-SPE had some advantages over some traditional prepara- tions, especially in time and cost. Both the extraction and cleanup only cost about 15 min per a sample. Then the GC-MS was used for quantitative and qualitative analysis. Matrix-matched standards solution and analyte protectant were compared to decrease the matrix effect, and the former showed a better efficacy. Acceptable linearity was achieved in the range of 0.05 - 0.30 mg/L. After matrix-matched standards calibration, recoveries were between 60 and 140%. For the most of pesticides, precision and repeatability were less than 10% and 16%, respectively. The result indicated that the developed method was suitable for the determination of the multi-pesticides in rice wine.

Share and Cite:

Chen, N. , Gao, H. , Ye, N. , Zhong, Q. , Xiong, Z. and Gu, X. (2012) Fast Determination of 22 Pesticides in Rice Wine by Dispersive Solid-Phase Extraction in Combination with GC-MS. American Journal of Analytical Chemistry, 3, 33-39. doi: 10.4236/ajac.2012.31006.

1. Introduction

Rice wine, beer and wine are considered as the three ancient wines [1]. Rice wine is an alcoholic beverage brewed from rice, and pesticides may be used during the period of rice growth. Rice is directly used for fermentation without any processing, and that causes the presence of pesticide residues in rice wine.

Many reports have been published for the determination of pesticides in alcoholic beverage. Major pretreatments of pesticides in food are liquid-liquid extraction (LLE) [2], solid-phase extraction (SPE) [3-6], and solidphase micro-extraction (SPME) [7,8]. In 2003, dispersive solid-phase extraction (d-SPE) method was introduced for the determination of pesticides by Anastassiades et al. [9], and d-SPE was a simple and rapid technique with high recovery for the determination of pesticides in fruit and vegetables [10]. In previous studies, the combination of several sorbents showed a better cleanup result than using primary-secondary amine (PSA) alone for some complex samples [11-13]. However, few reports were introduced for the determination of the pesticides in rice wine.

In this study, a rapid method was introduced for the determination of multi-pesticides in rice wine by GCMS/SIM. Pesticides in rice wine samples were extracted with acetonitrile and cleaned by d-SPE by using the combination of PSA and octadecylsilane (ODS).

2. Experimental

2.1. Reagents and Standards

Acetonitrile (LC grade) was purchased from Merck (Darmstadt, Germany). PSA and ODS were provided by Bonna-Agela Technologies (Tianjin, China). All the standards of pesticide were obtained from Agricultural Environmental Protection Institution (Tianjin, China), and listed in Table 1. Polyethylene glycol (PEG300) and triphenyl phosphate (TPP) were purchased from SCRC (Beijing, China). Other chemicals were from Beijing Chemical Works (Beijing, China). All of the rice wines and olive oil were purchased from local supermarkets, and the wine samples were kept in a freezer (2˚C - 4˚C).

2.2. Instrumentation

Separations of pesticides were performed on a gas chromatography equipped with a mass detector and an autosampler (GC-MS 2010 plus, Shimadzu, Japan). The ex-

Table 1. Information of pesticide and IS, retention time (Rt), molecular weight (Mw), quantification and Identification ions.

tractant of pesticides were injected with a splitless mode.

DB-1701 capillary column (30 m × 0.25 mm × 0.25 μm) was provided by Agilent (Palo Alto, CA, USA). Helium was used as carrier gas, and the flow rate was kept at 1.2 mL/min. The column temperature was maintained at 40˚C for 1 min, and then ramped at 30˚C/min up to 130˚C, then at 5˚C/min up to 250˚C, and finally at 20˚C/min up to 280˚C. The injector temperature was 280˚C, the volume of injection was 1 μL. The MS ionization energy was 70 eV, the ion-source temperature was 230˚C, and the interface temperature was set at 280˚C. The MS detection was performed in Selection ion mode (SIM), and the characteristic of pesticides are listed in Table 1.

2.3. Sample Preparation

TPP (10.00 mg/L, dissolved by acetonitrile) was used as the internal standard (IS) solution, and 100 μL IS solution and 2.4 mL acetonitrile were added into 5.0 mL rice wine sample, and the mixture was vigorously shaken for 2 min. then NaCl (0.50 g) and anhydrous MgSO4 (2.00 g) were added and then vortexed slightly for 1 min. The extract was then centrifuged for 5 min at 5000 rpm. An aliquot of 1.0 mL of the upper layer was transferred to a 2.0 mL micro-centrifuge tube containing 50 mg PSA, 50 mg ODS and 150 mg MgSO4, shaken for 2 min, and then centrifuged for 4 min at 8000 rpm. Finally, 500 μL of extract added 50 μL analyte protectant (prepared as it described by Xu et al. [14]) was placed into an autosampler vial for GC/ MS analysis.

3. Results and Discussion

3.1. Optimization of d-SPE Procedure

3.1.1. Optimization of Sorbents

PSA, ODS, graphitized carbon black (GCB), and Florisilsilica were used as sorbents in d-SPE procedure [15,16]. Among these sorbents, PSA can retain fatty acids and other organic acids, but only slightly reduces the color and vitamin. ODS has a remarkable cleanup ability for non-polar compound, such as some non-polar pigments and vitamins [17]. GCB is a powerful sorbent for pigments, but some pesticides containing benzene ring can be adsorbed by GCB [12]. As shown in Figure 1, peak

Figure 1. GCB adsorbed some pesticides containing benzene ring. Names of pesticides are listed Table 1.

areas of some pesticides reduced when GCB was used as the sorbent of d-SPE. Due to the light color of rice wine, GCB was not necessary. It is important for the cleanup to select an appropriate material as the sorbent. In previous works, some sorbents such as PSA, ODS, anhydrous MgSO4, and GCB, or their combination was selected for the cleanup of pigments in extracts of wine and grape [18-20]. In this study, the combination of 50 mg PSA, 50 mg ODS, and 150 mg anhydrous MgSO4 was selected in d-SPE for rice wine extracts cleanup. The SIM chromatogram of pesticide standards and the internal standard was shown in Figure 2.

3.1.2. Optimization of Temperature and pH

The low temperature minimizes the degradation of some heat-sensitive pesticides [11]. Rice wine and other reagents were kept in freezer (4˚C) overnight before sample preparation. Keeping the samples in low temperature during the d-SPE procedure was important.

The pH of samples will be increased when PSA was added and the stability of some alkali-labile pesticides was affected by pH [18]. Two ways were usually taken to resolve the problem, one was acidifying the extracts quickly to pH∼5, and another was the usage of citrate buffer [21]. In this study, rice wine samples were acidity, and the pH of samples was not obviously increased with the addition of 50 mg PSA.

3.2. Matrix Effects

In GC analysis, analyte protectants and matrix-matched calibration solutions were proved to be effective approaches to minimizing matrix effect [22]. The effects of analyte protectants were compared by Xu et al. [14], and the results showed that PEG300 and olive had a better effect. In our study, the combination of PEG300 and olive was used to be the analyte protectant, and the peak

Figure 2. GC-MS/SIM chromatogram of a pesticide standard of 1.0 mg/L for each pesticide and the internal standard. Names of pesticides are listed Table 1.

areas of pesticides were compared under the three situations (in pure solvent, matrix-matched calibration solutions and analyte protectant). As shown in Figure 3, both analyte protectant and matrix-matched calibration solution can reduce the matrix effect. The former had a better effect on diazinon, fenvalerate and cypermethrin, but for phorate, pyrimethanil, heptachlor, and chlorpyrifosmethyl, matrix-matched solution was better. In our study the method of matrix-matched calibration solution was selected for the minimizing of matrix effect.

3.3. Comparison with Other Preparation

Modern sample preparation techniques should be simple, reliable, cheap, and be similar to common analytical techniques, in order to minimize errors [23]. Information of the major methods used for determining pesticides in alcoholic beverages was presented in Table 2.

d-SPE had advantages in time and cost, but SPE and some other methods had a better cleanup.

3.4. Methodology Evaluation

Linearity was investigated in the range 0.05 - 0.30 mg/L with four calibration points, and the correlation coefficients for pesticides were listed in Table 3. Precision was less than 10%, and the recoveries were from 60% to 140% at three concentration levels (0.10, 0.20 and 0.30 mg/L). A SIM chromatography for blank rice wine sample and spiked rice wine was shown in Figure 4. LOQ, LOD, and other information were also listed in Table 3.

Figure 3. Comparison of pesticide peak areas in pure solvent, matrix-matched standards and adding analyte protectant of mixed PEG and olive oil in optimal concentrations. Names of pesticides are listed Table 1.

4. Conclusion

In this work, a rapid method was developed for the determination of multi-pesticides in rice wine by using dSPE-GC-MS. The effect of different adsorbents was investigated, and the combination of different adsorbents was used for the d-SPE procedure with a high results. And then the approaches of minimizing the matrix effect were compared. And the developed method can be used for the determination of pesticides in rice wine samples.

Table 2. Information of some preparations.

(a)(b)

Figure 4. SIM chromatography for (a) blank rice wine sample; (b) blank rice wine spiked with 0.3 mg/L of the pesticides. Names of pesticides are on Table 1.

Table 3. Average recovery (%), precision (%, RSD), repeatability (%, RSD), limit of quantitation (LOQ, mg/L), limit of detection (LOD, mg/L) and R2 obtained with the d-SPE method and analyzed by GC/MS. Spiking concentration levels were 0.10, 0.20,and 0.30 mg/L, respectively.

5. Acknowledgements

This work was supported by China Spark Program (No. 2010GA700005).

NOTES

Conflicts of Interest

The authors declare no conflicts of interest.

References

[1] H. Yu, Y. Ying, X. Fu and H. Lu, “Quality Determination of Chinese Rice Wine Based on Fourier Transform Near Infrared Spectroscopy,” Journal of Near Infrared Spec- troscopy, Vol. 14, No. 1, 200, pp. 37-44. doi:10.1255/jnirs.584
[2] D. T. Likas, N. G. Tsiropoulos and G. E. Miliadis, “Rapid Gas Chromatographic Method for the Determination of Famoxadone, Trifloxystrobin and Fenhexamid Residues in Tomato, Grape and Wine Samples,” Journal of Chro- matography A, Vol. 1150, No. 1-2, 2007, pp. 208-214. doi:10.1016/j.chroma.2006.08.041
[3] A. Economou, H. Bo-titsi, S. Antoniou and D. Tsipi, “De- termination of Multi-class Pesticides in Wines by Solid- phase Extraction and Liquid Chromatography-Tandem Mass Spectrometry,” Journal of Chromatography A, Vol. 1216, No. 31, 2009, pp. 5856-5867. doi:10.1016/j.chroma.2009.06.031
[4] J. J. Jimenez, J. L. Bernal, M. J. Del Nozal, L. Toribio and J. Bernal, “Use of SPE—GC/EIMS for Residue Ana- lysis in Wine Elaborated from Musts Spiked with Formu- lations of Chlorpyri-phos—Methyl, Methiocarb, Dicofol, and Cyproconazol,” Journal of Separation Science, Vol. 30, No. 4, 2007, pp. 547-556. doi: 10.1002/jssc.200600345
[5] I. Carpinteiro, M. Ramil, I. Rodríguez and R. Cela, “Determination of Fungicides in Wine by Mixed-mode Solid Phase Extraction and Liquid Chromatography Coupled to Tandem Mass Spectrometry,” Journal of Chromatography A, Vol. 1217, No. 48, 2010, pp. 7484-7492. doi:10.1016/j.chroma.2010.09.080
[6] G. F. Pang, C. L. Fan, Y. M. Liu, Y. Z. Cao, J. J. Zhang, B. L. Fu, X. M. Li, Z. Y. Li and Y. P. Wu, “Multi-Resi- due Method for the Determination of 450 Pesticide Resi- dues in Honey, Fruit Juice and Wine by Double-Cartridge Solid-Phase Extraction/Gas Chromatogra-phy-Mass Spectrometry and Liquid Chromatography-Tandem Mass Spec- trometry,” Food Additives & Contaminants: Part A, Vol. 23, No. 8, 2006, pp. 777-810. doi:10.1080/02652030600657997
[7] D. Zhan, R. E. Anli, N. Vural and M. Bayram, “Determination of Chloroanisoles and Chlorophenols in Cork and Wine by Using HS-SPME and GC-ECD Detection,” Jour- nal of the Institute of Brewing, Vol. 115, No. 1, 2009, pp. 71-77.
[8] L. M. Ravelo-Pérez, J. Hernández-Borges, T. M. Borges- Miquel and Má Rodríguez-Delgado, “Solid-Phase Mi- croextraction and Sample Stacking Micellar Electroki- netic Chromatography for the Analysis of Pesticide Re- sidues in Red Wines,” Food Chemistry, Vol. 111, No. 3, 2008, pp. 764-770. doi:10.1016/j.foodchem.2008.04.020
[9] M. Anastassiades, S. J. Lehotay, D. Tajnbaher and F. J. Schenck, “Fast and Easy Multiresidue Method Employing Acetonitrile Extrac-tion/Partitioning and ‘Dispersive Solid- Phase Extraction’ for the Determination of Pesticide Re- sidues in Produce,” Journal of AOAC International, Vol. 86, No. 2, 2003, pp. 412-431.
[10] J. Dong, X. M. Gong, L. Zhang and H. T. Wang, “Determination of Imidacloprid, Tebufenozide, Avennectins and Hexythiazox in Vegetables by QuEChERS-HPLC,” Chi- nese Journal of Analysis Laboratory, Vol. 3, 2008, pp. 91-94.
[11] S. H. Patil, K. Banerjee, S. Dasgupta, D. P. Oulkar, S. B. Patil, M. R. Jadhav, R. H. Savant, P. G. Adsule and M. B. Deshmukh, “Multiresidue Analysis of 83 Pesticides and 12 Dioxin-like Polychlorinated Biphenyls in Wine by Gas Chro-matography-Time-of-Flight Mass Spectrometry,” Jour- nal of Chromatography A, Vol. 1216, No. 12, 2009, pp. 2307-2319. doi:10.1016/j.chroma.2009.01.091
[12] K. Zhang, J. W. Wong, D. G. Hayward, P. Sheladia, A. J. Krynitsky, F. J. Schenck, M. G. Webster, J. A. Ammann and S. E. Ebeler, “Multiresidue Pesticide Analysis of Wines by Dispersive Solid-Phase Extrac-tion and Ultra- high-Performance Liquid Chromatogra-phy-Tandem Mass Spectrometry,” Journal of Agricultural and Food Chem- istry, Vol. 57, No. 10, 2009, pp. 4019-4029. doi:10.1021/jf9000023
[13] S. C. Cunha, J. O. Fernandes, A. Alves and M. Oliveira, “Fast Low-pressure Gas Chromatogra-phy-Mass Spectro- metry Method for the Determination of Multiple Pesti- cides in Grapes, Musts and Wines,” Journal of Chroma- tography A, Vol. 1216, No. 1, 2009, pp. 119-126. doi:10.1016/j.chroma.2008.11.015
[14] X. Xu, L. Li, W. Zhong and Y. He, “Rapid GC-MS Ana- lysis of Pesticide Residues Using Analyte Protectants,” Analytical Letters, Vol. 42, No. 16, 2009, pp. 2578-2591. doi:10.1080/00032710903243646
[15] J. M. Lee, J. W. Park, G. C. Jang and K. J. Hwang, “Com- parative Study of Pesticide Multi-Residue Extraction in Tobacco for Gas Chromatogra-phy—Triple Quadrupole Mass Spectrometry,” Journal of Chromatography A, Vol. 1187, No. 1, 2008, pp. 25-33. doi:10.1016/j.chroma.2008.02.035
[16] Y. Jiang, X. Li, J. Xu, C. Pan, J. Zhang and W. Niu, “Multiresidue Method for the Determination of 77 Pes- ticides in Wine Using QuEChERS Sample Preparation and Gas Chromatography with Mass Spec-trometry,” Food Additives & Contaminants: Part A, Vol. 26, No. 6, 2009, pp. 859-866. doi:10.1080/02652030902822794
[17] W. Shen, K. Yu, Q. Gui, Y. Jiang, Z. Zhao, C. Shen, B. Wu and X. Chu, “Determination of 107 Pesticide Resi- dues in Vegetables Using Off-Line Dispersive Solid- phase Extraction and Gas Chroma-tography-tandem Mass Spectrometry,” Chinese Journal of Chromatography, Vol. 4, 2009, pp. 391-400.
[18] P. Payá, M. Anastassiades, D. Mack, I. Sigalova, B. Tas- delen, J. Oliva and A. Barba, “Analysis of Pesticide Re- sidues Using the Quick Easy Cheap Effective Rugged and Safe (QuEChERS) Pesticide Multiresidue Method in Com- bination with Gas and Liquid Chromatography and Tan- dem Mass Spectrometric Detection,” Analytical and Bioanalytical Chemistry, Vol. 389, No. 6, 2007, pp. 1697- 1714. doi:10.1007/s00216-007-1610-7
[19] C. Le-sueur, P. Knittl, M. Gartner, A. Mentler and M. Fuerhacker, “Analysis of 140 Pesticides from Conven- tional Farming Foodstuff Samples after Extraction with the Modified QuECh-eRS Method,” Food Control, Vol. 19, No. 9, 2008, pp. 906-914. doi:10.1016/j.foodcont.2007.09.002
[20] T. D. Nguyen, J. E. Yu, D. M. Lee and G. H. Lee, “A Multiresidue Method for the Determination of 107 Pe- sticides in Cabbage and Radish Using QuEChERS Sam- ple Preparation Method and Gas Chromato-graphy Mass Spectrometry,” Food Chemistry, Vol. 110, No. 1, 2008, pp. 207-213. doi:10.1016/j.foodchem.2008.01.036
[21] A. Garrido Frenich, J. L. Martínez Vidal, E. Pastor- Montoro and R. Romero-González, “High-Throughput Determination of Pesticide Residues in Food Commodi- ties by Use of Ultra-performance Liquid Chromatography —Tandem Mass Spectrometry,” Analytical and Bioanalytical Chemistry, Vol. 390, No. 3, 2008, pp. 947-959. doi:10.1007/s00216-007-1746-5
[22] K. Ma?tovská, S. J. Le-hotay and M. Anastassiades, “Com- bination of Analyte Protec-tants to Overcome Matrix Ef- fects in Routine GC Analysis of Pesticide Residues in Food Matrixes,” Analytical Chemistry, Vol. 77, No. 24, 2005, pp. 8129-8137. doi:10.1021/ac0515576
[23] A. Beyer and M. Biziuk, “Ap-plications of Sample Prepa- ration Techniques in the Analysis of Pesticides and PCBs in Food,” Food Chemistry, Vol. 108, 2008, pp. 669-680. doi:10.1016/j.foodchem.2007.11.024

Copyright © 2024 by authors and Scientific Research Publishing Inc.

Creative Commons License

This work and the related PDF file are licensed under a Creative Commons Attribution 4.0 International License.