Determination of pesticides and persistent organic pollutants in honey by accelerated solvent extraction and GC-MS/MS
Applications | 2017 | Thermo Fisher ScientificInstrumentation
Honey is valued for its nutritional and medicinal attributes but is vulnerable to contamination by persistent organic pollutants and pesticides used in apiculture and agriculture.
Monitoring these residues is crucial for consumer safety and compliance with stringent regulations for organic products.
This study aimed to develop and validate a multiresidue analytical method combining accelerated solvent extraction with inline cleanup and GC–MS/MS detection for quantification of PCBs, PBDEs, organochlorine and organophosphorus pesticides, and other agrochemicals in honey.
A total of 59 organic honey samples from three Italian regions (Calabria, Trentino Alto Adige, Lombardia) were analyzed to assess regional contamination profiles.
The single-step ASE protocol with inline cleanup reduces solvent use, extraction time, and sample handling. Combined with GC–MS/MS, it provides high sensitivity and selectivity for routine monitoring of honey and similar matrices.
Further development may include expanded analyte panels, application to other food matrices, miniaturized extraction formats, and seamless integration with automated workflows and data analysis platforms.
The validated ASE–GC–MS/MS method offers a rapid, reliable, and environmentally friendly approach for comprehensive profiling of pesticide and POP residues in honey, supporting food safety and regulatory compliance efforts.
1. Consonni R; Cagliani LR; Cogliati C. NMR characterization of saccharides in Italian honeys. J Agric Food Chem. 2012;60:4526.
2. FDA. Code of Federal Regulations Title 21 Part 556 Tolerances for residues on new animal drugs. 2016.
3. Canadian Food Inspection Agency. Working Residue Levels in Honey. 2016.
4. Council Regulation (EC) No 1804/1999 on organic production. Official Journal of EU. 1999.
5. Commission Regulation (EC) No 396/2005 on maximum pesticide residues. EU, 2005.
6. Commission Regulation (EC) No 839/2008 amending Directive 396/2005. EU, 2008.
7. EFSA. Monitoring of non-dioxin-like PCBs in food and feed. EFSA J. 2010;8:35.
8. Commission Recommendation 2014/118/EU on monitoring brominated flame retardants in food. 2014.
9. Chiesa LM; Labella GF; Panseri S, et al. POPs in tuna. Chemosphere. 2016;153:162.
10. Chiesa LM; Labella GF; Giorgi A, et al. Pesticides and POPs in Italian organic honeys. Chemosphere. 2016;154:482.
11. Thermo Scientific CAN 120. TPH in Soils by ASE and GC-FID. 2015.
12. Thermo Scientific CAN 121. PCBs in Soils by ASE and GC-MS/MS. 2015.
13. Thermo Scientific CAN 122. POPs in Fish Tissues by ASE and GC-MS/MS. 2015.
14. Ezzell J; Richter B; Francis E. Selective extraction of PCBs using ASE. Am Environ Lab. 1996;8(12):12.
15. Thermo Scientific Application Note 322. PCB extraction from fish tissue using ASE. 1996.
16. Björklund E; Müller A; von Holst C. Fat retainers in ASE for PCBs. Anal Chem. 2001;73:4050.
17. Sporring S; Björklund E. ASE optimization for food and feed. J Chromatogr A. 2004;1040:155.
18. Haglund P; et al. Shape-selective extraction from fish lipid. Anal Chem. 2007;79:2945.
19. Thermo Scientific App Note 356. Perchlorate in vegetation by ASE. 2006.
20. Gentili A; et al. ASE and LC–MS/MS of sulfonamides in foods. J Agric Food Chem. 2004;52:4614.
21. Björklund E; et al. Extraction of POPs from food and feed. Trends Anal Chem. 2006;25:318.
22. Hussen A; et al. ASE for DDT in contaminated soils. Anal Bioanal Chem. 2006;386(5):1525.
23. Hussen A; et al. Pressurized liquid extraction of α-endosulfan. J Chromatogr A. 2006;1103:202.
24. Sporring S; von Holst C; Björklund E. ASE of PCBs with high lipid. Chromatographia. 2006;64:553.
25. Wiberg K; Sporring S; Haglund P; Björklund E. PLE of PCDD/Fs and PCBs. J Chromatogr A. 2007;1138:55.
26. Hussen A; Westbom R; Megersa N; Mathiasson L; Björklund E. PLE of PCBs from soil. J Chromatogr A. 2007;1152:247.
27. Thermo Scientific App Note 409. Acrylamide in food by ASE. 2003.
28. Poerschmann J; Carlson R. ‘In-Cell Fractionation’ by ASE. J Chromatogr A. 2006;1127:18.
29. Poerschmann J; et al. Sequential ASE for fatty acids. J Chromatogr A. 2006;1127:26.
GC/MSD, GC/MS/MS, Sample Preparation, GC/QQQ
IndustriesManufacturerThermo Fisher Scientific
Summary
Importance of the Topic
Honey is valued for its nutritional and medicinal attributes but is vulnerable to contamination by persistent organic pollutants and pesticides used in apiculture and agriculture.
Monitoring these residues is crucial for consumer safety and compliance with stringent regulations for organic products.
Objectives and Study Overview
This study aimed to develop and validate a multiresidue analytical method combining accelerated solvent extraction with inline cleanup and GC–MS/MS detection for quantification of PCBs, PBDEs, organochlorine and organophosphorus pesticides, and other agrochemicals in honey.
A total of 59 organic honey samples from three Italian regions (Calabria, Trentino Alto Adige, Lombardia) were analyzed to assess regional contamination profiles.
Methodology and Instrumentation
- Sample Preparation: 2 g honey mixed with dispersant and sodium sulfate, extracted using Thermo Scientific Dionex ASE 350 with Florisil inline cleanup (hexane/ethyl acetate 4:1, 80 °C, 1500 psi).
- Concentration: Rocket Evaporator to 200 μL final volume.
- Analysis: Thermo Scientific TRACE 1310 GC with PTV injector and TSQ 8000 Evo triple quadrupole MS/MS, operated in SRM mode; software: Xcalibur and TraceFinder.
- Quantification: Matrix-matched calibration, LOD/LOQ calculation, recoveries and repeatability evaluated at 10 ng/g.
Main Results and Discussion
- Method performance: Excellent linearity (r² ≥ 0.99), recoveries between 75 % and 105 %, LOQs from 0.03 to 3.36 ng/g, and repeatability CV ≤ 14 %.
- PCBs: Detected in all samples at 0.27–0.92 ng/g with no significant regional differences.
- PBDEs: Not detected, likely reflecting organic production environments.
- Organochlorine pesticides: Endrin, DDT and metabolites, heptachlor, and endosulfan sulfate were found at low ng/g levels, under current MRLs.
- Organophosphorus pesticides: Multiple OPs (e.g., diazinon 1.13–1.15 ng/g, mevinphos, coumaphos) were prevalent in Trentino Alto Adige and Calabria; Captan noted in Lombardia.
Benefits and Practical Applications
The single-step ASE protocol with inline cleanup reduces solvent use, extraction time, and sample handling. Combined with GC–MS/MS, it provides high sensitivity and selectivity for routine monitoring of honey and similar matrices.
Future Trends and Potential Applications
Further development may include expanded analyte panels, application to other food matrices, miniaturized extraction formats, and seamless integration with automated workflows and data analysis platforms.
Conclusion
The validated ASE–GC–MS/MS method offers a rapid, reliable, and environmentally friendly approach for comprehensive profiling of pesticide and POP residues in honey, supporting food safety and regulatory compliance efforts.
References
1. Consonni R; Cagliani LR; Cogliati C. NMR characterization of saccharides in Italian honeys. J Agric Food Chem. 2012;60:4526.
2. FDA. Code of Federal Regulations Title 21 Part 556 Tolerances for residues on new animal drugs. 2016.
3. Canadian Food Inspection Agency. Working Residue Levels in Honey. 2016.
4. Council Regulation (EC) No 1804/1999 on organic production. Official Journal of EU. 1999.
5. Commission Regulation (EC) No 396/2005 on maximum pesticide residues. EU, 2005.
6. Commission Regulation (EC) No 839/2008 amending Directive 396/2005. EU, 2008.
7. EFSA. Monitoring of non-dioxin-like PCBs in food and feed. EFSA J. 2010;8:35.
8. Commission Recommendation 2014/118/EU on monitoring brominated flame retardants in food. 2014.
9. Chiesa LM; Labella GF; Panseri S, et al. POPs in tuna. Chemosphere. 2016;153:162.
10. Chiesa LM; Labella GF; Giorgi A, et al. Pesticides and POPs in Italian organic honeys. Chemosphere. 2016;154:482.
11. Thermo Scientific CAN 120. TPH in Soils by ASE and GC-FID. 2015.
12. Thermo Scientific CAN 121. PCBs in Soils by ASE and GC-MS/MS. 2015.
13. Thermo Scientific CAN 122. POPs in Fish Tissues by ASE and GC-MS/MS. 2015.
14. Ezzell J; Richter B; Francis E. Selective extraction of PCBs using ASE. Am Environ Lab. 1996;8(12):12.
15. Thermo Scientific Application Note 322. PCB extraction from fish tissue using ASE. 1996.
16. Björklund E; Müller A; von Holst C. Fat retainers in ASE for PCBs. Anal Chem. 2001;73:4050.
17. Sporring S; Björklund E. ASE optimization for food and feed. J Chromatogr A. 2004;1040:155.
18. Haglund P; et al. Shape-selective extraction from fish lipid. Anal Chem. 2007;79:2945.
19. Thermo Scientific App Note 356. Perchlorate in vegetation by ASE. 2006.
20. Gentili A; et al. ASE and LC–MS/MS of sulfonamides in foods. J Agric Food Chem. 2004;52:4614.
21. Björklund E; et al. Extraction of POPs from food and feed. Trends Anal Chem. 2006;25:318.
22. Hussen A; et al. ASE for DDT in contaminated soils. Anal Bioanal Chem. 2006;386(5):1525.
23. Hussen A; et al. Pressurized liquid extraction of α-endosulfan. J Chromatogr A. 2006;1103:202.
24. Sporring S; von Holst C; Björklund E. ASE of PCBs with high lipid. Chromatographia. 2006;64:553.
25. Wiberg K; Sporring S; Haglund P; Björklund E. PLE of PCDD/Fs and PCBs. J Chromatogr A. 2007;1138:55.
26. Hussen A; Westbom R; Megersa N; Mathiasson L; Björklund E. PLE of PCBs from soil. J Chromatogr A. 2007;1152:247.
27. Thermo Scientific App Note 409. Acrylamide in food by ASE. 2003.
28. Poerschmann J; Carlson R. ‘In-Cell Fractionation’ by ASE. J Chromatogr A. 2006;1127:18.
29. Poerschmann J; et al. Sequential ASE for fatty acids. J Chromatogr A. 2006;1127:26.
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