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Stereoselective Separation of Triazole Fungicides Using the ACQUITY UPC2 System and ACQUITY UPC2 Trefoil Chiral Columns

Applications | 2015 | WatersInstrumentation
SFC
Industries
Environmental, Food & Agriculture
Manufacturer
Waters

Summary

Importance of the Topic

The enantioselective analysis of chiral pesticides is critical in agrochemical research and environmental monitoring.
Different stereoisomers can exhibit distinct biological activity and environmental fate, making accurate resolution of enantiomers and diastereomers essential.
Rapid and reliable separation of these isomers supports optimized pesticide efficacy and reduced environmental impact.

Objectives and Overview

This study presents fast and reproducible analytical methods for stereoselective separation of twelve triazole fungicides using supercritical fluid chromatography (SFC) on the Waters ACQUITY UPC2 system coupled with Trefoil chiral columns.

Methodology and Instrumentation

  • Instrument: Waters ACQUITY UPC2 System with Photodiode Array Detector and Empower 3 Software
  • Columns: ACQUITY UPC2 Trefoil AMY1 and CEL1 (3.0 × 150 mm, 2.5 µm)
  • Mobile phase: Supercritical CO2 with methanol or mixed alcohol co-solvents (ethanol, 2-propanol)
  • Operating conditions: Pressure 110–207 bar, flow rates 1.5–3.5 mL/min, temperatures 10–45 °C
  • Sample preparation: Racemic standards in methanol or acetonitrile at 1 mg/mL (100 µg/mL for selected compounds)

Main Results and Discussion

  • Twelve triazole fungicides were resolved with baseline separation for most compounds in under 1.5 minutes on AMY1 with methanol modifier.
  • Uniconazole, penconazole, and hexaconazole achieved baseline separation in less than 1.2 minutes using a 50:50 2-propanol/ethanol mixture.
  • Propiconazole (two chiral centers) was resolved in under 2.8 minutes on AMY1, while cyproconazole and bromuconazole were separated in under 4.5 minutes on CEL1.
  • Resolution factors (Rs) exceeded 1.75 for all stereoisomers, reaching values above 10 and up to 27 for some transitions.
  • Reproducibility (n=8) showed percent RSDs ≤ 0.60% for retention time, peak area, height, and resolution for bromuconazole.
  • Compared to normal-phase HPLC and conventional SFC, UPC2 delivered 3–40 times faster separations with reduced solvent consumption.

Benefits and Practical Applications

  • Enhanced sample throughput with run times often below two minutes.
  • Reduced consumption of organic solvents and lower hazardous waste.
  • Reliable enantiomeric and diastereomeric quantification for quality control and environmental studies.

Future Trends and Opportunities

Integration of advanced chiral stationary phases and mass spectrometric detection could extend this approach to a broader range of chiral agrochemicals and complex matrices.
Automation and online fraction collection may further increase throughput and facilitate preparative separations.
Enantioselective analyses will support regulatory compliance and environmental fate investigations.

Conclusion

The combination of UPC2 and Trefoil chiral columns offers a rapid, robust, and green method for stereoselective separation of triazole fungicides, enabling high-resolution enantiomeric analysis with minimal solvent use and improved laboratory productivity.

Instrumentation

  • Waters ACQUITY UPC2 System
  • ACQUITY UPC2 Photodiode Array Detector
  • Empower 3 Software
  • ACQUITY UPC2 Trefoil AMY1 and CEL1 Columns (3.0 × 150 mm, 2.5 µm)

References

  • Sekhon BS. Chiral pesticides. J Pestic Sci 34:1–12, 2009.
  • Liu WP. Pesticide Environmental Chemistry. Chemical Industry Press, Beijing, China, 2006.
  • Jin L et al. Enantiomeric resolution of five chiral pesticides by SFC. J Chrom Sci 49:739–743, 2011.
  • Toribo L et al. Chiral separation of triazole pesticides by SFC. J Chrom A 1046:249–253, 2004.
  • McCauley JP et al. Enantiomeric and Diastereomeric Separations of Pyrethroids Using UPC2. Waters Application note, 2012.
  • Perez-Fernandez V et al. Chiral separation of agricultural fungicides. J Chrom A 1218:6561–682, 2011.
  • Zhou Y et al. Enantiomer separation of triazole fungicides by HPLC. Chirality 21:421–427, 2009.
  • Ye J et al. Enantioselective separation and analysis of chiral pesticides by HPLC. Trends Anal Chem 28(10):1148–1163, 2009.
  • Wang P et al. Direct enantiomeric resolutions of chiral triazole pesticides by HPLC. J Biochem Biophys Methods 62:219–230, 2005.
  • Wang P et al. Chiral separation of triazole pesticide enantiomers by amylose-tris(3,5-dimethylphenylcarbamate) CSP. J Chrom Sci 46:787–792, 2008.
  • Zhang H et al. HPLC-MS/MS enantioseparation of triazole fungicides using polysaccharide CSPs. J Sep Sci 35:773–781, 2012.
  • Zhang Q et al. Enantioselective bioactivity, acute toxicity and dissipation of flutriafol. J Hazard Mater 284:65–72, 2015.
  • Qiu J et al. Enantiomeric separation of triazole fungicides with 3-µm and 5-µm chiral columns by RP-HPLC. Chirality 23:479–486, 2011.
  • Chai T et al. Stereoselective determination of chiral fungicides in soil by LC-MS/MS. J Sep Sci 37:595–601, 2014.
  • Ye X et al. Enantioselective degradation of tebuconazole in wheat and soil. Adv Mater Res 726–731:348–356, 2013.
  • Wang X et al. Enantioselective degradation of tebuconazole in vegetables and soils. Chirality 24:104–111, 2012.
  • Wang H et al. Enantioselective bioaccumulation of diniconazole in earthworms. Ecotoxicol Environ Safety 99:98–104, 2014.
  • Li Y et al. Enantioselective determination of triazole fungicides in soil and water by LC-MS/MS. J Chrom A 1224:51–60, 2012.
  • del Nozal MJ et al. Separation of triadimefon and triadimenol stereoisomers by SFC. J Chrom A 986:135–141, 2003.

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