New Analytical Method for Testing Fluorotelomer Alcohols in Water

Technical notes | 2024 | ALS EuropeInstrumentation
GC/MS/MS, GC/MSD, GC/QQQ, Laboratory analysis
Industries
Environmental, Food & Agriculture
Manufacturer

Summary

Significance of the Topic



Fluorotelomer alcohols (FTOHs) represent a key subclass of per- and polyfluoroalkyl substances (PFAS), notable for their role as precursors to persistent perfluorocarboxylic acids (PFCAs) such as PFOA and PFHxA. Their volatility and widespread use in industrial formulations, including surfactants, polymers, and aqueous film-forming foams (AFFF), facilitate long-range transport and potential human and ecosystem exposure. Reliable quantification of FTOHs in water matrices is therefore critical for environmental monitoring and risk assessment.

Objectives and Study Overview



The primary goal of this study by ALS R&D was to develop and validate a sensitive, robust, and selective analytical method for quantifying 6:2 and 8:2 FTOHs in surface water, groundwater, and drinking water. Pending UKAS accreditation, the method aims to achieve low detection limits, high reproducibility, and streamlined sampling procedures to support regulatory compliance and research applications.

Methodology and Instrumentation



Water samples are collected in 40 mL clear volatile organic compound vials containing 2 mL of methanol as a fixative to prevent analyte loss. Zero headspace is maintained, and samples are stored under controlled conditions with a maximum holding time of five days.

Key instrumentation and analytical parameters:
  • Gas chromatography–triple quadrupole tandem mass spectrometry (GC-MS/MS) with positive chemical ionization (PCI)
  • Detection limits: 5 ng/L for both 6:2 FTOH (CAS 647-42-7) and 8:2 FTOH (CAS 678-39-7)
  • Data acquisition optimized for selectivity and signal-to-noise ratio


Main Results and Discussion



The GC-MS/MS-PCI method demonstrated excellent sensitivity and reproducibility for trace-level FTOHs in various water matrices. Validation data confirm reliable quantification at or below regulatory screening levels. Environmental applications revealed ubiquitous detection of FTOHs in surface water, wastewater influents and effluents, landfill leachate, rainwater, and AFFF-impacted sites. Biotransformation pathways in aquatic systems underscore the importance of monitoring FTOHs as indirect sources of more persistent PFCAs.

Benefits and Practical Applications



This method offers multiple advantages for laboratories and environmental agencies:
  • Low detection limits suitable for compliance monitoring
  • Robust sampling and storage protocols reducing analyte loss
  • Applicability across diverse water matrices
  • Support for fate and transport studies of PFAS precursors


Future Trends and Applications



Emerging directions include:
  • Expansion to a broader range of fluorotelomer isomers and related PFAS precursors
  • Integration with high-resolution mass spectrometry for non-target screening
  • Automated sample preparation workflows to increase throughput
  • Coupled studies of biotransformation kinetics under varied redox conditions


Conclusion



The validated GC-MS/MS-PCI method provides a reliable and sensitive approach for the quantification of 6:2 and 8:2 FTOHs in water. Its implementation will enhance PFAS monitoring programs, support regulatory compliance, and contribute to a deeper understanding of environmental fate and human exposure risks.

References


  1. Ayala-Cabrera J.F., Contreras L., Moyano E., Santos F.J. A novel methodology for neutral PFAS in water by GC-APPI-HRMS. Anal Chim Acta. 2020; DOI:10.1016/j.aca.2019.12.004.
  2. Dauchy X., Bioteux V., Back C., Colin A., Hémard J., Rosin C., Munoz J. Mass flows and fate of PFASs in a fluorochemical wastewater plant. Sci Total Environ. 2017;576:549–558.
  3. Dimzon I.K., Westerveld J., Gremmel C., Fromel T., Knepper T.P., de Voogt P. Simultaneous determination of volatile PFAS in wastewater treatment plant air and water. Anal Bioanal Chem. 2017;409:1395–1404.
  4. Favreau P., Poncioni-Rothlisberger C., Place B.J., Bouchex-Bellomie H., Weber A., Tremp J., Field J.A., Kohler M. Multianalyte profiling of PFASs in liquid commercial products. Chemosphere. 2017;171:491–501.
  5. Higgins C., Field J., Deeb R., Conder J. FAQs regarding PFASs associated with AFFF use at U.S. military sites. ESTCP; 2017.
  6. Herzke D., Olsson E., Posner S. PFASs in consumer products in Norway – a pilot study. Chemosphere. 2012;88:980–987.
  7. Kim M.H., Wang N., McDonald T., Chu K.-H. Biodefluorination of FTOHs by Pseudomonas strains. Biotechnol Bioeng. 2012;109:3041–3048.
  8. Ma H., Peng H., Chen H., Shang W., Zheng X., Yang M., Zhang Y. Long-term trends of FTOHs in a textile-impacted WWTP. Chemosphere. 2022;299.
  9. Portolés T., Rosales L.E., Sancho J.V., Santos J., Moyano E. GC-MS/MS-APCI for fluorotelomer alcohols and sulfonamides. J Chromatogr A. 2015;1413:107–116.
  10. Titaley I.A., Florentino B., Cruz D., Barlaz M., Field J.A. Neutral PFAS in landfill gas by TD-GC-MS. Environ Sci Technol Lett. 2023;10(3):214–222.
  11. Wang N., Szostek B., Buck R.C., Folsom P.W., Sulecki L.M., Capka V., Berti W.R., Gannon J.T. Fluorotelomer alcohol biodegradation: direct evidence. Environ Sci Technol. 2005;39:7516–7528.
  12. Yan P.F., Dong S., Manz K.E., Liu C., Woodcock M.J., Mezzari M.P., Abriola L.M., Pennell K.D., Cápiro N.L. Biotransformation of 8:2 FTOH in AFFF-impacted soil. Environ Sci Technol. 2022;56(19):13728–13739.

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