Direct Injection Screening Method for Per- and Polyfluoroalkyl Substances (PFAS) in Drinking Water Using the High Resolution Time of Flight Mass Spectrometer, the Xevo™ G3 QTof
Applications | 2024 | WatersInstrumentation
Per and polyfluoroalkyl substances (PFAS) are persistent environmental contaminants with widespread industrial and consumer applications. Their resistance to degradation leads to accumulation in water sources and potential health risks. Monitoring both regulated and emerging PFAS in drinking water is critical to protect public health and comply with evolving regulations.
This study evaluates a streamlined direct injection screening workflow for PFAS in drinking water using high resolution time of flight mass spectrometry. It aims to assess sensitivity, dynamic range, and the capability to detect known and unknown PFAS without extensive sample preparation.
Water samples and PFAS standards were injected (10 µL) directly into an UPLC system modified to minimize PFAS background. Data were acquired in negative ion mode using data independent acquisition (MSE) and processed with UNIFI software. Calibration curves were generated from serial dilutions spanning 0.5 to 5000 ng/L.
Forty-six PFAS compounds were screened, with thirty detected at limits of detection ≤5 ng/L and dynamic range exceeding three orders of magnitude. Exemplary sensitivity was demonstrated for perfluorobutanesulfonic acid (PFBS) with a detection limit of 2 ng/L and linearity up to 2000 ng/L (R2=0.99915). Direct analysis of tap, filtered, and MilliQ water identified perfluorohexanoic acid (PFHxA) in tap water at 5 ng/L with mass accuracy better than 1 ppm.
Advances may include higher injection volumes for improved detection, integration of larger suspect and in silico libraries for de novo PFAS identification, and application of complementary structural techniques. Automation and real-time screening could further enhance throughput and data confidence.
The direct injection HRMS workflow on the Xevo G3 QTof provides a rapid, sensitive, and broad-spectrum approach for PFAS screening in drinking water, overcoming limitations of targeted methods and enabling detection of regulated and emerging PFAS with minimal sample preparation.
LC/MS, LC/MS/MS, LC/TOF, LC/HRMS
IndustriesEnvironmental
ManufacturerWaters
Summary
Importance of the Topic
Per and polyfluoroalkyl substances (PFAS) are persistent environmental contaminants with widespread industrial and consumer applications. Their resistance to degradation leads to accumulation in water sources and potential health risks. Monitoring both regulated and emerging PFAS in drinking water is critical to protect public health and comply with evolving regulations.
Objectives and Study Overview
This study evaluates a streamlined direct injection screening workflow for PFAS in drinking water using high resolution time of flight mass spectrometry. It aims to assess sensitivity, dynamic range, and the capability to detect known and unknown PFAS without extensive sample preparation.
Methodology
Water samples and PFAS standards were injected (10 µL) directly into an UPLC system modified to minimize PFAS background. Data were acquired in negative ion mode using data independent acquisition (MSE) and processed with UNIFI software. Calibration curves were generated from serial dilutions spanning 0.5 to 5000 ng/L.
Used Instrumentation
- ACQUITY Premier UPLC System with PFAS kit
- Xevo G3 QTof High Resolution Mass Spectrometer
- UNIFI Scientific Information System and waters_connect software
Main Results and Discussion
Forty-six PFAS compounds were screened, with thirty detected at limits of detection ≤5 ng/L and dynamic range exceeding three orders of magnitude. Exemplary sensitivity was demonstrated for perfluorobutanesulfonic acid (PFBS) with a detection limit of 2 ng/L and linearity up to 2000 ng/L (R2=0.99915). Direct analysis of tap, filtered, and MilliQ water identified perfluorohexanoic acid (PFHxA) in tap water at 5 ng/L with mass accuracy better than 1 ppm.
Benefits and Practical Applications
- Eliminates bias and recovery limitations of SPE by direct injection
- High mass accuracy and sensitivity enable quantification at low ng/L levels
- Allows retrospective data mining for non-target PFAS discovery
- Simplifies workflow and reduces analysis time for routine monitoring
Future Trends and Opportunities
Advances may include higher injection volumes for improved detection, integration of larger suspect and in silico libraries for de novo PFAS identification, and application of complementary structural techniques. Automation and real-time screening could further enhance throughput and data confidence.
Conclusion
The direct injection HRMS workflow on the Xevo G3 QTof provides a rapid, sensitive, and broad-spectrum approach for PFAS screening in drinking water, overcoming limitations of targeted methods and enabling detection of regulated and emerging PFAS with minimal sample preparation.
References
- Giesy JP and Kannan K. Global Distribution of Perfluorooctane Sulfonate in Wildlife. Environ Sci Technol. 35:1339-1342. 2001.
- Pan CG, Liu YS, Ying GG. Perfluoroalkyl Substances in Waste Water Treatment Plants and Drinking Water Treatment Plants. Water Res. 106:562-570. 2016.
- Podder A, Sadmani AHMA, Reinhart D, Chang NB, Goel R. Per and Polyfluoroalkyl Substances as a Contaminant of Emerging Concern in Surface Water. J Hazard Mater. 419:126361. 2021.
- Travis DR. Evidence that There are Two Forms of Fluoride in Human Serum. Nature. 27:1050-1051. 1968.
- Hansen KJ, Clemen LA, Ellefson ME, Johnson HO. Compound Specific Quantitative Characterisation of Organic Fluorochemicals in Biological Matrices. Environ Sci Technol. 35:766-770. 2001.
- Dickman RA and Aga DS. A Review of Recent Studies on Toxicity, Sequestration, and Degradation of Per and Polyfluoroalkyl Substances. J Hazard Mater. 436:129120. 2022.
- European Union Reference Laboratory for Halogenated POPs in Feed and Food. Guidance Document on Analytical Parameters for PFAS in Food and Feed. Version 1.2. May 2022.
- Stockholm Convention on Persistent Organic Pollutants. Text of the Convention. 2019.
- US EPA. Analysis of Per and Polyfluoroalkyl Substances in Aqueous, Solid, Biosolids, and Tissue Samples by LC-MS/MS. Draft Method 1633. July 2023.
- Adams S, Dreolin N, Organtini KL, Hancock P. Analysis of PFAS in Animal Products with an Enhanced Sensitivity LC-MS/MS Method. Waters Application Note 720008108. 2023.
- Organtini K, Rosnack K, Hancock P. Analysis of PFAS in Accordance With EPA 1633 Part 1. Waters Application Note 720008117. 2023.
- US EPA. CompTox Chemicals Dashboard PFAS Master List. Accessed November 2023.
- Charbonnet JA, McDonough CA, Xiao F, et al. Communicating Confidence of PFAS Identification via High Resolution MS. Environ Sci Technol Lett. 9:473-481. 2022.
- US EPA. Method 533 Determination of PFAS in Drinking Water by Isotope Dilution SPE and LC-MS/MS. November 2019.
- NIST Public Data Repository. Suspect List of Possible PFAS. 2023.
- Camdzic D, Dickman RA, Joyce AS, et al. Quantitation of Total PFAS with Fluorine NMR Spectroscopy. Anal Chem. 95:5484-5488. 2023.
- Schymanski EL, Singer HP, Slobodnik J, et al. Non-target Screening with HRMS in Water Analysis. Anal Bioanal Chem. 407:6237-6255. 2015.
- Towhig M, Fujimoto G, Mohan A, et al. Approaches to Non-targeted Analyses of PFAS in Environmental Samples. Waters Application Note 720007184. 2021.
- Khoury-Hollins H, Riba I, Kirk J. Optimization of Source and Transmission Parameters for PFAS Using the Xevo G3 QTof. Waters Application Note 720008118. 2024.
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