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The PFAS conundrum:
Mass spectrometry
solutions for addressing it
Shimadzu Scientific Instruments, Columbia, MD
Introduction
The increasing interest regarding the occurrence of Per- and Polyfluoroalkyl
Substances (PFAS) in the environment since the general public become aware of the
results from the Unregulated Contaminant Monitoring Rule 3 and the quantitation of
GenX in drinking water has resulted in an acceleration of activities by stakeholders
involved in addressing this issue.
Multiple Federal and State Agencies (e.g. EPA, DOD, DEQs and DEPs) in the United
States as well as international organizations (e.g. ASTM) are quickly publishing new
analytical methodologies for PFAS monitoring and establishing more stringent limits.
However, these rapid changes in monitoring requirements pose a challenge for
environmental laboratories.
Introduction
Liquid Chromatography with Mass Spectrometry-based detection is established as the
most suitable technology for meeting the requirements from official methods released
up to date for monitoring PFAS. These methods require sample preconcentration by
Solid Phase Extraction using different sorbents or allow for direct sample injection. In
the work presented here, samples were prepared and analyzed following the
requirements from current EPA and ASTM methods (EPA 537, EPA 537.1, ASTM
D7979). Various mass spectrometry platforms (LC/MS/MS, LC/QTOF) presenting
different technical specifications were employed for this purpose.
A comparison of instruments’ performance was conducted in this work. The ultimate
goal was to create a guidance tools for selecting the most appropriate platform for the
analysis of PFAS based on end-user’ objective.
Experimental Approach
Linearity, repeatability, precision, accuracy and method detection limits were
determined with reagent water and selected environmental samples for the purpose of
comparing instruments’ performance for up to 30 individual PFAS included in either
EPA or ASTM methods. Quantitation of selected samples for assessing repeatability,
precision and accuracy was performed with the three same instruments for developing
instrument’s selection guidelines.
A summary of analytical methods evaluated, list of target compounds monitored and
instrumentation employed in this work are included in Table 1.
Experimental Approach
Table 1. Methods, target compounds and
instruments evaluated
Experimental Approach
Figure 1. Methods Detection Limits of common targets from methods evaluated
Method Detection Limit,
ng/L
(537.1-8045)
HFPO-DA 0.88
ADONA 0.58
9Cl-PF3ONS 0.82
11Cl-
PF3OUdS
1.25
Experimental Approach
Figure 2. % recoveries with %RSD from Precision and Accuracy studies
Results
Calibration curves ranging between 5 ng/L and 400 ng/L (based on the 250x
concentration factor established in the EPA methods) presented acceptable linearity
(R2>0.99). Method Detection Limits (MDLs) calculated based on the results from three
instruments of different technical specifications ranged between 0.6 ng/L and 5.4 ng/L.
Individual MDLs from common compounds in the three methods studied are reported
in Figure 1. Precision and Accuracy results are included in Figure 2 as % recoveries
and %RSD.
Results
Figure 3. Guidance Tool
Conclusion
Performance of three instruments (two LC/MS/MS – Triple Quad LCMS-8045 and
LCMS-8060; one LC/QTOF – QTOF-9030) was similar for the quantitation of
selected target PFAS. The MDLs were comparable, independently from the
sample preparation approach. Precision and accuracy did not differ between the
methods and instruments. A guidance tool to help selecting the most appropriate
instrumentation for this application is included in Figure 3.
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questions or require additional information about our research,
products, or services, please visit our Web site at:
www.ssi.shimadzu.com
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The PFAS conundrum: Mass spectrometry solutions for addressing it.

  • 1. The PFAS conundrum: Mass spectrometry solutions for addressing it Shimadzu Scientific Instruments, Columbia, MD
  • 2. Introduction The increasing interest regarding the occurrence of Per- and Polyfluoroalkyl Substances (PFAS) in the environment since the general public become aware of the results from the Unregulated Contaminant Monitoring Rule 3 and the quantitation of GenX in drinking water has resulted in an acceleration of activities by stakeholders involved in addressing this issue. Multiple Federal and State Agencies (e.g. EPA, DOD, DEQs and DEPs) in the United States as well as international organizations (e.g. ASTM) are quickly publishing new analytical methodologies for PFAS monitoring and establishing more stringent limits. However, these rapid changes in monitoring requirements pose a challenge for environmental laboratories.
  • 3. Introduction Liquid Chromatography with Mass Spectrometry-based detection is established as the most suitable technology for meeting the requirements from official methods released up to date for monitoring PFAS. These methods require sample preconcentration by Solid Phase Extraction using different sorbents or allow for direct sample injection. In the work presented here, samples were prepared and analyzed following the requirements from current EPA and ASTM methods (EPA 537, EPA 537.1, ASTM D7979). Various mass spectrometry platforms (LC/MS/MS, LC/QTOF) presenting different technical specifications were employed for this purpose. A comparison of instruments’ performance was conducted in this work. The ultimate goal was to create a guidance tools for selecting the most appropriate platform for the analysis of PFAS based on end-user’ objective.
  • 4. Experimental Approach Linearity, repeatability, precision, accuracy and method detection limits were determined with reagent water and selected environmental samples for the purpose of comparing instruments’ performance for up to 30 individual PFAS included in either EPA or ASTM methods. Quantitation of selected samples for assessing repeatability, precision and accuracy was performed with the three same instruments for developing instrument’s selection guidelines. A summary of analytical methods evaluated, list of target compounds monitored and instrumentation employed in this work are included in Table 1.
  • 5. Experimental Approach Table 1. Methods, target compounds and instruments evaluated
  • 6. Experimental Approach Figure 1. Methods Detection Limits of common targets from methods evaluated Method Detection Limit, ng/L (537.1-8045) HFPO-DA 0.88 ADONA 0.58 9Cl-PF3ONS 0.82 11Cl- PF3OUdS 1.25
  • 7. Experimental Approach Figure 2. % recoveries with %RSD from Precision and Accuracy studies
  • 8. Results Calibration curves ranging between 5 ng/L and 400 ng/L (based on the 250x concentration factor established in the EPA methods) presented acceptable linearity (R2>0.99). Method Detection Limits (MDLs) calculated based on the results from three instruments of different technical specifications ranged between 0.6 ng/L and 5.4 ng/L. Individual MDLs from common compounds in the three methods studied are reported in Figure 1. Precision and Accuracy results are included in Figure 2 as % recoveries and %RSD.
  • 10. Conclusion Performance of three instruments (two LC/MS/MS – Triple Quad LCMS-8045 and LCMS-8060; one LC/QTOF – QTOF-9030) was similar for the quantitation of selected target PFAS. The MDLs were comparable, independently from the sample preparation approach. Precision and accuracy did not differ between the methods and instruments. A guidance tool to help selecting the most appropriate instrumentation for this application is included in Figure 3.
  • 11. Need More Info? Thank you for viewing this presentation. Should you have any questions or require additional information about our research, products, or services, please visit our Web site at: www.ssi.shimadzu.com Follow us on Twitter @shimadzussi

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