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PFOS or PreFOS? Are perfluorooctane sulfonate precursors (PreFOS) important determinants of human and environmental perfluorooctane sulfonate (PFOS) exposure?
Abstract
The extent to which perfluorooctanesulfonate precursors (PreFOS) play a role in human or environmental exposure to perfluorooctanesulfonate (PFOS) is not well characterized. The diversity of manufactured PreFOS and its degradation products (e.g. C(8)F(17)SO(2)R and C(8)F(17)SO(2)NR'R'', where R is H or F, and R' and R'' are various) has made it difficult to track their fate. Temporal trends of PFOS in both humans and wildlife are discrepant, thus it is difficult to predict future exposure, and hypotheses about the role of PreFOS have been raised. Although abiotic degradation of commercially important PreFOS materials requires further research, current data suggest that the yield of PFOS is negligible or minor. On the other hand, in vivo biotransformation of PreFOS yields PFOS as the major metabolite, and >32% yields have been observed. In Canadians, exposure to PreFOS was equivalent or greater than direct PFOS exposure prior to 2002. In most ocean water, PFOS is dominant to PreFOS, but in the oceans east of Greenland there may be more PreFOS than PFOS, consistent with the fact that whales and humans in this region also show evidence of substantial PreFOS exposure. Quantitative assessments of PFOS body-burdens coming from PreFOS are complicated by the fact that PreFOS partitions to the cellular fraction of blood, thus biomonitoring in serum under predicts PreFOS relative to PFOS. Many unknowns exist that prevent accurate modelling, thus analytical methods that can distinguish directly manufactured PFOS, from PFOS that has been biotransformed from PreFOS, should be applied in future human and environmental monitoring. Two new source tracking principles are presented and applied to human serum.
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“PFSAs and their precursors have been manufactured almost exclusively by ECF which produced a mixture of linear (70%) and many branched (total 30%) isomers [32].”
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“Migration of N-EtFOSE based chemicals from carpet cleaning products and food packaging materials and subsequent transformation to PFOS may explain these results [10, 11].”
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Self-citationWood, R. J., Sidnell, T., Ross, I., McDonough, J. T., Lee, J., & Bussemaker, M. (2020) · Ultrasonics Sonochemistry · doi:10.1016/j.ultsonch.2020.105196 · Cited by 104
Chen, M., Qiang, L., Pan, X., Fang, S., Han, Y., & Zhu, L. Y. (2015) · Environmental Science & Technology · doi:10.1021/acs.est.5b00488 · Cited by 99
Systematic developmental toxicity assessment of a structurally diverse library of PFAS in zebrafish
Truong, L., Rericha, Y., Thunga, P., Marvel, S. W., Wallis, D. J., Simonich, M. T., Field, J. A., Cao, D., Reif, D. M., & Tanguay, R. L. (2022) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2022.128615 · Cited by 102
“FOSA, an intermediate metabolite of longer-chain PFOS precursors (Martin et al., 2010), has been identified in previous studies as particularly bioactive compared to other PFAS in zebrafish (Dasgupta et al.”
BackgroundBraune, B. M., & Letcher, R. J. (2013) · Environmental Science & Technology · doi:10.1021/es303733d · Cited by 98
Zhao, Y. G., Wong, C. K. C., & Wong, M. H. (2012) · Chemosphere · doi:10.1016/j.chemosphere.2012.05.043 · Cited by 101
Treatment of perfluorooctane sulfonic acid (PFOS) using a large-scale sonochemical reactor
Gole, V. L., Fishgold, A., Sierra‐Álvarez, R., Deymier, P. A., & Keswani, M. (2017) · Separation and Purification Technology · doi:10.1016/j.seppur.2017.11.009 · Cited by 97
Sedlak, M. D., Benskin, J. P., Wong, A., Grace, R., & Greig, D. J. (2017) · Chemosphere · doi:10.1016/j.chemosphere.2017.04.096 · Cited by 99
Self-citationPer- and polyfluoroalkyl substances (PFAS) and total fluorine in fire station dust
Young, A. S., Sparer, E. H., Pickard, H. M., Sunderland, E. M., Peaslee, G. F., & Allen, J. G. (2021) · Journal of Exposure Science & Environmental Epidemiology · doi:10.1038/s41370-021-00288-7 · Cited by 105
Franklin, J. (2015) · Integrated Environmental Assessment and Management · doi:10.1002/ieam.1642 · Cited by 95
“For TMFs, the ratio of themaximum to minimum reported values is not so great, but it reaches about 20 for the most intensely studied PFASs (PFOA and PFOS).”
BackgroundInfluentialChen, M., Zhu, L. Y., Wang, Q., & Shan, G. (2020) · Environmental Pollution · doi:10.1016/j.envpol.2020.115887 · Cited by 99
Gebbink, W. A., Glynn, A. W., & Berger, U. (2015) · Environmental Pollution · doi:10.1016/j.envpol.2015.01.024 · Cited by 98
“The manufacturing of PFOS and its precursors resulted in a mixture of linear and branched isomers (Martin et al., 2010), and production was phased out by the main manufacturer”
BackgroundInfluentialGebbink, W. A., Glynn, A. W., Darnerud, P. O., & Berger, U. (2015) · Environmental Pollution · doi:10.1016/j.envpol.2014.12.022 · Cited by 94
“When using a biotransformation factor determined in a study with rats (20% biotransformation of precursors to PFOS (Martin et al., 2010)) the total dietary intakes of PFOS (precursor intakes converted to PFOS on a molar basis) were”
BackgroundMethodWidening the Lens on PFASs: Direct Human Exposure to Perfluoroalkyl Acid Precursors (pre-PFAAs)
McDonough, C. A., Li, W., Bischel, H. N., Silva, A. O. D., & DeWitt, J. C. (2022) · Environmental Science & Technology · doi:10.1021/acs.est.2c00254 · Cited by 88
Recent developments in trace analysis of poly- and perfluoroalkyl substances
Berger, U., Kaiser, M. A., Kärrman, A., Barber, J. L., & van Leeuwen, S. P. J. (2011) · Analytical and Bioanalytical Chemistry · doi:10.1007/s00216-011-4823-8 · Cited by 87
“The role of neutral precursor PFASs in bioaccumulation and human exposure is a controversial issue that is currently debated [41].”
BackgroundDassuncao, C., Hu, X. C., Zhang, X., Bossi, R., Dam, M., Mikkelsen, B., & Sunderland, E. M. (2017) · Environmental Science & Technology · doi:10.1021/acs.est.7b00293 · Cited by 90
Greaves, A. K., Letcher, R. J., Sonne, C., & Dietz, R. (2013) · Environmental Toxicology and Chemistry · doi:10.1002/etc.2107 · Cited by 86
“Perfluorooctane sulfonamide (FOSA) is the most commonly detected precursor that is degraded to PFOS [33].”
BackgroundMyers, A. L., Crozier, P. W., Helm, P. A., Brimacombe, C., Furdui, V. I., Reiner, E. J., Burniston, D., & Marvin, C. H. (2012) · Environment International · doi:10.1016/j.envint.2012.02.002 · Cited by 87
Detection of fluorotelomer alcohols in indoor environments and their relevance for human exposure
Schlummer, M., Gruber, L., Fiedler, D., Kizlauskas, M., & Müller, J. (2013) · Environment International · doi:10.1016/j.envint.2013.03.010 · Cited by 89
Robuck, A. R., Cantwell, M. G., McCord, J. P., Addison, L. M., Pfohl, M., Strynar, M. J., McKinney, R. A., Katz, D. R., Wiley, D. N., & Lohmann, R. (2020) · Environmental Science & Technology · doi:10.1021/acs.est.0c01951 · Cited by 85
Riverine inputs and source tracing of perfluoroalkyl substances (PFASs) in Taihu Lake, China
Ma, X., Shan, G., Chen, M., Zhao, J., & Zhu, L. Y. (2017) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2017.08.235 · Cited by 80
Jia, X., Li, X., Zhou, L., Hui, Y., Li, W., Cai, Y., & Shi, Y. (2023) · Environmental Science & Technology · doi:10.1021/acs.est.2c08995 · Cited by 80
Liu, Y., Li, A., Buchanan, S. N., & Liu, W. (2020) · Environment International · doi:10.1016/j.envint.2020.106012 · Cited by 82
Gewurtz, S. B., Backus, S. M., Silva, A. O. D., Ahrens, L., Armellin, A., Evans, M. S., Fraser, S., Gledhill, M., Guerra, P., Harner, T., et al. (2013) · Environment International · doi:10.1016/j.envint.2013.05.008 · Cited by 80
“…Harbour, Toronto Harbour, Lake Ontario, and the St. Lawrence River, the PFAA profile was similar and typical of abiotic and food web studies e.g., (Ahrens et al., 2010; Furdui et al., 2008a; Kelly et al., 2009; Kwadijk et al., 2010; Labadie and Chevreuil, 2011; Martin et al., 2003a, 2003b, 2004).”
MethodLetcher, R. J., Chu, S., McKinney, M. A., Tomy, G. T., Sonne, C., & Dietz, R. (2014) · Chemosphere · doi:10.1016/j.chemosphere.2014.04.022 · Cited by 76
“In particular, the degradation of PFOS precursors (or ‘‘PreFOS’’) is largely unknown, which refers to the complexity of fluorinated precursors that can degrade and give rise to PFOS in exposed biota (Parsons et al., 2008; Martin et al., 2010; Liu and Avendaño, 2013; Wang et al., 2013).”
BackgroundMethodResultSun, Y., Angelotti, B., Brooks, M., Dowbiggin, B., Evans, P. J., Devins, B., & Wang, Z.-W. (2018) · Chemosphere · doi:10.1016/j.chemosphere.2018.06.162 · Cited by 76
Metadata
- Authors
- Martin, J. W., Asher, B. J., Beesoon, S., Benskin, J. P., & Ross, M. S.
- Affiliations
- University of Alberta (CA)
- Corresponding author
- Martin, Jonathan W.
- Venue
- Journal of Environmental Monitoring
- Publisher
- Royal Society of Chemistry (RSC)
- Published
- 2010
- Volume
- 12
- Issue
- 11
- Pages
- 1979
- ISSN
- 1464-0325 (ISSN-L)
- 1464-0333
- OpenAlex
- W2088093177
- Cited by
- 311
- References
- 169
- Citations by year
- 2026: 21 · 2025: 21 · 2024: 18 · 2023: 22 · 2022: 24 · 2021: 19 · 2020: 21 · 2019: 9 · 2018: 22 · 2017: 17 · 2016: 10 · 2015: 19 · 2014: 23 · 2013: 19 · 2012: 27
- FWCI
- 2.61
- Type
- journal article
- Language
- en
- Open access
- closed
- Locations
- Journal of Environmental Monitoring (publishedVersion)
- PubMed (publishedVersion)
- Topics
- Physical Sciences › Environmental Science › Environmental Chemistry › Per- and polyfluoroalkyl substances research
- Physical Sciences › Environmental Science › Health, Toxicology and Mutagenesis › Toxic Organic Pollutants Impact
- Physical Sciences › Chemistry › Organic Chemistry › Fluorine in Organic Chemistry
- Keywords
- PFOS, human exposure, environmental exposure, serum biomonitoring, body burden, source tracking, whales, abiotic degradation, temporal trends
- MeSH terms
- Animals, Biotransformation, Environmental Exposure, Environmental Monitoring, Environmental Pollutants, Fluorocarbons, Food Analysis, Humans, Alkanesulfonic Acids
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