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Estimating Consumer Exposure to PFOS and PFOA
Abstract
Perfluorinated compounds have been used for more than 50 years as process aids, surfactants, and for surface protection. This study is a comprehensive assessment of consumer exposure to perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA) from a variety of environmental and product-related sources. To identify relevant pathways leading to consumer exposure to PFOS and PFOA a scenario-based approach has been applied. Scenarios represent realistic situations where age- and gender-specific exposure occurs in the everyday life of consumers. We find that North American and European consumers are likely to experience ubiquitous and long-term uptake doses of PFOS and PFOA in the range of 3 to 220 ng per kg body weight per day (ng/kg(bw)/day) and 1 to 130 ng/kg(bw)/day, respectively. The greatest portion of the chronic exposure to PFOS and PFOA is likely to result from the intake of contaminated foods, including drinking water. Consumer products cause a minor portion of the consumer exposure to PFOS and PFOA. Of these, it is mainly impregnation sprays, treated carpets in homes, and coated food contact materials that may lead to consumer exposure to PFOS and PFOA. Children tend to experience higher total uptake doses (on a body weight basis) than teenagers and adults because of higher relative uptake via food consumption and hand-to-mouth transfer of chemical from treated carpets and ingestion of dust. The uptake estimates based on scenarios are within the range of values derived from blood serum data by applying a one-compartment pharmacokinetic model.
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“Thus, the homologue pattern of PFASs in cosmetics appear to follow the same trend as treated textiles and papers where recent studies typically report the highest concentrations and detection frequency for C6 compounds.”
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Gu, Z., Cheng, J., Zhang, M., He, J., & Ni, P. (2017) · Polymer · doi:10.1016/j.polymer.2017.02.073 · Cited by 30
PBDE exposure from food in Ireland: optimising data exploitation in probabilistic exposure modelling
Trudel, D., Tlustoš, P., Goetz, N. V., Scheringer, M., & Hungerbühler, K. (2010) · Journal of Exposure Science & Environmental Epidemiology · doi:10.1038/jes.2010.41 · Cited by 30
Self-citationHusøy, T., Caspersen, I. H., Thépaut, É., Knutsen, H. K., Haug, L. S., Andreassen, M., Gkrillas, A., Lindeman, B., Thomsen, C., Herzke, D., et al. (2023) · Environmental Research · doi:10.1016/j.envres.2023.117341 · Cited by 31
Sánchez‐Resino, E., Marquès, M., Gutiérrez-Martín, D., Restrepo-Montes, E., Martínez, M. Á., Salas‐Huetos, A., Babió, N., Salas‐Salvadó, J., Gil‐Solsona, R., & Gago-Ferrero, P. (2023) · Environmental Science & Technology · doi:10.1021/acs.est.3c04347 · Cited by 28
“68,69,70 In fact, drinking water health advisory limit have changed from 70 ng/L (combining both PFOS and PFOA) in 2016 to 0.004 and 0.02 ng/L for PFOA and PFOS, respectively, in 2022.”
BackgroundInfluentialLee, J., Lee, S., Baek, M., Lee, B., Lee, H., Kwon, T. K., Park, P., Shin, T., Khang, D., & Kim, S. (2016) · Journal of Applied Toxicology · doi:10.1002/jat.3389 · Cited by 29
“Because the primary means of PFOA exposure had been demonstrated as ingestion of agent-contaminated food and/or water (Trudel et al., 2008), the main purpose of the present study was whether to ascertain if oral exposure to PFOA augmented mast cell-mediated allergic inflammation with IgE activation.”
Perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA)
Viberg, H., & Eriksson, P. O. (2011) · Elsevier eBooks · doi:10.1016/b978-0-12-382032-7.10047-5 · Cited by 32
Perfluoroalkyl substances exposure and hearing impairment in US adults
Ding, N., & Park, S. K. (2020) · Environmental Research · doi:10.1016/j.envres.2020.109686 · Cited by 28
“PFAS are ubiquitous environmental toxicants to which humans are exposed on a daily basis (Trudel et al., 2008).”
BackgroundPer- and polyfluorinated substances in the Nordic Countries
Posner, S., Roos, S., Poulsen, P. B., Jörundsdóttir, H. Ó., Gunnlaugsdóttir, H., Trier, X., Jensen, A. A., Katsogiannis, A. A., Herzke, D., Bonefeld‐Jørgensen, E. C., et al. (2013) · doi:10.6027/tn2013-542 · Cited by 31
“The uptake of PFOS in children on a body weight basis tend to be higher because of a higher relative uptake from food and hand- mouth transfer from treated carpets and ingestion of dust (Trudel et al., 2008).”
BackgroundInfluentialThe Dilemma of perfluorooctanoate (PFOA) human half-life
Dourson, M., & Gadagbui, B. (2021) · Regulatory Toxicology and Pharmacology · doi:10.1016/j.yrtph.2021.105025 · Cited by 27
Mitro, S. D., Liu, J., Jaacks, L. M., Fleisch, A. F., Williams, P. L., Knowler, W. C., Laferrère, B., Perng, W., Bray, G. A., Wallia, A., et al. (2020) · International Journal of Hygiene and Environmental Health · doi:10.1016/j.ijheh.2020.113680 · Cited by 27
Wang, M., Li, Q., Hou, M., Chan, L., Liu, M., Ter, S. K., Dong, T., Xia, Y. F., Chotirmall, S. H., & Fang, M. (2021) · Proceedings of the National Academy of Sciences · doi:10.1073/pnas.2011957118 · Cited by 27
“Children may have greater risk of exposure than teenagers and adults (20, 21), possibly because PFCs are transferred through the placenta (22) and have postnatal sources of exposure including human milk and house dust (23).”
BackgroundEast, A. W., Egeghy, P. P., Hubal, E. A. C., Slover, R., & Vallero, D. A. (2021) · Journal of Exposure Science & Environmental Epidemiology · doi:10.1038/s41370-021-00374-w · Cited by 28
Zhang, J., Liang, J., Zhu, H., Li, C., & Wu, Q. (2011) · Environmental Toxicology · doi:10.1002/tox.20723 · Cited by 27
“Moreover, some reports have suggested that young people tend to experience higher uptake doses, through hand-tomouth transfer, than do adults (Trudel et al., 2008).”
BackgroundThe effect of PFAS exposure on glucolipid metabolism in children and adolescents: a meta-analysis
Zheng, Q., Yan, W., Gao, S., & Li, X. (2024) · Frontiers in Endocrinology · doi:10.3389/fendo.2024.1261008 · Cited by 26
Forthun, I. H., Roelants, M., Haug, L. S., Knutsen, H. K., Schell, L. M., Jugessur, A., Bjerknes, R., Sabaredzovic, A., Bruserud, I. S., & Juliusson, P. B. (2023) · International Journal of Hygiene and Environmental Health · doi:10.1016/j.ijheh.2023.114199 · Cited by 26
Additives in the Textile Industry
Roman, R. M. D., Dan, J. R. G., Casal, J., Àgueda, A., Capri, E., Fait, G., Schuhmacher, M., Nadal, M., Rovira, J., Grundmann, V., et al. (2011) · The handbook of environmental chemistry · doi:10.1007/698_2011_101 · Cited by 26
Hu, X. Y., Li, S., Cirillo, P. M., Krigbaum, N. Y., Tran, V., Jones, D. P., & Cohn, B. A. (2020) · Reproductive Toxicology · doi:10.1016/j.reprotox.2020.01.001 · Cited by 27
Gallocchio, F., Moressa, A., Zonta, G., Angeletti, R., & Lega, F. (2022) · Molecules · doi:10.3390/molecules27227899 · Cited by 26
“Dietary intake is considered as one of the main pathways for human exposure to PFASs, with food of animal origin being a primary source of exposure [4,13,14].”
BackgroundCharacterization of age-based trends to identify chemical biomarkers of higher levels in children
Nguyen, V. K., Colacino, J. A., Arnot, J. A., Kvasnicka, J., & Jolliet, O. (2018) · Environment International · doi:10.1016/j.envint.2018.10.042 · Cited by 25
“The exposure patterns of other PFASs from treated consumer products (Trudel et al. 2008), water (Gyllenhammar et al.”
BackgroundEmbryonic exposure to PFAS causes long-term, compound-specific behavioral alterations in zebrafish
Hawkey, A. B., Mead, M., Natarajan, S., Gondal, A., Jarrett, O., & Levin, E. D. (2023) · Neurotoxicology and Teratology · doi:10.1016/j.ntt.2023.107165 · Cited by 25
Emerging Per- and Polyfluoroalkyl Substances in Tap Water from the American Healthy Homes Survey II
Boettger, J. D., DeLuca, N. M., Zurek-Ost, M. A., Miller, K. E., Fuller, C., Bradham, K. D., Ashley, P., Friedman, W., Pinzer, E. A., Cox, D. C., et al. (2025) · Environmental Science & Technology · doi:10.1021/acs.est.4c08037 · Cited by 30
PFAS Biomonitoring in Higher Exposed Populations
Olsen, G. W. (2015) · Molecular and integrative toxicology · doi:10.1007/978-3-319-15518-0_4 · Cited by 23
Aghaei, Z., Steeves, K. L., Jobst, K. J., & Cahill, L. S. (2021) · Biology of Reproduction · doi:10.1093/biolre/ioab223 · Cited by 25
Wilhelm, M., Wittsiepe, J., Völkel, W., Fromme, H., & Kasper-Sonnenberg, M. (2015) · International Journal of Hygiene and Environmental Health · doi:10.1016/j.ijheh.2015.07.001 · Cited by 24
Cousins, E. M., Richter, L., Cordner, A., Brown, P., & Diallo, S. (2019) · NEW SOLUTIONS A Journal of Environmental and Occupational Health Policy · doi:10.1177/1048291119852674 · Cited by 27
Effects of Per- and Polyfluoroalkylated Substances on Female Reproduction
González-Alvarez, M. E., Antwi-Boasiako, C., & Keating, A. F. (2024) · Toxics · doi:10.3390/toxics12070455 · Cited by 26
Xu, J., Wang, Q., Jiao, X., Kong, P., Chen, S., Yang, W., Liu, W., Li, K., Teng, X., & Guo, Y. (2025) · Environmental Health Perspectives · doi:10.1289/ehp15422 · Cited by 23
Fujii, Y., Harada, K. H., Haraguchi, K., & Koizumi, A. (2017) · Chemosphere · doi:10.1016/j.chemosphere.2017.02.073 · Cited by 23
Endocrine-Disrupting Chemicals: Introduction to the Theme
Lisco, G., Giagulli, V. A., Iovino, M., Guastamacchia, E., Pergola, G. D., & Triggiani, V. (2021) · Endocrine Metabolic & Immune Disorders - Drug Targets · doi:10.2174/1871530321666210413124425 · Cited by 23
Metadata
- Authors
- Trudel, D., Horowitz, L., Wormuth, M., Scheringer, M., Cousins, I. T., & Hungerbühler, K.
- Affiliations
- ETH Zurich (CH)
- Stockholm University (SE)
- Corresponding author
- Scheringer, Martin
- Venue
- Risk Analysis
- Publisher
- Wiley
- Published
- 2008-04
- Volume
- 28
- Issue
- 2
- Pages
- 251-269
- ISSN
- 0272-4332 (ISSN-L)
- 1539-6924
- OpenAlex
- W2038447616
- Cited by
- 514
- References
- 79
- Citations by year
- 2026: 24 · 2025: 32 · 2024: 40 · 2023: 30 · 2022: 36 · 2021: 38 · 2020: 31 · 2019: 29 · 2018: 26 · 2017: 25 · 2016: 21 · 2015: 21 · 2014: 24 · 2013: 24 · 2012: 23
- FWCI
- 21.90
- Type
- journal article
- Language
- en
- Open access
- closed
- Locations
- Risk Analysis (publishedVersion)
- PubMed (publishedVersion)
- Funders
- Bundesamt für Gesundheit
- Health Canada
- 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 › Environmental Science › Water Science and Technology › Fluoride Effects and Removal
- Keywords
- PFOS, perfluorooctanoic acid, perfluorinated compounds, consumer exposure, exposure assessment, food contamination, drinking water contamination, consumer goods, food contact materials, children's exposure, dust ingestion, one-compartment model
- MeSH terms
- Adolescent, Adult, Caprylates, Child, Child, Preschool, Dust, Environmental Exposure, Environmental Monitoring, Environmental Pollutants, Female, Fluorocarbons, Humans, Infant, Male, Water Pollutants, Chemical, Air Pollution, Indoor, Alkanesulfonic Acids
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