PFAS levels and determinants of variability in exposure in European teenagers - Results from the HBM4EU aligned studies (2014-2021).


Journal

International journal of hygiene and environmental health
ISSN: 1618-131X
Titre abrégé: Int J Hyg Environ Health
Pays: Germany
ID NLM: 100898843

Informations de publication

Date de publication:
01 2023
Historique:
received: 08 07 2022
revised: 14 09 2022
accepted: 21 10 2022
pubmed: 4 11 2022
medline: 7 12 2022
entrez: 3 11 2022
Statut: ppublish

Résumé

Perfluoroalkyl substances (PFAS) are man-made fluorinated chemicals, widely used in various types of consumer products, resulting in their omnipresence in human populations. The aim of this study was to describe current PFAS levels in European teenagers and to investigate the determinants of serum/plasma concentrations in this specific age group. PFAS concentrations were determined in serum or plasma samples from 1957 teenagers (12-18 years) from 9 European countries as part of the HBM4EU aligned studies (2014-2021). Questionnaire data were post-harmonized by each study and quality checked centrally. Only PFAS with an overall quantification frequency of at least 60% (PFOS, PFOA, PFHxS and PFNA) were included in the analyses. Sociodemographic and lifestyle factors were analysed together with food consumption frequencies to identify determinants of PFAS exposure. The variables study, sex and the highest educational level of household were included as fixed factors in the multivariable linear regression models for all PFAS and each dietary variable was added to the fixed model one by one and for each PFAS separately. The European exposure values for PFAS were reported as geometric means with 95% confidence intervals (CI): PFOS [2.13 μg/L (1.63-2.78)], PFOA ([0.97 μg/L (0.75-1.26)]), PFNA [0.30 μg/L (0.19-0.45)] and PFHxS [0.41 μg/L (0.33-0.52)]. The estimated geometric mean exposure levels were significantly higher in the North and West versus the South and East of Europe. Boys had significantly higher concentrations of the four PFAS compared to girls and significantly higher PFASs concentrations were found in teenagers from households with a higher education level. Consumption of seafood and fish at least 2 times per week was significantly associated with 21% (95% CI: 12-31%) increase in PFOS concentrations and 20% (95% CI: 10-31%) increase in PFNA concentrations as compared to less frequent consumption of seafood and fish. The same trend was observed for PFOA and PFHxS but not statistically significant. Consumption of eggs at least 2 times per week was associated with 11% (95% CI: 2-22%) and 14% (95% CI: 2-27%) increase in PFOS and PFNA concentrations, respectively, as compared to less frequent consumption of eggs. Significantly higher PFOS concentrations were observed for participants consuming offal (14% (95% CI: 3-26%)), the same trend was observed for the other PFAS but not statistically significant. Local food consumption at least 2 times per week was associated with 40% (95% CI: 19-64%) increase in PFOS levels as compared to those consuming local food less frequently. This work provides information about current levels of PFAS in European teenagers and potential dietary sources of exposure to PFAS in European teenagers. These results can be of use for targeted monitoring of PFAS in food.

Sections du résumé

BACKGROUND
Perfluoroalkyl substances (PFAS) are man-made fluorinated chemicals, widely used in various types of consumer products, resulting in their omnipresence in human populations. The aim of this study was to describe current PFAS levels in European teenagers and to investigate the determinants of serum/plasma concentrations in this specific age group.
METHODS
PFAS concentrations were determined in serum or plasma samples from 1957 teenagers (12-18 years) from 9 European countries as part of the HBM4EU aligned studies (2014-2021). Questionnaire data were post-harmonized by each study and quality checked centrally. Only PFAS with an overall quantification frequency of at least 60% (PFOS, PFOA, PFHxS and PFNA) were included in the analyses. Sociodemographic and lifestyle factors were analysed together with food consumption frequencies to identify determinants of PFAS exposure. The variables study, sex and the highest educational level of household were included as fixed factors in the multivariable linear regression models for all PFAS and each dietary variable was added to the fixed model one by one and for each PFAS separately.
RESULTS
The European exposure values for PFAS were reported as geometric means with 95% confidence intervals (CI): PFOS [2.13 μg/L (1.63-2.78)], PFOA ([0.97 μg/L (0.75-1.26)]), PFNA [0.30 μg/L (0.19-0.45)] and PFHxS [0.41 μg/L (0.33-0.52)]. The estimated geometric mean exposure levels were significantly higher in the North and West versus the South and East of Europe. Boys had significantly higher concentrations of the four PFAS compared to girls and significantly higher PFASs concentrations were found in teenagers from households with a higher education level. Consumption of seafood and fish at least 2 times per week was significantly associated with 21% (95% CI: 12-31%) increase in PFOS concentrations and 20% (95% CI: 10-31%) increase in PFNA concentrations as compared to less frequent consumption of seafood and fish. The same trend was observed for PFOA and PFHxS but not statistically significant. Consumption of eggs at least 2 times per week was associated with 11% (95% CI: 2-22%) and 14% (95% CI: 2-27%) increase in PFOS and PFNA concentrations, respectively, as compared to less frequent consumption of eggs. Significantly higher PFOS concentrations were observed for participants consuming offal (14% (95% CI: 3-26%)), the same trend was observed for the other PFAS but not statistically significant. Local food consumption at least 2 times per week was associated with 40% (95% CI: 19-64%) increase in PFOS levels as compared to those consuming local food less frequently.
CONCLUSION
This work provides information about current levels of PFAS in European teenagers and potential dietary sources of exposure to PFAS in European teenagers. These results can be of use for targeted monitoring of PFAS in food.

Identifiants

pubmed: 36327670
pii: S1438-4639(22)00140-7
doi: 10.1016/j.ijheh.2022.114057
pmc: PMC9758614
pii:
doi:

Substances chimiques

Fluorocarbons 0
Alkanesulfonic Acids 0
Environmental Pollutants 0

Types de publication

Journal Article Review Research Support, Non-U.S. Gov't

Langues

eng

Sous-ensembles de citation

IM

Pagination

114057

Informations de copyright

Copyright © 2022 The Authors. Published by Elsevier GmbH.. All rights reserved.

Références

Chemosphere. 2020 Mar;242:125250
pubmed: 31896205
EFSA J. 2020 Sep 17;18(9):e06223
pubmed: 32994824
Environ Health Perspect. 2004 Dec;112(17):1691-6
pubmed: 15579415
Environ Res. 2019 Feb;169:114-121
pubmed: 30447498
Int J Hyg Environ Health. 2021 May;234:113740
pubmed: 33774419
Environ Int. 2014 Aug;69:58-66
pubmed: 24815340
Environ Res. 2021 Apr;195:110740
pubmed: 33460636
Int J Hyg Environ Health. 2021 Aug;237:113809
pubmed: 34455198
Environ Int. 2010 Oct;36(7):772-8
pubmed: 20579735
Sci Total Environ. 2020 Sep 1;733:139186
pubmed: 32474294
Environ Int. 2021 Feb;147:106340
pubmed: 33422968
Environ Sci Technol. 2015 Oct 6;49(19):11849-58
pubmed: 26333069
J Hazard Mater. 2021 Jun 15;412:125159
pubmed: 33951855
Food Nutr Res. 2018 Aug 28;62:
pubmed: 30186087
Environ Sci Pollut Res Int. 2013 Feb;20(2):1193-202
pubmed: 23184128
Int J Hyg Environ Health. 2016 Nov;219(8):867-875
pubmed: 27451073
Int J Hyg Environ Health. 2021 Aug;237:113821
pubmed: 34375847
Int J Environ Res Public Health. 2022 Jun 01;19(11):
pubmed: 35682369
Int J Hyg Environ Health. 2017 Mar;220(2 Pt A):152-166
pubmed: 27914867
Environ Sci Technol. 2018 Mar 20;52(6):3738-3747
pubmed: 29516726
Int J Hyg Environ Health. 2015 Jul;218(5):437-43
pubmed: 25921520
Int J Environ Res Public Health. 2021 Dec 07;18(24):
pubmed: 34948492
Environ Sci Technol. 2014 Aug 19;48(16):9600-8
pubmed: 25026485
Chemosphere. 2017 Mar;171:617-624
pubmed: 28056448
Int J Hyg Environ Health. 2022 May;242:113972
pubmed: 35453051
Int J Hyg Environ Health. 2017 Mar;220(2 Pt A):94-97
pubmed: 28284775
Environ Int. 2015 Nov;84:71-81
pubmed: 26232143
Environ Health Perspect. 2007 Nov;115(11):1596-602
pubmed: 18007991
Environ Int. 2011 Oct;37(7):1206-12
pubmed: 21620474
Sci Total Environ. 2022 Nov 15;847:157481
pubmed: 35868372
Int J Epidemiol. 2016 Apr;45(2):382-8
pubmed: 27063603
Environ Int. 2016 Jul-Aug;92-93:357-65
pubmed: 27132161
Int J Hyg Environ Health. 2017 Mar;220(2 Pt A):36-45
pubmed: 28160993
Environ Res. 2007 Feb;103(2):176-84
pubmed: 16893538
PLoS One. 2018 Dec 31;13(12):e0209255
pubmed: 30596681
Int J Hyg Environ Health. 2014 Jan;217(1):52-61
pubmed: 23601780
Environ Int. 2018 Oct;119:165-173
pubmed: 29958117
Environ Int. 2018 Dec;121(Pt 2):1304-1310
pubmed: 30420127
Chemosphere. 2015 Jun;129:203-9
pubmed: 25147004
Environ Int. 2020 Oct;143:105985
pubmed: 32731096
Environ Pollut. 2022 Aug 15;307:119478
pubmed: 35588958

Auteurs

D Richterová (D)

Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia.

E Govarts (E)

VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium.

L Fábelová (L)

Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia.

K Rausová (K)

Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia.

L Rodriguez Martin (L)

VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium.

L Gilles (L)

VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium.

S Remy (S)

VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium.

A Colles (A)

VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium.

L Rambaud (L)

Department of Environmental and Occupational Health, Santé Publique France, Saint-Maurice, France.

M Riou (M)

Department of Environmental and Occupational Health, Santé Publique France, Saint-Maurice, France.

C Gabriel (C)

Environmental Engineering Laboratory, Department of Chemical Engineering, Aristotle University of Thessaloniki, Thessaloniki, Greece; HERACLES Research Center on the Exposome and Health, Center for Interdisciplinary Research and Innovation, Balkan Center, Greece.

D Sarigiannis (D)

Environmental Engineering Laboratory, Department of Chemical Engineering, Aristotle University of Thessaloniki, Thessaloniki, Greece; HERACLES Research Center on the Exposome and Health, Center for Interdisciplinary Research and Innovation, Balkan Center, Greece; Environmental Health Engineering, Institute of Advanced Study, Pavia, Italy.

S Pedraza-Diaz (S)

National Centre for Environmental Health, Instituto de Salud Carlos III (ISCIII), Madrid, Spain.

J J Ramos (JJ)

National Centre for Environmental Health, Instituto de Salud Carlos III (ISCIII), Madrid, Spain.

T Kosjek (T)

Jožef Stefan Institute, Department of Environmental Sciences, Ljubljana, Slovenia.

J Snoj Tratnik (J)

Jožef Stefan Institute, Department of Environmental Sciences, Ljubljana, Slovenia.

S Lignell (S)

Swedish Food Agency, Uppsala, Sweden.

I Gyllenhammar (I)

Swedish Food Agency, Uppsala, Sweden.

C Thomsen (C)

Norwegian Institute of Public Health, Oslo, Norway.

L S Haug (LS)

Norwegian Institute of Public Health, Oslo, Norway.

M Kolossa-Gehring (M)

German Environment Agency (UBA), GerES V-sub, Germany.

N Vogel (N)

German Environment Agency (UBA), GerES V-sub, Germany.

C Franken (C)

Provincial Institute for Hygiene, Antwerp, Belgium.

N Vanlarebeke (N)

Provincial Institute for Hygiene, Antwerp, Belgium.

L Bruckers (L)

BioStat, Data Science Institute, Hasselt University, Martelarenlaan 42, 3500, Hasselt, Belgium.

L Stewart (L)

Public Health England, Chilton, United Kingdom.

O Sepai (O)

Public Health England, Chilton, United Kingdom.

G Schoeters (G)

VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium.

M Uhl (M)

Umweltbundesamt, Vienna, Austria.

A Castaño (A)

National Centre for Environmental Health, Instituto de Salud Carlos III (ISCIII), Madrid, Spain.

M Esteban López (M)

National Centre for Environmental Health, Instituto de Salud Carlos III (ISCIII), Madrid, Spain.

T Göen (T)

Institute and Outpatient Clinic of Occupational, Social and Environmental Medicine, Friedrich-Alexander-Universität Erlangen-Nürnberg, Erlangen, Germany.

Ľ Palkovičová Murínová (Ľ)

Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia. Electronic address: lubica.murinova@szu.sk.

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