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Fábelová L, Beneito A, Casas M, Colles A, Dalsager L, Den Hond E, Dereumeaux C, Ferguson K, Gilles L, Govarts E, Irizar A, Lopez Espinosa MJ, Montazeri P, Morrens B, Patayová H, Rausová K, Richterová D, Rodriguez Martin L, Santa-Marina L, Schettgen T, Schoeters G, Haug LS, Uhl M, Villanger GD, Vrijheid M, Zaros C, Palkovičová Murínová Ľ. PFAS levels and exposure determinants in sensitive population groups. Chemosphere 2023; 313:137530. [PMID: 36509187 PMCID: PMC9846180 DOI: 10.1016/j.chemosphere.2022.137530] [Citation(s) in RCA: 1] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 07/15/2022] [Revised: 11/25/2022] [Accepted: 12/09/2022] [Indexed: 05/25/2023]
Abstract
BACKGROUND Per- and polyfluoroalkyl substances (PFAS) are persistent organic pollutants. The first exposure to PFAS occurs in utero, after birth it continues via breast milk, food intake, environment, and consumer products that contain these chemicals. Our aim was to identify determinants of PFAS concentrations in sensitive population subgroups- pregnant women and newborns. METHODS Nine European birth cohorts provided exposure data on PFAS in pregnant women (INMA-Gipuzkoa, Sabadell, Valencia, ELFE and MoBa; total N = 5897) or newborns (3xG study, FLEHS 2, FLEHS 3 and PRENATAL; total N = 940). PFOS, PFOA, PFHxS and PFNA concentrations were measured in maternal or cord blood, depending on the cohort (FLEHS 2 measured only PFOS and PFOA). PFAS concentrations were analysed according to maternal characteristics (age, BMI, parity, previous breastfeeding, smoking, and food consumption during pregnancy) and parental educational level. The association between potential determinants and PFAS concentrations was evaluated using multiple linear regression models. RESULTS We observed significant variations in PFAS concentrations among cohorts. Higher PFAS concentrations were associated with higher maternal age, primipara birth, and educational level, both for maternal blood and cord blood. Higher PFAS concentrations in maternal blood were associated with higher consumption of fish and seafood, meat, offal and eggs. In cord blood, higher PFHxS concentrations were associated with daily meat consumption and higher PFNA with offal consumption. Daily milk and dairy consumption were associated with lower concentrations of PFAS in both, pregnant women and newborns. CONCLUSION High detection rates of the four most abundant PFAS demonstrate ubiquitous exposure of sensitive populations, which is of concern. This study identified several determinants of PFAS exposure in pregnant women and newborns, including dietary factors, and these findings can be used for proposing measures to reduce PFAS exposure, particularly from dietary sources.
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Affiliation(s)
- L Fábelová
- Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia
| | - A Beneito
- Epidemiology and Environmental Health Joint Research Unit, FISABIO-Universitat Jaume I-Universitat de València, Valencia, Spain
| | - M Casas
- ISGlobal, Barcelona, Spain; Universitat Pompeu Fabra (UPF), Barcelona, Spain; Spanish Consortium for Research on Epidemiology and Public Health (CIBERESP), Instituto de Salud Carlos III, C/Monforte de Lemos 3-5 28029 Madrid, Spain
| | - A Colles
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - L Dalsager
- Institute of Public Health, University of Southern Denmark, Odense, Denmark
| | - E Den Hond
- Provincial Institute of Hygiene (PIH), Antwerp, Belgium
| | | | - K Ferguson
- National Institute of Environmental Health Sciences (NIEHS), North Carolina, USA
| | - L Gilles
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - E Govarts
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - A Irizar
- Spanish Consortium for Research on Epidemiology and Public Health (CIBERESP), Instituto de Salud Carlos III, C/Monforte de Lemos 3-5 28029 Madrid, Spain; Biodonostia, Epidemiology and Public Health Area, Environmental Epidemiology and Child Development Group, 20014 San Sebastian, Spain
| | - M J Lopez Espinosa
- Epidemiology and Environmental Health Joint Research Unit, FISABIO-Universitat Jaume I-Universitat de València, Valencia, Spain; Spanish Consortium for Research on Epidemiology and Public Health (CIBERESP), Instituto de Salud Carlos III, C/Monforte de Lemos 3-5 28029 Madrid, Spain; Faculty of Nursing and Chiropody, Universitat de València, Valencia, Spain
| | | | - B Morrens
- Faculty of Social Sciences, University of Antwerp, Belgium
| | - H Patayová
- Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia
| | - K Rausová
- Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia
| | - D Richterová
- Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia
| | - L Rodriguez Martin
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - L Santa-Marina
- Spanish Consortium for Research on Epidemiology and Public Health (CIBERESP), Instituto de Salud Carlos III, C/Monforte de Lemos 3-5 28029 Madrid, Spain; Biodonostia, Epidemiology and Public Health Area, Environmental Epidemiology and Child Development Group, 20014 San Sebastian, Spain; Public Health Division of Gipuzkoa, Basque Government, 20013 San Sebastian, Spain
| | - T Schettgen
- Institute for Occupational, Social and Environmental Medicine, RWTH Aachen University, Aachen, Germany
| | - G Schoeters
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - L S Haug
- Norwegian Institute of Public Health (NIPH), Oslo, Norway
| | - M Uhl
- Umweltbundesamt, Vienna, Austria
| | - G D Villanger
- Norwegian Institute of Public Health (NIPH), Oslo, Norway
| | - M Vrijheid
- ISGlobal, Barcelona, Spain; Universitat Pompeu Fabra (UPF), Barcelona, Spain; Spanish Consortium for Research on Epidemiology and Public Health (CIBERESP), Instituto de Salud Carlos III, C/Monforte de Lemos 3-5 28029 Madrid, Spain
| | - C Zaros
- Institut national d'études démographiques (INED), Aubervilliers, France
| | - Ľ Palkovičová Murínová
- Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia.
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Richterová D, Govarts E, Fábelová L, Rausová K, Rodriguez Martin L, Gilles L, Remy S, Colles A, Rambaud L, Riou M, Gabriel C, Sarigiannis D, Pedraza-Diaz S, Ramos JJ, Kosjek T, Snoj Tratnik J, Lignell S, Gyllenhammar I, Thomsen C, Haug LS, Kolossa-Gehring M, Vogel N, Franken C, Vanlarebeke N, Bruckers L, Stewart L, Sepai O, Schoeters G, Uhl M, Castaño A, Esteban López M, Göen T, Palkovičová Murínová Ľ. PFAS levels and determinants of variability in exposure in European teenagers - Results from the HBM4EU aligned studies (2014-2021). Int J Hyg Environ Health 2023; 247:114057. [PMID: 36327670 PMCID: PMC9758614 DOI: 10.1016/j.ijheh.2022.114057] [Citation(s) in RCA: 15] [Impact Index Per Article: 15.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 07/08/2022] [Revised: 09/14/2022] [Accepted: 10/21/2022] [Indexed: 11/05/2022]
Abstract
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.
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Affiliation(s)
- D Richterová
- Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia
| | - E Govarts
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - L Fábelová
- Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia
| | - K Rausová
- Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia
| | - L Rodriguez Martin
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - L Gilles
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - S Remy
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - A Colles
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - L Rambaud
- Department of Environmental and Occupational Health, Santé Publique France, Saint-Maurice, France
| | - M Riou
- Department of Environmental and Occupational Health, Santé Publique France, Saint-Maurice, France
| | - C Gabriel
- 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
- 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
- National Centre for Environmental Health, Instituto de Salud Carlos III (ISCIII), Madrid, Spain
| | - J J Ramos
- National Centre for Environmental Health, Instituto de Salud Carlos III (ISCIII), Madrid, Spain
| | - T Kosjek
- Jožef Stefan Institute, Department of Environmental Sciences, Ljubljana, Slovenia
| | - J Snoj Tratnik
- Jožef Stefan Institute, Department of Environmental Sciences, Ljubljana, Slovenia
| | - S Lignell
- Swedish Food Agency, Uppsala, Sweden
| | | | - C Thomsen
- Norwegian Institute of Public Health, Oslo, Norway
| | - L S Haug
- Norwegian Institute of Public Health, Oslo, Norway
| | | | - N Vogel
- German Environment Agency (UBA), GerES V-sub, Germany
| | - C Franken
- Provincial Institute for Hygiene, Antwerp, Belgium
| | | | - L Bruckers
- BioStat, Data Science Institute, Hasselt University, Martelarenlaan 42, 3500, Hasselt, Belgium
| | - L Stewart
- Public Health England, Chilton, United Kingdom
| | - O Sepai
- Public Health England, Chilton, United Kingdom
| | - G Schoeters
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - M Uhl
- Umweltbundesamt, Vienna, Austria
| | - A Castaño
- National Centre for Environmental Health, Instituto de Salud Carlos III (ISCIII), Madrid, Spain
| | - M Esteban López
- National Centre for Environmental Health, Instituto de Salud Carlos III (ISCIII), Madrid, Spain
| | - T Göen
- Institute and Outpatient Clinic of Occupational, Social and Environmental Medicine, Friedrich-Alexander-Universität Erlangen-Nürnberg, Erlangen, Germany
| | - Ľ Palkovičová Murínová
- Slovak Medical University in Bratislava, Faculty of Public Health, Department of Environmental Medicine, Bratislava, Slovakia.
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Bil W, Govarts E, Zeilmaker MJ, Woutersen M, Bessems J, Ma Y, Thomsen C, Haug LS, Lignell S, Gyllenhammar I, Palkovicova Murinova L, Fabelova L, Tratnik JS, Kosjek T, Gabriel C, Sarigiannis D, Pedraza-Diaz S, Esteban-López M, Castaño A, Rambaud L, Riou M, Franken C, Colles A, Vogel N, Kolossa-Gehring M, Halldorsson TI, Uhl M, Schoeters G, Santonen T, Vinggaard AM. Approaches to mixture risk assessment of PFASs in the European population based on human hazard and biomonitoring data. Int J Hyg Environ Health 2023; 247:114071. [PMID: 36446273 DOI: 10.1016/j.ijheh.2022.114071] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 05/26/2022] [Revised: 09/25/2022] [Accepted: 11/05/2022] [Indexed: 11/27/2022]
Abstract
Per- and polyfluoroalkyl substances (PFASs) are a highly persistent, mobile, and bioaccumulative class of chemicals, of which emissions into the environment result in long-lasting contamination with high probability for causing adverse effects to human health and the environment. Within the European Biomonitoring Initiative HBM4EU, samples and data were collected in a harmonized way from human biomonitoring (HBM) studies in Europe to derive current exposure data across a geographic spread. We performed mixture risk assessments based on recent internal exposure data of PFASs in European teenagers generated in the HBM4EU Aligned Studies (dataset with N = 1957, sampling years 2014-2021). Mixture risk assessments were performed based on three hazard-based approaches: the Hazard Index (HI) approach, the sum value approach as used by the European Food Safety Authority (EFSA) and the Relative Potency Factor (RPF) approach. The HI approach resulted in the highest risk estimates, followed by the RPF approach and the sum value approach. The assessments indicate that PFAS exposure may result in a health risk in a considerable fraction of individuals in the HBM4EU teenager study sample, thereby confirming the conclusion drawn in the recent EFSA scientific opinion. This study underlines that HBM data are of added value in assessing the health risks of aggregate and cumulative exposure to PFASs, as such data are able to reflect exposure from different sources and via different routes.
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Affiliation(s)
- W Bil
- National Institute for Public Health and the Environment (RIVM), Bilthoven, the Netherlands.
| | - E Govarts
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - M J Zeilmaker
- National Institute for Public Health and the Environment (RIVM), Bilthoven, the Netherlands
| | - M Woutersen
- National Institute for Public Health and the Environment (RIVM), Bilthoven, the Netherlands
| | - J Bessems
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - Y Ma
- National Food Institute, Technical University of Denmark (DTU), Lyngby, Denmark
| | - C Thomsen
- Norwegian Institute of Public Health (NIPH), Oslo, Norway
| | - L S Haug
- Norwegian Institute of Public Health (NIPH), Oslo, Norway
| | - S Lignell
- Swedish Food Agency, Uppsala, Sweden
| | | | | | - L Fabelova
- Faculty of Public Health, Slovak Medical University (SZU), Bratislava, Slovakia
| | | | - T Kosjek
- Jožef Stefan Institute (IJS), Ljubljana, Slovenia
| | - C Gabriel
- Environmental Engineering Laboratory, Department of Chemical Engineering, Aristotle University of Thessaloniki (AUTH), Thessaloniki, Greece; HERACLES Research Center on the Exposome and Health, Center for Interdisciplinary Research and Innovation, Balkan Center, Thessaloniki, Greece
| | - D Sarigiannis
- Environmental Engineering Laboratory, Department of Chemical Engineering, Aristotle University of Thessaloniki (AUTH), Thessaloniki, Greece; HERACLES Research Center on the Exposome and Health, Center for Interdisciplinary Research and Innovation, Balkan Center, Thessaloniki, Greece; Environmental Health Engineering, Institute of Advanced Study, Pavia, Italy
| | - S Pedraza-Diaz
- National Centre for Environmental Health, Instituto de Salud Carlos III (ISCIII), Madrid, Spain
| | - M Esteban-López
- National Centre for Environmental Health, Instituto de Salud Carlos III (ISCIII), Madrid, Spain
| | - A Castaño
- National Centre for Environmental Health, Instituto de Salud Carlos III (ISCIII), Madrid, Spain
| | - L Rambaud
- Santé Publique France, Saint-Maurice, France
| | - M Riou
- Santé Publique France, Saint-Maurice, France
| | - C Franken
- Provincial Institute for Hygiene, Antwerp, Belgium
| | - A Colles
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - N Vogel
- German Environment Agency (UBA), Berlin, Germany
| | | | - T I Halldorsson
- Faculty of Food Science and Nutrition, University of Iceland (UI), Reykjavik, Iceland
| | - M Uhl
- Environment Agency Austria (EAA), Vienna, Austria
| | - G Schoeters
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - T Santonen
- Finnish Institute of Occupational Health (FIOH), Työterveyslaitos, Finland
| | - A M Vinggaard
- National Food Institute, Technical University of Denmark (DTU), Lyngby, Denmark
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4
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Schoeters G, Verheyen VJ, Colles A, Remy S, Martin LR, Govarts E, Nelen V, Den Hond E, De Decker A, Franken C, Loots I, Coertjens D, Morrens B, Bastiaensen M, Gys C, Malarvannan G, Covaci A, Nawrot T, De Henauw S, Bellemans M, Leermakers M, Van Larebeke N, Baeyens W, Jacobs G, Voorspoels S, Nielsen F, Bruckers L. Internal exposure of Flemish teenagers to environmental pollutants: Results of the Flemish Environment and Health Study 2016-2020 (FLEHS IV). Int J Hyg Environ Health 2022; 242:113972. [PMID: 35453051 DOI: 10.1016/j.ijheh.2022.113972] [Citation(s) in RCA: 2] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 01/04/2022] [Revised: 04/07/2022] [Accepted: 04/09/2022] [Indexed: 12/12/2022]
Abstract
The Flemish Environment and Health Study (FLEHS) collects information on internal exposure to a broad range of environmental chemicals in the general population in Flanders, the Northern region of Belgium. The aim is to establish biomonitoring exposure distributions for the general population in support of public health and environmental policy, environmental risk assessment and risk management decisions. In 2017-2018, urine and blood samples were collected from 428 teenagers by a stratified clustered two stage randomized design. Samples were analyzed for a broad range of biomarkers related to exposure to chlorinated and newer pesticides, brominated and organophosphate flame retardants (BFR/OPFR), polychlorinated biphenyls (PCBs), bisphenols, phthalates and alternative plasticizers, per-and polyfluoroalkyl substances (PFAS), polycyclic aromatic hydrocarbons (PAHs), benzene, metals and trace elements. The geometric mean levels and percentiles of the distribution were estimated for each biomarker, for the whole study population and following stratification for sex, the household educational attainment and the residence area's urbanicity. Geometric means of biomarkers of lead, dichlorodiphenyltrichloroethane (DDT), PCBs, PAHs, regulated phthalates and bisphenol A (BPA) were lower than in the previous FLEHS cycles. Most biomarker levels were below health-based guidance values (HB-GVs). However, HB-GVs of urinary arsenic, blood lead, blood cadmium, sum of serum perfluorooctane sulfonate (PFOS) and perfluoro-1-hexanesulfonate (PFHxS) and the urinary pyrethroid metabolite (3-PBA) were exceeded in respectively 25%, 12%, 39.5%, 10% and 22% of the teenagers. These results suggest that the levels of exposure in the Flemish population to some environmental chemicals might be of concern. At the same time, we noticed that biomarkers for BPA substitutes, metabolites of OPFRs, an expanded list of PFAS, glyphosate and its metabolite could be measured in substantial proportions of participants. Interpretation of these levels in a health-risk context remains uncertain as HB-GVs are lacking. Household educational attainment and residential urbanicity were significant exposure determinants for many biomarkers and could influence specific biomarker levels up to 70% as shown by multiple regression analysis. The research consortium also took care of the broader external communication of results with participants, policy makers, professional groups and civil society organizations. Our study demonstrated that teenagers are exposed to a wide range of chemicals, it demonstrates the success of public policies to reduce exposure but also points to concern and further priorities and needs for follow up.
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Affiliation(s)
- G Schoeters
- VITO Health, Flemish Institute for Technological Research (VITO), Boeretang 200, 2400, Mol, Belgium; Department of Biomedical Sciences, University of Antwerp, Universiteitsplein 1, 2610, Wilrijk, Belgium.
| | - V J Verheyen
- VITO Health, Flemish Institute for Technological Research (VITO), Boeretang 200, 2400, Mol, Belgium; Department of Biomedical Sciences, University of Antwerp, Universiteitsplein 1, 2610, Wilrijk, Belgium
| | - A Colles
- VITO Health, Flemish Institute for Technological Research (VITO), Boeretang 200, 2400, Mol, Belgium
| | - S Remy
- VITO Health, Flemish Institute for Technological Research (VITO), Boeretang 200, 2400, Mol, Belgium
| | - L Rodriguez Martin
- VITO Health, Flemish Institute for Technological Research (VITO), Boeretang 200, 2400, Mol, Belgium
| | - E Govarts
- VITO Health, Flemish Institute for Technological Research (VITO), Boeretang 200, 2400, Mol, Belgium
| | - V Nelen
- Provincial Institute of Hygiene, Kronenburgstraat 45, 2000, Antwerp, Belgium
| | - E Den Hond
- Provincial Institute of Hygiene, Kronenburgstraat 45, 2000, Antwerp, Belgium
| | - A De Decker
- Provincial Institute of Hygiene, Kronenburgstraat 45, 2000, Antwerp, Belgium
| | - C Franken
- Provincial Institute of Hygiene, Kronenburgstraat 45, 2000, Antwerp, Belgium
| | - I Loots
- Department of Sociology, Faculty of Social Sciences, University of Antwerp, Sint-Jacobstraat 2, 2000, Antwerp, Belgium
| | - D Coertjens
- Department of Sociology, Faculty of Social Sciences, University of Antwerp, Sint-Jacobstraat 2, 2000, Antwerp, Belgium
| | - B Morrens
- Department of Sociology, Faculty of Social Sciences, University of Antwerp, Sint-Jacobstraat 2, 2000, Antwerp, Belgium
| | - M Bastiaensen
- Toxicological Centre, University of Antwerp, Universiteitsplein 1, 2610, Wilrijk, Belgium
| | - C Gys
- Toxicological Centre, University of Antwerp, Universiteitsplein 1, 2610, Wilrijk, Belgium
| | - G Malarvannan
- Toxicological Centre, University of Antwerp, Universiteitsplein 1, 2610, Wilrijk, Belgium
| | - A Covaci
- Toxicological Centre, University of Antwerp, Universiteitsplein 1, 2610, Wilrijk, Belgium
| | - T Nawrot
- Centre for Environmental Sciences, Hasselt University, Agoralaan building D, 3590, Diepenbeek, Belgium
| | - S De Henauw
- Department of Public Health and Primary Care, Faculty of Medicine and Health Sciences, Ghent University, De Pintelaan 185, 9000, Ghent, Belgium
| | - M Bellemans
- Department of Public Health and Primary Care, Faculty of Medicine and Health Sciences, Ghent University, De Pintelaan 185, 9000, Ghent, Belgium
| | - M Leermakers
- Analytical, Environmental and Geo- Chemistry, Vrije Universiteit Brussel, Brussels, Belgium
| | - N Van Larebeke
- Analytical, Environmental and Geo- Chemistry, Vrije Universiteit Brussel, Brussels, Belgium
| | - W Baeyens
- Analytical, Environmental and Geo- Chemistry, Vrije Universiteit Brussel, Brussels, Belgium
| | - G Jacobs
- VITO GOAL, Flemish Institute for Technological Research (VITO), Boeretang 200, 2400, Mol, Belgium
| | - S Voorspoels
- VITO GOAL, Flemish Institute for Technological Research (VITO), Boeretang 200, 2400, Mol, Belgium
| | - F Nielsen
- Institute of Public Health, Department of Environmental Medicine, University of Southern Denmark, Odense, Denmark
| | - L Bruckers
- BioStat, Data Science Institute, Hasselt University, Martelarenlaan 42, 3500, Hasselt, Belgium
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Lambrechts N, Govarts E, Colles A, Remy S, Morrens B, Leermaekers M, Van De Mieroop E, Hond ED, Nelen V, Loots I, Schoeters G. Low level arsenic exposure during pregnancy in the 3xG cohort in Flanders: Less efficient detoxification is associated with higher oxidative stress. Toxicol Lett 2016. [DOI: 10.1016/j.toxlet.2016.06.1867] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [What about the content of this article? (0)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/16/2022]
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Croes K, Colles A, Koppen G, De Galan S, Vandermarken T, Govarts E, Bruckers L, Nelen V, Schoeters G, Van Larebeke N, Denison MS, Mampaey M, Baeyens W. Determination of PCDD/Fs, PBDD/Fs and dioxin-like PCBs in human milk from mothers residing in the rural areas in Flanders, using the CALUX bioassay and GC-HRMS. Talanta 2013; 113:99-105. [PMID: 23708629 PMCID: PMC3690775 DOI: 10.1016/j.talanta.2013.03.086] [Citation(s) in RCA: 28] [Impact Index Per Article: 2.5] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 11/01/2012] [Revised: 03/26/2013] [Accepted: 03/29/2013] [Indexed: 11/21/2022]
Abstract
Since the CALUX (Chemically Activated LUciferase gene eXpression) bioassay is a fast and inexpensive tool for the determination of dioxin-like compounds in a large number of samples and requires only small sample volumes, the use of this technique in human biomonitoring programs provides a good alternative to GC-HRMS. In this study, a new CALUX method for the separate analysis of PCDD/Fs and dioxin-like PCBs (dl-PCBs) in small amounts of human milk samples with the new sensitive H1L7.5c1 cell line was used to analyze 84 human milk samples, collected from mothers residing in the Flemish rural communities. The geometric mean CALUX-Bioanalytical Equivalent (CALUX-BEQ) values, reported for the 84 mothers from the study area were 10.4 (95% CI: 9.4-11.4) pg CALUX-BEQ per gram lipid or 0.41 (95% CI: 0.37-0.45) pg CALUX-BEQ per gram milk for the PCDD/Fs and 1.73 (1.57-1.91) pg CALUX-BEQ per gram lipid or 0.07 (95% CI: 0.06-0.08) pg CALUX-BEQ per gram milk for the dioxin-like PCBs. Multiple regression analysis showed significant associations between PCDD/Fs and weight change after pregnancy, smoking and consumption of local eggs. One pooled human milk sample was analyzed with both CALUX and GC-HRMS. The ratio of CALUX and GC-HRMS results for this sample were respectively 1.60, 0.58 and 1.23 for the PCDD/Fs, the dl-PCBs and the sum of both fractions, when using the 2005-TEF values. Additionally, also low levels of certain brominated dioxins and furans were detected in the pooled sample with GC-HRMS.
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Affiliation(s)
- K Croes
- Vrije Universiteit Brussel, Department of Analytical and Environmental Chemistry (ANCH), Pleinlaan 2, 1050 Brussels, Belgium.
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Croes K, Colles A, Koppen G, Govarts E, Bruckers L, Van de Mieroop E, Nelen V, Covaci A, Dirtu AC, Thomsen C, Haug LS, Becher G, Mampaey M, Schoeters G, Van Larebeke N, Baeyens W. Persistent organic pollutants (POPs) in human milk: a biomonitoring study in rural areas of Flanders (Belgium). Chemosphere 2012; 89:988-994. [PMID: 22840535 DOI: 10.1016/j.chemosphere.2012.06.058] [Citation(s) in RCA: 83] [Impact Index Per Article: 6.9] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 02/28/2012] [Revised: 06/06/2012] [Accepted: 06/30/2012] [Indexed: 06/01/2023]
Abstract
To collect information on the concentrations of persistent organic pollutants (POPs) in the rural areas in Flanders (Belgium), 84 breastfeeding mothers were recruited in rural communities in East and West Flanders and Flemish Brabant in 2009-2010. Polychlorinated biphenyl (PCB) congeners, organochlorine pesticides, brominated flame retardants, perfluorinated compounds, polychlorinated dibenzodioxines and dibenzofurans, and dioxin-like PCBs were measured in individual milk samples and in a pooled milk sample, while some additional pollutants were only measured in the pooled sample. For most pollutants, the concentrations in this study were lower or comparable to the concentrations measured in the pooled Belgian sample of the WHO human milk study of 2006, except for the pesticides dichlorodiphenyltrichloroethane DDT (+25% for ΣDDT and metabolites) and trans-nonachlor (+94%), and for the brominated flame retardant hexachlorocyclododecane HBCD (+153%). Perfluorinated compounds were for the first time determined in human milk samples from Belgium and the concentrations were comparable to those from other European countries. Also, interesting associations were found between the concentrations of POPs measured in human milk and personal characteristics as well as dietary habits of the study population. PFOS en PFOA concentrations were significantly higher in milk of primiparous participants compared to mothers who gave birth to their second child. Lower brominated PBDE congeners increased with increasing BMI of the mothers (p=0.01 for BDE 47, p=0.02 for BDE 99 and p=0.02 for BDE 100). Participants consuming milk or dairy products daily had significant higher concentrations of ΣDDTs (p=0.03) and oxychlordane (p=0.047) in their human milk samples.
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Affiliation(s)
- K Croes
- Free University of Brussels, Department of Analytical and Environmental Chemistry, Brussels, Belgium.
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Croes K, Van Langenhove K, Den Hond E, Bruckers L, Colles A, Koppen G, Loots I, Nelen V, Schoeters G, Nawrot T, Van Larebeke N, Denison MS, Vandermarken T, Elskens M, Baeyens W. Quantification of PCDD/Fs and dioxin-like PCBs in small amounts of human serum using the sensitive H1L7.5c1 mouse hepatoma cell line: optimization and analysis of human serum samples from adolescents of the Flemish human biomonitoring program FLEHS II. Talanta 2011; 85:2484-91. [PMID: 21962672 PMCID: PMC3523230 DOI: 10.1016/j.talanta.2011.07.103] [Citation(s) in RCA: 12] [Impact Index Per Article: 0.9] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 05/10/2011] [Revised: 07/28/2011] [Accepted: 07/29/2011] [Indexed: 11/26/2022]
Abstract
Since the CALUX (Chemically Activated LUciferase gene eXpression) bioassay is a fast and inexpensive tool for the throughput analysis of dioxin-like compounds in a large number of samples and requires only small sample volumes, the use of this technique in human biomonitoring programs provides a good alternative to GC-HRMS. In this study, a method for the separate analysis of PCDD/Fs and dioxin-like PCBs (dl-PCBs) in human serum with the new sensitive H1L7.5c1 mouse hepatoma cell line was optimized. Sample dilution factors of 5 and 2.4 were selected for routine analysis of respectively the PCDD/Fs and dl-PCBs. The validation studies showed that repeatability and within-lab reproducibility for the quality control (QC) standard were within the in-house criteria. A long-term within-lab reproducibility of 25% for the PCDD/F fraction and 41% for the dl-PCB fraction for the analysis of pooled serum samples, expressed as pg BEQ/g fat, was determined. CALUX recoveries of the spiked procedural blanks were within the acceptable in-house limits of 80-120% for both fractions and the LOQ was 30.3 pg BEQ/g fat for the PCDD/Fs and 14.5 pg BEQ/g fat for the dl-PCBs. The GC-HRMS recovery of a C13-spiked pooled serum sample was between 60 and 90% for all PCDD/F congeners and between 67 and 82% for the non-ortho PCBs. An adequate separation between both fractions was found. The CALUX/GC-HRMS ratio for a pooled serum sample was respectively 2.0 and 1.4 for the PCDD/Fs and the dl-PCBs, indicating the presence of additional AhR active compounds. As expected, a correlation was found between human serum samples analyzed with both the new H1L7.5c1 cell line and the more established H1L6.1c3 cell line. The geometric mean CALUX-BEQ values, reported for the adolescents of the second Flemish Environment and Health Study (FLEHS II) recruited in 2009-2010, were 108 (95% CI: 101-114) pg CALUX-BEQ/g fat for the PCDD/Fs and 32.1 (30.1-34.2) pg CALUX-BEQ/g fat for the dioxin-like PCBs.
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Affiliation(s)
- K Croes
- Vrije Universiteit Brussel, Department of Analytical and Environmental Chemistry (ANCH), Pleinlaan 2, 1050 Brussels, Belgium.
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Colles A. On the Operation of Tying the Subclavian Artery. Edinb Med Surg J 1815; 11:1-25. [PMID: 30329444 PMCID: PMC5743393] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Download PDF] [Figures] [Subscribe] [Scholar Register] [Indexed: 10/26/2022]
Affiliation(s)
- A. Colles
- Professor of Anatomy and Surgery, Royal College of Surgeons in Ireland, and one of the Surgeons of Dr Steven's Hospital, Dublin
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Colles A. On the Fracture of the Carpal Extremity of the Radius. Edinb Med Surg J 1814; 10:182-186. [PMID: 30329360 PMCID: PMC5743240] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Download PDF] [Figures] [Subscribe] [Scholar Register] [Indexed: 06/08/2023]
Affiliation(s)
- A Colles
- one of the Professors of Anatomy and Surgery in the Royal College of Surgeons in Ireland
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