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Current exposure to phthalates and DINCH in European children and adolescents - Results from the HBM4EU Aligned Studies 2014 to 2021.
Vogel, Nina; Schmidt, Phillipp; Lange, Rosa; Gerofke, Antje; Sakhi, Amrit K; Haug, Line S; Jensen, Tina Kold; Frederiksen, Hanne; Szigeti, Tamás; Csákó, Zsófia; Murinova, Lubica Palkovicova; Sidlovska, Miroslava; Janasik, Beata; Wasowicz, Wojciech; Tratnik, Janja Snoj; Mazej, Darja; Gabriel, Catherine; Karakitsios, Spyros; Barbone, Fabio; Rosolen, Valentina; Rambaud, Loïc; Riou, Margaux; Murawski, Aline; Leseman, Daan; Koppen, Gudrun; Covaci, Adrian; Lignell, Sanna; Lindroos, Anna Karin; Zvonar, Martin; Andryskova, Lenka; Fabelova, Lucia; Richterova, Denisa; Horvat, Milena; Kosjek, Tina; Sarigiannis, Denis; Maroulis, Marios; Pedraza-Diaz, Susana; Cañas, Ana; Verheyen, Veerle J; Bastiaensen, Michiel; Gilles, Liese; Schoeters, Greet; Esteban-López, Marta; Castaño, Argelia; Govarts, Eva; Koch, Holger M; Kolossa-Gehring, Marike.
Afiliação
  • Vogel N; German Environment Agency (UBA), Berlin, Germany. Electronic address: nina.vogel@uba.de.
  • Schmidt P; German Environment Agency (UBA), Berlin, Germany.
  • Lange R; German Environment Agency (UBA), Berlin, Germany.
  • Gerofke A; German Environment Agency (UBA), Berlin, Germany.
  • Sakhi AK; Norwegian Institute of Public Health, Oslo, Norway.
  • Haug LS; Norwegian Institute of Public Health, Oslo, Norway.
  • Jensen TK; IST - Clinical Pharmacology, Pharmacy and Environmental Medicine, Odense, Denmark.
  • Frederiksen H; Department of Growth and Reproduction, Copenhagen University Hospital - Rigshospitalet, Copenhagen, Denmark; International Center for Research and Research Training in Endocrine Disruption of Male Reproduction and Child Health (EDMaRC), Copenhagen University Hospital - Rigshospitalet, Copenhagen, De
  • Szigeti T; National Public Health Center, Budapest, Hungary.
  • Csákó Z; National Public Health Center, Budapest, Hungary.
  • Murinova LP; Slovak Medical University, Faculty of Public Health, Bratislava, Slovakia.
  • Sidlovska M; Constantine the Philosopher University in Nitra, Slovakia.
  • Janasik B; Nofer Institute of Occupational Medicine, Lodz, Poland.
  • Wasowicz W; Nofer Institute of Occupational Medicine, Lodz, Poland.
  • Tratnik JS; Jozef Stefan Institute, Department of Environmental Sciences, Ljubljana, Slovenia.
  • Mazej D; Jozef Stefan Institute, Department of Environmental Sciences, Ljubljana, Slovenia.
  • 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, Thessaloniki-Thermi, Greece.
  • Karakitsios S; 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, Thessaloniki-Thermi, Greece.
  • Barbone F; Department of Medicine-DAME, University of Udine, Udine, Italy.
  • Rosolen V; Institute for Maternal and Child Health - IRCCS "Burlo Garofolo", Trieste, Italy.
  • Rambaud L; Santé publique France, Environmental and Occupational Health Division, Saint-Maurice, France.
  • Riou M; Santé publique France, Environmental and Occupational Health Division, Saint-Maurice, France.
  • Murawski A; German Environment Agency (UBA), Berlin, Germany.
  • Leseman D; National Institute for Public Health and the Environment (RIVM), Bilthoven, the Netherlands.
  • Koppen G; VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium.
  • Covaci A; Toxicological Center, University of Antwerp, Wilrijk, Belgium.
  • Lignell S; Swedish Food Agency, Uppsala, Sweden.
  • Lindroos AK; Swedish Food Agency, Uppsala, Sweden.
  • Zvonar M; RECETOX, Faculty of Science, Masaryk University, Brno, Czech Republic.
  • Andryskova L; RECETOX, Faculty of Science, Masaryk University, Brno, Czech Republic.
  • Fabelova L; Slovak Medical University, Faculty of Public Health, Bratislava, Slovakia.
  • Richterova D; Slovak Medical University, Faculty of Public Health, Bratislava, Slovakia.
  • Horvat M; Jozef Stefan Institute, Department of Environmental Sciences, Ljubljana, Slovenia.
  • Kosjek T; Jozef Stefan Institute, Department of Environmental Sciences, Ljubljana, Slovenia.
  • 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, Thessaloniki-Thermi, Greece; Environmental Health Engineeri
  • Maroulis M; 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, Thessaloniki-Thermi, Greece.
  • Pedraza-Diaz S; National Centre for Environmental Health, Instituto de Salud Carlos III, Majadahonda, Madrid, Spain.
  • Cañas A; National Centre for Environmental Health, Instituto de Salud Carlos III, Majadahonda, Madrid, Spain.
  • Verheyen VJ; VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium.
  • Bastiaensen M; Toxicological Center, University of Antwerp, Wilrijk, Belgium.
  • Gilles L; VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium.
  • Schoeters G; VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium; University of Antwerp, Dept of Biomedical Sciences and Toxicological Centre, Antwerp, Belgium.
  • Esteban-López M; National Centre for Environmental Health, Instituto de Salud Carlos III, Majadahonda, Madrid, Spain.
  • Castaño A; National Centre for Environmental Health, Instituto de Salud Carlos III, Majadahonda, Madrid, Spain.
  • Govarts E; VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium.
  • Koch HM; Institute for Prevention and Occupational Medicine of the German Social Accident Insurance, Institute of the Ruhr University Bochum (IPA), Bochum, Germany.
  • Kolossa-Gehring M; German Environment Agency (UBA), Berlin, Germany.
Int J Hyg Environ Health ; 249: 114101, 2023 04.
Article em En | MEDLINE | ID: mdl-36805185
ABSTRACT
Phthalates are mainly used as plasticizers for polyvinyl chloride (PVC). Exposure to several phthalates is associated with different adverse effects most prominently on the development of reproductive functions. The HBM4EU Aligned Studies (2014-2021) have investigated current European exposure to ten phthalates (DEP, BBzP, DiBP, DnBP, DCHP, DnPeP, DEHP, DiNP, DiDP, DnOP) and the substitute DINCH to answer the open policy relevant questions which were defined by HBM4EU partner countries and EU institutions as the starting point of the programme. The exposure dataset includes ∼5,600 children (6-11 years) and adolescents (12-18 years) from up to 12 countries per age group and covering the North, East, South and West European regions. Study data from participating studies were harmonised with respect to sample size and selection of participants, selection of biomarkers, and quality and comparability of analytical results to provide a comparable perspective of European exposure. Phthalate and DINCH exposure were deduced from urinary excretions of metabolites, where concentrations were expressed as their key descriptor geometric mean (GM) and 95th percentile (P95). This study aims at reporting current exposure levels and differences in these between European studies and regions, as well as comparisons to human biomonitoring guidance values (HBM-GVs). GMs for children were highest for ∑DEHP metabolites (33.6 µg/L), MiBP (26.6 µg/L), and MEP (24.4 µg/L) and lowest for∑DiDP metabolites (1.91 µg/L) and ∑DINCH metabolites (3.57 µg/L). In adolescents highest GMs were found for MEP (43.3 µg/L), ∑DEHP metabolites (28.8 µg/L), and MiBP (25.6 µg/L) and lowest for ∑DiDP metabolites (= 2.02 µg/L) and ∑DINCH metabolites (2.51 µg/L). In addition, GMs and P95 stratified by European region, sex, household education level, and degree of urbanization are presented. Differences in average biomarker concentrations between sampling sites (data collections) ranged from factor 2 to 9. Compared to the European average, children in the sampling sites OCC (Denmark), InAirQ (Hungary), and SPECIMEn (The Netherlands) had the lowest concentrations across all metabolites and ESTEBAN (France), NAC II (Italy), and CROME (Greece) the highest. For adolescents, comparably higher metabolite concentrations were found in NEB II (Norway), PCB cohort (Slovakia), and ESTEBAN (France), and lower concentrations in POLAES (Poland), FLEHS IV (Belgium), and GerES V-sub (Germany). Multivariate analyses (Survey Generalized Linear Models) indicate compound-specific differences in average metabolite concentrations between the four European regions. Comparison of individual levels with HBM-GVs revealed highest rates of exceedances for DnBP and DiBP, with up to 3 and 5%, respectively, in children and adolescents. No exceedances were observed for DEP and DINCH. With our results we provide current, detailed, and comparable data on exposure to phthalates in children and - for the first time - in adolescents, and - for the first time - on DINCH in children and adolescents of all four regions of Europe which are particularly suited to inform exposure and risk assessment and answer open policy relevant questions.
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Texto completo: 1 Base de dados: MEDLINE Assunto principal: Ácidos Ftálicos / Poluentes Ambientais Tipo de estudo: Prognostic_studies / Risk_factors_studies Limite: Adolescent / Child / Humans Idioma: En Ano de publicação: 2023 Tipo de documento: Article

Texto completo: 1 Base de dados: MEDLINE Assunto principal: Ácidos Ftálicos / Poluentes Ambientais Tipo de estudo: Prognostic_studies / Risk_factors_studies Limite: Adolescent / Child / Humans Idioma: En Ano de publicação: 2023 Tipo de documento: Article