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Katsonouri A, Gabriel C, Esteban López M, Namorado S, Halldorsson TI, Snoj Tratnik J, Rodriguez Martin L, Karakoltzidis A, Chatzimpaloglou A, Giannadaki D, Anastasi E, Thoma A, Domínguez-Morueco N, Cañas Portilla AI, Jacobsen E, Assunção R, Peres M, Santiago S, Nunes C, Pedraza-Diaz S, Iavicoli I, Leso V, Lacasaña M, González-Alzaga B, Horvat M, Sepai O, Castano A, Kolossa-Gehring M, Karakitsios S, Sarigiannis D. HBM4EU-MOM: Prenatal methylmercury-exposure control in five countries through suitable dietary advice for pregnancy - Study design and characteristics of participants. Int J Hyg Environ Health 2023; 252:114213. [PMID: 37393843 DOI: 10.1016/j.ijheh.2023.114213] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 03/27/2023] [Revised: 06/02/2023] [Accepted: 06/22/2023] [Indexed: 07/04/2023]
Abstract
BACKGROUND Seafood is a major source of vital nutrients for optimal fetal growth, but at the same time is the main source of exposure to methylmercury (MeHg), an established neurodevelopmental toxicant. Pregnant women must be provided with dietary advice so as to include safely fish in their diet for nutrition and mercury control. The aim of this work is to present the design of a multicentre randomized control trial (RCT), which combines human biomonitoring (HBM) with dietary interventions using seafood consumption advice to pregnant women for MeHg control, and to collect information about other possible sources of exposure to mercury. It also presents the materials developed for the implementation of the study and the characteristics of the study participants, which were self-reported in the first trimester of pregnancy. METHODS The "HBM4EU-MOM" RCT was performed in the frame of the European Human Biomonitoring Initiative (HBM4EU) in five coastal, high fish-consuming European countries (Cyprus, Greece, Spain, Portugal and Iceland). According to the study design, pregnant women (≥120/country, ≤20 weeks gestational age) provided a hair sample for total mercury assessment (THg) and personal information relevant to the study (e.g., lifestyle, pregnancy status, diet before and during the pregnancy, information on seafood and factors related to possible non-dietary exposures to mercury) during the first trimester of pregnancy. After sampling, participants were randomly assigned to "control" (habitual practices) or "intervention" (received the harmonized HBM4EU-MOM dietary advice for fish consumption during the pregnancy and were encouraged to follow it). Around child delivery, participants provided a second hair sample and completed another tailored questionnaire. RESULTS A total of 654 women aged 18-45 years were recruited in 2021 in the five countries, primarily through their health-care providers. The pre-pregnancy BMI of the participants ranged from underweight to obese, but was on average within the healthy range. For 73% of the women, the pregnancy was planned. 26% of the women were active smokers before the pregnancy and 8% continued to smoke during the pregnancy, while 33% were passive smokers before pregnancy and 23% remained passively exposed during the pregnancy. 53% of the women self-reported making dietary changes for their pregnancy, with 74% of these women reporting making the changes upon learning of their pregnancy. Of the 43% who did not change their diet for the pregnancy, 74% reported that their diet was already balanced, 6% found it difficult to make changes and 2% were unsure of what changes to make. Seafood consumption did not change significantly before and during the first trimester of pregnancy (overall average ∼8 times per month), with the highest frequency reported in Portugal (≥15 times per month), followed by Spain (≥7 times per month). During the first-trimester of pregnancy, 89% of the Portuguese women, 85% of the Spanish women and <50% of Greek, Cypriot and Icelandic women reported that they had consumed big oily fish. Relevant to non-dietary exposure sources, most participants (>90%) were unaware of safe procedures for handling spillage from broken thermometers and energy-saving lamps, though >22% experienced such an incident (>1 year ago). 26% of the women had dental amalgams. ∼1% had amalgams placed and ∼2% had amalgams removed during peri-pregnancy. 28% had their hair dyed in the past 3 months and 40% had body tattoos. 8% engaged with gardening involving fertilizers/pesticides and 19% with hobbies involving paints/pigments/dyes. CONCLUSIONS The study design materials were fit for the purposes of harmonization and quality-assurance. The harmonized information collected from pregnant women suggests that it is important to raise the awareness of women of reproductive age and pregnant women about how to safely include fish in their diet and to empower them to make proper decisions for nutrition and control of MeHg, as well as other chemical exposures.
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Affiliation(s)
| | - Catherine Gabriel
- HERACLES Research Center - KEDEK, Aristotle University of Thessaloniki, Thessaloniki, Greece; Environmental Engineering Laboratory, Department of Chemical Engineering, Aristotle University of Thessaloniki, Thessaloniki, Greece.
| | - Marta Esteban López
- Environmental Toxicology Unit, National Centre for Environmental Health. Instituto de Salud Carlos III (CNSA-ISCIII), Madrid, Spain
| | - Sonia Namorado
- Department of Epidemiology, National Institute of Health Dr. Ricardo Jorge (INSA), Lisbon, Portugal; NOVA National School of Public Health, Public Health Research Centre, Universidade NOVA de Lisboa, Lisbon, Portugal; Comprehensive Health Research Center (CHRC), Lisbon, Portugal
| | | | | | | | - Achilleas Karakoltzidis
- HERACLES Research Center - KEDEK, Aristotle University of Thessaloniki, Thessaloniki, Greece; Environmental Engineering Laboratory, Department of Chemical Engineering, Aristotle University of Thessaloniki, Thessaloniki, Greece
| | - Anthoula Chatzimpaloglou
- HERACLES Research Center - KEDEK, Aristotle University of Thessaloniki, Thessaloniki, Greece; Environmental Engineering Laboratory, Department of Chemical Engineering, Aristotle University of Thessaloniki, Thessaloniki, Greece
| | | | - Elena Anastasi
- State General Laboratory, Ministry of Health, Nicosia, Cyprus
| | - Anthi Thoma
- State General Laboratory, Ministry of Health, Nicosia, Cyprus
| | - Noelia Domínguez-Morueco
- Environmental Toxicology Unit, National Centre for Environmental Health. Instituto de Salud Carlos III (CNSA-ISCIII), Madrid, Spain
| | - Ana I Cañas Portilla
- Environmental Toxicology Unit, National Centre for Environmental Health. Instituto de Salud Carlos III (CNSA-ISCIII), Madrid, Spain
| | | | - Ricardo Assunção
- Egas Moniz School & Health Science, Campus Universitário, Quinta da Granja, 2829-511, Monte de Caparica, Almada, Portugal
| | - Maria Peres
- Department of Epidemiology, National Institute of Health Dr. Ricardo Jorge (INSA), Lisbon, Portugal
| | - Susana Santiago
- Department of Epidemiology, National Institute of Health Dr. Ricardo Jorge (INSA), Lisbon, Portugal
| | - Carla Nunes
- Department of Epidemiology, National Institute of Health Dr. Ricardo Jorge (INSA), Lisbon, Portugal
| | - Susana Pedraza-Diaz
- Environmental Toxicology Unit, National Centre for Environmental Health. Instituto de Salud Carlos III (CNSA-ISCIII), Madrid, Spain
| | - Ivo Iavicoli
- Department of Public Health University of Naples Federico II, Naples, Italy
| | - Veruscka Leso
- Department of Public Health University of Naples Federico II, Naples, Italy
| | - Marina Lacasaña
- Andalusian School of Public Health (EASP), Granada, Spain; Instituto de Investigación Biosanitaria, Ibs.GRANADA, Granada, Spain; CIBER Epidemiology and Public Health (CIBERESP), Madrid, Spain; Andalusian Health and Environment Observatory (OSMAN), Granada, Spain
| | - Beatriz González-Alzaga
- Andalusian School of Public Health (EASP), Granada, Spain; Instituto de Investigación Biosanitaria, Ibs.GRANADA, Granada, Spain; CIBER Epidemiology and Public Health (CIBERESP), Madrid, Spain
| | | | - Ovnair Sepai
- UK Health Security Agency, Radiation, Chemicals and Environment Division, Harwell, UK
| | - Argelia Castano
- Environmental Toxicology Unit, National Centre for Environmental Health. Instituto de Salud Carlos III (CNSA-ISCIII), Madrid, Spain
| | | | - Spyros Karakitsios
- HERACLES Research Center - KEDEK, Aristotle University of Thessaloniki, Thessaloniki, Greece; Environmental Engineering Laboratory, Department of Chemical Engineering, Aristotle University of Thessaloniki, Thessaloniki, Greece
| | - Dimosthenis Sarigiannis
- HERACLES Research Center - KEDEK, Aristotle University of Thessaloniki, Thessaloniki, Greece; Environmental Engineering Laboratory, Department of Chemical Engineering, Aristotle University of Thessaloniki, Thessaloniki, Greece; Environmental Health Engineering, School for Advanced Study IUSS, Pavia, Italy
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Vogel N, Schmidt P, Lange R, Gerofke A, Sakhi AK, Haug LS, Jensen TK, Frederiksen H, Szigeti T, Csákó Z, Murinova LP, Sidlovska M, Janasik B, Wasowicz W, Tratnik JS, Mazej D, Gabriel C, Karakitsios S, Barbone F, Rosolen V, Rambaud L, Riou M, Murawski A, Leseman D, Koppen G, Covaci A, Lignell S, Lindroos AK, Zvonar M, Andryskova L, Fabelova L, Richterova D, Horvat M, Kosjek T, Sarigiannis D, Maroulis M, Pedraza-Diaz S, Cañas A, Verheyen VJ, Bastiaensen M, Gilles L, Schoeters G, Esteban-López M, Castaño A, Govarts E, Koch HM, Kolossa-Gehring M. Current exposure to phthalates and DINCH in European children and adolescents - Results from the HBM4EU Aligned Studies 2014 to 2021. Int J Hyg Environ Health 2023; 249:114101. [PMID: 36805185 DOI: 10.1016/j.ijheh.2022.114101] [Citation(s) in RCA: 7] [Impact Index Per Article: 7.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 09/19/2022] [Revised: 12/02/2022] [Accepted: 12/08/2022] [Indexed: 02/19/2023]
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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Affiliation(s)
- Nina Vogel
- German Environment Agency (UBA), Berlin, Germany.
| | | | - Rosa Lange
- German Environment Agency (UBA), Berlin, Germany
| | | | | | - Line S Haug
- Norwegian Institute of Public Health, Oslo, Norway
| | - Tina Kold Jensen
- IST - Clinical Pharmacology, Pharmacy and Environmental Medicine, Odense, Denmark
| | - Hanne Frederiksen
- 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, Denmark
| | | | - Zsófia Csákó
- National Public Health Center, Budapest, Hungary
| | | | | | - Beata Janasik
- Nofer Institute of Occupational Medicine, Lodz, Poland
| | | | - Janja Snoj Tratnik
- Jozef Stefan Institute, Department of Environmental Sciences, Ljubljana, Slovenia
| | - Darja Mazej
- Jozef Stefan Institute, Department of Environmental Sciences, Ljubljana, Slovenia
| | - Catherine 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, Thessaloniki-Thermi, Greece
| | - Spyros Karakitsios
- 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
| | - Fabio Barbone
- Department of Medicine-DAME, University of Udine, Udine, Italy
| | - Valentina Rosolen
- Institute for Maternal and Child Health - IRCCS "Burlo Garofolo", Trieste, Italy
| | - Loïc Rambaud
- Santé publique France, Environmental and Occupational Health Division, Saint-Maurice, France
| | - Margaux Riou
- Santé publique France, Environmental and Occupational Health Division, Saint-Maurice, France
| | | | - Daan Leseman
- National Institute for Public Health and the Environment (RIVM), Bilthoven, the Netherlands
| | - Gudrun Koppen
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - Adrian Covaci
- Toxicological Center, University of Antwerp, Wilrijk, Belgium
| | | | | | - Martin Zvonar
- RECETOX, Faculty of Science, Masaryk University, Brno, Czech Republic
| | - Lenka Andryskova
- RECETOX, Faculty of Science, Masaryk University, Brno, Czech Republic
| | - Lucia Fabelova
- Slovak Medical University, Faculty of Public Health, Bratislava, Slovakia
| | - Denisa Richterova
- Slovak Medical University, Faculty of Public Health, Bratislava, Slovakia
| | - Milena Horvat
- Jozef Stefan Institute, Department of Environmental Sciences, Ljubljana, Slovenia
| | - Tina Kosjek
- Jozef Stefan Institute, Department of Environmental Sciences, Ljubljana, Slovenia
| | - Denis 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, Thessaloniki-Thermi, Greece; Environmental Health Engineering, Institute of Advanced Study, Pavia, Italy
| | - Marios Maroulis
- 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
| | - Susana Pedraza-Diaz
- National Centre for Environmental Health, Instituto de Salud Carlos III, Majadahonda, Madrid, Spain
| | - Ana Cañas
- National Centre for Environmental Health, Instituto de Salud Carlos III, Majadahonda, Madrid, Spain
| | - Veerle J Verheyen
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | | | - Liese Gilles
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - Greet Schoeters
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium; University of Antwerp, Dept of Biomedical Sciences and Toxicological Centre, Antwerp, Belgium
| | - Marta Esteban-López
- National Centre for Environmental Health, Instituto de Salud Carlos III, Majadahonda, Madrid, Spain
| | - Argelia Castaño
- National Centre for Environmental Health, Instituto de Salud Carlos III, Majadahonda, Madrid, Spain
| | - Eva Govarts
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - Holger M Koch
- Institute for Prevention and Occupational Medicine of the German Social Accident Insurance, Institute of the Ruhr University Bochum (IPA), Bochum, Germany
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Buekers J, Baken K, Govarts E, Martin LR, Vogel N, Kolossa-Gehring M, Šlejkovec Z, Falnoga I, Horvat M, Lignell S, Lindroos AK, Rambaud L, Riou M, Pedraza-Diaz S, Esteban-Lopez M, Castaño A, Den Hond E, Baeyens W, Santonen T, Schoeters G. Human urinary arsenic species, associated exposure determinants and potential health risks assessed in the HBM4EU Aligned Studies. Int J Hyg Environ Health 2023; 248:114115. [PMID: 36689783 DOI: 10.1016/j.ijheh.2023.114115] [Citation(s) in RCA: 8] [Impact Index Per Article: 8.0] [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: 07/07/2022] [Revised: 12/21/2022] [Accepted: 01/17/2023] [Indexed: 01/22/2023]
Abstract
The European Joint Programme HBM4EU coordinated and advanced human biomonitoring (HBM) in Europe in order to provide science-based evidence for chemical policy development and improve chemical management. Arsenic (As) was selected as a priority substance under the HBM4EU initiative for which open, policy relevant questions like the status of exposure had to be answered. Internal exposure to inorganic arsenic (iAs), measured as Toxic Relevant Arsenic (TRA) (the sum of As(III), As(V), MMA, DMA) in urine samples of teenagers differed among the sampling sites (BEA (Spain) > Riksmaten adolescents (Sweden), ESTEBAN (France) > FLEHS IV (Belgium), SLO CRP (Slovenia)) with geometric means between 3.84 and 8.47 μg/L. The ratio TRA to TRA + arsenobetaine or the ratio TRA to total arsenic varied between 0.22 and 0.49. Main exposure determinants for TRA were the consumption of rice and seafood. When all studies were combined, Pearson correlation analysis showed significant associations between all considered As species. Higher concentrations of DMA, quantitatively a major constituent of TRA, were found with increasing arsenobetaine concentrations, a marker for organic As intake, e.g. through seafood, indicating that other sources of DMA than metabolism of inorganic As exist, e.g. direct intake of DMA or via the intake of arsenosugars or -lipids. Given the lower toxicity of DMA(V) versus iAs, estimating the amount of DMA not originating from iAs, or normalizing TRA for arsenobetaine intake could be useful for estimating iAs exposure and risk. Comparing urinary TRA concentrations with formerly derived biomonitoring equivalent (BE) for non-carcinogenic effects (6.4 μg/L) clearly shows that all 95th percentile exposure values in the different studies exceeded this BE. This together with the fact that cancer risk may not be excluded even at lower iAs levels, suggests a possible health concern for the general population of Europe.
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Affiliation(s)
- Jurgen Buekers
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium.
| | - Kirsten Baken
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | - Eva Govarts
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium
| | | | - Nina Vogel
- German Environment Agency (UBA), Berlin, Germany
| | | | | | | | | | | | | | - Loïc Rambaud
- Department of Environmental and Occupational Health, Santé publique France, Saint-Maurice, France
| | - Margaux Riou
- Department of Environmental and Occupational Health, Santé publique France, Saint-Maurice, France
| | - Susana Pedraza-Diaz
- National Centre for Environmental Health, Instituto de Salud Carlos III, Madrid, Spain
| | - Marta Esteban-Lopez
- National Centre for Environmental Health, Instituto de Salud Carlos III, Madrid, Spain
| | - Argelia Castaño
- National Centre for Environmental Health, Instituto de Salud Carlos III, Madrid, Spain
| | - Elly Den Hond
- Provincial Institute of Hygiene (PIH), Antwerp, Belgium
| | - Willy Baeyens
- Analytical, Environmental & Geo-Chemistry, Free Universtiy of Brussels (VUB), Brussels, Belgium
| | - Tiina Santonen
- Finnish Institute of Occupational Health, Helsinki, Finland
| | - Greet Schoeters
- VITO Health, Flemish Institute for Technological Research (VITO), Mol, Belgium; Department of Biomedical Sciences, University of Antwerp, Antwerp, Belgium
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Rodriguez Martin L, Ottenbros I, Vogel N, Kolossa-Gehring M, Schmidt P, Řiháčková K, Juliá Molina M, Varea-Jiménez E, Govarts E, Pedraza-Diaz S, Lebret E, Vlaanderen J, Luijten M. Identification of Real-Life Mixtures Using Human Biomonitoring Data: A Proof of Concept Study. Toxics 2023; 11:toxics11030204. [PMID: 36976969 PMCID: PMC10058482 DOI: 10.3390/toxics11030204] [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] [Track Full Text] [Subscribe] [Scholar Register] [Received: 12/30/2022] [Accepted: 01/28/2023] [Indexed: 06/01/2023]
Abstract
Human health risk assessment of chemical mixtures is complex due to the almost infinite number of possible combinations of chemicals to which people are exposed to on a daily basis. Human biomonitoring (HBM) approaches can provide inter alia information on the chemicals that are in our body at one point in time. Network analysis applied to such data may provide insight into real-life mixtures by visualizing chemical exposure patterns. The identification of groups of more densely correlated biomarkers, so-called "communities", within these networks highlights which combination of substances should be considered in terms of real-life mixtures to which a population is exposed. We applied network analyses to HBM datasets from Belgium, Czech Republic, Germany, and Spain, with the aim to explore its added value for exposure and risk assessment. The datasets varied in study population, study design, and chemicals analysed. Sensitivity analysis was performed to address the influence of different approaches to standardise for creatinine content of urine. Our approach demonstrates that network analysis applied to HBM data of highly varying origin provides useful information with regards to the existence of groups of biomarkers that are densely correlated. This information is relevant for regulatory risk assessment, as well as for the design of relevant mixture exposure experiments.
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Affiliation(s)
| | - Ilse Ottenbros
- Institute for Risk Assessment Sciences (IRAS), Utrecht University, 3584 CM Utrecht, The Netherlands
- Center for Sustainability, Environment and Health, National Institute for Public Health and the Environment (RIVM), 3720 BA Bilthoven, The Netherlands
| | - Nina Vogel
- German Environment Agency (UBA), 14195 Berlin, Germany
| | | | | | - Katarína Řiháčková
- RECETOX, Faculty of Science, Masaryk University, 625 00 Brno, Czech Republic
| | - Miguel Juliá Molina
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Majadahonda, Spain
| | - Elena Varea-Jiménez
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Majadahonda, Spain
| | - Eva Govarts
- Health, Flemish Institute for Technological Research (VITO), 2400 Mol, Belgium
| | - Susana Pedraza-Diaz
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Majadahonda, Spain
| | - Erik Lebret
- Institute for Risk Assessment Sciences (IRAS), Utrecht University, 3584 CM Utrecht, The Netherlands
- Center for Sustainability, Environment and Health, National Institute for Public Health and the Environment (RIVM), 3720 BA Bilthoven, The Netherlands
| | - Jelle Vlaanderen
- Institute for Risk Assessment Sciences (IRAS), Utrecht University, 3584 CM Utrecht, The Netherlands
| | - Mirjam Luijten
- Centre for Health Protection, National Institute for Public Health and the Environment (RIVM), 3720 BA Bilthoven, The Netherlands
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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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6
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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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7
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Tarazona JV, Cattaneo I, Niemann L, Pedraza-Diaz S, González-Caballero MC, de Alba-Gonzalez M, Cañas A, Dominguez-Morueco N, Esteban-López M, Castaño A, Borges T, Katsonouri A, Makris KC, Ottenbros I, Mol H, De Decker A, Morrens B, Berman T, Barnett-Itzhaki Z, Probst-Hensch N, Fuhrimann S, Tratnik JS, Horvat M, Rambaud L, Riou M, Schoeters G, Govarts E, Kolossa-Gehring M, Weber T, Apel P, Namorado S, Santonen T. A Tiered Approach for Assessing Individual and Combined Risk of Pyrethroids Using Human Biomonitoring Data. Toxics 2022; 10:toxics10080451. [PMID: 36006130 PMCID: PMC9416723 DOI: 10.3390/toxics10080451] [Citation(s) in RCA: 8] [Impact Index Per Article: 4.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Track Full Text] [Download PDF] [Figures] [Subscribe] [Scholar Register] [Received: 07/04/2022] [Revised: 07/29/2022] [Accepted: 08/01/2022] [Indexed: 12/04/2022]
Abstract
Pyrethroids are a major insecticide class, suitable for biomonitoring in humans. Due to similarities in structure and metabolic pathways, urinary metabolites are common to various active substances. A tiered approach is proposed for risk assessment. Tier I was a conservative screening for overall pyrethroid exposure, based on phenoxybenzoic acid metabolites. Subsequently, probabilistic approaches and more specific metabolites were used for refining the risk estimates. Exposure was based on 95th percentiles from HBM4EU aligned studies (2014–2021) covering children in Belgium, Cyprus, France, Israel, Slovenia, and The Netherlands and adults in France, Germany, Israel, and Switzerland. In all children populations, the 95th percentiles for 3-phenoxybenzoic acid (3-PBA) exceeded the screening value. The probabilistic refinement quantified the risk level of the most exposed population (Belgium) at 2% or between 1–0.1% depending on the assumptions. In the substance specific assessments, the 95th percentiles of urinary concentrations in the aligned studies were well below the respective human biomonitoring guidance values (HBM-GVs). Both information sets were combined for refining the combined risk. Overall, the HBM data suggest a low health concern, at population level, related to pyrethroid exposure for the populations covered by the studies, even though a potential risk for highly exposed children cannot be completely excluded. The proposed tiered approach, including a screening step and several refinement options, seems to be a promising tool of scientific and regulatory value in future.
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Affiliation(s)
- Jose V. Tarazona
- European Food Safety Authority (EFSA), 43126 Parma, Italy
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain
- Correspondence: (J.V.T.); (T.S.)
| | - Irene Cattaneo
- European Food Safety Authority (EFSA), 43126 Parma, Italy
| | - Lars Niemann
- Department of Safety of Pesticides, German Federal Institute for Risk Assessment, 10589 Berlin, Germany
| | - Susana Pedraza-Diaz
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain
| | | | | | - Ana Cañas
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain
| | | | - Marta Esteban-López
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain
| | - Argelia Castaño
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain
| | - Teresa Borges
- General-Directorate of Health, Ministry of Health, 1049-005 Lisbon, Portugal
| | | | - Konstantinos C. Makris
- Cyprus International Institute for Environmental and Public Health, Cyprus University of Technology, Limassol 3036, Cyprus
| | - Ilse Ottenbros
- National Institute for Public Health and the Environment (RIVM), Antonie van Leeuwenhoeklaan 9, 3721 Bilthoven, The Netherlands
| | - Hans Mol
- Wageningen Food Safety Research (WFSR), 6700 Wageningen, The Netherlands
| | | | - Bert Morrens
- Department of Sociology, University of Antwerp, 2020 Antwerpen, Belgium
| | | | - Zohar Barnett-Itzhaki
- Ruppin Research Group in Environmental and Social Sustainability, Ruppin Academic Center, Emek Hefer 4025000, Israel
| | - Nicole Probst-Hensch
- Swiss Tropical and Public Health Institute, Kreuzstrasse 2, 4123 Allschwil, Switzerland
| | - Samuel Fuhrimann
- Swiss Tropical and Public Health Institute, Kreuzstrasse 2, 4123 Allschwil, Switzerland
| | - Janja Snoj Tratnik
- Jozef Stefan Institute, Department of Environmental Sciences, 1000 Jubljana, Slovenia
| | - Milena Horvat
- Jozef Stefan Institute, Department of Environmental Sciences, 1000 Jubljana, Slovenia
| | - Loic Rambaud
- Department of Environmental and Occupational Health, Santé Publique France, 12 rue du Val d’Osne, Saint-Maurice, CEDEX, 94415 Paris, France
| | - Margaux Riou
- Department of Environmental and Occupational Health, Santé Publique France, 12 rue du Val d’Osne, Saint-Maurice, CEDEX, 94415 Paris, France
| | - Greet Schoeters
- VITO Health, Flemish Institute for Technological Research (VITO), 2020 Mol, Belgium
| | - Eva Govarts
- VITO Health, Flemish Institute for Technological Research (VITO), 2020 Mol, Belgium
| | | | - Till Weber
- German Environment Agency (UBA), 14195 Berlin, Germany
| | - Petra Apel
- German Environment Agency (UBA), 14195 Berlin, Germany
| | - Sonia Namorado
- Department of Epidemiology, National Institute of Health Dr. Ricardo Jorge, Avenida Padre Cruz, 1649-016 Lisbon, Portugal
| | - Tiina Santonen
- Finnish Institute of Occupational Health, Työterveyslaitos, P.O. Box 40, 00032 Helsinki, Finland
- Correspondence: (J.V.T.); (T.S.)
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8
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Tarazona JV, González-Caballero MDC, de Alba-Gonzalez M, Pedraza-Diaz S, Cañas A, Dominguez-Morueco N, Esteban-López M, Cattaneo I, Katsonouri A, Makris KC, Halldorsson TI, Olafsdottir K, Zock JP, Dias J, Decker AD, Morrens B, Berman T, Barnett-Itzhaki Z, Lindh C, Gilles L, Govarts E, Schoeters G, Weber T, Kolossa-Gehring M, Santonen T, Castaño A. Improving the Risk Assessment of Pesticides through the Integration of Human Biomonitoring and Food Monitoring Data: A Case Study for Chlorpyrifos. Toxics 2022; 10:toxics10060313. [PMID: 35736921 PMCID: PMC9228629 DOI: 10.3390/toxics10060313] [Citation(s) in RCA: 9] [Impact Index Per Article: 4.5] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Track Full Text] [Download PDF] [Figures] [Subscribe] [Scholar Register] [Received: 05/05/2022] [Revised: 05/26/2022] [Accepted: 05/30/2022] [Indexed: 02/05/2023]
Abstract
The risk assessment of pesticide residues in food is a key priority in the area of food safety. Most jurisdictions have implemented pre-marketing authorization processes, which are supported by prospective risk assessments. These prospective assessments estimate the expected residue levels in food combining results from residue trials, resembling the pesticide use patterns, with food consumption patterns, according to internationally agreed procedures. In addition, jurisdictions such as the European Union (EU) have implemented large monitoring programs, measuring actual pesticide residue levels in food, and are supporting large-scale human biomonitoring programs for confirming the actual exposure levels and potential risk for consumers. The organophosphate insecticide chlorpyrifos offers an interesting case study, as in the last decade, its acceptable daily intake (ADI) has been reduced several times following risk assessments by the European Food Safety Authority (EFSA). This process has been linked to significant reductions in the use authorized in the EU, reducing consumers’ exposure progressively, until the final ban in 2020, accompanied by setting all EU maximum residue levels (MRL) in food at the default value of 0.01 mg/kg. We present a comparison of estimates of the consumer’s internal exposure to chlorpyrifos based on the urinary marker 3,5,6-trichloro-2-pyridinol (TCPy), using two sources of monitoring data: monitoring of the food chain from the EU program and biomonitoring of European citizens from the HB4EU project, supported by a literature search. Both methods confirmed a drastic reduction in exposure levels from 2016 onwards. The margin of exposure approach is then used for conducting retrospective risk assessments at different time points, considering the evolution of our understanding of chlorpyrifos toxicity, as well as of exposure levels in EU consumers following the regulatory decisions. Concerns are presented using a color code, and have been identified for almost all studies, particularly for the highest exposed group, but at different levels, reaching the maximum level, red code, for children in Cyprus and Israel. The assessment uncertainties are highlighted and integrated in the identification of levels of concern.
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Affiliation(s)
- Jose V. Tarazona
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain; (M.d.C.G.-C.); (M.d.A.-G.); (S.P.-D.); (A.C.); (N.D.-M.); (M.E.-L.)
- European Food Safety Authority (EFSA), I-43126 Parma, Italy;
- Correspondence: (J.V.T.); (A.C.)
| | - Maria del Carmen González-Caballero
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain; (M.d.C.G.-C.); (M.d.A.-G.); (S.P.-D.); (A.C.); (N.D.-M.); (M.E.-L.)
| | - Mercedes de Alba-Gonzalez
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain; (M.d.C.G.-C.); (M.d.A.-G.); (S.P.-D.); (A.C.); (N.D.-M.); (M.E.-L.)
| | - Susana Pedraza-Diaz
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain; (M.d.C.G.-C.); (M.d.A.-G.); (S.P.-D.); (A.C.); (N.D.-M.); (M.E.-L.)
| | - Ana Cañas
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain; (M.d.C.G.-C.); (M.d.A.-G.); (S.P.-D.); (A.C.); (N.D.-M.); (M.E.-L.)
| | - Noelia Dominguez-Morueco
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain; (M.d.C.G.-C.); (M.d.A.-G.); (S.P.-D.); (A.C.); (N.D.-M.); (M.E.-L.)
| | - Marta Esteban-López
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain; (M.d.C.G.-C.); (M.d.A.-G.); (S.P.-D.); (A.C.); (N.D.-M.); (M.E.-L.)
| | - Irene Cattaneo
- European Food Safety Authority (EFSA), I-43126 Parma, Italy;
| | | | - Konstantinos C. Makris
- Cyprus International Institute for Environmental and Public Health, Cyprus University of Technology, Limassol 3036, Cyprus;
| | - Thorhallur I. Halldorsson
- Faculty of Food Science and Nutrition, School of Health Sciences, University of Iceland, 102 Reykjavik, Iceland;
- Department of Epidemiology Research, Statens Serum Institut, DK-2300 Copenhagen, Denmark
| | - Kristin Olafsdottir
- Department of Pharmacology and Toxicology, University of Iceland, 107 Reykjavik, Iceland;
| | - Jan-Paul Zock
- National Institute for Public Health and the Environment (RIVM), Bilthoven, 3720 BA De Bilt, The Netherlands;
| | - Jonatan Dias
- Wageningen Food Safety Research (WFSR), 6700 AE Wageningen, The Netherlands;
| | | | - Bert Morrens
- Department of Sociology, University of Antwerp, 2020 Antwerpen, Belgium;
| | - Tamar Berman
- Ministry of Health, Jerusalem 9446724, Israel; (T.B.); (Z.B.-I.)
| | - Zohar Barnett-Itzhaki
- Ministry of Health, Jerusalem 9446724, Israel; (T.B.); (Z.B.-I.)
- Ruppin Research Group in Environmental and Social Sustainability, Ruppin Academic Center, Emek Hefer 4025000, Israel
| | - Christian Lindh
- Division of Occupational and Environmental Medicine, Institute of Laboratory Medicine, Lund University, 22363 Lund, Sweden;
| | - Liese Gilles
- VITO Health, Flemish Institute for Technological Research (VITO), 2400 Mol, Belgium; (L.G.); (E.G.); (G.S.)
| | - Eva Govarts
- VITO Health, Flemish Institute for Technological Research (VITO), 2400 Mol, Belgium; (L.G.); (E.G.); (G.S.)
| | - Greet Schoeters
- VITO Health, Flemish Institute for Technological Research (VITO), 2400 Mol, Belgium; (L.G.); (E.G.); (G.S.)
- Department of Biomedical Sciences, University of Antwerp, 2020 Antwerp, Belgium
| | - Till Weber
- German Environment Agency (UBA), 14195 Berlin, Germany; (T.W.); (M.K.-G.)
| | | | - Tiina Santonen
- Finnish Institute of Occupational Health, P.O. Box 40 Helsinki, Finland;
| | - Argelia Castaño
- National Centre for Environmental Health, Instituto de Salud Carlos III, 28220 Madrid, Spain; (M.d.C.G.-C.); (M.d.A.-G.); (S.P.-D.); (A.C.); (N.D.-M.); (M.E.-L.)
- Correspondence: (J.V.T.); (A.C.)
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9
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Regidor-Cerrillo J, Pedraza-Diaz S, Rojo-Montejo S, Vazquez-Moreno E, Arnaiz I, Gomez-Bautista M, Jimenez-Palacios S, Ortega-Mora L, Collantes-Fernandez E. Neospora caninum infection in stray and farm dogs: Seroepidemiological study and oocyst shedding. Vet Parasitol 2010; 174:332-5. [DOI: 10.1016/j.vetpar.2010.08.033] [Citation(s) in RCA: 9] [Impact Index Per Article: 0.6] [Reference Citation Analysis] [What about the content of this article? (0)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 05/18/2010] [Revised: 08/13/2010] [Accepted: 08/23/2010] [Indexed: 10/19/2022]
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10
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Price TS, Regan R, Mott R, Hedman Å, Honey B, Daniels RJ, Smith L, Greenfield A, Tiganescu A, Buckle V, Ventress N, Ayyub H, Salhan A, Pedraza-Diaz S, Broxholme J, Ragoussis J, Higgs DR, Flint J, Knight SJL. SW-ARRAY: a dynamic programming solution for the identification of copy-number changes in genomic DNA using array comparative genome hybridization data. Nucleic Acids Res 2005; 33:3455-64. [PMID: 15961730 PMCID: PMC1151590 DOI: 10.1093/nar/gki643] [Citation(s) in RCA: 79] [Impact Index Per Article: 4.2] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Grants] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/17/2022] Open
Abstract
Comparative genome hybridization (CGH) to DNA microarrays (array CGH) is a technique capable of detecting deletions and duplications in genomes at high resolution. However, array CGH studies of the human genome noting false negative and false positive results using large insert clones as probes have raised important concerns regarding the suitability of this approach for clinical diagnostic applications. Here, we adapt the Smith–Waterman dynamic-programming algorithm to provide a sensitive and robust analytic approach (SW-ARRAY) for detecting copy-number changes in array CGH data. In a blind series of hybridizations to arrays consisting of the entire tiling path for the terminal 2 Mb of human chromosome 16p, the method identified all monosomies between 267 and 1567 kb with a high degree of statistical significance and accurately located the boundaries of deletions in the range 267–1052 kb. The approach is unique in offering both a nonparametric segmentation procedure and a nonparametric test of significance. It is scalable and well-suited to high resolution whole genome array CGH studies that use array probes derived from large insert clones as well as PCR products and oligonucleotides.
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Affiliation(s)
- Thomas S. Price
- The Wellcome Trust Centre for Human Genetics, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
| | - Regina Regan
- Oxford Genetics Knowledge Park, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
| | - Richard Mott
- The Wellcome Trust Centre for Human Genetics, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
| | - Åsa Hedman
- The Wellcome Trust Centre for Human Genetics, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
| | - Ben Honey
- Oxford Genetics Knowledge Park, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
| | - Rachael J. Daniels
- Weatherall Institute of Molecular Medicine, John Radcliffe HospitalHeadley Way, Headington, Oxford OX3 9DS, UK
| | - Lee Smith
- Mammalian Genetics Unit, Medical Research CouncilHarwell, Didcot, OX11 0RD, UK
| | - Andy Greenfield
- Mammalian Genetics Unit, Medical Research CouncilHarwell, Didcot, OX11 0RD, UK
| | - Ana Tiganescu
- The Wellcome Trust Centre for Human Genetics, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
| | - Veronica Buckle
- Weatherall Institute of Molecular Medicine, John Radcliffe HospitalHeadley Way, Headington, Oxford OX3 9DS, UK
| | - Nicki Ventress
- Weatherall Institute of Molecular Medicine, John Radcliffe HospitalHeadley Way, Headington, Oxford OX3 9DS, UK
| | - Helena Ayyub
- Weatherall Institute of Molecular Medicine, John Radcliffe HospitalHeadley Way, Headington, Oxford OX3 9DS, UK
| | - Anita Salhan
- The Wellcome Trust Centre for Human Genetics, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
| | - Susana Pedraza-Diaz
- The Wellcome Trust Centre for Human Genetics, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
| | - John Broxholme
- The Wellcome Trust Centre for Human Genetics, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
| | - Jiannis Ragoussis
- The Wellcome Trust Centre for Human Genetics, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
| | - Douglas R. Higgs
- Weatherall Institute of Molecular Medicine, John Radcliffe HospitalHeadley Way, Headington, Oxford OX3 9DS, UK
| | - Jonathan Flint
- The Wellcome Trust Centre for Human Genetics, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
| | - Samantha J. L. Knight
- The Wellcome Trust Centre for Human Genetics, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
- Oxford Genetics Knowledge Park, Roosevelt Drive, Churchill HospitalHeadington, Oxford OX3 7BN, UK
- To whom correspondence should be addressed at The Wellcome Trust Centre for Human Genetics, Roosevelt Drive, Churchill Hospital, Headington, Oxford OX3 7BN, UK. Tel: +44 1865 287511; Fax: +44 1865 287501;
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12
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Laustsen PG, Rasmussen TE, Petersen K, Pedraza-Diaz S, Moestrup SK, Gliemann J, Sottrup-Jensen L, Kristensen T. The complete amino acid sequence of human placental oxytocinase. Biochim Biophys Acta 1997; 1352:1-7. [PMID: 9177475 DOI: 10.1016/s0167-4781(97)00036-5] [Citation(s) in RCA: 48] [Impact Index Per Article: 1.8] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 02/04/2023]
Abstract
The complete amino acid sequence of human placental oxytocinase (placental leucine aminopeptidase) has been determined by cDNA cloning and sequencing. Oxytocinase is a type II integral membrane protein of 1025 amino acid residues, consisting of an acidic intracellular region of 110 amino acids followed by a hydrophobic transmembrane segment of 22 residues and 893 extracellular residues containing the characteristic Zn2+ coordination sequence element His-Glu-Xaa-Xaa-His-(18 residues)-Glu found in gluzincins. Two sets of cDNA clones with different 5'-ends were isolated and suggested to represent different spliced products of 3.6 kb (mature mRNA) and 12 kb, respectively. Oxytocinase mRNA is present in large amounts in placenta, heart and skeletal muscle and in small amounts in brain, kidney, liver and pancreas. A conserved sequence element, the GAMEN motif, which distinguishes the aminopeptidase family among gluzincins from other gluzincins, has been identified.
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Affiliation(s)
- P G Laustsen
- Department of Molecular and Structural Biology, Aarhus University, Denmark
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