Toxicological and Health Aspects of Bisphenol A

Total Page:16

File Type:pdf, Size:1020Kb

Toxicological and Health Aspects of Bisphenol A Toxicological and Health Aspects of Bisphenol A Report of Joint FAO/WHO Expert Meeting 2–5 November 2010 and Report of Stakeholder Meeting on Bisphenol A 1 November 2010 Ottawa, Canada Food and Agriculture Organization of the United Nations WHO Library Cataloguing-in-Publication Data Joint FAO/WHO expert meeting to review toxicological and health aspects of bisphenol A: final report, including report of stakeholder meeting on bisphenol A, 1-5 November 2010, Ottawa, Canada. 1.Phenols - toxicity. 2.Food contamination. 3.Food packing. I.World Health Organization. II.Food and Agriculture Organization of the United Nations. ISBN 978 92 14 156427 4 (NLM classification: QV 223) © World Health Organization 2011 All rights reserved. Publications of the World Health Organization are available on the WHO web site (www.who.int) or can be purchased from WHO Press, World Health Organization, 20 Avenue Appia, 1211 Geneva 27, Switzerland (tel.: +41 22 791 3264; fax: +41 22 791 4857; e-mail: [email protected]). Requests for permission to reproduce or translate WHO publications – whether for sale or for noncommercial distribution – should be addressed to WHO Press through the WHO web site (http://www.who.int/about/licensing/copyright_form/en/index.html). The designations employed and the presentation of the material in this publication do not imply the expression of any opinion whatsoever on the part of the World Health Organization concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. Dotted lines on maps represent approximate border lines for which there may not yet be full agreement. The mention of specific companies or of certain manufacturers’ products does not imply that they are endorsed or recommended by the World Health Organization in preference to others of a similar nature that are not mentioned. Errors and omissions excepted, the names of proprietary products are distinguished by initial capital letters. All reasonable precautions have been taken by the World Health Organization to verify the information contained in this publication. However, the published material is being distributed without warranty of any kind, either expressed or implied. The responsibility for the interpretation and use of the material lies with the reader. In no event shall the World Health Organization be liable for damages arising from its use. Typeset in Switzerland Printed in Switzerland Toxicological and Health Aspects of Bisphenol A Report of Joint FAO/WHO Expert Meeting 2–5 November 2010 and Report of Stakeholder Meeting on Bisphenol A 1 November 2010 Ottawa, Canada Food and Agriculture Organization of the United Nations TAble of contents Acknowledgements _________________________________________________________________________ 5 List of acronyms and abbreviations _____________________________________________________________ 6 Executive summary _________________________________________________________________________ 7 Introduction ______________________________________________________________________________ 14 Declarations of interests ____________________________________________________________________ 16 Summary, conclusions and recommendations ___________________________________________________ 17 1. Analytical methods for the determination of BPA in food and biological samples ___________________________ 17 2. Sources and occurrence of BPA _____________________________________________________________ 18 3. Exposure assessment _____________________________________________________________________ 20 3.1 National estimates of exposure __________________________________________________________ 20 3.2 International estimates of exposure _______________________________________________________ 20 3.2.1 Potential dietary exposure for infants 0–6 months of age ___________________________________ 22 3.2.2 Potential dietary exposure for infants 6–36 months of age __________________________________ 23 3.2.3 Potential dietary exposure for children over 3 years of age _________________________________ 23 3.2.4 Potential dietary exposure for adults (including pregnant women) ____________________________ 24 3.3 Exposure from non-food sources _________________________________________________________ 24 3.4 Conclusions and data gaps _____________________________________________________________ 25 4. Metabolism and toxicokinetics _______________________________________________________________ 26 5. Biological activities of BPA __________________________________________________________________ 28 6. Human data ____________________________________________________________________________ 29 6.1 Biomonitoring data ___________________________________________________________________ 29 6.2 Epidemiological studies _______________________________________________________________ 31 6.2.1 Reproductive end-points __________________________________________________________ 32 6.2.1.1 Semen quality _____________________________________________________________ 32 6.2.1.2 Ovarian response ___________________________________________________________ 32 6.2.2 Puberty _______________________________________________________________________ 33 6.2.3 Growth and neurodevelopment _____________________________________________________ 33 6.2.4 Cardiovascular disease and diabetes _________________________________________________ 34 7. Toxicology ______________________________________________________________________________ 34 7.1 Acute and repeated-dose toxicity _________________________________________________________ 34 7.2 Genotoxicity ________________________________________________________________________ 35 7.3 Carcinogenicity _____________________________________________________________________ 35 7.4 Reproductive and developmental toxicity of BPA in mammalian species _____________________________ 36 7.5 Neurobehavioural, neurotoxic and neuroendocrine effects _______________________________________ 38 7.6 Other effects _______________________________________________________________________ 40 7.6.1 Immunotoxicity _________________________________________________________________ 40 7.6.2 Cardiovascular effects ___________________________________________________________ 40 7.6.3 Metabolic disorders _____________________________________________________________ 41 8. Risk characterization ______________________________________________________________________ 42 8.1 Exposure assessment _________________________________________________________________ 42 8.2 Hazard characterization _______________________________________________________________ 44 8.3 Conclusion _________________________________________________________________________ 45 9. Alternative materials ______________________________________________________________________ 46 References _______________________________________________________________________________ 47 Annex 1 List of participants _________________________________________________________________ 53 Annex 2 Agenda __________________________________________________________________________ 55 Annex 3 Report of Stakeholder Meeting on Bisphenol A ____________________________________________ 56 Acknowledgements The World Health Organization and the Food and Agriculture Organization of the United Nations gratefully acknowledge the contributions of the participants at the Expert Meeting (listed in Annex 1) as well as the authors of the background papers published electronically in addition to this report (http://www.who.int/ foodsafety/chem/chemicals/bisphenol/en/) to provide more detailed information. The financial support of the European Food Safety Authority, Health Canada, the United States National Institute of Environmental Health Sciences and the United States Food and Drug Administration is gratefully acknowledged. The World Health Organization and the Food and Agriculture Organization of the United Nations wish to thank Dr Ouahiba Laribi, working as a volunteer at the World Health Organization, for the significant work performed in the preparation of this meeting. The organizations also wish to thank Ms Marla Sheffer for her assistance in the preparation of this report. LIst of acronyms and abbreviations AC50 half-maximal activity concentration BASC-2 Behavioural Assessment System for Children-2 BMD benchmark dose BMDL 95% lower limit on the benchmark dose BMDL10 95% lower limit on the benchmark dose for a 10% response BMI body mass index BPA bisphenol A BRIEF-P Behavior Rating Inventory of Executive Function (Preschool Version) bw body weight CVD cardiovascular disease CYP cytochrome P450 DES diethylstilbestrol DMBA 7,12-dimethylbenz[a]anthracene DNA deoxyribonucleic acid ELISA enzyme-linked immunosorbent assay ESR1 estrogen receptor 1 F1 first filial generation FAO Food and Agriculture Organization of the United Nations GD gestation day HPG hypothalamic–pituitary–gonadal IUPAC International Union of Pure and Applied Chemistry JECFA Joint FAO/WHO Expert Committee on Food Additives LOAEL lowest-observed-adverse-effect level LOEC lowest-observed-effect concentration MS mass spectrometry MS/MS tandem mass spectrometry NHANES National Health and Nutrition Examination Survey (USA) NOAEL no-observed-adverse-effect level NTP National Toxicology Program (USA) P0 first parental generation PBPK physiologically based pharmacokinetic PC polycarbonate PND postnatal day PVC polyvinyl chloride USA United States of America USEPA United States Environmental Protection Agency
Recommended publications
  • Characterization of an Abiraterone Ultraresponsive Phenotype in Castration-Resistant
    Author Manuscript Published OnlineFirst on December 19, 2016; DOI: 10.1158/1078-0432.CCR-16-2054 Author manuscripts have been peer reviewed and accepted for publication but have not yet been edited. 1 Characterization of an Abiraterone Ultraresponsive Phenotype in Castration-Resistant 2 Prostate Cancer Patient-Derived Xenografts 3 4 Hung-Ming Lam1,2*, Ryan McMullin3*†, Holly M. Nguyen1, Ilsa Coleman4, Michael Gormley5, 5 Roman Gulati4, Lisha G. Brown1, Sarah K. Holt1, Weimin Li5, Deborah S. Ricci6, Karin 6 Verstraeten7, Shibu Thomas5, Elahe A. Mostaghel4, 8, Peter S. Nelson4, 8, Robert L. Vessella1, 7 9, and Eva Corey1 8 9 Affiliation of authors: 1Department of Urology, University of Washington School of 10 Medicine, Seattle, Washington; 2State Key Laboratory of Quality Research in Chinese 11 Medicine, Macau Institute for Applied Research in Medicine and Health, Macau University of 12 Science and Technology, Macau (SAR), China; 3LabConnect, Seattle, Washington; 4Fred 13 Hutchinson Cancer Research Center, Seattle, Washington; 5Janssen Research & 14 Development, Spring House, Pennsylvania; 6Janssen Research & Development, Raritan, 15 New Jersey; 7Janssen Research & Development, Beerse, Belgium; 8Department of 16 Medicine, University of Washington, Seattle, Washington; 9Department of Veterans Affairs 17 Medical Center, Seattle, Washington 18 19 *Co-primary lead authors 20 †Current affiliation: Janssen Research & Development, Spring House, Pennsylvania 21 22 23 Running title (60 characters max): Abiraterone Response and Resistance 24 25 Keywords: abiraterone acetate, prostate cancer, xenografts, biomarkers, androgen 26 receptor, glucocorticoid receptor, castration resistance 27 28 Grant/funding support: The work was supported by The Richard M. Lucas Foundation, the 29 Prostate Cancer Foundation, SU2C, a NIH PO1 CA085859, and the PNW Prostate Cancer 1 Downloaded from clincancerres.aacrjournals.org on September 23, 2021.
    [Show full text]
  • Pesticides Reduce Symbiotic Efficiency of Nitrogen-Fixing Rhizobia and Host Plants
    Pesticides reduce symbiotic efficiency of nitrogen-fixing rhizobia and host plants Jennifer E. Fox*†, Jay Gulledge‡, Erika Engelhaupt§, Matthew E. Burow†¶, and John A. McLachlan†ʈ *Center for Ecology and Evolutionary Biology, University of Oregon, 335 Pacific Hall, Eugene, OR 97403; †Center for Bioenvironmental Research, Environmental Endocrinology Laboratory, Tulane University, 1430 Tulane Avenue, New Orleans, LA 70112-2699; ‡Department of Biology, University of Louisville, Louisville, KY 40292 ; §University of Colorado, Boulder, CO 80309; and ¶Department of Medicine and Surgery, Hematology and Medical Oncology Section, Tulane University Medical School, 1430 Tulane Avenue, New Orleans, LA 70112-2699 Edited by Christopher B. Field, Carnegie Institution of Washington, Stanford, CA, and approved May 8, 2007 (received for review January 8, 2007) Unprecedented agricultural intensification and increased crop by plants, in rotation with non-N-fixing crops (8, 15). The yield will be necessary to feed the burgeoning world population, effectiveness of this strategy relies on maximizing symbiotic N whose global food demand is projected to double in the next 50 fixation (SNF) and plant yield to resupply organic and inorganic years. Although grain production has doubled in the past four N and nutrients to the soil. The vast majority of biologically fixed decades, largely because of the widespread use of synthetic N is attributable to symbioses between leguminous plants (soy- nitrogenous fertilizers, pesticides, and irrigation promoted by the bean, alfalfa, etc.) and species of Rhizobium bacteria; replacing ‘‘Green Revolution,’’ this rate of increased agricultural output is this natural fertilizer source with synthetic N fertilizer would cost unsustainable because of declining crop yields and environmental Ϸ$10 billion annually (16, 17).
    [Show full text]
  • OECD Conceptual Framework for Testing and Assessment of Endocrine Disrupters As a Basis for Regulation of Substances with Endocrine Disrupting Properties
    OECDOECD ConceptualConceptual FrameworkFramework for forTesting Testing and and Assessment Assessment of Endocrineof EndocrineDisrupters Disruptersas a basis asfor aregulation basis of forsubstances regulation with of substances endocrine disrupting with endocrineproperties disrupting properties Ulla Hass, Majken Dalgaard, Kirsten Jarfelt and Thuri S.A. Kledal Department of Toxicology and Risk Assessment, Danish Institute for Food and Veterinary Research, Denmark TemaNord 2004:555 OECD Conceptual Framework for Testing and Assessment of Endocrine Disrupters as a basis for regulation of substances with endocrine disrupting properties TemaNord 2004:555 © Nordic Council of Ministers, Copenhagen 2004 ISBN 92-893-1073-1 ISSN 0908-6692 Nordic Council of Ministers Nordic Council Store Strandstræde 18 Store Strandstræde 18 DK-1255 Copenhagen K DK-1255 Copenhagen K Phone (+45) 3396 0200 Phone (+45) 3396 0400 Fax (+45) 3396 0202 Fax (+45) 3311 1870 www.norden.org Nordic Environmental Co-operation Environmental co-operation is aimed at contributing to the improvement of the environment and forestall problems in the Nordic countries as well as on the international scene. The co- operation is conducted by the Nordic Committee of Senior Officials for Environmental Affairs. The co-operation endeavours to advance joint aims for Action Plans and joint projects, exchange of information and assistance, e.g. to Eastern Europe, through the Nordic Environmental Finance Corporation (NEFCO). The Nordic Council of Ministers was established in 1971. It submits proposals on co-operation between the governments of the five Nordic countries to the Nordic Council, implements the Council's recommendations and reports on results, while directing the work carried out in the targeted areas. The Prime Ministers of the five Nordic countries assume overall responsibility for the co-operation measures, which are co-ordinated by the ministers for co-operation and the Nordic Co-operation committee.
    [Show full text]
  • Fighting Bisphenol A-Induced Male Infertility: the Power of Antioxidants
    antioxidants Review Fighting Bisphenol A-Induced Male Infertility: The Power of Antioxidants Joana Santiago 1 , Joana V. Silva 1,2,3 , Manuel A. S. Santos 1 and Margarida Fardilha 1,* 1 Department of Medical Sciences, Institute of Biomedicine-iBiMED, University of Aveiro, 3810-193 Aveiro, Portugal; [email protected] (J.S.); [email protected] (J.V.S.); [email protected] (M.A.S.S.) 2 Institute for Innovation and Health Research (I3S), University of Porto, 4200-135 Porto, Portugal 3 Unit for Multidisciplinary Research in Biomedicine, Institute of Biomedical Sciences Abel Salazar, University of Porto, 4050-313 Porto, Portugal * Correspondence: [email protected]; Tel.: +351-234-247-240 Abstract: Bisphenol A (BPA), a well-known endocrine disruptor present in epoxy resins and poly- carbonate plastics, negatively disturbs the male reproductive system affecting male fertility. In vivo studies showed that BPA exposure has deleterious effects on spermatogenesis by disturbing the hypothalamic–pituitary–gonadal axis and inducing oxidative stress in testis. This compound seems to disrupt hormone signalling even at low concentrations, modifying the levels of inhibin B, oestra- diol, and testosterone. The adverse effects on seminal parameters are mainly supported by studies based on urinary BPA concentration, showing a negative association between BPA levels and sperm concentration, motility, and sperm DNA damage. Recent studies explored potential approaches to treat or prevent BPA-induced testicular toxicity and male infertility. Since the effect of BPA on testicular cells and spermatozoa is associated with an increased production of reactive oxygen species, most of the pharmacological approaches are based on the use of natural or synthetic antioxidants.
    [Show full text]
  • Toxicological Profile for Bisphenol A
    TT TOXICOLOGICAL PROFILE FOR BISPHENOL A September 2009 Integrated Risk Assessment Branch Office of Environmental Health Hazard Assessment California Environmental Protection Agency Toxicological Profile for Bisphenol A September 2009 Prepared by Office of Environmental Health Hazard Assessment Prepared for Ocean Protection Council Under an Interagency Agreement, Number 07-055, with the State Coastal Conservancy LIST OF CONTRIBUTORS Authors Jim Carlisle, D.V.M., Ph.D., Senior Toxicologist, Integrated Risk Assessment Branch Dave Chan, D. Env., Staff Toxicologist, Integrated Risk Assessment Branch Mari Golub, Ph.D., Staff Toxicologist, Reproductive and Cancer Hazard Assessment Branch Sarah Henkel, Ph.D., California Sea Grant Fellow, California Ocean Science Trust Page Painter, M.D., Ph.D., Senior Toxicologist, Integrated Risk Assessment Branch K. Lily Wu, Ph.D., Associate Toxicologist, Reproductive and Cancer Hazard Assessment Branch Reviewers David Siegel, Ph.D., Chief, Integrated Risk Assessment Branch i Table of Contents Executive Summary ................................................................................................................................ iv Use and Exposure ............................................................................................................................... iv Environmental Occurrence ................................................................................................................. iv Effects on Aquatic Life ......................................................................................................................
    [Show full text]
  • Polystyrene Microplastics Do Not Affect Juvenile Brown Trout (Salmo Trutta F
    Schmieg et al. Environ Sci Eur (2020) 32:49 https://doi.org/10.1186/s12302-020-00327-4 RESEARCH Open Access Polystyrene microplastics do not afect juvenile brown trout (Salmo trutta f. fario) or modulate efects of the pesticide methiocarb Hannah Schmieg1*, Sven Huppertsberg2, Thomas P. Knepper2, Stefanie Krais1, Katharina Reitter1, Felizitas Rezbach1, Aki S. Ruhl3,4, Heinz‑R. Köhler1 and Rita Triebskorn1,5 Abstract Background: There has been a rising interest within the scientifc community and the public about the environmen‑ tal risk related to the abundance of microplastics in aquatic environments. Up to now, however, scientifc knowledge in this context has been scarce and insufcient for a reliable risk assessment. To remedy this scarcity of data, we inves‑ tigated possible adverse efects of polystyrene particles (10 4 particles/L) and the pesticide methiocarb (1 mg/L) in juvenile brown trout (Salmo trutta f. fario) both by themselves as well as in combination after a 96 h laboratory expo‑ sure. PS beads (density 1.05 g/mL) were cryogenically milled and fractionated resulting in irregular‑shaped particles (< 50 µm). Besides body weight of the animals, biomarkers for proteotoxicity (stress protein family Hsp70), oxidative stress (superoxide dismutase, lipid peroxidation), and neurotoxicity (acetylcholinesterase, carboxylesterases) were analyzed. As an indicator of overall health, histopathological efects were studied in liver and gills of exposed fsh. Results: Polystyrene particles by themselves did not infuence any of the investigated biomarkers. In contrast, the exposure to methiocarb led to a signifcant reduction of the activity of acetylcholinesterase and the two carboxy‑ lesterases. Moreover, the tissue integrity of liver and gills was impaired by the pesticide.
    [Show full text]
  • Estrogen-Like Effect of Mitotane Explained by Its Agonist Activity on Estrogen Receptor-Α
    biomedicines Article Estrogen-Like Effect of Mitotane Explained by Its Agonist Activity on Estrogen Receptor-α Elisa Rossini 1,†, Edoardo Giacopuzzi 2,3,† , Fabrizio Gangemi 4,† , Mariangela Tamburello 1, Deborah Cosentini 5, Andrea Abate 1, Marta Laganà 5, Alfredo Berruti 5 , Salvatore Grisanti 5,‡ and Sandra Sigala 1,*,‡ 1 Section of Pharmacology, Department of Molecular and Translational Medicine, University of Brescia, 25123 Brescia, Italy; [email protected] (E.R.); [email protected] (M.T.); [email protected] (A.A.) 2 Wellcome Centre for Human Genetics, University of Oxford, Oxford OX3 7BN, UK; [email protected] 3 National Institute for Health Research Oxford Biomedical Research Centre, Oxford OX4 2PG, UK 4 Unit of Physics, Department of Molecular and Translational Medicine, University of Brescia, 25123 Brescia, Italy; [email protected] 5 Medical Oncology Unit, Department of Medical and Surgical Specialties, Radiological Sciences, and Public Health, University of Brescia at A.S.S.T. Spedali Civili di Brescia, 25123 Brescia, Italy; [email protected] (D.C.); [email protected] (M.L.); [email protected] (A.B.); [email protected] (S.G.) * Correspondence: [email protected] † These Authors equally contributed to this paper. ‡ These authors are co-senior authors of this paper. Citation: Rossini, E.; Giacopuzzi, E.; Abstract: Mitotane is the cornerstone of medical treatment of adrenocortical carcinoma. Estrogenic- Gangemi, F.; Tamburello, M.; like side effects frequently occur in patients, and previous studies explored the chemical nature Cosentini, D.; Abate, A.; Laganà, M.; of the interaction between estrogen receptor-α (ER-α) and toxic compounds, including the DDD Berruti, A.; Grisanti, S.; Sigala, S.
    [Show full text]
  • Abiraterone and MDV3100 Inhibits the Proliferation and Promotes The
    Han et al. Cancer Cell Int (2019) 19:332 https://doi.org/10.1186/s12935-019-1021-9 Cancer Cell International PRIMARY RESEARCH Open Access Abiraterone and MDV3100 inhibits the proliferation and promotes the apoptosis of prostate cancer cells through mitophagy Jingli Han1† , Junhua Zhang1†, Wei Zhang2, Dalei Zhang3, Ying Li1, Jinsong Zhang2, Yaqun Zhang3, Tongxiang Diao3, Luwei Cui3, Wenqing Li1, Fei Xiao1,2,4, Ming Liu3* and Lihui Zou1* Abstract Background: Abiraterone and MDV3100 are two efective anticancer agents for prostate cancer, however, the mechanism of their downstream action remains undefned. Methods: A dual fuorescent biosensor plasmid was transfected in LNCaP cells to measure mitophagy. The DNA of LNCaP cells was extracted and performed with quantitative real-time PCR to detect mitochondrial DNA copy number. JC-1 staining was utilized to detect the mitochondrial membrane potential and electron microscope was performed to analyze mitochondrial morphology. Moreover, the protein levels of mitochondrial markers and apoptotic markers were detected by western blot. At last, the proliferation and apoptosis of LNCaP cells were analyzed with CCK-8 assay and fow cytometry after abiraterone or MDV3100 treatment. Results: Mitophagy was induced by abiraterone and MDV3100 in LNCaP cells. The low expression level of mito- chondrial DNA copy number and mitochondrial depolarization were further identifed in the abiraterone or MDV3100 treatment groups compared with the control group. Besides, severe mitochondria swelling and substantial autophagy-lysosomes were observed in abiraterone- and MDV3100-treated LNCaP cells. The expression of mito- chondria-related proteins, frataxin, ACO2 and Tom20 were signifcantly downregulated in abiraterone and MDV3100 treated LNCaP cells, whereas the expression level of inner membrane protein of mitochondria (Tim23) was signif- cantly upregulated in the same condition.
    [Show full text]
  • STATE of the ART ASSESSMENT of ENDOCRINE DISRUPTERS Final Report
    STATE OF THE ART ASSESSMENT OF ENDOCRINE DISRUPTERS Final Report Project Contract Number 070307/2009/550687/SER/D3 Authors: Andreas Kortenkamp, Olwenn Martin, Michael Faust, Richard Evans, Rebecca McKinlay, Frances Orton and Erika Rosivatz 23.12.2011 TABLE OF CONTENTS TABLE OF CONTENTS 0 EXECUTIVE SUMMARY ......................................................................................................................... 7 1 INTRODUCTION .................................................................................................................................... 9 1.1 TERMS OF REFERENCE, SCOPE OF THE REPORT ........................................................................... 9 1.2 STRUCTURE OF THE REPORT ....................................................................................................... 11 2 DEFINITION OF ENDOCRINE DISRUPTING CHEMICALS ...................................................................... 13 2.1 THE ENDOCRINE SYSTEM ............................................................................................................ 13 2.2 ADVERSITY ................................................................................................................................... 15 2.2.1 DEFINITION........................................................................................................................... 15 2.2.2 ASSAY REQUIREMENTS ........................................................................................................ 16 2.2.3 ECOTOXICOLOGICAL EFFECTS .............................................................................................
    [Show full text]
  • Exposure to Endocrine Disrupting Chemicals and Risk of Breast Cancer
    International Journal of Molecular Sciences Review Exposure to Endocrine Disrupting Chemicals and Risk of Breast Cancer Louisane Eve 1,2,3,4,Béatrice Fervers 5,6, Muriel Le Romancer 2,3,4,* and Nelly Etienne-Selloum 1,7,8,* 1 Faculté de Pharmacie, Université de Strasbourg, F-67000 Strasbourg, France; [email protected] 2 Université Claude Bernard Lyon 1, F-69000 Lyon, France 3 Inserm U1052, Centre de Recherche en Cancérologie de Lyon, F-69000 Lyon, France 4 CNRS UMR5286, Centre de Recherche en Cancérologie de Lyon, F-69000 Lyon, France 5 Centre de Lutte Contre le Cancer Léon-Bérard, F-69000 Lyon, France; [email protected] 6 Inserm UA08, Radiations, Défense, Santé, Environnement, Center Léon Bérard, F-69000 Lyon, France 7 Service de Pharmacie, Institut de Cancérologie Strasbourg Europe, F-67000 Strasbourg, France 8 CNRS UMR7021/Unistra, Laboratoire de Bioimagerie et Pathologies, Faculté de Pharmacie, Université de Strasbourg, F-67000 Strasbourg, France * Correspondence: [email protected] (M.L.R.); [email protected] (N.E.-S.); Tel.: +33-4-(78)-78-28-22 (M.L.R.); +33-3-(68)-85-43-28 (N.E.-S.) Received: 27 October 2020; Accepted: 25 November 2020; Published: 30 November 2020 Abstract: Breast cancer (BC) is the second most common cancer and the fifth deadliest in the world. Exposure to endocrine disrupting pollutants has been suggested to contribute to the increase in disease incidence. Indeed, a growing number of researchershave investigated the effects of widely used environmental chemicals with endocrine disrupting properties on BC development in experimental (in vitro and animal models) and epidemiological studies.
    [Show full text]
  • Bisphenol a (BPA) Description/Chemical Forms: Sources/Routes of Exposure: Health Effects
    Bisphenol A (BPA) Description/Chemical Forms: Sources/Routes of Exposure: Health Effects: BPA is a synthetic compound derived Sources: There are no natural sources of Animal studies have shown the ability of from diphenylmethane that is used to BPA and since this compound is used in this chemical to cause harmful make polycarbonate, a rigid plastic used polycarbonate production, it can be endocrine effects, including decreased in a variety of industrial and house-hold found in food can linings, plastic water sperm production/fertility, mammary products. It has been in production bottles, dental sealants, Tupperware, gland development, and lowered since the 1960s and is still used by many disposable food packages, medical antioxidant enzymes. In addition, early industries today. devices, ink on receipts, and some onset puberty, and behavioral changes, appliances. Also, landfill leachate can like aggression and hyperactivity can seep into waterways and adversely occur with exposure. affect aquatic species. Young children and infants may also be exposed Fetal exposure is also a concern due to through baby bottles and plastic food BPA crossing the placenta and causing containers. development effects both in the womb and later stages of life. Young children Main Route of Exposure: and infants may also be exposed through baby bottles and plastic food Ingestion-the chemical has been containers. shown to leach into foods and beverages that are stored with packaging containing BPA; fish and seafood due to biomagnification Bisphenol A (BPA) Diagnosis/Treatment Options: Prevention Strategies: Links for Additional Information: BPA is poorly soluble in water and is Advise patients to purchase BPA- More information concerning BPA therefore most effectively detected in free containers, especially baby exposure and health effects can be urine.
    [Show full text]
  • Influence of Occupational Exposure to Bisphenol a on the Sex Hormones of Male Epoxy Resin Painters
    Available online at www.tox.or.kr Influence of Occupational Exposure to Bisphenol A on the Sex Hormones of Male Epoxy Resin Painters Bong Suk Cha1, Sang Baek Koh2, Jun Ho Park2, BPA] is a monomer used in the production of poly- Aeyong Eom3, Kang Myeung Lee1 & carbonates and epoxy resins. The amount of BPA Hong Soon Choi4 used in the world is estimated at 3.7 million tons (2004) and is predicted to increase by 6 to 7% every 1 1Department of Preventive Medicine, Institute of Occupational year . Because products made from BPA are used and Environmental Medicine, Yonsei University Wonju widely in daily life, the general population’s exposure College of Medicine, Wonju, Gangwon 220-701, Korea is estimated to be 9 μg/kg/day of BPA2. Krishnan et 2Department of Preventive Medicine, Institute of Life Long Health, al.3 suggested weak estrogenic activity of BPA which Yonsei University Wonju College of Medicine, Wonju, has been demonstrated in a variety of assays. Cell Gangwon 220-701, Korea - 3 proliferation is induced within the MCF 7 cells and Department of Nursing, Margaret Prtchard University, Jeonju, stimulates the release of prolactin from the pituitary Jeonbuk 560-714, Korea 4 4 GH3 cells . The estrogenic potency of BPA is 1/15,000 Institute of Occupational and Environmental Health, β Kwandong University, Gangneung, Gangwon 210-701, Korea lower than 17 -estradiol and 1/10 lower than 4-nonyl- 5,6 Correspondence and requests for materials should be addressed phenol . The estrogenecity of BPA in vivo is deter- to J. H. Park ([email protected]) mined by the route of administration and oral bioavail- ability of BPA is low, and thus BPA glucuronide with- 7-9 Accepted 18 June 2008 out estrogenecity is formed intensively in the liver .
    [Show full text]