Guidance on Identifying Endocrine Disrupting Effects
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Recipe 2016 V1.1 a Harmonized Life Cycle Impact Assessment Method at Midpoint and Endpoint Level Report I: Characterization
ReCiPe 2016 v1.1 A harmonized life cycle impact assessment method at midpoint and endpoint level Report I: Characterization RIVM Report 2016-0104a RIVM Report 2016-0104 Colophon © RIVM 2017 Parts of this publication may be reproduced, provided acknowledgement is given to: National Institute for Public Health and the Environment, along with the title and year of publication. M.A.J. Huijbregts (author), Radboud University Nijmegen Z.J.N. Steinmann (author), Radboud University Nijmegen P.M.F. Elshout (author), Radboud University Nijmegen G. Stam (author), Radboud University Nijmegen F. Verones (author), NTNU Trondheim M.D.M. Vieira (author), Radboud University Nijmegen, Pré Consultants A. Hollander (author), RIVM M. Zijp (author), RIVM R. van Zelm (author), Radboud University Nijmegen Contact: Anne Hollander RIVM/DMG [email protected] This investigation has been performed by order and for the account of Ministerie IenM, within the framework of Van Afval naar Grondstof This is a publication of: National Institute for Public Health and the Environment P.O. Box 1 | 3720 BA Bilthoven The Netherlands www.rivm.nl/en Page 2 of 201 RIVM Report 2016-0104 Synopsis ReCiPe 2016 v1.1 A harmonized life cycle impact assessment method at midpoint and endpoint level Report I: Characterization Life cycle assessment (LCA) enables the assessment of the pressure a certain (production) process places on the environment. The assessment comprises all phases needed to produce and use a product, from the initial development to the treatment of waste (the total life cycle). The goal of LCA is, for example, to compare alternatives or to identify phases in the production process that place a relatively high level of pressure on the environment. -
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. -
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. -
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 ...................................................................................................................... -
Scientific Committee on Toxicity, Ecotoxicity and the Environment
EUROPEAN COMMISSION DIRECTORATE-GENERAL HEALTH AND CONSUMER PROTECTION Directorate C – Scientific Opinions on Health Matters Unit C2 – Management of Scientific Committees I Scientific Committee on Toxicity, Ecotoxicity and the Environment Brussels, C2/JCD/csteeop/Ter91100/D(0) SCIENTIFIC COMMITTEE ON TOXICITY, ECOTOXICITY AND THE ENVIRONMENT (CSTEE) Opinion on THE AVAILABLE SCIENTIFIC APPROACHES TO ASSESS THE POTENTIAL EFFECTS AND RISK OF CHEMICALS ON TERRESTRIAL ECOSYSTEMS Opinion expressed at the 19th CSTEE plenary meeting Brussels, 9 November 2000 CSTEE OPINION ON THE AVAILABLE SCIENTIFIC APPROACHES TO ASSESS THE POTENTIAL EFFECTS AND RISK OF CHEMICALS ON TERRESTRIAL ECOSYSTEMS FOREWORD AND SCOPE OF THIS DOCUMENT The concept "terrestrial environment" cannot be easily defined. It is characterised as the part of the biosphere that is not covered by water, less than one third of the total surface. From a geological viewpoint it just represents a thin line (a few meters wide) of the interface between both the solid (soil) and the gaseous (atmosphere) phases of the Earth, several orders of magnitude wider than this line. However, from the biological point of view, this thin line concentrates all non-aquatic living organisms, including human beings. Humans use the terrestrial environment for living and developing most of their activities, which include the commercial production of other species by agriculture and farming. Human activities deeply modify the terrestrial environment. Particularly in developed areas such as Europe, the landscape has been intensively modified by agricultural, mining, industrial and urban activities and only in a small proportion (mostly in extreme conditions such as high mountains, Northern latitudes, wetlands or semi-desert areas) of the European surface the landscape still resembles naive conditions. -
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. -
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 ............................................................................................. -
Persistent Organic Pollutants (Pops): State of the Science
Environmental Pollution 100 (1999) 209±221 www.elsevier.com/locate/envpol Persistent organic pollutants (POPs): state of the science K.C. Jones a,*, P. de Voogt b aEnvironmental Science Department, Institute of Environmental and Natural Sciences, Lancaster University, Lancaster, LA1 4YQ, UK bDepartment of Environmental and Toxicological Chemistry, Amsterdam Research Institute for Substances in Ecosystems (ARISE), University of Amsterdam, Nieuwe Achtergracht 166, 1018 WV Amsterdam, Netherlands Received 15 November 1998; accepted 22 March 1999 Abstract The environmental chemistry and ecotoxicology of persistent organic pollutants (POPs) are fascinating areas of scienti®c research. Our objective in this paper is to provide a brief, focussed overview of what constitutes a POP, highlight the harmful eects they may have on biota, make some comments on their environmental sources and analysis, their environmental trends and pro- cesses, their movement through foodchains and highlight some important regional-and global-scale environmental transport issues. Finally, we oer some personal thoughts on some current and future areas of scienti®c enquiry on POPs. # 1999 Elsevier Science Ltd. All rights reserved. Keywords: Persistent organic pollutant, POP; Sources; Air±surface exchange; Biota; Foodchains 1. What are Persistent Organic Pollutants (POPs) and They also partition into lipids in organisms rather than their properties? entering the aqueous milieu of cells and become stored in fatty tissue. This confers persistence on the chemical There are many thousands of POP chemicals, often in biota since metabolism is slow and POPs may there- coming from certain series or `families' of chemicals (e.g fore accumulate in foodchains. there are theoretically 209 dierent polychlorinated Importantly, POPs have the propensity to enter the biphenyls, diering from each other by level of chlor- gas phase under environmental temperatures. -
Benzyl Butyl Phthalate Or BBP)
Toxicity Review for Benzylnbutyl Phthalate (Benzyl Butyl Phthalate or BBP) Introduction Benzyl butyl phthalate (BBP) is a man‐made phthalate ester that is mostly used in vinyl tile (CERHR, 2003). BBP can also be found as a plasticizer in polyvinyl chloride (PVC) for the manufacturing of conveyor belts, carpet, weather stripping and more. It is also found in some vinyl gloves and adhesives. BBP is produced by the sequential reaction of butanol and benzyl chloride with phthalic anhydride (CERHR, 2003). The Monsanto Company is the only US producer of BBP (IPCS, 1999). When BBP is added during the manufacturing of a product, it is not bound to the final product. However, through the use and disposal of the product, BBP can be released into the environment. BBP can be deposited on and taken up by crops for human and livestock consumption, resulting in its entry into the food chain (CERHR, 2003). Concentrations of BBP have been found in ambient and indoor air, drinking water, and soil. However, the concentrations are low and intakes from these routes are considered negligible (IPCS, 1999). Exposure to BBP in the general population is based on food intake. Occupational exposure to BBP is possible through skin contact and inhalation, but data on BBP concentrations in the occupational environment is limited. Unlike some other phthalates, BBP is not approved by the U.S. Food and Drug Administration for use in medicine or medical devices (IPCS, 1999; CERHR, 2003). Based on the National Toxicology Program (NTP) bioassay reports of increased pancreatic lesions in male rats, a tolerable daily intake of 1300 µg/kg body weight per day (µg/kg‐d) has been calculated for BBP by the International Programme on Chemical Safety (IPCS) (IPCS, 1999). -
Leachate Ecotoxicity - Characterization and Risk Assessment
Leachate ecotoxicity - characterization and risk assessment Olof Berglund Chemical Ecology & Ecotoxicology Department of Ecology Lund University Leachate ecotoxicity • To compare toxic potency of different leachates, and effects of treatment methods - combine chemical and toxicological characterization • For environmental risk assessments -use ecotoxicological approaches with endpoints on population, community or ecosystem level Source • How do you estimate leachate toxicity? • How do you assess impact on recipient? Leachate Recipient • Chemical and toxicological characterization • Environmental risk assessments Landfill leachates • Complex mixture of organic and inorganic constituents • Characterization of leachates • Information needed for: – selection of treatment methods – risk assessments of landfill emissions Xenobiotic organic compounds Baun et al. 2004 Pesticides Phtalates Baun et al. 2004 What information? • Information on compounds present and concentrations • Limitations in traditional chemical analyses - time, money and detection limits • Biological effects - toxicity and environmental impact Leachate toxicity • To predict leachate toxicity both toxicological and chemical characterization required • Toxicological - we cannot analyze and detect everything • Chemical - toxicity tests do not reveal the identity of the potential problematic compounds Battery-of-tests approach Exposure Test Organism Endpoint time MicrotoxTM bacteria 15 min luminescence Selenastrum algae 96h growth mortality Daphnia zooplankton 48h (immobility) -
Toxicological Summary for Bisphenol a (PDF)
Health Based Guidance for Water Health Risk Assessment Unit, Environmental Health Division 651-201-4899 Adopted as Rule: November 2015 Toxicological Summary for: Bisphenol A CAS: 80-05-7 Synonyms: BPA; 4'-(1-Methylethylidene)bisphenol 4,4'-Bisphenol A; 4,4'- Isopropylidenediphenol; Phenol, 4,4'-(1-methylethylidene)bis- p,p'- isopropylidenebisphenol; 2,2-bis(4-hydroxyphenyl)propane Acute Non-Cancer Health Risk Limit (nHRLAcute) = Not Derived (Insufficient Data) Short-term Non-Cancer Health Risk Limit (nHRLShort-term) = 100 µg/L (Reference Dose, mg/kg/d) x (Relative Source Contribution) x (Conversion Factor) (Short-term intake rate, L/kg-d) = (0.16 mg/kg/d) x (0.2*) x (1000 µg/mg) (0.289 L/kg-d) = 111 rounded to 100 µg/L *MDH utilizes the EPA Exposure Decision Tree (EPA 2000) to select appropriate RSCs. Given the significant potential non- drinking water sources of exposure from multiple sources available for infants, an RSC of 0.2 is selected rather than the default value of 0.5 used for nonvolatile chemicals. Reference Dose/Concentration 0.16 mg/kg-d (rat) Source of toxicity value MDH, 2014 Point of Departure (POD): 2.7 mg/kg-d (NOAEL, Delclos et al. 2014) Human Equivalent Dose (MDH, 2011: 2.7 x 5.8 = 16 mg/kg-d [chemical-specific DAF for neonatal rats] Total uncertainty factor: 100 Uncertainty factor allocation 3 for interspecies differences (for toxicodynamics), 10 for intraspecies variability, and 3 for database uncertainty (additional studies to evaluate latent effects of early life exposure, neurobehavioral, immune system, and metabolic -
Assessment Report Triclosan Chemical Abstracts Service
Assessment Report Triclosan Chemical Abstracts Service Registry Number 3380-34-5 Environment and Climate Change Canada Health Canada November 2016 Assessment Report: Triclosan 2016-11-26 En14-259/2016E-PDF 978-0-660-05976-1 Information contained in this publication or product may be reproduced, in part or in whole, and by any means, for personal or public non-commercial purposes, without charge or further permission, unless otherwise specified. You are asked to: Exercise due diligence in ensuring the accuracy of the materials reproduced; Indicate both the complete title of the materials reproduced, as well as the author organization; and Indicate that the reproduction is a copy of an official work that is published by the Government of Canada and that the reproduction has not been produced in affiliation with or with the endorsement of the Government of Canada. Commercial reproduction and distribution is prohibited except with written permission from the author. For more information, please contact Environment and Climate Change Canada’s Inquiry Centre at 1-800-668-6767 (in Canada only) or 819-997-2800 or email to [email protected]. © Her Majesty the Queen in Right of Canada, represented by the Minister of the Environment, 2016. Aussi disponible en français Assessment Report: Triclosan 2016-11-26 Synopsis An assessment of triclosan has been conducted under the Canadian Environmental Protection Act, 1999 (CEPA) to determine if it poses a risk to Canadians and their environment. Triclosan was also scheduled for re-evaluation under Health Canada’s Pest Management Regulatory Agency (PMRA) pesticide re-evaluation program pursuant to the Pest Control Products Act (PCPA).