Toxicity and Assessment of Chemical Mixtures
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Activated Carbon in Sediment Remediation
ACTIVATED CARBON IN SEDIMENT REMEDIATION. BENEFITS, RISKS AND PERSPECTIVES Darya KUPRYIANCHYK Thesis committee Promoter Prof. dr. A.A. Koelmans Professor Water and Sediment Quality Co-promoter Dr. ir. J.T.C. Grotenhuis Assistant professor Environmental Technology Other members Prof. dr. R.N.J. Comans, Wageningen University Prof. dr. ir. W.J.G.M. Peijnenburg, RIVM, Leiden University Prof. dr. ir. A.J. Hendriks, Radboud University Nijmegen Dr. ir. M.T.O. Jonker, Utrecht University This research was conducted under the auspices of the Graduate School for Socio-Economic and Natural Sciences of the Environment (SENSE). ACTIVATED CARBON IN SEDIMENT REMEDIATION. BENEFITS, RISKS AND PERSPECTIVES Darya KUPRYIANCHYK Thesis submitted in fulfilment of the requirements for the degree of doctor at Wageningen University by the authority of the Rector Magnificus Prof. dr. M.J. Kropff, in the presence of the Thesis Committee appointed by the Academic Board to be defended in public on Friday 1 February 2013 at 4.00 p.m. in the Aula Darya Kupryianchyk Activated carbon in sediment remediation. Benefits, risks and perspectives 264 pages. Thesis, Wageningen University, Wageningen, The Netherlands (2013) With references and summaries in English and Dutch ISBN 978-94-6173-431-0 To my mother “who told me songs were for the birds, then taught me all the tunes I know and a good deal of the words.” Ken Kesey Contents Chapter 1. General introduction....................................................................................... 9 Chapter 2. In situ remediation of contaminated sediments using carbonaceous materials. A review......................................................................................... 17 Chapter 3. In situ sorption of hydrophobic organic compounds to sediment amended with activated carbon..................................................................................... -
AN INTRODUCTION to AQUATIC TOXICOLOGY This Page Intentionally Left Blank ÂÂ an INTRODUCTION to AQUATIC TOXICOLOGY
AN INTRODUCTION TO AQUATIC TOXICOLOGY This page intentionally left blank AN INTRODUCTION TO AQUATIC TOXICOLOGY MIKKO NIKINMAA Professor of Zoology, Department of Biology, Laboratory of Animal Physiology, University of Turku, Turku, Finland AMSTERDAM • BOSTON • HEIDELBERG • LONDON NEW YORK • OXFORD • PARIS • SAN DIEGO SAN FRANCISCO • SINGAPORE • SYDNEY • TOKYO Academic press is an imprint of Elsevier Academic Press is an imprint of Elsevier The Boulevard, Langford Lane, Kidlington, Oxford, OX5 1GB, UK 225 Wyman Street, Waltham, MA 02451, USA Copyright © 2014 Elsevier Inc. All rights reserved. No part of this publication may be reproduced or transmitted in any form or by any means, electronic or mechanical, including photocopying, recording, or any information storage and retrieval system, without permission in writing from the publisher. Details on how to seek permission, further information about the Publisher’s permissions policies and our arrangement with organizations such as the Copyright Clearance Center and the Copyright Licensing Agency, can be found at our website: www.elsevier.com/permissions This book and the individual contributions contained in it are protected under copyright by the Publisher (other than as may be noted herein). Notices Knowledge and best practice in this field are constantly changing. As new research and experience broaden our understanding, changes in research methods, professional practices, or medical treatment may become necessary. Practitioners and researchers must always rely on their own experience and knowledge in evaluating and using any information, methods, compounds, or experiments described herein. In using such information or methods they should be mindful of their own safety and the safety of others, including parties for whom they have a professional responsibility. -
Genetic and Molecular Ecotoxicology: a Research Framework
Genetic and Molecular Ecotoxicology: A Research Framework Susan Anderson,1 Walter Sadinski,1 Lee Shugart,2 Peter Brussard,3 Michael Depledge,4 Tim Ford,5 JoEllen Hose,6 John Stegeman,7 William Suk,8 Isaac Wirgin,9 and Gerald Wogan0 1Lawrence Berkeley Laboratory, Berkeley, California; 2Oak Ridge National Laboratory, Oak Ridge, Tennessee; 3University of Nevada Reno, Reno, Nevada; 4University of Plymouth, Plymouth, UK; 5Harvard University, Cambridge, Massachusetts; 6 CCidental College, Los Angeles, California; 7Woods Hole Oceanographic Institute, Woods Hole, Massachusetts; 8National Institute of Environmental Health Sciences, Research Triangle Park, North Carolina; 9New York University Medical Center, Tuxedo, New York; 10Massachusetts Institute of Technology, Cambridge, Massachusetts Participants at the Napa Conference on Genetic and Molecular Ecotoxicology assessed the status of this field in light of heightened concerns about the genetic effects of exposure to hazardous substances and recent advancements in our capabilities to measure those effects. We present here a synthesis of the ideas discussed throughout the conference, including definitions of important concepts in the field and critical research needs and opportunities. While there were many opinions expressed on these topics, there was general agreement that there are substantive new opportuni- ties to improve the impact of genetic and molecular ecotoxicology on prediction of sublethal effects of exposure to hazardous substances. Future studies should emphasize integration of genetic ecotoxicology, ecological genetics, and molecular biology and should be directed toward improving our understanding of the ecological implications of genotoxic responses. Ecological implications may be assessed at either the population or ecosys- tem level; however, a population-level focus may be most pragmatic. -
Shortcomings of the Laboratory-Derived Median Lethal Concentration for Predicting Mortality in Field Populations: Exposure Duration and Latent Mortality
Environmental Toxicology and Chemistry, Vol. 23, No. 9, pp. 2147±2153, 2004 q 2004 SETAC Printed in the USA 0730-7268/04 $12.00 1 .00 SHORTCOMINGS OF THE LABORATORY-DERIVED MEDIAN LETHAL CONCENTRATION FOR PREDICTING MORTALITY IN FIELD POPULATIONS: EXPOSURE DURATION AND LATENT MORTALITY YUAN ZHAO* and MICHAEL C. NEWMAN Department of Environmental and Aquatic Animal Health, Virginia Institute of Marine Science, College of William and Mary, P.O. Box 1346, Gloucester Point, Virginia 23062-1346, USA (Received 15 October 2003; Accepted 9 February 2004) AbstractÐExposure duration and intensity (concentration or dose) determine lethal effects of toxicants. However, environmental regulators have focused on exposure intensity and have considered duration only peripherally. Conventional testing for toxicology tends to ®x exposure time and to use the median lethal concentration (LC50) at that time to quantify mortality. Fixing the exposure duration and selecting the 50% mortality level for reasons of statistical and logistical convenience result in the loss of ecologically relevant information generated at all other times and ignore latent mortality that manifests after the exposure ends. In the present study, we used survival analysis, which is widely employed in other ®elds, to include both time and concentration as covariates and to quantify latent mortality. This was done with two contrasting toxicants, copper sulfate (CuSO4) and sodium pentachlorophenol (NaPCP). Amphipods (Hyalella azteca) were exposed to different toxicant concentrations, and the percentage mortalities were noted both during and after the exposure ended. For CuSO4 at the conventional 48-h LC50 concentrations, the predicted proportions dead after including latent mortality were 65 to 85%, not 50%. -
Fish Bioconcentration Data Requirement: Guidance for Selection of Number of Treatment Concentrations
Document ID No.: EPA 705-G-2020-3708 Fish Bioconcentration Data Requirement: Guidance for Selection of Number of Treatment Concentrations [Supplement to OCSPP Test Guideline 850.1730] July 15, 2020 Disclaimer: The contents of this document do not have the force and effect of law and are not meant to bind the public in any way. This document is intended only to provide clarity to the public regarding existing requirements under the law or agency policies. Office of Pesticide Programs Office of Chemical Safety and Pollution Prevention U.S. Environmental Protection Agency I. Purpose The purpose of this document is to clarify EPA recommendations for the number of treatment concentrations needed to result in acceptable fish bioconcentration factor (BCF) studies for pesticide registration. EPA routinely requires BCF studies to determine whether pesticide active ingredients have the potential to accumulate in fish, enter the food chain, and cause adverse effects in fish-eating predators such as aquatic mammals and birds of prey. In April 2017, EPA was approached by an outside party, the National Centre for the Replacement, Refinement and Reduction of Animals in Research (NC3R), with a suggestion to modify the test guideline for the BCF study to reduce the number of animals used in BCF testing, by reducing the number of concentration levels used from three (two positive doses and one control) to two (one positive level and one control). NC3R stated that this would be “[i]n the interest of international harmonization and reducing unnecessary animal testing” because “[a]t the moment the Japanese and US EPA guideline require that two concentrations are always tested, which is in contrast to the OECD Test Guideline[1]; therefore, many companies are understandably continuing to test two concentrations to ensure acceptance within these regions.” This modification has the potential to reduce the number of fish used by one-third. -
European Centre for Ecotoxicology and Toxicology of Chemicals
EUROPEAN CENTRE FOR ECOTOXICOLOGY AND TOXICOLOGY OF CHEMICALS EUROPEAN CENTRE FOR ECOTOXICOLOGY AND TOXICOLOGY OF CHEMICALS ECETOC at a glance 2 Purpose 3 Values 3 Vision 3 Mission 3 Approach 3 Membership 4 ECETOC Member Companies 4 Membership benefits 5 Message from the Chairman 6 ECETOC Board of Administration 7 Report from the Secretary General 8 Science Programme 10 Foreword from the Scientific Committee Chairman 10 ECETOC revises its science strategy 11 Summary of the 2011 Science Programme 12 Highlights of 2011 15 Task forces established 16 Task forces completed 18 Workshops 21 Symposia and other meetings 24 Science Awards 28 Long-range Research Initiative 29 Communication 31 Publications 31 Online communication 32 External Representation 32 Members of the Scientific Committee 34 Members of the Secretariat 34 Finance 35 Abbreviations 36 ECETOC I European Centre for Ecotoxicology and Toxicology of Chemicals I Annual Report 2011 I page 2 Introduction Membership Message Board of Report from Science Science Long-range Communication Members of Finance Abbreviations from the Administration the Secretary Programme Awards Research the Scientific Chairman General Initiative Committee Established in 1978, ECETOC is Europe’s leading industry association for developing and promoting top quality science in human and environmental risk assessment of chemicals. Members include the main companies with interests in the manufacture and use of chemicals, biomaterials and pharmaceuticals, and organisations active in these fields. ECETOC is the scientific forum where member company experts meet and co-operate with government and academic scientists, to evaluate and assess the available data, identify gaps in knowledge and recommend research, and publish critical reviews on the ecotoxicology and toxicology of chemicals, biomaterials and pharmaceuticals. -
Perfluorooctane Sulfonate (PFOS) and Perfluorooctanoic Acid (PFOA) November 2017 TECHNICAL FACT SHEET – PFOS and PFOA
Technical Fact Sheet – Perfluorooctane Sulfonate (PFOS) and Perfluorooctanoic Acid (PFOA) November 2017 TECHNICAL FACT SHEET – PFOS and PFOA Introduction At a Glance This fact sheet, developed by the U.S. Environmental Protection Agency Manmade chemicals not (EPA) Federal Facilities Restoration and Reuse Office (FFRRO), provides a naturally found in the summary of two contaminants of emerging concern, perfluorooctane environment. sulfonate (PFOS) and perfluorooctanoic acid (PFOA), including physical and Fluorinated compounds that chemical properties; environmental and health impacts; existing federal and repel oil and water. state guidelines; detection and treatment methods; and additional sources of information. This fact sheet is intended for use by site managers who may Used in a variety of industrial address these chemicals at cleanup sites or in drinking water supplies and and consumer products, such for those in a position to consider whether these chemicals should be added as carpet and clothing to the analytical suite for site investigations. treatments and firefighting foams. PFOS and PFOA are part of a larger group of chemicals called per- and Extremely persistent in the polyfluoroalkyl substances (PFASs). PFASs, which are highly fluorinated environment. aliphatic molecules, have been released to the environment through Known to bioaccumulate in industrial manufacturing and through use and disposal of PFAS-containing humans and wildlife. products (Liu and Mejia Avendano 2013). PFOS and PFOA are the most Readily absorbed after oral widely studied of the PFAS chemicals. PFOS and PFOA are persistent in the exposure. Accumulate environment and resistant to typical environmental degradation processes. primarily in the blood serum, As a result, they are widely distributed across all trophic levels and are found kidney and liver. -
ECETOC Guidance on Dose Selection
ECETOC Guidance on Dose Selection Technical Report No. 138 EUROPEAN CENTRE OFOR EC TOXICOLOGY AND TOXICOLOGY OF CHEMICALS ECETOC Guidance on Dose Selection ECETOC Guidance on Dose Selection Technical Report No. 138 Brussels, March 2021 ISSN-2079-1526-138 (online) ECETOC TR No. 138 1 ECETOC Guidance on Dose Selection 224504 ECETOC Technical Report No. 138 © Copyright – ECETOC AISBL European Centre for Ecotoxicology and Toxicology of Chemicals Rue Belliard 40, B-1040 Brussels, Belgium. All rights reserved. No part of this publication may be reproduced, copied, stored in a retrieval system or transmitted in any form or by any means, electronic, mechanical, photocopying, recording or otherwise without the prior written permission of the copyright holder. Applications to reproduce, store, copy or translate should be made to the Secretary General. ECETOC welcomes such applications. Reference to the document, its title and summary may be copied or abstracted in data retrieval systems without subsequent reference. The content of this document has been prepared and reviewed by experts on behalf of ECETOC with all possible care and from the available scientific information. It is provided for information only. ECETOC cannot accept any responsibility or liability and does not provide a warranty for any use or interpretation of the material contained in the publication. ECETOC TR No. 138 2 ECETOC Guidance on Dose Selection ECETOC Guidance on Dose Selection Table of Contents 1. SUMMARY 6 2. INTRODUCTION, BACKGROUND AND PRINCIPLES 9 2.1. Background and Principles 9 2.2. Current Regulatory Framework and Guidance 10 2.2.1. Historical perspectives and the evolution of test guidelines 10 2.2.2. -
Wildlife Toxicology: Environmental Contaminants and Their National and International Regulation" (2012)
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln USGS Staff -- ubP lished Research US Geological Survey 2012 Wildlife Toxicology: Environmental Contaminants and Their aN tional and International Regulation K. Christiana Grim Center for Species Survival, Smithsonian Conservation Biology Institute Anne Fairbrother EcoSciences Barnett A. Rattner U.S. Geological Survey, [email protected] Follow this and additional works at: http://digitalcommons.unl.edu/usgsstaffpub Part of the Geology Commons, Oceanography and Atmospheric Sciences and Meteorology Commons, Other Earth Sciences Commons, and the Other Environmental Sciences Commons Grim, K. Christiana; Fairbrother, Anne; and Rattner, Barnett A., "Wildlife Toxicology: Environmental Contaminants and Their National and International Regulation" (2012). USGS Staff -- Published Research. 969. http://digitalcommons.unl.edu/usgsstaffpub/969 This Article is brought to you for free and open access by the US Geological Survey at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in USGS Staff -- ubP lished Research by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. Published in New Directions in Conservation Medicine: Applied Cases in Ecological Health, edited by A. Alonso Aguirre, Richard S. Ostfield, and Peter Daszak (New York: Oxford University Press, 2012). Authors K. Christiana Grim, D.V.M. Research Associate Center for Species Survival Smithsonian Conservation Biology Institute Front Royal, Vrrginia Anne Fairbrother, D.V.M., M.S., Ph.D. Senior Managing Scientist EcoSciences Exponent Seattle, Washington Barnett A. Rattner, Ph.D. Ecotoxicologist U.S. Geological Survey Patuxent Wildlife Research Center Beltsville Laboratory Beltsville, Maryland WILDLIFE TOXICOLOGY Environmental Contaminants and Their National and International Regulation K. Christiana Grim, Anne Fairbrother, and Barnett A. -
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. -
Ecotoxicology Knowledgebase
ECOTOXicology Knowledgebase: Modernizing the Literature Review and Data Curation Processes, and Mapping Ecological Toxicity of Per- and Polyfluoroalkyl Substances (PFAS) Jennifer OlkerPhoto, image Postdoctoral area measures 2” H x 6.93” W and can be Researchermasked by a collage strip of one, two or three images. Colleen ElonenThe photo, imageECOTOX area is located 3.19” from coordinator left and 3.81” from top of page. Each image used in collage should be reduced or cropped to a maximum of 2” high, stroked with a 1.5 pt white frame and positioned edge-to-edge with accompanying images. US EPA ECOTOX Project Team: Colleen Elonen Jennifer Olker GDIT contract staff Dale Hoff SEE staff Rong-Lin Wang Office of Research and Development www.epa.gov/ecotox Overview • Background and History for ECOTOX Knowledgebase • Modernizing the ECOTOX Pipeline (C. Elonen, SOT 2020) • Mapping ecological toxicity of PFAS with ECOTOX Protocols (J. Olker, SOT 2020) 2 What is the ECOTOX Knowledgebase? Publicly available, curated database providing toxicity data from single-chemical exposure studies to aquatic life, terrestrial plants, and wildlife • From comprehensive search and review of open and grey literature – Data extracted from acceptable studies, with up to 250 fields – Updated quarterly • 30+ year history: www.epa.gov/ecotox/ Originated in the early 1980s, US Environmental Protection Agency Office of Research and Development 3 Who uses the ECOTOX Knowledgebase? Clients Contacting ECOTOX Support line 2005 - 2016 (n = 2813) US EPA Headquarters Local Govt. International Govt. 4% 1% 8% Govt. Contractors 25% US EPA Regional Office 4% Unknown 5% University/Academia Other Federal 6% Agencies 4% US EPA Laboratory 4% State Govt. -
Lecture Notes on Toxicology
LECTURE NOTES For Medical Laboratory Science Students Toxicology Dr. Biruh Alemu (MD), Ato Mistire Wolde (MSC, MSC) Hawassa University In collaboration with the Ethiopia Public Health Training Initiative, The Carter Center, the Ethiopia Ministry of Health, and the Ethiopia Ministry of Education May 2007 Funded under USAID Cooperative Agreement No. 663-A-00-00-0358-00. Produced in collaboration with the Ethiopia Public Health Training Initiative, The Carter Center, the Ethiopia Ministry of Health, and the Ethiopia Ministry of Education. Important Guidelines for Printing and Photocopying Limited permission is granted free of charge to print or photocopy all pages of this publication for educational, not-for-profit use by health care workers, students or faculty. All copies must retain all author credits and copyright notices included in the original document. Under no circumstances is it permissible to sell or distribute on a commercial basis, or to claim authorship of, copies of material reproduced from this publication. ©2007 by Dr. Biruh Alemu, Ato Misire Wolde All rights reserved. Except as expressly provided above, no part of this publication may be reproduced or transmitted in any form or by any means, electronic or mechanical, including photocopying, recording, or by any information storage and retrieval system, without written permission of the author or authors. This material is intended for educational use only by practicing health care workers or students and faculty in a health care field. PREFACE The scope of toxicology widened tremendously during the last few years. An important development in this discipline is mandatory because of the expansion of different industrial, medical, environmental, animal and plant noxious substances.