AQUATIC TOXICOLOGY: Aquaticaquatic Ecotoxicologyecotoxicology Isis Aa Newnew Fieldfield

Total Page:16

File Type:pdf, Size:1020Kb

AQUATIC TOXICOLOGY: Aquaticaquatic Ecotoxicologyecotoxicology Isis Aa Newnew Fieldfield AQUATIC TOXICOLOGY: AquaticAquatic EcotoxicologyEcotoxicology isis aa NewNew fieldfield • Rachel Carson, Silent Spring (1962) Rachel Carson biographer Linda Lear, who tells the story of Carson"s courageous defense of her truths in the face of ruthless assault from the chemical industry in the year following the publication of Silent Spring and before her untimely death in 1964. • Aquatic Toxicology (Published first in 1981) Pollutant Responses in Marine Organisms (PRIMO) THE BEAT GOES ON Polar Bears Face New Toxic Threat: Flame Retardants By Marla Cone, Times Staff Writer Flame retardants called polybrominated diphenyls, or PBDEs, are growing at a rapid pace in people and wildlife. Although they have been found in much lower concentrations in the Arctic, scientists say their toxic legacy will persist there for years because they are slow to break down, particularly in cold climates. PBDEs disrupted thyroid and sex hormones and damaged developing brains, impairing motor skills and mental abilities, including memory and learning. Chemicals with properties similar to PBDEs are already weakening the bears' immune systems, altering their bone structure, skewing their sex hormones and perhaps even causing small numbers of hermaphroditic bears. Virtually every animal and person tested on Earth contains traces of brominated flame retardants. Americans have the highest levels found so far, and many U.S. women carry concentrations in their breast milk that are close to the amounts that altered the brains of newborn mice in lab tests. Another flame retardant used in building materials and household furnishings, called HBCD, or hexabromocyclododecane, in Arctic bears. Chemists had thought it had a low potential to migrate long distances but now believe it is spreading globally. AquaticAquatic EcotoxicologyEcotoxicology isis aa ComplexComplex MultidisciplinaryMultidisciplinary ScienceScience Comparisons between Human Toxicology and Ecotoxicology. Pharmacology/Toxicology Ecotoxicology To protect humans against toxic exposure Protect the ecosysyem. Target organism known Susceptible species not known, variable Mammalian models as human proxy Direct Experiments on indicator species Most are poikilothermic and many Models are homeothermic and static conformers Administered dosage via a number of Toxin identity, dosage and duration often routes can be measured accurately. known but many additional variables can Dosimetry available. alter dosimetry Less basic research but more empirical to Basic research: to understand mechanisms estimate threshold concentrations necessary for regulation. Methods new and are just now being Test methods well developed standardized. AQUATIC TOXICOLOGY: Some Definitions: Aquatic: Growing living or found in water Toxicology: The branch of science concerned with poisons, their nature, effects and antidotes. Toxicant: Agent that cause deleterious perturbations and responses outside of the “normal” range for a healthy non-perturbed organism. Pollution: Introduction of foreign material/substances/energy/organisms into the aquatic environment (freshwater/marine) by humans Pollutant: Introduced foreign toxicants and substances together with physical changes that decrease the quality of the environment. Xenobiotic: Normally refers to a synthetic, non-natural, man-made chemical that can cause deleterious effects The Medium: all bodies of water, freshwater, brackish, saline, permanent, transient Aquatic toxicology: a new multidisciplinary discipline evolved from pharmacology What Constitutes a Toxicant (Assumptions Underlying Toxicity): 1) Causality: Cause-Effect relationship exists (direct or indirect) 2) A dose-response or concentration -response relationship exists a) The effect or response in question results from the toxic agent interacting with sites of toxic action in the organism b) The dosage of toxin is related to dosage and possibly duration of exposure c) above a statistically based threshold value the magnitude of effect is proportional to amount of toxin reaching the sites of action d) dose and concentration relate more to potency at target site of interaction than administered external concentration 3) Effects can be quantified in an accurate and precise manner However toxic response is complex and predicated upon a number of biological, physical and chemical factors that are often hard to measure and control. ThreeThree PhasesPhases (P(P’’s)s) ofof ToxicToxic ActionAction TYPESTYPES OFOF POLLUTANT:POLLUTANT: Major classes of pollutant can be broken down into different categories based either upon source, chemistry or effect: • Oil • Sewage • Chemicals • synthetic organic chemicals e.g. pesticides • inorganic chemicals e.g. metals, fertilizers • Non biodegradable, persistent solid wastes. e.g. plastics, tins, cans • Thermal Pollution – power stations • Nuclear Pollution - radioactive contaminants and irradiation • Biological Pollution – introduction of non-native, alien species • Atmospheric Pollution – particles, volatile compounds, greenhouse effect, ozone depletion and acid rain. Aquatic:Aquatic: GrowingGrowing livingliving oror foundfound inin waterwater Basic Physical and Chemical Properties of Water and Seawater and important in understanding environmental factors affecting availability toxicity and essentiality (trace essential metals) ImportantImportant PropertiesProperties ofof LiquidLiquid WaterWater.
Recommended publications
  • Aquatic Toxicology MEES 743 3 Credits SPRING 2019 (Also Listed As TOX 625)
    Aquatic Toxicology MEES 743 3 credits SPRING 2019 (also listed as TOX 625) Course Objectives / Overview This course will provide students with a broad perspective on the subject INSTRUCTOR DETAILS: of aquatic toxicology. It is a comprehensive course in which a definitive description of basic concepts and principles, laboratory testing and field Faculty Details: situations, as well as examples of typical data and their interpretation and Dr. Carys Mitchelmore use by industry and water resource managers, will be discussed. The fate [email protected] and toxicological action of environmental pollutants will be examined in 410-326-7283 aquatic ecosystems, whole organisms and at the cellular, biochemical and molecular levels. Current and emerging issues will be used as case studies CLASS MEETING DETAILS: throughout the course to illustrate specific ecosystems (e.g. Chesapeake Bay), pollution events (e.g. Deepwater Horizon Oil Spill), particular Date: Monday/Wednesday organisms (e.g. coral reefs) or a specific class of contaminants. Classes Time: 12-1.30pm will consist of lectures by the instructor together with some guest Originating Site: UMCES, CBL speakers in addition to group discussions. IVN bridge number: (800414) Phone call in number: (***) Expected Learning Outcomes Room phone number: CBL, Ed Houde Teaching suite Following completion of this course students will; (1) Have experience applying basic concepts in environmental COURSE TYPE: science, including environmental chemistry, biology and Check all that apply physiology, ecosystem health, management and regulatory issues, ☐ as they relate to pollution of aquatic ecosystems. Foundation (2) Be able to identify a current topic of concern and summarize ☐ Professional Development current data/papers in an oral presentation including directing an ☐ Issue Study Group open discussion with the rest of the class.
    [Show full text]
  • AN INTRODUCTION to AQUATIC TOXICOLOGY This Page Intentionally Left Blank €ƒÂ€ 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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%.
    [Show full text]
  • Harmful Algal Blooms (Habs) and Public Health: Progress and Current Challenges
    Harmful Algal Blooms (HABs) and Public Health: Progress and Current Challenges Edited by Lesley V. D’Anglada, Elizabeth D. Hilborn and Lorraine C. Backer Printed Edition of the Special Issue Published in Toxins www.mdpi.com/journal/toxins Lesley V. D’Anglada, Elizabeth D. Hilborn and Lorraine C. Backer (Eds.) Harmful Algal Blooms (HABs) and Public Health: Progress and Current Challenges This book is a reprint of the Special Issue that appeared in the online, open access journal, Toxins (ISSN 2072-6651) from 2014–2015 (available at: http://www.mdpi.com/journal/toxins/special_issues/HABs?sort=asc). Guest Editors Lesley V. D’Anglada U.S. Environmental Protection Agency USA Elizabeth D. Hilborn United States Environmental Protection Agency USA Lorraine C. Backer National Center for Environmental Health USA Editorial Office MDPI AG Klybeckstrasse 64 Basel, Switzerland Publisher Shu-Kun Lin Managing Editor Chao Xiao 1. Edition 2016 MDPI • Basel • Beijing • Wuhan • Barcelona ISBN 978-3-03842-155-9 (Hbk) ISBN 978-3-03842-156-6 (PDF) © 2016 by the authors; licensee MDPI, Basel, Switzerland. All articles in this volume are Open Access distributed under the Creative Commons Attribution license (CC BY), which allows users to download, copy and build upon published articles even for commercial purposes, as long as the author and publisher are properly credited, which ensures maximum dissemination and a wider impact of our publications. However, the dissemination and distribution of physical copies of this book as a whole is restricted to MDPI, Basel, Switzerland. III Table of Contents List of Contributors ............................................................................................................ VII About the Guest Editors......................................................................................................... X Preface Reprinted from: Toxins 2015, 7, 4437-4441 http://www.mdpi.com/2072-6651/7/11/4437 ....................................................................
    [Show full text]
  • 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.
    [Show full text]
  • Toxicity and Assessment of Chemical Mixtures
    Toxicity and Assessment of Chemical Mixtures Scientific Committee on Health and Environmental Risks SCHER Scientific Committee on Emerging and Newly Identified Health Risks SCENIHR Scientific Committee on Consumer Safety SCCS Toxicity and Assessment of Chemical Mixtures The SCHER approved this opinion at its 15th plenary of 22 November 2011 The SCENIHR approved this opinion at its 16th plenary of 30 November 2011 The SCCS approved this opinion at its 14th plenary of 14 December 2011 1 Toxicity and Assessment of Chemical Mixtures About the Scientific Committees Three independent non-food Scientific Committees provide the Commission with the scientific advice it needs when preparing policy and proposals relating to consumer safety, public health and the environment. The Committees also draw the Commission's attention to the new or emerging problems which may pose an actual or potential threat. They are: the Scientific Committee on Consumer Safety (SCCS), the Scientific Committee on Health and Environmental Risks (SCHER) and the Scientific Committee on Emerging and Newly Identified Health Risks (SCENIHR) and are made up of external experts. In addition, the Commission relies upon the work of the European Food Safety Authority (EFSA), the European Medicines Agency (EMA), the European Centre for Disease prevention and Control (ECDC) and the European Chemicals Agency (ECHA). SCCS The Committee shall provide opinions on questions concerning all types of health and safety risks (notably chemical, biological, mechanical and other physical risks) of non- food consumer products (for example: cosmetic products and their ingredients, toys, textiles, clothing, personal care and household products such as detergents, etc.) and services (for example: tattooing, artificial sun tanning, etc.).
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • Comparative Study of Potential Transfer of Natural and Anthropogenic Cadmium to Plankton Communities in the North-West African Upwelling
    1 Science Of The Total Environment A chimer February 2015, Volume 505 Pages 870-888 r http://archimer.ifremer.fr http://dx.doi.org/10.1016/j.scitotenv.2014.10.045 http://archimer.ifremer.fr/doc/00252/36310/ © 2014 Elsevier B.V. All rights reserved. Comparative study of potential transfer of natural and anthropogenic cadmium to plankton communities in the North-West African upwelling Auger Pierre-Amael 1 * , Machu Eric 1, 4, Gorgues Thomas 1, 4, Grima Nicolas 3, 4, Waeles Mathieu 2, 4 1 UBO, IRD, IFREMER, LPO,UMR 6523,CNRS, F-29280 Plouzane, France. 2 UBO, IRD, Lab Environm Mario LEMAR, UMR 6539,CNRS, F-29280 Plouzane, France. 3 CNRS, France 4 Ifremer, France * Corresponding author : Pierre Amael Auger, tel.: + 33 298498662 ; email address : [email protected] Abstract : A Lagrangian approach based on a physical-biogeochemical modeling was used to compare the potential transfer of cadmium (Cd) from natural and anthropogenic sources to plankton communities (Cd-uptake) in the NorthWest African upwelling. In this region, coastal upwelling was estimated to be the main natural source of Cd while the most significant anthropogenic source for marine ecosystem is provided by phosphate industry. In our model experiment, Cd-uptake (natural or anthropogenic) in the North-West African upwelling is the result of an interplay between the Cd dispersion (by advection processes) and the simulated biological productivity. In the Moroccan waters, advection processes limit the residence time of water masses resulting in a low natural Cd-uptake by plankton communities while anthropogenic Cd-uptake is high. As expected, the situation is reversed in the Senegalo-Mauritanian upwelling where natural Cd-uptake is higher than anthropogenic Cd-uptake.
    [Show full text]
  • 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.
    [Show full text]