Assessing the Hazard of Metals and Inorganic Metal Substances in Aquatic and Terrestrial Systems - Chapter 1 ppsx

Title Page
Coordinating Editor of SETAC Books
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Gorsuch Environmental Management Services, Inc.
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Proceedings from the Workshop on
Hazard Identification Approach for Metals and
Inorganic Metal Substances
3-8 May 2003
Pensacola Beach, Florida USA
CRC Press is an imprint of the
Taylor & Francis Group, an informa business
Boca Raton London New York
Edited by
William J. Adams
Peter M. Chapman
Assessing the Hazard of
Metals and
Inorganic Metal Substances in
Aquatic and
Terrestrial Systems

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Library of Congress Cataloging-in-Publication Data
Adams, William J., 1946-
Assessing the hazard of metals and inorganic metal substances in aquatic and terrestrial
systems / William J. Adams and Peter M. Chapman.

p. cm.
Includes bibliographical references and index.
ISBN-13: 978-1-4200-4440-9 (alk. paper)
1. Metals Environmental aspects. 2. Environmental risk assessment. 3.
Metals Toxicology. I. Chapman, Peter M. II. Title.
TD196.M4A33 2006
577.27 dc22
2006022030
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Table of Contents

Acknowledgments xi
Editors xiii
Workshop Participants xv

Chapter 1

A Pellston Workshop on Metals Hazard Assessment 1

William J. Adams and Peter M. Chapman

1.1 Introduction to the Workshop 1
1.2 Hazard Identification, Classification, and Assessment 2
1.3 Workshop Purpose and Goals 4
References 4

Chapter 2

Executive Summary 7

William J. Adams and Peter M. Chapman

2.1 Introduction 7
2.2 Persistence 7
2.3 Bioaccumulation 8
2.4 Toxicity 8
2.5 Terrestrial Environment 9
2.6 Conclusion 10

Chapter 3

Integrated Approach for Hazard Assessment of Metals and
Inorganic Metal Substances: The Unit World Model Approach 11

Adam Peters, William J. Adams, Miriam L. Diamond, William Davison,
Dominic M. Di Toro, Patrick J. Doyle, Donald Mackay, Jerome Nriagu,
Carol Ptacek, James M. Skeaff, Edward Tipping, and Hugo Waeterschoot

3.1 Introduction 11
3.1.1 Background 11
3.1.2 A Unifying Model 13
3.2 The Unit World Model (UWM) 14
3.3 Hazard Assessment Framework for a Generic Environment 16
3.3.1 Generalized Model Framework 16
3.3.2 Water Column/Sediment Model 17
3.3.3 Soil Model 21
3.3.4 Key Processes 23
3.4 Source Term 23
3.4.1 Natural Occurrence of Metals 24

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3.4.2 Determining the Input Term 24
3.4.2.1 Measuring Tool for the Aquatic Compartment 26
3.4.2.2 Measuring Tool for the Soil Compartment 26
3.4.3 Combinations of Commercial Compounds 28
3.4.4 Generic Data Needs 28

3.5 Application of the UWM 28
3.5.1 Application to Classification 30
3.5.2 Application to Ranking 30
3.5.3 Application to Screening Assessment 31
3.5.4 Distribution of the Mass Input into Compartments for
Different Assessment Levels 31
3.5.5 Precautionary Approach 31
3.6 Illustrations of Hazard Assessments 32
3.6.1 Example 1: The Generic Environment (Unit World) 32
3.6.1.1 Organic Compounds 34
3.6.1.2 2 Metals 41
3.6.2 Example 2: A Simple Approach for Soils 41
3.6.2.1 Defining a Unit World Soil 41
3.6.2.2 Scoping Calculations 45
3.6.2.3 Application 46
3.6.3 Example 3: The Water Column/Sediment Model 46
3.7 Steps Required to Proceed from a Prototype to a Workable Model 48
3.7.1 Implementation 48
3.7.2 UWM Evaluation and Validation 49
Acknowledgments 51
References 51

Chapter 4

Bioaccumulation: Hazard Identification of Metals and
Inorganic Metal Substances 55

Christian E. Schlekat, James C. McGeer, Ronny Blust, Uwe Borgmann,
Kevin V. Brix, Nicolas Bury, Yves Couillard, Robert L. Dwyer, Samuel N. Luoma,
Steve Robertson, Keith G. Sappington, Ilse Schoeters, and Dick T.H.M. Sijm

4.1 Introduction 55
4.2 Regulatory Objectives of Bioaccumulation in Hazard Assessment 56
4.2.1 European Union (EU) 56
4.2.2 United States 56
4.2.3 Canada 57
4.3 Scientific Basis of Metal Bioaccumulation: Current State of
Understanding 57
4.3.1 Mechanisms of Metal Uptake 57
4.3.2 Gill vs. Gut Environments 58
4.3.3 Chemical Speciation and Biological Availability 59
4.3.4 Bioaccumulation and Toxicity 60
4.3.5 Metal Exposure Concentrations and Accumulation 62

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4.4 Limitations of Current Approach to Bioconcentration Factors (BCFs)
and Bioaccumulation Factors (BAFs) 63
4.4.1 Metal Bioaccumulation, Toxicity, and Trophic Transfer 63
4.4.1.1 Inverse Relationships 63
4.4.1.2 Bioaccumulation in Relation to Chronic Toxicity 64
4.4.1.3 Trophic Transfer 65
4.4.2 Implication 65
4.5 Further Guidance on Bioaccumulation 65
4.5.1 Biodynamic Models 65
4.5.2 Application of BCF and BAF Data 66
4.5.2.1 Linking BCF with Chronic Lethality 66
4.5.2.2 Accounting for Accumulation from Background
Concentrations 71

4.5.2.3 Calculating BCF and BAF Values over a Limited
Range of Concentrations 71
4.5.2.4 Bioaccumulation in Relation to Dietary Toxicity 72
4.6 Integration of Chronic Thresholds and Trophic Transfer into the Unit
World Model 72
4.6.1 Introduction 72
4.6.2 Trophic Transfer Models 73
4.6.2.1 Conceptual Framework 73
4.6.2.2 Biodynamic Bioaccumulation Models 75
4.6.2.3 Use of Model Outputs 78
4.6.3 Uncertainties 79
4.6.3.1 Bioaccumulation Models 79
4.6.3.2 Toxicity Reference Values (TRVs) 81
4.6.3.3 Protectiveness of Environmental Quality Standards 81
4.7 Conclusions 82
References 83

Chapter 5

Aquatic Toxicity for Hazard Identification of Metals and
Inorganic Metal Substances 89

Andrew S. Green, Peter M. Chapman, Herbert E. Allen, Peter G.C. Campbell,
Rick D. Cardwell, Karel De Schamphelaere, Katrien M. Delbeke, David R. Mount,
and William A. Stubblefield

5.1 Introduction 89
5.2 Data Acceptability 90
5.2.1 Data Evaluation and Species Selection Criteria 90
5.2.2 Culture and Test Conditions 92

5.2.2.1 Background and Essentiality 92
5.2.2.2 Other Relevant Test System Characteristics 94
5.2.2.3 Algal Tests 95
5.3 Sediment Effect Thresholds 95
5.4 Dietary Exposure 97

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5.5 Bioavailability 98
5.5.1 Speciation 98
5.5.2 Biotic Ligand Model (BLM) 99
5.5.3 Algae 99
5.5.4 BLM Data Gaps and Future Directions 101
5.5.5 Taking Bioavailability into Account 101
5.6 Integrated Approach for Risk/Hazard Assessments Using Toxicity 103
5.6.1 Approach 103
5.6.2 Examples 105
5.7 Conclusions and Recommendations 106
Acknowledgment 107
References 107

Chapter 6

Hazard Assessment of Inorganic Metals and Metal Substances
in Terrestrial Systems 113

Erik Smolders, Steve McGrath, Anne Fairbrother, Beverley A. Hale, Enzo Lombi,
Michael McLaughlin, Michiel Rutgers, and Leana Van der Vliet

6.1 Foreword 113
6.2 Introduction 113
6.3 Persistence of Metals in Soil 114
6.3.1 Residence Time of Metals in Soil 114
6.3.2 Critical Loads of Metals 114
6.3.3 Aging of Metals in Soil 115
6.3.4 Transformation of Sparingly Soluble Compounds 118
6.4 Bioaccumulation of Metals in the Terrestrial Food Chain 119
6.4.1 Defining Bioaccumulation Factor (BAF) and Bioconcentration
Factor (BCF) in the Terrestrial Environment 119
6.4.2 Measuring BAF/BCFs — The Denominator 120
6.4.3 Interpreting BAF/BCFs 121
6.4.4 Trophic Transfer Factors 121
6.4.5 Trophic Transfer of Metals 122
6.4.6 Proposed Approach for Incorporation of BAF into Hazard
Assessment 122
6.5 Ranking Metal Toxicity in Terrestrial Systems 123
6.6 Conclusions and Recommendations 129
References 130

Appendix A:

A Unit World Model for Hazard Assessment of Organics
and Metals 135
A.1 The Aquivalence Approach 135
A.2 Unit World Parameters 136
A.3 Mass Balance Equations 137
References 140

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© 2007 by the Society of Environmental Toxicology and Chemistry (SETAC)

Acknowledgments

This book presents the proceedings of a Pellston Workshop convened by the Society
of Environmental Toxicology and Chemistry (SETAC) in Pensacola, Florida, in May
2003. The 47 scientists, managers, and policymakers involved in this workshop
represented seven countries. We thank all participants for their contributions, both
in the workshop and in subsequent discussions resulting in this book.
The workshop and this book were made possible by the generous support of the
following organizations (in alphabetical order):
• Center for the Study of Metals in the Environment (CSME)
• Environment Canada
• Eurometaux
• International Copper Association
• International Lead Zinc Research Organization
• Kennecott Utah Copper Corporation
• Kodak
• Natural Resources Canada
• Nickel Producers Environmental Research Association (NiPERA)
• Rio Tinto
• U.S. Environmental Protection Agency (Office of Research and Development)
The workshop would also not have been possible without the very capable
management and excellent guidance provided by Greg Schiefer, Linda Longsworth,
and Mimi Meredith, and the support of SETAC Executive Director Rodney Parrish.
In particular, the efforts of Mimi Meredith in the production of this book are
gratefully acknowledged.

William J. Adams
Peter M. Chapman

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© 2007 by the Society of Environmental Toxicology and Chemistry (SETAC)

Editors

William J. Adams, Ph.D.

is a Principal Environmental Scientist and General Man-
ager for Rio Tinto, Salt Lake City, Utah. He was previously the Director of Environ-
mental Science for 6 years at Kennecott Utah Copper, Vice President of ABC Lab-
oratories for 5 years, and Science Fellow at Monsanto Company for 14 years. His
research interests include developing ecotoxicology risk assessment methods for
metals, site-specific methodologies for water quality criteria for metals, and devel-
opment of an approach for hazard assessment of metals. Dr. Adams has published
several papers on methods for assessing sediments and was instrumental in developing
the science supporting equilibrium partitioning theory (EqP) for nonpolar organic
substances. He has also published in the area of water quality assessments. He was
a member of the U.S. Environmental Protection Agency (EPA) Science Advisory
Board (SAB) for 10 years and has served on several other national committees.

Peter M. Chapman

is a Principal and Senior Environmental Scientist with Golder
Associates in North Vancouver, British Columbia, Canada. He has been an active
researcher for almost 30 years in the fields of aquatic ecology, ecotoxicology, and
environmental risk assessment, with a particular focus on metals and metalloids. He
has published more than 140 articles in international, peer-reviewed scientific jour-
nals, and in book chapters. He is Senior Editor of the international, peer-reviewed
journal

Human and Ecological Risk Assessment

, a member of the editorial board of
two other international peer-reviewed journals, and edits a highly popular series of
scientific “Learned Discourses” in the

SETAC Globe

. In 1996 he received an award
from the EPA for resolving environmental issues in Port Valdez, Alaska. In 2001,
the Society of Environmental Toxicology and Chemistry awarded him their highest
award for lifetime achievement and outstanding contributions to the environmental
sciences: The Founders Award.

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Workshop Participants*

Steering Committee Member (SCM)
Workshop Chair (WC)

WORKGROUP 1: PERSISTENCE

William J. Adams (WC) (SCM)

Rio Tinto
Murray, Utah

William Davison

Lancaster University
Lancaster, United Kingdom

Dominic M. Di Toro

Hydroqual
Englewood, New Jersey

Miriam L. Diamond

University of Toronto
Toronto, Ontario, Canada

Patrick J. Doyle (SCM)

Environment Canada
Hull, Ontario, Canada

Samuel Luoma

U.S. Geological Survey
Menlo Park, California

Donald Mackay

Trent University
Peterborough, Ontario, Canada

Jerome Nriagu

University of Michigan
Ann Arbor, Michigan

Johanna Peltola-Thies

Federal Environmental Agency
Berlin, Germany

Adam Peters (Rapporteur)

Environment Agency
Wallingford, United Kingdom

Carol Ptacek

University of Waterloo
Waterloo, Ontario, Canada

James M. Skeaff

Natural Resources Canada
Ottawa, Ontario, Canada

Edward Tipping

Centre for Ecology and Hydrology
Cumbria, United Kingdom

Hugo Waeterschoot

Eurometaux
Brussels, Belgium

John Westall (Chair) (SCM)

Oregon State University
Corvallis, Oregon

William Wood (SCM)

U.S. Environmental Protection Agency
Washington, D.C.

* Affiliations were current at the time of the workshop.

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WORKGROUP 2: BIOACCUMULATION

Ronny Blust

University of Antwerp
Antwerp, Belgium

Uwe Borgmann

Environment Canada

Burlington, Ontario, Canada

Kevin Brix

EcoTox
Newport, Oregon

Nicolas Bury

King’s College
London, United Kingdom

Yves Couillard

Environment Canada
Hull, Quebec, Canada

Robert L. Dwyer

International Copper Association
New York, New York

Samuel N. Luoma

U.S. Geological Survey
Menlo Park, California

James C. McGeer (Rapporteur)

Natural Resources Canada

Ottawa, Ontario, Canada

Steve Robertson (SCM)

Environment Agency
Wallingford, United Kingdom

Keith G. Sappington

U.S. Environmental Protection Agency
Washington, D.C.

Christian Schlekat (Chair)

U.S. Borax
Valencia, California

Ilse Schoeters (SCM)

European Copper Institute
Brussels, Belgium

Dick T.H.M. Sijm

National Institute for Public Health and
the Environment (RIVM)
Bilthoven, The Netherlands

WORKGROUP 3: TOXICITY

Herbert E. Allen

University of Delaware
Newark, Delaware

Peter G.C. Campbell (SCM)

Université du Québec
Ste. Foy, Quebec, Canada

Richard D. Cardwell

Parametrix
Corvallis, Oregon

Peter M. Chapman (Rapporteur)
(SCM)

EVS Consultants
North Vancouver, British Columbia,
Canada

Amy Crook

Center for Science in Public
Participation/Environmental Mining
Council
Victoria, British Columbia, Canada

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© 2007 by the Society of Environmental Toxicology and Chemistry (SETAC)

Karel De Schamphelaere

University of Ghent
Ghent, Belgium

Katrien Delbeke

European Copper Institute
Brussels, Belgium

Andrew S. Green (Chair)

International Lead Zinc Research
Organization
Research Triangle Park, North Carolina

David R. Mount

U.S. Environmental Protection Agency
Duluth, Minnesota

William A. Stubblefield

Parametrix
Corvallis, Oregon

WORKGROUP 4: TERRESTRIAL

Anne Fairbrother

U.S. Environmental Protection Agency
Corvallis, Oregon

Beverly A. Hale

University of Guelph
Guelph, Ontario, Canada

Enzo Lombi

Commonwealth Scientific and
Industrial Research Organization
(CSIRO) Land and Water
Adelaide, Australia

Steve McGrath

IACR-Rothamsted
Herts, United Kingdom

Michael McLaughlin

Commonwealth Scientific and
Industrial Research Organization
(CSIRO) Land and Water
Adelaide, Australia

Michiel Rutgers

National Institute for Public Health and
the Environment (RIVM)
Bilthoven, The Netherlands

Erik Smolders (Chair) (SCM)

K.U. Leuven
Heverlee, Leuven, Belgium

Leana Van der Vliet

Environment Canada
Ottawa, Ontario, Canada

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1

1

A Pellston Workshop
on Metals Hazard
Assessment

William J. Adams and Peter M. Chapman

1.1 INTRODUCTION TO THE WORKSHOP

This book is the result of discussions that took place at the Pellston Workshop on
Assessing the Hazard of Metals and Inorganic Metal Substances in Aquatic and
Terrestrial Systems. The workshop, sponsored by the Society of Environmental
Toxicology and Chemistry (SETAC), was held 3–8 May, 2003, in Pensacola, FL.
The workshop built upon the findings of a previous SETAC workshop, which
provided an in-depth discussion of the potential to assess bioavailability of metals
to fish and invertebrates (Bergman and Dorward-King 1996) and which led to the
development of the Biotic Ligand Model (BLM) (Di Toro et al. 2001, 2005).
The purpose of the workshop was to allow for a focused discussion regarding
the fate and effects of metals in the environment (the focus was on inorganic
substances; however, where appropriate, organometallic substances were also con-
sidered) and incorporating important advances in the state of knowledge that had
occurred in the intervening 7 years. Specifically, this workshop allowed for a forum
for further discussions among scientists, environmental regulators, and environmen-
tal managers, on the utility of persistence, bioaccumulation, and toxicity (PBT) for
hazard identification and classification procedures for metals and inorganic metal
substances.
The workshop brought together a multidisciplinary and international group of
47 scientists, managers, and policymakers from Australia, Belgium, Canada, Ger-
many, The Netherlands, the United Kingdom, and the United States for 6 days of
discussions on various means to assess the environmental hazard posed by metals
and inorganic metal substances. Participants included representatives from regulatory
and nonregulatory government agencies, academia, industry, environmental groups,
and consulting firms involved in assessment, management, and basic research on
metals and metal substances.
During the first day of the workshop, presentations were given on the appli-
cation of PBT criteria in the different regulatory arenas in Canada, Europe, and
the United States. Additional presentations highlighted the state of the science
regarding the interpretation of PBT for metals. These presentations provided the

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2

Assessing the Hazard of Metals and Inorganic Metal Substances

basis for subsequent plenary and workgroup discussions. Participants were
assigned to 4 different workgroups as follows:
1. Persistence — reviewing the scientific underpinnings of the use of
persistence in hazard evaluation and of persistence measures as applied
to metals, including the potential to use bioavailability measures in
aquatic systems.
2. Bioaccumulation — reviewing the soundness of current uses of bioaccu-
mulation in hazard evaluation of metals in aquatic species and aquatic-
linked food chains.
3. Toxicity — reviewing toxicity procedures used to assess the hazard of
metals as used within PBT approaches.
4. Terrestrial systems — evaluating current uses of PBT measures for metals
in terrestrial ecosystems, with a view to improving the approach or iden-
tifying an alternative methodology.
In each of these discussions, participants were urged to seek consensus, where
possible, on specific technical issues of concern for assessing the hazard of metals
and metal substances, and to identify recommendations for future research that could
lead to improvements in the existing methods available. Chapter 3 through Chapter
6 in this book provide a synopsis of the discussions and conclusions from each of
the workgroups; an overall executive summary is provided in Chapter 2.
This book provides the basis for substantive improvements to the current model
for the hazard assessment of metals and metal substances. It is our hope that this
book will not only advance the science, but will also serve as the basis for further

discussions and advances in the foreseeable future.

1.2 HAZARD IDENTIFICATION, CLASSIFICATION,
AND ASSESSMENT

Hazard identification and classification procedures currently used in many countries
are based on PBT measurements. Procedures for aquatic hazard identification or
classification of organic and inorganic substances have been harmonized by the
Organisation for Economic Cooperation and Development (OECD 2001) for the
purpose of classifying market-place substances in terms of their potential hazard.
PBT criteria are further used within the regulatory context to rank and identify
substances of concern. In the United States, PBT criteria have been used to identify
substances of concern for waste minimization, emissions reporting, and for the
identification of substances for stricter regulations (air, water, and solid waste). In
Canada, a PBT-type approach is used for categorizing substances on the Domestic
Substances List (DSL) to determine if a screening assessment is required. Depend-
ing upon the assessment findings, actions to reduce exposure may be taken. In the
European Union (EU), in the framework of the New Chemicals Policy, discussions
are ongoing on whether to use PBT criteria to identify substances of very high
concern, which will have to be given use-specific permission before they can be

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A Pellston Workshop on Metals Hazard Assessment

3

employed in particular uses. In addition, the EU New Chemicals Policy (REACH:
Registration, Evaluation, Authorization, and Restriction of Chemicals) will neces-

sitate authorization for use of substances classified as PBT and vPvB (very persis-
tent and very bioaccumulative).
Materials used in manufacturing and commerce may be hazardous to the
environment.

Hazard

is defined as a measure of the inherent (intrinsic) capacity
of a substance to cause an adverse response in a living organism (OECD 1995).
Organisms will be placed at possible risk if the substance enters the environment,
with the degree (probability) of risk related to the hazardous nature of the substance
and the amount of exposure that occurs. Therefore, substances that are very
hazardous have a greater likelihood of causing environmental injury in the case
of spills or other accidents than those that are less hazardous. Hazard assessment
is differentiated from risk assessment in that it does not quantitatively evaluate
exposure and deals with inherent properties, not probabilities. Measures of per-
sistence, such as biodegradation and hydrolysis, may be viewed as surrogates of
biota exposure to different substances. There have been several primary uses of
hazard information:
• environmental hazard classification of substances;
• ranking and/or selection of priority substances;
• Selection of contaminated sites for further evaluation;
• derivation of water, soil, and sediment quality guidelines or criteria for
individual substances; and
• ecological risk assessments, both site-specific (i.e., local) and generic (i.e.,
regional), in conjunction with appropriate exposure data.
A more detailed discussion on hazard assessment of metals is presented in Adams
et al. (2000) and Fairbrother et al. (2002).
The scientific community and many regulators recognize that there are significant
challenges associated with the application of traditional PBT hazard evaluation tools

for inorganic metals and metal substances (collectively termed metals) and that
additional tools and techniques may be needed for the proper hazard identification
and risk assessment of metals. Further, it is understood that hazard (and risk)
assessment must be performed in such a way as to ensure that all substances are
evaluated equally and fairly while ensuring that both the environment and human
health are protected.
Key issues associated with the application of PBT concepts to metals are as
follows (full details are provided in the respective chapters):

Persistence (Chapter 3):

Traditional degradation mechanisms used for
organic substances to evaluate persistence (or the converse, biodegradation)
of metals have been criticized as inappropriate (Canada/European Union
1996). A key question remains as to whether alternative mechanisms and
measurements are needed for metals and, if so, which of these are accept-
able and under what conditions do they apply? Although it is recognized

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