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RESEARCH STRATEGY
Global Change Research Program

Peer Review Draft, September 2000

Office of Research and Development
U.S. Environmental Protection Agency


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Disclaimer

This document is a draft for review purposes only and does not constitute U.S. Environmental Protection
Agency policy. Any mention of trade names or commercial products does not constitute endorsement or
recommendation for use.

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TABLE of CONTENTS

List of Tables	 iv

List of Figures	 iv

Authors and Contributors	v

Executive Summary 	1

Preface	5

Purpose of Research Strategy	6

Context for the Global Change Research Strategy	7

Global Change Research Program Purpose 	7

Consistency of Research Strategy with ORD Strategic Plan

and Responsiveness to GPRA 	7

Support to EPA Regulatory and Regional Offices 	8

The U.S. Global Change Research Program 	8

CPA's Role in the USGCRP 	8

National Assessment	8

The International Policy Process: Involvement in the

Intergovernmental Panel on Climate Change (IPCC) 	10

Program Capabilities 	11

National Program Director Leadership	10

Intramural Capabilities: Utilizing Global Change Program Labs and Centers	10

Extramural Capabilities: Utilizing the STAR Grants Program	13

The Integral Role of Stakeholders	13

Effectively Managing Information	14

Measures of Program Success 	15

Assessment Orientation	15

The Assessment Process	15

Stakeholder Involvement	16

The Relationship Between Assessment and Research	16

Strategic Principles 	17

Program Focus Areas 	18

Introduction and Criteria for Prioritizing 	18

Focus Area I: Human Health	20

Assessing the Effects of Global Change on Human Health 	20

Weather-related Morbidity	22

Water- and Vector-borne Diseases 	22

Air Pollution-related Health Effects	23

Additional Considerations	23

Making the Connection — from Adaptation Research to Assessment 	23

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Focus Area II: Ecosystems 	26

Assessing the Effects of Global Change on Ecosystems 	26

Aquatic Ecosystems	26

Making the Connection — from Ecosystem Research to Assessment 	27

Nonindigenous Invasive Species	28

Ecosystem Services	29

Focus Area III: Air Quality 	31

Assessing the Effects of Global Change on Air Quality	31

Making the Connection — from Air Quality Research to Assessment 	33

Adaptation — Potential Human Responses and Co-benefits 	33

Focus Area IV: Water Quality	36

Assessing the Effects of Global Change on Water Quality	36

Pollutants and Microbial Pathogens	36

Making the Connection — from Water Quality Research to Assessment 	37

Biocriteria 	37

Epilogue	41

Glossary and Important Concepts	42

Appendix A: Historical Overview 	44

Appendix B: The Global Change Research Act of 1990 		47

References	49

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LIST of TABLES

Table 1. The flow of assessment and research activities through FY2010 	4

Table 2.	Relationship of the Assessment Orientation of the Global Change Program to

ORD's Long-Term Goals	8

Table 3. Major Focus Areas of USGCRP Agencies, by Program Element	9

Table 4. Research and Assessment in Focus Area I: Human Health 	24

Table 5. Research and Assessment in Focus Area II: Ecosystems	29

Table 6. Research and Assessment in Focus Area III: Air Quality	34

Table 7. Research and Assessment in Focus Area IV: Water Quality 	38

LIST of FIGURES

Figure 1. Assessment in the Global Change Research Program 	16

Figure 2. Potential Health Effects of Climate Change and

Stratospheric Ozone Depletion	20

Figure 3. Components of an Integrated Air Quality Assessment	32

Figure 4. Budgetary History of Global Change Research Program	44

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AUTHORS and CONTRIBUTORS

Members of Global Change Research Program
Research Coordination Team (RCT) as of July 2000

Joel D. Scheraga,	Douglas McKinney, NRMRL

National Program Director	John Meckley, ORMA

Thomas Barnwell, NERL	Bill Russo, NHEERL

Robert Fegley, OSP	Bernice Smith, NCER

National Center for Environmental Assessment Writing Team

John Furlow	Susan Herrod Julius

Janet L. Gamble	Catriona E. Rogers

Anne Grambsch

Contributing Authors

Gary Ankley, NHEERL
Peter Beedlow, NHEERL
Curtis M. Edmonds, NERL
Robert V. Hendriks, NRMRL
K. Bruce Jones, NERL
Johnnie Johnson, NHEERL
Hal Kibby, NHEERL
Ray R. Lassiter, NERL
Barbara Levinson, NCER

Deborah R. Mangis, NERL
Jennifer Orme-Zavaleta, NHEERL
William J. Rhodes, NRMRL
Jack H. Shreffler, NERL
A1 Solomon, NHEERL
Hal Walker, NHEERL
Barbara Walton, NHEERL
Ray Wilhour, NHEERL
Richard G. Zepp, NERL

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I RESEARCH STRATEGY

Global Change Research Program
Office of Research and Development

EXECUTIVE SUMMARY

Earth's environment is constantly in flux. A
complex interplay of natural processes and human
activities foster wide-ranging change. Climate
change and variability, change in land-use patterns,
and change in UV radiation all are occurring on a
global scale. The potential consequences of these
global changes include adverse effects on human
health, ecosystems, and socioeconomic well-being.
Policy makers and resource managers recognize
that decisions made today may have important
long-term ramifications for the Earth system.
Providing them with comprehensive assessments of
potential consequences allows them to anticipate
and to avoid or adapt to coming changes. The
purpose of the Global Change Research Program is
to provide scientific information to stakeholders
and policy makers in order to support them as they
decide whether and how to respond to the risks and
opportunities presented by global change.

The Research Strategy of the Global Change
Research Program articulates a vision of the
Program's long-term goals for developing
comprehensive assessments of global change issues
and the research to support such efforts. The
Strategy reflects the significant redirection of the
Program towards an emphasis on assessing the
consequences of global change. This new direction
is a response to several factors: the Congressional
mandate in the Global Change Research Act of
1990 that is strongly restated in the U.S. Global
Change Research Program's (USGCRP) planning
process (see Our Changing Planet, 1998, 1999,
2000); direction provided by external peer
reviewers in a 1997 independent evaluation of
ORD's Global Change Program draft research
strategy; and the guidance contained in the National
Research Council's Pathways report which set the
stage for a reorientation of the USGCRP (1999).

The new focus is on areas where EPA enjoys a
comparative advantage relative to other federal
agencies and where EPA can truly make a
difference.

Over the next decade, the Global Change Program
plans a series of research and assessment activities
culminating (in FY 2010) in a multi-sector, multi-
region assessment of the consequences of global
change in the US. These activities address those
topics that represent the greatest risks to people and
their environment, have demonstrated policy
relevance, and show promise for extending the
research community's assessment capabilities.

Assessment is an iterative, analytic process that
engages both analysts and stakeholders in the
evaluation and interpretation of the interactions of
dynamic physical, biological, and social systems.
The goal of assessment is to communicate insights
about the possible consequences of global change
and the potential for adaptive responses to the
affected parties. Research and assessment are
parallel and complementary activities. Assessment
guides the foundation research program by
identifying knowledge gaps and prioritizing research
needs. Research, in turn, generates the flow of
scientific and socioeconomic information needed in
the assessment process. In planning for this
ongoing, iterative research and assessment process,
the Global Change Program ensures that the most
timely topics are considered and that research
needs and knowledge gaps are addressed.

The emphasis of the Program's research and
assessment strategy is on understanding the risks
and opportunities presented by global change, the
interdependent and interactive effects of multiple
stresses, the human dimensions of global change
(human activities that catalyze as well as those that

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respond to global change), and adaptation options.
The Global Change Program is unique among
ORD's research activities in that its goal is not to
study current conditions and processes, but rather
to build upon ongoing research to examine possible
future changes and their influence on issues that are
important to the public. ORD's air, water,
ecosystems, and human health research programs
provide monitoring, modeling, and process
information that the Global Change Program can
use to develop scenarios to assess possible impacts
of changes in climate and land use on human
health, ecosystems, and socio-economic well-being
in the United States.

Table 1 provides a brief overview of the research
and assessment activities planned for the Global
Change Program through FY 2010. The four or
five-year time periods allotted to each activity
reflect the coupling of research and assessment
efforts that comprise each assessment activity.

This time period is somewhat arbitrary (reflecting
the timing of project reports) and does not
foreclose the option of continued work.

The other important feature of this plan is the flow
of work within and across focus areas. Related
activities are arranged in a logical sequence. For
instance, the assessment of water-borne illnesses is
conducted in parallel with assessments of aquatic
ecosystems and of aquatic pollutants and microbial
pathogens. Likewise, the human health assessment
of the effects of tropospheric ozone under
conditions of global change occurs after the air
quality assessment of the global change impacts on
ozone.

The Global Change Program has made a major
commitment to and plans continued involvement in
National Assessment activities organized through
the USGCRP. The National Assessment is an
ongoing process with scheduled reports to Congress
in FY 2000, 2004, and 2008 (indicated by darker
shading in Table 1) as mandated in the 1990 Global
Change Research Act.

The first of four focus areas is Human Health.

Since health is affected by a variety of social,
economic, political, environmental, and
technological factors, assessing the health impacts
of global change is a complex challenge. As a
result, health assessments in the Global Change

Program will need to look beyond epidemiological
and toxicological research to develop integrated
health assessment frameworks that consider the
effects of multiple stresses, their interactions, and
adaptive responses. Along with three health
assessments conducted in conjunction with the
USGCRP National Assessment process, there will
be research and assessment activities examining the
consequences of global change on weather-related
morbidity and vector- and water-borne diseases.
Results from the air quality assessments will be
utilized in the assessments of the health
consequences associated with exposures to
tropospheric ozone and particulate matter.

The second focus area is Ecosystem Health. The
EPA's mission is not only to protect human health
but also to safeguard the natural environment.
EPA pledges to provide environmental protection
that "contributes to making communities and
ecosystems diverse, sustainable, and economically
productive" (EPA 1997). Three research and
assessment activities are planned that evaluate the
effects of global change on 1) aquatic ecosystems
(which may include lakes, rivers, streams,
wetlands, and estuaries); 2) nonindigenous invasive
species; and 3) ecosystem services. The
assessment of aquatic ecosystems will contribute to
the Water Quality assessment of biocriteria. The
ecosystem services assessment will draw on work
from the preceding ecosystem and water quality
assessments. All three assessment activities will
contribute to the National Assessment process.

The third focus area is Air Quality. Few studies
have investigated the effect of global change on air
quality. Examining the effects of global change on
air quality is a logical focus of the Global Change
Program, given EPA's legal mandates with respect
to air pollution and substantial capability and
expertise in modeling air quality and evaluating
integrated responses. Assessments are planned that
will examine the potential consequences of global
change on tropospheric ozone and particulate
matter. Each of these assessments is paired with a
related Human Health assessment. Once again,
these assessment activities are designed to support
the National Assessment process.

The fourth focus area is Water Quality. Water
quality is affected by changes in runoff following
changes in precipitation and evapotranspiration

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and/or changes in land use. ORD plans two
assessments of the possible impacts of global
change (climate and land-use change) on water
quality. Both water quality assessments will either
contribute to or benefit from Human Health and
Ecosystems assessments. In addition, results from
the assessment of pollutants and microbial
pathogens will be used in the assessment of
biocriteria. These assessment will also contribute
to the National Assessment process.

The culmination of the 11 assessments and the
National Assessment activities is a multi-sector,
multi-region assessment of the consequences of
global change for human health, ecosystems, and
socioeconomic well-being in the United States
scheduled for completion in FY2010. This
assessment will synthesize and elaborate prior
work.

Intramural and extramural research will provide
crucial material to all of the assessments.

Intramural efforts will be conducted through EPA's
National Center for Environmental Assessment
(NCEA), the National Exposures Research Lab
(NERL), the National Health andEnvironmental
Effects Research Lab (NHEERL), and the National
Risk Management Research Lab (NRMRL). In
addition, a significant portion of the program's
resources are dedicated to extramural research
grants administered by the National Center for
Environmental Research (NCER) through the
STAR (Science to Achieve Results) grants
program. The STAR program focuses on two
principal areas related to global change research —
science to support assessments of the
consequences of global change and human
dimensions research.

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Table 1. The flow of assessment and research activities in ORD's Global Change Research Program
through FY 2010.



Research and Assessment Activities in the

F

Y
?

F

Y
?

F

Y
9

F

Y
9

F

Y
9

F

Y
9

F

Y
9

F

Y
9

F

Y
9

F

Y
9

F

Y
9



Global Change Research Program9

0
0
0

0

0

1

0
0

2

0
0
3

0
0
4

0
0
5

0
0
6

0
0
7

0
0
8

0
0
9

0

1
0

USGCRP National
Assessments

Regional issues and human health b





1





1





HUMAN HEALTH

Climate change effects on weather-related morbidity c























Climate and land-use change effects on water
and vector-borne diseases











1











Health effects of tropospheric ozone under global change























Health effects of particulate matter under global change



















ECOSYSTEMS

Global change effects on aquatic ecosystems







¦















Global change effects on nonindigenous invasive species























Global change effects on ecosystem services d

¦















AIR QUALITY

Global change effects on air quality — tropospheric ozone







¦















Global change effects on air quality — particulate matter





















WATER QUALITY

Global change effects on water quality —
pollutants and microbial pathogens











1













Global change effects on water quality — biocriteria

















1





MULTI-SECTOR

Synthesis assessment of the consequences of global change for
human health, ecosystems, and social well-being in the US





















1

NOTE: The darker shading indicates the year in which an assessment report is due. Lighter shading indicates years in which the assessment
and research process is underway.

a Additional activities occur each year through the extramural STAR grants program. However, the nature and scope of these research grants
is difficult to anticipate prior to development of the Request for Applications. The STAR grant program contributes to the assessment process
by sponsoring research to support assessment activities (e.g., the development of models of human dimensions or of the effects of multiple
stressors) that benefits the scientific community at-large.

B The National Assessment process is ongoing. Thus, the representation of continual Global Change Program effort with reports to Congress
required no less than every four years, in FY 2000, 2004, and 2008.

c Each activity outlined in the table assumes that a concurrent process of research and assessment will be carried out across a four or five
year period resulting in a final assessment report as well as independent research reports. In addition to assessments of consequences of
global change, analyses of the interplay of human dimensions and of possible adaptation responses will be included in assessment activities.
d The FY 2000 ecosystem services activity reflects completion of a preliminary analysis planned and initiated prior to FY 2000.

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PREFACE

This document presents the research strategy for
the Global Change Research Program of the
Environmental Protection Agency's (EPA) Office
of Research and Development (ORD). While the
program is not new, this Strategy reflects a major
redirection of the program. ORD began conducting
research in Global Change in 1990 at the time of
the passage of the Global Change Research Act
and the establishment of the U.S. Global Change
Research Program (USGCRP).

Much of the research from 1990-1996 was focused
on atmospheric stabilization of the buildup of
carbon dioxide and other greenhouse gases. This
research emphasized terrestrial ecosystem-
atmosphere carbon cycling; biomass burning
detection; regional climate scenarios; comparative
technology assessments and evaluations; specific
greenhouse gas reduction technologies; effects
research; and strategies for enhancing biospheric
carbon storage. The research involved a
combination of experimental, remote sensing, and
modeling research, especially related to carbon
cycling, greenhouse gas emissions, development of
an Earth Systems Model, and control technologies.
A list of publications from this era of the Global
Change Program is included in Appendix A.

In 1997, three important events occurred which
required ORD to re-evaluate its Global Change
Research Program. First, an external peer review
was critical of a program strategy written in 1996.
Second, ORD experienced nearly a 50% reduction
in appropriations for global change research.

Third, the USGCRP requested that EPA redirect
its program to emphasize the assessment of the
consequences of global change.

After a decade of basic research on climate change,
variability, and other global change, the agencies of
the USGCRP believe it is time to focus on
understanding the Earth system as a whole, the
dynamics of environmental change, and the
connection of that knowledge to societal needs. An
effort is being made to eliminate programmatic
overlap among USGCRP member agencies and to
ensure that agencies contribute in those areas
where they have the greatest comparative

advantage. ORD's Global Change Program's
advantage is in assessing the consequences of
global change in the United States.

In response to the USGCRP request and to the
findings of the 1997 peer review, ORD created the
position of National Program Director for Global
Change Research (in 1998) to guide the
restructuring and to coordinate research and
assessment activities across ORD Laboratories and
Centers. Since that time, the program has
undergone important changes. Global Change
Program activities have been optimized given
budget limitations to focus on those areas where
EPA has the most to offer — assessments of the
consequences of global change on air quality, water
quality, human health, and ecosystem health.

These four areas were selected because they are 1)
areas where EPA has recognized expertise among
government agencies; 2) areas that are consistent
with the mandate and goals of the USGCRP; and
3) areas where EPA can make a difference. This
strategy establishes a rationale for a coherent
framework through which ORD will assess the
consequences of global change in these four areas.

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PURPOSE of the RESEARCH STRATEGY

Earth's environment is constantly changing due to
the complex interplay of both natural processes and
human activities. Evidence from scientific research
has begun to show that humans play an important
and expanding role as agents of global
environmental change. Many of these changes
cannot be reversed quickly, if at all, due to the long
time cycles associated with many of the Earth's
systems. The potential consequences of global
change are wide-ranging and could adversely affect
human health, ecological systems, and
socioeconomic interests, all of which are vital to
sustainable development.

Policy makers and resource managers have begun
to recognize that decisions made today may have
important long-term ramifications for the Earth
system. As global change increasingly becomes an
issue of national and international policy, the
importance of research into the consequences of
global change grows. Human adaptation to global
environmental change will be critical in reducing
adverse impacts and realizing the benefits of new
opportunities. New scientific tools will be needed
to understand and respond to global environmental
risks. Global change research is an important
investment for the future of the nation, its
economy, and its citizens.

This document, the Research Strategy for the
Global Change Research Program, articulates a
vision for the long-term goals of the program. Since
1997, the Program has been redirected to become
more assessment-oriented in response to: 1)
Congressional mandates in the Global Change
Research Act of 1990; 2) a 1997 external peer
review of the program's research strategy; and 3)
guidance provided in the National Research
Council's "Pathways" report (1998). The
Research Strategy is intended to be a living
document and will be updated to remain current
with end-user needs and with the state of the
science in global change research.

Publication of this Research Strategy is consistent
with requirements of the new Government
Performance and Results Act (GPRA). GPRA
calls for federal agencies to provide the Congress
with "performance goals" and "performance

measures" through which work is monitored and
performance appraised. The Global Change
Program has developed a timeline that establishes
interim performance goals necessary to achieve the
Program's long-term goal for 2010.

The Research Strategy describes the direction of
the Program, not its implementation. As a result, it
provides only the framework components of the
research and assessment process, not a listing of
specific projects. Detailed project implementation
plans are documented and reviewed separately
from the Strategy. They are developed annually
based on Congressional budget appropriations.
ORD's ability to achieve the long-term goals of the
Global Change Research Program and to fulfill its
role under the Global Change Research Act of
1990 will depend in part on adequate Congressional
appropriations.

This document provides an overview of the critical
activities of the Global Change Program for the
next ten years. The first section, Context of the
Global Change Program Strategy, describes how
the goals and vision outlined in this Strategy relate
to planning within ORD, the mandate of the
USGCRP, and work in the international
community. The next section, Program
Capabilities, outlines the management structure and
extramural and intramural capacities of the
Program. Immediately following is a box that
describes the Measures of Success used to evaluate
the Program's effectiveness. The next section,
Assessment Orientation, describes key strategic
principles that guide the Program's research and
assessment efforts. The final section, Program
Focus Areas, identifies and provides justification
for the four areas upon which the Program focuses
its research and assessment activities — the
potential effects of global change on human health,
ecosystems, air quality, and water quality. It also
outlines the criteria that are used to decide which
projects will be undertaken by the Program.

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CONTEXT of the GLOBAL CHANGE PROGRAM STRATEGY

Global Change Research Program Purpose

The purpose of the Global Change Research
Program is to provide scientific information to
stakeholders and policy makers to support them as
they decide whether and how to respond to the
risks and opportunities presented by global change.
These assessments will not offer policy guidance
— policy must reflect the values of those affected
and the constraints of political and social
institutions and fiscal realities — but will provide
the scientific underpinnings to inform the policy
making process.

Consistency of Research Strategy with ORD
Strategic Plan and Responsiveness to GPRA

The development of this Strategy complements the
Office of Research and Development's Strategic
Planning Process. The ORD strategic vision is to
provide the scientific foundation that supports
EPA's mission. That mission is divided into four
elements: 1) to perform research and development
activities; 2) to provide technical support; 3) to
integrate the work of ORD's scientific partners;
and 4) to offer leadership in addressing emerging
environmental issues (USEPA 1997a).

The Global Change Research Program has a
similar, multi-part mission that is consistent with
the ORD mission. The mission of the Global
Change Program is to:

#	improve the scientific basis for evaluating
effects of global change in the context of other
stressors and human dimensions;

#	conduct assessments of the consequences of
global environmental change; and,

#	improve society's ability to effectively respond
to the risks and opportunities presented by
global change as they emerge.

The Research Strategy is also consistent with
requirements of the Government Performance and
Results Act (GPRA), which require agencies to
provide the Congress with measurable "annual
performance goals" and "performance measures."
In response to GPRA, the Global Change Program
has developed a timeline that establishes interim
performance goals necessary to achieve the

Program's long-term goal for 2010 (see Table 1).

The long-term goal of the Global Change Program
is to understand and articulate, in terms that are
meaningful for decision-makers and other
stakeholders, the consequences of global
environmental change for human health,
ecosystems, and social well-being in the U.S.

Global change is a broad concept that can include
many things that influence the Earth system. To
narrow the potential scope of the program while
ensuring consistency with the short- and long-term
objectives of the USGCRP, the Global Change
Program will focus on the following stressors and
interactions:

#	The potential consequences of climate change
and climate variability. EPA's focus on
climate change and variability is in keeping with
USGCRP's First National Assessment. Air and
water quality — the protection of which is
EPA's mandate — may be strongly influenced
by climate change. Such effects must be
understood to meet the Agency's basic mission.

#	The effects of UV radiation. Here, EPA's
primary concern is the effect of changes in UV
radiation on ecosystems, their components, and
the services they provide.

#	The effects of land-use changes. Further
understanding is needed regarding how to
assess the underlying processes that determine
how land-use change interacts with climate
change to affect land cover, ecosystem
services, hydrologic cycles, species distribution,
biodiversity, and social and economic systems.

ORD's strategic plan articulates six long-term,
overarching goals (see Table 2). These goals are
intended to inform decisions about research
directions for years to come. Together with more
specific research objectives, the goals also provide
greater accountability for results (as required by
GPRA). The Global Change Research Strategy
was developed with these goals in mind.

Conducting assessments and the research to support
assessments is consistent with ORD's long-term
goals.

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Table 2. Relationship of Assessment Orientation of
Global Change Program to ORD's Long-Term Goals.

ORD's Long-Term

Assessment Orientation of

Goals

Global Change Program

Develop scientifically

/Assess potential

sound approaches to

consequences of global

assess and characterize

change for human health,

risks to human health

ecosystems, and social well-

and the environment

being

Integrate human health

Assess global change in

and ecological

context of risks to multiple

assessment methods in

systems; integrate methods in

comprehensive

holistic framework

multimedia methods



Provide common sense,

Conduct assessments to

cost-effective

provide critical findings to

approaches to prevent

stakeholders about the nature

and manage risks

of global change risks and



adaptation options

Provide credible, state-

Provide credible, state-of-the-

of-the-science risk

science assessments of

assessments, methods,

potential consequences of

models, and guidance

global change

Exchange reliable risk

Utilize assessment findings to

assessment/risk

communicate reliable risk

management

information to stakeholders

information with



stakeholders



Provide leadership to

Provide leadership in the

identify emerging

conduct of assessments to

environmental issues,

characterize key risks

characterize risks

associated with global change

associated with these

and to describe adaptive

issues, and develop

responses to reduce risks

ways to prevent or



reduce risks



Support to EPA Regulatory and Regional Offices

The assessments described in this Strategy will
support EPA's Program and Regional Offices by
providing insights regarding possible future
conditions of the resources within their oversight.
For example, the Office of Air and Radiation has a
strategic goal of bringing all areas of the country
into attainment with the National Ambient Air
Quality Standards (NAAQS) for ozone and
particulate matter (PM) by 2012 (USEPA 1997b).
The Global Change Program plans an assessment
of the consequences fo global change on
tropospheric ozone and PM under different climate
scenarios, including assessing the ability of
communities to achieve the NAAQS. Health
assessments will build on the air quality
assessments to project potential health effects. The
Global Change Program will work with the

Program and Regional Offices to ensure that
assessments address issues of concern.

The U.S. Global Change Research Program

The USGCRP was created as a Presidential
Initiative in 1989 and formalized in 1990 with
congressional passage of the Global Change
Research Act (see Appendix B). The global change
research activities of all participating federal
agencies are coordinated to ensure that the overall
goals of the USGCRP are achieved. At the same
time, agencies are assigned responsibilities that are
consistent with their own missions and take
advantage of their respective areas of expertise (see
Table 3) (USGCRP 1999). Interagency
partnerships are encouraged and duplication of
efforts avoided. Through the USGCRP, the global
change research activities of multiple agencies are
coordinated and "a comprehensive program of
scientific research and assessment on the multiple
issues presented by climatic and other changes in
the Earth system" is supported (Subcommittee on
Global Change Research, 1999, p.l). For
additional information see www.usgcrp.gov.

EPA's Role in the U.S. Global Change Research
Program

Among the USGCRP member agencies, EPA is
responsible for assessing the potential consequences
of global change on human health, the environment,
and social well-being in the United States. The
involvement of the EPA Global Change Program in
the USGCRP is consistent with the National
Academy of Sciences" recommendation to engage
in "a formal process" to "identify and coordinate
areas of research that are supported by multiple
agencies" (NAS 1999). ORD's Global Change
Program responded with a redirection towards a
more assessment-oriented program in 1998.

National Assessment

The Global Change Research Act of 1990 mandates
the preparation of periodic scientific assessments of
the potential consequences of global change for the
United States. The goal of the first National
Assessment is to determine the regional and national
implications of climate change and variability for the
people, environment, and economy of the United

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States in the context of other, non-climate
(environmental, economic, and social) stresses.
The first National Assessment emphasizes a
process driven by the needs of stakeholders —
persons best positioned to identify important
information needs and optimal ways of responding.
The National Assessment is founded on the
principles of scientific excellence and openness.

The first National Assessment includes 19
geographic regions, five sectors (human health,
coastal areas and marine resources, forests,
agriculture, and water resources), and an overall
synthesis. These different elements provide
perspectives from multiple scales and for different
audiences. Currently, EPA co-chairs the National
Assessment Working Group (NAWG), the federal
interagency group overseeing the Assessment
Process.

Table 3. Major Focus Areas of USGCRP Agencies, by Program Element



Agency

Program Element

DOC/
NOAA

DOE

DOI/
USGS

EPA

HHS/
NIH

NASA

NSF

SI

USDA

Understanding the Earth's Climate System

!

!

!





!

!





Atmospheric Composition & Chemistry

!

!







!

!



!

Global Water Cycle











!







Carbon Cycle Science

!

!

!





!





!

Biology & Biochemistry of Ecosystems



!

!

!





!

!

!

Human Dimensions of Global Change
(including Assessment of Consequences)







!

!





!



Paleoenvironment/Paleoclimate













!

!



(NOTE: Area was considered major if constituted 10% or more of agency spending on global change research. Source: Our Changing
Planet: The FY2000 U.S. Global Change Research Program)

EPA also sponsors the Mid-Atlantic Regional
Assessment, the Great Lakes Regional Assessment,
the Gulf Coast Regional Assessment, and the
Health Sector Assessment in this first National
Assessment. The Global Change Program will be a
major participant in subsequent National
Assessments, which are to be conducted no less
than every four years. Additional information on
the National Assessment can be found at the
USGCRP web-site (www.nacc. usgcrp.org).

Conducting assessments of the consequences of
global change at regional scales is consistent with
ORD's Ecological Research Strategy (Linthurst et

ctl. 2000). ORD's ecological research program
strives to understand relative ecological risks in the
context of multiple stressors, at multiple scales and
multiple levels of biological organization. The
integrative techniques articulated in the Ecological
Strategy suggest that research be conducted at
"places" or regional-scale settings, such as the Mid-
Atlantic, the Great Lakes or the Gulf Coast. EPA
has long emphasized the importance of
understanding environmental consequences from a
regional perspective. Thus, this Strategy remains
consistent with the Agency's strategic direction.

The International Policy Process: Involvement in

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the Intergovernmental Panel on Climate Change
(IPCC)

The Intergovernmental Panel on Climate Change
was established by the United Nations Environment
Programme (UNEP) and the World Meteorological
Organization (WMO) in 1988 to assess scientific
information about climate change relevant to
international and national policy formulation. The
United States, through the USGCRP, has
consistently played a leading role in the IPCC, by
co-chairing working groups and by supporting the
world's most comprehensive set of climate
research activities. ORD's Global Change Program
contributes to the IPCC effort directly through
scientific information produced by EPA researchers
and through involvement as lead and contributing
authors, review coordinators and reviewers of
IPCC Reports, and indirectly through participation
in the National Assessment of the Potential
Consequences of Climate Variability and Change
for the United States. Additional information on
the IPCC, the Second Assessment report, the
upcoming Third Assessment report, and other
IPCC Special Reports and Technical Papers is
available at the IPCC web-site (www.ipcc.ch).

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PROGRAM CAPABILITIES

National Program Director Leadership

The agency-wide GPRA goal for effective
management guides the Global Change Program's
internal management plan. Strong management
encompasses "effective vision and leadership;
sound management practices; results-based
planning and budgeting; fiscal accountability; and
quality customer service" (EPA 1999, p. x-1).
Building an integrated program based on uniform
objectives is key to implementing effective
management in the Global Change Program. To
provide leadership in this process, a National
Program Director was appointed in 1998.
Establishing overall leadership for the Global
Change Program addressed a need for centralized
program management identified by the peer
review panel (1997) and reflects ""ORD's strong
commitment to specific emerging research
efforts" (February 1999 memorandum from
Assistant Administrator Norine E. Noonan
announcing the National Program Director
positions). The National Program Director is
responsible for coordinating planning and
implementation efforts (in conjunction with the
Research Coordination Team), for resource
allocation recommendations to the Executive
Council (ORD senior management), for reporting
on progress, and for programmatic review. The
responsibility for program implementation
remains with the lab or center conducting the
activity.

Intramural Capabilities: Utilizing Global
Change Program Labs and Centers

The Global Change Program is designed around
both intramural and extramural components. The
intramural component includes both research and
assessment activities coordinated across multiple
ORD laboratories and centers. The extramural
component consists of grants administered
through ORD's Science to Achieve Results
(STAR) program. Deciding how Program work
is best accomplished — whether through
intramural or extramural activities — is based on
several factors: 1) the type of work or expertise
required; 2) the urgency of the need for a
particular product; 3) the extent to which

involving multiple institutions provides added
value; 4) the opportunities for leveraging
resources; and 5) the extent to which there is a
need to support basic, independent research to
advance the assessment capabilities of the
scientific community at large. Guidance for
cross-lab efforts is provided by a Research
Coordination Team with representation from each
of ORD's labs and centers. Specific projects
undertaken by ORD labs and centers are
identified by the Research Coordination Team
every year and outlined in each lab's Annual
Implementation Plan. An annual meeting of the
multi-lab team provides an additional opportunity
for reviewing program-wide work.

Each of EPA's labs and centers has specialized
expertise. The use of these skills is coordinated
by the National Program Director, in partnership
with the Research Coordination Team, to meet
the assessment goals outlined in Table 1. A
detailed description of the specific assessments
planned for each of the program's four focus
areas appears later in this Strategy. The focus
area discussions outline the specific steps that are
necessary to complete the scheduled assessments
and refer back to the following descriptions of lab
and center capabilities.

The National Exposures Research
Laboratory's (NERL) activities involve
experimental and modeling research. The
NERL's in-house research program provides the
capability to assess the vulnerability of aquatic
ecosystems and water quality to global change.
In addition, the NERL has expertise in air quality
modeling that can contribute to the assessment of
the consequences of global change for air quality.
Finally, NERL can contribute to the assessment
of the exposure of ecosystems to UV radiation.

Through the NERL, the EPA Global Change
Program currently supports (in cooperation with
the National Park Service) a network of
continuously operated stations monitoring UV
radiation at a range of longitudes, latitudes, and
elevations across the U.S. The UV monitoring
network was established in 1992 to provide
reliable data to 1) improve understanding of the

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status and trends in UV flux, temporally and
spatially, 2) to characterize the physical and
chemical parameters that modify UV flux, and 3)
to improve radiative transfer models and
inferences that can be drawn from them,
including consequences of UV exposure for
human and ecological health. Data from these
monitors make it possible to evaluate the intensity
of and trends in UV radiation reaching the Earth's
surface and can be used as input for human and
ecological assessments.

An important component of global change over
the next 30-40 years will be land use or land
cover change in watersheds and basins. These
changes, which are largely driven by human
activities, will interact with other changes, such as
climate and UV change, to alter aquatic
ecosystem functioning and structure with
concurrent effects on drinking water quality,
diversity of aquatic life, and resilience to
catastrophic flooding. NERL is focusing its
expertise on the following issues related to global
change: 1) development of landscape indicators
and indicators of surface water conditions; 2)
research into the interactions between aquatic
ecosystem functioning and changes in climate,
UV, and land use; and 3) evaluation of UV
radiation exposure in aquatic ecosystems.

The National Health and Environmental
Effects Research Laboratory's (NHEERL) in-

house research program is focused primarily on
improving capabilities to assess global change in
two areas: 1) research on the effects of UV
radiation on ecosystem health; and 2) research on
the effects of global change on coastal
ecosystems. These activities are coordinated with
other USGCRP agencies, such as the U.S.
Geological Survey, to ensure that EPA's efforts
are not duplicative of other programs.

An important component of understanding the
consequences to ecosystem health is evaluating
the world-wide decline in amphibians. NHEERL
will be conducting research into the
interrelationships of UV radiation, exposures,
chemical contamination, nonindigenous species,
and climate change on the decline of amphibians
and the occurrence of morphological
malformations in populations in the upper Mid-
west. It is plausible that multiple factors are at

work and that climate change and UV radiation
act as exacerbating stressors to chemical
contamination and habitat loss.

Another component of NHEERL's research is in
understanding the consequences of climate
change on coastal ecosystems, specifically on the
Gulf Coast and along the Atlantic Coast from the
mid-Atlantic to New England. Research will
focus on the interrelationships of multiple
stressors on coral ecosystems in the Florida Keys
and in evaluating the change in the environmental
quality of estuaries and coastal watersheds along
the Atlantic Coast. The changes in environmental
quality reported from EPA's Environmental
Monitoring and Assessment Program (EMAP) for
the Atlantic Coast may be due, in part, to changes
in the climate cycle (US EPA 1998). For
example, climate change effects on sea level and
changes in rainfall patterns can alter the water
cycle in coastal watersheds. These changes can
lead to increased nutriflcation and subsequent
reduction in oxygen levels in the coastal estuaries.
In turn, the altered system may result in
conditions that favor invasive species over native
organisms.

Researchers in the National Risk Management
Research Laboratory (NRMRL) are focused on
developing methods, models, and data required to
assess the multiple or co-benefits of adaptation
strategies needed to protect air and water quality
under a variety of climate change scenarios.

Their goal is to develop options for risk
management (i.e. adaptation) that may be
pursued in response to the potential consequences
of climate change. NRMRL researchers are
examining how climate-induced changes will
impact other environmental problems that pose
health and environmental risks such as
tropospheric ozone and drinking water
contamination while identifying approaches (both
technological and socioeconomic) to adapt to
those changes. Initial work will investigate the
influence of future transportation fuel choices and
renewable energy options and their relationship to
climate change. In addition, NRMRL will study
climate and land use change impacts on water
quality.

Much of the infrastructure now in place to
prevent or control releases of environmental

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contaminants is based on ORD research.

Expertise in developing and testing air pollution
control, drinking water treatment, and wastewater
treatment technologies as well as capabilities to
model and analyze watersheds, surface water
systems, storm water runoff, and groundwater
systems can be utilized to assess the potential
viability of adaptations to climate change. For
example, existing expertise in air pollution control
technology can be directly applied to identifying
potential adaptation options for increased
tropospheric ozone under conditions of climate
change.

NRMRL has the capability for undertaking a
variety of analyses relevant for assessments of
co-control benefits, including 1) estimation of the
amount and type of reduction in ozone precursors
or particles that must be implemented to meet
current National Ambient Air Quality Standards
(NAAQS) under future climate conditions; 2)
evaluation of how future technological and
societal choices may alter global change impacts;
3) evaluation of how wastewater plan capabilities
may be affected under various climate scenarios;
and 4) evaluation of changes in water quality and
aquatic habitat under different temperature and
flow regimes associated with climate change.
Drawing on results from extramural grants and
EPA intramural programs, the National Center
for Environmental Assessment (NCEA) is
ultimately responsible for producing the
assessments listed in Table 1. NCEA assessors
engage both researchers and end-users to analyze,
evaluate, and interpret information from multiple
disciplines to draw conclusions that are both
timely and useful for decision makers.

NCEA also is responsible for supporting and
contributing to the Congressionally-mandated
National Assessment process. This includes
conducting multiple regional and sectoral
assessments for inclusion in periodic reports to
the Congress. EPA-sponsored assessments will
continue to be conducted through public-private
partnerships, engaging researchers from the
academic community, decision makers, resource
managers, and other affected stakeholders. In
addition, NCEA is responsible for maintaining an
orientation to stakeholder needs throughout the
assessment process.

NCEA also has an important coordination
function within the U.S. Global Change Research
Program (USGCRP). The National Program
Director, who resides in NCEA, is the Chair of
the National Assessment Working Group
(NAWG). The NAWG is composed of
representatives of the relevant federal agencies
that provide oversight to the National Assessment
process. The NAWG is the principal interagency
venue for these activities, linking agencies and
offices of the federal government to the
USGCRP and the National Assessment.

Extramural Capabilities: Utilizing the STAR
Grants Program

In order to capitalize on expertise in the academic
community, a significant portion of the program's
resources is dedicated to extramural research
grants administered through the STAR grants
program. The STAR Program's support of long-
term research promotes work in high-priority
areas of science (identified in Agency and
Program strategic plans). Managed by ORD's
National Center for Environmental Research
(NCER), the STAR Program's role consists of
competitively awarded grants offered through
Requests for Applications (RFAs) and written to
be consistent with and responsive to the Global
Change Program's strategic plan. The STAR
grants program focuses on two principal areas of
global change research: 1) science to support
assessments of consequences; and 2) human
dimensions research. Extramural grants help the
Global Change Program attain its long-term
objectives and encourage scientific work
supporting global change assessments. Because
of the nature of the grants process, grants are not
used to conduct assessments themselves. ORD
has no authority to compel grantees to respond to
stakeholder input (a key component of the
assessment process), and the timing or needs of
specific assessments cannot determine the
requirements of grant-sponsored research.

Expert peer review by independent, external
reviewers is used to evaluate proposals and
subsequent work products. In this way, the
Global Change Program's extramural research is
responsive to the National Academy of Sciences'
recommendations for the conduct of research
under GPRA that "Federal agencies should use

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expert review to assess the quality of research
they support, the relevance of that research to
their mission, and the leadership of the research"
(NAS 1999).

The Integral Role of Stakeholders

Through the grants program and collaborations
within the USGCRP and the IPCC, the Global
Change Program builds strong relationships with
scientific and stakeholder communities. The
Global Change Program has ties to EPA Program
and Regional offices, to other federal agencies
(e.g., through involvement in the USGCRP and
the National Assessment process), to the non-
governmental and academic communities (e.g.,
through STAR grants), to the international
scientific community (e.g., through IPCC
assessments), and to stakeholders (including
public health officials, water- and air-quality
managers, natural resource managers, etc.).

As an assessment-oriented program, the Global
Change Program is especially focused on
stakeholder concerns. Interacting with
stakeholders is essential to ensure that useful
information is developed, that relevant stressors
and effects are identified and investigated, and
that policy-relevant results are effectively
communicated. Stakeholder involvement has
played a central role in the conduct of the first
National Assessment. As USGCRP agencies plan
for post-2000 assessment activities, they affirm
that "close collaboration with ... resource
managers, decision makers, and other
stakeholders is essential to ensure that USGCRP
assessments adequately and accurately
incorporate and reflect the sensitivities, resilience,
and realistic adaptation options of managed and
natural systems" (National Assessment Working
Group 1999).

The Global Change Program is committed to
continuing efforts to maintain and expand
stakeholder networks established during the first
National Assessment by incorporating stakeholder
components in intramural research and external
assistance agreements and by developing a two-
way flow of information through internet access
to documents, data, and analytic tools. In
addition, the Global Change Program engages
stakeholders in workshops to develop long-term

global change research plans for air and water
quality, human health, and ecosystems.

Effectively Managing Information

In an environment in which global change issues
are featured news, where information quality is
uneven, where the subject matter is complex, and
where uncertainty is considerable, the Global
Change Program has an important role to play in
information management. Just as the Agency has
set management goals for quality customer
service and goals for the expansion of Americans"
right to know about their environment, the Global
Change Program is committed to sharing
information more broadly and in more ways than
ever before. To that end, RFAs funded by the
Global Change Program now require the
investigator to release to the EPA, for public use,
the data, tools, and documents produced during
the period of the grant or cooperative agreement.

A publicly accessible website for the Program is
currently being developed utilizing a linked
database, the Environmental Information
Management System (EIMS) (Shepanek 1997).
(The EIMS database website is accessible at:
http://www.epa.gov/eims/eims.html). The EIMS
organizes descriptive information (metadata) for
data sets, databases, documents, models,
projects, and spatial data and provides a
repository for scientific documentation accessible
with standard Web browsers. The fully
integrated EIMS database links data, documents,
and tools by concept, project, location, and/or
time frame.

The website will allow the Global Change
Program to provide access to program products,
including project descriptions, updates, and
reports, other program documents, workshop
announcements and proceedings, data, and
analytic tools. Interactive tools and models
support the decision and analytic needs of
planners, resource managers, and other data
users.

The products produced by the Global Change
Program are subject to formal peer review (when
review is appropriate), consistent with Agency-
wide guidance (EPA 1998b). Finalized materials

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are made available upon request and, as the
Global website is expanded, will be available
online as well. The Global Change Program will
actively solicit the input of clients (Program and
Regional offices, USGCRP agencies, and other
stakeholders) and will partner with them to design
more effective communication strategies.

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MEASURES of PROGRAM SUCCESS

The 1997 Update to ORD's Strategic Plan outlines four measures of success. These measures are appropriate
yardsticks for measuring the performance and products of the Global Change Research Program.

Significance — Is the Global Change Program working on the right issues?

This is a measure that stakeholders help determine and the larger scientific community can help judge. Since
stakeholder input is integral to the assessment process, the work of the Global Change Program will, by design, be
significant. With stakeholder input, the program targets areas for research that have scientific merit and that people
care about.

Relevance — Is the Global Change Program providing useful and useable information and data?

Research findings are relevant only if they respond to the stated needs of end-users and are presented in an
understandable, timely manner. Achieving and maintaining relevance is a central goal of the Program's research
and assessment activities and of information management within the Program.

Credibility — Are the Global Change Program's research and assessment activities of the highest quality?

Stakeholders and the larger scientific community are the judge. The Global Change Program's research and
assessment activities undergo rigorous peer review. The Program is committed to upholding Agency-wide peer
review policies (EPA 1998b).

Timeliness — Is the Global Change Program addressing long-term issues with adequate preparation and
fulfilling assessment and research objectives in a timely manner?

The optimal timing for research or assessment activities is not always apparent; nonetheless, the Global Change
Program has an obligation to work to identify and pursue timely topics. By soliciting input from stakeholders, the
Program is assured that the topics addressed are important to end-users now. In addition, the Program strives to
respond to customer inquiries and to release products in a timely manner.

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ASSESSMENT ORIENTATION

The Assessment Process

Assessment is a scientific process of analysis,
review, and synthesis that brings together different
groups of people with common interests to address
environmental concerns. The assessment process
ensures that researchers and decision makers
understand what issues are of greatest concern to
stakeholders, and that stakeholders understand the
scientific basis for resource planning decisions. For
example, if stakeholders express concern about an
increase in the spread of vector-borne disease as a
result of climate change, an assessor might integrate
research on climate change, precipitation change,
vegetation, rodent population, and the spread of
disease to determine if a warmer climate may lead
to a greater risk. Results of such an assessment
could provide the scientific information needed by
public health officials and affected communities.

Assessment of global change is an iterative, analytic
process. Analysts and stakeholders are engaged in
evaluating and interpreting the interactions of
dynamic physical, biological, and social systems.
Useful insights about the significant causes and
likely consequences of global change are
communicated to end-users concerned with
resource policy and management. The assessment
process and its dynamic interactions with other
aspects of the Global Change Program is illustrated
in Figure 1.

Assessment consists of three principal elements:
problem formulation, analysis, and characterization
of consequences. The problem formulation phase
includes identification of issues of concern,
synthesis of existing information, selection of
assessment endpoints, identification of scientific
relationships and/or models that can be used to
estimate consequences, and identification of
important information gaps.

In the second phase of assessment — the analysis
phase — data are evaluated to determine what
global changes are likely to occur and what the
potential effects may be. For example, data on
past and current weather patterns, water quality,
and water-borne disease incidence can be used to
project how changes in precipitation might affect
water quality and human health. The strengths and

limitations of available data and models are
examined and uncertainties are evaluated. Where
information is insufficient or unavailable, proxies
may be used. Remaining uncertainties are
evaluated and additional research needs may be
identified.

Planning /
Stakeholder Input

Assessment



Problem Formulation



JL Jl 1L



Analysis



Jl Jl Jl



Characterization of
Consequences



Communicating
Results

Research

Generating Hypotheses

n." 	

Hypothesis Testing

41- IZ

Data and Information
Management

Human Adaptation
to Global Change

Figure 1. The assessment process with complementary research
component envisioned by the Global Change Program (adapted from
ORD's Ecological Risk Assessment Framework, 1998).

Since global change is likely to affect many systems
simultaneously, the third phase of assessment —
characterizing consequences — involves
integrating global change data (e.g., climate
scenarios), models of stressor-response
relationships, and other environmental and social
data that have a bearing on estimates of potential
effects (e.g., air pollutant emission inventories,
population growth and demographic data, or
economic data). Ultimately the characterization of
consequences involves integration across multiple
categories of endpoints (e.g., health, ecological, air
quality, water quality, and economic). Tools must
be developed that allow integration of different
types of models, different types of data, and
different temporal and spatial scales. In addition,
human responses to global change need to be
evaluated and incorporated in the assessment.

Stakeholder Involvement

Throughout the assessment process, stakeholder
involvement is crucial to ensure that the assessment
is relevant and that results are communicated

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effectively. Open and well-designed stakeholder
participation can increase the credibility of the
assessment effort and build public support. In
addition, inclusion of stakeholders in the
assessment process promotes understanding of and
interest in the assessment findings.

Both the public and private sectors need to address
global change. Scientists, assessors, decision
makers and other interested parties are all
stakeholders. They must collaborate from the
earliest stages of the assessment process to identify
key data and knowledge gaps and to assist in the
development of research agendas. This
collaboration helps to ensure the policy relevance
of the assessment results. In addition, stakeholders
may provide information and expertise. By
capitalizing on these partnerships, the assessment
can be designed to address questions of concern,
while helping stakeholders to understand how
uncertainties in the environmental, economic, and
social systems relate to the uncertainties faced by
decision makers. The Global Change Program will
hold stakeholder workshops to assist in identifying
and prioritizing issues and concerns and to establish
conceptual frameworks for conducting
assessments.

The Relationship Between Assessment and
Research

Assessment and research are viewed as
complementary activities in the Global Change
Program. The research program is guided by the
assessment activities and, in turn, provides a steady
flow of new scientific and socioeconomic
information necessary for conducting assessments.
This ongoing, iterative process of research and
assessment ensures that the Program addresses
relevant topics in a timely manner while remaining
responsive to stakeholder needs. Research to
support assessments will be provided through the
intramural efforts in ORD labs and centers and by
extramural funding of STAR grants (see discussion
in the Program Capabilities section).

Strategic Principles

The following strategic principles guide the Global
Change Program's research and assessment
activities.

#	Focus on Future Stresses and the Dynamics of
Change. The Global Change Program is
unique among ORD's research activities in that
it's goal is not to study current conditions and
processes, but rather to build upon ongoing
research by examining how possible future
changes may influence areas of importance to
the public. ORD's air, water, ecosystems, and
human health research programs provide
monitoring, modeling, and process information
that the Global Change Program can use to
develop scenarios of the possible impacts of
changes in climate and land-use on human
health, ecosystems, and socio-economic well-
being in the United States.

#	Focus on Both Risks and Opportunities.

Global change will pose both risks and
opportunities to society. The Program will
identify and assess both adverse and beneficial
aspects of global change, in order to help
decision makers maximize social well-being.

#	Focus on Multiple Stresses. Changes in
climate, climate variability, land use, and UV
radiation are projected to occur in the context
of other stresses. For instance, pollution of the
nation's air and water and invasion of
ecosystems by harmful nonindigenous species
are associated with a variety of adverse
ecological, economic, and human health
effects. The Earth's ecological,
socioeconomic, and climate systems are closely
linked. To understand the consequences of
future global changes, assessments must
consider multiple stresses on multiple systems
and across multiple species that share
interactive and interdependent relationships.
Assessments also must consider the various
scales over which stressors and species interact
and the many endpoints that are of concern to
human society. Assessments that do not
account for interactive effects may provide
inadequate or inaccurate information for
developing adaptive responses and may
increase the likelihood that ineffective or
maladaptive strategies will be adopted.

#	Fluman Dimensions Considerations. Human
dimensions encompass "analysis of the human
causes of global environmental
transformations, the consequences of such

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changes for societies and economies, and the
ways in which people and institutions respond
to the changes. They also involve the broader
social, political, and economic processes and
institutions that frame human interactions with
the environment and influence human behavior
and decisions" (NRC 1999, p. 295). Research
on the environmental effects of human
activities is critical for understanding global
change. The National Academy of Science's
Pathways report (1998) and the IPCC have
both affirmed that understanding how global
change affects and is affected by human
society is a crucial element of assessment. The
Global Change Program incorporates
considerations of human dimensions in both its
assessment activities and its research program.

#	Assessment of Adaptation Options (including
Potential Multiple Benefits). Adaptive actions
involve adjusting practices, processes, or
structures of systems to reduce damages or to
take advantage of potential benefits of global
change. Adaptation responses may be made in
reaction to global change as it occurs or in
anticipation of future global change. The
assessment of adaptation options is an essential
component of global change assessment. Such
assessments inform policy and management
decisions by improving our understanding of
the consequences of global change. The design
of effective adaptation measures requires
characterization of potential impacts across
different populations and geographic regions,
and depends on the mechanisms by which the
impacts occur. Adaptation strategies need to
be evaluated for their effectiveness as well as
for any ancillary impacts..

#	Appropriate Geographic Scale. Perturbations
of physical systems associated with global
change vary geographically. For example,
general circulation model projections show a
wide range of changes in temperature and
precipitation at regional levels. The resulting
impacts on air and water quality, ecosystems,
and human health also vary depending on the
amount of change in a particular location, the
sensitivity of systems to those changes, and the
opportunities for adaptation. Many impacts
can only be understood at regional or
subregional (e.g., watersheds) scales. Since

vulnerability to global change differs from place
to place, research and assessment activities
must utilize appropriate geographic scales. To
realize the overall goal — an assessment of the
consequences of global change for the U.S. —
the Global Change Program will coordinate and
aggregate multiple research and assessment
activities from a variety of geographic areas
and scales.

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Introduction and Criteria for

The primary emphasis of EPA's activities will be
on those areas in which it has a comparative
advantage relative to other agencies conducting
global change research. In coordination with other
USGCRP agencies, EPA has decided to focus its
work in four areas: the effects of global change on
human health, air quality, water quality, and
ecosystems. ORD's Global Change Program will
be able to build upon a strong research foundation
in each of the focus areas to anticipate future
opportunities or risks.

The four focus areas are interdependent. For
example, changes in air or water quality may have
important implications for human health. Changes
in ecosystems due to climate or land-use change
may affect water quality or the spread of infectious
diseases. Changes in the frequency or intensity of
extreme weather events (e.g., floods, droughts,
wildfires) could simultaneously affect public health,
air and water quality, and ecosystems.

Assessments must capture the interactions between
the focus areas.

Several criteria have been identified to help in
developing the Program's long-term objectives and
to aid in setting priorities for research and
assessment. These criteria include:

#	Address the Highest Risks to People and the
Environment. Reduction of global
environmental risks is one of EPA's goals
(EPA, 1997). Global change also is identified
in the 1997 Update to ORD 's Strategic Plan
as a research area of high importance. In
addition, the proposed research areas are
consistent with recommendations in the IPCC
Assessments and from the USGCRP.

#	Make a unique contribution. It is the mission
of EPA to protect human health and to
safeguard the natural environment — air,
water, and land — upon which life depends
(EPA, 1997). Other federal agencies also have
responsibility for investigating global
environmental change as members of the
USGCRP. However, EPA has a unique role

that goes beyond resource management to the
protection of human health, air quality, water
quality, and entire ecosystems from
environmental risks.

#	Demonstrate relevance to Internal Policy
Community (including adaptation responses).
Emphasis is placed on the expected utility of
the research and assessment products for
addressing both short- and long-term global
change risks. EPA's Offices of the
Administrator, Air and Radiation, Water,
Pollution Prevention and Toxic Substances,
and Policy, Economics, and Innovation as well
as EPA Regional Offices are the primary
internal clients for these products.

Assessments conducted by the Global Change
Program should help these clients meet their
strategic goal and objectives (USEPA 1997b)
by supplying information on the potential
consequences of global change on the
resources for which they have oversight. In
addition to supporting Gloal 6 (Global Risks),
assessments will address issues outlined in
Strategic Goal 1 (Clean Air), Goal 2 (Clean
Water), and Goal 8 (Sound Science). The
assessments will also support regulatory
requirements of the Clean Air Act and
Amendments, the Clean Water Act and
Amendments, the Safe Drinking Water Act and
Amendments, the Food Quality Protection Act,
and the Federal Insecticide, Fungicide, and
Rodenticide Act.

#	Demonstrate relevance to the External Policy
Community. External clients include regional,
state, and local resource managers, other
federal agencies, and other stakeholder
communities. The input of these client groups
will aid in identifying and prioritizing the
Program's research.

#	Demonstrate relevance to the National
Assessment process. The assessment activities
of the Global Change Program are designed to
be consistent with and provide meaningful
input to the USGCRP National Assessments.

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Hence, the appropriateness of research and
assessment work is judged, in part, by its
ability to contribute to the goals of the National
Assessment.

# Develop capabilities to assess impacts. In
order to meet the Program's long-term goal of
comprehensively assessing potential
consequences of global change to human health
and ecosystems, it will be necessary to foster
the development of tools and models that
capture interactions between global
environmental changes, physical and biological
processes, and human dimensions.

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Focus Area I: Human Health

Ways Global Change Can Affect Human Health



CLIMATE CHANGE:

•	Temperature

•	Precipitation

•	Weather Patterns

\

STRATOSPHERIC
OZONE DEPLETION"

Source: Adapted from IPCC, 1995.

Exposure to Thermal extremes
(especially heat waves)

Altered frequency/intensity of other
extreme weather (e.g., floods, storms)

DISTURBANCES OF
ECOLOGICAL SYSTEMS

Effects on range and activity of vectors
and infective parasites

Altered local ecology of water-borne and
food-borne infective agents

Altered food productivity, and associated
pests and diseases

Sea level rise, population displace-
ment, and damage to infrastructure

Levels of air pollution, including
pollens and spores

Increased UV radiation,
effects on air quality levels,
ecological changes

Changes in heat- and cold-related
illnesses and deaths

Deaths, injuries, psychological disorders:
damage to public health infrastructure

Changes in geographic ranges and
incidence of vector-borne diseases

Changed incidence of diarrheal and
other infectious diseases

Regional malnutrition and hunger,
impaired child growth and development

Injuries, risks of infectious disease (due
to migration, crowding, contaminated
drinking water), psychological disorders

Asthma and allergic disorders; acute and
chronic respiratory disorders and deaths

Skin cancers and cataracts; indirect
effect through air quality changes (e.g.,
respiratory illnesses) and impaired
productivity of ecological systems

Figure 2. Potential health effects of climate change and stratospheric ozone depletion.

Assessing the Effects of Global Change on
Human Health

Health effects associated with global change may
be wide-ranging and occur via pathways of varying
directness and complexity. A framework for
analyzing potential health effects of climate change
and UV radiation (see WHO 1996, IPCC 1996a)
involves two major categories of effects, direct and
indirect (see Figure 2).

Health is affected by a variety of social, political,
economic, environmental, and technological
factors, including urbanization, affluence (with
respect to funds available for research, sanitation,
surveillance, and monitoring), scientific
developments, and individual behavior.
Unanticipated variables can have profound effects
on health. For example, in 1997 an avian strain of
influenza that had never before infected humans
infected and killed previously healthy people in
Hong Kong (MMWR 1997;"MMWR 1998).

Environmental conditions (e.g., degraded air quality
or water contamination) can also affect health
status.

Assessing health impacts of global change poses a
complex challenge. Global change health impacts
take place against a backdrop of continuing changes
in demographics, new technologies that pose their
own environmental and health risks, and human
behavior. Such stresses can affect human health
directly or through interactions with global changes.
At the same time, improvements in medical care
and public health systems moderate outcomes and
need to be incorporated in health impact
assessments.

Health assessments augment traditional
epidemiologic and toxicologic approaches by
incorporating impacts of multiple stressors and their
interactions. Health assessments under the Global
Change Program must integrate information on
global changes; other environmental stresses (e.g.,

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air and water pollution); ecological and biological
processes; social, economic, and political factors;
and individual behaviors. Research on relationships
between climate change, climate variability, land-
use change, long term changes in UV radiation, and
health outcomes will be needed to support these
assessment efforts.

Assessments also must account for human
responses to global change impacts. Adaptive
measures — including better management of
ecosystems; improved public health monitoring,
surveillance, and control programs; disaster
preparedness; and the wider use of protective
technologies (e.g., sun screen, water purification,
and vaccination) — may moderate the effects of
global change (WHO 1996, IPCC 1996a). In
addition, risks to health from some technological
advancements must be considered. For example,
increased use of air conditioning protects against
heat stress, but may increase emissions of
greenhouse gases and conventional air pollutants
(e.g., particulates and nitrogen oxides) that have
adverse health effects. Similarly, the effects of
pesticides on human health, insect predators, and
increased insect resistance need to be evaluated if
new pesticides are to be used to control disease
vectors. In other cases, adaptation options may
yield ancillary benefits.

Relatively little research is available to enable
quantitative descriptions of probable health impacts
associated with global change. There are even
fewer integrated assessment frameworks to allow
simultaneous evaluation of several stresses (e.g.,
climate change and land-use change) and account
for adaptive responses. The Global Change
Program's research and assessment activities will
focus on the following analyses of potential health
impacts associated with global change (see also
Table 4):

#	Assessment of the consequences of climate
change and climate variability on human health
and subsequent assessments of the impacts of
global change on human health: USGCRP
First (FY2000), Second (FY2004), and Third
(FY2008) National Assessments;

#	Assessment of potential consequences of
climate change and variability on weather-
related morbidity (FY2003);

#	Assessment of potential consequences of global
change (including climate change and variability
and land-use changes) on water- and vector-
borne diseases (FY2005);

#	Assessment of potential health consequences of
changes in tropospheric ozone due to global
change (FY2007); and

#	Assessment of potential health consequences of
changes in particulate matter due to global
change (FY2009).

The Global Change Program does not plan to
conduct assessments of the health effects of long-
term changes in UV radiation. The National
Institutes of Health through the National Cancer
Institute, the National Eye Institute, the National
Institute of Arthritis and Muscoloskeletal and Skin
Diseases, and the National Institute of
Environmental Health Sciences are conducting
studies in this area (Our Changing Planet, 2000, p.
71-72).

The Global Change Program's health assessments
suport EPA's overarching mission to protect
human health. In particular, each assessment
supports both Goal 6: Reduction of Global and
Cross-Border Environmental Risks and Goal 8:
Sound Science, Improved Understanding of
Envrironmental Risk, and Greater Innovation to
Address Environmental Problems. In addition, the
health assessments of tropospheric ozone and
particulate matter changes associated with global
change are relevant to Goal 1: Clean Air.
Information from the Global Change Program will
also support EPA's Office of Air and Radiation,
both in fulfilling their responsibilities under the
Clean Air Act and in support of their climate
change activities.

The planned health assessments will directly and
indirectly support the National Assessment process.
The Health Sector Assessment from the first
National Assessment identified several research
needs which have been used to guide the selection
of the health impacts EPA will study. Future
assessments will examine the potential effects of
global change, including climate change and
variability, on the health of the U.S. population
during the 21st century. The uncertainties
surrounding many variables, including population
growth, future economic conditions, other possible
changes in health or society (e.g., an epidemic or

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war), and the complexities of human behavior, will
be addressed. These assessments will be
conducted as public-private partnerships involving a
range of government, academic, and private
institutions (see www.nacc.usgcrp. gov
/sectors/health).

Other factors that guided the development of the
Strategy include whether other USGCRP agencies
are conducting research and assessments on a
particular health endpoint (e.g., the exclusion of UV
health effects work due to NIH's involvement in
UV research), unique EPA capabilities (e.g., in
assessing health endpoints associated with air
pollution), and past EPA experience (e.g., with
research on weather-related mortality).

Weather-related Morbidity

Some preliminary analyses of weather-related
mortality have been conducted (EPA 1989, WHO
1996, Kalkstein and Greene 1997). While our
understanding of certain issues associated with
future weather-related mortality remains poor (e.g.,
the degree to which people can acclimatize to
increased warmth, how much of increased
temperature-related mortality is mortality
displacement [the shortening of a human life by
only a few days], and the balance between heat-
and cold-related mortality) there are even fewer
studies focused on climate change and heat-related
morbidity. A number of heat-related morbidity
effects need to be investigated, including: heat-
related symptoms that do not require a visit to a
medical provider (e.g., heat nausea, heat cramps,
headache, heat fainting) and emergency room visits
or hospital admissions for heat-related illnesses.

The direct effect of weather on public health goes
beyond extreme temperatures. Climate change
could also affect precipitation (rain and snowfall),
precipitation intensity (flash flooding), and extreme
events such as storms and hurricanes. Land use
changes, such as increased urbanization in
floodplains and coastal areas, could exacerbate
vulnerability to these climatic changes. Potential
health effects from inclement weather include
deaths, injuries, and illnesses. For example,
blizzards and snowfalls have been associated with
increased mortality (Glass and Zack 1979; Goijanc
et al. 1999). Secondary health effects resulting
from economic losses and natural resource

devestation in the aftermath of extreme weather
events could also be significant and are largely
unexplored.

Water- and Vector-borne Diseases

An assessment of water- and vector-borne diseases
is expected to be conducted from FY 2002 through
FY 2005. These activities will build on a
concurrent Water Quality assessment on pollutants
and microbial pathogens.

Water-borne Diseases. An assessment of water-
borne diseases will focus on two topics: 1) water-
borne diseases spread through contaminated
drinking water or recreational water; and 2)
coastal/marine health issues, including harmful algal
blooms. There are many determinants of these
types of diseases, such as poor sanitation, poor
erosion control, application of agricultural
fertilizers, and coastal sewage release. In addition,
many cases of water-borne diseases go unreported.
This contributes to the lack of understanding of the
full extent of the problems caused by contaminated
water sources. Nonetheless, water contamination
appears to be an important environmental risk
(EPA 1990) and poses a risk management
challenge for drinking water suppliers (EPA
1998a).

Global change may further exacerbate the health
risks associated with these factors through more
intense precipitation events, more droughts, and
increased water temperature. Both increases in
flooding and water shortages can impair local
sewerage, degrade water quality, and alter the
potential risks of diarrheal and dysentery
epidemics. Several environmental factors including
sunlight, pH, ocean currents, winds, sea surface
temperatures, and nutrients can influence algal
production (Valiela 1984; Epstein et al. 1993).
Algal blooms can influence the transmission of
some bacterial diseases such as V. vulnificus and
V. parahemolyticus. Algal blooms also are
associated with biotoxin contamination of fish and
shellfish. Increases in UV radiation also can alter
microbial and viral activity in aquatic ecosystems
(Herndl et al. 1997. Zcpp et al. 1998).

Vector-borne Diseases. There is an extensive
literature on the relationship between
meteorological variables, especially temperature,

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and various aspects of vector-borne disease
transmission (e.g., parasite development, biting
behavior, reproduction rates, bioclimatological
thresholds). These relationships have been
summarized in several review articles and book
chapters (Patz etal. 1996, WHO 1996). There
also have been some efforts to develop integrated
systems-based models that include: theoretical
constructs that describe the various components in
the system, relationships between these
components (e.g., vectorial capacity), and the best
available information from field and laboratory
studies that can be used to estimate parameters
describing these relationships. With a few
exceptions, existing models have not been linked to
global changes, such as climate scenarios from
General Circulation Models (GCMs). Even fewer
models include human dimensions or explicitly
consider costs and the implications of medical
interventions.

Air Pollution-related Health Effects

Global change may affect exposures to air
pollutants by affecting: 1) weather, and thereby
local and regional pollution concentrations; 2) UV
radiation, and thereby local and regional pollution
concentrations, especially tropospheric ozone; 3)
anthropogenic emissions through adaptations
involving increased fuel combustion for power
generation; and 4) biogenic emissions. In addition,
global change may increase or decrease the amount
of time individuals spend indoors, resulting in
changed exposure to indoor pollutants and allergens
that are, in some cases, more hazardous than
ambient conditions. Changes in air pollutant
concentrations are discussed more fully in the third
focus area, Air Quality. Assessment activities in
the Air Quality focus area will provide baseline
information about ozone and particulate matter
under conditions of global change that will be used
to derive health effects estimates.

The substantial body of scientific literature relating
air pollution to health effects has been discussed
elsewhere (see for example:
www.epa.gov/ncea/partmatt.htm and
www.epa.gov/ncea/ozone.htm). In assessments of
the health impacts associated with global change-
induced changes in air pollution levels, the Global
Change Program will rely on this literature and on
ORD expertise.

Additional Considerations

As noted above, various adaptive responses at the
societal or individual level, could substantially
reduce the impacts of global change on human
health. Many of these responses are simply an
intensification or enhancement of ongoing public
health programs. In other cases, application of
existing protective technologies can reduce health
impacts (e.g., air conditioning, sanitation, water
purification). Human responses to health risks
posed by global change will be included in the
research and assessments described above. The
effectiveness and costs associated with adaptive
measures will be evaluated along with the potential
co-benefits or maladaptations that may accompany
various adaptation strategies.

Making the Connection — from
Adaptation Research to Assessment

Human responses to global change must
be accounted for in assessments of health
impacts. ORD researchers are in the
process of identifying approaches (both
technological and socioeconomic). In
particular, technologies implemented for
one environmental problem may impact
(positively or negatively) other
environmental stressors. Researchers
are examining these "ancillary" effects.

This research will contribute to the Global
Change Program's ability to accurately
assess the effects of global change on
human health.

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Table 4. Focus Area I: Human Health

Research Questions
(see related Assessment Component in next column)

Assessment Components
(Fiscal Year Due Date)

Assessment of Weather-Related Morbidity

What is the quantitative relationship between heat stress and
cold stress and various illnesses, particularly in vulnerable
populations? (1,2,5)

How will the incidence of these illnesses change as the earth
warms? (1,2,5)

How are temperature-related illnesses modified by personal
characteristics and behaviors? (1,2,5)

How are changes in weather patterns (e.g., inclement weather,
snowfall, storms) associated with morbidity, including injuries
and other public health outcomes? (3,4,5)

1.	Evaluate heat and cold morbidity in children (2003)

review and summarize literature and identify existing data
where possible, statistically analyze the relationship
between morbidity and temperature extremes

2.	Statistically analyze the association of ER and hospital
admissions for heat-related illnesses with variations in
temperature and humidity and socio-demographic
characteristics (2003)

3.	Statistically analyze the relationship between inclement
weather and accidental injury, especially injuries caused by
motor vehicle accidents (2003)

4.	Examine existing literature and conduct preliminary analysis
of existing data on the relationship of public health concerns,
such as violent crime, to weather variation (2003)

5.	Develop a peer-reviewed assessment report on aspects of
weather-related morbidity (2003)

Assessment of Water- and Vector-Borne Disease

Which water-borne diseases are sensitive to climate and land-
use change? (1,2,6)

Which aspects of climate and land-use change exert the most
important effects on water-borne disease risks? (1,2,6)

Based on what we know about potential changes in the
hydrological cycle, water temperatures, frequency of extreme
conditions, sea-level rise, and land-use changes, how are water-
borne disease risks likely to be affected? (1,2,6)

Based on what we know about changes in climate and land
use, how are habitats of disease-carrying vectors (terrestrial,
freshwater, marine) likely to be altered? (3,6)

How can existing models be utilized to estimate potential
changes in future disease risks? (3,6)

How effective and costly are adaptive measures designed to
manage adverse health impacts associated with water and
vector-borne diseases? (3,6)

How do allergic responses to flora and fauna vary with changes
in climatic conditions? (4,6)

How is the quality of life impacted by variations in vector
populations mediated by changes in climate or land-use? (5,6)

1.	Conduct a workshop to establish a research agenda for the
study of water-borne disease risk under climate and land-use
change (2005)

2.	Assess water-borne disease risk under climate and land-
use change (2005)

~	review and summarize literature

~	adapt existing models to estimate effects

3.	Assess climate and land use-related vector-borne disease
risk, adaptation potential, and economic valuation of risk (2005)

~	review and summarize literature

~	adapt existing models to estimate effects

4.	Analyze climate-related variation in allergic reactions to flora
and fauna (2005)

5.	Examine quality of life effects associated with vector
prevalence related to climate variability and land-use change
(2005)

6.	Develop a peer-reviewed assessment report on water- and
vector-borne diseases under global change (2005)

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Assessment of Ozone Health Effects under Global Change

How do changes in climatic conditions and changes in
anthropogenic and biogenic emissions associated with climate
and land-use change affect human exposures to tropospheric
ozone? (1,3)

What health effects are associated with ozone exposures
mediated by climate and land-use changes? (2,3)

How would societal changes and technology advancements
adopted either to respond to climate change or reduce harmful
ambient levels of tropospheric ozone affect health risks and
what combinations of these human adaptive responses would
provide the greatest combined risk reduction (co-benefits) at the
lowest cost? (3)

1.	Utilizing existing literature and models, assess climate and
land-use change impacts on human tropospheric ozone
exposures (2007)

2.	Apply human dose-response estimates for ozone in Section
812 Health Benefits Model to estimate health effects (2007)

3.	Develop a peer-reviewed assessment, accounting for human
adaptation, to report on ozone health effects under global
change (2007)

Assessment of Particulate Matter Health Effects under Global Change

How do changes in climatic conditions and changes in
anthropogenic and biogenic emissions associated with climate
and land-use change affect human exposures to particulate
matter? (1,3)

What health effects are associated with particulate matter
exposures mediated by climate and land-use changes? (2,3)

How would societal changes and technology advancements
adopted either to respond to climate change or reduce harmful
ambient levels of particulate matter affect health risks and what
combinations of these human adaptive responses would provide
the greatest combined risk reduction (co-benefits) at the lowest
cost? (3)

1.	Utilizing existing literature and models, assess climate and
land-use change impacts on human particulate matter
exposures (2009)

2.	Apply human dose-response estimates for particulate matter
in Section 812 Health Benefits Model to estimate health effects
(2009)

3.	Develop a peer-reviewed assessment, accounting for human
adaptation, to report on particulate matter health effects under
global change (2009)

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Focus Area II: Ecosystems

Assessing the effects of global change on
ecosystems

EPA's mission is not only to protect human health
but to safeguard the natural environment. EPA
has pledged to provide environmental protection
that "contributes to making communities and
ecosystems diverse, sustainable and economically
productive" (EPA 1997). This pledge requires
EPA to think comprehensively about entire
ecological systems. Therefore, a priority of the
Global Change Research Program is to conduct
assessments of the effects of global change on
ecosystems in the context of other stressors and
human dimensions in order to improve society's
ability to respond to the future consequences of
global change.

Changes in the climate system, in human behavior,
and in human demands on ecosystems will
continue to occur, necessitating the development
of predictive conceptual models to assess future
ecosystem status that incorporate multiple
stressors. For each research and assessment
activity outlined below, the Global Change
Program will examine the future consequences of
global change on dominant physical aspects of
ecosystems and/or on key species within the
ecosystem type, how these changes will affect
ecosystem functioning and the services provided,
and potential adaptation measures. The primary
focus of ecosystem assessment activities will be on
aquatic ecosystems, in keeping with the long-
standing emphasis of EPA's ecosystem work.
The Global Change Program's assessment and
research activities are focused on three areas:

#	Assessing the consequences of global change
for aquatic ecosystems (2004);

#	Assessing the consequences of global change
for nonindigenous invasive species (2006);

#	Assessing the consequences of global change
for ecosystem services (2009).

These three assessments are related to each other
and also to the two Water Quality assessments.
In addition, each ecosystem assessment supports
multiple EPA strategic goals, including: Goal 2:
Clean and Safe Water, Goal 6: Global Risks, and
Goal 8: Sound Science. Likewise, information

from the Global Change Program will support the
Office of Water in fulfilling their responsibilities
under the Clean Water Act and Amendments
which calls for restoration and maintenance of the
integrity of the Nation's waters, including
conservation of waters for the protection and
propagation of fish and aquatic life and wildlife,
and for recreational purposes.

In addition to supporting EPA Program Offices,
the ecosystem assessments will support the
ongoing analytic efforts of the USGCRP. In
particular, the National Assessment's Water Sector
assessment calls for the development of models
linking climate variability and ecological processes
and for integrated assessments of the potential
impacts and response options related to alternative
future climates (Meyer et al. 1999).

Aquatic Ecosystems

Aquatic ecosystems (i.e., streams, rivers, lakes,
wetlands, and estuaries) are sensitive to changes in
climate, climate variability, land use, and UV
radiation. Changes in climate and climate
variability will affect precipitation patterns (the
timing, form, and seasonality of precipitation; and
the frequency and intensity of precipitation events)
and evapotranspiration rates (which are
temperature dependent). Climate change and
variability will also affect aquatic ecosystems via
increased concentrations of carbon dioxide,
increased air and water temperatures, sea level
rise, storm surges, changes in streamflow to the
coast, altered pollution loads, and salinity changes
in coastal ecosystems.

UV radiation affects plants, microbes and animals
directly, and indirect ecosystem effects are
mediated by changes in plant composition,
microbial populations, secondary chemistry, plant
litter decomposition, and air quality (Caldwell et
al. 1998). In addition to short-term effects, the
impacts of elevated UV radiation on natural
systems will include shifts in species that may alter
ecosystem functioning and productivity (Herndl et
al. 1997, Karentz et al. 1994. Lindcll et al. 1995,
Rozemaeftf/. 1997, Wetzel et al. 1995, Zepp et
al. 1998).

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Land-use change, considered to be the most
pervasive human cause of loss of biodiversity, is
leading to habitat destruction through conversion
from one habitat type to another or through
modification of conditions within a habitat type.
Changes in sediments, nutrients, toxics, and
nonindigenous species are examples of the multiple
stressors that shape the context in which land use
and climatic changes are occurring. Climate
variability, including extreme events like
hurricanes, droughts, and floods will also affect
ecosystem functioning. Droughts that lead to
intermittent flows and drying of streambeds for
extended periods reduce ecosystem productivity as
aquatic habitat is restricted, water quality is
reduced, and intense competition and predation
reduce total biomass (IPCC WGII 1996).

Making the Connection — from
Ecosystem Research to Assessment

Changes in stream flow and thermal
regimes are likely to have significant
effects on the composition of fish
communities. ORD researchers are
engaged in creating a nationwide fish-
temperature-flow matched dataset and
developing empirical relationships between
flow and thermal regime metrics and fish
species presence. This research will
directly contribute to the Global Change
Program's ability to assess the effects of
global change on aquatic ecosystems.

The impact of global changes on aquatic
ecosystems and their functioning is recognized as
an important area for research and assessment
because of the goods and services they supply
(Daily 1997; National Assessment Synthesis Team
2000) and because these systems may be
significantly affected by global change (National
Assessment Synthesis Team 2000; Pathways
1999). In particular, the effects of climate change
and variability on aquatic ecosystems is as an
important research area because our understanding
of how these stressors affect the physical,
chemical, and biological characteristics of aquatic
ecosystems is limited (Meyer, et cil.; IPCC 1996).
More extensive data sets and better models are
needed that link hydrologic regimes with
ecosystem processes, with ecological interactions
and with water quality.

With a focus on selected river basins, this
assessment will adopt a taxonomy for
understanding and expressing the changes that
aquatic ecosystems may undergo due to changes
in climate and climate variability, land use, and UV
radiation. Where possible, the taxonomy of
ecosystem services will be used to express
assessment results. The term "ecosystem services"
describes both the conditions and the processes
through which ecosystems sustain and fulfill
human life. Ecosystem services maintain
biodiversity, produce goods, and perform life-
support functions. People are generally willing to
invest resources to protect things they know they
value. Natural systems are sometimes
undervalued because their importance to society is
often not well understood by the public. Using
ecosystem services as assessment endpoints
provides a means to articulate how global changes
will affect aquatic ecosystems, and the
implications of those changes for society.

Using this approach, an overview of the effects of
global changes on ecosystem services for different
aquatic ecosystem types will be developed, based
on expert opinion and a review of the literature.
Similar aggregate assessments have been done of
the impacts of climate change on aquatic
ecosystems for physiographic regions in the U.S.,
but they have not used ecosystem services as
assessment endpoints (see Meyer et cil. for an
overview of these studies).

Next, smaller-scale studies (case studies), will be
conducted to build on insights gained from the
larger scale assessment. These studies will employ
the ecosystem services framework developed by
this program for assessments of global changes at
the scale of watersheds. This framework will
provide guidance for identifying ci priori the types
of services most likely to be affected by various
stressors (climate change, land-use change, UV
radiation), and methods for measuring, modeling,
or estimating the ecosystem services impacts at
specific sites.

The locations for the case studies will represent
diverse geographic regions and aquatic ecosystem
types, different land-use pressures (e.g.,
agricultural pressures, urban growth pressures),
and different future climate-induced changes (e.g.,

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increased versus decreased runoff). These sites
will be chosen because of their highly-valued
ecosystem services (e.g., recreational activities
such as birding and fishing or irrigation), and the
amount of available data and existing research on
which our program can build. The results of this
assessment will have direct applicability to the
regional assessments and the water sector
assessment within the National Assessment, and to
the fourth assessment report of the IPCC.

Existing stakeholder contacts and processes
developed through the National Assessment will be
tapped for information and collaboration during
the conduct of the site-specific case studies.

Table 5 outlines the research questions that will
guide the assessment and the components
necessary to complete the aquatic ecosystems
assessment. These components map directly into
capabilities of the labs and centers and those of the
extramural grants program (see Program
Capabilities section). The assessment report will
include a conceptual model (see Glossary) that
describes predicted relationships among global
change, resultant stressors on aquatic ecosystems,
exposure, and the response of aquatic ecosystem
endpoints. The idea of ecosystem services will be
used to guide the selection of aquatic ecosystem
endpoints.

Nonindigenous Invasive Species

Harmful non-indigenous species (NIS) are
responsible for a variety of deleterious effects,
including the decline of many indigenous species
(even contributing to the extinction of some
species), the transformation of ecological
communities and ecosystems (e.g., by altering
processes such as primary productivity,
decomposition, hydrology, geomorphology,
nutrient cycling, and/or disturbance regimes), and
the reduction of global biodiversity (OTA 1993,
Vitousek et al. 1996, Vitousek et al. 1997).
Pimental et al. (2000) estimate that nonindigenous
species cost the United States over $137 billion
annually in losses to agriculture, forestry, fisheries,
water use, utilities, buildings, and natural areas.
Climate change could accelerate losses of
threatened or endangered native species while
failing to exert the same negative pressure on
harmful nonindigenous species, possibly

exacerbating current problems (Dukes et al.

1999).

Many federal government agencies and academic
institutions are actively engaged in research on
invasive species. Yet, this stressor has not been
widely considered in current research plans (Our
Changing Planet 2000). The Executive Order on
Invasive Species (E.O. 13112) established an
interagency National Invasive Species Council that
is required to develop an invasive species
Management Plan. Some of the member agencies
and academic institutions involved include the
Smithsonian Institution, USDA, USGS, NOAA,
DOD, NSF, DOC, DOI, EPA, APHIS, FAS, and
the Association of Systematics Collections. As
part of the Management Plan, ORD is
collaborating with NOAA and the states of
California, Oregon, Washington, Hawaii, and
Alaska to run a monitoring program (Western
EMAP) that will survey the nonindigenous
benthos and fishes of the coastal ecosystems of
the West Coast. This program will generate
estimates of the extent and nature of invasions
along the entire coast. EPA is also participating in
the Delaware Basin Invasive Species Monitoring
Program, a program that will develop monitoring
systems for invasive plants, insects, and pathogens
integrated with forest health and water quality
monitoring in the Delaware River basin.

To capitalize on these planned outputs, the Global
Change Research Program will leverage limited
resources to examine the additional effects of
climate change on nonindigenous species based on
the existing literature (Table 5). This effort is
consistent with the FY 2000 priorities of the
USGCRP who list among their areas of focus the
development of "methods that assess the
invasiveness of nonindigenous species by
combining the science of landscape ecology with
the principles of risk assessment" (Our Changing
Planet 2000). Insights gained from this effort will
be shared with other agencies engaged in NIS
research. In addition, the results of this
assessment will have direct applicability to the
USGCRP regional assessments and to the IPCC.

Ecosystem Services

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The ecosystem services assessment will extend the
aquatic ecosystems assessment by incorporating
more quantitative approaches and indices,
especially biocriteria. States use biocriteria
programs to evaluate the status of aquatic
ecosystems, to diagnose threats, and to develop
strategies for protecting aquatic ecosystems.

Some of the biological indicators that are used in
biocriteria programs may be useful indicators of
ecosystem services. By 2008, the Global Change
Program will have provided states with a
framework to evaluate whether global change will
impair their ability to meet biocriteria standards
and to identify adaptation options to help them
cope with global change (see Water Quality
biocriteria assessment).

For this assessment of ecosystem services, the
Global Change Program will partner with states to
develop tools to evaluate the vulnerability of
aquatic ecosystem services, to identify adaptation
options, and to incorporate ecosystem services
into biocriteria or other state programs. The
components that are necessary for this assessment
are described in Table 5. These components build
on previous assessments (aquatic ecosystems
described above and Water Quality assessments of
pollutants and pathogens and of biocriteria).

Linking biocriteria and the production of
ecosystem services could strengthen state
biocriteria programs by articulating how stressors
(including those induced by global change) affect
the conditions and processes through which
aquatic ecosystems sustain and fulfill human life.
This may help policymakers and the general public
to evaluate and prioritize actions needed to protect
aquatic ecosystems. The goal of this assessment
is consistent with the NRC's Science Priorities for
the Human Dimensions of Global Change (NRC
1994), the USGCRP's Our Changing Planet (FY
2000) and the National Assessment process.

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Table 5. Focus Area II: Ecosystems

Research Questions
(see related Assessment Component in next column)

Assessment Components
(Fiscal Year Due Date)

Assessment of Aquatic Ecosystems



How should aquatic ecosystem types and ecosystem services
be classified to facilitate analysis? (1)

What is a useful framework to apply to assess the impacts of
global change on aquatic ecosystem services? (2)

How are different aquatic ecosystem types potentially vulnerable
to future changes in climate and climate variability? (3)

What are the problems that arise because of extrapolation from
individual studies to conclusions about effects on ecosystem
types? (3)

What are the other major sources of uncertainty (e.g., in climate
science, in ecological modeling)? (3)

How are different aquatic ecosystem types potentially vulnerable
to future changes in UV radiation? (4)

How are different aquatic ecosystem types potentially vulnerable
to future changes in land use? (5)

How can geographically-specific, quantitative analyses improve
our understanding of the vulnerability of specific aquatic
ecosystem types? What can we learn by examining the
relationships among aquatic ecosystem types within a river
basin, the interactions of multiple stressors, and the adaptation
strategies that are available to stakeholders in a specific region?
(6)

What should we communicate to stakeholders to facilitate their
understanding of the vulnerability of aquatic ecosystems,
including ecosystem services, to global change and to aid their

1.	Establish taxonomy of aquatic ecosystem types and
services for purposes of assessment. (2001)

2.	Develop ecosystem services framework to apply to aquatic
ecosystem assessments at the scale of river basins. (2001)

3.	Use methods of eliciting scientific expert opinion to
conduct qualitative assessment of climate change and variability
effects on aquatic ecosystems by ecosystem type. (FY2003)

Articulate from the existing literature a conceptual model
(see Glossary) of the effects of climate variability and
change on aquatic ecosystems. Include literature from
pollutants and pathogens assessment as it becomes
available.

Write a paper that draws conclusions about potential
effects of climate variability and change on aquatic
ecosystem services for each ecosystem type, and
identifies uncertainties, research needs and
methodological issues.

Convene a workshop of experts to review the paper and
develop a consensus on the paper's conclusions.

4. Utilizing the work of ORD labs, grantees, and the existing
literature, produce a document that synthesizes the
literature/studies (and articulates a conceptual model) on the
potential future effects of UV radiation on aquatic ecosystems
by ecosystem type. (2003)

5.	Utilizing the work of ORD labs, grantees, and the existing
literature, produce a document that synthesizes the
literature/studies (and articulates a conceptual model) on the
potential effects of future land use on aquatic ecosystems by
ecosystem type. Include information from pollutants and
pathogens assessment as it becomes available. (2003)

6.	Perform 3 in-depth case studies and draw from the EPA-
sponsored regional assessments to quantitatively estimate the
effects of climate, land-use change, and UV radiation on
different types of aquatic ecosystems. (2004)

Draw on other federal agencies and research institutions to
obtain regionally specific climate change scenarios
Develop or obtain regionally or locally specific land-use
change scenarios

Adapt linked hydrologic and ecological models

Refine existing sea level rise models

Adapt existing, regionally specific vegetation models

Estimate future climate, land-use, and UV radiation effects

on water quantity, water quality, aquatic habitat quality and

extent, ecosystem services

Examine adaptation options

Based on results, develop future research priorities

7.	Write final assessment that synthesizes the results of
impacts of climate, land use, and UV radiation on diifferent
aquatic ecosystem types. (One product of this assessment is
an overarching conceptual model of climate, land-use, and UV

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evaluation of adaptation options to protect vulnerable ecosystem
services? (7)

effects on aquatic ecosystems.) (2004)

Assessment of Nonindigenous Invasive Species

How could climate variability and change affect the distribution
of nonindigenous species and alter their effects on native
species and ecological communities? (1)

How might the Global Change Program encourage federal
agencies and research institutions to consider the effects of
climate variability and change on nonindigenous invasive
species? (2)

1.	Conduct literature review and write a paper on the effect of
climate change and variability on nonindigenous invasive
species in preparation for the workshop to be held in FY2006.
(2005)

2.	Facilitate workshop with other agencies, the IPCC, and
academic institutions and prepare a workshop report that
summarizes the state of the science and updates the research
agenda. (2006)

Assessment of Ecosystem Services

What tools can states use to aid their evaluation of the
vulnerability of aquatic ecosystem services to global change and
identify adaptation options to protect aquatic ecosystem
services? (1)

Could biological indicators that are used for state biocriteria
programs be used as indicators of ecosystem services? (1)
Can states use their biocriteria programs to monitor the status
of and diagnose threats to ecosystem services? (1)

Are there other state programs that could be used to assess
the vulnerability of aquatic ecosystem services to global
change? (1)

What strategies are available to states to protect ecosystem
services? How can states identify adaptation options to meet
biocriteria that relate to ecosystem services, and how can they
link these adaptation options to tools they already have (e.g.,
National Pollutant Discharge Elimination System, Non-point
Source Pollution programs, Total Maximum Daily Loads,
watershed restoration)? (1)

What should we communicate to states, the Office of Water,
and other stakeholders to facilitate their assessment of the
vulnerability of ecosystem services to global change, and to aid
their evaluation of adaptation options? (2)

1.	Utilizing the work of ORD labs, the Office of Water, and
previous Global Change Program assessments, conduct a
study with the Office of Water and selected states to determine
what tools states could use to aid their evaluation of the
vulnerability of aquatic ecosystem services to global change and
identify adaptation options to protect aquatic ecosystem
services. (2009)

Drawing on the preceding aquatic ecosystems
assessment and the Water Quality assessments (of
pollutants and pathogens and of biocriteria), identify
indicators of ecosystem services and determine if
indicators used in biocriteria programs or other state
programs could be used as indicators of ecosystem
services.

Construct an updated conceptual model for the effects of
global change on aquatic ecosystem services using the
results and conceptual models from the aquatic
ecosystems assessment and the Water Quality
assessments.

Work with the Office of Water and selected states to
determine how state biocriteria programs and other state
programs could be used to monitor the status of
ecosystem services, identify threats (e.g., global change)
to ecosystem services, and develop adaptation strategies
to protect ecosystem services.

2.	Prepare a final report that identifies tools that states can use
to assess the vulnerability of their aquatic ecosystem services
to global change, to identify adaptation options, and to
incorporate ecosystem services into state programs. (2009)

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Focus Area HI: Air Quality

Assessing the effects of global change on air
quality

Air pollution continues to be a widespread public
health and environmental problem in the United
States. People are constantly exposed to air
pollutants, whether indoors or outdoors. The
health effects of air pollution range from episodes
of increased mortality at high pollutant
concentrations to more subtle effects on respiratory
health. Air pollution also has been associated with
increased use of health care services, including
visits to physicians and emergency rooms and
admissions to hospitals. Other effects of air
pollution include reduced visibility, damage to crops
and buildings, and acid deposition on soil and in
water bodies where the chemistry of the water and
resident aquatic species are affected (USEPA
2000).

Ambient concentrations are largely determined by
the air pollutant emissions and the meteorological
conditions at the time of pollutant release. Climate
change, UV radiation, and land-use change can
each influence emissions, meteorological variables,
or both. Other factors affecting emissions include
population, level of economic activity, structure of
the economy, energy demand and generation (fuel
use, type, and efficiency), and emission controls.

Few studies have investigated the effects of global
change on air quality. Examining the effects of
global change on air quality is a major focus of the
Global Change Research Program, given EPA's
legal mandate with respect to air pollution, the
agency's substantial capability and expertise in
modeling air quality, EPA regulatory efforts in this
area, and the important health effects that have
been associated with both tropospheric ozone and
particulate matter.

The Global Change Program plans the following
two assessments focused on air quality:

#	Assess potential consequences of global change
on tropospheric ozone concentrations
(FY2004), and

#	Assess potential consequences of global change
on particulate matter concentrations (FY2007).

The Global Change Program's air quality
assessments directly support EPA's Goal 1: Clean
Air in addition to Goal 6: Reduction of Global and
Cross-Border Environmnetal Risks and Goal 8:
Sound Science. Information from the Global
Change Program will also support EPA's Office of
Air and Radiation, both in fulfilling their
responsibilities under the Clean Air Act and in
support of their climate change activities.

The planned assessments will also support the
ongoing National Assessment process. In
particular, the Health Sector Assessment from the
first National Assessment identified as a high
priority research area work on determining the
relationships between weather and air pollution.
Other factors that guide this Strategy include
examination of global change affected air pollution
concentrations and the importance of pollutants in
terms of extent, health impacts, Agency policies,
and ongoing ORD research efforts and programs.

The goal of the two air quality assessments is to
answer the following questions: What is the effect
of projected changes in climate, climate variability,
UV radiation, and land-use patterns on air quality
(specifically ground level ozone and particulate
matter)? Which areas will experience the largest
deterioration in air quality due to global change?
Which areas will experience improvements in air
quality due to global change? How many areas will

Integrated Air Quality Assessment Framework

Future air pollution
control programs
1 GHG mitigation policies

1 Economic growth
Energy demand
1 Population growth
1 Vehicle miles traveled

Climatic Change

•	Temperature

•	Precipitation

•	Wind Speed

•	Cloud Cover



Emissions
(Anthropogenic
and Biogenic)

\\

Land Use Change

Atmospheric
Modeling

I

Air Quality

Figure 3. Framework of an Integrated Air Quality
Assessment.

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fail to attain air quality standards due to global
change? Because atmospheric processes can be
highly non-linear, the Air Quality assessments will
also account for changes in emissions across time
and underlying factors driving emissions such as
the level of economic activity, energy demand and
generation, and emission controls.

Figure 3 illustrates how the effects on air quality of
future changes in climate, UV radiation, and land-
use will be modeled. A set of meteorological
variables needed for air quality simulations will be
developed, and the relationships between weather
and tropospheric ozone and particulate matter
(PM) will be statistically analyzed. Baseline and
future emissions scenarios will be developed for
ozone and PM using scenarios of economic
growth, energy demand, population growth, vehicle
miles traveled, policy scenarios, and information
about anthropogenic and biogenic emissions. Base
case and future concentrations of ozone and PM
will be simulated, and peer-reviewed assessment
reports will be developed for these two air
pollutants. Table 6 lays out the research questions
that will guide these assessments and the
components necessary to complete the
assessments. These components map directly into
capabilities of the labs and centers and those of the
extramural grants program (see Program
Capabilities, p. 10-11).

Global climate change will likely result in changes
in regional and local weather, which in turn may
affect air pollution levels by altering rates of
atmospheric chemical reactions, transport
processes, and export of pollutants. Emissions of
photochemical oxidant precursors from both
anthropogenic and natural sources also are affected
by regional and local weather. Warmer
temperatures affect energy demand and therefore
emissions from fossil fuel-based electric utilities. In
addition, evaporative emissions from mobile
sources are temperature-sensitive. Studies show
that ozone concentrations can be strongly
influenced by natural emissions as well (Fehsenfeld
et al. 1992, Chameides et al. 1988). Temperature
and other meteorological variables influence
processes related to production, transport, and
release of most biogenic gases. Soil temperature
and moisture affect emissions from soils.

Making the Connection — from Air
Quality Research to Assessment

ORD scientists provide substantial
support ito the Agency in computer
modeling of pollutant transport and fate.
They perform analyses integrating inter-
continental transport and global change
effects with regional and urban scales
found in air quality models. This research
will directly contribute to the Global
Change Program's ability to assess the
effects of global change on air quality.

UV radiation affects chemical activity in the
troposphere and can either increase of decrease
ambient concentrations of air pollutants (UNEP
1998). Some ozone depleting substances and some
of their substitutes are also greenhouse gases and
thus can contribute to global climate change. Solar
radiation also plays a key role in determining fluxes
and leaf temperatures which are determinants of
biogenic emissions. Finally, patterns of land-use
can influence biogenic and anthropogenic emissions
(e.g., increased urban sprawl may result in higher
emissions from transportation sources or
construction activities that lead to fugitive dust).
Simultaneous changes in land-use and climate could
affect PM emissions (related to fugitive dust and
wildfire frequency) and emissions of volatile
organic compounds or VOCs (related to changes in
vegetation), important precursors of tropospheric
ozone. In addition, human activities can also
influence biological emissions (e.g., fertilized
agricultural soils tend to have high NOx emissions)
(Kinnee et al 1997). Quantitative estimates of the
potential magnitude of these combined effects are
needed for future assessments.

Existing atmospheric dispersion and transformation
models can be used in the assessments. Some
have been developed in support of federal clean air
programs and state implementation plans (SIPs).
These analytical and numerical models describe the
transport, dispersion, transformation, and removal
of atmospheric pollutants on local, urban, and
regional scales. Examples include the Industrial
Source Complex Model (ISC3) and the Urban
Airshed Model (UAM).

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More recently, ORD has developed a third-
generation air quality modeling system, Models-3.
This modeling system will be able to simulate an
atmosphere with various mixes of pollutants up to
continental scales and incorporate feedbacks
between chemical and meteorological components.
This will enable researchers to see how pollutant
concentrations are affected by climate changes or
how pollutants are transported across large
geographic areas.

The "one atmosphere" perspective of ORD's
Models-3 is consistent with the ultimate air quality
assessment goal of the Global Change Program.
However, the Program will not be directly involved
in Models-3 development. Instead, the Program
anticipates using Models-3 in future assessments of
global change impacts (augmented by models of
land-use change, energy demand, population
growth, climate change, and regulatory scenarios).
(For additional information see
www.epa.gov/asmdner/models3/.)

More generally, while current global stresses —
climate variability, UV radiation, and land-use
patterns — are affecting air quality, there are a
number of basic scientific questions that must be
resolved before the Global Change Program can
assess the air quality consequences of global
change. Many of these questions are the subject of
ongoing EPA research. While the Global Change
Program will not directly conduct scientific studies
on these questions it will work closely with others
in EPA involved in that research and will
incorporate new scientific findings in its
assessments of the air quality effects of global
change.

Adaptation — Potential Human Responses and
Co-Benefits

EPA currently has an extensive program to control
anthropogenic emissions of ozone precursors.
Knowledge of potential global change impacts on
ambient concentrations (e.g., through effects on
anthropogenic and biogenic emissions, atmospheric
transport, and stagnation frequencies) is needed to
design effective emissions control strategies.
Adaptive responses to global change will likely
involve continuation and possibly enhancement of
ongoing emission reduction efforts. However, it
will be necessary to evaluate potentially adverse

consequences of adaptation strategies. For
example, a strategy to reduce emissions from a
coal-fired power plant may involve building a new
gas pipeline through a sensitive ecosystem.

Impacts on the ecosystem should be considered
when evaluating this adaptive response.

In addition, there have been few studies of the
impact of policies and new technologies to reduce
greenhouse gas emissions on concentrations of
criteria air pollutants. As fossil fuel combustion is a
major source of both types of emissions, control
programs and new technologies can be expected to
yield substantial co-benefits. For example, in a
study examining the impact of a climate policy on
particulate emissions, major reductions in
particulate air pollution were realized (developed
countries reduce C02 emissions to 15% below
1990 levels, developing countries reduce C02
emissions to 10% below forecasted 2010 levels)
(Working Group on Public Health and Fossil-Fuel
Combustion, 1997). While this study relied on a
number of assumptions, the results can be viewed
as illustrative of the potential magnitude of the co-
control benefits of mitigation policies. Future
assessments in the Global Change Program will
rely, to the extent possible, on state-of-the-art air
quality models. EPA also plans to conduct the
research to support assessments of co-benefits
(e.g., the development of databases of criteria
pollutants and GHG emissions from alternative
technologies).

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Table 6. Focus Area III: Air Quality

Research Questions
(see related Assessment Component in next column)

Assessment Components
(Fiscal Year Due Date)

Assessment of Global Change Effects on Tropospheric Ozone

How will global climate change affect local and regional weather
patterns which influence air quality? (1)

What is the quantitative effect of global change on tropospheric
concentrations of ozone? (2,4)

Which geographic areas will experience the largest changes
(positive and negative) due to global change? (2,4)

How many areas will fail to attain the ozone levels required by
NAAQS due to global change? (2,4)

What is the effect of global change on emissions of ozone
precursors? (3)

How would societal chanaes and technoloav advancements
adoDted either to resDond to climate chanae or to reduce
harmful ambient levels of troDOSDheric ozone influence
emissions of troDOSDheric ozone Drecursors? What
combinations of human adaDtive resDonses would Drovide the
greatest reduction in ozone precursors at the lowest cost? (5)

What should be communicated to stakeholders about the
effects of global change on tropospheric ozone and potential
adaptation options? (5)

1.	Develop set of meteorological variables needed for air quality
simulations. (2002)

Obtain source code for the Regional Climate

Model/Mesoscale Model5 (RCM/MM5)

Obtain General Circulation Model (GCM) output data for

use as input data to RCM/MM5

Implement RCM/MM5 on EPA National Environmental

Supercomputing Center Cray T3E and UC Davis Beowulf

computer

Run baseline and future climate scenarios based on GCM
output data
Review scenarios

2.	Statistically analyze the relationship between tropospheric
ozone and weather. (2001)

3.	Develop baseline and future emissions scenarios. (2003)

Driver scenarios based on existing scenarios of economic
growth, energy demand, population growth, and vehicle
miles traveled
Policy scenarios

Future anthropogenic emissions scenarios
Future biogenic emissions scenarios

4.	Develop basecase ozone simulations and simulate future
ozone scenarios (2004)

5.	Develop a peer-reviewed assessment report on global
change effects on tropospheric ozone (2004)

Assessment of Global Change Effects on Particulate Matter

What will be the effect on fine particulate concentrations of
elevated temperatures and other meteorological changes that
may occur with global change? (1, 2, 4)

What is the quantitative effect of global change on atmospheric
concentrations of particulates? (2,4)

Which geographic areas will experience the largest changes
(positive and negative) due to global change? (2,4)

How many areas will exceed the NAAQS for particulates due to
global change? (2,4)

What is the effect of global change on particulate emissions?

(3)

1.	Conduct workshop for setting research agenda re: the global
change effects on particulate matter. (2001)

2.	Statistically analyze the relationship between particulate
matter and weather. (2003)

3.	Develop baseline (2005) and future emissions scenarios.
(2006)

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How would societal chanaes and technoloav advancements
adoDted either to resDond to climate chanae or to reduce
harmful ambient levels of Darticulate matter influence Darticulate
emissions? What combinations of human adaDtive resDonses
would Drovide the greatest reduction in particulate matter at the
lowest cost? (5)

What should be communicated to stakeholders about the
effects of global change on particulate matter and potential
adaptation options? (5)

Driver scenarios based on existing scenarios of economic
growth, energy demand, population growth, and vehicle
miles traveled
Policy scenarios

Future anthropogenic emissions scenarios
Future biogenic emissions scenarios

4.	Develop base case particulate matter simulations. (2007)
and simulate future particulate matter scenarios. (2007)

5.	Develop a peer-reviewed assessment report on global
change effects on particulate matter. (2008)

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Focus Area IV: Water Quality

Assessing the effects of global change
on water quality

The objective of the Clean Water Act is "to
restore and maintain the chemical, physical, and
biological integrity of the Nation's waters." To
achieve this objective, watersheds and their
aquatic ecosystems are being restored and
protected to improve human health, enhance
water quality, reduce flooding, and provide
habitat for wildlife. The Global Change Program
will assess the effects of global change on the
provision of clean and safe drinking water, the
protection of surface waters, and the treatment of
waste water.

Water quality is currently threatened by pollutants
and pathogens (e.g., nutrients, sediments,
microbial pathogens, pesticides, and other toxic
pollutants) and alterations in freshwater habitats,
streamflow, and water temperatures. These
threats to water quality could be exacerbated or
ameliorated by climate change, climate variability
or land-use change. Changes in climate and
climate variability may affect water quality,
primarily through changes in runoff. Runoff is
water that does not evaporate or seep into the
soil, but flows into streams, rivers, or lakes, and
may carry pollutants [IPCC 1998, p. 502],

Climate models predict increases in both
precipitation and evapotranspiration globally, with
regional variations. Runoff will increase in areas
where increases in precipitation exceed increases
in evapotranspiration. Depending on land-use
choices, the increased runoff may increase the
runoff of pollutants as well. Paving or grading
surfaces increases the amount, speed, and
temperature of runoff, thus increasing stream
temperatures and disrupting natural streamflows.
Increases in storm intensity can have the same
effect. High runoff speeds generally move more
pollutants. Conversely, wetlands and riparian
buffer zones can slow runoff, filter out pollutants,
and moderate alterations of temperature and
streamflow. Increases in pollutant runoff may
increase concentrations of pollutants in a water
body, depending on the diluting effects of the
increased runoff. If evapotranspiration rates
exceed precipitation, runoff will drop, and

pollutant runoff will drop as well. However, this
can have the effect of concentrating pollutants in
the water body as water levels drop. Changes in
climate that produce higher water temperatures,
lower flows, and lower water levels will increase
the negative effects of wastewater on freshwater
ecosystems (IPCC 1998).

The Global Change Program will assess the
effects of global change — changes in climate,
climate variability, and land-use — on water
quality, thus helping the Agency to fulfill its
commitment to safeguard the Nation's waters.
Specifically, the Program plans to assess the
consequences of global change for:

#	water quality related to pollutants and
microbial pathogens (2005), and

#	water quality related to biocriteria (2008).

Pollutants and microbial pathogens

Global change could alter the concentrations of
pollutants and pathogens in surface and ground
waters. These changes could have ramifications
for aquatic ecosystems, human recreational uses,
and drinking water. The Global Change Program
will examine the ability of public water systems to
respond to altered drinking water and waste water
treatment needs due to global change. In
addition, the availability of adaptation options to
protect surface waters for aquatic ecosystems and
for recreational uses will be explored.

Nutrients, microbial pathogens, pesticides and
other toxics pose a variety of risks to humans and
aquatic life. In addition, saltwater intrusion poses
a risk to aquatic life and coastal drinking supplies.
In 1999, about 10% of public water failed to meet
health-based drinking water standards. Many of
these violations were related to microbial
pathogens. EPA's Science Advisory Board
concluded in 1990 that exposure to microbial
contaminants such as bacteria, viruses, and
protozoa (e.g., Giardia lamblia or
Cryptosporidium) was likely the greatest
remaining health risk management challenge for
drinking water suppliers (www.epa.gov/
OGWDW/mdbp/mdhr) htmlY In 2000, the EPA
reported that over 20,000 water bodies have been
identified as polluted.

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(www.eDa.gov/owow/tmdl/finalrule/factsheetl.ht
ml). Nutrient pollution is a particularly serious
problem. According to EPA's National Water
Quality Inventory: 1994 Report to Congress,
excessive nutrient enrichment impairs 23% of the
nation's surveyed rivers, 43% of its surveyed
lakes, and 47% of its surveyed estuaries (EPA
1998a).

Making the Connection — from Water
Quality Research to Assessment

ORD's expertise in developing and testing
water treatment technologies and in
modeling and analyzing surface water
systems will be applied to assess
adaptation needs and options for water
system managers. ORD researchers are
modeling the effects of a range of climate
change scenarios on runoff in the Ohio
River basin and examining the impacts of
these changes on surface water quality.
Changes in pollutant concentrations in
surface waters may affect the ability of
drinking water and waste water treatment
systems to meet water quality standards.

The Global Change Program's assessment of
pollutants and pathogens will focus on three
aspects of water quality: drinking water
infrastructure, wastewater treatment, and surface
water quality. Municipal and industrial waste
waters must be treated in order to protect
downstream water quality. The quality of surface
waters affects the ability of municipalities to use
the surface water as a drinking water source and
the ability of the aquatic ecosystems to support
aquatic life and recreation. The Global Change
Program's assessment will assess the
consequences of global change for these three
aspects, and will examine the potential for
adaptive responses to protect drinking and surface
waters for human and ecosystem uses. The
interconnectedness of the three aspects may
provide opportunities to look at multiple benefits
associated with watershed protection strategies.
Table 7 outlines the research questions that will
guide the assessment and the components
necessary to complete the assessment. These
components map directly into capabilities at the
labs and centers and those of the extramural
grants program (see Program Capabilities, p. 10-

11).

Biocriteria

To comply with the Clean Water Act's
requirement that state water quality standards
shall consist of designated uses and the criteria for
protecting such uses (Section 303(c)(2)(A)), and
with the objective of restoring the biological
integrity of the nation's waters, EPA is working
with states to develop biocriteria (Section 101(a)).
The Water Quality Criteria and Standards
Program is pursuing the development of
biocriteria as an improved basis for aquatic life
protection because "biocriteria and
bioassessments will help to identify ... the
cumulative impacts of all stressors within a water
body" (EPA 1998a). Biological indicators are
used to measure the ability of a water body to
support aquatic life; biocriteria are those attributes
that a water body should possess to support
aquatic life (Gibson 1996). The EPA has
developed technical guidance documents to assist
states and tribal nations in developing biological
assessment methods and criteria for streams and
wadeable rivers and for lakes and reservoirs. The
states are in the process of implementing these
methods, and three states (Ohio, Maine and
Florida) have developed numerical biocriteria for
streams and wadeable rivers.

The ability of states to attain biocriteria will be
influenced by changes in climate, climate
variability, land-use and UV radiation. These
global changes could alter water temperatures,
stream morphology, stream flow and lake levels,
UV effects on aquatic life, pollutant
concentrations in water bodies, and
sedimentation. These changes will in turn affect
aquatic life and be reflected by changes in
biological indicators that are used for biocriteria.
(See also the assessment of Aquatic Ecosystems
in the Ecosystems Focus Area and the assessment
of Pollutants and Pathogens in the Water Quality
Focus Area. These assessments will contribute to
the Biocriteria assessment.)

The Global Change Program will develop a
framework that states can use to assess the
effects of global change on their ability to meet
biocriteria and to identify adaptation strategies to
cope with global change. Detailed studies will be
conducted in two to four states that have
established biocriteria for streams and wadeable
rivers. Later detailed studies will expand the

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framework to biocriteria for lakes and reservoirs.
The final step of the analysis will evaluate the
applicability of the framework to states that were
not included in the detailed studies. Table 7
outlines the research questions that will guide the
assessment and the components necessary to
complete the assessment.

Table 7. Focus Area IV: Water Quality

Research Questions
(see related Assessment Component in next column)

Assessment Components
(Fiscal Year Due Date)

Assessment of Impact of Global Change on Water Quality: Pollutants and Microbial Pathogens

Which pollutants do public water systems currently have
difficulty treating? (1)

How may global change affect the loads of those pollutants?
What new challenges may arise due to global change? (1)

Wll public water systems be able to treat changing loads of
pollutants or handle new challenges? (1)

How much will treatment to meet current standards under
future conditions cost? (1)

Are there alternatives to traditional treatment methods, what do
they cost, and what other benefits or costs do they incur? (1)

Do communities rely on coastal aquifers and rivers for their
public water supplies? How many people are served? (2)

Are rising seas, storm surges, and changes in river flows likely
to lead to saltwater intrusion in public water systems? (2)

What can be done to protect water supplies? (2)

Which pollutants currently inhibit attainment of water quality
criteria, and what are their sources? (3)

If those pollutants are susceptible to changes in runoff and land-
use, how may future changes in climate and land-use affect
water quality? (3)

What adaptation strategies might water resource managers and
other stakeholders use to achieve water quality criteria for
surface waters under conditions of global change? (3)

1.	Assessment of Drinking Water Infrastructure (2001)

Draw from current reports to identify current challenges
involved in meeting Safe Drinking Water Act and
Amendments (SDWAA) standards

Estimate effects of global change on those challenges.
Identify possible new challenges.

Determine if current treatment methods are adequate for
future treatment needs based on future global change
impacts (to meet SDWAA standards)

Identify costs of any additional treatment needs

Identify alternative approaches to treatment, their costs,
and multiple benefits.

2.	Assessment of Sea Level Rise on Coastal Aquifers and
Rivers (2001)

Identify public water systems that rely on coastal rivers
and aquifers for their water supply. Identify numbers of
people served by those systems

Utilize existing projections of sea-level rise and changes in
river flow to determine vulnerability of public water systems

Develop options for adaptation and their costs

3.	Assessment of Pollutants and Pathogens in Surface Waters
(2003)

Determine from available sources which pollutants and
pathogens currently pose problems for lakes, rivers, and
streams, and identify the sources of those pollutants and
pathogens.

Use existing land-use, regional climate, and hydrology
models to estimate how climate and land-use change may
alter the concentrations of pollutants and pathogens in
surface waters.

Identify approaches for adapting to global change.

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What challenges do industrial and municipal waste water
treatment systems face currently? (4)

How may climate and land-use change exacerbate or
ameliorate those challenges? (4)

What changes in treatment methods may be needed to respond
to current and future challenges and meet water quality
standards? (4)

How much will it cost to respond to current or future
challenges? (4)

What range of approaches is available to protect water
resources? (4)

How can we effectively summarize what we have learned about
global change impacts on pollutants and microbial pathogens
for stakeholders? (5)

4.	Assessment of Waste Water Treatment (2003)

Determine from available sources current challenges for
wastewater treatment facilities.

Utilize federal and private research to obtain regionally
specific climate change, land-use, and hydrology
scenarios.

Determine changes needed in treatment in order to meet
receiving water standards under conditions of global
change

Determine costs associated with changing treatment
requirements

Identify alternative approaches to treatment, their costs,
and multiple benefits.

5.	Develop a peer-reviewed assessment report summarizing
findings on global change impacts on pollutants and microbial
pathogens. (2005)

Summarize the findings of the drinking water, wastewater,
and pollutant and pathogen studies, including the options
for adaptation and consideration of multiple benefits
approaches.

Assessment of Impact of Global Change on Water Quality: Biocriteria

Which biological indicators may be used, or are being used, by
the states to develop biocriteria for streams and wadeable
rivers? (1)

Which of these biological indicators might be sensitive to
climate variability and change? to land-use change? to UV
radiation? (1)

How could changes in climate, climate variability, land-use and
UV radiation affect states' abilities to attain biocriteria in their
streams and wadeable rivers? (1)

How can states identify adaptation strategies that could help
them attain biocriteria in the face of global change? (2)

How can state-specific analyses improve our understanding of
the vulnerability of streams and wadeable rivers (as measured
by states' ability to attain biocriteria) to global change? (3)
Are the biological indicators sensitive to global change as
forecasted by scenarios? Could global change affect the ability
of these states to meet biocriteria? (3)

What adaptation options are available to states? How do
adaptation options link to other environmental programs (e.g.,
NPDES, TMDL, watershed protection, ecological restoration)?
(3)

1.	Develop a paper describing the potential sensitivity of
biocriteria for lakes, rivers and streams to climate change and
variability, changes in land-use and UV radiation. Convene an
expert workshop to review the paper and establish consensus
on its conclusions. (FY2004)

Identify biological indicators that can be used by states to
develop biocriteria.

Adapt the conceptual model developed for the Aquatic
Ecosystems assessment to include these indicators.
Include relevant information from the Pollutants and
Pathogens assessment.

2.	Develop a paper that outlines a framework that states could
use to identify adaptation strategies that could help them meet
biocriteria, given potential changes in land-use, climate, climate
variability, and UV radiation. Convene an expert panel to review
the adaptation paper and establish consensus on the its
conclusions. (FY2005)

Use the first paper to identify challenges that states might
face in meeting biocriteria under conditions of global
change.

Draw on expert opinion, literature review, and the previous
assessments of Aquatic Ecosystems and Pollutants and
Pathogens for information about adaptation options.

3.	Conduct detailed studies in 2-4 states (e.g., Ohio, Maine and
Florida) that have established biocriteria for streams and
wadeable rivers. Work with the states and EPA's Office of
Water to test the framework for assessing potential effects of
global change on the ability of states to meet biocriteria for
streams and wadeable rivers and assess adaptation options to
cope with global change. (FY2006)

Use or adapt existing climate, land-use, and UV scenarios
for the identified states.

Identify which biocriteria for streams and wadeable rivers
for these states are potentially sensitive to global change.
Evaluate the direction, approximate magnitude, and level of

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How does the framework need to be modified to apply to lakes?
(4)

What is the vulnerability of lakes (as measured by states' ability
to attain biocriteria) to global change? (4)

What adaptation options are available to states? (4)

What biological indicators are used by other states to develop
biocriteria? (5)

Are the results developed for specific states for streams,
wadeable rivers and lakes applicable to biological indicators
used by other states and global change scenarios for other
states? (5)

What should we communicate to states, the EPA Office of
Water, and other stakeholders to facilitate their understanding of
the vulnerability of aquatic ecosystems - as measured by their
attainment of biocriteria - to global change, and to aid their
evaluation of adaptation options? (6)

uncertainty for the effects of global change on biological
indicators used as biocriteria by states.

Identify adaptation options that could help these states
meet their biocriteria.

4. Expand the framework so that it can address biocriteria for

lakes. (FY2007)

Develop a paper, adapting the approach used in the first
two papers (about the sensitivity of biocriteria for streams
and wadeable rivers and adaptation options for these
systems) and apply it to lakes.

Conduct detailed studies in previously studied states
(e.g., Ohio, Maine and Florida) and/or in new ones to
assess potential effects of global change on their ability to
meet biocriteria for lakes. Assess adaptation options to
cope with global change.

5.	Evaluate the applicability of the framework for states that
were not included in the detailed studies of specific states.
(FY2007)

Identify which biological indicators are used by other
states that have developed biocriteria.

Using conceptual models, evaluate whether the framework,
developed by specific states for specific biological
indicators, global change scenarios, and adaptation
options, is applicable to other states.

6.	Prepare a final report that describes a framework that states
can use to assess their vulnerability, with respect to biocriteria,
to global change and what adaptation options are available to
them to help them meet biocriteria in the face of global change.
The report will include results for particular states that were
developed in the case studies and extrapolate those results, as
appropriate, to other situations. (FY2008)

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EPILOGUE

This Research Strategy outlines an ambitious ten-
year plan for the Global Change Research
Program. The assessment orientation is a
significant departure from global change research
conducted by ORD in the past. A redirection of
such proportions has not been easy, and without
the cooperation and collaboration of individuals
and institutions across ORD it would not have
been possible.

The redirection is necessary, however, if we are
to satisfy the needs of our stakeholders. The aim
of the assessments described in this Strategy is to
provide scientifically sound support to
stakeholders as they try to make policy and
resource management decisions under conditions
of uncertainty. By providing a better

understanding of the consequences of a range of
actions, including inaction, the Global Change
Program will be poised to inform the difficult
choices expected of decision makers.

The redirection is also necessary to make the
most of limited research budgets, and to ensure
that the various Federal Agencies coordinate their
efforts to exploit relative strengths. EPA's
strength lies in assessments of the possible
impacts of global change. ORD will not be able
to fulfill the expectations outlined in this Strategy
without the contributions of all of the constituent
labs and centers, our academic partners, and the
general stakeholder community.

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GLOSSARY and IMPORTANT CONCEPTS

adaptability (or adaptation)

Adaptation refers to human interventions that
can be carried out in response to, or in
anticipation of, changes in condition due to
projected or actual changes in climate and
other environmental stresses.

assessment

An iterative analytic process that engages both
analysts and end-users to evaluate and interpret
the interactions of dynamic physical, biological,
and social systems and communicate useful
insights about the significant causes and likely
consequences of global change (NAWG 1999).

biocriteria

Biocriteria are the specific attributes that a
water body should possess, and thus can be
used in biological assessment to determine how
well a water body supports aquatic life (Gibson
1996). Biological assessments of aquatic
ecosystems examine the density and relative
abundance of resident organisms, the condition
of their immediate habitat, and the condition of
their watershed. Sites that are being evaluated
are compared against a specified reference
condition to determine the level and nature of
impairment (Larsen 1997).

biodiversity

"The variability among living organisms from
all sources, including, inter alia, terrestrial,
marine, and other aquatic ecosystems and the
ecological complexes of which they are part;
this includes diversity within species, between
species, and of ecosystems" (UNEP 1995, p.8,
adopted from Article 2, "Use of Terms", in the
Convention on Biological Diversity).

climate

The average course or condition of the weather
at a place, usually over a period of 30 years or
more.

climate change

"Any change in climate over time whether due
to natural variability or as a result of human
activity" (IPCC 1996c, p.3).

climate variability

Fluctuations in climate at different time scales,
e.g., seasonal, annual, inter-annual, decadal,
and beyond, usually expressed on a regional
basis.

conceptual model

A written description and visual representation
of predicted relationships between ecological
entities and the stressors to which they may be
exposed. Conceptual models are developed
from information about stressors, potential
exposure, and predicted effects on an
ecological entity. Conceptual models consist of
two principal components: 1) a set of risk
hypotheses that describe predicted relationships
among stressor, exposure, and assessment
endpoint response, along with the rationale for
their selection, and 2) a diagram that illustrates
the relationships presented in the risk
hypotheses. (U.S. EPA 1998c)

ecosystem

"All individuals, species, and populations in a
spatially defined area, the interactions among
them, and those between the organisms and the
abiotic environment" (UNEP 1995, p. 281).

ecosystem functioning

"The sum total of processes operating at the
ecosystem level, such as the cycling of matter,
energy, and nutrients, as well as those
processes operating at lower ecological levels
which impact on patterns or processes at the
ecosystem level" (UNEP 1995, p.281).

ecosystem services

"The conditions and processes through which
natural ecosystems, and the species that make
them up, sustain and fulfill human life" (Daily
1997, p.3).

extreme event

A climatic event that is a deviation from normal
climate, and that has a finite but usually low
probability of occurring in a particular place.
Examples include extreme precipitation events
(floods, droughts), extreme temperature events,

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extreme wind events (tornados, hurricanes,
etc.).

global change

Changes in the global environment (including
alterations in climate, land use and
productivity, oceans and other water resources,
atmospheric chemistry, and ecological systems)
that occur at rates that may alter the capacity
of the Earth to sustain life.

human dimensions of global change

"Encompasses analysis of the human causes of
global environmental transformations, the
consequences of such changes for societies and
economies, and the ways in which people and
institutions respond to the changes. It also
involves the broader social, political, and
economic processes and institutions that frame
human interactions with the environment and
influence human behavior and decisions"
(NRC 1999, p.295).

land cover

"The pattern of ecological resources and
human activities dominating different areas of
the earth's surface" (EPA 1997). A land cover
category is "that which overlays or currently
covers the ground, especially vegetation,
permanent snow and ice fields, water bodies,
or structures. Barren land is also considered a
"land cover" although technically it is lack of
cover. Land cover can be thought of as
applying to the setting in which action (one or
more different land-uses) takes place" (USDA
1989).

land-use

Refers to the purpose to which land is put
(e.g., protected areas, forestry for timber
products, plantations, row-crop agriculture,
pastures, or human settlements). Land cover,
which is the ecological state and physical
appearance of the land, is often used as a
proxy for land-use (Daly et al. 1999).

potential multiple benefits or co-benefits

Secondary benefits associated with strategies to
address the risks and opportunities created by
global change.

resilience

The ability of an ecosystem (or other system)
to maintain its valuable attributes despite
pressures upon the system exerted by stressors.

sensitivity

In the context of climate change, sensitivity is
defined as "the degree to which a system will
respond to a change in climatic conditions (e.g.,
the extent of change in ecosystem composition,
structure, and functioning, including primary
productivity, resulting from a given change in
temperature or precipitation)" (IPCC WGII
1996).

stakeholder

"Any organization, governmental entity, or
individual that has a stake in or may be
impacted by a given approach to environmental
regulation, pollution prevention, energy
conservation, etc." (EPA 1999).

stressor

"Any physical, chemical, or biological entity
that can induce an adverse response" (EPA
1998c).

vulnerability

In the context of climate change, vulnerability
is defined as "the extent to which climate
change may damage or harm a system. It
depends not only on a system's sensitivity but
also on its ability to adapt to new climatic
conditions" (IPCC WGII 1996).

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APPENDIX A: HISTORICAL OVERVIEW

Prior to the significant redirection described in this
document, the Global Change Program traditionally
responded to USGCRP goals of data collection
(e.g., carbon flux tracking), process-oriented
research (e.g., carbon cycle analysis and
development of carbon sequestration options).
Another focus of the program was on the
development of technologies to mitigate greenhouse
gas emissions. The shift towards an assessment-
oriented program entails significant disinvestments
in specific activities and redirections of resources.
Today, the Global Change Program no longer
addresses mitigation policies, technology
development, carbon cycle analysis, and carbon
sequestration issues.

While the redirection of the Global Change
Program was based in large part on a fundamental
shift in priorities and on the focusing of the
USGCRP mandate to member agencies, the
budgetary figures for the 1990s (Figure 4) reflect
an additional impetus for change — the need for
program restructuring given the significant added
constraints of a nearly 50% reduction in budgetary
resources from 1994 to 1997.

~ The following publications are examples of the
excellent scientific work completed in the
Global Change Program prior to the
redirection.

Benrenfeld H, Gucinski L. 1993. Acute and
chronic effects of ultraviolet-b radiation on marine
phytoplankton. Marine Environmental Research.
35: 349-363.

Berdowski JJM, Beck L, Piccot S, Olivier JGJ,
Veldt C. 1993. Working Group Report: Methane
Emissions from Fuel Combustion and Industrial
Processes. In AR vanAmstel (editor), Proceeding
of an International IPCC Workshop on Methane
and Nitrous Oxide: Methods in National Emissions
Inventories and Options for Control. RIVM Report
No. 481507003. Bilthoven, The Netherlands.

Borgwardt RH. 1997. Biomass and Natural Gas
as Co-feedstocks for Production of Fuel for Fuel-
cell Vehicles. Biomass and Bioenergy. 12(5): 333-
345.

Borgwardt RH. 1992. A Technology for
Reduction of C02 Emissions from the
Transportation Sector. Energy Conversion
Management. 33(5-8) 443-449.

CD
"O

co

c c
ro o

ra ?

35
30
25
20
15
10

Budget History
Global Change Research Program

ll

1989 1991 1993 1995 1997 1999

1990 1992 1994 1996 1998 2000

Fiscal Year

Figure 4. Budgetary History of ORD's Global Change
Program

Burke RA, Zepp RG, Tarr MA, Miller WL, Stocks
BJ. 1997. Effect of fire on soil-atmosphere
exchange of carbon dioxide and methane in a
Canadian boreal forest. Journal of Geophysical
Research. 102(D24-29): 29289-29300.

Cleland JG, Purvis CR. 1996. Independent Power
Plant Using Wood Waste. Energy Conversion
Management. 37(6-8): 1205-1209.

Cole V, Cerri C, Minami K, Rosenberg N,
Sauerbeck D, Mosier A, Barnwell T, Dumanski J,
Duxbury J, Feller C, Freney J, Gupta R,
Hein-meyer O, Kolcugina T, Lai R, Lee J, Ojima
D, Paustian K, Post W, Powlson D, Sampson N,
Tiesses H, van Noordwijk M, Zhao Q, Kimble J,
Fisher M, Tarnocai C, Monreal C, Desjardin RL,
Gregorich EG, Cambell CA, Abrol IP, Vinson T.
1996. Chapter III.E: Mitigation Options in
Agriculture. In Houghton JJ, Meiro Filho LG,

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Callander BA, Harris N, Kattenberg A, Maskell K
(Editors). Climate Change 1995: Impacts,
Adaptations and Mitigation of Climate Change:
Scientific-Technical Analyses. Contribution of
Working Group II to the Second Assessment
Report of the Intergovernmental Panel on Climate
Change. Cambridge University Press. Cambridge,
UK.

Eaton JG, McCormick JG, Goodno BE, O'Brien
DG, Stefan HG, Hondo M, Scheller RM. 1995. A
field information-based system for estimating fish
temperature tolerances. Fisheries. 20(4): 10-18.

Elvidge CD, Yuan D, Weerackoon RD, Lunetta
RS. 1995. An automated scattergram controlled
regression technique for image normalization.
Photogrammetric Engineering and Remote Sensing.
61(10): 1255-1260.

Donigian AS, Barnwell TO, Jackson RB,
Patwardhan AS, Weinrich KB, Rowell AL,
Chinnaswamy RV, Cole CV. April 1994.
Assessment of Alternative Management Practices
and Policies Affecting Soil Carbon in
Agroecosystems of the Central United States.
EPA/600/R-94/067. U.S. Environmental
Protection Agency, Environmental Research
Laboratory, Athens GA.

Flach KW, Barnwell TO, Crosson P. 1996.
Impacts of Agriculture on Atmospheric Carbon
Dioxide. In Paul EA, Paustian K, Elliott ET, Cole
CV (Editors), Soil Organic Matter in Temperate
Agroecosystems: Long-Term Experiments in
North America. CRC Press. Boca Raton, FL.

Gage CL, Troy E. November, 1998. Reducing
Refrigerant Emissions from Supermarkets.
ASHRAE Journal.

Heggem DT, Neale AC, Edmonds CM, Bice L,
Jones KB. 1999. An Ecological Assessment of the
Louisiana Tensas River Basin. EPA
600/R-99/016. U.S. Environmental Protection
Agency, Office of Research and Development,
Washington DC.

Kazachki GS, Gage CL, Hendriks RV. August 20-
25, 1995. Chlorine-Free Alternatives for CFC-114:
Theoretical and Experimental Investigations.

Proceedings of the XlXth International Congress of
Refrigeration. The Hague, Netherlands.

Kirchgessner DA, Piccot SD, Chadha A. 1993.
Estimation of Methane Emissions from a Surface
Coal Mine Using Open-Path FTIR Spectroscopy
and Modeling Techniques. Chemosphere. 26: 23-
44.

Kirchgessner DA, Lott RA, Cowgill RM, Harrison
MR, Shires TM. 1997. Estimate of methane
emissions from the U.S. natural gas industry.
Chemosphere. 35: 1365-1390.

Lunetta RS, Lyon JG, Sturdevant JA, Dwyer JL,
Elvidge CD, Fenstermaker LK, Yuan D, Hoffer
SR, Werrackoon R. 1993. North American
Landscape Characterization: Research Plan.
EPA/600/R-93/135. 419p.

Lunetta RS, Lyon JG, Guindon B, Elvidge CD.
1998. North American Landscape Characterization
Dataset Development and Data Fusion Issues.
Photogrammetric Engineering & Remote Sensing.
64(8): 821-829.

Lunetta RS, Elvidge CD (Editors). 1998.
Environmental Monitoring Methods and
Applications Book. Remote Sensing Change
Detection. 318p.

Lunetta RS, Elvidge CD (Editors). 1999. Remote
Sensing Change Detection: Environmental
Monitoring Methods and Applications. ISBN
1-57504-037-9. Ann Arbor Press. Chelsea, MI.
350p.

Lyon JG, Ding D, Lunetta RS, Elvidge CD. 1998.
A change detection experiment using vegetation
indices. Photogrammetric Engineering and Remote
Sensing. 62(2): 143-150.

Piccot SD, Beck LL, Sinivasan S, Kersteter SL.
October 20, 1996. Global Methane Emissions
from Minor Anthropogenic Sources and Biofuel
Combustion in Residential Stoves. Journal of
Geophysical Research. 101(D17).

Solomon AM, et al. 1995. Wood Production
Under Changing Climate and Land-use. In
Climate Change 1995 Intergovernmental Panel on
Climate Change.

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Solomon AM, Leemans R. 1997. Boreal forest
carbon stocks and wood supply: past, present and
future responses to changing climate, agriculture
and species availability. Agricultural and Forest
Meteorology. 84: 137-151

Solomon AM, Kirlenko AP. 1997. Climate Change
and terrestrial biomass: what if trees do not
migrate? Global Ecology and Biogeography. 6:
139-148

Summers JK, Tonnessen KE. 1998. Linking
monitoring and effects research: EMAP's intensive
site network program. Environmental Monitoring
and Assessment, 51:369-380.

Thompson SL, Pollard D. 1997. Greenland and
Antarctic mass balances for present and doubled
C02 from the GENESIS version-2 global climate
model. Journal of Climate. 10: 871-900.

Thorneloe SA, Barlaz MA, Peer R, Huff LC,

Davis L, Mangino J. 1993. Global Methane
Emissions from Waste Management. Published in
The Global Methane cycle: Its Sources, Sinks,
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ASI Series.

Zepp RG, Callaghan TV, Erickson DJ. 1998.
Effects of enhanced solar ultraviolet radiation on
biogeochemical cycles. Journal of Photochemical
Photobiology. B(46): 69-82.

# The following are selected publications
produced by STAR grantees working on
global change research since the inception of
the STAR program in 1995.

Chun J, Huq A, Colwell RR. 1999. Identification
of Vibrio cholerae based on genes coding for 16S-
23 S rRNA internal transcribes spacers. Applied
Environmental Microbiology. 65: 2202-2208.

Doering OC, Habeck M, Lowenberg-DeBoer J,
Randolph JC, Johnston JJ, Littlefield BS,

Mazzocco M, Kinwa M, Pfeifer R. 1997.
Mitigation strategies and unforeseen consequences:
a systematic assessment of the adaptation of upper
Midwest agriculture to future climate change.

World Resource Review. 9: 447-459.

Kocagil P, Demarteau N, Fisher A, Shortle JS.
1998. The Value of Preventing Cryptosporidium
Contamination. Risk: Health, Safety and
Environment. 9:175-196.

Littlefield BZ, Ehman JL, Fan W, Johnston JJ,
Offerle B, Randolph JC. 1998. Climate change
effects on agricultural productivity in the
Midwestern Great Lakes Region. Ch. 49 in
Multiple Objective Decision Making for Land,
Water and Environmental Management (SA El-
Swaify and DS Yakawitz, editors) Lewis
Publishing.

Southworth J, Randolph JC. 1998. The
implications of current and future climate variability
on crop growth in the Midwestern region of the
United States. Bulletin of the Ecological Society
America 79:219.

Vogel RM, Bell C, Fennessey NM. 1997.

Climate, Streamflow and Water Supply in
Northeastern United States. Journal of Hydrology.
198(1-4): 42-68.

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APPENDIX B: GLOBAL CHANGE RESEARCH ACT of 1990

U.S. Global Change Research Program Act of 1990
Public Law 101-606(11/16/90) 104 Stat. 3096-3104

An Act to require the establishment of a United States Global Change Research Program aimed at
understanding and responding to global change, including the cumulative effects of human activities and
natural processes on the environment, to promote discussions toward international protocols in global
change research, and for other purposes.

Be it enacted by the Senate and House of Representatives of the United States ofAmerica in Congress

assembled,

SECTION 1. SHORT TITLE.

This Act may be cited as the "Global Change Research Act of 1990".

TITLE I—UNITED STATES GLOBAL CHANGE RESEARCH PROGRAM

SEC. 101. Findings And Purpose.

(a)	Findings — The Congress makes the following findings:

1.	Industrial, agricultural, and other human activities, coupled with an expanding world population, are
contributing to processes of Global change that may significantly alter the Earth habitat within a few
human generations.

2.	Such human-induced changes, in conjunction with natural fluctuations, may lead to significant
global warming and thus alter world climate patterns and increase Global sea levels. Over the next
century, these consequences could adversely affect world agricultural and marine production,
coastal habitability, biological diversity, human health, and Global economic and social well-being.

3.	The release of chlorofluorocarbons and other stratospheric ozone-depleting substances is rapidly
reducing the ability of the atmosphere to screen out harmful ultraviolet radiation, which could
adversely affect human health and ecological systems.

4.	Development of effective policies to abate, mitigate, and cope with Global change will rely on
greatly improved scientific understanding of Global environmental processes and on our ability to
distinguish human-induced from natural Global change.

5.	New developments in interdisciplinary Earth sciences, Global observing systems, and computing
technology make possible significant advances in the scientific understanding and prediction of these
Global changes and their effects.

6.	Although significant Federal Global change research efforts are underway, an effective Federal
research program will require efficient interagency coordination, and coordination with the research
activities of State, private, and international entities.

(b)	Purpose — The purpose of this title is to provide for development and coordination of a
comprehensive and integrated United States research program which will assist the Nation and the world
to understand, assess, predict, and respond to human-induced and natural processes of global change.

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SEC. 106. SCIENTIFIC ASSESSMENT.

On a periodic basis (not less frequently than every 4 years), the Council, through the Committee, shall
prepare and submit to the President and the Congress an assessment which —

#	integrates, evaluates, and interprets the findings of the Program and discusses the scientific
uncertainties associated with such findings;

#	analyzes the effects of Global change on the natural environment, agriculture, energy production
and use, land and water resources, transportation, human health and welfare, human social systems,
and biological diversity; and

#	analyzes current trends in Global change, both human- induced and natural, and projects major
trends for the subsequent 25 to 100 years.

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