Final Report
Superfund Subcommittee of the
National Advisory Council for
Environmental Policy and Technology

April 12, 2004
 This is the Final Report of the Superfund Subcommittee of the National Advisory Council for Environmental
 Policy and Technology. The Subcommittee has completed its deliberations and its charter has ended. This
 final Subcommittee report has been transmitted in draft to the NACEPT Council for the Council's
 consideration.

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                      ~ NOTICE ~

The  National Advisory  Council for Environmental Policy and
Technology is an independent federal advisory committee that
provides  recommendations to the Administrator of the  U.S.
Environmental  Protection  Agency  on  a  broad  range  of
environmental issues. NACEPT provides balanced and expert
assessments  of policy  matters related to the  environmental
programs of the United States. Its operation is supported by the
EPA.  The Superfund Subcommittee of NACEPT was formed in
June, 2002 to  consider the role of the A/PL, Superfund mega
sites,  and Superfund Program performance measures in the
context of other federal, state,  and Tribal programs. The findings
and recommendations of the  Subcommittee as reflected in this
report  do  not  necessarily  represent  the  views   of the
Environmental Protection Agency.

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Final  Report
Superfund Subcommittee
-J me
	j
 This is the Final Report of the Superfund Subcommittee of the National Advisory Council for Environmental \
 Policy and Technology. The Subcommittee has completed Its deliberations and its charter has ended. This \
 final Subcommittee report has been transmitted In draft to the NACEPT Council for the Council's \
 consideration.                                        \

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Contents
Subcommittee Members
Introduction from the Chair

Executive Summary	i
I.  Introduction	1
II.  Background and Context for NPL/Mega Sites	7
III. Listing and Management of Sites on the NPL	25
IV. Mega Sites	69
V.  Measuring Program Progress	79
VI. Additional Priority Issues	97
Glossary of Terms	111
List of Acronyms	115

Attachment A:  Subcommittee Members' Individual Statements
Appendix I:     Revised Charge to the Subcommittee
Appendix II:     Original Charge to the Subcommittee
Appendix III:    Memo from Elliott P. Laws Concerning Remedial Action Priority
               Setting
Appendix IV:    Memo from Henry L. Longest II Concerning Guidance on Setting
               Priorities for NPL Candidate Sites
Appendix V:    Performance Profile
Appendix VI:    Additional Elements of Comprehensive Reporting
Appendix VII:    Community Satisfaction Survey
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                                                                   Contents

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List of Figures
Figure 11-1:    How Sites Get Listed on the NPL	9
Figure II-2:    Pipeline Status of 1,518 Final and Deleted Sites on the NPL	12
Figure II-3:    Distribution of 142 Mega Sites by Region	14
Figure II-4:    All NPL Activity Type (Proposed, Final, Deleted)	15
Figure II-5:    Activity Type (and Manufacturing Subtype) for 142 NPL Mega Sites.... 15
Figure II-6:    Actual/Planned Construction Obligations for 60 Fund- and
              Mixed-Lead Non-Federal NPL Mega Sites	18
Figure II-7:    Total Appropriations to the Superfund Program, 1993-2004	19
Figure II-8:    Superfund Program Expenditures by Category
              (e.g., Removal, Remedial), FY 2002 (Excludes ORD and OIG)	20
Figure II-9:    Superfund Expenditures by Office, FY2003 (Total $1.265 Billion)	21
Figure 11-10:   Superfund Expenditures—Programmatic and Administrative,
              FY 1999-2003	21
Figure 11-11:   Superfund Cleanup Expenditures  (Removal, Remedial  Action,
              Long-Term Response Action), FY 1993-2003	22
Figure V-1:    Superfund Construction Completions by Fiscal Year	81
Contents
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Subcommittee Members
All members served on the Subcommittee from June 2002 through March 2004 unless
indicated with alternate dates.
Raymond Loehr - Chairman
Hussein M. Alharthy
Centennial Chair Emeritus
University of Texas at Austin
Lansdowne, VA
William Adams
Director of Environmental Science
Kennecott Utah Copper Corporation
Magna, UT

Sue Briggum
Director, Environmental Affairs
Waste Management, Inc.
Washington, DC

Doris Cellarius*
Vice Chair,
Environmental Quality Strategy Team
Sierra Club
Prescott, Arizona
(June 2003-March 2004)

Grant Cope*
Attorney
Earthjustice
Seattle, WA

James Derouin
Attorney
Steptoe & Johnson LLP
Phoenix, AZ
Richard Dewling
President
Dewling Associates, Inc.
Environmental Engineers and Scientists
Union, NJ

Steve Elbert
Senior Vice President
BP America, Inc.
Warrenville, IL

Jane Gardner
Manager& Counsel,
Remediation Programs
Corporate  Environmental Programs
General Electric Company
Fair-field, CT

Mark Giesfeldt
Director,
Remediation and Redevelopment
Program
Wl Department of Natural Resources
Madison, Wl
(June 2002-March 2003)
* All individuals listed  as  Subcommittee members  participated  fully in  the deliberations of the
Subcommittee. Their perspectives helped to shape the consensus recommendations and are reflected in
the range of views expressed throughout the Final Report.  However, the individuals indicated do not
support the document as a whole because of either their strongly held opposition to the ideas presented or
the way in which the ideas have been described. For elaboration on dissenting opinions, please refer to
the three-page individual statements in Attachment A.
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                                                             Subcommittee Members

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Glen Hammer
Vice President,
Environmental Health and Safety
Ashland, Inc.
Columbus, OH

Dolores Herrera
Senior Advisor
Alianza Ambiental Center
Environmental Justice
Albuquerque, NM

Robert Hickmott
Senior Vice President
Smith-Free Group
Washington, DC

Aimee Houghton*
Associate Director
Center for Public Environmental
Oversight
Washington, DC

Ken Jock
Director, Environment Division
St. Regis Mohawk Tribe
Akwesasne, NY

Frederick M. Kalisz, Jr.
Mayor
City of New Bedford
New Bedford, MA

Gary King
Manager,  Division of Remediation
Management
Bureau of Land
Illinois Environmental Protection Agency
Springfield, IL
(June 2003-March 2004)

Ed Lorenz
Chair, Pine River Superfund Task
Force/Professor of History and
Political Science
Alma College
Alma, Ml
Mildred McClain
Executive Director
Harambee House, Inc.
Savannah, GA

Michael Mittelholzer
Director, Regulatory Affairs
National Association of Home Builders
Washington, DC

Tom Newlon
Attorney
Stoel Rives
Seattle, WA

Lindene E. Patton
Vice President and Counsel
Zurich Specialties
Zurich North America
Great Falls, VA

Victoria Peters
Senior Assistant Attorney General
Natural Resources and
Environment Section
Colorado Attorney General's Office
Denver, CO

Kate Probst
Senior Fellow
Resources for the Future
Washington, DC

Ed Putnam*
Assistant Director
Remedial  Response Element
NJ Department of Environmental
Protection
Trenton, NJ

Catherine Sharp
Assistant Division Director
Land Protection Division
OK Department of Environmental
Quality
Oklahoma City, OK
* All individuals  listed as Subcommittee members participated fully in the  deliberations  of the
Subcommittee. Their perspectives helped to shape the consensus recommendations and are reflected in
the range of views expressed throughout the Final Report.  However, the individuals indicated do not
support the document as a whole because of either their strongly held opposition to the ideas presented or
the way in which the ideas have been described. For elaboration on dissenting opinions, please refer to
the three-page individual statements in Attachment A.
Subcommittee Members
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Alexandra Shultz*
Director, Legislative and Regulatory
Affairs
Earthworks (formerly known as
Mineral Policy Center)
Washington, DC

Mel Skaggs
President
InDepth Environmental Associates
Southlake, TX

Richard Stewart
University Professor
Center on Environmental and
Land Use  Law
New York University School of Law
New York, NY

Wilma Subra
Technical  Advisor
Louisiana  Environmental Action Network
New Iberia, LA

Michael Tilchin
Vice President
CH2M HILL
Washington, DC

Jason White
Environmental Specialist
Office of Environmental Services
Cherokee Nation
Tahlequah, OK

Robin Wiener
President
Institute of Scrap Recycling Industries
Washington, DC
EPA Ex-officio Representatives:

Barry Breen
Principal Deputy Assistant Administrator
Office of Solid Waste and
Emergency Response
U.S. Environmental Protection Agency
Washington, DC

Phyllis Harris
Deputy Assistant Administrator
Office of Enforcement and
Compliance Assurance
U.S. Environmental Protection Agency
Washington, DC

Lawrence Starfield
Deputy Regional Administrator
EPA Region 6
U.S. Environmental Protection Agency
Dallas, TX
The subcommittee was facilitated
by the Meridian Institute and
Ross and Associates Environmental
Consulting, Ltd.:

John Ehrmann
Senior Partner
The Meridian Institute

Molly Mayo
Senior Mediator
The Meridian Institute

Elizabeth McManus
Senior Associate
Ross and Associates
Environmental Consulting, Ltd.
* All individuals  listed as Subcommittee members  participated fully  in the deliberations of the
Subcommittee. Their perspectives helped to shape the consensus recommendations and are reflected in
the range of views expressed throughout the  Final Report.  However, the individuals  indicated do not
support the document as a whole because of either their strongly held opposition to the ideas presented or
the way in which the ideas have been described. For elaboration on dissenting opinions, please refer to
the three-page individual statements in Attachment A.
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                                                              Subcommittee Members

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Subcommittee Members                NACEPT Superfund Subcommittee Final Report |  April 12, 2004

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Introduction from the  Chair
In the spring of 2002, the Superfund Subcommittee of the National Advisory Council for
Environmental Policy and Technology  (NACEPT) was  established  to assist the U.S.
Environmental Protection Agency (EPA) in identifying the  future direction  of the
Superfund Program.  Specifically, the EPA Administrator asked that the Subcommittee
"spur a national dialogue on the role of the National Priorities List (NPL), mega sites, and
program  performance measures" ... "in the  context of  other federal, state and Tribal
waste cleanup programs."

To accomplish this effort, the EPA Administrator appointed 32 senior-level  individuals to
the  Superfund Subcommittee.  The members reflected  a wide range  of  interests and
viewpoints  from   academia;  business  and  industry;  community  and environmental
advocacy groups;  federal, state,  local, and Tribal governments;  and environmental
justice, nongovernmental, and professional organizations. This breadth  was intended to
be reasonably representative of the concerns U.S. society has regarding  reducing risks to
human health and the environment at Superfund sites.

Throughout the Subcommittee's many meetings  and discussions, several major themes
provided  a basis for its deliberations:

    -* The overriding focus of the Superfund Program should be to improve the public
       health and environmental conditions at actual sites.
    -* There should be early, active and continuous involvement of all affected parties
       and communities in decisions related to Superfund sites.
    -* There should be efficiency in the use of appropriated  Superfund monies and
       there  should be  adequate funds to investigate and clean up sites of  concern.

The discussion and recommendations in this report relate to these major themes.

This report reflects 22  months of intense  discussion  and  deliberations with strong
opinions  and  different views provided  by individual Subcommittee  members.  These
discussions and deliberations occurred during nine multi-day public meetings, more than
20 work  group meetings that focused  on specific  issues, more than  100 work group
telephone conference calls and as part of a multitude  of individual telephone  calls to
review and discuss additional specific issues, wording, and recommendations.

Although  the report was drafted with EPA as  the primary audience, many others should
be  interested  in  the report's recommendations, comments  and views  for improving
Superfund,  such  as   Congress,  other government  entities,  Tribal Nations,   and
representatives from environmental and citizen groups, industry, and the  public.

While EPA provided the Subcommittee's charge, background information,  and ongoing
guidance, in each  case, the Subcommittee carefully  and  independently  reviewed and
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evaluated the material  provided.  In  certain  cases,  the Subcommittee sought  and
considered additional  information.  Thus,  the  Subcommittee  views this as  being  an
independent report.

The  Subcommittee  appreciates the detailed  factual  material provided by  EPA, the
Agency  for  Toxic  Substances  and  Disease  Registry,  the  National  Institute  of
Environmental Health  Sciences,  the  Subcommittee  members,  and the  individual
members  of the  public who  provided specific comments.  However, the report is the
product of the Subcommittee  members  only.  Individuals and organizations that provided
information to the Subcommittee,  including  EPA personnel, did  not participate in the
decisions made by the  Subcommittee regarding the final content of this report.

I believe  this  report presents  a fair and accurate  summary of the  comments, views and
recommendations the Subcommittee wishes  to forward to EPA. Where consensus was
not reached on specific statements and  recommendations, the report identifies the issues
and  presents the  various  points  of view of  the  Subcommittee  members.   The
recommendations, discussion and different points of view are provided to inform EPA as
the Agency considers how best to adequately protect human health and the environment
at actual and potential Superfund sites.

The Subcommittee  looks forward to EPA's serious  consideration and  implementation of
the advice provided in this report.  By doing so, the Agency will improve national efforts to
reduce the human and  environmental risks associated with Superfund sites.

In closing, I would like to thank the Subcommittee  members for the  dedication, intellectual
contributions, and extensive commitment of time and personal energy they contributed to
the deliberations  of the Subcommittee and to this report.  This type of work is not easy,
and the issues are complex.  The members fulfilled their charge extremely well and have
done so  professionally and positively.  It has  been a  pleasure working with  them, the
facilitators and the many individuals from EPA and other organizations who provided the
Subcommittee with the rich material needed to complete its task.
Raymond C. Loehr, Chair                                              March 2004
NACEPT Superfund Subcommittee
Introduction from the Chair            NACEPT Superfund Subcommittee Final Report |     12, 2004

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Final Report
Superfund  Subcommittee  of  the National  Advisory
Council for Environmental Policy and Technology
                 Executive
Summary
This report was prepared as a result of a request from the EPA Administrator to help
identify the future direction of the Superfund Program. This effort was conducted by the
Superfund Subcommittee of the EPA National Advisory Council for Environmental Policy
and Technology over a period of 22 months.  The Subcommittee first met in June 2002
and completed this Final Report in March 2004.

Members of the Subcommittee consisted of 32 senior-level individuals from academia,
business, and industry; community and environmental advocacy groups; federal, state,
local, and Tribal organizations;  and environmental justice,  nongovernmental, and
professional organizations. The Subcommittee was specifically asked to consider the
role of the Superfund Program's National Priorities List (NPL), how best to address mega
Superfund sites, and approaches that can be used to measure  the Program's
performance  and progress.   During  the Subcommittee's deliberations,  a number of
additional important issues arose.  These issues are identified and discussed in Chapter
VI of this report.

The Subcommittee  met nine times between June 2002 and March  2004. The original
term of the Subcommittee members was to be from May 2002 to December 2003. That
term was extended to March 31, 2004, by Acting EPA Administrator Marianne Horinko to
allow the Subcommittee adequate time to complete its discussions and deliberations and
this Final Report

EPA ex officio Subcommittee members participated in discussions  at meetings and in
conference calls to  clarify current procedures, provide background and updates on the
Superfund Program,  and, where appropriate,  provide  insights  into   the  practical
implications of implementing  recommendations being  considered by the Subcommittee.
EPA representatives did not participate in the Subcommittee's final decision making. The
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Agency also supported Subcommittee deliberations by making staff available to present
informational  briefings and  provide relevant information to the Subcommittee. The
Agency also provided the  Subcommittee with professional facilitators (a partnership of
Meridian Institute and  Ross and Associates Environmental Consulting) who assisted the
Subcommittee throughout  its deliberations by facilitating  meetings, developing  meeting
summaries and developing the draft documents and  reports that were reviewed by the
Subcommittee members at the public  meetings.  While the facilitators  prepared the
various reports, the  statements  in  this Final Report  represent  the  views  of the
Subcommittee itself.

In developing this  report,  Subcommittee members discussed  their  views on  many
complex and  interrelated  issues.   This Final Report is an integrated  package that
represents the Subcommittee's best effort to formulate consensus recommendations and
to present differing views on the complex issues considered by the Subcommittee. The
divergent  views were  included in the report in an effort  to  provide value  and be
responsive to  the  requests of the Agency.   In her remarks made at the Superfund
Subcommittee's  September  3,  2004,  meeting  in   Washington,  D.C.,  Assistant
Administrator Marianne Horinko indicated that, in the absence of consensus on difficult
issues, the Agency was interested in receiving clearly articulated details of the  strongly
held, divergent views on issues that the Subcommittee discussed  but could  not reconcile.

Between Subcommittee meetings, small  working  groups of Subcommittee members
spent countless hours  interacting via conference calls, through e-mail, and in face-to-face
meetings  to  continue  deliberations and  develop options  and  recommendations for
consideration by the full Subcommittee.  Thus, this report has resulted from continual,
serious, and often intense discussion of these  complex issues.

The report was developed through a cooperative drafting process and an open review
process. Many individuals contributed  text to the seven report drafts, and all members
were asked to comment on the drafts through a variety of mechanisms. Each version of
the report attempted to blend the range of individual comments submitted into a narrative
that reflected the perspective of the Subcommittee as a whole. This Final Report is not a
compilation of individual views. The Subcommittee worked to reach the greatest degree
of consensus  possible among the wide range  of views reflected  in  its  membership.
Consensus was defined as "an outcome that  everyone can live with," though aspects of
any particular finding  or  recommendation may not be  the first choice of individual
members. When consensus was not reached, this Final  Report describes the range of
views held by Subcommittee members.

As indicated, the deliberations throughout the 22 months of Subcommittee discussion
revealed a range of views  regarding some topics associated with the charge. Although
the members worked very hard to formulate  consensus recommendations on all  of the
issues addressed in this report, consensus recommendations on every topic could not be
reached.  In such situations, the differing views are presented as accurately as  possible
to fairly reflect the  deliberations and range  of  opinions. In addition,  if Subcommittee
members wanted to provide additional clarification or  elaboration, they had the option of
indicating  their support for or disagreement with  a  particular recommendation  or


Executive Summary-M                NACEPT Superfund                      |    12,

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discussion through a footnote or a three-page individual statement. The individual or joint
statements submitted by 21 of the Subcommittee members are included in Attachment A.

Except  as noted,  all  members  of the  Subcommittee  agree  with  the consensus
recommendations in this Final Report. Issues on which consensus could not be reached
are noted in this Executive Summary, but readers should consult the full report for a
summary  of the Subcommittee's  views on those issues.   On a  number  of issues,
Subcommittee  members held fundamentally different views.  The Subcommittee urges
readers to go beyond the  major recommendations, and read the comments, logic, and
differing views  provided to sharpen the focus and dialogue concerning the effectiveness
of the Superfund Program.

Because the issues addressed in this report are complex, have many important facets,
and affect different  parts of society in varying ways, they will be the focus of continuing
dialogue.  However, the goal of all parties interested in and affected by the  Superfund
Program is the  need to reduce the risks to human health and the environment associated
with Superfund  sites.  The Subcommittee trusts that  the information and advice in this
report will help the Agency and the nation achieve this  goal.

While this report was prepared with the assumption  that EPA is its primary audience,
many others should be interested  in the report, such as Congress,  other governmental
entities, environmental and community groups, Tribal Nations, industry, and the public.
The  Subcommittee looks forward  to  EPA's  and   other interested  parties' serious
consideration of the report's discussions, views, advice and recommendations.

In addition to chapters  providing background and introductory information, the report has
three chapters that  contain the Subcommittee's recommendations according to the three
main issues outlined in EPA's charge (use of the NPL, mega sites, and  performance
measures) and  a final chapter that  contains  recommendations on additional  important
issues discussed by the Subcommittee.  The recommendations in these chapters should
not be considered in isolation; they are a package. To  emphasize the interconnectedness
of the Subcommittee's recommendations, they are grouped in this Executive Summary in
terms of the following five major themes:
Increase the Transparency and Rigor of EPA Decision
Making
EPA has the responsibility to make difficult choices about site cleanup.  If a site is listed
on the NPL, choices about remedy selection and implementation are made in the context
of the open, public process associated with NPL cleanups.  Choices about how many and
what types of sites to  list on the NPL and  choices about which NPL sites receive
Superfund money to pay for site evaluation  and cleanup also need to be made in a
transparent fashion.
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Executive Summary-iii

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Awareness and understanding of these difficult decisions serve  EPA, officials at other
levels of government, Tribal  Nations, affected communities, and  potentially responsible
parties (PRPs). EPA must recommit to its existing coordinating practices and  reach out
effectively to affected communities and PRPs.

The Subcommittee makes six recommendations to increase the rigor and transparency of
EPA decision making:

    -* EPA should apply a set of consistent factors from year to year to choose which
       NPL-eligible sites to  propose  for listing in  each listing  cycle.  (Recommendation
       1.)
    -* EPA  should  work with  stakeholders to review the application  of the  hazard
       ranking system (MRS) model to ensure that it (1) accurately characterizes threats
       at sites  located  in  sparsely populated  areas   and  appropriately  considers
       environmental justice concerns, traditional lifestyles, and other issues; and (2)
       uses site-specific data that EPA determines are available and reliable rather than
       defaulting to presumptions in the MRS to estimate exposures. (Recommendation
       4.)
    -* EPA should improve the information and data on the Superfund Program and
       publish an annual report that presents  key data on the Program,  including
       Program progress and  expenditures, anticipated costs, a summary of sites
       considered  for  listing,  and the   listing  decisions   and   criteria   applied.
       (Recommendation 5.)
    -* EPA should establish standard protocols to ensure that regional offices publicly
       communicate available information  on site conditions  and current and potential
       future threats to humans and the environment: (A) when  a site is dropped from
       the Superfund site assessment process; and (B) when an NPL- candidate site is
       not proposed for NPL listing.  (Recommendation 6)
    -* EPA should develop  a system to track, evaluate and increase the effectiveness
       and  the performance of land-use controls  and long-term stewardship at NPL
       sites(Recommendation 16)
    -* EPA's strategy for Superfund  Alternatives Sites (SASs) should remain a small
       pilot program until significantly more input is received from a broad  range of
       perspectives, and an  independent body produces for public review and  comment
       a  report  describing  the  extent and  performance  of the  SAS  program  and  its
       compliance with the  Comprehensive Environmental Response,  Compensation
       and Liability Act. (Recommendation 17)

The Subcommittee also discussed, but did not reach consensus on, specific factors that
EPA might consider to determine which NPL-eligible sites to  propose  for listing on the
NPL, and the role that estimates of cleanup cost and Program funding should play in NPL
listing decisions.

In addition, the Subcommittee held strong and divergent views about the role that risk
should play in decisions about the types of sites that  are  eligible for the  NPL and
management and cleanup of listed sites.
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Spend Resources Wisely
Both public and private resources available for environmental cleanups are not unlimited.
A  consistent  theme during the Subcommittee's  deliberations was  the  need for the
Superfund  Program to  use its resources wisely.  In this context, the Subcommittee
discussed,  but did  not reach consensus  on, leveraging resources from non-Superfund
programs, setting priorities for funding among sites listed on the NPL, whether resources
should be  shifted  to removals and remedial actions  and away from other Agency
activities, auditing Superfund spending trends with a view towards identifying efficiencies,
contract  reforms,  financial  assurances,  and the  role of  prevention  relative  to  the
Superfund Program.

In  addition, the Subcommittee vigorously debated and has strongly held and divergent
views about  whether  the  Superfund  Program  should  receive  a temporary,  limited
supplemental  appropriation to address the backlog of remedial  actions that are ready for
construction.
Expand Efforts at Coordination and Collaboration
EPA must coordinate effectively with a wide range of partners for the Superfund Program
to be effective.  Decisions about how to best address a contaminated site are site-and
community-specific.  No two sites or communities present the same set of challenges or
imperatives.  Increased coordination  and collaboration  will  bring forward important
information about actual and potential releases, the potential use of other environmental
programs, and community-specific concerns and  priorities.  This information, and the
involvement of stakeholders, will help EPA make better, more informed and inclusive,
decisions about sites.

The   Subcommittee  makes  five  recommendations   related  to  coordination  and
collaboration.

    -* EPA regional offices should continue  and improve collaboration with states, local
       governments, and Tribal nations as they consider which  sites to recommend to
       EPA headquarters for NPL listing.  (Recommendation 2)
    -* EPA should reach  out  to potentially affected communities, local  governments,
       and potentially  responsible parties earlier in the Superfund  site assessment
       process to  share and solicit  information about sites being considered for NPL
       listing. (Recommendation 3)
    -* EPA should  (A) ensure that regional offices have knowledge and understanding
       of the capabilities  and applicability  of non-Superfund programs; (B) develop
       relationships with key managers in  other programs, particularly federal programs,
       to facilitate coordination; and (C) promote greater standardization of coordinating
       mechanisms, particularly for large, complex sites. (Recommendation 7.)
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Executive Summary-V

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    -*  EPA should continue to invest in capacity building for state and Tribal cleanup
       programs. (Recommendation 8)
    -*  EPA should improve its cooperative  relationship with the Agency for  Toxic
       Substances and Disease Registry (ATSDR). EPA, in coordination with ATSDR,
       should make a concerted effort to work with affected communities,  states, and
       Tribal nations to  regularly identify, on a  site-specific and  nationwide basis,
       projects and research efforts that would be most helpful in determining adverse
       health effects posed by  releases of hazardous  substances, thereby informing
       decisions related  to NPL  listings,  investigations, and remedy selection and
       implementation.    EPA  should  include  recommendations  both in proactive
       suggestions  for  projects,  and  in  reactive comments on  ATSDR proposed
       projects.   ATSDR's  responsiveness  to  these  recommendations  should  be
       included in EPA's (annual) reporting. (Recommendation 13)
    -*  EPA should establish  a transparent and  cooperative relationship with the
       National  Institute of Environmental  Health  Sciences (NIEHS)  to  provide
       recommendations and rationale for research, and to become educated on the
       efforts and findings of NIEHS.  In so doing, EPA Site Managers and  Community
       Involvement Coordinators should be educated as  to the resources available from
       NIEHS  (and ATSDR)  and should always inform the community of  these
       resources. (Recommendation 14)
    -*  EPA, working with ATSDR  and  NIEHS, should convene a national dialogue on
       the roles of ATSDR  and NIEHS in the Superfund Program. (Recommendation
       15)

The Subcommittee also discussed, but  did not reach consensus on the circumstances
under which  non-Superfund programs should  be  used at NPL-eligible sites, the
expansion of technical  assistance grants  to  certain  NPL-eligible  sites that are not
proposed for the NPL, and the  need for a national-level dialogue  to address effective
community involvement and issues unique to federal facilities.
Expensive Cleanups Deserve Special Attention
In  many ways, mega sites  present the same types of challenges posed by other NPL
sites, except that the high cost of mega site cleanups means that decisions about how to
best address them  have greater impacts on the Superfund budget.   Subcommittee
members  had  widely  divergent  views   about  whether mega  sites  warranted  a
fundamentally different cleanup approach than that currently provided by the Superfund
Program. These views are described briefly in Chapter IV of the report. However, even in
the context of these divergent views, the Subcommittee agreed that when mega sites are
addressed by the Superfund Program, they warrant special attention.  The Subcommittee
makes one recommendation related to the management of mega site  clean ups:  EPA
should establish practices that result  in mega sites' receiving the necessary resources
and attention from senior Agency managers. (Recommendation 9)
Executive Summary-vi
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The Subcommittee also discussed, but did not reach consensus on, whether EPA should
consider carrying out an expanded site inspection/remedial investigation at large complex
sites and how EPA should best make decisions about large geographic areas.
Measure and Communicate Progress and Performance
Comprehensively
It is an axiom that what is measured is done. This means that measurements of the
progress and performance of the Superfund Program should  illustrate the Program's core
purpose.   However, measures currently used  by the  Superfund  Program, such as
"construction complete" tell only part of the  story.  The  Subcommittee makes three
recommendations about improving measures of Program progress.

   -*  EPA should apply the following  National  Priority Measures  to its national-level
       reporting requirements:
           >   number of sites with all final remedies selected,
           >   number of construction completions at the site level,
           >   percentage of construction completions at the operable unit level, and
           >   number of sites deleted from the NPL (Recommendation 10).
   -*  EPA should continue with  its efforts  to  develop and  implement a  system to
       ensure clear, transparent dissemination of a core set of data for all NPL sites and
       Superfund Program activities. (Recommendation 11)
   -*  EPA should develop  measures of performance that assess the effectiveness of
       Agency coordination  with Tribal, state and local governments and community
       stakeholders. (Recommendation 12)

Finally,  Attachment  A  contains  the  three-page  comment  papers  submitted by
Subcommittee members to elaborate on their individual perspectives and the Appendices
contain supporting documents and elaboration on the topics addressed in the body of the
report.
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             Introduction
   n July 2001, the Deputy Administrator of the U.S. Environmental Protection Agency
   (EPA) directed the development of an action plan to address the recommendation in
   the Resources  for the Future report to Congress Superfund's Future: What Will It
Cosf?1 regarding the future of the  Superfund Program's National Priorities List (NPL).
The action plan called for the creation of a Superfund Subcommittee under the auspices
of the National Advisory Council for Environmental Policy  and  Technology, an  EPA
advisory committee under the Federal Advisory Committee Act.  This Subcommittee was
established in June 2002 to spur a national dialogue on the role of the NPL, Superfund
mega sites, and Program performance measures in the context of other federal, state,
and Tribal programs.

Members of the Subcommittee were senior-level individuals from academia; business
and industry; community and environmental advocacy groups; federal, state, local, and
Tribal  governments;  and  environmental justice, nongovernmental,  and professional
organizations.
EPA's Charge to the Subcommittee
EPA's charge to the Subcommittee asked specifically for advice in three areas:

   -*  Determining the Role of the National Priorities List—What should be the role
       of the NPL?  For example, how should it be used in the context of other cleanup
       programs, who should be consulted with regard to determining the sites that are
       listed, and what types of sites should be listed?
   -*  Addressing  Mega Sites—How can EPA best address mega sites (defined as
       sites  where  total cleanup costs  are expected to exceed  $50  million)?  For
       example, should cost continue to be the determining factor when identifying
       mega sites,  are there viable alternatives for placing mega sites on the  NPL
       and/or containing their costs, are there feasible and reasonable policy options for
       addressing these sites, and do  mega sites  have unique  aspects that might
       require a different decision-making process for NPL listing?
   -*  Measuring  Performance  and Progress—EPA did  not ask specific questions
       regarding measuring the Superfund  Program's progress or performance, but
       noted that the Agency expected to share new ideas it was formulating regarding
       measures and would seek the Subcommittee's feedback on those ideas.

After reviewing the EPA charge, the Subcommittee discussed and elaborated on these
three  major topics  to incorporate additional issues of concern to members of the
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Subcommittee.   The  original  charge and  the modified  charge  accepted  by  the
Subcommittee are included in Appendix I and II.
The Deliberative Process
The Subcommittee met nine times between June 2002 and March 2004.  The original
term of the Subcommittee members was to be from May 2002 to December 2003. That
term was extended to March 31, 2004, by Acting EPA Administrator Marianne Horinko to
allow the Subcommittee adequate time to complete its discussions and deliberations and
this  Final Report.   Between Subcommittee  meetings,  small  working  groups  of
Subcommittee members spent countless hours interacting via conference calls, through
email and in face-to-face  meetings to continue deliberations and develop options and
recommendations  for consideration by  the full Subcommittee.  Thus, this report has
resulted from continual, serious, and often intense discussion of these complex issues.
   Public and Ex Officio Participation

EPA ex officio Subcommittee members participated in discussions at meetings and in
conference calls to clarify current procedures, provide background on and status of the
Superfund  Program,   and,  where  appropriate,  provide  insights  into  the  practical
implications of implementing recommendations being considered by the Subcommittee.
The Agency also  supported Subcommittee deliberations by making staff available to
provide informational briefings  and other materials to the Subcommittee.  The Agency
also  provided  professional  facilitators  who  assisted the  Subcommittee throughout  its
deliberations  by facilitating  meetings  and  developing  meeting summaries and draft
reports.   EPA representatives  did not participate in the Subcommittee's  final decision
making.

In accordance with the requirements of the Federal Advisory Committee Act, notices of
full Subcommittee  meetings  were published in the Federal Register, and  the  meetings
were open to the  public.  Opportunities  for public comment  were  provided at each
meeting,  and the  public comments  are included in the meeting transcripts.  Meeting
agendas, transcripts, and other materials are available through the Superfund Docket at
www.epa.gov/edocket  or by phone  at 202-566-0276 and reference docket #SFUND-
2002-0005.
The Consensus Process
In  developing  this report,  Subcommittee  members discussed  their views on  many
complex  and interrelated issues.   This  final  report is  an integrated package that
represents the Subcommittee's best effort to formulate consensus  recommendations.
The report was developed through a cooperative drafting process and an  open review
Chapter l-Page 2
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process.  Many individuals contributed text to the seven drafts of the report. All members
were asked to comment on the drafts through a variety of mechanisms.

Each  revision  of the report  attempted  to  blend  the  range of individual comments
submitted together into a narrative that reflected the perspective of the Subcommittee as
a whole.  The report is not a compilation of individual views. The Subcommittee worked
to reach  the greatest degree of consensus possible among the wide  range  of views
reflected  in its  membership.  Consensus was defined as "an outcome that everyone can
live with," though aspects of any particular finding or recommendation may not be the first
choice of individual members. When consensus was not reached, the report describes
the range of views held by Subcommittee members.

During the Subcommittee's deliberations, a number of additional important issues arose
that the Subcommittee believes are important to the success of the Superfund  Program
and, therefore, that EPA should seriously consider.  They are discussed in Chapter VI.

The deliberations also revealed a range of views regarding some topics associated with
the charge.   Although the  members  worked  very  hard to  formulate  consensus
recommendations  on  all  of  the  issues  addressed   in  the  report,   consensus
recommendations on every topic could not be reached.   In such situations,  the differing
views are presented as accurately as possible to fairly reflect the deliberations and range
of opinions.  However, in trying to succinctly characterize the differences of opinion, the
Subcommittee  may have sacrificed  some degree of detail regarding individual positions
or nuance. In  some cases,  the Subcommittee was unable to resolve differences  of
opinion about how to present a recommendation or range of views and, therefore,  could
not reach consensus on final text.  In those cases, members were given the option  of
using  a footnote  to indicate the specific portion(s)  of the report they could not live with.
Additionally, in any situation where members wanted to provide additional clarification  or
elaboration on their opinions, they  had the option of submitting personal comments  or
views in the form of three-page individual statements, which are included in Attachment
A.
Organization of the Report
The body of the report begins with the Introduction, which provides a summary of the key
characteristics of the  process  and the report.   The  background chapter that follows
discusses  the critical background  material that helped to provide a foundation for the
Subcommittee's deliberations. The background material provides a brief overview of the
NPL listing and cleanup processes, the composition of the  NPL, and key budget data.
The following three chapters address the three  issues in the charge: use of  the NPL
(Chapter  III),  mega sites  (Chapter IV), and  measures  of  program  progress  and
performance  (Chapter V). Chapter VI discusses additional  priority issues that warrant
serious  consideration  and  follow-up.   Finally,  the  appendices  contain  supporting
documents and  elaboration on the topics addressed  in the body  of the report.
Additionally, Attachment A contains the three-page individual statements submitted by
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Subcommittee members to elaborate on their personal perspectives or issues that they
believe are not adequately addressed in the body of the report.
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1 Probst, Katherine N., et al. Superfund's Future: What Will It Cost? Washington, DC: Resources for
the Future, 2001.
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              Background
and  Context  for
NPL/Mega Sites
     This chapter provides an introduction to the Superfund Program, including the site
     investigation and cleanup process, the status and composition of the current
     National Priorities List (NPL), and the Program budget. It is not intended to be a
comprehensive or detailed description of the Superfund Program or law.  Rather, it is
intended to provide context for the  Subcommittee's recommendations and to assist
readers who may be less familiar with the Superfund Program and its history. Wherever
possible, this chapter relies on independent sources of information and data, such as
reports from  the General Accounting Office  (GAO) and  the  Office of the Inspector
General (OIG).  This chapter also relies heavily on information  provided by EPA, which
was not independently verified for accuracy. During the course of the Subcommittee's
deliberations, a number of unresolved differences were noted among data presented to
the Subcommittee, including differences between EPA data and data represented in
GAO and OIG reports.  This chapter cites the source of information for all charts and
tables.
Origin and Growth of the Superfund Program
In 1980 Congress passed the Comprehensive Environmental Response, Compensation,
and Liability Act (CERCLA), more commonly known as Superfund, to provide for cleanup
of releases of hazardous substances.  The Superfund Program implements two basic
types of cleanups: (1) remedial actions, which generally are long-term cleanup actions at
sites listed on the NPL; and (2) removal actions,  which generally are shorter-term
cleanups needed to  mitigate more immediate  threats at listed and unlisted sites.1
Remedial actions generally  are designed to provide a permanent remedy and thus can
take a considerable  amount of time  and money,  depending  on the nature of the
contamination being addressed.  Cleanups at  NPL sites progress through several steps
which include investigation and study, remedy selection and design,  and remedy
implementation. Because  the Subcommittee's deliberations  focused on  the remedial
action program, the remainder of this chapter focuses on facts related to  that program
and not to the removal program.
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Under CERCLA, EPA has the authority to clean up hazardous substance releases itself
(typically by hiring environmental contractors to do the work in the field) or to compel
responsible parties to perform clean up.  CERCLA initially established a $1.6 billion Trust
Fund, financed primarily by taxes on  crude  oil  and  certain chemicals,  for EPA to
implement the Program and  pay for clean ups. The implementing regulations provide
that a site must be listed on the NPL to receive financing for remedial actions.2

In  1986,  Congress  amended  CERCLA  with  the  Superfund  Amendments  and
Reauthorization Act (SARA).  The SARA amendments, among other things, emphasized
the importance of human  health considerations,  community  involvement,  cooperation
with  state  and local governments, and permanent  cleanup remedies,  and provided
guidance on cleanup standards.  SARA also increased the ceiling amount  of the Trust
Fund to $8.5 billion  and added a third taxing mechanism, the corporate  environmental
income tax.

The Superfund Program has over 3,000 full-time-equivalent (FTE) staff, largely located in
the ten  EPA regional  offices.    Regional staff  coordinate  site assessments  and
investigations; make decisions about what sites need removal or  remedial action; carry
out site-related oversight, enforcement, community involvement, and other activities;  and
oversee the work of EPA contractors  hired to carry out site  investigation and response
activities financed by the Superfund Program. Regional staff also largely are responsible
for coordination with officials in state and local governments and Tribal Nations, who are
critical partners in the Program's successful implementation.

Staff at  EPA  headquarters  are responsible  for the  Superfund Program's  overall
coordination, management and development, and policy direction.   NPL listing decisions
are also made at EPA headquarters, by the Assistant Administrator for the Office of Solid
Waste and Emergency Response (OSWER).

In fiscal year (FY) 2002, there were approximately 2,500 FTEs in the regional offices and
644 FTEs at EPA headquarters.  In addition to funding staff in OSWER, the Superfund
Program budget funds staff and other activities  in offices that support enforcement (e.g.,
the Office of Enforcement and Compliance Assurance (OECA) and  Department of Justice
(DOJ));  management (e.g., the  Office of Administration  and Resources Management
(OARM), Office of the Administrator (OA), Office of the Inspector General (OIG), Office of
the Chief Financial Office (OCFO),  Office of Environmental Information (OEI), Office of
Program Planning and Evaluation (OPPE)); and technology (e.g., the Office of Research
and Development (ORD)).  In FY 2003, these offices outside of OSWER received $404.3
million of the $1.265 billion total Superfund operating budget,3 nearly one-third of the total
budget.

At the end  of 1995, the  taxing authority that was  used to finance the Superfund Trust
Fund expired.  The Fund continues to receive revenue from other sources, including cost
recoveries,  interest from investments, fines, and penalties. Since 1995, the Program has
been increasingly funded through appropriations from general  revenues (see page  14 for
further discussion on appropriations).
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Citizen
Complaints/
Petitions

PRP
Volunteers
 Figure 11-1:  How Sites Get Listed
           on the NPL
                                       How Sites Get Listed on the
                                       NPL
The  Superfund  process  begins when  a
potentially hazardous  site  is  reported to
EPA,  usually  by  a  state  environmental
agency, but  sometimes  by local or Tribal
governments,  individuals,  and  community
groups.   The EPA regional office, often in
conjunction  with  a   state  environmental
agency,   carries   out  a   pre-screening
evaluation   to  verify   that   hazardous
substances are present at the site and to
evaluate  whether the site  is  covered  by
EPA's    Resource    Conservation    and
Recovery  Act  (RCRA)  program or  state
programs. When EPA determines that the
Superfund  site  assessment  process  is
warranted, the Agency enters  information
about the sites  into  the Comprehensive
Environment Response, Compensation, and
Liability   Act   Information  System   (or
CERCLIS), which is the Agency's database
of sites   that   may   need  action  under
Superfund,  and  the   Superfund   site
assessment  process begins.  In FY 2003,
EPA  added   more  than  240  sites  to
CERCLIS.4

The Superfund site assessment process is
carried out largely by EPA regional offices,
working  with state  environmental agencies
and Tribal Nations.   This  process  has a
number of steps, each  designed to  send
forward only the sites that warrant additional
attention  under Superfund.  Sites may not
undergo further assessment for a number of
reasons,  including a determination that no
further remedial  action under  CERCLA is
planned (NRFAP);  a determination that an
assessment  using  the   Hazard  Ranking
System (MRS)  most likely would not result in
an MRS score of 28.5, the threshold for NPL
eligibility; or  referral of the  site to another
environmental  cleanup program.  Sites that
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   Superfund Alternative Sites
Some sites that are eligible for the NPL
may not be listed and instead may be
designated as a Superfund Alternative
site (SAS).  EPA's goal for the SAS
program is a process that results in
cleanups by responsible parties
equivalent to NPL sites, without actually
listing the site on the NPL.  Sites must
meet the National Contingency Plan
criteria for listing (i.e., HRS of 28.5 or
higher), require long-term response
(i.e., remedial action), and have fully
viable, cooperative responsible parties.
State and Tribal Nation involvement is
similar to NPL sites, including
consultation on the SAS designation,
notice of enforcement actions, and
remedy select!on.a

As of the end of FY 2003, there were  109
SASs, accounting for a total expenditure
from the Superfund Program of
approximately $227 million between FY
1983 and FY 2003. For FY 2003,
expenditures on SASs totaled $13.4
million. These funds are primarily spent
on removal actions (42%) and other costs
associated with the early stages of the
Superfund process, including site
investigation, feasibility studies, and
community involvement—all activities
that may have been started while  the SAS
enforcement agreement is negotiated.13

a  See OSWER 92-08.0-17, Response Selection and
Enforcement Approach for Superfund Alternative
Sites.
  Information provided by EPA to the
Subcommittee on December 5, 2003.
          are  not  screened  out  during  the
          Superfund site assessment process and
          that have  an  HRS score  of  28.5 or
          greater  are  considered  NPL-eligible
          sites.

          From among the identified NPL-eligible
          sites, EPA regional offices choose which
          sites to submit to EPA headquarters for
          possible addition to the NPL.   Regions
          make these decisions by considering, in
          a qualitative sense, a variety of factors,
          including    the    severity    of    the
          contamination,   the   urgency  of  the
          problem, and the types of environment
          affected. EPA guidance5  specifies  that
          high priority should  be  given  to  the
          following types of sites:

              -*  Current   human  exposure  to
                  hazardous         substances,
                  pollutants or contaminants;
              -*  Documented     contamination,
                  especially at or above a health-
                  based    benchmark    (SARA
                  Section  118 requires that a site
                  be  considered  a  high  priority
                  where releases  have resulted in
                  closing  drinking-water wells or
                  have contaminated a  principal
                  drinking-water supply);
              -*  Proximity to a large potentially
                  affected human  population;
              -*  Documented contamination  of a
                  sensitive environment or fishery;
              -*  State recommendation  that the
                  site be listed on the NPL; or,
              -*  The    Agency    for    Toxic
                  Substances    and    Disease
                  Registry  has  or is  planning to
                  issue a  health advisory related
                  to  the  site  or  to  activities
                  associated with the site.
EPA headquarters works with the regional offices during this process by evaluating HRS
scoring for the site to ensure that only sites with technically and legally defensible scores
of 28.5 or higher are sent forward, and by ensuring that Superfund Program guidance is
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properly applied. NPL-eligible sites that the regional offices identify as priorities are sent
forward to headquarters for proposed addition to the NPL.  Sites that the regions send
forward are referred to as NPL candidates and represent a subset of NPL-eligible sites.

Beginning in  2002, EPA established  a  new  step  in the Superfund site assessment
process,  whereby the entire pool of NPL candidate sites submitted to headquarters by
the regions undergoes an additional evaluation by a committee made up of regional and
headquarters personnel. According to  EPA officials, this group primarily considers risks
to human health and the environment and the urgency of the need for response to further
prioritize  NPL candidate sites.  It also considers program management factors, such as
projected costs to the Superfund Program and timing of funding needs;  maintaining a
strong  enforcement program; leveraging cleanups  by  others; land  use potential; and
state, Tribal and community support for listing.  This additional step  in 2002 represents
the first time cost was considered as a factor for listing sites on the NPL.

Those  discussions are then considered by headquarters  staff, who develop options for
recommending NPL candidate sites to the Assistant Administrator for the OSWER.  The
Assistant Administrator makes the final decision about which  sites to propose for NPL
listing.  Listing proposals are then published in the  Federal Register tor public review and
comment.  EPA considers all  comments received  during a 60-day comment period and
then makes a  final  listing decision that is  also published  in the Federal Register.
Historically, EPA has finalized the majority of listings that it proposes.
What Happens Once a Site Is on the NPL
Once a site is listed on the NPL, the remedial-or clean up-process starts.  The first step
in the remedial  process  is a remedial investigation and feasibility study (RI/FS), during
which a site is investigated to characterize the  nature and extent of contamination and
contaminant sources, to  calculate the risks posed by such contamination, and to identify
and  evaluate remedial options.  The  culmination of the RI/FS is EPA's issuance of a
Proposed Plan for remediation. After public review and comment on the Proposed Plan,
a Record  of Decision (ROD) is issued.  The  selected  remedy  is  then designed (the
remedial design (RD) phase) and implemented (the remedial action (RA) phase).

Sites are often divided by geography, pathways  of the contamination (e.g., groundwater),
or type  of remedy into  smaller units,  known  as operable units.  Sites with  multiple
operable units often move through the process described above in different time frames,
resulting in multiple actions of the same type, rather than in the linear method described.

When physical construction of the remedy is complete, a site generally is identified  as
"construction complete."  After the remedial action phase, a site enters the operation and
maintenance (O&M)  phase of cleanup, during which  remedy implementation and
monitoring  continues.   For federally  financed  remedial  actions,  once the  action  is
completed, the responsibility and cost for O&M transfer to the state. Once remedial goals
have been achieved, EPA may delete a site from the NPL, even though O&M continues.
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If a remedy involves groundwater or surface water restoration, achievement of remedial
goals may take several decades.  When such a remedy is federally financed,  the  site
moves into a long-term response action (LIRA) phase after the remedial action phase.
LIRA is eligible for federal funding for a period of up to ten years, after which time the
responsibility and continued implementation costs  of the remedy transfer to the state.6
Figure 11-2 represents the pipeline  status of the most advanced operable unit of each of
the 1,518 sites on the  NPL at the end  of FY  2003, including the 274 sites considered
deleted. Sites that are proposed for the NPL are not represented in this chart.
         Study Pending
        Studyor Design
    Construction Underway
   Construction Complete
             Referred
                     18
                                 247
                                        363
                                                                   I 886
                   0     100    200   300    400   500    600   700    800   900   1000
      Figure 11-2:  Pipeline Status of 1,518 Final and Deleted Sites on the NPL
Throughout the Superfund process, cleanup costs are paid for either by the Superfund
Program or by potentially responsible parties (PRPs). Orphan sites are sites where EPA
is  unable to identify a financially viable responsible party.   At these sites, all cleanup
costs are initially borne by the Superfund Program, although in some cases costs may be
recovered later from responsible  parties.   More  typically,  cleanup  costs are shared
between PRPs and the Superfund Program.  Even at  sites where cleanup costs are
funded entirely by the PRPs, the Program generally incurs costs to oversee PRP work,
which it then seeks to recover from responsible parties, if  possible.A
Current Composition of the NPL
After 23 years of Superfund implementation, EPA and its partners in state environmental
agencies and Tribal governments have identified over 45,000 sites for assessment under
A Subcommittee member Jane Gardner notes that approximately 70% of Superfund
Program cleanups are PRP-funded.
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Superfund. The vast majority (nearly 75%) have been determined not to require remedial
action under the Program.

At the end of FY 2003, 1,572 sites were on the NPL.7  This total includes sites proposed
for the NPL and sites deleted from the NPL that may have ongoing O&M activities related
to remedial actions.  The status of these sites is as follows:

    -* 54 sites (~3.5%)  are proposed for listing, but listing is not yet finalized;
    -* 1,244 sites (~ 79%) are listed; and
    -* 274 sites (-17.5%) have been deleted.8

Over half of the sites listed as final on the NPL  (716 of 1,244) were listed prior to 1986,
and thus are considered pre-SARA (or teenager) sites.9   For the last  decade of the
Program, additions to the NPL have outpaced deletions and the NPL has continued to
grow,  with an average of 28 new sites added each year.  Deletions have averaged 21
sites a year over the same time period.
    Mega Sites

Sites on the NPL are categorized in several ways. One categorization distinguishes sites
based on the expected costs of remediation. Large, complex, and costly sites have come
to be referred to  as "mega sites"  —defined as  sites where total cleanup costs (i.e.,
combined  extramural, actual,  and  planned  removal and  remedial action costs) are
expected to equal  or exceed  $50 million incurred by either the Superfund Program or
PRPs.10

Of the  1,518 final and deleted sites on the NPL at the end of FY  2003, EPA estimates
that 142 nonfederal facilities are or are likely to become mega sites.11   Ninety-three, or
65%12 of these mega sites are  pre-SARA sites.

While mega sites make up a relatively small  percentage of the NPL (<10%), they have
important impacts on the Superfund budget.   Sixty mega sites are Fund-lead  or have
orphan shares that will require funds directly from the Superfund Program. The remaining
sites are PRP-lead  or "undetermined lead."13 In a recent report to Congress, the Office of
the Inspector General  (OIG)  noted that  in  FY 2003, funding needs  for eight  large,
complex sites (out  of a total of 94 sites receiving funding) accounted for approximately
50% of the  money available that year for Fund-led remedial actions.14  EPA allocated
$224.4 million of FY 2003 appropriations for remedial action work.15 Eight sites received
a total of nearly $109 million;16 seven of these  sites are classified as mega sites.

As shown in Figure II-3, mega sites  are distributed across the country, with some in every
region.
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    Federal Facilities
                                               Region 10
                                                  6%
                         Region 1
                           7%
                                     RegionQ
                                       17%
                                   Region 2
                                     17%
                                   Regions
                                     11%
                                                                        Regions
Another    way    that   EPA
categorizes sites on the NPL is
as   federal    or    nonfederal
facilities.  Federal facilities  are
sites owned  and  operated  by
federal  agencies,  such as  the
Departments     of    Defense,
Energy, and the Interior.  While
federal facilities on the NPL fall
under the regulatory structure of
the Superfund law, cleanups at
federal facilities are not usually
funded    by   the   Superfund
Program,    but    by    other
mechanisms,  such  as  direct
appropriations  to   responsible
agencies.     Of   the  1,572
proposed, final, or deleted NPL
sites,  177  (6  proposed;  158
final; 13 deleted)17 are federal
facilities.18 They include, among  other things, abandoned  mines;  nuclear, biological,
chemical, and traditional weapons productions plants; military base industrial sites, such
as aircraft and naval  ship maintenance facilities; and  federal landfills.   The primary
federal agencies responsible for the 177 federal facility NPL sites are the Department of
Defense (80% of NPL federal facility sites) and the  Department of Energy (12%).19
                                      Region 7
                                        4%
                                   Region 4
                                     7%
                                            Regions
                                              11%
                           Regions
                            12%
                                            Figure II-3:  Distribution of 142
                                                 Mega Sites by Region
    Categorization by Type of Activity
Sites  on the  NPL  are  also  categorized  by types of industrial  facilities or activities
associated  with  the contamination, such  as manufacturing, waste management,  and
recycling.   A number of catch-all categories are also used, such as "multiple," which
refers to sites where more than one activity caused the site to be listed, and  "other,"
which includes groundwater and contaminated sediment sites with no identifiable  source,
military/ordnance production,  dry cleaners, transportation, retail, and  storage sites.  As
shown in Figure II-4, of  all 1,572 sites on the NPL, including proposed sites, more than
two-thirds fall into the manufacturing and waste management categories.20
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                                    M ining
                                     2%
                       Other
                       16%
                                                         Manufacturing
                                                             36%
              Figure II-4: All NPL Activity Type (Proposed, Final, Deleted)

Figure II-5 shows the distribution of mega sites across site type classifications, including
subtypes within the  manufacturing category.  It  also includes two other types of sites:
groundwater  plume sites with no identifiable source and  contaminated sediment sites
with no identifiable source (captured under "Other" in Figure II-4).  The type of industrial
facility or prior site activity does not significantly differ for mega sites when compared to
site types for  all NPL sites.  In any given category, mega sites represent a relatively small
percentage of the total sites on the NPL. Similar to the NPL as a whole, the categories of
waste management and manufacturing represent the largest percentage of mega sites,
with the subtypes for manufacturing comprising 35%.21
                  Ground water plume site
                    with no identifiable
                       M ining
                                    M ultiple
Chemicals and allied
    products
      15%
           Contaminated sediment
            site with no identifiable
                 source
                  3%
                    Waste Managem
                          26%
         Lumber and wood
          products/wood
        preserving/treatment
              6%

          Electronic/electrical
             equipment
               5%

         Primary metals/mineral
             processing
                4%
           Radioactive products
         ^      4%
 Recycling \—
Fabrics/textiles
    1%
                                               Other
                                                6%
   Figure II-5: Activity Type (and Manufacturing Subtype) for 142 NPL Mega Sites
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   Mining and Sediments
In its charge to the  Subcommittee, EPA noted that mining and sediment sites warrant
particular consideration.  Because mining sites pose special challenges to the Superfund
Program, EPA has established the Abandoned Mine Lands Team (AMLT) to provide a
consistent framework for addressing both active and abandoned hard-rock mining sites.
While the  AMLT is a  work  in  progress,  its  preliminary  strategy aims  to  reduce
environmental  liabilities through both  regulatory  and nonregulatory  activities at active
mines sites and to consider various remediation options at abandoned mine sites on and
outside of the NPL.

The AMLT is in the process of finalizing and distributing for internal review a web site and
reference notebook specific to contamination problems on abandoned mine lands. Both
are intended to help clarify the  policy and technical issues related to  abandoned mines.
The Subcommittee did not review either the web site or the reference notebook.

Many Superfund  cleanups  address contaminated  sediments as one component of
cleanup.  To ensure scientifically sound and nationally  consistent decisions related to
contaminated sediments sites being considered for CERCLA actions, in 2002 EPA issued
eleven principles for managing  risks from contaminated sediments 22and draft technical
and policy guidance23 related to the eleven principles. The guidance  established a  new
headquarters consultation process for all CERCLA and federal-led RCRA sites where a
significant sediment cleanup  is expected. In general, these risk management principles
are designed to support site-specific,  risk-based remedial action decisions using an
iterative  process  that  encourages  early  and  meaningful  involvement  of  affected
stakeholders. The Subcommittee did not review the management principles.

The consultation process is a  two-tiered procedure, where Tier 1 sites are those for which
the sediment action will address more than 10,000 cubic yards or more than five acres of
contaminated sediment,  and  Tier 2  sites are very large, controversial,  or complex
sediment sites. Tier 2 sites are overseen by the Contaminated Sediments Technical
Advisory Group (CSTAG), which is composed of staff from each of the ten EPA  regions
plus  five  headquarters staff.    CSTAG assists site  managers in  selecting appropriate
remedies  and   managing the  cleanup  process  in  accordance  with  the  eleven  risk
management principles.

Currently,  EPA  has identified seven NPL sites that warrant CSTAG review.24 Of these
seven sites, three are mega sites, and one has been proposed to  the NPL but does not
yet have a final listing.
Cost of Cleanup
Accurate estimates for cleanup costs are very difficult to obtain and predict for several
reasons. One is that EPA only tracks costs once a remedy selection has been made, so
as not to prejudice the remedy selection process.  While EPA tracks costs it incurs for
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pre-remedy selection work and removal actions, when estimating future cleanup costs,
EPA relies on planned obligation data only for those remedies that have been selected.
Another reason  it is difficult to obtain costs is that EPA only has cleanup cost information
for sites or portions of sites where cleanup is paid for using Superfund Program funds.
PRPs are  not obligated to disclose the amount they spend on cleanup.8

In the  FY 2000 appropriations conference report, Congress asked Resources for the
Future (RFF)  to conduct  an independent  study  to estimate the  cost  to  EPA  of
implementing the Superfund Program through FY 2009. Completed in 2001, Superfund's
Future: What Will it Cost included estimates of future costs in six separate categories, as
well as information  on past Superfund Program expenditures. The authors included three
estimates  of future  costs:  a base case, and a  high and low case. The report's base case
estimated  annual EPA expenditures to range from a low  of $1.3 billion in FY 2009 to a
high  of $1.7 billion  in FY  2003.  The estimates suggest that needed EPA expenditures,
under current law  and  policies, would be above $1.4 billion  in nine of the ten years
covered in the report.25  Under the high case scenario, estimates of EPA's funding needs
equal or surpass $1.6 billion for seven of the ten years.
26
Using available data from  several years and making  certain  assumptions about the
number of operable units,27 the RFF analysis concluded that the  average cost per site for
cleanup was $12 million for non-mega sites and $140 million  for  mega sites. A relatively
small number of sites,  even if not mega sites, that require  large infusions of remedial
action dollars in any given year can skew these average costs and can significantly strain
the Superfund cleanup budget.

Because mega sites in particular can impact the  overall Superfund Program remedial
action budget,  and because some mega sites are expected to cost into the hundreds of
millions  of dollars, the Subcommittee  paid special attention to cleanup costs associated
with  mega sites on the NPL, especially the 60 sites at which cleanup activities are entirely
or partly funded by the Superfund  Program. Of particular interest to the Subcommittee
was  whether the type of industrial facility or prior site activity  affected site cleanup costs.
EPA provided data on actual and planned remedy construction obligations in increments
of $50 million  for these 60 sites,28 along with site type activity, which is displayed  in
Figure II-6.

At roughly half (31)  of  the sites, EPA's  actual  and  planned remedy  construction
obligations fall  under the $50 million threshold for mega sites. (These are most likely all
mixed-funding  sites,  where both EPA and PRPs are  paying cleanup costs.)   The
remaining 29 sites have costs estimated at  between $50 million and $350 million.  The
most expensive site displayed has been on the NPL since 1983 and has received to date
$165 million of Trust Fund money and EPA  plans to obligate another $150 million in the
B Subcommittee member Jane Gardner notes that a group of several companies that
comprise the Superfund Settlement Project collectively estimate their expenditures
for hazardous site cleanup over the last twenty years at more than $6 billion, as noted
in a January 22, 2004 hand delivered letter to Ms. Elizabeth Craig, Deputy Assistant
Administrator for EPA's Office of Air & Radiation.
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future. This does not include the dollars provided by PRPs or work conducted by PRPs
at this site, which also have been substantial. Some of the $315 million actual or planned
obligations for  this site  ultimately may  be  cost-recovered.   EPA  does  not have
construction obligation data for the remaining 82 mega sites on the NPL because these
sites  are  PRP-led  cleanups  and  responsible  parties  do  not report  cleanup cost
information to EPA, or because not all anticipated construction projects have yet begun at
a site.
The distribution by type of activity shows manufacturing as the primary site type for sites
where actual and planned costs are expected to exceed $100 million (11 of 15 sites are
manufacturing subtypes).
29
                           ££

                               <=150          <=200
                               Site Obligation Categories in Multipl
                                 <=250
                            es of $50 Million
Ranned/Actual Obligations include only resources (including appropriated funds and resources recovered from private parties) that EPA is, or w ill use, to construct remedies,
                        but does not include costs incurred by private parties to conduct response w ork.


       Figure II-6: Actual/Planned Construction Obligations for 60 Fund- and
                     Mixed-Lead Non-Federal NPL Mega Sites
Superfund Budget
   Appropriations
Money  appropriated to the  Superfund Program  from 1993  to  2004  has diminished.
According to the July 2003 GAO report to Congress (and as updated  on February 18,
2004) on the financial  status of the Superfund Program,  the  Program's total  annual
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appropriations (in nominal  dollars) has  decreased from a  high of approximately $1.6
billion in  FY 1993 to $1.25 billion in recent years.30  If adjusted for inflation using 2003
dollars, this would represent a decrease from $1.9 billion to approximately $1.25 billion.
This decrease  primarily  represents a  $100  million  reduction to the EPA  Superfund
appropriation beginning in FY 2000, a government-wide rescission  of 0.22 percent in FY
2001  and an additional  0.65 percent government-wide rescission  in  FY 2003, and
Congressional decisions  to separately  appropriate resources to other agencies and
programs that were formerly included in the Superfund Program  budget, including the
Agency for Toxic Substances and Disease Registry (ATSDR), the National Institute of
Environmental Health Sciences (NIEHS), and the Brownfields program.  Since FY 2001,
Congress has separately  appropriated resources to ATSDR and NIEHS; beginning in FY
2003, Brownfields has been a separate appropriation.31

The total annual appropriation  (including  congressional earmarks)  to  the  Superfund
Program from 1993 to 2004 is shown in Figure II-7,  along with the relative percentage of
the source of the appropriation, which is either Trust Fund32 or general  revenues. 33
Originally, the Superfund  Trust Fund was funded through excise taxes on crude oil and
some petroleum products, the sale of certain chemicals regularly found at toxic waste
sties, and after passage  of the SARA  amendments in 1986, an environmental fee on
profits in  excess of $2 million for some large corporations. While Congress allowed these
taxes to  lapse at the end of 1995, the amount of money appropriated to the  Superfund
Program has fluctuated over the past ten years.  The Program, however, has been
increasingly  funded  with  general revenues.  In FY 2004,  as noted  in Figure II-7, the
appropriation from general revenues was the only source of funds for the Program.
     $1,800 -,
     $1,600 -
   o
   T3
   O
   Q
            1993   1994   1995    1996   1997   1998    1999   2000   2001   2002   2003   2004

                                       Fiscal Year

                 General Revenues  Available balance and other revenues of Superfund Trust Fund


      Figure II-7:  Total Appropriations to the Superfund Program, 1993-2004
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Chapter 11-Page 19

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    Expenditures
Funds allocated to the Superfund  Program are used for specific types of expenditures,
which  can  be  broadly  divided  into  programmatic  and  administrative  categories.
Administrative costs include staff payroll costs, facilities, equipment, supplies, and non-
site travel.  The  majority  of enforcement costs are  included as administrative because
enforcement resources primarily consist of payroll.   Programmatic costs are generally
external to the Agency  (e.g., contracts, grants), and  within the Superfund  cleanup
program include  site-specific cleanup activities, site assessment and NPL listing work,
investigations  and remedy design,  state and community participation,  and program
management and  policy development.

Expenditures,  as opposed  to   appropriations,  represent  the  programmatic and
administrative  resources  EPA has actually paid out.  Because  Superfund projects are
often  multi-year endeavors, resources appropriated in a given year may be paid out over
multiple years. Additionally, because unused resources from prior years are returned to
the Superfund budget in the form of deobligations, expenditures for any given year can
exceed appropriations.
                                             Response
                                              support
                                               7%
Remedial actions and related
site-specific work, such  as
site  investigations,  remedy
design,           community
involvement,           post-
construction monitoring, and
oversight   of   responsible
parties, represent the largest
portion of the resources EPA
spends  in  the  Superfund
Program-approximately
31%, or $415.4 million,  in FY
2002  (excluding  ORD  and
OIG  expenditures).      In
general,            program
management activities, such
as   policy   development,
emergency    preparedness
activities,    contract    and
information    management,
training, and general support
have consumed the second largest share of the budget -approximately 22%, or $294.8
million  in FY 2002.   Figure II-8, from GAO's 2002 report on the Superfund Program,
illustrates  EPA's  Superfund Program  expenditures in  FY 2002 for  everything except
expenditures to ORD and OIG.34
                                                             M anagement
                                                                and
                                                             administration
                                                                22%
                                Figure II-8: Superfund Program Expenditures by
                                  Category (e.g., Removal, Remedial), FY 2002
                                           (Excludes ORD and OIG)
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 As mentioned in the beginning of this chapter, the Superfund Program provides funding
 for various other offices that provide enforcement, management, and technology services
 to the Program.  Figure  11-9 shows the percent of Superfund expenditures for  each of
 these offices for FY 2003.
                          OCFO
                     OARM
                      6.7%
                     OECA
                     13.5%
               Figure 11-9:  Superfund Expenditures by Office, FY 2003
                                (Total $1.265 Billion)
   1600 -,-

   1400 --

   1200

<2  TOO
o
=  800

.E  600
tf>
   400

   200

     0
                             I
 I    II     II
	1	1	1	1	
 1999    2000    2001     2002    2003
             • Administrative   Programmatic

    Figure 11-10: Superfund Expenditures-
       Programmatic and Administrative,
                 FY 1999-2003
Overall,  the   percent  of  the
Superfund  Program expenditures
categorized   as   programmatic
costs  has  declined somewhat  in
recent years, from nearly 75%  of
all expenditures ($1.117 billion  of
a  $1.492  billion budget)  in FY
1999 to roughly 65%  in FY 2003
($818  million  of a  $1.265  billion
budget).    Approximately  2%  of
this decline is attributed to shifting
$130  million   for  ATSDR  and
NIEHS   from   the   Superfund
appropriation     to     separate
appropriations  beginning   in FY
2001.  Figure 11-10 indicates this
decline overtime.35
 NACEPT Superfund Subcommittee Final Report  April 12, 2004
                                                            Chapter 11-Page 21

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According to EPA officials, a significant reason why administrative costs have increased
over time relative to programmatic costs is that the Superfund budget generally is not
increased yearly to  account  for cost-of-living salary adjustments  (COLAs)  and other
salary  increases for federal employees,  or for multi-year inflation  related to rent  and
utilities.  EPA typically covers these increases in administrative costs  by reducing the
resources available for programmatic functions, rather than reducing staff resources.36
Because the focus of the Superfund Program is  on  cleanup of sites contaminated with
hazardous substances,  the Subcommittee was  concerned  about  this decline in  the
amount of money  available to be spent  on cleanup activities within the programmatic
expenditures.  Figure 11-11 displays the total amount spent on removal  actions, remedial
actions, and long-term response actions, which tends to reflect payments made by EPA
to cleanup contractors.   It is based  on data provided  by EPA and  shows  a steady
decrease from FY1997 to FY 2001,37
    ro
    c
    £
       600 -T-
       500 --
       400	
    o
    Q
       200 -
        100 --
                            •Removal, Remedial Action, and LIRA Obligations
            1993    1994    1995    1996    1997    1998    1999    2000   2001   2002   2003

                                       Fiscal Year

    Figure 11-11: Superfund Cleanup Expenditures (Removal, Remedial Action,
                   Long-Term Response Action), FY 1993-2003
Chapter Il-Page 22
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1 Removal actions generally are limited to a 1-year effort and $2 million in expenditures.
240CFR300.425(b)(1)
3 See Admin_Prog Historic SF Allocation Charts.pdf, sent by EPA on January 5, 2004.
4  Information provided by EPA from eFACTS on October 16, 2003.
5  U.S. EPA Guidance on Setting Priorities for NPL Candidate Sites,  OSWER Directive 9203.1-06,
1992.
6  See 40  CFR  §300.435(f)(3) and July 2003  EPA Directive OSWER 9355.0-81 FS,  Transfer of
Long-Tern Response Action Projects to States.
7 EPA tracks the status of sites on the  NPL as proposed, final, or deleted. Analysis conducted as
part of this report follows this  practice for consistency.   Generally, the report delineates which sites
are considered in any particular tabulation.
8 Information provided by EPA from eFACTS on October 16, 2003.
9  Pre-SARA refers  to  sites listed  prior to the enactment of  Superfund  Amendment  and
Reauthorization Act, October  16, 1986.  Number of sites provided by EPA on November 25, 2003.
10 For CERCLIS reporting purposes,  as presented in  OSWER Directive 9200.3-14-1G-Q (April 7,
2003), sites are defined as mega sites if any combination of remedial action costs, excluding long-
term remedial actions, exceeds $50 million.
11 Source: EPA list of 142 mega sites  provided  to Subcommittee on November 25, 2003; data
current as of 10/15/03 from CERCLIS.
12 Number of sites provided by EPA on November 25, 2003.
13 Sites are designated as "undetermined lead" when not all anticipated construction projects have
yet begun.
14 See Office of the Inspector General,  Special Report: Congressional Request on Funding Needs
for Non-Federal Superfund Sites, Report 2004-P-00001, issued January 7,  2004, p. 10.
15 Ibid., see p.6.
16 Ibid.,  Enclosure  3; New Bedford, p. 1;  Nascolite Corp.,  p. 2; Combe  Fill  South Landfill, p. 2;
Federal Creosote,  p. 3;  Welsbach &  General Gas Mantle (Camden Radiation), p. 4; Coleman-
Evans Wood Preserving Co., p.  8; Velsicol Chemical  Corp. (Michigan),  p.11; and Libby Asbestos
Site, p. 19.
17 EPA's Federal Facilities Restoration and  Reuse Office: Program Facts for Fiscal Year 2003, data
from CERCLIS on 10/14/2003, http://www.epa.gov/swerffrr/documents/ffcc.htm
18 Facilities owned or operated by a department, agency or instrumentality of the U.S.
19 See http://www.epa.gov/swerffrr/documents/ffcc.htm
20 Source: Data  provided by EPA from Superfund eFacts database, as of October 16, 2003.
21 Data provided by EPA on November 25, 2003; data as of end of FY 2003.
22 OSWER Directive 9285.6-08
23 OSWER Directive 9355.0-85
24 See http://www.ep.gov/superfund/resources/sediment/cstag_sites.htm
25  Probst, Katherine N., et  al,  Superfund's  Future: What  Will It Cost?,  p.  158,  Table  7-4.
Washington, DC: Resources for the Future, 2001.
26 All numbers are in 1999 dollars.
27 Operable  units are a distinct cleanup project at a site based on remedy, geography, or path of
exposure.  The RFF study assumed 3.8 operable  units for mega sites; 1.6  for non-mega sites. See
p. 87.
28  Fund-lead or  mixed-lead, nonfederal  facilities,  NPL  mega  site  that  have  not  achieved
construction  completion.
29 Manufacturing subtypes include chemicals and  allied products, lumber and  wood products/wood
preserving/  treatment,  electronic/electrical  equipment,   primary  metals/mineral  processing,
radioactive products, and fabrics/textiles.
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30 U.S. General Accounting Office, GAO-03-850, Superfund Program: Current Status and Future
Fiscal Challenges (July 2003), p. 11;  and February 18, 2004, letter to Senator Jeffords, Superfund
Program: Updated Appropriation and Expenditure Data.
31 Data on the history of congressional appropriations  for the Superfund Program 1999-2003
provided by EPA September 2003.  In FY 1999, appropriations for ATSDR and NIEHS totaled $136
million, while the  Brownfields  appropriation totaled $90 million; in FY 2000, ATSDR and NIEHS
totaled $130  million, while Brownfields totaled $88 million. For both FY 2001  and FY 2003,
appropriations for Brownfields were $93 million.
32 Revenue sources for the Trust Fund include taxes,  cost recoveries, fine/penalties,  and the
interest on unexpended balance. Taxes provided the majority of resources through FY 1996.
33 GAO-03-850 Report to Congress:  Superfund  Program -  Current Status and Future Fiscal
Challenges, July 2003, pp. 9-11; and GAO-04-475R: Superfund Program: Updated Appropriations
and Expenditure Data, p.3.
34 Data provided  to  GAO by EPA,  which also determined which  activities  to include  in each
category.  See GAO,  Superfund Program Current Status and Future Fiscal Challenges (July 2003),
p. 13.  Total  program expenditures  for  FY 2002 were  $1.34  billion.   Remedial costs include
investigations,   remedy design, community  involvement,  construction,  post-construction,  and
oversight of responsible parties.   Removal costs include  assessments,  investigations,  removal
construction, and oversight.   Response  support includes site-specific costs related to technical
assistance, technology innovation,  contract  management,  records management,  and  general
support to other organizations through  grants,  interagency  and/or  cooperative  agreements.
Management and administration includes non-site specific costs  such as program management
and budget, policy development and implementation,  emergency preparedness activity,  contract
and information management,  training,  and general support. Enforcement costs include searching
for and negotiating agreements with responsible parties.  Other includes site assessment, federal
facilities, and Brownfields, which is no  longer funded through a Superfund appropriation as of FY
2003.
35 Adm_Prog Historic SF Allocation Charts.pdf, sent by EPA on January 5, 2004.
36 Ibid.
37 See Obs_Exp  02.xls, provided  by EPA to the Subcommittee during  the  November  5, 2003
meeting.
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  III.
                 Listing  and
Management  of
Sites  on the  NPL
In Section 105(a)(8)(B) of the Comprehensive Environmental Response, Compensation
and Liability Act (CERCLA), Congress requires the President to "list...national priorities
among the known releases or threatened releases throughout the United States...." This
list has come to be known as the National Priorities List, or the NPL.  It is further defined
by regulation at 40 CFR 300.5 as "the list, compiled by EPA pursuant to CERCLA Section
105, of uncontrolled hazardous substance releases in the United States that are priorities
for long-term remedial evaluation and response."

The NPL is  one of the cornerstones of the Superfund Program. Decisions about the
number and types of sites to  list on the NPL have  important implications for the
Superfund budget and for affected communities and  potentially responsible  parties
(PRPs). For instance, under 40 CFR 300.425(b)(1), only sites listed on the NPL are
eligible for funding of long-term cleanups (i.e., remedial actions) from the Superfund Trust
Fund.  Under EPA's current regulations, only communities near sites that are proposed
for or listed on the NPL are eligible for technical assistance grants. Finally, Congress and
other program  overseers  monitor progress at NPL sites  to measure and evaluate the
Superfund Program's performance.

In September 2002, in response to questions from this Subcommittee, EPA headquarters
informally surveyed EPA  regional offices about the factors that most often prompt
initiation of  the Superfund site assessment process and inform eventual NPL listing.
Based on responses from seven  regional offices, it appears that the vast majority of sites
considered for  the NPL come to EPA's attention based on recommendations from state
governments or Tribal Nations, or through collaboration between a regional office and a
state or Tribe.  State regulators, for the most part, are the  primary  discoverers of
contaminated sites, and state programs tend to be the cleanup mechanism used for most
contaminated sites.  When these  programs  cannot adequately address a site,  for
example, because of a significant orphan share or the need for specialized expertise,
Superfund and  other alternatives are considered.  The regions reported that the need for
Superfund money to pay for cleanup was the reason for approximately one-third of new
NPL listings, another third resulted from lack of cooperation from PRPs, and the final third
was due to a combination of other factors.
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Because NPL sites remain the focus of the Superfund budget and because progress at
NPL sites largely defines the success of the Program, EPA asked the Subcommittee to
focus some of its deliberations on the role of the NPL, particularly as it relates to other
cleanup programs.

This chapter describes the Subcommittee  deliberations related to use and management
of the NPL.    The Subcommittee framed five questions under which it organized its
discussion of this topic.

    -* How should EPA make the best  NPL listing decisions?
    -* How should EPA increase the transparency of its listing decisions?
    -* What should be the role of other programs?
    -* How should EPA set priorities among listed sites?
    -* What are the options for increasing the resources available for cleanup?

The Subcommittee's deliberations and recommendations described in this chapter apply
to all NPL sites, including mega sites. In addition, the Subcommittee anticipates that its
deliberations and recommendations will be applied equally to sites addressed through the
Superfund Alternative Sites program.
How Should EPA Make the Best Listing Decisions?
The Subcommittee approached the question "What types of sites belong on the NPL?"
by examining the NPL listing process and asking "How should NPL listing decisions be
made?" This approach was taken because the Subcommittee  reasoned that if listing
decisions are based on good information and analysis, the universe of sites identified will
be improved. Subcommittee deliberations focused on improving the use of the NPL by
optimizing  EPA's current listing and management practices, rather than on redefining the
Program.
   Different Views on Risk

Subcommittee members had very different views about how the concept of risk should be
addressed in the Superfund Program.   Some members believe that the fundamental
problem causing concern over the number and types of sites to list on the NPL is related
to how the Agency  uses  risk  in decision making.  They believe  the Program should
primarily focus on sites or portions of sites that pose current significant threats to humans
or sensitive  environments, and should  use  Program remedial  action resources where
there are not viable  responsible parties.  Under this approach, the Program should first
prioritize ongoing significant threats that require government funding for cleanup,  and
should  use other environmental cleanup programs to address  less significant current
threats and potential future threats and to administer and oversee cleanups at sites that
have viable responsible parties.  These members believe that the  Program's resources
should  be  guided using assessments of risk, and that EPA should  increasingly use risk
Chapter Ill-Page 26
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as a way to make decisions about NPL eligibility and to set priorities for spending. They
stress that good site identification and outreach to communities and PRPs should yield
the data to make solid decisions about the risks actually posed at sites and also  are
concerned that the Hazard  Ranking System (MRS), the current method by which EPA
most often determines whether a site is eligible for the NPL, does not rely heavily enough
on assessments of current site risks.A

Other Subcommittee members strongly disagreed with these views. These members
believe the Superfund Program must address both current and potential  future threats to
both humans and the environment.  They argue that due to the uncertainties inherent in
risk assessment (e.g., multiple chemical exposures or sensitive subpopulations) and the
uncertainty associated with  exposures and physical and  institutional controls, "current"
and "potential future" threats, and "significant" and "insignificant" threats,  often cannot be
clearly distinguished.  These Subcommittee members argue that waiting  until actual
exposure and adverse effects are experienced before acting would be inappropriate and
more costly to the Superfund Program. Further, they believe that any diminution in EPA's
efforts  to address both  current and  potential future threats to both humans and  the
environment would  be inconsistent with the Agency's statutory responsibilities under
CERCLA, and  they are  concerned that  EPA's  implementation of the Program  may
underestimate or inadequately address certain types of risks at certain sites.8

This  fundamental  difference  in  views   created  the  backdrop  against with   the
Subcommittee carried out many of its deliberations.

In the  context of these  divergent views, the Subcommittee makes  four consensus
recommendations on NPL  listing.  Recommendation  1  calls on EPA to use a set of
consistent factors to choose which NPL-eligible sites to propose for listing in each listing
cycle.    Discussion  associated  with Recommendation  1  describes  Subcommittee
members' range  of views  on the  set of factors that EPA should  consider in listing
decisions, and on the role that estimates of cleanups costs or the amount of money in the
Superfund Program  budget  should play in  decision making. Recommendations 2 and 3
call for  EPA  to continue and expand its  practices of coordination, collaboration, and
information gathering and sharing during the site screening and  assessment processes.
Recommendation 4  suggests some specific improvements to EPA's  implementation of
the MRS and describes the Subcommittee members' divergent views about whether EPA
should undertake a more fundamental reevaluation of the MRS.
A Subcommittee member Richard Stewart supports this view. See Attachment A for
Mr. Stewart's individual statement and elaboration on his position.

B Subcommittee member Vicky Peters supports this view of risk. See Attachment A for
Ms. Peters' individual statement.
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    Recommendation 1:  EPA should apply a set of consistent factors
    from year to year to choose which NPL-eligible sites to propose for
    listing in each listing cycle.
NPL eligibility is largely determined based on screening for threats and potential threats
at a site. EPA1 determines  NPL candidacy (i.e., the subset  of eligible sites the Agency
decides to  propose for the  NPL)2 by also  taking into consideration factors  related to
program  management,  such as whether the site  is being appropriately addressed  by
another program, or whether there is support in the affected community or the state or
Tribal  government  for NPL  listing.   As described  in  Recommendation 1,  the
Subcommittee believes that EPA should make its decisions about which NPL-eligible
sites to propose for NPL listing based on a consistent set of factors, and that factors used
should be considered on a site-by-site basis.0

The  Subcommittee deliberated on factors that  EPA might consider when determining
which NPL-eligible sites to propose for listing on the NPL, but  did not reach consensus on
a specific set of factors to recommend.

Some Subcommittee members support the set of five factors  described below, which are
drawn  largely from the factors  that  EPA  already considers  in determining which NPL-
eligible sites to propose for listing.0 Because these factors are based on and incorporate
the  factors  described in EPA's current  guidance for setting  priorities at  NPL-candidate
sites (OWSER Directive  9203.1-06) Subcommittee members  who support  their use
anticipate that  EPA  could  implement  a process  that  considers these  factors  in a
consistent manner without making major changes to the Agency's current procedures or
incurring  significant administrative costs.
Risk
       What are the risk drivers?  Current EPA guidance on setting priorities for NPL-
       candidate sites (OSWER Directive 9203.1-06) lists seven sets of considerations
       that, although addressed in MRS scoring, should also be evaluated qualitatively
c The support  of Subcommittee members Gary King, Catherine  Sharp and Vicky
Peters for Recommendation 1  is qualified by their position that anticipated cleanup
costs and the amount of funds available in the Superfund Program budget should not
be criteria used to  include or exclude sites from the NPL.  See Appendix I for Mr.
King's and Ms. Sharp's joint statement and the individual statement of Ms. Peters.

D Subcommittee member Vicky Peters supports the set of listing factors based in part
on her  understanding that  EPA's  current policy does  not factor in incremental
reduction of risk from removals or PRP cleanup standards in determining whether a
site should be listed on the NPL and that this practice is intended to ensure that  sites
that would  qualify as a national priority are cleaned up in compliance with CERCLA
standards, and do not fall off the table because just enough cleanup  occurs to result in
the site  no longer scoring 28.5 on the HRS.   See Attachment A for Ms.  Peters'
individual statement.
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       using best professional judgment for both scored and unscored MRS pathways.
       These considerations include whether a release has been observed, the types of
       exposures present, the types of threats and potential threats to humans and the
       environment present, and whether the Agency for Toxic Substances and Disease
       Registry (ATSDR) has issued or is planning to issue a health advisory.
    -*  Are there risks not accurately reflected  in the MRS score?

Likely Outcomes of Activities by Other Programs or PRPs
    -*  Is or will another program appropriately address the site?  The Agency should
       not use scarce Superfund time, attention, or funding when another program could
       appropriately address  a site and  has the capacity (funding and resources)  to
       appropriately carry  out site evaluation and cleanup or appropriately provide
       oversight of work funded by responsible parties.3 Such  programs might include
       state  or Tribal environmental  programs,  redevelopment programsE, and other
       federal programs, such as the Resource Conservation and Recovery Act (RCRA)
       program.
    -*  Are  removal actions  complete,  underway, or scheduled?   If so, will they
       significantly reduce risks to ensure long-term protection of human  health and the
       environment^
    -*  Have PRPs  completed, undertaken, or scheduled response actions at the site?
       If so, are such actions likely to continue?  Many state environmental cleanup
       programs have the authority to enter  into enforceable agreements that can be
       used  to  ensure  and oversee cleanup.   In  general,  sites that  are  being
       appropriately addressed  under  such programs should  not  be considered
       candidates for the NPL.

Degree of Public Concern
    -*  What is the degree of public concern? One of the reasons that the NPL is the
       most  appropriate approach for some sites is that using Superfund may be the
       only practical way to  respond to the high degree of public  concern  in some
       communities. In evaluating this issue, EPA should consider the extent to which a
E Subcommittee member Vicky Peters  supports  the set of listing factors with the
qualification that that NPL candidate sites should not be "deferred" to redevelopment
programs because, although NPL candidate sites should take advantage of resources
and partnerships for cleanup from other programs  "redevelopment programs" do
not provide the oversight, expertise, cleanup standards and other requirements of a
cleanup program.  See Attachment A for Ms. Peters' individual statement.

F Subcommittee member Vicky Peters supports the set of listing factors based in part
on her  understanding that EPA's  current policy does not factor in incremental
reduction of risk from removals or PRP cleanup standards in determining whether a
site should be listed on the NPL and that this practice is intended to ensure that sites
that would qualify as a national priority  are cleaned up in compliance with CERCLA
standards, and do not fall off the table because just enough cleanup occurs to result in
the site  no longer scoring 28.5.    See Attachment A  for Ms. Peters' individual
statement.
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       community has been informed about a site and involved in  site screening and
       assessment.

Support for Listing from State and Local  Governments, Tribal Nations and
Communities
    -* What is the degree of support for listing from state or Tribal governments? EPA
       has a policy of seeking state Governors' and Tribal governments' concurrences
       on all new NPL listings, and has a procedure in place to attempt to resolve issues
       when states  or Tribal Nations are concerned about a  listing.  Although the
       Subcommittee could  not  reach  consensus on whether Governors' and Tribal
       governments' concurrences should  be required for listing, members did agree
       that the views of states and local governments  and  Tribal  Nations should be
       considered during the listing process.

Environmental Justice
    -* Are environmental justice concerns associated with the site?

Other Subcommittee  members do not support this set of factors or have concerns with
one or more of the individual factors.  These members have a variety of concerns with
the factors, including (1)  concern  that the  factors did not  adequately call for EPA to
consider actual, current threats to humans and the environment in listing decisions, and
(2) concern that the factors allowed too  much consideration of, and  potentially reliance
on, non-Superfund programs, particularly redevelopment programs.
   Cleanup Costs v. National Priorities
Many Subcommittee discussions about NPL listing focused on the role (if any) that cost
should play in EPA's decisions about which NPL-eligible sites to propose for listing.  The
Subcommittee did not reach consensus on this issue.

Some Subcommittee members believe strongly that EPA should  not use estimates  of
cleanup costs or the amount of money available in  the Superfund Program budget  to
make decisions  to  include or  exclude  sites on the NPL.  While  these members
acknowledged that decision makers may have an awareness of costs and knowledge  of
likely program funding, they believe that this knowledge should not be used to limit  or
expand the number or types of sites listed  on the NPL. Rather, they believe that the NPL
should represent true national priorities—sites that meet the eligibility criteria and are
judged by EPA to need the expertise and resources that only the Superfund Program can
provide.

Subcommittee members who argued that  budget and cost estimates should not be used
to make decision to include or  exclude sites from the NPL acknowledged that one of the
implications of this approach is that the NPL may grow faster in  the near term, putting
additional pressure  on  EPA  to do  more  with  the resources  it  has.    They  also
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acknowledged that there may continue to be sites on the NPL at which EPA is unable to
move cleanups  forward, and remedies may be delayed  because of limits on funding.
However, these  Subcommittee members feel strongly that the NPL should reflect the true
need for funding—not be limited to the sites the Agency thinks it can afford.

Other Subcommittee  members did  not support a recommendation  calling for EPA to
disregard estimates of cleanup costs or the amount of money available in the Superfund
Program budget when making NPL listing decisions.  Subcommittee  members who held
this view discussed a  number of reasons.  Some Subcommittee members were willing to
support a recommendation against consideration of costs  in individual listing packages if
the Subcommittee was able to reach consensus on the role that costs and funding should
play in shaping  the Program over the longer term; however, the Subcommittee did not
reach consensus on this point.  Other members were uncomfortable supporting such a
strong statement against consideration  of costs  in the absence  of what they viewed as
related recommendations on improvements they  think are needed in the NPL listing
process and management of sites  on the NPL.  They  noted  that improvements  are
particularly  needed in the areas of consideration of non-Superfund programs, setting
priorities among sites listed  on  the NPL, EPA's  allocation of Superfund resources, and
how large geographic areas  are addressed.  The Subcommittee discussed each of these
issues, as described later in this Report.

Matching the Size of the Program to Funding Over Time
Some Subcommittee  members  believe that, overtime, EPA management is responsible
for matching the size of the Superfund Program with the funds appropriated by Congress.
These members believe that because of this responsibility, the timing and numbers of
sites listed should, over time, be legitimately shaped  by EPA to manage the Program to
an overall size that corresponds to Congressional appropriations.  They also believe that,
over the long term, EPA management has no choice but either to match the Program's
dimensions to  the resources  provided by Congress or to successfully seek greater
resources from Congress.  These members stressed that EPA's greatest responsibility
should be to achieve timely cleanup at the priority sites it places  on the NPL, rather than
the creation of an expansive  site list.G

Other Subcommittee  members  did not support this position, believing  instead that EPA
should place sites on the NPL based solely on consideration of a  set of consistent factors
and that anticipated cleanup costs and the amount of money in  the Superfund Program
budget should never  be criteria used to include or exclude sites from the NPL.  They
contend that EPA has a responsibility to  communicate to the executive and  legislative
branches of government, as well as to the public, the most accurate information about the
existence of national priority sites and  their  funding  needs.   These members  are
concerned that if EPA chooses not to list sites on the NPL  in an effort to match the size of
the Program to the funding available, the Agency will deny and obfuscate the true need
G Subcommittee member Richard Stewart supports this view.  See Attachment A for
Mr. Stewart's individual statement.
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for funding,  thus  reducing the likelihood that adequate funding  will  be requested  or
appropriated.
    Recommendation 2:  EPA regional offices should continue and
    improve collaboration with states, local governments, and Tribal
    nations as they consider which sites to recommend to EPA
    headquarters for NPL listing.
Of the hundreds of thousands of contaminated sites across the United States, only a
small fraction may rise to the level of a national priority needing  Superfund Program
attention.   EPA  routinely  collaborates  with  state  officials  in  identifying  sites  for
consideration  for the NPL and  in the pre-screening and  Superfund  site assessment
processes that lead to a decision to propose a site for NPL listing. EPA also coordinates
and collaborates with Tribal and local governments in these  processes.  However, based
on the knowledge and experiences of some Subcommittee members,  coordination and
collaboration with local governments and Tribal  Nations appears to be more ad hoc than
EPA's interaction with state environmental agencies.

Collaboration and coordination among Tribal nations, states, local governments, and EPA
regional offices are critical to sorting through the many contaminated sites that may need
attention, and  ensuring that  resources for site assessment and eventual cleanup  are
oriented toward  the  sites that  truly  require national attention  under the Superfund
Program.  Recommendation 2 is intended to ratify the importance  of collaboration and
coordination efforts and relationships, and to encourage EPA to strengthen them where
possible.

As  EPA implements  Recommendation  2,  the  Subcommittee  cautions  against  the
Agency's spending significant resources to develop extensive guidance on coordination.H
In general, individual EPA regional offices have developed practices of coordination that
they believe are appropriate  to  their region- and state-specific circumstances.  These
practices include Regional Decision Teams, site "watch lists," and other strategies.  From
their individual experiences, Subcommittee members had a range of views about existing
regional coordination mechanisms. Some members think that existing mechanisms  are
working well and do not need significant improvement; other  Subcommittee  members
think that coordination is not consistently or reliably achieved.

Within  this range of views the Subcommittee  agrees that informal region- and state-
specific approaches can be appropriate, so long as coordination is consistently achieved
and  national-level  guidance  is  applied.   If EPA believes that existing  coordination
H Subcommittee member Mel Skaggs addresses his concerns about  the potential
cumulative budgetary impact of the many new processes, surveys, committees, and
studies discussed throughout this report in his individual statement.  See Attachment
A for Mr. Skaggs' individual statement.
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activities in the regional offices need strengthening, it might consider a few discrete, time-
and resource-limited tasks to further Recommendation 2. These might include:

    -*  Evaluating of regional  coordination activities  to  document  best practices and
        ensure that all regions have coordination practices in place, and
    -*  Issuing  of a  brief guidance  on  coordination to  the regions to promote  a
        reasonable degree of  national consistency and  ensure an  adequate level of
        consultation with states and local governments, Tribal Nations, and  other federal
        agencies.
   The National-Level Review Process

In 2002,  EPA  instituted a new national-level review  process in which officials from the
regional offices and headquarters evaluate  all  NPL-candidate  sites and group them  in
tiers.  Tier groupings are based largely on the relative significance and urgency of risk but
also taking into consideration other program management factors, including budgetary
constraints.    When   sites  are  tiered,   the  national-level  review  group  makes
recommendations  to  the  Assistant  Administrator for  Solid  Waste and  Emergency
Response about which NPL-candidate sites should  be proposed for NPL listing.

Prior to this change, EPA headquarters generally provided guidance and oversight to the
regions on national listing policy and ensured that listing  packages were appropriate and
legally defensible.   Most NPL-candidate sites  recommended  by regional offices  were
proposed for listing on the NPL, provided national policy was followed and the MRS score
was valid. Since the advent of this new  national-level review process, approximately half
of the NPL-candidate sites sent forward by  regional  offices to  headquarters have  been
proposed for NPL  listing.  The remaining NPL candidates sent forward  by the  regions
have been held over for reconsideration  in future listing cycles.

The Subcommittee had a range of views about this national-level review process.  Some
Subcommittee  members were very supportive of a national-level review, seeing  it  as a
necessary step toward EPA's ensuring quality listing decisions, and an important factor in
providing the Assistant Administrator for Solid Waste  and  Emergency Response the
information and perspective needed to fulfill the delegated responsibility to  make listing
decisions.1

Other Subcommittee  members viewed a national-level review  as an  unnecessary step,
further removing decision making from  the state and regional  managers who are  most
familiar  with  site-specific  circumstances   and,  therefore,  best  equipped  to  make
recommendations  about which sites constitute a national  priority.   These members
believe that EPA's previous practice was appropriate, i.e., using a national-level review to
1 Subcommittee member Richard Stewart supports this view. See Attachment A for Mr.
Stewart's individual statement.
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ensure  national  listing policy was applied  and  MRS  packages  represented  sound
                                                    IK
professional judgment and could withstand legal challenge.

Within these differences, Subcommittee members  agreed that the national-level  review
process (if it is continued) should focus on:

    -*  Bringing national consistency and a national perspective and judgment to bear
       on NPL listing proposals,1
    -*  Monitoring regional offices' implementation of Program guidance,
    -*  Considering geographic fairness in NPL listings so that one region of the country
       does not inappropriately dominate the NPL, and
    -*  Ensuring that MRS packages are legally defensible and of high quality.
    Recommendation 3:  EPA should reach out to potentially affected
    communities, local governments, and potentially responsible parties
    earlier in the Superfund site assessment process to share and solicit
    information about sites being considered for NPL listing.
Currently, potentially affected communities, local governments, and PRPs (if known) are
involved in the Superfund site assessment4 process only on an ad hoc basis, if at all.
Expanding outreach practices to involve more individuals and  entities earlier  in the
process should foster information sharing  about  sites under consideration  and give
communities, local governments, and PRPs more opportunities to participate in the site
screening and  assessment processes.  Earlier involvement and information sharing are
important for a  number of reasons:

    -* Community leaders, site neighbors, local officials,  previous site workers, PRPs
       and  community  and  public  interest  groups  can  be  sources  of  historical
       information  and   knowledge  concerning  site  activities,  contamination,  and
       exposure  pathways.   While this  information  may  come  forward eventually,
       particularly for sites that move through the screening and assessment process to
J Subcommittee member Jim Derouin feels that EPA Headquarters must make final
listing decisions because it is  responsible for and,  therefore,  must  be  held
accountable for,  overall  management  of the Program;  and  feels that  Program
management would suffer if this duty were delegated to the regions and/or states and
listing decisions were to be made without any regard to cost. See Attachment A for
Mr. Derouin's individual statement.

K Subcommittee member Vicky Peters supports the view that a national level review is
an unnecessary step. See Attachment A for Ms. Peters' individual statement.

L Subcommittee member Vicky Peters does not support this role. See Attachment A
for Ms. Peters' individual statement.
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       an NPL listing,  bringing it forward earlier may help EPA make better screening,
       assessment, and listing decisions.
    -* Earlier involvement  may prompt PRPs to  undertake and  fund   some or all
       investigation or clean up activities without an  NPL listing, for example, under the
       auspices  of a  state  environmental  cleanup program  if appropriate,  thereby
       reducing or delaying the number of sites  at which   Superfund resources are
       needed.   This  may be the case  particularly where PRPs who may be willing to
       undertake or fund site investigations  under a non-Superfund program do  not own
       the site under consideration.  Under EPA's current process, these PRPs  often do
       not become involved until after a site is placed on the NPL and the  opportunity to
       proceed under another program is lost.
    -* Earlier involvement may serve to  identify site-specific data that are available and
       reliable and that can  be  used during MRS scoring,  as described more fully in
       Recommendation 4.
    -* As  part  of  reaching  out to stakeholders,  particularly state, local and  Tribal
       governments, EPA can gather information  on and make connections with non-
       Superfund programs that may have independent missions or activities that could
       positively or negatively affect clean up of a site. This information could  be used
       to capitalize on  potential positive effects and avoid negative effects.  (Note that,
       the Subcommittee had a range of views about the  role of non-Superfund  cleanup
       program; this range of views is described further later in this chapter.)
    -* Earlier involvement may help EPA identify potential redevelopment opportunities
       that could provide additional focus  and funding  for the cleanup if they  were
       pursued and integrated into clean-up activities early  in the process.  (Note that,
       the  Subcommittee  had a range of views  about  the  role  of non-Superfund
       programs.  Some Subcommittee  members  were particularly  concerned that
       redevelopment  programs  are  not cleanup  programs and   have  distinct and
       potentially incompatible missions. This  range of views is described further later
       in this chapter.)

In addition,  as  discussed in Chapter IV, some Subcommittee members believe that EPA
should consider a range of options and evaluate a specific set of factors  when making
decisions about a large, geographic area where multiple, unrelated contaminant sources
are present. These options include addressing the area as one "site" or as smaller units
more  closely tied  to individual releases of hazardous substance.  These members note
that earlier involvement of stakeholders could help the Agency determine which  releases
are truly national priorities, and whether releases are inextricably intertwined or  whether
cleanup would  be expedited or made more efficient if discrete releases were addressed
separately as multiple cleanups under the NPL, under other  appropriate programs, or a
combination of these approaches." N   (Note  that the Subcommittee had a range  of views
M  Subcommittee member Tom  Newlon notes his support  for  early  stakeholder
involvement as part of a package of reforms, some of which did not make it into the
final report as recommendations, that are needed to more effectively and efficiently
address potential mega sites, particularly those encompassing a large geographic
area. See Attachment A for Mr. Newton's individual statement.
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on this issue, and some members did not support EPA's considering the possibility of
listing only portions of a large geographic area.  This range of views is discussed further
in Chapter IV.)
   Procedures and Timing for Early Involvement and Outreach

The Subcommittee  is not recommending a specific procedure that EPA should  use to
reach out to local governments, PRPs, or communities.  EPA should use targeted efforts
and informal mechanisms where effective, should take care to contact representatives of
disparate interests, and should ensure that participants have enough information about a
site under consideration to participate in a meaningfully.

The Subcommittee also is not recommending that outreach start at a specific point in the
site screening or assessment process. Involvement should begin as early as practicable,
considering  site-specific  circumstances.    To  facilitate  earlier   identification  and
involvement  of  PRPs,  the Agency should   increase emphasis  on  guidance  that
encourages PRP searches as early as practicable  after a site  is  identified  to be of
interest, instead of after site listing.5

The  Subcommittee emphasizes that it  is not recommending  diversion  of Superfund
resources to extensive outreach and involvement activities at every new site entered into
the Comprehensive Environmental  Response,  Compensation  and Liability Information
System  (CERCLIS) data base.  (In 2003, EPA entered more than 240 new sites into
CERCLIS.)6  Rather, EPA should focus its efforts on the subset of sites that likely will be
found to be eligible for NPL listing.
    Recommendation 4:  EPA should work with stakeholders to
    review the application of the Hazard Ranking System model to ensure
    that it (1) accurately characterizes threats at sites located in sparsely
    populated areas and appropriately considers environmental justice
    concerns, traditional lifestyles, and other issues; and (2) uses site-
    specific data that EPA determines are available and reliable, rather
    than defaulting to presumptions in the MRS to estimate exposures.
The Subcommittee did not carry out a detailed assessment of how the MRS currently is
functioning, and is not making recommendations related to the 28.5 MRS scoring cut off

N Subcommittee member Jim Derouin believes that EPA should have the flexibility to
evaluate  risks/exposures presented by portions of mega sites rather than being
bound to assume that, once a mega site is listed, all portions of such a site must be
treated as posing an equal risk.  He feels that, without such flexibility, EPA cannot
efficiently direct funding to the sites, or portions of sites, that pose the most risk at any
given point in time. See Attachment A for Mr. Derouin's individual statement.
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or the MRS model generally.  At the same time, because the MRS is the means by which
EPA most often  defines which sites  are  eligible for NPL  listing, the Subcommittee
discussed the MRS during its deliberations on the NPL listing  process and is providing a
number of suggestions for improvements to EPA's implementation of the MRS.

The  MRS serves a specific and limited function in  the  Superfund  Program.  It is a
screening tool  that  assigns  certain  numerical values  to a  variety of  exposure
characteristics known  or assumed to be associated  with  a  site.  It is intended to  be
conservative, and while Subcommittee members had a range  of views as to whether the
MRS was too conservative or not conservative enough, all recognized that it delineates a
set of sites for EPA to consider for the NPL and is not a risk assessment.

Once an evaluation of one or more of the critical exposure pathways at a site results in
an MRS score of 28.5 or higher, a site becomes eligible for the NPL. EPA generally does
not  invest additional resources  in completing  calculations  for all pathways to determine
how high the site  score would be if all  pathways were considered.   Because of this
practice, MRS scores cannot be used to compare the  relative  degree of risk among NPL
sites, and cannot be relied  upon to make judgments about the total risk posed by an
individual site. As described further later in this section, Subcommittee members had a
range of views about the fact that the MRS cannot be  used to make risk comparisons or
judgments.

Once sites are determined  to  be eligible for listing,  they  are not automatically listed.
Indeed, many sites that score 28.5 or higher are not  listed. Rather, these eligible sites
are  further screened by EPA and  only a subset is proposed for the NPL. Because EPA
routinely exercises its discretion not to list NPL-eligible sites, an inappropriate or less
than perfect application of the scoring system  can be corrected during EPA's exercise of
discretion relative  to  listing decisions.  Subcommittee members who generally are
comfortable with the use of the MRS as a screening tool, rather than a  risk assessment
tool, noted that if application of the MRS either over- or underestimates  threats at a site,
earlier  involvement of affected communities and PRPs (Recommendation 3) most likely
will  improve MRS scoring and  interpretation by bringing more  information to the table
earlier  in the site screening and assessment processes.  (If a site does not score 28.5 or
higher, EPA generally does not consider it for NPL listing.)

Subcommittee members identified a number of concerns related to implementation of the
MRS.  Some Subcommittee members expressed concern that limitations of the MRS as
implemented may preclude NPL listing  of sites that pose legitimate and serious risks to
humans and the environment and that warrant national attention under Superfund. Other
members had concerns about the opposite problem, that  application of the MRS may
result in the listing of sites that do not truly pose the types of legitimate, significant risks to
humans or the environment that the Superfund program was designed to address. Some
of these Subcommittee  members suggested  that layers of conservatism built into the
MRS model  result in unreasonably conservative listing decisions, while others  believed
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the MRS does not appropriately weight  real and  present threats  to  humans  or  the
environment versus potential future exposures.0

The   Subcommittee   suggests   a   number  of  specific  improvements  to  EPA's
implementation of the MRS. Subcommittee members who support  greater use of  risk
assessment in decision making about NPL listings appreciate that the improvements to
MRS implementation  described below may help the MRS better function as a screening
tool.  Nevertheless, as described further later in this section, they also  believe that a more
basic evaluation of the role of risk in decision  making about NPL eligibility is needed.p

Sparsely Populated Areas and Environmental Justice Communities
While CERCLA requires that the prioritization process take into  account to the extent
possible  the  population at risk, it does  not express an  intention to  protect  dense
populations  to  the exclusion or detriment  of  sparse  populations.   If EPA's  initial
investigation of this issue reveals that the MRS model is screening high-risk sites from
further consideration for the NPL because  they are located in sparsely populated areas,
the Agency should initiate a dialogue, including the relevant stakeholders, to determine
how to address the MRS bias towards heavily populated areas.

Subcommittee members were also concerned that the MRS model may not adequately
incorporate environmental justice considerations.  Many believe that  socio economically
depressed areas and communities of color are often subjected to a greater proportion of
environmental insult  as a  result of ongoing  and  abandoned releases of hazardous
substances, and fewer redevelopment opportunities. As a result,  a community could be
exposed  to a number of sites, none of which  scores 28.5,  but that together may pose
greater risks to receptors than sites currently on the NPL.  In addition, genetics, inferior
nutrition,  and poor health care  may predispose people to  disease  and other adverse
effects from contaminated sites.  As  a  site-specific screening tool,  the MRS does  not
incorporate such considerations;  rather, it evaluates releases in isolation.

Although  the  Subcommittee acknowledges this issue, it did not have the opportunity to
thoroughly evaluate the MRS components  and arrive at a definitive proposed resolution.
Therefore, the Subcommittee suggests  that EPA formulate policies  that would ensure
that predisposition to disease as a result of  genetics, poor nutrition, or health care, and
cumulative  exposures  from a disproportionate  number  of contaminant sources,  be
considered  in NPL listing decisions.  In this effort the Agency should  coordinate with  the
National Environmental Justice Advisory Committee, which is engaged in similar efforts.
Additionally,  EPA  should  consider  convening  a  broad  stakeholder task  force
(EPA/state/Tribal/industry/public) to make recommendations on scientifically supportable
policies to address concerns about environmental justice issues related to NPL listing.
° Subcommittee member Richard Stewart supports this view. See Attachment A for
Mr. Stewart's individual statement.

p Subcommittee member Richard Stewart supports this view. See Attachment A for
Mr. Stewart's individual statement.
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Traditional Lifestyles
EPA should consider creating a working forum with Tribal associations, including Alaskan
Natives,  Hawaiian  Islanders,  and Native American  Indians,  to  develop  reasonably
anticipated exposure scenarios  for these groups and to  determine what regulatory
actions are needed to ensure that such scenarios are incorporated  into listing decisions.
The  Subcommittee was briefed on traditional lifestyles.  As part of this briefing, Tribal
members  presented their experience  that,  at least  in some  cases, traditional  and
subsistence practices of Tribal members are  not sufficiently  addressed in any aspect of
the Superfund Program - from NPL decisions, to  risk assessment, to remedy selection
and deletion.  In addition, although traditional lifestyles tend to be associated with Tribal
Nations, they also can be important in non-Tribal communities,  particularly communities
of color, where traditional  religious practices are  predicated on the  use of the natural
environment.

Vapor Intrusion
The  Subcommittee  supports  EPA's  current  investigation of  the  prevalence  and
seriousness of vapor intrusion at sites currently  listed on the NPL. In the meantime, EPA
should work  with the  Association of State  and  Territorial  Solid  Waste  Management
Officials in its ongoing effort to  determine whether vapor exposure  pathways  can be
addressed adequately through application of the MRS.   If it is determined that MRS
screening is sufficient, EPA should disseminate  its findings through training and/or new or
revised  guidance and policy directives.  If  it is  determined that the MRS does  not
adequately reflect  risks from  vapor  pathways, EPA  should  work with states, Tribal
Nations, and  other appropriate individuals to decide what steps to take to ensure that
sites posing significant enough risks via vapor intrusion are eligible for listing on the NPL.

Explosive Hazards
EPA should determine, with input from relevant  stakeholders, whether it currently has the
option of placing explosive hazard sites on the NPL, and if not, whether such an option
would expedite and  improve the cleanup of such sites.  Meanwhile, EPA should address
imminent and substantial dangers to the public  health or welfare posed by explosive
hazards by taking removal  actions where appropriate.7  Hazards resulting from exposure
to unexploded and other ordnance pose threats  not only at federal facilities, which are not
specifically addressed in this report, but also at numerous formerly used Department of
Defense sites and  private  party sites.  These  threats currently may not be adequately
addressed by the MRS.

Use of Real, Site-Specific Data
EPA should supplement MRS scores calculated using the standard  pathway models and
default assumptions with additional consideration of actual, up-to-date site-specific data
where such data are available and reliable.  Use of site-specific data may help to clarify
MRS default assumptions and underlying presumptions such as fish consumption rates,
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and likely contaminant receptors.0 Consideration of site-specific data, where practicable,
should ensure  that decisions based  on MRS scores accurately  reflect actual site
conditions and risks.

Using the  process of earlier involvement suggested in Recommendation 3, EPA should
encourage affected communities,  PRPs, and other stakeholders to provide available up-
to-date, site-specific data that could be used to improve upon the MRS model's uniform
incorporation of default assumptions and underlying presumptions by facilitating a more
thorough understanding of actual site conditions, threats and potential threats.   Besides
improving  the accuracy of screening and assessment of NPL-eligible sites, this  enhanced
use of site-specific  data avoids  EPA's having to  modify the MRS  model parameters
(which are established in large part by regulation),  because the data  are considered
during interpretation  of MRS scores.

Other Concerns About the MRS
In addition to the concerns  about implementation  of the  MRS described  above,  some
Subcommittee members had  a much more basic concern that because the MRS is not a
risk assessment, but is  rather a  screening evaluation that  considers both current and
hypothetical potential future threats, it does not provide the  type of risk characterization
that EPA should use to  make decisions about which sites to propose for listing on the
NPL.   These members  believe that EPA should determine NPL eligibility by using a
scoring system that evaluates  the actual  risks posed  by sites to people and the
environment,  i.e., an  approach  akin to risk assessment.   At a minimum,   these
Subcommittee members believe that EPA should undertake an open, public process to
revise the MRS so that it is more risk based.R  These concerns are described in more
detail earlier in this chapter in the discussion of Subcommittee members' different  views
about risk.

Other Subcommittee members strongly opposed this view.  They believe that using the
MRS as a screening tool to determine NPL eligibility is appropriate, and  that the current
MRS, particularly with  the improvements suggested earlier in this section, will likely be
successful in identifying sites that should be eligible  for the  NPL.  These  members
believe that more intensive and expensive risk assessment should not be undertaken at
each  of the many contaminated sites that EPA may consider in  each year but, rather,
should be  undertaken only after EPA has decided that a site should be proposed for NPL
listing. Furthermore, these members observed that the cost and regulatory uncertainty
that would accompany any sort of reconsideration  of the  basic MRS model most likely
would be a significant drain on the Superfund budget and  other EPA  resources, thereby
0 Subcommittee member Vicky Peters supports the use of site-specific data in the HRS
with the caveat that she does not believe that exposure default assumptions generally
lead to over-estimated risk and she therefore  believes  that listing should not be
delayed in order to obtain such site specific data. See Attachment A for Ms. Peters'
individual statement.

R Subcommittee member Richard Stewart supports this view.  See Attachment A for
Mr. Stewart's individual statement.
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potentially reducing the  funding available for cleanups,  and could impede  EPA's and
states' abilities to obtain cleanup commitments from PRPs.s T
Cautionary Note to All NPL Listing Recommendations
The Subcommittee has chosen to address the question of "What sites belong on the
NPL?" by recommending improvements to the current NPL listing process. However, this
is not to suggest that EPA should delay listing a site that obviously will not be adequately
addressed by a non-NPL program. EPA retains sole discretion to make decisions about
which sites to list on the NPL. The recommendations made by the Subcommittee are not
intended  and should  not be interpreted  to limit  that discretion.  The Agency  has  a
responsibility to make listing decisions and to get  NPL sites cleaned up in a timely and
efficient manner, in accordance with  promulgated  procedures and based on credible
technical evidence.

In addition, the Subcommittee is not advocating that EPA redirect major resources from
on-the-ground cleanup activities to these reforms,  or develop significant new systems or
guidance.u  Because these reforms represent improvements to existing procedures, the
Subcommittee expects that the  Agency can accomplish them using  existing program
administration resources.
How Should EPA Make Its Decisions about Screening,
Assessing, and Listing Sites More Transparent?
 The Subcommittee  understands that EPA and its  partners  in  state environmental
agencies and local and Tribal governments must have the ability to exercise professional
discretion and wisely use public resources in decisions about the number and types of
sites to list on the NPL.  However, they should not exercise this discretion in a vacuum.
These groups have a responsibility to  ensure that the implications of their decisions are
understood by those who are most affected by  them—namely, the communities around
potential NPL sites, the parties who are responsible for cleanup, and the state, local, and
Tribal environmental programs to which communities and PRPs most likely will turn when
s Subcommittee member Jim Derouin feels that EPA Headquarters must make final
listing  decisions  because  it is  responsible  for  and, therefore,  must  be  held
accountable for,  overall  management  of the  Program;  and feels  that Program
management would suffer if this duty were delegated to the regions and/or states and
listing decisions were to be made without any regard to cost.  See Attachment A for
Mr. Derouin's individual statement.

T Subcommittee member Vicky Peters supports this (opposing) view of the HRS.  See
Attachment A for Ms. Peters' individual statement.

u Subcommittee member Jim Derouin believes that one efficiency problem facing EPA
is that it should direct, as a percentage of its budget, more funding to actual bricks
and mortar remediation. See Attachment A for Mr. Derouin's individual statement.
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a potential NPL site is not listed on the NPL. It is also important that such decisions and
the logic  for  them are transparent  to  the  public, Congress,  and other Program
stakeholders.

The Subcommittee recommendations on this issue are intended to bring a reasonable
level of transparency to EPA's decision  making,  and at the same  time  respect the
Agency's  discretion.   Recommendation  5 describes an  annual reporting process.
Recommendation  6 calls  for  EPA  to be  more  consistent and  informative  in  its
communication of decisions to screen sites out of the Superfund process.
    Recommendation 5:  EPA should improve the information and
    data on the Superfund Program and publish an annual report that
    presents key data on the Program, including program  progress and
    expenditures, anticipated costs, a summary of sites considered for
    listing, and the listing decisions and criteria applied.
The  Subcommittee relied heavily on EPA to provide data and  information about the
numbers of sites being addressed by the  Superfund  Program,  Program progress and
remaining cleanup obligations, estimates  of the  potential future cost burden to the
Program, and the numbers and types of NPL-eligible sites and NPL-candidate sites being
considered  by the Agency.   While the Agency was forthcoming with some of this
information, it was clear that often the information was produced with difficulty and at
considerable staff effort. Often it was necessary for  EPA officials to revise or correct
information  provided to the Subcommittee, to account for updated  data or to correct
errors in previous reporting.

The  purpose of information collected  by the Superfund Program should be  to inform
decisions and  allow the Program to  plan effectively by  spotting trends  before they
become crises.  The Subcommittee's  impression is that EPA decision makers do not
have  key Program management  information at their fingertips,  and even where that
information can be made available, it often must undergo extensive revisions for quality
control before it can be used. This seems particularly true with  respect to information
about (1) the types of site  conditions that  are driving  remedies  at listed sites, (2)  the
significant impediments to progress at so called "teenager" or pre-SARA sites, (3) the
numbers and types of potential  future NPL sites, and (4) program expenditures and
potential future  costs.   The  Subcommittee encourages  the Agency to increase its
understanding of these four data sets and to improve the quantity and quality of real-time
data available to EPA  managers and to the public on  these issues.  This is particularly
important for mega sites and potential mega sites, because of the potential of such sites
to dramatically affect Program funding  needs and priorities. (Recommendation 11 calls
for increased management  attention for mega sites.)  Increased use of Internet or other
web-based  systems may be  an  efficient  way  to make  real-time data more readily
available.
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In  addition, EPA should communicate the data it does have more freely and  openly.
Recommendation 5 calls for an annual report on Superfund Program accomplishments
and anticipated future costs. At a minimum, this report should include:

    -*  A summary of  program activities, progress at sites, and expenditures by fiscal
       year;
    -*  The status of listed sites including a summary of remaining work to be done and
       projected future costs; and
    -*  The NPL-candidate sites considered for listing, listing decisions made, and, if an
       NPL candidate  is not proposed for listing,  an explanation of the criteria  applied
       and reasons for this decision.

The Superfund annual  report should identify the sites (and associated future costs) that
EPA anticipates will be funded using the Superfund budget (i.e.,  costs for Fund-lead
actions) and the sites  (and  associated future costs) that the Agency  anticipates  that
PRPs will fund.  It also should show program  expenditures in intramural and extramural
cost categories. The Subcommittee recognizes that  EPA may have legitimate concerns
about maintaining the  confidentiality  sometimes necessary to  preserve the Agency's
enforcement discretion  and may need to structure  the report accordingly. However, the
Subcommittee does not believe that EPA should continue to keep confidential the names
and locations of NPL-candidate sites that the Agency chooses  not to list in any given
listing cycle.

The Superfund  annual  report should  consist  largely of  data and information that EPA
generates from its data systems, and should not be a glossy publication prepared using
many hours  of  EPA staff time  and extramural  resources.   In  past years  the Agency
produced under CERCLA Section  301(h)(1)  annual reports to  Congress on Program
progress.  These previous reports  are useful models for the Agency to consider as it
implements Recommendation 5.
    Recommendation 6: EPA should establish standard protocols to
    ensure that regional offices publicly communicate available information
    on site conditions and current and potential future threats to humans
    and the environment: (1) when a site is dropped from the Superfund
    site assessment process, and (2) when an NPL- candidate site is not
    proposed for NPL listing.
Recommendation 6 asks that in the future EPA improve the transparency of its decision
making and increase the information it makes available to the public at two critical points:
(1) when sites are screened from further assessment under Superfund, and (2) when the
Agency chooses not to list an NPL-candidate site.
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Sites Screened Out During the Superfund Site Assessment Process
Sites are screened from further consideration under Superfund mainly for two reasons:
(1) EPA determines that they will not achieve an MRS score of 28.5 or higher, and (2) a
number of other reasons cause eligible sites to be screened out, for example the site can
be appropriately addressed  under a non-NPL  cleanup  program, such as the RCRA
corrective action program, or because PRPs enter into a voluntary agreement to carry out
the cleanup.

EPA also might screen out an NPL-eligible site if the default assumptions and  underlying
presumptions  used in  the  MRS  model  are not  consistent  with  actual site-specific
conditions,  based on an evaluation  of the immediacy and significance of current and
potential threats posed by the site  and the number and types of receptors (humans and
environmental) that may be at risk. The Agency also might screen out an NPL-eligible
site if EPA headquarters review indicates  an error  in site characterization  or any other
problem with an MRS package, or if the EPA decision-maker for NPL listing, the Assistant
Administrator for Solid Waste and  Emergency Response determines in his  or her
judgment that a site does not warrant  listing.

Generally,  sites  that are screened  from  further assessment  are  reflected in EPA's
Superfund  information tracking  system (CERCLIS) as  "No Further  Remedial Action
Planned  under CERCLA" or "NFRAP."   Sometimes, particularly in the case of NPL-
eligible sites, sites  that are screened out are not reflected as  NFRAP  and instead are
tracked informally by the EPA regional offices for future consideration.

Although sites screened from further consideration have been judged by EPA to not
require  action  under  Superfund,  they  typically  are  not  contaminant free—some
environmental contamination  may be  present even if it does not rise to the level of being
a national priority under Superfund.  While the Subcommittee recognizes that minimizing
further expenditure of Superfund  resources at these  sites  is  important,  it  is also
concerned  that sites  screened from further assessment  under  Superfund may  be
misconstrued by some as being "clean," even when site conditions may pose threats to
humans  and the  environment.   To prevent such  misunderstandings,  EPA  should
communicate clearly and publicly about  the condition  and  status  of sites that are
screened from further consideration under Superfund.

NPL-Candidate Sites Not  Proposed for Listing
While the Subcommittee  recognizes and  affirms EPA's  need  to exercise professional
judgment and discretion in selecting which sites to propose for listing on the NPL, it
believes these decisions should be  transparent. EPA cannot assume that its decisions to
not list NPL-candidate sites will somehow change the fundamental equation that caused
the sites to be recommended  for listing in the first place.  Except in cases where PRPs or
others step forward to initiate and fund appropriate cleanup, the Subcommittee does not
expect that NPL-candidate sites will  be  addressed  by other environmental remediation
programs.  Generally  other  appropriate programs are considered  by regional offices
during the site screening process and, if another program is available and appropriate,
sites generally are  addressed by that program rather than recommended for NPL listing.
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Thus, EPA especially must communicate clearly and timely about its decisions to list or
not list NPL-candidate sites.

Standard Communication Protocols
Recommendation 6 advises  EPA to establish standard  protocols to ensure that in the
future regional offices communicate publicly and clearly about sites that are screened out
during the Superfund  site assessment process and NPL-candidate sites  that are not
proposed  for listing.  The Subcommittee discussed that these standard communication
protocols  would  apply  to future  decisions to screen sites  out  of the Superfund  site
assessment process and future decisions about NPL-candidate  sites.  Communication
should focus on the known interested parties associated with  a site,  such as state
environmental agencies, Tribal and local governments, potentially affected communities,
and known PRPs.  EPA's efforts to provide opportunities for stakeholders to  become
involved earlier in the  site  assessment process will assist the Agency in  identifying
interested  parties (Recommendation 3).  Communication should  state  explicitly that the
site has not  been determined to be clean (unless it  has);  should  include whatever
information is readily available about the types and concentrations of contaminants likely
to be  present, the environmental  media  affected,  the potential receptors, on going
cleanup efforts under other  programs,  if any,  and other  relevant site conditions;  and
should explain EPA's  reasons for screening the site from further consideration under
Superfund or,  in  the case of an NPL-candidate site, deciding not to  propose the site to
the NPL.

When  determining  the most appropriate  communication  mechanism,  EPA  should
consider whether there are ongoing efforts by other parties to address sites, and whether
there are ongoing stakeholder and community involvement efforts.  For example, where a
state  environmental  program  is adequately  addressing  a site and is appropriately
involving stakeholders, the best communication method may be to post  information about
the site assessment process and the decision to screen out a site on  the EPA website
and work with the state  environmental program to notify stakeholders  of the availability of
this information.   Where there are not ongoing efforts, more direct communication to
individual stakeholders is particularly important.

The  Subcommittee emphasizes  that  EPA should  avoid  duplication  of effort  and
duplicative (and potentially confusing) communication with stakeholders where effective
communication  is  already  taking  place,  and  that  EPA  should  implement  this
recommendation using the least costly communication methods that are effective.  This
point was  particularly important to some Subcommittee members who  believe that EPA
should carefully limit the amount of resources it devotes to reports on sites that are a low
priority or are being adequately addressed  under non-Superfund programs.v  These
members stress that EPA should apply Recommendation 6 to future decisions, and not
v Subcommittee member Mel Skaggs  addresses his concerns about  the  potential
cumulative budgetary impact of the many new processes, surveys, committees, and
studies discussed throughout this report in his individual statement.  See Attachment
A for Mr. Skaggs' individual statement.
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divert Program resources to additional reports on the over 43,000 sites that have been
screened out of Superfund to date.
w
What Should Be the Relationship of Other Programs to the
NPL?
In 2002, in  response to  questions posed  by the Subcommittee, EPA surveyed the
regional offices about their efforts to consider other programs during the site screening
and assessment  processes.  All ten EPA regional offices confirmed that they convene
meetings of a Regional Decision Team or similar body to  coordinate evaluation of which
sites most need  to be addressed using the NPL and  which  might  be appropriately
addressed using a non-Superfund cleanup  program.   However, the non-Superfund
alternatives considered and the methods and nature of  this analysis  vary significantly
among regions.  Nine regions reported routine meetings with state program managers to
coordinate cleanup priorities;  seven  reported similar  meetings  with the  Superfund
removal program; and three reported routine meetings with other EPA programs, such as
the RCRA corrective  action program.   The regions also reported that they consult
informally with these programs before proposing  a site to the NPL, and eight regions
reported  that they  also  consider other federal  agency response  programs  before
proposing a  site  to the NPL, such as  those of the Departments of Defense and the
Interior.

The Subcommittee  had extensive discussions about the role that other cleanup programs
should play  relative  to the  NPL.  The  primary  outcome of these  discussions  was
recognition that other cleanup programs should work in harmony with the NPL, and that
both a strong, functioning NPL  program and strong, functioning non-Superfund cleanup
programs are needed to address the  full  range of contaminated sites and cleanup
challenges that exist in this country. A strong NPL program is important, in part, because
it serves  to strengthen other cleanup programs, particularly state programs, by providing
a strong enforcement mechanism if progress is  not made.  A  strong, well-financed
Superfund enforcement program can increase cleanups and reduce the need for federal
funding.

The second outcome of the Subcommittee deliberations on other programs was a desire
to ensure that to the extent other programs offer authorities, processes, or funds that will
facilitate  cleanup of NPL-eligible sites,  these "tools" are known and  available to EPA
regional offices.

The Subcommittee identified several ways  in which non-Superfund cleanup programs
might work in harmony with the NPL and NPL cleanups.
w Subcommittee member Vicky Peters agrees that EPA should not spend its resources
tracking sites that would not qualify for the NPL. See Attachment A for Mr. Peters'
individual statement.
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Supplemental Funding.   A non-Superfund program might provide sources of funding
that  could  be  used to supplement funding under  Superfund.   For  example, the
Subcommittee discussed whether, under some circumstances the U.S. Army Corps  of
Engineers,8  might provide funding for environmental dredging in  ways that may
complement  an ongoing  Superfund  cleanup.   The programs considered  by the
Subcommittee  in general  do  not  have  resources  adequate to independently fund
expensive NPL-caliber cleanups. At the same time, any potential for additional resources
at specific sites should be seriously considered and carefully investigated, especially in a
time of funding challenges when even  a  relatively small amount  of additional  funding
might make a difference at a particular site.   In cases where funding  is provided at a
Superfund site by another government Agency, it is critical that EPA retain the authorities
it already has under CERCLA, which ensures that cleanups are protective of human
health and the environment.

Additional Cleanup Authority^  Authorities from non-Superfund programs might  be
used in combination with the Superfund Program to provide additional cleanup authorities
or strategies  to augment a Superfund cleanup.   These coordinated approaches have
been used at a  number of Superfund sites, such as the Grand Calumet cleanup, and are
currently  being piloted under EPA's and the U.S. Army Corps of Engineers' Urban Rivers
Restoration Initiative and Land Revitalization Agenda.7

Supplemental  Administrative Oversight and Enforcement^   Some non-Superfund
programs might provide a viable  alternative administrative framework under which
cleanup  activities at a site  could  be appropriately  overseen or enforced so  that a
Superfund action is not necessary.  For example, Superfund already has a policy  of
deferring  responsibility for cleanup to the  RCRA corrective action program, where that
program applies.9 Use of a non-Superfund program to oversee or enforce cleanup might
also be appropriate where site investigations  and cleanup activities will be funded by
PRPs and a state program can provide appropriate oversight of the PRP cleanup.  Again,
to the extent that non-Superfund programs can provide  appropriate oversight of cleanup
of NPL-eligible sites and have the capacity (staff, authorities and resources) to carry out
this  oversight,  they  are  important  alternatives  and  their use  will  allow  Superfund
resources to be directed only toward sites where such resources are most needed.

This section describes the Subcommittee's consensus recommendations  on three ways
for EPA improving  EPA's coordination with non-Superfund  programs (Recommendation
7), and encourages EPA to continue to invest in building the capacities of state and Tribal
environmental  programs  (Recommendation  8).   This  section  also describes the
Subcommittee's deliberations on three issues  about which it did  not reach consensus:
the circumstances under which non-Superfund programs should be used at NPL-eligible
sites, the circumstances under which available funds from non-Superfund  programs
should be leveraged at listed NPL sites,  and whether technical assistance grants should
be available at certain NPL-eligible sites that are not proposed for listing.
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    Recommendation 7: EPA should  (1)  ensure that regional offices
    have knowledge and understanding of the capabilities and applicability
    of non-Superfund  programs; (2) develop relationships with key
    managers in other programs, particularly federal programs, to facilitate
    coordination; and  (3) promote greater standardization of coordinating
    mechanisms, particularly for large, complex sites.
Recommendation 7 calls on EPA to improve its coordination with other programs in three
areas:  information and knowledge, relationship building, and coordinating mechanisms.
As described earlier, the Subcommittee also discussed, but did  not reach  consensus on,
a recommendation that  EPA should consistently consider non-Superfund programs to
address all or portions of NPL-eligible sites. Some Subcommittee members felt strongly
that  EPA should  consider  and,  where  appropriate, ensure  use  of non-Superfund
programs for NPL-eligible sites.x Other members were uncomfortable with use of non-
Superfund programs unless such programs meet or exceed Superfund standards. The
Subcommittee's range of views on this issue is described more fully later in this section.

Information, Knowledge, and Relationship  Building
EPA should ensure that states, regions, and other interested parties have easy access to
accurate, up-to-date information about the strengths, weaknesses,  and  capabilities of
other federal  programs  that undertake cleanups or activities  that  might result in or
contribute to cleanups (and therefore potentially complement Superfund activities).  EPA
also  should  provide  support  for regional project  managers  who wish  to  consider
coordination or  collaboration with  such programs.   This will assist regional offices in
determining whether and how non-NPL programs might be appropriate for a specific site.

Similarly, other agencies' knowledge of Superfund should be improved so  they can more
effectively plan  their activities  to be complementary  to Superfund cleanup objectives.
EPA should identify other programs with a potential to be  useful at Superfund sites, and
should  make an effort to educate staff in EPA and in the other programs about potential
opportunities for, and benefits of, working together.

When it can be done without diminishing EPA's core mission to protect human health and
the environment, EPA should explore options such as memoranda of agreement or other
arrangements with  non-NPL programs to further coordination  and  ensure that  EPA's
statutory authorities under CERCLA are not impaired/
x Subcommittee member Richard Stewart supports this view. See Attachment A for
Mr. Stewart's individual statement.

Y Subcommittee  member  Mel Skaggs  summarizes  one  such application  of  a
memoranda of understanding,  between  USEPA and USAGE in the  Urban Rivers
Restoration Initiative pilot program, in his individual statement. See Attachment A for
Mr. Skaggs' individual statement.
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Greater Standardization of Coordination Efforts
EPA should establish guidelines for consideration of non-Superfund programs.  Such
guidelines should not impede the discretion of EPA to list a site as soon as it determines
listing is warranted, but should also emphasize the potential usefulness of non-Superfund
cleanup programs where they can provide oversight or other resources to appropriately
clean up sites.

For most sites, the Subcommittee favors an approach that advises EPA to achieve the
outcomes of coordination,  but  leaves  to  EPA  and its  partners  the responsibility of
determining how best to achieve those outcomes.  It seems likely that the  most efficient
means  for  EPA  to  accomplish  the  coordination  outcomes  recommended  by  the
Subcommittee by improving the regional infrastructures for coordination where they exist
(for example, Regional Decision Teams) or by creating new regional mechanisms,  rather
than establishing a new standardized, national mechanism.  (Note that in the description
of the Subcommittee deliberations on Recommendation 3, the Subcommittee observed
that  it may be necessary to establish  national guidance  on coordination  or take other
steps to further coordination goals.)

The  exception to this  general  principle is mega sites,  for  which  the Subcommittee
believes that a more formal, standardized approach is warranted.

The  Subcommittee  had extensive discussions  about  the  exact  form that this  more
standardized  approach to  coordination for mega  sites should  take and  discussed at
length  the  concept of a  "coordinating committee" to  accomplish coordination  goals.
Some Subcommittee members strongly supported a coordinating committee as a way to
formalize and routinize coordination practices.2   Other members were concerned  that a
coordination committee might impede EPA's discretion to  make listing decisions.  In the
end, the Subcommittee did not reach consensus  about whether such committees should
be established or, if established, the "level" at which a coordinating committee for mega
sites should operate (e.g.,  national, regional, or site-specific),  the individuals who  might
serve on such a committee, and whether a committee  should serve as an information-
sharing  venue  only  or should  offer non-binding  recommendations to  EPA decision
makers.

Despite its diversity of views, the Subcommittee  did reach consensus on both the need
for increased, formalized coordination on large, complex sites  and on a number of goals
for such a coordination effort, as follows:

    -* Coordinating  mechanisms should provide a forum for  evaluating large, complex
       and  expensive sites and  sharing  and  soliciting  information  with and from
       interested parties in a way that enables EPA to make  more fully informed  listing
       decisions.
z Subcommittee member Richard Stewart supports this view. See Attachment A for
Mr. Stewart's individual statement.
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    -* Coordination   should   be  carried  out  transparently,   and  should  provide
       opportunities  for  involvement  by officials from  other  programs, PRPs, site
       neighbors, affected communities, and other interested groups and individuals, by
       reaching out to them to share and solicit information.
    -* Coordinating  mechanisms should not constrain EPA's discretion to make NPL
       listing decisions.   EPA alone  is  responsible  for listing  decisions, and has a
       responsibility  to make such decisions in a timely and efficient way in light of site-
       specific data  that EPA determines is  available and  reliable.  (Note  that while
       Subcommittee members  agreed on  this point, they  did  not agree on whether
       coordinating   committees,   if   established,   should   offer   non-binding
       recommendations or function solely as information-sharing venues.)

In addition, some Subcommittee members believed that coordinating mechanisms should
have as one of their goals evaluating the challenges and opportunities presented by large
complex  sites  and ensuring  that the capacity of  other cleanup programs to  provide
oversight and funding inappropriately considered. Other Subcommittee members did not
support this view,  largely because of their concern about the  use  of non-Superfund
programs that might not meet  or exceed Superfund standards.  (This issue is  discussed
further in the description on the Subcommittee's  range of views  on the  use  of non-
Superfund programs.)
    Recommendation 8: EPA should continue to invest in capacity
    building for state and Tribal cleanup programs.
The  Subcommittee  considered  a  great deal of information on the range  of cleanup
programs among the states, including the Environmental Law Institute's Analysis of State
Superfund Programs:  2001 Update.  The  ELI  analysis is  a  compendium of statutes,
program  organization,  staff, funding,  cleanup  standards and  activities, enforcement
provisions, and amount of money spent on cleanup for all 50 states.10 Given the array of
individual state capacities  and the challenges faced  by state  programs (e.g., declining
state budgets), the Subcommittee urges EPA to continue its efforts to build the capacity
of state remediation programs.  Less  is  known about Tribal  environmental cleanup
programs, many of which are still in the early stages of program development.

While states and Tribal Nations do not have the resources  to independently pay for
cleanup at most  NPL-caliber sites, building capacity within state and Tribal programs to
continue to fund cleanup at smaller, lower-risk sites and to oversee PRP-lead cleanup is
essential to  maintaining  a strong national  Superfund program.   Using  information
available in the ELI analysis, EPA should evaluate and consider ways to build capacity in
states and Tribal  Nations that have:

    -*  A significant number of unaddressed or unevaluated sites;,
    -*  Insufficient cleanup programs; or
    -*  Ineffective use of enforcement authorities or prevention programs.
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EPA should particularly continue to invest  in capacity building  for interested Tribal
Nations, to enable them to address more sites under their jurisdictions.

While exact capacity building activities will depend on the needs of the state or Tribal
Nations in question, they might include many  of the activities EPA already undertakes to
assist state and  Tribal  programs, such as federal grants, education  and  training, and
technical support.

Special Consideration of State Programs
Virtually every state has some form of cleanup program.  Many states have multiple
programs, including brownfields programs, voluntary cleanup programs, property transfer
programs, and state programs modeled  after the federal Superfund Program.  State
cleanup programs are  an  important piece of the cleanup puzzle.   They serve  as a
complement to the national Superfund Program by providing for the cleanup of many
sites that are  not eligible for the NPL and, in some cases, by providing administrative
mechanisms to oversee cleanups at sites that would be eligible for the NPL.  Collectively,
state programs have addressed many thousands of contaminated sites - including some
NPL-eligible sites - and it is expected they will continue to do so.

Subcommittee  members had  very divergent  views  about  the  range  of cleanup
approaches, strengths, weaknesses, and capacities across state  programs.  Many
Subcommittee  members had direct experience with various state programs and believe
that EPA should consider a  study  to evaluate the  strengths and weakness of  state
approaches and to consider the relevance of these approaches to the  federal Superfund
Program. Other  Subcommittee members were concerned that state programs may not
have the resources or authorities to adequately provide for or oversee the cleanup  of an
NPL-eligible site, or were concerned that state  programs may not meet or exceed  NPL
standards and therefore should not be used at NPL-eligible sites.
   Deliberations on Ensuring Consideration of and
Coordination with Non-NPL Programs

The Subcommittee considered but did not reach consensus on a recommendation that
would call for EPA to ensure that regional offices consistently evaluate the availability of
state cleanup programs and non-Superfund federal programs to clean up all or portions
of NPL-eligible sites and to encourage use of such programs where they can provide for
appropriate cleanup (either with funding or through oversight of PRP-funded actions).

The Subcommittee's lack of consensus  on  this matter turned on the  issue of what
standards or procedures non-Superfund programs should use to appropriately clean up
all or a portion of an NPL-eligible site.  Subcommittee members had very strong views
about what  it means for anther program to  "appropriately" clean up an NPL-eligible site.
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Some Subcommittee members believe that non-Superfund programs should be used at
all  or  portions of NPL-eligible  sites  only  where  such programs  meet  or exceed
Superfund's protections for public health, community participation, environmental quality,
liability, and other vital, health-protective standards. These Subcommittee members also
were concerned that allowing for use of non-Superfund programs at all or portions of an
NPL-eligible site could result in (1) passing responsibility for cleanup to programs that are
ill-equipped to  handle an NPL-eligible site, (2) weakening protections to humans or the
environment, or (3) transferring cleanup costs to taxpayers.

Other Subcommittee members believe that a wide range of procedures can be used to
achieve a remedy that adequately cleans up a  site.  These members cautioned against
an  approach that  would require non-Superfund programs to be  operationally like  the
Superfund Program to adequately clean up all or portions of NPL-eligible  sites.  They
emphasized that all  cleanup programs,  including Superfund, have both strengths and
weaknesses.   Non-Superfund programs exist under  their own statutory constructs,  are
designed to achieve their results in manners consistent with their respective statutory
purpose, and do not have to emulate Superfund's process in order to achieve outcomes
that will result in protection of human health and the environment with meaningful public
involvement.   Further, these members  noted  that, wherever cleanups are  performed
under other statutes,  EPA retains its authority  under Superfund should it be needed if
non-Superfund programs are not acting appropriately.AABB
   Deliberations on Leveraging Non-Superfund Program
Resources

The Subcommittee considered but did not reach consensus on, a recommendation that
would have  advised  EPA  to  use its understanding  of non-Superfund  programs and
relationship with key mangers  in non-Superfund programs to optimize and leverage the
use of any available resources from these programs to meet EPA's obligations at NPL
sites. cc

The  example  of how this  leveraging  might work  most  often  discussed  by the
Subcommittee  was normal dredging activities  carried  out by the U.S.  Army Corps  of
Engineers.  If properly carried out and coordinated with Superfund, the  mobilization  of
AA Subcommittee member Richard Stewart supports this view.  See Attachment A for
Mr. Stewart's individual statement.

BB Subcommittee member Vicky Peters disagrees with this statement. See Attachment
A for Ms.  Peters'  individual statement and  for the individual  statement  of  Doris
Cellarius. Ms. Peters' agrees with Ms. Cellarius' views on this issue.

cc Subcommittee member Vicky Peters supports  leveraging of funds from  other
programs with the understanding that such funds would be used at taxpayer funded
cleanups or, as appropriate, to fund "orphan shares", not to supplant responsible
parties' liability. See Attachment A for Ms. Peters' individual statement.
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people and equipment associated with these activities could serve "double duty" by also
dredging or conducting  other activities beneficial to a Superfund cleanup, so long as
EPA retains its authorities under CERCLA to ensure that cleanups protect human health
and the environment.DD  The Subcommittee also considered the economic opportunities
that  may  be  associated  with  NPL  sites at  or near areas  being  proposed for  re-
development.

The Subcommittee also discussed that, for routine activities carried out by non-Superfund
programs to complement cleanup of an  NPL site,  project managers in other programs
may have to  work with project managers from the Superfund Program to coordinate
standard protocols and decision making.  The  Subcommittee discussed that EPA may
wish to explore memoranda of agreement or other arrangements with non-NPL programs
to facilitate such coordination.

In the  end, the Subcommittee  did not reach  consensus on  a recommendation about
leveraging resources from non-Superfund  programs,  largely because of its inability to
reach consensus on what standards or  procedures a non-Superfund programs should
use to appropriately clean up all or a portion of an NPL-eligible site. As described above,
some Subcommittee members believe that non-Superfund programs should be used at
all or  portions  of NPL-eligible sites only where such programs  meet  or  exceed
Superfund's protections for public health, community participation, environmental quality,
liability, and other vital, health-protective standards.  Other members believe that a wide
range of procedures can be used to achieve a remedy that adequately cleans up a site.
   Deliberations on Expanding Technical Assistance Grants

The  Subcommittee  also considered  but  was  unable to  reach  consensus  on  a
recommendation dealing with technical assistance grants orTAGs.

Some Subcommittee members wanted  to recommend  that EPA enable TAGs to be
given, where appropriate, to groups of individuals affected by NPL-eligible sites that are
not listed.  These members were comfortable that EPA's rulemaking authority gives the
Agency the discretion to extend the availability of TAGs in this way.  CERCLA provides
that the "President may make grants available to any group  of individuals which may be
affected by a release or threatened release at any facility which is listed on the National
Priorities  List  under the  National Contingency  Plan"  (42 U.S.C.  9617(e)).   Some
Subcommittee  members believe that this provision does  not preclude EPA from making
such grants available to other groups.  They noted that current EPA regulations regarding
TAGs already interpret CERCLA to allow grants at sites that are not listed on the NPL but
that are proposed for listing (40 CFR 35.4020(a)(1)).
DD  Subcommittee  member  Mel  Skaggs  addresses  one  such  approach  using
memoranda of understanding, between USEPA and USAGE  in the  Urban Rivers
Restoration Initiative pilot program, in his individual statement.  See Attachment A for
Mr. Skaggs' individual statement.
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Subcommittee members who support EPA's expanding the availability of TAGs believe
that such an expansion will further increase the capacity of state and Tribal cleanup
programs, by improving the  ability  of affected communities  to participate in cleanup
actions.  They do not argue that TAGs be provided for every contaminated site.  Rather,
these members believe TAGs should be considered only for NPL-eligible sites that, in the
absence of another acceptable cleanup program, would need to be listed and remediated
under CERCLA.  Under this approach, TAGs for non-NPL sites would only be available
when TAG  funding  exceeds  requests for TAGs  at  listed sites.    Relatively  few
communities desire a TAG, but where the public believes having one is essential to their
comfort with the  cleanup process, provision of a TAG at an unlisted, NPL-eligible site
could facilitate public buy-in to a non-Superfund cleanup program and thereby conserve
Superfund Program resources.EE

Other Subcommittee members  were unwilling to support a recommendation  that EPA
expand  the  availability of TAGs,  believing that such an  expansion  could  not  be
accomplished without  a statutory  change and that recommending such a statutory
change was beyond the  scope of the  Subcommittee.  These  members were also
concerned that expanding the TAG program to non-NPL sites could  further decrease the
money available  to carry  out cleanups at  NPL  sites,  counter to  many  of the
Subcommittee's other recommendations in this report.FF
How Should EPA Set Priorities Among Listed Sites?
The Subcommittee considered, but did not reach consensus on a recommendation that
EPA should set priorities for funding at sites listed  on the NPL by using a rigorous and
transparent process based primarily on threats to humans and  the environment, but also
taking into consideration socioeconomic and program management factors.

Some Subcommittee members believe that any site listed on the NPL is by definition a
national priority, and should be investigated and cleaned up  in a timely fashion.  For
these members, prioritizing among such sites creates very difficult choices,  as  the
selection of any site or activity  for action may  mean  another site will not  receive
resources and may  remain a threat to human health  and  the  environment.  These
Subcommittee members believe that such choices should be  made in  consideration of
both threats to humans  and the environment and program management considerations
and that, in some instances, programs management considerations (such as maintaining
a strong enforcement program or  seizing  an opportunity to leverage funds from a non-
Superfund program) could significantly influence priority setting.
EE Subcommittee member Vicky Peters supports expanding the availability of TAG's.
See Attachment A for Ms. Peters' individual statement.

FF Subcommittee member Richard Stewart supports these views. See Attachment A for
Mr. Stewart's individual statement.
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Other Subcommittee members disagreed with this view. They recognize that decisions
about prioritization could be very difficult, and agreed that EPA should consider threats to
humans and the environment and program management considerations.  However, they
also believe that information on actual threats to humans and the environment should be
used to guide difficult priority choices and that addressing ongoing threats to humans
should be the Agency's highest priority.GGHH

Differences in views about how EPA  should set priorities for funding sites listed  on the
NPL were complicated by the  Subcommittee's  differences in views about the types  of
sites that should be listed in the first place.   Some Subcommittee members believe that
EPA's  current approach to making  decisions about  NPL eligibility—which relies  on the
MRS as a screening tool to identify eligible sites and the professional judgment of EPA
decision  makers to identify which  eligible sites to  propose for listing—is  appropriate.
Furthermore,  these members believe that more intensive and expensive risk assessment
should be undertaken only at the eligible sites that EPA decides to list on the  NPL.

Other Subcommittee members disagree with these  views.  Some of them believe that
EPA should make decisions about which sites to list  by evaluating the actual risks posed
by  sites  to people and the  environment, i.e.,  an  approach akin to risk assessment.
Others believe that the MRS allows too many sites to become eligible for NPL listing and
that, because a wide range of sites  are eligible,  EPA has too much  discretion to choose
to list sites that may not present current threats to people or the environment."
    Deliberations on Principles for Priority Setting

In the context of its divergent views, the Subcommittee recognized the practical reality
that EPA most likely will continue to have to set priorities for spending at NPL sites.  The
Subcommittee discussed but did not reach consensus on a set of principles that might be
used to guide priority setting.

During these deliberations, some Subcommittee members supported use of the following
principles to guide priority setting.JJ
GG Subcommittee member Jim Derouin believes that, to assure both the integrity and
the efficiency of the Program, the Agency must adopt a "worst first" priority approach
that assures that funds are directed to those sites, and those portions of mega sites,
that pose  the  worst human  health risks/exposures.  See Attachment A for Mr.
Derouin's individual statement.

HH Subcommittee member Richard Stewart supports this view. See Attachment A for
Mr. Stewart's individual statement.

11 Subcommittee member Richard Stewart supports this view.  See Attachment A for
Mr. Stewart's individual statement.

N Subcommittee member Vicky Peters supports these principles.  See Attachment A
for Ms. Peters' individual statement.
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    -* The primary question  EPA  should evaluate when  considering  priorities for
       funding is "What is the consequence of delaying remedial action?"  While this
       question may be implied in EPA's current prioritization process,  it  is necessary
       for the Agency to consider it explicitly, and weigh the consequences thoughtfully
       at each site. In  some cases, such implications could be on-going unacceptable
       risks, or a  lost  opportunity  to  leverage  activities and  resources from other
       programs.   In others,  delay could allow  contaminant migration and result in
       greater and  more significant contaminated natural resources, and  greater risks to
       future  populations who should be  afforded equal protection as that provided
                                 KK
       current exposed  populations.
    -* Priorities should be set remedial action  by  remedial action.   EPA's  current
       practice is to prioritize remedial actions, not entire  releases or sites.  Thus, one
       remedial action  at one  site may rank  as  a high  priority and be provided with
       funding, while  others  at  the same site wait for later  funding cycles.  The
       Subcommittee concurs with this  practice, which can be particularly important at
       large, complex sites with discrete remedial activities.
    -* Any prioritization should be conducted  with meaningful participation by affected
       stakeholders, who should  be  consulted regarding the considerations that should
       determine the prioritization of remedial activities  at  their site, the  conclusions
       reached based  upon input provided, and any ultimate  prioritization decisions.
       This transparency is critical  in  order  to improve  decision making and foster
       greater acceptance of decisions by the public.
    -* Setting  priorities is about deciding which remedial actions to fund first.  It is not
       about re-defining cleanup outcomes. All NPL listed sites must be cleaned up so
       that humans and the environment are fully protected  as required  by law.  Every
       NPL site should  be cleaned up within a reasonable timeframe.
    -* Considerations  for setting priorities for  remedial actions  may differ from those
       applied to removals.  For example, a removal action to provide  an  alternate water
       supply  to  individuals  currently  exposed  to  significantly elevated  levels of
       contamination may be a very high priority for the removal program. However, the
       restoration of the contaminated aquifer may rank lower than prophylactic or other
       remedial measures that could be taken elsewhere where exposure  pathways
       cannot be intercepted.
    -* No prioritization  process should assume its outcome.  While as a practical matter
       it  may be rare  that threats to a  sensitive ecosystem would be  given a higher
       priority than ongoing threats to humans,  such an outcome is possible, depending
       upon the facts presented.

Other Subcommittee members did not support these principles, arguing that they would
not offer EPA enough guidance on how it should approach difficult choices and/or that
KK Subcommittee member Richard Stewart believes that EPA should not focus solely
on the consequences of delaying remedial action at given sites, but must balance
such consequences against the consequences of not using the funds for clean up at
other sites  that may present greater risks  to  health  and the  environment.  See
Attachment A for Mr. Stewart's individual statement.
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they allow for the  possibility that environmental  concerns could be  prioritized  over
ongoing threats to humans.LL
    Deliberations on Factors for Priority Setting

Similarly, in the context of its divergent views about the types of sites that should be listed
on the NPL, and the role that evaluation of ongoing threats to  humans should play in
priority setting, the Subcommittee discussed a set of 16 factors  divided into 2 tiers that
EPA might use to guide priority decisions.MM

Tier 1 included primary factors, those most  closely related to threats to humans  and the
environment and  source control.   Tier 2 included secondary  factors, those largely
associated with socioeconomic issues and program management concerns.
Some Subcommittee members supported consideration of the  following factors to set
priorities among listed sites, noting that they are drawn in large part from EPA's current
priority-setting  practices, as outlined  in the guidance memo "Remedial Action Priority
Setting" (January 19, 1996).11

Tier 1:   Primary Factors Related to  Threats to Humans and Significant
Environments and Source Control
Human Receptors
    -*  Threats to human  population  exposed:  These include  population size and
       proximity to contaminants.
    -*  Likelihood of exposure if no remedial action is taken:  This includes consideration
       of the  stability of contaminants, reliability of any  containment structures, and
       effectiveness of any institutional or physical controls.
    -*  Nature of likely exposure: This includes consideration of whether an exposure is
       currently occurring or is a potential future occurrence and whether exposures are
       acute or chronic.
    -*  Sensitive receptors or exposure pathways: These include receptors with  multiple
       chemical exposures  or other confounding  factors and  receptors that may be
       exposed via multiple exposure pathways.
    -*  Contaminant toxicity:  This includes toxic and carcinogenic effects, volume, and
       contaminant concentrations.
LL Subcommittee member Richard Stewart supports this view. See Attachment A for
Mr. Stewart's individual statement.

MM Subcommittee member Vicky Peters supports the application of these factors. See
Attachment A for Ms. Peters' individual statement.
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Significant Environments
    -* Threats  to  ecological  receptors:   These  include  threats  to  threatened or
       endangered species and their critical habitats, keystone species, migratory birds,
       amphibians, fisheries, and other sensitive ecological receptors.
    -* Threats  to environmental  receptors:  These include  threats to ground-water
       aquifers  and other significant natural resources.

Source Control
    -* Remedial actions that result in control of ongoing sources of contamination are
       particularly  important  because  of their potential to  reduce overall  cleanup
       burdens  and costs.

Tier 2:  Secondary Factors Related to Program Management
    -* Environmental  justice factors:   These  include factors at sites that affect Tribal
       interests, treaties,  statutory requirements  (e.g.,  American  Indian  Religious
       Freedom Act) and trust responsibilities.
    -* Maintaining  a  strong  enforcement  presence:   One  of the benefits of the
       Superfund Program is that the mere possibility of a Superfund action may prompt
       responsible parties to initiate and fund cleanups, reducing burdens on the limited
       public funding  available.  Because these cleanups are often initiated and then
       overseen under  state  environmental remediation   programs, a strong,  vital
       Superfund program is also important in maintaining strong, vital state programs.
       For this  benefit to continue, the  threat of Superfund  action must continue to be
       real.  Consideration of this factor may cause  EPA to  elevate the  priority of sites
       that, based strictly on an  evaluation of threats, may  present  less concern than
       other sites.
    -* Evaluating short- and long-term implications:  A focus on controlling sources and
       addressing current human exposures does not obviate the need to address other
       risks  and  remaining contaminants.   On  a site-by-site  basis,  delaying  site
       investigation and cleanup will increase overall site costs and increase social and
       opportunity costs to communities that must tolerate  contaminated sites longer,
       even  though they are not experiencing  current exposures.   This overall  cost
       increase at individual sites and in  individual communities  must be balanced
       against the dilemma that,  particularly in a climate of limited resources, the costs
       of failing to adequately address current exposures and ongoing sources at all
       sites may result in the growth of both adverse  human health impacts and cleanup
       costs.  In some cases, the cost savings of rapid action  may be dramatic, if it
       prevents migration  of contamination to, for example, additional  media, cultural
       resources, receptors, or sensitive ecosystems.  Evaluations  of short- and long-
       term   implications   should  consider  life-cycle   costs  related   to   prompt
       implementation versus postponement of planned activities, and any cost savings
       that might be achieved  by reducing  routine management costs associated  with
       maintenance of interim actions or  other controls that might be instituted in
       advance of final cleanup.
    -* Minimizing costs  associated with  mobilization and demobilization for cleanup:
       Cleanup strategies  should maximize  the  use of skilled and  knowledgeable
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       workers, labs, cleanup  contractors  and managers with institutional memory.
       Work flow logic in connection with other planned or ongoing activities should also
       be considered.
    -* Making  meaningful progress in all communities: Progress should be made in all
       communities, with a particular emphasis placed on  communities that have been
       disproportionately affected by environmental contamination.
    -* Leveraging activities that are already funded or have the potential to be funded
       by  other  programs:   The  ability to leverage funding  associated  with other
       programs  or activities may justify the assignment of a higher priority to a  site
       because it could lower overall costs.
    -* Advancing  knowledge of innovative  treatment technologies:  The development
       and implementation of new technologies at one or more sites could pave the way
       to their wider use  and greater cost  savings  at other sites  with  similar
       contamination.
    -* Support for cleanup: An important factor should be the degree of support from
       affected communities and from state,  local, and Tribal governments.

Other Subcommittee members were generally comfortable with the factors described, but
believed  they would not provide  useful guidance to the Agency without additional
information on how the factors should be applied. Again, in discussions of this issue, it
became clear that the Subcommittee did not agree on the role that evaluation of  risk
should play in determining EPA's actions under the Superfund Program.  Some members
believed that EPA should prioritize  ongoing  threats to  humans over other  threats  and
considerations.NN  Other Subcommittee  members strongly disagreed, believing that such
an approach would be contrary to CERCLA  and would abrogate EPA's responsibility to
ensure that cleanup protect both humans and the environment.

Some  Subcommittee members  thought  the factors  were  incomplete, and  should  be
expanded to include consideration of additional societal and economic factors,  such as
the potential negative impacts of requiring expenditures of taxpayer or private money for
unnecessary studies or cleanups. Other Subcommittee members strongly disagreed with
this view.
   Increasing Transparency in EPA's Decisions about Priorities

Although they had very different views about how EPA should set priorities for funding
among sites listed on the NPL, Subcommittee members  agreed that that EPA should
create  more openness and  transparency around decisions about setting priorities and
allocating  funding.   The current prioritization process  seems to occur entirely  within
EPA—without opportunities  for input even  from  the  Agency's  co-regulators  in state
NN Subcommittee member Jim Derouin believes that, to assure both the integrity and
the efficiency of the Program, the Agency must adopt a "worst first" priority approach
that assures that funds are directed to those sites, and those portions of mega sites,
that  pose the  worst  human health risks/exposures.   See  Attachment A  for Mr.
Derouin's individual statement.
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environmental agencies and Tribal governments. Without prescribing a specific process
that  EPA  should  use to  increase the transparency  of  priority-setting  decisions,  the
Subcommittee emphasizes that these  difficult choices and their implications should be
made using clear and understandable criteria and should be explained publicly.
   Setting Priorities at Other Stages in the Pipeline

The Subcommittee also discussed but did not fully resolve  issues associated with other
points in the cleanup pipeline at which EPA should set priorities. The outcome of these
discussions was an acknowledgment that EPA should be encouraged to look at the full
range of its site-specific activities in any given year when setting priorities, with the most
formal priority setting occurring for the most expensive activities (i.e., remedial actions).
This  emphasis is  not intended to diminish the importance of robust funding for other
pipeline activities.  In particular, EPA must continue to fund remedial investigations and
feasibility studies and other necessary site characterization activities at newly listed sites,
so that the Agency will have  more complete information upon which to base subsequent
priority-setting decisions.
Should EPA Reallocate Resources? If So, How?
The success of the Superfund Program depends both upon EPA's ability to manage and
direct human and financial resources efficiently and  upon having an  adequate  budget
consistent with  carrying  out the  Program's responsibilities.   The  Subcommittee
considered but was unable to reach consensus on a number of issues related  to how
EPA allocates Superfund Program resources and Program funding.
   Deliberations on EPA Spending Decisions

Overall and  as  a percentage of the total  Superfund  Program budget,  the amount of
money EPA spends for activities at specific sites has declined in  recent years.  The
Subcommittee believes this spending  trend should be reversed, so that EPA spends
more, rather than less, money on work directly related to improving public health and
environmental conditions at actual sites. While the Subcommittee agreed on this point, it
did not agree on two related points and therefore could not reach consensus on a specific
recommendation about how EPA should prioritize Superfund Program spending.

First, some Subcommittee members were unwilling to support a recommendation calling
for EPA  to  shift spending within  the Superfund  Program without a complementary
recommendation to increase the overall level of Program funding to address the backlog
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of remedial actions that are ongoing or ready to start but cannot proceed or must proceed
more slowly because of lack of federal funds. °°

Second, Subcommittee members did not share a common view about the types  of
activities that are directly related to improving public health and environmental conditions
at actual sites,  and that should therefore be the focus  of Program spending.  Some
members thought that EPA should spend a larger percentage of its budget on extramural
work at sites that are ready for remedial action, in order to complete remedial design and
construction at a greater number of NPL sites.pp   Others argued that removals and long-
term response actions are also critical elements  to improving site conditions and should
be included in any  recommendation about how  EPA should target Superfund Program
spending.

Other Subcommittee members stressed that funding should be increased for all activities
directly related to improving public health and environmental conditions at sites, including
removals,  remedial  actions,  long-term  response  actions, site  investigations  and
characterization, studies,  enforcement,  and other activities that are  necessary  to
preconditions  to the overall process of remedy selection and  implementation.  Still other
members stressed that increasing funding for cleanup would also increase  the need for
contract management and oversight activities, and that  activities by the Office of the
Inspector General  (OIG),  the Office of Research  and Development (ORD), and the
Department of  Justice (DOJ) and other necessary actions are all  important links  to
ensuring  that the  Superfund  Program  can adequately  protect  public  health  and
environmental quality.
   Deliberations on Auditing Superfund Appropriation Spending

The Subcommittee also considered  but did not reach consensus on a recommendation
calling  for a neutral,  independent audit of all  activities paid for with money  from the
Superfund appropriation.

The  Subcommittee could  not  reach  consensus on a recommendation for  an audit
because of its inability to reach consensus on a recommendation addressing the overall
funding level for the Superfund Program.   As described above, some Subcommittee
00 Subcommittee member Vicky Peters supports this view with the clarification that
increased funding  is necessary  because  reallocation  of insufficient funding has
resulted  in  bottle-necks elsewhere in the pipeline, decreased enforcement and
oversight, decreased research and development, and reductions in  other activities
essential to  an effective program, and because she believes the allocation would
likely change from year to year as various sites advanced through the pipeline and
important policy issues arose. See Attachment A for Ms. Peters' individual statement.

pp Subcommittee member Jim Derouin believes that one efficiency problem facing
EPA is that the Agency should direct, as a percentage of its budget, more funding to
actual bricks and mortar remediation.  See Attachment A for Mr. Derouin's individual
statement.
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members  were unwilling  to  support  recommendations  for an  independent  audit of
Superfund Program spending without a complementary recommendation to increase the
overall level of Program funding, at least temporarily, to address the backlog of remedial
actions.QQ

The  Subcommittee was aware that in the  2004 Superfund  appropriation, Congress
required  that  the  OIG  to evaluate  Superfund  Program  expenditures within  EPA
headquarters and in the regional offices, and to recommend  options for both increasing
resource  allocation to  extramural  funds  for cleanup  and  minimizing  administrative
         RR
expenses.   In general, Subcommittee members who supported a neutral independent
audit did  not view the OIG audit  as covering all of the audit elements that should be
addressed.  These additional  elements  include  consideration  of EPA's practice of
covering  budget shortfalls created by cost-of-living increases in federal salaries by
reducing  the extramural funding available to pay for cleanup,   and evaluation of the
numerous EPA offices  besides OSWER  that are partly funded with  money  from the
Superfund appropriation. Some Subcommittee members noted that these offices include
the OIG  and  believe  that  if an audit  is carried out, it should be comprehensive and
conducted by a truly independent, neutral third party.
   Deliberations on Contract Reforms

The Subcommittee also considered but did not reach consensus on a recommendation
advising EPA to pilot a number of specific contracts reforms, such as guaranteed, fixed-
price  remediation contracts;  indefinite quantity  contracts with  guaranteed  minimums;
incentive based contracts; and requirements contracts.

As with the neutral, independent audit of the Superfund appropriation, the Subcommittee
could  not  reach  consensus on a recommendation on  pilot testing  contracts  reforms
because of its inability to reach consensus on a recommendation addressing the overall
funding level for the Superfund Program.ss
00 Subcommittee member Vicky  Peters believes that although the OIG  and the
independent review by a high-level official in the Air Office would not provide the
same information  as the  review the Subcommittee  was  considering, spending
additional money on yet a third "audit" was not justifiable given the overwhelming
evidence  that the program was under-funded,  and the fact that no one on the
Subcommittee identified specific areas of programmatic waste apart from "earmarks
to OIG and other offices." See Attachment A for Ms. Peters' individual statement.

RR Subcommittee member Jim Derouin believes that one efficiency problem facing
EPA is that the Agency should direct, as a percentage of its budget, more funding to
actual bricks and mortar remediation. See Attachment A for Mr. Derouin's individual
statement.

ss Subcommittee  member Vicky Peters believes that it was not clear from the
Subcommittee's  discussion that contract reforms would  be beneficial and worth
pursuing and based on the little known about these reforms, some  were impracticable
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Subcommittee members who support EPA's pilot testing contract reforms  noted that a
significant  portion  of  the  Superfund  budget—particularly  the  budget  for  site
assessments  and  remedial actions—is spent through contracts, referred to by EPA  as
"extramural"  spending.    These  Subcommittee members  recognize  that reforming
contracting practices poses challenges, but believe that because of the important role
contracting plays in  the overall Superfund budget particularly in the budget for on-the-
ground  cleanup  activities—-EPA should  explore and capitalize  on  opportunities  to
improve its contracting practices.11  These members further observed that other federal
agencies such as  the Departments of Defense and Energy have used a number of the
contracting reforms discussed by the Subcommittee  and believe that EPA should work
with these agencies to gain from  their experiences and use this information to improve
the Agency's contract reform efforts.
   Different Views on Superfund Program  Funding

Subcommittee members agreed that the Superfund Program should:

    -* have sufficient resources to fulfill its responsibility of protecting human health and
       the environment at Superfund sites; and
    -* spend more, rather than less, money on work directly related to improving public
       health and environmental conditions at NPL sites.uu

Subcommittee  members  had  differing views  on  how these  outcomes  should  be
accomplished.

During the Subcommittee's  deliberations EPA informed the members that there are a
number of NPL sites at which remedial designs are complete but where remedial  actions
are slowed—or not yet started—because of insufficient funding.  A series of OIG reports12
and the congressionally requested estimate of funding needs for the Superfund Program,
Resources for the  Future's "Superfund's  Future: What  Will  it  Cost?"13 confirm that,
although  some  additional money has periodically been  made available for funding at
some sites, a  backlog of sites that require federal funding  for removals, remedial actions,
long-term response actions, and other activities remains.
given budget constraints, and some have been problematic when initiated by DOD.
See Attachment A for Ms. Peters' individual statement.

TT Subcommittee member Tom Newlon supports contract reforms as a component part
of reforms that could help  address the mega  site backlog, consistent with his
individual  statement  and other footnotes.   See  Attachment A  for  Mr. Newlon's
individual statement.

uu Subcommittee member Jim Derouin believes that one efficiency problem facing
EPA is that the Agency should direct, as a percentage of its budget, more funding to
actual bricks and mortar remediation. See Attachment A for Mr. Derouin's individual
statement.
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EPA uses diligent enforcement efforts to identify responsible parties and have them pay
for cleanup; nonetheless, federal funding is needed at some sites.  Some  of the sites in
the  backlog have been in the Superfund Program for many years.  The Subcommittee
recognized that,  if not addressed, this backlog of sites will continue to pose threats to
communities,  and cleanup costs at these sites will increase, sometimes dramatically.
New Bedford, Massachusetts, where the Subcommittee held one its June 2003 meeting,
is an example of such a site. The New Bedford Harbor mega site  has been in the
Superfund system for more than twenty years. The site is ready for remedy construction.
Because of funding  constraints,  however,  remedial action  may stretch out for another
twenty-five years, a schedule that is sub-optimal in terms of cost effectiveness as well as
public health and the environment. The Subcommittee agreed that sites in the backlog
should be cleaned up in a timely way.

Subcommittee members vigorously debated whether they could agree to  recommend a
temporary, limited, targeted  increase in  appropriations to the Superfund Program to
address  remedial actions  at the backlog of sites until an  independent audit of the
Superfund budget was completed  and  a  long-term  Program  spending  plan  was
developed. Ultimately, the Subcommittee was unable to reach consensus  on such a
recommendation  because  of differences of  opinion about three key issues:  (1) the
amount  of funding that may be needed, (2) the  extent to which the  recommendation
should restrict the types of sites at which EPA  could expend supplemental funding, and
(3) the sources of the funding -taxes or general appropriations^

Funding Amount
The  Subcommittee was not able to agree to an amount of supplemental  funding to
recommend.    Some  members  argued  the  need  for  $300-$800  million a   year.
Subcommittee members who supported funding  in this  range cited  three  reports to
support their view. First, Resources for the Future reported that the Superfund Program
would likely  need  increased  funding  throughout  this decade  to  adequately  fund
cleanups.14 However, actual  appropriations have  been $300-$800 million  below RFF's
inflation-adjusted base  and high estimates.  Second, EPA's 2004 OIG report released
Agency  documents demonstrating that the resource needs for activities included in the
FY 2002 remedial action advise of allowance (i.e.  remedial actions, long-term response
actions,   five-year reviews,  enforcement  fairness projects, above-the-base  removal
actions,  and redevelopment/reuse projects) are nearly three times the budgeted amount
of $224  million.15 Third, the General Accounting Office also recently reported that over
the  last  ten years the  Superfund Program has suffered a decline in funding  of  $672
million, adjusted  for inflation.16  These Subcommittee members  further observed that
even the $300-$800 million funding range does not account for adverse impacts caused
by several years  of what they see as under- funding of the Superfund Program.
w Subcommittee Member Vicky Peters does not agree that the description in the
report accurately reflects the deliberations that took place. See Attachment A for Ms.
Peters' individual statement and the individual statement of Aimee Houghton.   Ms.
Peters agrees with Ms. Houghton's views on this issue.
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Other Subcommittee members were unwilling to support supplemental funding in  this
range, because they are not confident the funds that are currently appropriated are being
spent in the most efficient and effective manner possible.™" These members believe  that
far too much Superfund money is devoted to non-OSWER costs, cost-of-living increases
for EPA staff,  and program management.  They also believe that far too little annual
appropriations  are devoted to extramural remedial action cleanup costs.xx  Given these
concerns,  they are  reluctant to support any supplemental funding for the  Superfund
Program until  after  a neutral,  independent  audit  to  identify program  efficiencies was
                                                YY
completed and program efficiencies are implemented.   Some Subcommittee members
believe that supplemental funding in the range of the $150 million that the Administration
has requested  in the past two budget cycles, or the $175  million range identified by the
OIG as the FY  2003  funding shortfall, is not unreasonable.17

Where  Should Funds be Spent
While all Subcommittee members  recognized the importance and value of a strong
enforcement program that  targets  all—not just some—responsible parties, encourages
proactive efforts by cooperative responsible parties, and discourages recalcitrance, some
members argued that if EPA were to receive supplemental funding for remedial actions at
the backlog of  sites, such funding should be limited to instances where the Agency  has
determined that there are no viable responsible parties.   Subcommittee members who
supported this  approach believe that viable PRPs who can perform or pay for cleanup
should do so, and  that EPA already has sufficient tools to compel viable PRPs to perform
or pay for necessary work under  CERCLA.   These members wanted to ensure  that
funding  would  be  focused  on the most serious funding needs, which  they describe as
"ready-to-go" extramural remedial costs at sites where, after diligent enforcement efforts,
EPA has determined that  no viable party could fund  cleanup. They noted that EPA's
efforts to find money to pay for such cleanup costs have handicapped implementation of
the Agency's fairness administrative reforms at other sites, and that these reforms  are
important to a  successful  Program.  For these reasons, these Subcommittee members
were willing to support temporary supplemental  funding,  pending the  results  of an
independent audit of Superfund expenditures, but only if such funding were limited to
ww Subcommittee member Jim Derouin does not believe that this report includes
recommendations that will lead  to significant efficiencies in the operation of the
Program and was, as a result, unwilling to support substantial new funding for the
Program.  See Attachment A for Mr. Derouin's individual statement.

xx Subcommittee member Jim Derouin  believes that one efficiency problem facing
EPA is that the Agency should direct, as a percentage of its budget, more funding to
actual bricks and mortar remediation. See Attachment A for Mr. Derouin's individual
statement.

^ Subcommittee member Richard Stewart also opposes funding increases at this time
because he believes EPA continues to badly waste program resources by failing to
target them on the most serious health and environmental risks. See Attachment A for
Mr. Stewart's individual statement.
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extramural  remedial  actions (construction)  at  sites like New Bedford  Harbor, where
federal funding is necessary to pay for orphan shares.

Other Subcommittee  members objected to limiting funding to instances where EPA has
determined there are  no viable  responsible  parties, believe  that  implementing  this
limitation would be difficult, if not impossible,  would violate Congressional intent and
common-sense by potentially forcing EPA to prioritize  expenditures  based  on the
absence of a viable PRP  or forgo cost recovery actions against PRPs and  entities
associated  with PRPs that the Agency is entitled to by the statute,  thereby undermining
the liability provisions  of CRECLA, and  would restrict EPA's  discretion to make the
decisions  the Agency  believes  are  necessary  to  protect human health and  the
environment.  These  Subcommittee members also rejected this constraint because they
did not want  political actors to apply this restriction to future program funding.  These
members believe EPA must have the flexibility to spend funds where the Agency believes
they will best help address threats to public health and  the environment, which may
include increased funding for enforcement actions.  Finally, they believe that the  current
funding  shortfall  has  adversely  impacted a  host of actions  necessary for cleaning up
sites, including studies, listings, removals,  and long-term clean-up activities, and  that
EPA should be allowed  to fund all these activities with any resources made available.

Funding Source
The Subcommittee had  very divergent views  about the appropriate funding source for the
Superfund  Program,  in  particular, the excise taxes on sales  of crude oil and petroleum
products, and sales of certain chemicals and  the environmental tax on corporations—all
of which lapsed at the end  of 1995. Some  Subcommittee members were very troubled
by the expiration of these taxes, which they  see as linked to what they believe is recent
under funding of the Superfund Program and the cause of the  backlog of remedial
actions  at  NPL sites.    Other members  did not see such  a  link,  observing  that
appropriations to the  Superfund Program have risen and fallen  over the past ten years
independent  of  the  taxes, as  described  in  the  recent GAO report  on  Superfund
                             7718
appropriations and expenditures.
zz  Subcommittee  Member Vicky  Peters  supports  neither  this position nor  this
interpretation of the GAO report.   See Attachment A for  Ms. Peters'  individual
statement and for the individual statement of Grant Cope. Ms.  Peters' agrees with Mr.
Cope's views on this issue.


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1  Use of the generic term "EPA" is meant to address both headquarters and regional
offices and to recognize that the EPA decision maker with respect to NPL listings is the
Assistant Administrator for Solid Waste and Emergency Response.
2  As used in this report, the term "NPL eligible" or "NPL-eligible site" means sites that
score 28.5 or higher under EPA's Hazard Ranking System or are otherwise eligible to be
considered for the NPL,  for example  because of an Agency for Toxic Substances and
Disease Registry health advisory.  Not all  NPL-eligible sites are proposed for listing  on
the NPL. The term "NPL candidate" or "NPL-candidate site" means that subset of NPL-
eligible sites that EPA regional offices recommend that EPA headquarters propose  for
listing on the NPL.
3  As discussed more fully in later in this chapter, Subcommittee members had a range of
views about the role of non-Superfund programs.  Some Subcommittee members do not
anticipate that many other cleanup programs will have access to the funding necessary to
independently pay for cleanup  at NPL-caliber sites.  Other members believe that non-
Superfund cleanup programs may, for certain sites, have access to useful resources.
4  As described earlier in this  report, the formal  Superfund site assessment process
begins when EPA first enters information  about a release or potential release into the
CERCLIS data system  and  continues through  preliminary  site assessments, site
inspections and other activities.  The  "Superfund site assessment" process ends either
when EPA determines that no further remedial action is  planned  under CERCLA, at
which point site assessment stops and site information is archived, or when EPA decides
to propose a site for listing on  the NPL, at which  point the Superfund site  assessment
phase of the process ends and the  listing process begins.  Note that "Superfund site
assessment process" is a term meant to describe activities that take place before EPA
makes a decision about whether to propose a site for listing. At sites that EPA decides to
propose for listing, assessment and evaluative activities (such  as remedial  investigations)
continue.
5  EPA's  current guidance on PRP searches indicates that searches for remedial  action
sites should begin as soon as  EPA determines that  a site is "NPL-caliber" and  that a
long-term response  is appropriate and  calls for the  search  to be completed 90 days
before the start of remedial design and remedial action (RD/RA) implementation. The
RD/RA occurs long after a site  is listed on the NPL.  If PRPs are not identified until this
time, it  is much too late to allow them (particularly those who do  not own the site in
question) to participate in discussions  about site investigations and remedy selection, or
consider voluntarily  undertaking site investigation  and  cleanup  under  a non-NPL
program.
6  Information provided by EPA from eFACTS on October 16, 2003.
7  The Subcommittee recognizes that the Department of Defense also has responsibilities
relative to removal actions under 40 CFR Part 300 Subpart B.
8  The Subcommittee did  not  carry  out  an assessment of the  US Army Corps  of
Engineers' programs, the Urban Rivers Restoration Initiative, or the Land Revitalization
Agenda.  Based on their individual experiences,  some  Subcommittee members  were
comfortable with these programs. Other Subcommittee members had serious concerns
about these programs' ability to appropriately clean  up  sites and concerns that using
other programs' funding models could erode Superfund's liability standards.
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9 The Subcommittee did not review the RCRA Deferral Policy or its outcomes in any
detail.   Based on  their individual experiences,  some  Subcommittee members  were
comfortable with  the  concept of deferring to RCRA sites that are subject  to RCRA
corrective action authority. Other Subcommittee members had concerns about the ability
of the RCRA program to achieve appropriate and timely cleanup outcomes at sites that
might be deferred.
10 Environmental Law Institute, An Analysis of State Superfund Programs: 50-State Study
2001 Update, Washington D.C., November 2002.
11 This  guidance  is also applied  to  decisions  about certain removal actions.   The
Subcommittee did not debate and is not taking a  position on priority setting for removal
actions.
12 EPA  Inspector General,  Congressional Request on Funding Needs for Non-Federal
Superfund Sites, Rpt. 2004-P-00001 (Jan. 7, 2004).
13 Probst, Katherine N.,  Et al., Superfund's Future: What Will It Cost?, Washington  D.C.:
resources for the Future, 2001 pp. xxi-xxiv.
14 Ibid.
15 EPA  Inspector General,  Congressional Request on Funding Needs for Non-Federal
Superfund Sites, Rpt.  2004-P-00001 (January 7, 2004); EPA, Memorandum from Elaine
F. Davies  to Superfund National Program Managers, OSWER 9275.1-04 (January 3,
2002).
16 GAO-04-475R Superfund Program, February 18, 2004.
17 EPA  Inspector General,  Congressional Request on Funding Needs for Non-Federal
Superfund Sites, Rpt. 2004-P-00001 (January 7, 2004) p. 4.
18 GAO-04-475R Superfund Program, February 18, 2004.
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                   Mega   Sites
The  Subcommittee   was  specifically  charged  with  considering   and  providing
recommendations related to management of large, complex and costly cleanups, often
referred to  a mega  sites.  Subcommittee  members had divergent views about the
implications of mega sites for the Superfund  Program. As a result, this chapter presents
consensus recommendations and briefly describes Subcommittee members' contrasting
views about what would be the best overall  approach to  resolving the difficult questions
raised by very expensive cleanups.
Defining and Characterizing Mega Sites
As requested by EPA, the Subcommittee discussed  how to  delineate the mega site
universe and generally agreed that a monetary limit can serve as a practical surrogate for
complexity and other factors associated with especially  expensive sites. The current $50
million or higher mega site definition was seen by some members as an appropriate
cutoff; others argued for a  higher trigger, such as $90-$100 million or higher.  In either
case, Subcommittee members agreed that while a monetary definition can serve as  a
practical way to  identify sites that  merit special attention,  a confluence of factors
contributes to the complexity of a site, which  in  turn  influence site  costs.  During its
deliberations, the Subcommittee identified the following  site factors or circumstances that
may contribute to overall site complexity and cost:

   -*  Large geographic area
   -*  Scientific and technical complexity
   -*  Administrative complexity
   -*  High-risk waste management activities (e.g., recycling)
   -*  Liability exemptions (e.g., recycling)
   -*  Site type (e.g., mining)
   -*  Media type (e.g., sediments)
   -*  Specific issues in specific regions (e.g., sediments in EPA Region 10)
   -*  Tribal and other communities where traditional  or religious  practices involve use
       of natural resources
   -*  Multiple discrete sources of contamination
   -*  Future risks
   -*  Impacts on multiple communities
   -*  Financial  status and/or willing participation of potentially responsible parties
       (PRPs)
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These factors were not considered definitive because they also may characterize less
expensive sites.  However, they can be particularly useful to help  increase the EPA's
awareness and  understanding of the complexity associated with mega sites.  In trying to
better  understand the mega site issue and characteristics other than cost that define
these expensive sites, the Subcommittee  found  that the lack of reliable data  on and
analysis of these expensive sites  impeded it's  ability to confidently establish  a clear
definition of a mega site and the challenges associated with  them.  The  corresponding
assumption was that if the data presented to the Subcommittee were inadequate, then
the data  must  also be  inadequate  for the  Agency.   These  data challenges were
interpreted as a significant hurdle to developing a clear understanding of mega site
issues and the management options for addressing them effectively in the future.

It is critical that EPA build its capacity to understand  and manage these  parameters of
complexity in the most effective and  efficient ways possible to improve the speed and
efficiency  of  cleanups at mega sites.  Once a site is designated as  a  mega site
(regardless of what monetary definition is used), it is very important that the EPA be able
to marshal the appropriate expertise  and management experience to determine how to
best address the risks posed by the site.

In response to the Agency's charge,  members of the Subcommittee worked to identify
important  issues related to mega sites, considered in depth the difficult policy questions
raised  by mega  sites,   and  explored  various  broad  policy-level options   for  the
management of large,  complex,  and costly sites.  Some of the difficult  questions  the
members raised included:

    -* Assuming funding constraints are affecting Fund-lead sites, should fewer sites be
       cleaned up more thoroughly, or should the Agency focus on  reducing immediate
       threats only, allowing more sites to be addressed?
    -* Should the most expensive sites be left off of the NPL? Should some subset be
       left off?
    -* If the Superfund Program does not address some or all mega sites or potions of
       mega sites, where would they be addressed?  What existing programs have  the
       funding,  resources, and experience to deal with sites of this magnitude?  What
       are the  ensuing implications (e.g., appropriations, liability)?  What programs  are
       available that  will  adequately protect  human  health  and the environment and
       effectively involve affected communities at these sites?
    -* Would the law allow EPA to treat these sites differently simply because they  are
       expensive?  What if they are large, complex, and expensive?
    -* Should  expenditures at mega sites be prioritized so that funds are dedicated to
       portions of such sites that pose the greatest threats?A
A Subcommittee member Jim Derouin believes that EPA should have the flexibility to
evaluate risks/exposures presented by portions of mega sites, rather than being
bound to assume that, once a mega site is listed, all portions of such a site must be
treated as posing an equal risk.  He feels that, without such flexibility, EPA cannot
efficiently direct funding to the sites, or portions of sites, that pose the most risk at any
given point in time. See Attachment A for Mr. Derouin's individual statement.
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    -*  Does the expenditure of funds at a mega site mean that the site as a whole has a
       priority claim  on future funding,  even though other sites may pose a greater
       threat of exposure?8
    -*  Should EPA receive increased funding to address these sites?
    -*  Do  these  sites  have  impacts  on  communities   (particularly  Tribal  and
       Environmental Justice communities) that should be considered?
Deliberations and Recommendations on Management of
Mega Sites
The  Subcommittee was unable to reach agreement  on a preferred comprehensive
approach for dealing with mega sites.  Due to the wide diversity of stakeholders on the
Subcommittee, the views regarding the overall manner in which mega sites should  be
managed  differed  fundamentally.    Individual  Subcommittee  member's views  are
described  in  the  individual papers  included in [a reference  will  be made to any
Subcommittee position  papers  addressing mega site  issues in Attachment  A].  The
Subcommittee extensively discussed the management recommendations in this section,
but did  not  reach  consensus on  all  of them.   The  members  believe the following
discussion of the issues can help improve how EPA addresses mega sites.  In addition,
some members believe that implementation  of these recommendations alone will not
satisfactorily  address  the need  to  manage mega sites more effectively, given existing
financial realities.

In  the context of the wide range of views about an overall approach  to mega sites, the
Subcommittee discussed a number of  potential recommendations on applying special
management consideration  and  attention to these sites.  The Subcommittee makes one
consensus recommendation on management of mega sites.  Recommendation  9 advises
EPA to bring focused and sustained management attention to mega sites, and gives a
number of examples of the types of attention that would be most useful.  In addition, the
Subcommittee considered but did  not reach  consensus on (1) a recommendation that
EPA consider an expanded site inspection/remedial investigation for potential mega sites,
and (2) a  recommendation  that EPA consider a specific set of factors when deciding,
consistent with Recommendation 3  on involvement of stakeholders in the listing process,
how  to address large geographic areas with  multiple  contaminant sources.  These
deliberations are described below.

The Subcommittee reiterates its expectation that its deliberations and recommendations
on listing and management of NPL sites, described  in  Chapter III, will be applied with
increased  attention and rigor to mega sites and potential mega  sites.   In particular,
B Subcommittee member Jim Derouin believes that EPA should have the flexibility to
evaluate risks/exposures presented by portions  of mega  sites rather than being
bound to assume that, once a mega site is listed, all portions  of such a site must be
treated as posing an equal risk.  He feels that, without such flexibility, EPA cannot
efficiently direct funding to the sites, or portions of sites, that pose the most risk at any
given point in time. See Attachment A for Mr. Derouin's individual statement.
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Recommendation 3 addresses the importance of outreach to and involvement of affected
communities, PRPs, and others early in the site assessment process (i.e., well before a
listing decision is  made).  In Chapter V, the Subcommittee makes recommendations
about additional  measures of  program  progress  that will accurately  reflect interim
progress made at all sites, which may be especially useful for large, complex sites.
    Recommendation 9:  EPA should establish practices that result in
    mega sites receiving the necessary resources and attention from
    senior Agency managers.
While all Superfund sites present management challenges, mega sites,  by definition,
present complexities  and investments that are at a  greater scale, and thus deserve
special  management attention.   In  the  private sector, very expensive projects are
commonly governed  by special  forms  of project  management  and receive  greater
attention from management.  Because mega sites tend to remain on the NPL for long
periods of time and their high costs can have important impacts on the Superfund budget
and the economy,  EPA should apply the following special management techniques to
mega sites.

First, the Agency should ensure that the  project managers assigned to mega sites have
the appropriate experience and expertise to manage that type and level of project. The
challenges associated with managing a large, complex, expensive,  multi-year project are
significant, and the Agency should strive to assign and retain its  most talented project
managers to and  on these  sites.   More  experienced  remedial  project  managers,
particularly those with successful experiences managing other large complex sites, may
be best suited to meet such challenges.  These seasoned staff should be familiar with
similarly complex sites around the  country or region, and should have  experience
implementing  cost-effective,   reliable  approaches   and  construction   management
strategies. This depth of experience is important fora large, complex site, where a newer
less experienced  project manager  might be more hesitant to make decisions, more easily
overwhelmed, or more likely to make errors in  judgment.  Some of the most important
skills for mega site project managers are construction and other  management skills -
such  as the  ability to  balance competing factors,  negotiate agreements,  and  make
decisions.  While also important,  the technical, financial, and other types of expertise
needed can be provided by other professionals who support the project manager.

In addition, when making decisions  about changing  or reassigning  mega site project
managers, EPA should consider the benefits that are  typically associated with stability in
the project  manager assignment.   A  number of Subcommittee members  have
experienced  a situation where there have been  multiple consecutive project managers at
a single site  in a  short period of time. These changes can cause  delays in cleanup, as
new  project  managers  must  become familiar  with the site  history, stakeholders, and
cleanup approaches.  The more complex a site, the steeper this learning curve.  Thus,
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EPA should explore creative personnel approaches to attract and retain the  best and
brightest project managers to mega sites and to reward their superior service.

Second, EPA should provide project managers with the support systems that they need.
Mega site  project  managers need access to specialized expertise to assist them in
overseeing a complex, expensive, multi-year cleanup.  In  particular, experts in technical
disciplines  relevant to  the  site  in question and  experts in  such  practices as cost
engineering and multi-year  funding are needed.   The Subcommittee emphasizes  the
potential usefulness of cost  engineering, a practice commonly used in the private sector
and by other government agencies, including the Department of Energy.  The focus of
cost engineering is use of the right tools, systems, and training to develop credible cost
estimates  and life-cycle costs to  assist in decision making for large,  complex projects.
Benefits can include increased accuracy of costs estimates, improved accountability, and
improved management.

Third, the Agency must apply sustained upper management attention to large,  complex,
and expensive sites.  These sites have the potential to  consume a  large amount of
human,  as well  as financial, resources.  It is important to  keep strong management
attention focused on  them to ensure that cleanup occurs at a predictable and  steady
pace.   The  Office  of Solid  Waste's  pre-SARA  (Superfund Amendments  and
Reauthorization Act) site review is a step in the right direction by attempting to focus on
the difficult problem of completing cleanups at sites (many  of them mega sites) listed
before 1986. However, more work and greater involvement by upper management is
needed to  map out effective  management strategies.

Finally, EPA should create specific centers of excellence  within the Agency and, where
appropriate, call  on  experts outside the Agency.   These centers should connect
individuals  who possess  an understanding of some of the  common characteristics of
expensive sites,  such as  sediment issues or issues related to sites located in Tribal or
other communities  where traditional practices involve use  of natural resources. Centers
of excellence should be  clearinghouses for information  on  successful  approaches to
addressing such  complexities and lessons learned, so that project managers of sites with
these characteristics can learn from and support one another.

While the Subcommittee agreed that mega sites should be given focused and sustained
management attention, it did not reach consensus on whether mega sites should be
subject  to  different technical processes or  cleanup  standards.   Some  Subcommittee
members  believe  that, because  of the high costs  of mega sites and the practical
limitations  on both  government and private funding, different  approaches for mega sites
are warranted and should be discussed in an open and public process.0  Other members
strongly opposed to this view,  stressing that care should  be taken not to interpret this
recommendation as a  call  for a different technical  process  or for different cleanup
standards  for mega sites.  These members believe that  mega sites  require  the same
attention and should be cleaned up to the same standards as all other NPL sites.
c Subcommittee member Richard Stewart supports this view. See Attachment A for
Mr. Stewart's individual statement.
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   Deliberations on Expanded Site Inspections/Remedial
Investigations at Large, Complex Sites

The Subcommittee considered but did not reach consensus on a recommendation that
EPA should  consider whether  to carry  out an  expanded site  inspection/remedial
investigation (ESI/RI) early in the Superfund site assessment process at large, complex
sites.  As described by current EPA guidance, an  ESI/RI may  be  used to  gather site
characterization data common to SI and Rl activities in one step, thereby expediting the
later collection  of  data when comprehensive Rl  activities are performed.  ESI/Rls
facilitate, but do not replace additional investigations that may occur if a site is  listed.

Subcommittee members who supported this  recommendation thought that an ESI/RI
could be used to:

    -*   Identify  site-specific  data that are available  and  reliable, and that can be used
       during MRS scoring,  as described more fully in Recommendation 4.
    -*  Gather information on sources and distribution of contamination to inform listing
       decisions and post-listing site management.
    -*  Gather  information  on  and  reach  out  to other programs  that  may  have
       independent missions or activities that could  have a positive or negative effect on
       the Superfund  cleanup,  and develop plans to  avoid  negative effects  and
       capitalize on potential positive effects, such as opportunities to leverage funding.
    -*  Aid EPA in setting  priorities after site listing.

These Subcommittee members argued that, given the level of commitment  needed for
large,  complex  sites, it is particularly important that  an understanding  of actual  site-
specific  conditions,  rather than  default  assumptions, drive decision  making.  These
members  believe  that additional  up-front  investments  in ESI/Rls  may  pay important
dividends  in helping EPA determine  how to best  address potential  mega sites.   In
addition, some Subcommittee members who supported an ESI/RI for all large, complex
sites observed that it would  provide information the  Agency could use to decide how to
best address the large area in the first instance.DE  This is discussed  more  fully in the
next section, which describes the Subcommittee's  range of views about how EPA should
address large geographic areas.
D Subcommittee member Tom Newlon supports the ESI/RI concept and approach for
large, complex areas of discontinuous contamination from multiple sources, based on
his view that more effective evaluation of potential approaches to these large areas is
needed to ensure that the most efficient and effective approach is put in place.  See
Attachment A for Mr. Newlon's individual statement.

E Subcommittee member Richard Stewart supports supports the ESI/RI  concept and
approach for large, complex sites.  See Attachment A for Mr. Stewart's individual
statement.
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Other Subcommittee  members do not believe EPA should automatically consider an
ESI/RI at every large, complex site.   They argued that EPA's decision to conduct an
ESI/RI should depend upon site-specific circumstances.  In some circumstances, such as
where site conditions, releases, and potential releases are well understood, carrying out
an  ESI/RI could needlessly  increase  up-front costs and  delay  cleanups.  In other
circumstances, such as where data on site conditions, releases, and potential releases
are not comprehensive, reliable, or up-to-date, an ESI/RI might make sense regardless of
site size or complexity.  In addition, some Subcommittee members who did not support
consideration of an  ESI/RI at every large, complex site were uncomfortable with some of
the potential  uses of an ESI/RI described above, particularly that an ESI/RI  might serve to
encourage use  of non-Superfund programs that might not meet or exceed  Superfund
standards.

Subcommittee members who were not willing to support a recommendation that EPA
should consider an ESI/RI for every large complex  site were willing  to  support a
recommendation that EPA should consider whether an ESI/RI is needed  as  part of the
outreach  to  and involvement of affected  communities, PRPs, and other stakeholders
early in the Superfund site assessment process, as described in Recommendation 3.
   Deliberations on Addressing Large Geographic Areas with
Multiple Contaminant Sources

The  Subcommittee considered but did not reach consensus  on a recommendation
advising that, when considering how to best address large geographic areas with multiple
sources of contamination, EPA should evaluate a variety  of potential approaches and
should consider  factors  related  to how these approaches would affect the  efficacy,
efficiency, and timeliness of the overall cleanup process.

When EPA makes a decision to pursue an NPL listing,  it describes the releases to be
listed.  Decisions about what constitutes the "site" for purposes of listing  may be difficult
when EPA is evaluating large geographic areas with  multiple sources of contamination.
This  may be the case especially where contamination is discontinuously distributed, with
large areas of relatively low-level contamination between "hotspots," or  where  multiple,
geographically distinct, unrelated sources of contamination  are present.  The number of
such sites currently on the NPL may  be very small and, based on some Subcommittee
members' individual  experiences, appear to be largely  aquatic sites that cover entire
urban bays and industrial waterways or watershed areas. However, also  based on some
Subcommittee members' individual experiences, cleanup and process-related  costs at
these sites can be high, as can be the risk of protracted remediation timelines.

There was a range of views on the Subcommittee about whether EPA  has in  the past
appropriately made decisions  about listing large geographic areas,  and how EPA should
evaluate these areas in the future. Some Subcommittee members believe EPA does not
look  closely enough at the potential value of addressing large geographic areas through
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focused attention on smaller units tied to individual releases or clusters of releases.  They
believe that when evaluating large geographic areas, EPA should consider alternatives to
a single NPL listing, such as (1) listing one or more smaller areas as separate NPL sites
tied to specific sources of contamination or responsible parties, (2) addressing portions of
an area through removal actions or adequate federal or state non-Superfund programs
instead  of an  NPL  listing, or  (3)  some  combination  of these  approaches.  These
Subcommittee members further believe that a single NPL listing—or perhaps any NPL
listing—is not  the  best  approach  to  addressing  areas  where contamination  is
discontinuously distributed so  that  there  are large  areas  of  relatively low-level
contamination  between  hotspots,  or where multiple,  geographically distinct, unrelated
sources  of contamination are present frequently.F  They think  EPA  should use the
increased early involvement of stakeholders described in Recommendation 3  and an
ESI/RI (discussed above) to gather information and input to guide its decision making on
how to best address individual large geographic areas.0

 Other Subcommittee members strongly disagree with this view, believing that EPA has
at times been too narrow in its definition of the "site" when considering a large geographic
area.  These members believe it is inappropriate for EPA to list only a small subsection of
a large geographic area, and prefer that EPA list entire  contaminated areas and then, if
appropriate, divide the sites into operable units after listing. These members argued that
listing only a small  potion of a large geographic area could:  (1) make it  more difficult to
list  other contaminated  portions of the same area in the  future;  (2)  hamper EPA's
exercise  of its  authority to ensure that the entire geographic area is cleaned  up;  and (3)
increase  the likelihood that portions of the area would  be left unaddressed, potentially
forever.

The Subcommittee also considered but did not reach consensus on  a set of factors and
questions that  EPA might consider when evaluating large geographic areas with multiple,
discrete contamination sources.

Some Subcommittee members supported the following set of factors:

    -*  Is the  overall cleanup likely to be improved  or expedited  by  listing the  large
       geographic areas as a single NPL site or through some other approach?  EPA
       should consider the potential for various listing strategies to affect the difficulty of
       negotiations, the length  of time before cleanup can start, process-related costs,
       and the time frame in which cleanup will ultimately be achieved.
    -*  What  is the  best  way to  manage  the  anticipated  total transaction  costs
       associated  with evaluation and  cleanup of the area?   On   the  one hand,
       addressing a large geographic area in terms of smaller units—either by separate
F Subcommittee member Tom Newlon supports this position which he believes is an
essential component of a package of reforms  that is needed to help EPA more
effectively and efficiently address potential mega sites.  See Attachment A for Mr.
Newlon's individual statement.

G Subcommittee member Richard Stewart supports these views.  See Attachment A for
Mr. Stewart's individual statement.
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       NPL  listings or by application of other programs  as discussed above—may
       simplify and streamline investigations and cleanups,  reduce transaction costs by
       avoiding diseconomies of scale, and allow remedies or portions of remedies to
       be  identified and  implemented sooner.   On the other hand, there may be
       economies  of scale,  improved understanding of the  inter-relationships of the
       technical and legal aspects of the site, consistency  gains, and more  integrated
       and efficient analysis that could be realized by listing a large geographic area as
       a single NPL site.
    -* Will areas not included in an NPL "site" at listing be adequately addressed?  EPA
       should  consider the  potential for various listing  strategies  to  leave  areas of
       contamination stranded and unlikely to be adequately addressed, as well as the
       potential for non-Superfund programs to adequately address areas that are not
       part of an NPL listing.
    -* Listing one  large geographic area provides communities with a unified basis for
       participation in the evaluation and cleanup of all the  contaminant hotspots in an
       area.   Listing  the entire area  also brings  into  play the  public  involvement
       advantages that come with a Superfund listing, including technical assistance
       grants to communities.   These factors should be weighed along with potential
       efficiency gains (and simplicity for the community) from more  directly addressing
       individual hotspots and clusters of hotspots within the area.
    -* EPA should consider whether sources of contamination,  although disparate, are
       integrated  in human or environmental  receptors and  how that  integration, if  it
       occurs, would best be  addressed.
    -* EPA  should consider whether hotspots  or contaminants in a large geographic
       area are likely to shift, particularly in dynamic aquatic systems, and how to best
       address that possibility.
    -* EPA  should consider  whether addressing a  large geographic area as one site
       versus  in multiple  smaller units or though other means would allow  for easier
       administration   by  EPA, states,  and  Tribal Nations,  or would  make  such
       administration more difficult and create more or less impact on the resources of
       regulatory agencies.

Other Subcommittee members did not support  these factors.  They strongly opposed
EPA's listing only a small portion of a  large geographic  area (as described in the
discussion  of the  Subcommittee's  range of views on  this  issue, above), and/or had
concerns  regarding  one  or  more   of  the  individual  factors.    In  particular,  some
Subcommittee members opposed any  consideration  of negotiation  and other process-
related or  transaction costs,  arguing that such considerations inappropriately  benefit
PRPs, not the Superfund Program or the general public. Some of these members were
concerned  that  the factors  allow for inappropriate consideration  of non-Superfund
programs that might not meet or exceed Superfund's standards (see discussion of the
role  of other programs in Chapter  III),  or  were concerned  that the  factors do not
adequately consider the potential that  portions of large geographic areas not listed on the
NPL may go unaddressed and remain contaminated indefinitely.
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              Measuring
Program  Progress
     The Subcommittee was asked to provide feedback on EPA's continuing efforts to
     develop measures  of Program  progress.  The Subcommittee supplied  such
     feedback primarily through a work group established for that purpose. In addition,
the Subcommittee is proactively suggesting additional measures and related activities for
EPA's consideration.  The Subcommittee's recommendations address how the Program
can improve its measurement and communication of performance on both national and
site-specific levels.

These ideas are presented as recommendations and guidelines for implementation and
policy consideration.  Although  the Subcommittee members had divergent views about
what  should be measured, how the Program should be measured and for what purpose,
a number of recommendations  achieved  consensus.   This  chapter  (1) provides
background and context  for the  Subcommittee's deliberations about measuring the
progress of the Superfund Program;  (2) presents a primary set of goals upon which to
measure the overall Program at a national level; (3)  describes additional measures of
progress that can be used  to indicate how the Program is working based on compilations
of data  for each National Priorities List (NPL) site; and  (4) suggests an approach to
measure the success of EPA's coordination with state and local governments, Tribal
Nations  and communities, and provides further recommendations for integrating  such
coordination meaningfully into the functioning of the Program.
Background and Context
The discussion of measuring the progress of the Superfund Program needs to be linked
to the purpose and goals of the Program. In 1980, Congress passed the Comprehensive
Environmental Response, Compensation and Liability Act (CERCLA) to increase federal
authority to respond to releases or threatened releases of hazardous substances that
may endanger public  health or welfare and the environment.  Thus, it is clear that
measurements of the Superfund Program's progress should include metrics that assess
the extent to which EPA has responded to those releases. In addition, as requested  by
the  EPA Administrator, the question  of Program  performance also was  evaluated.
Comments on measures that can be considered to identify both the performance and the
progress of the Superfund Program are included in this chapter.
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    Using Construction Completions to Measure Progress

Over approximately the past eight years,1 the key measure of progress used by EPA for
sites  on the  National Priorities List (NPL)  has been the  number  of construction
completions  by site each  year.  EPA defines construction completion as "a benchmark
used to show that  all significant construction activity has been completed, even though
additional remediation may be needed for all cleanup goals to be met.2"

The date  a site  reaches  construction  completion provides  an indication  of interim
progress toward meeting  the primary cleanup goals of the  Program.   This date is an
important  indicator for public reporting  because  it is straightforward  and objectively
verifiable. It remains a primary concern of affected communities, provides an indication of
progress toward meeting the  basic cleanup goals  of  the  Program,  and  reflects  a
significant budgetary  milestone  since  remedial  construction tends to  be the most
expensive component of cleanup.

Nevertheless, focusing solely on construction completion to gauge Program progress has
limitations.  For example, it reflects the  outcome of the construction phase and not the
interim accomplishments  i.e., site investigation, risk assessment, remedy selection,  and
interim response actions.  Additionally,  construction  completion does  not necessarily
reflect threat(s) that a  site may continue to pose  to humans and the environment after
construction. Thus, it fails to capture meaningful progress at different stages of cleanup.

Finally,  reporting based  solely  on  the  number of construction  completions does not
indicate the size,  complexity and cost of the respective sites, rendering  a half-million-
dollar site cleanup indistinguishable from a half-billion-dollar site cleanup. This issue was
raised by the Subcommittee in particular with respect to mega sites, which can take many
years to clean  up,  have multiple operating  units (OUs), and require tens or hundreds of
millions of dollars to complete construction.

Figure V-1,3 which  summarizes the number of construction completions  at sites  by year,
indicates that the annual rate of construction completions has varied  over time. However,
the Agency explained to the Subcommittee that the spikes and dips in the figure do not
correspond to shifts in the Superfund Program's overall level of effort or spending.4A The
1991-92 increase from 12 to 88 construction completions is considered  an artifact of an
administrative  and  accounting function.5  As a result  of its formalization of an official
definition of  the term  construction completion, the Agency was able to  identify many
cases where a  relatively small amount of work would complete the major  site construction
effort.   This  resulted  in EPA's counting these sites  as construction  completions.
Approximately  the  same rate of construction completions was  maintained from 1992 to
2000.
A Subcommittee member Vicky Peters does not support this interpretation of the data.
See Attachment A for Ms. Peters' individual statement and for the individual statement
of Grant Cope, which addresses this issue.
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90

70

50
40

20

n -
8







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8 • •
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8

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47

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  1983 1985  1986 1987 1988 1989 1990  1991 1992  1993 1994 1995 1996 1997 1998 1999  2000 2001 2002 2003 2004
                                  Fiscal Year

         Figure V-1: Superfund Construction Completions by Fiscal Year


k. Focusing on Measures to Complement and Strengthen
Construction  Completions

The  Subcommittee focused  on how the Superfund Program can  improve the way it
captures  and communicates progress  on both national and  site-specific levels  by
exploring measures  that would supplement construction completion and would more
comprehensively  reflect  significant milestones in  protecting human  health and  the
environment at Superfund sites. In doing so, the  Subcommittee members provided
individual feedback to the Agency  on  their efforts to  develop additional measures of
progress as applied to NPL sites through a work group discussion and the documentation
of individual comments.

The Subcommittee supports the Agency's attempts to improve and  better communicate
measures  of program progress and is aware  of the pressure the  agency is under to
quantify reductions in human health and environmental risks similar to measures in the
Clean Air and Clean  Water programs.  While the Subcommittee members grappled with
this issue, they were unable to reach consensus on a  meaningful, simple, objective
measure of risk reduction. Additionally, the Subcommittee did not discuss whether such
pressure from other  programs is appropriate  or whether such measures are valuable.
Superfund's site-specific nature  and complexity make the development and applicability
of such direct measures of improvement to human health and the environment extremely
difficult.
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    Understanding the Significance of Various Types of
Measures

The Subcommittee discussed the significance of the many possible types of measures of
progress for the Superfund Program.  For example, there are measures that relate to
cleanup progress (e.g. reducing hazards); overall Program performance (e.g. efficient
use of resources); and Program management (e.g.  coordination  with the public, Tribal
Nations, and state and local governments). Different measures make sense for different
purposes.  A measure of progress  should  be  meaningful to EPA and state program
managers, members of Congress,  regulators, stakeholders, and other parties  using that
measure.  Performance measures for the Superfund Program should inform the decision
making process and help those responsible for and affected by the Program make better
decisions on site-specific, regional,  and national levels.

The Subcommittee discussed the  importance  of  applying measures  to the  Superfund
Program that would address critical  aspects of a well-functioning and effective federal
program. The goals of such measures include: (1)  budget transparency—how dollars are
being  used in the Superfund  Program, and (2) general Program tracking—ensuring that
needed  information about the Program is  reliable  and  readily accessible. Current EPA
data systems do not adequately or accurately capture a number of important areas, such
as site activities, site  risks, contamination, costs (to EPA,  potentially responsible parties
(PRPs), and states), and  remedy effectiveness.  Suggestions about data and Program
tracking are also discussed in Chapter III of this report, with respect to the development
of an annual report.

The Subcommittee  discussed the  value of  qualitative and quantitative  measures.
Historically, government reporting of progress in various programs  has been biased in
favor of quantitative measures because they are perceived as easier to track and report.
Critics claim this tendency for "bean  counting" offers clear numbers, but these numbers
do not accurately represent the progress of a complex program such  as the Superfund
Program.  Others claim  that  counting  the completion  of  discrete phases of  the
investigation and  cleanup  process accurately  reflects the Program's progress toward
achieving  its goal of cleaning  up sites.  The  Subcommittee  discussed the  value  of
qualitative measures to better understand  and set the context for  quantitative  measures
that may be applicable to the Superfund Program. The Subcommittee also recognized
that the Agency is in  the process of developing more sophisticated  means of collecting
quantitative and qualitative data about the Program that in combination would allow for
more comprehensive reporting.

In the Subcommittee discussions, some members noted the respective  value of and need
for  both outcome and output measures to address  the performance  of the  Superfund
Program.  Outcomes are an assessment of the results of a program activity compared to
its intended  purpose.  Outputs are a tabulation, calculation, or recording of  activity or
effort  undertaken  to implement the  authorizing statute.   Performance measures  may
address the type or level of program activities  conducted  (process), the direct products
and services delivered by the program (outputs), and/or the results of those products or
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services - such as improvements to the environment or decreased threats to human
health (outcomes). There is an effort throughout the federal government to move away
from outputs that  measure "things" in favor of outcome measures that reflect a relative
direction or accomplishment.  However, some Subcommittee members  believe that both
outcome and output measures of performance are necessary to comprehensively track
progress  at  Superfund sites  and, on a national level, within the Superfund Program.
Furthermore, some members believe that the success of the Program can be adequately
demonstrated by evidence that releases are being addressed pursuant to the statute, and
that efforts to create other measures, gather additional data, and compile and report such
data in a meaningful way could unnecessarily divert scarce resources from cleaning up
sites.

The  Subcommittee  also  discussed the  secondary impacts  that will result from the
institutionalization  of any measures of performance. In addition  to the explicit and primary
goal of accounting for the accomplishments  of the Program,  progress  measures drive
both behavior and expectations. Therefore, it  is important to consider the positive as well
as the potentially  unintended  negative behavior modification  that may result from the
implementation of a specific performance measure.  For example, reporting construction
completions  as a  percentage of the number of current NPL sites, rather than as a total
number, may create a disincentive to list new sites.  Finally, it is important to consider the
influence that measures will have on the expectations and resulting degree of satisfaction
of interested parties, including communities, Congress, EPA managers, and the general
public.

The Subcommittee emphasized the need to be clear about the purpose of any measure
of progress  and to carefully consider the type of measure  that best addresses that
purpose.  In this chapter  of the  report, the Subcommittee has attempted  to address a
variety of types of measures and to clearly articulate its opinion of the appropriate use of
those measures.   However,  the  Subcommittee  recognizes  that developing  suitable
measures of progress is complex, and that such measures will most effectively evolve
over time through  an iterative process. The following recommendations are not intended
to be prescriptive. Ultimately EPA will need  to make decisions  about the appropriate
application of these measures and will need  to monitor whether they work as  intended
and modify them if they do not.
   Terminology

Throughout this  section of the report, the term measure  is used  to  define factors
associated with the progress of the Superfund Program. Depending on the intended use,
these measures may need to be translated into specific goals, objectives, sub-objectives,
or targets (for whose development guidance exists).  For the purpose of this report, the
Subcommittee  has  focused  its recommendations on measures, and will  rely on the
Agency to translate  the suggested measures as appropriate for the purpose of tracking
and  reporting progress in terms that meaningfully reflect  the  accomplishments of the
Program.
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   Types of Measures Framing the Subcommittee's
Recommendations

The  Subcommittee framed  its recommendations  for measuring  Superfund  Program
progress around three types of measures.

National priority measures  are "macro" measures of the Program's  progress at the
national level.  They are overall Program-level  accomplishments for  which goals,
objectives and numeric targets could  be set and  for which consequences could flow
based on whether the targets are met. Sample consequences of relevance might be how
senior  managers in the  Program are evaluated, how funding is  allocated within the
Program, and  what appropriations are provided to the Program.

Measures of Program  progress are also  measurable indicators of the Program's
progress, but  they may not be appropriate as "external targets" against which Congress
or oversight agencies would pass official judgment  on the Program's  performance.
These  additional measures  of performance  derived  from site-specific performance
profiles can be used to inform decision making, and to document significant milestones at
a variety of levels.  They also  can be packaged in a variety of ways to meet the needs of
the intended  audience.  Such  additional measures  can be reported  at the  national,
regional, state or congressional district, and site levels.

Measures  of  coordination and  collaboration  have  been  addressed   by  the
Subcommittee in this  report to  highlight a set of critical Program  measures that have
historically received inadequate attention. These are management-level measures that
reflect important elements of a successful project, and when rolled up to include multiple
sites, might be able to be used to reflect the Program's progress at a national level. The
Subcommittee has focused on measures associated with how the affected Tribal Nations,
communities,  and  state and  local  institutions are  integrated into  the decision-making
process, and the degree to which their participation in the decision-making process has
been meaningful. Generally, these measures have been difficult to quantify. The goal of
focusing on them was to underscore the need to integrate these critical elements into the
measurement of the  Program's progress so as to encourage  implementation of the
Agency's guidance.
Recommended National Priority Measures
The Superfund Program is required to report its progress to Congress, the  Office of
Management  and Budget, and  a variety of external stakeholders  for a variety of
purposes.  EPA's measures need to be simple, meaningful, and  brief.  To meaningfully
represent the  Program, national measures should address both exposure reduction and
pipeline progress.
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The  Subcommittee  recommends the following primary national measures that, in
combination,  reflect  the  significant  elements  of  the  Program's  progress   and
accomplishments.
    Recommendation  10:  EPA should apply the following National
    Priority Measures to its national-level reporting requirements:

        •> Number of sites with all final remedies selected,
        •> Number of construction completions at the site level,
        •> Percentage of  construction completions  at the  operable unit
           level, and
        •> Number of sites deleted from the NPL.
The Agency is already reporting the number of final remedies selected and the number of
construction completions at the site level.  The Subcommittee supports the continued use
of these measures.

The Subcommittee feels that deletions of sites from the NPL are reasonable, appropriate,
and important to add to the list of primary measures. Deletion from the NPL is the only
measure that reflects that all unacceptable risks from a site have been eliminated, and no
further expenditures beyond operation, maintenance, and monitoring are expected.

While  acknowledging  some  concerns  about  this  approach,  the   Subcommittee
recommends reporting  the percentage of construction completions at the operable unit
(OU) level as a national measure.  The Subcommittee recognizes that the definition and
characteristics of OUs differ among sites.  Some sites have a few very complex OUs and
some have many and less-complex  OUs.    Most  Subcommittee  members  felt  that
reporting this measure  as a percentage of total OUs, and by including site construction
completions and sites with all final remedies selected as additional measures, could fairly
reflect a useful increment of progress being made at a sub-site level, without creating an
incentive to unnecessarily subdivide sites. Accounting for the Program's progress at a
sub-site level was particularly relevant to the discussion of mega sites, where  complex
and costly sites taking years or decades to complete might  have interim milestones that
reflect  national-level priority measures or progress.  However,  some  members are
concerned that EPA will create small  OUs that can be cleaned  up relatively quickly so
that the Agency  can inflate the  percentage of OU constructions complete to satisfy
Program progress goals.  EPA should continue  to define  OUs based on site-specific
factors and conditions.

The Subcommittee also discussed the two  Resource Conservation and  Recovery Act
(RCRA) measures that are currently being used by the Agency to report RCRA program
progress at the national level: (1) the number of sites with  human exposure under control
(from  land and/or groundwater  contamination),  and  (2)  the  number  of  sites with
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contaminated groundwater migration  under control.  The Superfund Program is also
using these measures to track progress at the national level. However, the Subcommittee
raised a variety of concerns regarding why they were  not appropriate for tracking the
Superfund Program as national priority measures.  Subcommittee members, therefore,
did  not  agree that  these were  appropriate measures  of progress for the  Superfund
Program.  Additional  details on  the  range of  views among Subcommittee members
regarding  the  use of RCRA measures  for the Superfund  Program  are  included  in
Appendix VI.

Additional Considerations
Recommendation  10  is  intended  for reporting  on   NPL  sites only, because the
Subcommittee believes it is inappropriate to integrate data from sites being cleaned up
under other programs  or strategies, even if Superfund  dollars are spent.  In  particular,
members were concerned about reporting Superfund Alternative Sites (SAS) as equal  to
those on the NPL.  Additional details regarding  the Subcommittees perspectives on the
SAS are included in Chapter VI.

The  Subcommittee  discussed  how to reflect  "reopened"  remedies  in measures  of
performance.   Remedies can be reopened for  a number of reasons, such  as remedy
failure due to error in judgment or insufficient data, failure of innovative technologies  to
achieve  performance standards,  or discovery of new,  more cost effective technology.
While tracking inadequate  remedies could  provide important lessons for the Program,
members  did not want to discourage the  use of innovative technologies,  or provide
disincentives to reopening any remedies that warranted it.  Therefore, members did not
agree to include a separate national priority measure  to capture the  number of sites
where remedies had been  reopened.  However, the running tally of national measures
must be corrected to reflect the actual conditions at each site. For example, if in a given
year EPA  completes construction at 40 sites, but selects new technologies  to address
problems  at three sites previously  considered  complete, the Agency would report 40
construction  completions  for that  year.   The cumulative  numbers  of construction
completes recorded  for the respective prior year periods, however, should be  adjusted  in
the  annual report, thereby reflecting the fact that additional construction work would be
conducted at sites previously considered complete.

 The Subcommittee  considered the reduction of threats  to the environment an important
goal of the Superfund Program and discussed many options for possible national priority
measures  of progress toward that goal. Members recognized that determining progress
toward this Program goal is an extremely complex undertaking,  but could not agree on
how to measure it and ultimately chose not to include it in their recommendation.  The
Subcommittee did  agree that if  an  appropriate CERCLA-specific ecological measure
could be  developed,  it should  be included  as  a  national priority  measure.    The
Subcommittee supports the Agency's continued  efforts to develop effective indicators  of
progress toward protecting sensitive  environments.

Some sites are much more  complicated than others.  Accounting equally for very large
complex and  costly sites as for small and  straightforward sites may cause difficulties.
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One option  suggested by the Subcommittee was to  note progress  on mega sites
differently from progress on other sites in order to more accurately reflect the significance
of those accomplishments and acknowledge that mega sites are expected to take longer
to investigate,  develop remedial options for, and ultimately clean up.B  However, EPA
should continue to provide incentives to  expeditiously complete cleanup activities at
these sites.
Measures of Program Progress
The Agency has been developing improved performance measures in parallel with the
work of the Subcommittee. EPA's development of the Performance Profile (June 2003)
reflected  much of the feedback received previously from Subcommittee  members.  A
mock-up of EPA's working draft of the Performance Profile is included in Appendix V. The
Performance  Profile  is consistent with  the  recommendations  throughout this  report,
particularly those addressing  transparency,  communication  with  communities, Tribal
Nations and states, and annual reporting.

The following material addresses a variety of types  of measures  identified to provide
feedback to the  Agency on how to more comprehensively  document and report the
accomplishments of the Program. As such, they are intended to:

    -* Inform decision making,
    -* Track and report progress at a variety of Program levels,
    -* Increase comprehensive budget transparency,
    -* Document the achievement of significant milestones,
    -* Communicate the accomplishments and effectiveness of the Program to a variety
       of audiences, and
    -* Create incentives for positive behaviors.

Some  measures reflect hazard reduction, some  reflect standards for good  Program
management, some reflect pipeline performance, and some help to characterize the site.
This input is provided with  the important caveat that many members of the Subcommittee
believe the Agency's  efforts to  measure and report progress should not divert significant
resources away from actual cleanup  in the field.

The measures discussed  in this section  could be  reported  in a variety of ways for a
multitude  of intended purposes   and  audiences.    During  its  deliberations,   the
Subcommittee referred to the national and site-level Performance Profile as an example
of one way EPA could package data.   Other formats were also considered  by the
Subcommittee.
B Subcommittee  member  Vicky Peters supported this  perspective  if the  same
measures are used for mega sites as for other sites.  These could then be compiled
and tracked separately for  mega  sites.  See Attachment A for Ms. Peters' individual
statement.
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The Subcommittee believes that developing and systematically reporting against a core
set of measures  is critical to  both accurately portray the progress of the Program and
communicate that progress to intended audiences. The Subcommittee therefore makes
the following recommendation:
    Recommendation 11:  EPA should continue with its efforts to
    develop and implement a system to ensure clear, transparent
    dissemination of a core set of data for all NPL sites and Superfund
    Program activities.
The Subcommittee believes that the Agency should focus on ensuring accurate reporting
on a core set of data for all NPL sites.  In the future, as the capacity of the Program's
tracking system  increases,  it should be  expanded  to include other  sites receiving
Superfund funding.  Some Subcommittee members also believe that such a system could
be used to effectively track sites that have been identified as potential NPL candidates.
However, the Agency should distinguish  the reporting of NPL sites from non-NPL sites.
For example, data  associated with Superfund Alternative  Site cleanups and cleanups
being implemented under other cleanup programs should be distinguished from NPL site
data.

The  Subcommittee recognizes  the complexity of effectively  developing, tracking  and
reporting measures. The Agency should implement the efforts  underway immediately as
part  of  an  iterative  process that  includes mechanisms for making improvements as
needed  in the future. For example, measures could undergo pilot testing and peer review
by  knowledgeable  individuals  and  organizations  prior  to  widespread adoption.
Additionally,  the  Subcommittee recommends the Agency extrapolate  the  site-specific
results to reflect regional and national progress and report the  results annually  so the
information   can  reflect   incremental  improvements.  Additional  details  on  the
Subcommittee's  recommendation   on annual reporting are  included  in  Chapter  III,
Recommendation 5.

Many Subcommittee members emphasized the value of limiting the data set to the most
meaningful information and only to information that can be reported in an easily readable
format.   However,  Agency  staff explained that  the  suggested data  could easily  be
translated into a variety of formats and that the total number of measures was not limited
by potential space constraints.  The  Subcommittee  encouraged the Agency to use the
core data set for other purposes, including, but not limited  to: on-line,  site-specific
reporting tools accessible to  the public; a 1-page report-card that would score a site and
allow comparisons among sites; and longer fact sheets for site stakeholders looking for a
comprehensive overview of  their site.  Some members of the  Subcommittee  saw the
ability to compare across sites as a significant value for EPA managers,  community
groups,  Congress, and other stakeholders. Different data sets may be appropriate for
different purposes.  However, the Subcommittee does not intend to create  an unwieldy
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data reporting  and tracking system.  A critical assumption driving the Subcommittee's
support for increasing the core set of data and encouraging a variety of applications is the
understanding  that such a  system could  be highly automated.  The Subcommittee's
understanding  is that the majority of the data could be efficiently downloaded from the
existing tracking system and automatically reported in a variety of formats.

Given  the  Agency's flexibility in  terms of the reporting format,  the Subcommittee
recommends that the Agency track additional measures (for which data currently exist),
and, in the future, add measures for which data do not currently exist but can reasonably
be obtained. While the  Subcommittee agreed to the value of  additional data, it did not
reach  consensus  regarding which  additional  items  should  be tracked.   Individual
members  offered  many suggestions as  examples of data  that could  increase the
effectiveness  of the Performance Profiles  or provide valuable  information  for other
purposes  as  described above.  The extensive list of ideas  and supporting text are
included  in  Appendix  VII.   (This  list does  not  represent  the  consensus  of the
Subcommittee, but reflects the compilation of individual suggestions  by of a number of
participants)

Given  that  measures  of  progress  and  performance  drive decision  making  and
expectations at the site  and Program levels, the measures being utilized to evaluate the
Program need to be consistent with the management goals and priorities that are guiding
the work being conducted.  Therefore, the  Subcommittee worked to ensure that the
recommendations in  this chapter of  the report  are consistent  with  the site  listing  and
management recommendations presented in other chapters.
Measures of Coordination and Collaboration
To highlight a set of critical Program elements that have historically received inadequate
attention, the Subcommittee focused on  issues associated with how affected Tribal
Nations, communities, and state and  local governments are integrated into the decision-
making process,  and the degree to which their participation in decision-making has been
meaningful. The  Subcommittee  realizes that there  are  many important elements of an
effective national Superfund Program and successful project  management. For example,
effective coordination with PRPs is also critical to the success  of the Program and the
quality and frequency  of such coordination can be  improved  by the Agency.  However,
the decision to focus on Tribal Nations,  communities, and state and local governments
was made not because it is more  important than these other elements, but because it
was seen  by many  Subcommittee  members  as  equally  important and  historically
underemphasized.   While all members supported the principles and recommendations
set forth in this section of the report, some members believed that the scope should have
been  expanded to  explicitly include measures that indicate  the effectiveness of EPA's
coordination with PRPs while other members believed that measures and data that are
currently available provide a reasonable indication of the effectiveness of the EPA/PRP
relationship.
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   Coordination with Tribal Nations, State and  Local
Governments and Communities

Effective  and efficient partnerships with  all  parties are critical to the success of the
Program and making good decisions regarding the listing and management of NPL sites,
leveraging existing resources and sharing the burdens of site cleanups.

Two expert panels helped to inform the Subcommittee on these  matters.  The comments
received  from  these  panels and  members of the public were very relevant to the
development of this section of the report. On January 7, 2003, in Washington, D.C. a
panel  of representatives of Tribal Nations appeared before the Subcommittee, and on
June 18, 2003 in New Bedford,  Massachusetts, a panel of Environmental Justice experts
appeared before the Subcommittee.  Their testimony and  that  of the public helped the
Subcommittee  understand the  concerns  and   complex  challenges  facing  these
underrepresented populations at NPL sites.  The following recommendation is intended
to address such concerns and challenges.
    Recommendation 12:  EPA should develop measures of
    performance that assess the effectiveness of Agency coordination with
    Tribal, state and local governments and community stakeholders.
By engaging a wide variety of perspectives in decision-making throughout the process,
the Subcommittee believes that EPA will gain better understanding of the problems and
issues posed by each site, and as a result will reduce the likelihood of delay caused  by
last-minute objections or new information from communities that would  have improved
decision making.  There are roles, authorities and jurisdictions unique to each of these
parties, and any proposed measures would supplement, document, and encourage the
appropriate  coordination and involvement in  decision  making  required by  these
established relationships.

Communities affected by the decisions made under Superfund are an integral part of the
decision-making process at both  the site and the national  levels.  While EPA reflects
support for this principle in  various guidance documents and has done  important work
recently in developing a collaborative model for work among communities, business and
governments on specific projects,  the practice of implementing guidance remains uneven
across  the country. Therefore, the Subcommittee's recommendations  are intended  to
reinforce  and  highlight the importance of the effective policies and  guidance that have
been developed to date by the Agency.  The Subcommittee believes it would be helpful
to emphasize the importance of meaningful Tribal, state  and local government and
community participation by 1) measuring the success related to such  participation, and 2)
more aggressively incorporating the concept into the Program's day-to-day management.
Recommendations related to both  of these approaches are included below.
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Measuring  the  quality of engagement  of stakeholders is  inherently difficult.  Many
traditional measures of public involvement have historically focused on formal "notice and
comment"  requirements  that represent nothing more than checking  a  box.   Such
measures can be useful in ensuring that certain activities and contacts are made, and the
Subcommittee continues this tradition to some extent with its recommendations aimed at
implementing existing  guidance.  However, this "check list" approach does not illuminate
the question of whether the engagement  is meaningful or merely perfunctory. Yet, clearly
there is  a  range in  the  impact,  quality, or thoroughness  of public participation  and
institutional coordination and involvement achieved among  Superfund sites.  Doubtless
there also is considerable variation in the interest of various publics and institutions in the
process,  ranging from indifference at some  places  to  intense  concern about or even
opposition to Agency procedures, decisions or actions at other locations.

The Subcommittee does not intend for EPA to measure the extent to which communities
are wholly  satisfied with  remedy decisions.  Communities are not monolithic and  may
reflect as many different opinions regarding the ideal remedy as there are participants at
the table.  Some of these views may be related to  issues other than the fundamental
questions of cleanup levels and technologies.  For example, traffic disruption, utilization
of local work force,  and end  uses of  a site can  be  of local  concern.   Rather, the
Subcommittee believes that EPA should attempt to capture whether communities believe
that (1) they have had an opportunity to  participate meaningfully in the remedy selection
process,  and that their input was considered and incorporated appropriately - even if
every participant did not get everything desired; and  (2) the decisions reached will most
likely prevent unacceptable risks to public health and the environment.

In the  cases of Tribal nations and  state and  local governments, the  Subcommittee
believes that a measure to indicate whether they "felt that EPA made a sincere effort to
cooperate/coordinate with you  on the  site" would be an appropriate  supplement to the
aforementioned questions in order to gain a more accurate measure of the effectiveness
of their relationships with EPA.

While investing  in  these activities diverts  resources  from on-the-ground   remedial
activities, most  members of the Subcommittee believe that coordination with Tribal
Nations,  communities and  state and local  governments  is integral to an  adequate
analysis  of  alternatives and  (similar to  remedial design) is  necessary to  ensure that
remedies will be effective and implemented in an efficient and timely manner, and  may
reduce the  need to re-design or reopen the remedy selection process at a later date.  In
the long  run, therefore, functional relationships with  all stakeholders  can help to speed
cleanups and reduce overall  costs.  However, some members of the Subcommittee felt
strongly that the Agency needs  to increase its allocation of resources toward on-the-
ground cleanup. A better understanding of the resources required to implement these
coordination recommendations  is necessary for the Agency to make decisions regarding
prioritization of its resources.
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National Performance Measures Versus Site-Specific Evaluation Tools
Similar to the site-level and national-level performance profiles addressed in the previous
recommendation, the Subcommittee recommends that the effectiveness of the Agency's
engagement  with Tribal  Nations,  state  and  local governments, and communities be
considered  at multiple levels.  A national performance measure along with site-specific
evaluation of the Agency's activities serve distinct and important  purposes related to
evaluation of Program success while simultaneously offering valuable management tools.

The Subcommittee discussed a number of potential metrics and approaches designed to
capture whether input from state and local governments, Tribal Nations, and  communities
were  appropriately considered by EPA.  It concluded, however,  that none of these
objective, measurable approaches would yield unambiguous,  usable  data. As a result,
the Subcommittee has decided that direct questioning of target audiences is most likely
to provide the information sought.  The Subcommittee acknowledges  that the design of
surveys  (and similar data  collection  tools) and  implementation of these tools  is a
specialized  discipline that is not represented among its  members. Therefore, members
do not believe they are qualified to identify the precise method and questions to be used
by EPA.  Nevertheless, they believe that the core issues that should be addressed by a
site-specific survey with data compiled at the national level are:

   -* Whether stakeholders  believe they  were offered sufficient opportunities  to
       provide meaningful input,
   -* Whether their input was thoughtfully considered and incorporated as appropriate,
       and
   -* Whether stakeholders believe that human and environmental  health have been
       or will be protected by measures taken pursuant to the Superfund Program.

By posing these questions to representatives  of affected communities, Tribal Nations,
and state and local governments at a site-specific level and aggregating the results at the
national  level, EPA could  use such  metrics to measure overall  Program success and
reflect incremental change or improvements.  The most meaningful interpretation of these
results will  be comparative over subsequent years.  As EPA's outreach improves, the
Agency  should  expect  the responses to  these  questions  to be  more  favorable.
Furthermore, aggregating  and interpreting results across  stakeholders by sites and
ultimately across the nation, will represent the whole range of views and reveal general
trends.  The  underlying  data would need to be  analyzed more particularly to discover
specific trends and perhaps areas or constituents  in need of improved communication.

Actual implementation of survey  tools  is likewise best left to experts.  However, the
Subcommittee is  aware of existing efforts to  implement such surveys and offers the
following  suggestions to improve the effectiveness of the efforts to  date:

   -* The collection of such data should be made as easy and convenient as possible,
       so as not to create an unwieldy administrative burden on the Program.
   -* To the extent possible, EPA should collect this kind of feedback through existing
       forms, interviews, public meetings, and other communication mechanisms and
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       tools,  as  opposed  to developing duplicative  new tools  for collecting data.
       (Specific examples of such tools are identified in the next section.)
    -* Technical  assistance grant (TAG) recipients should be asked to provide answers
       to these core questions (online options should be available) along with their other
       reporting duties.
    -* Community  Advisory   Groups  (CAGs)  should  be  asked  to  provide input
       (recognizing that in most cases they are  not receiving funds from EPA and may
       have very limited resources).
    -* Input should be sought not only from the  most active participants but also from a
       representative sampling  of entire affected  communities,  including the local
       governmental officials.
    -* Care should be taken to  distinguish feedback from residents  most directly
       affected by the contamination and decisions at the site.
    -* Data should  be  collected  so  as to  enable  separate  analysis and reporting of
       results for mega sites, federal facilities,  fund-lead versus PRP-lead sites, TAG
       recipients, CAG members, immediate neighbors to facilities,  and other categories
       as may be identified as distinguishable, as well as totals for the entire Program.

Site-Level  Measurements and Management Tools
Some  members  of  the  Subcommittee  also recommend  that the  Agency  provide
incentives to implement existing guidance and  policies by measuring the success of
these efforts on a  site-specific basis. For example, the Agency should maximize the  use
of the required community interviews and Community Involvement Plans by:

    -* Targeting  a broad  set of  key  stakeholder  audiences and  Natural Resource
       Trustees  during  the  community  interviews  and  during  the   design  and
       implementation of the community involvement plan;
    -* Making community involvement and institutional  coordination more integral to  site
       management; and
    -* Integrating community involvement  and institutional  coordination factors  into
       reporting requirements.

Additionally, the Agency should increase its emphasis on the implementation of site-level
efforts underway, including site-specific community effectiveness surveys ("What Do You
Think about EPA's Community Involvement Efforts at X  Site?" in Attachment 5C.),  and
the questionnaire  templates that have  been developed  for CAGs, listening sessions,
public meetings and community interviews. These tools can collect  valuable information
about the Program's  effectiveness and have the  potential  to better inform decision
making at the site and regional levels. Therefore, these members of the Subcommittee
believe that EPA should implement the following guidance:

    -* Target a  broad set  of  key  stakeholders  in  the  distribution  of the various
       evaluation tools.
    -* Take advantage of existing mechanisms for the circulation, communication  and
       collection  of results from various tools to  minimize additional  expenditures.
       Consider hand delivery of survey forms.
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    -* Aggressively apply the tools to mega sites in particular. Outreach may be more
       complex and expensive to  administer at some  of  these sites  due to the
       distribution of affected  individuals over large geographical areas.  However, the
       costs of bad or delayed decision-making are likely to be higher at such sites as
       well.
    -* Prioritize Environmental Justice  communities  as a primary target for outreach
       efforts.
    -* Increase the number of surveys conducted at sites (14 have been completed)
       and  do not limit surveys to sites at which community coordinators or  remedial
       project managers request them.
    -* Dedicate  additional  resources  to  survey administration,  interpretation,  and
       distribution of results.
    -* Carefully consider the timing of such surveys.   It may be that feedback—
       especially from large, expensive  sites—would be useful at least at the  remedial
       investigation, feasibility study, and record of decision stages.  Surveys related to
       inactive sites also could provide valuable input.
    -* Provide respondents the opportunity to submit information anonymously.

EPA may also  want to  consider collecting information from PRPs and perhaps  other
sources (regarding  their experience), in order to accurately and comprehensively capture
the nature of Tribal, state and local  government, and community engagement at the site.
In particular, the perspectives of all  of these entities regarding the  responsiveness of the
Superfund Program could be useful if supported with concrete examples of modifications
made to decisions based on input received from communities and institutions.

Some Subcommittee members also recommend that the Agency continue to invest in the
development and  implementation  of tools  for  conducting,  tracking and  evaluating
community and Tribal involvement,  with a view toward  increasing awareness throughout
the Agency  of the value and  benefits of the perspective  of these stakeholders.  For
example, the Agency may want to consider sensitivity training and environmental justice
training for its regional project managers.

Finally, some members  of the Subcommittee recommend that the Agency explore the
option  of engaging  independent  reviewers  or  outside  consultants to evaluate the
effectiveness of Tribal, state, and local government, and community coordination efforts,
and initiate a national dialogue to further explore these issues, as described in Chapter
VI.
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1 Reported by EPA in the Charge to the NACEPT Superfund Subcommittee
2 2003-2008 EPA Strategic Plan: Direction for the Future, U.S. Environmental Protection
Agency, September 30, 2003, pre-publication copy.
3 Revised version provided to the Subcommittee by EPA via email 1/20/04
4 Reported  by the Agency as an  explanation  of Figure 4-1 to the Subcommittee in its
November 2003 meeting.
5 The term  construction complete was  codified in the NCP Federal Register notice of
March 8, 1990.
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  VI.
Additional
Priority Issues
      As indicated earlier, the Subcommittee was established to help EPA shape the
      future of the Superfund Program by providing advice on the role of the National
      Priorities List (NPL), how to manage mega  sites, and  how to measure the
Program's  progress and performance.  During their deliberations, the Subcommittee
members identified several additional issues that they felt are important to the success of
the Superfund Program and should receive serious consideration by EPA and others
interested in the Program.  In some cases, the topics were beyond the Subcommittee's
ability to fully deliberate or reach consensus on within the time available. In other cases,
some Subcommittee members thought that the topics were outside of their areas of
expertise.  Despite these limitations, the Subcommittee wanted to bring these issues to
the attention  of those interested in the  Superfund Program and believe they should be
part of the  continuing dialogue  about the Program.   In  some cases, consensus
recommendations have been developed to address these issues, and in other cases the
Subcommittee was unable to reach consensus and therefore offers a range of views on
the following:

   -* Emphasizing prevention;
   -* Ensuring adequate financial assurances;
   -* Examining the roles of the Agency for Toxic Substances and Disease Registry;
      (ATSDR) and the National Institute of Environmental Health Sciences (NIEHS);
   -* Increasing the effectiveness of land-use controls and long-term stewardship;
   -* Determining the need for input on the Superfund Alternatives Sites; and
   -* Continuing the discussion of important national issues
         >  Issues unique to cleanup at federal facilities and
         >  Effective community involvement.
Deliberations on Emphasizing Prevention
The topic of pollution prevention was not specifically part of the Subcommittee's Charge.
However, some members of the Subcommittee believed that this topic was relevant to
address in the report because of its focus on sites that could be considered for the NPL
and the desire to prevent the need for major cleanup at facilities in the future. While all
members held a common interest  in preventing the  creation  of new Superfund sites,
some felt that the Resource Conservation  and Recovery Act  (RCRA), rather than the
Comprehensive Environmental Response,  Compensation and Liability Act (CERCLA),
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was the appropriate statutory authority and that given CERCLA's focus on cleanup, the
topic was outside of the scope of the Subcommittee's charged

The federal government, states, Tribal Nations, and other jurisdictions have statutory and
regulatory programs designed to promote safe management of hazardous materials.  In
addition,  many private  companies and facilities  have integrated  significant  pollution
prevention steps into their everyday operations with marked success.   In other cases,
however, because of either  a lack of adequate enforcement  or  a lack of sufficient
environmental controls,  contamination  continues  to  occur at some facilities.   If not
addressed, this contamination could turn into a  major cleanup need  at some operations.
In addition, where insufficient financial assurances have been  provided,  some cleanups
could get shifted to the NPL, further burdening an  already overstretched Program. While
pollution prevention efforts will not prevent all sites from being added to the NPL, such
measures could reduce the numbers of sites that  might otherwise be listed.  To address
these concerns, the Subcommittee  believes that EPA  should take steps  both to prevent
the creation of sites that may need cleanup in  the future and to prevent sites that  may
need  clean  up from having  to  draw  upon the  financial resources of the  Superfund
Program.

Some members of the Subcommittee believe  it  would be prudent for EPA to identify
prevention techniques across all programs to determine if their application to Superfund
would prove useful.  Further, EPA should  review sites added to the  NPL in recent years
to determine whether trends exist with  respect to  contaminants, types of sites and other
characteristics so  as to  assess whether a stronger focus on pollution prevention could
have kept those sites from becoming Superfund  sites.  The information from such a
review could potentially be used to strengthen  the  focus on  pollution prevention  in
Environmental Impact Assessments and Statements.

The intent of this analysis is to support the development of guidance to the Regions and
states for a  renewed focus on pollution prevention.  In  addition, the results of such an
analysis could support efforts by the Agency to  improve financial assurances so that,
over time, fewer fund-lead sites would be created. (See the following discussion in this
hapter on financial assurances) This effort should not be so intensive that it unduly drains
resources from the goal of cleanup.

EPA should  undertake pollution prevention reviews in  an open and  transparent fashion.
Communities located near facilities have  a  long-term  interest  in working with EPA and
industry to  promote pollution  prevention programs that provide opportunities for sound
economic development, while reducing threats to public  health and the environment.
Similarly, companies that engage in  pollution prevention  activities  have an interest  in
ensuring that all companies undertake  such  measures in order to ensure  a level playing
field.
A Subcommittee member Richard Stewart supports this view.  See Attachment A for
Mr. Stewart's individual statement and elaboration on his position.
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Deliberations on Ensuring Adequate Financial
Assurances
While the Subcommittee as a whole did not spend considerable time researching or
deliberating the complex issue  of financial assurances, to try to ensure that currently
operating  facilities  do not need  Superfund  dollars for  cleanup  in the future, some
Subcommittee  members felt that the issue was integral to the role of the NPL. B These
members believe that the role of the NPL should not be focused on newly contaminated
sites; rather, existing programs should prevent and rapidly respond to such contamination
as it happens.  Other members of the Subcommittee felt that the topic was outside of the
scope and areas of expertise of most of the members and, therefore, was inappropriate
to address in this report. Additionally, while the scope of the Subcommittee was focused
on Superfund,  some members felt that the scope of the recommendation should not be
limited to Superfund sites, since this approach could be used to prevent the creation of
future NPL-caliber sites.

Members who  felt that the issue should be addressed  by the Subcommittee were very
concerned about the adequacy, quality, and long-term  stability of financial  assurances.
These members believe that EPA and the states should develop the skills to rigorously
and uniformly evaluate proffered financial assurance in a manner consistent with the best
financial practices used by the financial industry.  Some of the Subcommittee members
suggested that the EPA look to the evaluation  procedures and techniques (such as those
employed by  Moody's, A.M. Best, and Standard and Poors) to  ensure  EPA  and its
delegate  administrators accept only financial assurance of the highest quality.  Any such
process should include both initial and  periodic reviews, in accordance with  financial
industry standards.   EPA  headquarters should  develop guidelines to implement the
rigorous process outlined above for the use of regional and delegate administrators.

Specifically, the Subcommittee members who supported addressing this issue proposed
that EPA undertake  efforts to enhance and implement financial assurances that can be
used for Superfund sites  in order to reduce  Program  expenses, encourage timely
settlements with viable and cooperative PRPs, and prevent the creation of new orphan
shares. They pointed  to  Section  108(b) of Superfund, which requires EPA to create
regulations mandating financial assurance for facilities.0
B Subcommittee member Vicky Peters agrees that improved financial assurances is
integral to the charge from EPA; in particular, the role of the NPL.  See Attachment A
for Ms. Peters' individual statement.

c Subcommittee member Vicky Peters  agrees  with  the perspectives presented in
support of the implementation of financial assurance measures.  See Attachment A for
Ms. Peters' individual statement.
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Examining the Roles of ATSDR and NIEHS
During the Subcommittee's deliberations, the relationships of both the Agency for Toxic
Substances and Disease Registry (ATSDR) and the National Institute of Environmental
Health Sciences (NIEHS) with the Superfund Program were initially raised in the context
of analyzing the Superfund budget.  In the  opinion of some of the Subcommittee
members, the ties  between these  agencies and  the  Superfund  Program  in terms of
funding and  the potential to influence site listing and management decisions justified
additional inquiry into the potential to increase program efficiencies and effectiveness.
   ATSDR Background

ATSDR was created in 1980 by CERCLA. As reported to the Subcommittee,1 ATSDR is
the principal federal public health  agency charged with evaluating the human health
effects of exposure to hazardous substances. ATSDR's mission  is to prevent exposure
to—and adverse human health effects and diminished  quality  of life  associated with
exposure to—hazardous substances from waste sites, unplanned releases, and other
sources of pollution present in the environment. ATSDR carries  out its  mission through
programs in public health assessments, consultations and studies, exposure and disease
registries, toxicological profiles, applied research, health education and  communication,
emergency response, and emergency events surveillance.

ATSDR evaluates the  potential health impacts at  hazardous  substance sites  or spills
through its public  "health  assessments" or  "health  consultations."   ATSDR health
assessments on sites include the following:

    -* An evaluation of the information available about site-specific contaminants,
    -* A determination of whether people might be exposed to  environmental  hazards
       from the site,
    -* A determination of what harm exposure to site contaminants might cause, and
    -* Recommendations for actions to protect people's health.

ATSDR and EPA respond to site-specific environmental concerns from  private  citizens,
as well as state and federal agencies to determine if there is  a  completed exposure
pathway, if there have been  prior  exposures, and the possible  health  effects  of such
exposures.    Depending on  the   existence  of or potential  for  exposures,  ATSDR
recommends or performs appropriate prevention and follow-up health activities.
   NIEHS Background

In  1966, the U.S. Surgeon General established the Division  of Environmental Health
Sciences as a  part of the National Institutes  of Health.  In 1986, under the Superfund
Amendments  and  Reauthorization Act,  Congress established  two  programs—the
Superfund Basic Research and Training Program (SBRP) and the Worker Education and
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Training Program (WETP)—to be managed within the National Institutes of Health (42
U.S.C. §9660).   NIEHS provides  funds  to  universities and  nonprofit  institutions to
accomplish the goals of both these programs.  Currently, there are 19 SBRP grantees
and 18 WETP grantees.

As reported to the Subcommittee,2 the SBRP is a university-based  program that supports
basic research and training grants in the area of risk assessment.  This research  is
designed  to address  the wide array  of scientific  uncertainties facing  the  national
Superfund Program. The goal of supporting research in this area is to provide a better
understanding  of contaminant toxicity issues,  so that emerging data can be integrated
into risk assessment and remediation decision making.  The primary objective  of the
WETP is to fund nonprofit organizations to provide high-quality training to workers who
are involved in handling  hazardous substances or in responding to emergency releases
of hazardous materials.

ATSDR and the two  programs  under NIEHS received their funding as pass-through
money from EPA until 2001,  when Congress chose to appropriate the funds for these two
programs  directly to the respective agencies.   Even  though the  appropriations are no
longer tied to  EPA's funding, CERCLA reflects Congress' intent that the information
generated and  services performed by ATSDR  and NIEHS would contribute to the goal of
appropriately identifying and cleaning up national priority sites. Furthermore, the money
previously appropriated to EPA for these agencies was subtracted from the  EPA budget
for conducting  Superfund activities.  Given the emphasis placed  on identifying  current
human health  threats  posed by releases  of hazardous  substances, it is imperative to
maximize  the utility and effectiveness of the  activities of these programs,  in particular
ATSDR, which  was specifically created to focus on human health issues at proposed and
listed  Superfund sites.  It is the experience  of many of the members of the Subcommittee
that the mission of these agencies,  with respect to their support for the Superfund
Program, has not been fully realized.

In August 2003, the Subcommittee sent to NIEHS and ATSDR a short list of fundamental
questions  regarding  the functioning  of their programs,  to  establish  a common
understanding  of the responsibilities of the agencies and the relationship between their
efforts and those of the Superfund Program.  The  intention was to build upon  that
common understanding to identify strengths and shortcomings in  the existing Program,
and to develop suggestions for EPA to improve the relationship and maximize efficiencies
with regard to  interrelated activities.  In  response to these requests, the Subcommittee
received the written correspondences referenced above.  In addition, Dr.  Henry Falk,
Assistant Administrator for ATSDR and Ms. Beth Anderson, Program Analyst of NIEHS,
participated in the Subcommittee's November 4, 2003, meeting.

Given time constraints, the breadth of its charge from EPA, and the difficulty obtaining the
necessary information, the Subcommittee was unable to delve into these issues to the
degree that many members desired. With the limited information provided, along with the
direct experience  of some Subcommittee members,  these  Subcommittee  members
identified a number of recommendations for  EPA related to the work of ATSDR  and
NIEHS.
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    Recommendation  13:  EPA should improve its cooperative
    relationship with ATSDR.  EPA in coordination with ATSDR should
    make a concerted effort to work with affected communities, states, and
    Tribal Nations to regularly identify, on a site-specific and nationwide
    basis, projects and research efforts that would be most helpful in
    determining adverse health  effects posed by releases of hazardous
    substances, thereby informing decisions  related to NPL listings,
    investigations,  and remedy selection and implementation.  EPA should
    include recommendations both in proactive suggestions for projects,
    and in reactive comments on ATSDR proposed projects.  ATSDR's
    responsiveness to these recommendations should be included in
    EPA's (annual) reporting.
Some members of the Subcommittee representing community, environmental justice,
state and  public interest perspectives believe that many stakeholders, particularly,
communities, have the perception that ATSDR is not adequately responsive, and its work
products are not useful  in understanding adverse health  effects and risks posed by
hazardous substance releases at Superfund sites. Dr. Falk informed the Subcommittee,
that his agency has a formal liaison with EPA, and tries to perform work projects where
requested by EPA. While coordination seems to take place at high levels between the
agencies, it is the perception of many Subcommittee members that such coordination
does not appear to consistently or effectively influence decision making at the site level.
Other members of the Subcommittee believed that the information presented for review
was insufficiently balanced to reach this conclusion.

To better match the output of ATSDR with reasonable expectations and the needs of the
Program and its stakeholders, the Subcommittee would like  EPA to be more proactive in
targeting the research efforts of ATSDR. For example, conducting in-depth body burden
studies of community members known to have the greatest exposure to a release could
provide greater  benefit to the community and EPA decision makers than  a cursory
summary of existing environmental and risk data for a site.  Such targeted  biomarker
studies could provide site-specific information more quickly,  in time to influence the early
decisions that must be  made for characterizing and  managing sites.  This  has the
potential to  save time and money, and to reduce impacts on  human health.  Under
ATSDR's interpretation of CERCLA, either of these activities would satisfy its mandate to
perform a health assessment at each NPL site.
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    Recommendation 14:  EPA should establish a transparent and
    cooperative relationship with NIEHS to provide recommendations and
    rationale for research, and to become educated on the efforts and
    findings of NIEHS.  In so doing,  EPA Site Managers and Community
    Involvement Coordinators should be educated as to the resources
    available from NIEHS (and ATSDR) and should always inform the
    community of these resources.
The Subcommittee respects the role of NIEHS in performing basic research.  However,
from the perspective of many stakeholders in the Superfund process, this role appears to
be divorced from the issues  and  needs of the Superfund Program  and  its affected
stakeholders.  EPA's views regarding  useful research initiatives should be provided to
NIEHS in a meaningful way, and the results of such research should  be referenced in
EPA's [bi] annual report. If such involvement is already taking place, the process should
be made more  transparent to affected stakeholders who may  have an  interest in
providing input and/or tracking the  results.   Such an effort is likely to  result in broader
application of the research and decreased duplication of research and reporting efforts.

EPA is the  agency with the most  direct and continuous  interaction with states, Tribal
Nations, and communities.  Therefore, EPA is in the best position to ensure that these
stakeholders are informed regarding the  potential available resources  and health
information relevant to site cleanups. Health issues are frequently the issues of greatest
concern to affected communities.   While NIEHS is primarily involved in basic research
and training, the  studies it funds address concerns at specific Superfund  sites. A process
to  convey the NIEHS findings to the field is lacking  and should be implemented,
especially in those communities with contaminants studied under NIEHS  funding.
    Recommendation 15:  EPA, working with ATSDR and NIEHS,
    should convene a national dialogue on the role of ATSDR and NIEHS
    in the Superfund Program.
Specific decisions regarding the most useful activities to be performed at a site will need
to be made at a local level. However, ATSDR and NIEHS have several responsibilities
that relate to national  issues, such as the compilation of toxicological profiles and the
Disease Registry.   For such national issues, and to better understand  and define
priorities,  best  practices,  and  lessons learned in performing site-specific studies, the
Subcommittee believes EPA should obtain input from stakeholders—in particular, states,
Tribal Nations, and communities through a national dialogue on the role of ATSDR and
NIEHS  in the Superfund Program.  This dialogue should be conducted in cooperation
with all the agencies  involved  and  could take the  form of a series of workshops or
meetings  culminating  in  collaborative thinking or  position statements (as  deemed
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appropriate by EPA). The findings and conclusions from this effort could be incorporated
into the proactive agenda-setting suggested in Recommendation 13, above.
   Guidance for Declaring Public Health  Emergencies

Some Subcommittee members believe that one of the primary concerns expressed by
affected communities relates to obtaining credible information on the possible health
effects resulting from exposures to hazardous substance releases, and on the medical
alternatives to  address  those health effects.   Such medical care and testing are
referenced in CERCLA, 42 U.S.C. §104(I)(1)(D) and (E), which provide as follows: "in the
case of public health emergencies caused or believed to be caused by exposure to toxic
substances, provide medical care and testing to exposed  individuals...."  However, the
services that can be provided,  and the circumstances under which such services can be
provided  are unclear.   Therefore, while consensus on  a  recommendation was not
reached,  some members of the Subcommittee believe that EPA, in cooperation  with
ATSDR, should create guidance that describes:  (1) the agency or agencies responsible
for  declaring "public health   emergencies" under  CERCLA,  including  42 U.S.C.
§104(i)(1)(D) and (E); and (2) the criteria that an agency or agencies will use to declare
such a public health emergency. This guidance should also describe how and when the
federal government intends  to implement  its  statutory  duty under §104(i)(1)(D)  of
CERCLA to, "in the case of public health emergencies caused or believed to  be caused
by exposure to toxic  substances,  provide medical care  and  testing  to exposed
individuals...," and  provide for "admission to hospitals and other facilities and services
operated  or provided by the  Public Health  Service,"  as  such facilities are  no longer
available.  EPA and ATSDR should develop this guidance in an  open and transparent
process that involves the representatives from  the Department of Health and Human
Services, and the public and other stakeholders, including written public comments.

Some  members of the  Subcommittee  questioned the merit of  this proposed policy.
Additionally, some  members felt that a recommendation on this topic is inappropriate
because adequate analysis  and evaluation of the  legal and policy  implications of the
above suggestions  were not explored in a balanced manner.
Increasing the Effectiveness of Land-Use Controls and
Long-Term Stewardship
    Recommendation 16:  EPA should develop a system to track,
    evaluate, and increase the effectiveness and the performance of land-
    use controls and long-term stewardship at NPL sites.
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The implementation, tracking, maintenance, and enforcement of land-use controls3 are
critical at most sites in ensuring long-term protectiveness.  Many issues still need to be
addressed regarding the use and enforcement of land-use controls, including ensuring
that needed controls are in fact implemented, and  providing  funding for the costs of
implementing, monitoring, and  enforcing these various controls.  Some Subcommittee
members believe that these issues are extremely important and should be a high priority
for the Superfund Program, given the Program's emphasis on permanent treatment.

Time constraints limited the  degree to which the Subcommittee was able to research and
discuss this  issue. However, the Subcommittee was informed of significant advances
EPA has made  in  recent years to address issues associated with land-use controls.  For
example, EPA has been promulgating thoughtful and thorough guidance supporting the
efforts of the National Conference of Commissioners on Uniform State Laws, and funding
the creation of a model Land Use Control Implementation Plan for use by state and local
governments.  In  addition,  EPA has  expended substantial  effort to  develop  a national
institutional controls tracking system, in cooperation with federal, state, Tribal, local, and
industry entities. This system is intended  both to enhance the effectiveness of land-use
controls and to provide information  on  all  cleanup sites with land-use controls in  a
community.

Continued effort is needed  to address the information gaps and respond to  ineffective
remedies. In particular,  improvements suggested by Subcommittee members included
the following:

    -*  Improve documentation of failures of land-use controls.
    -*  Improve documentation of actions that have been  taken to enforce land-use
        controls.
    -*  Address the  overlapping  and often disconnected responsibilities at different
        levels  of  government  for   implementation  of  tracking,  monitoring,  and/or
        enforcement.
    -*  Improve the standardization of terms.
    -*  Increase federal, state, Tribal, and local agencies and industry's  participation in
        the coordinated tracking effort.
    -*  Assess the effectiveness of five-year reviews to evaluate such controls.
    -*  Increase the  Agency's compliance  with CERCLA's preference  for permanent
        remedies.

The  Subcommittee supports  the continued  investment  in  the  Agency's  efforts,  and
encourages EPA to improve training and accountability among project managers, many
of whom do not follow EPA's existing guidance. Further, the Subcommittee concurs with
EPA's view that the development of performance measures for long-term stewardship
activities is critical. (This topic is addressed briefly in chapter V.)  The Subcommittee
regrets that  it  did  not have sufficient time  to undertake the elements  of the Charge
dealing with long-term stewardship issues,  and encourages EPA to pursue the issue
through ongoing national dialogue.
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The Need for Input on the Superfund Alternatives Strategy
    Recommendation 17:  EPA's strategy for Superfund Alternative
    Sites should remain a small pilot program until significantly more input
    is received from a broad range of perspectives, and an independent
    body produces for public review and comment a report describing the
    extent and performance of this program and its compliance with
    CERCLA.
Significant concerns  were raised by  the Subcommittee  members  before and  after
reviewing the limited information provided by the Agency on Superfund Alternative Sites
(SASs).   Questions  were raised about whether the approach used at SASs  was
consistent with the general trend toward increased transparency that the Subcommittee
is advocating throughout the  report. Additionally, the Agency's policy at SASs may have
the  potential to  be inconsistent with  a number  of EPA administrative  reforms and
guidance. This policy is based upon  EPA's individual arrangements with private parties
outside of the NPL listing process.   Although  such  guidance for the SASs  requires
consistency with the National Contingency Plan and a mandatory technical assistance
grant, it is not clear what oversight will be conducted, whether remedies selected will be
comparable to those selected for sites on the  NPL,  and whether these  sites will be
cleaned  up faster or slower than NPL sites.   While sharing  these  concerns, some
Subcommittee members also believe that the Agency should be encouraged to explore
creative  approaches  to achieving cleanup results outside the standard NPL-based
process, and that the fundamental objectives of the SAS program to help facilitate more
efficient and timely cleanups are important to maintain.  However, these Subcommittee
members are also concerned about the potential use of programs like SAS  to avoid
fundamental  process protections and reforms that benefit a wide variety of  interests
Because  of the  above  reasons and because the information needed for a thorough
evaluation unavailable,  the Subcommittee feels that the SAS efforts should remain small
and  in a pilot  phase administered  by headquarters until significantly more  input is
received from a broad range of perspectives on the value and limitations of this strategy.
Deliberations on Continuing the Discussion of Important
National Issues
During  its deliberations,  the  Subcommittee identified  additional  issues that  some
members felt were critical to the success of the Superfund Program, but were beyond
their ability to fully examine during the time available.   Some of these issues were
addressed in conjunction with  other  topics  in  the  report,  such as  the  ATSDR
recommendations  above.   Some  of  these  issues  were  not  discussed  by  the
Subcommittee and some members feel they warrant additional consideration by EPA and
others interested in and impacted by the Program.  Those members have proposed that
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EPA continue the national-level dialogue on (1) effective community involvement and (2)
issues unique to federal facilities. The goal of such ongoing dialogue is to provide better-
informed and more comprehensive input to the agency on some of the challenges that
the Subcommittee identified but did not adequately address.

Many members were  concerned that these  national dialogue efforts  could be  very
expensive  and time consuming and would drain resources from site cleanups.  They felt
that, if implemented at all, these initiatives should be implemented in a  manner that is
efficient and sensitive to their impact on Program resources. Therefore, many members
felt strongly that these dialogues should not take the  form of a Federal  Advisory
Committee Act  Process (FACA) because they believe  that the  FACA  process  is
unnecessarily resource intensive and inefficient.0 Other members felt that a FACA was
an effective option that provides weight  and  authority to the outcome  and therefore
should be  considered among the many forums  available for convening a constructive
national dialogue on these important issues related to Superfund.
   National Dialogue to Develop Recommendations on Effective
Community Involvement

As discussed in Chapter V of this report, one  measure of a successful cleanup program
is the effectiveness of the community involvement program.  Though  much has been
written about  community  involvement via Agency guidance and other national  policy
dialogues, consensus and  general understanding of what constitutes effective community
involvement do not exist.  To achieve such understanding and perhaps consensus, the
Subcommittee recommends that EPA conduct a national dialogue, possibly one that falls
under the umbrella of NACEPT (though Subcommittee members disagree on whether a
federal advisory committee is the  best forum) Regardless of the most appropriate format,
this effort is intended to serve the following purposes:

   1.  By establishing consensus  recommendations,  the  dialogue would  clarify  the
       appropriate role of the community in the cleanup decision-making process for the
       benefit of both EPA and the community.
   2.  Further, it would  help  to  establish  reasonable  expectations regarding  the
       capabilities of the  Superfund Program  in  general and the role of the public in
       particular.
   3.  Any  effective  dialogue would  provide EPA  with  solid recommendations  to
       implement throughout  all of its programs and  would be useful in establishing
       measures  of meaningful community involvement.
D Subcommittee member Richard Stewart supports this view.  See Attachment A for
Mr. Stewart's individual statement and elaboration on his position.
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    National Dialogue on Issues EPA and Other Stakeholders
Face Unique to Cleanup Activities at Federal Facilities

While federal facilities were excluded from the Subcommittee's charge, some members
felt strongly that this report would  not be complete without a discussion of this critical
component of the Superfund Program. Federal facilities that are designated on the NPL
fall under the regulatory structure of the Superfund law, but they do not depend on money
from the Fund itself or from EPA appropriations. Cleanups at federal sites are funded by
the responsible federal agency.

As a group,  federal facilities  are the  most  expensive remediation projects  in the
Superfund Program. There are 171 federal facilities on the NPL and 6 sites proposed to
the NPL for a total of 177 federal sites. The annual budget for EPA, the  Department of
Defense and the Department of Energy federal facilities exceeds $9 billion.  In addition to
the NPL sites, great numbers of formerly owned federal sites and federal non-NPL sites
compound the magnitude of the problem.

The  cleanup of  contaminated federal  lands,  now well  underway,  is  technically
challenging, legally complex and enormously expensive. Many federal facilities resemble
private industrial contamination sites, with decades  of  industrial  dumping and leaks
contaminating soil and groundwater.  As a whole, however, federal facilities differ from
sites owned by private parties or local governments in at least five ways:

    1.  Contaminated federal properties tend to be larger, combining several types of
       contamination and contaminated media on a single property.
    2.  Certain federal pollutants, such as waste from nuclear weapons production and
       unexploded  bombs and shells,  are  unusual or unique,  with  no commonly
       accepted, cost-effective cleanup technology.  In some cases, the technology to
       clean up these sites simply  does not exist.
    3.  Federal agencies are more resistant to oversight  by the agencies established to
       regulate environmental  contamination—EPA and  its state counterparts.  Only in
       1992  did Congress pass the Federal Facilities Compliance Act, clarifying that
       states had the power to enforce hazardous waste management laws at  federal
       facilities.  The Department of Defense has mounted a concerted campaign to roll
       back the provisions of this and the Superfund law.
    4.  Agencies with  national  security missions, such as the Department of Defense
       and the Department of  Energy's nuclear weapons complex, were - and in some
       cases still are -  reluctant to  disclose information about contamination  at their
       facilities.    This   lack  of  disclosure  complicates  investigative  studies  and
       subsequent remedial designs by ensuring that the full extent of contamination is
       not adequately characterized.
    5.  Due  to the nature of contamination  at Defense  and Energy sites, cleanup is
       projected to take hundreds of years to achieve, if ever.

Additionally, some members of the Subcommittee perceive that federal agencies have
been delegated  certain cleanup authorities under Executive Orders that may limit the
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authorities of regulatory agencies.  Other members strongly disagree, believing that the
delegation of certain cleanup authorities does not supersede provisions of CERCLA and
other laws that subject federal facilities to regulatory oversight.

Because federal facilities are the nation's largest landowner, their contamination touches
many lives in all types of communities, from Tribal lands, to rural towns, to national parks,
to heavily populated areas.  The  unique challenges posed  by these  sites,  and the
evolution of the Superfund Program since the release  of the Federal  Environmental
Restoration   Dialogue  Committee  Report,4 suggest that  federal  facilities  warrant
significant consideration by a group of diverse interests specially constituted to focus
solely on cleanup issues at federal facilities.
NACEPT                       Report      12,                       Chapter Vl-Page 109

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1 11/4/03 written correspondence via email "NACEPTresponse-OPEA-2003-11-3-rev"
2
  09/5/03 written correspondence via email "NACEPT1.doc"
3  In  this context,  land-use controls  is  intended to  include  institutional controls,
administrative controls, containment and other controls, such as signs and fences.
4 Final Report of the Federal Facilities Environmental Restoration Dialogue: Consensus
Principles and Recommendations  for  Improving  Federal Facilities  Cleanup.  EPA,
April,1996.
Chapter Vl-Page 110                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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              Glossary  of
Terms
This is a previously approved glossary of terms. Many of the terms and definitions have
been reported previously in "Superfund's Future: What Will It Cost?", Probst, Katherine N.
and Konisky, David M., et al,  2001, and are being reprinted with permission.
construction complete: A site at which the physical construction of all cleanup actions
is complete, all immediate threats have been addressed, and all long-term threats are
under control. Construction complete sites can still have one (the last) remedial action
underway.

deleted NPL site: A National Priorities List site at which EPA has determined, with state
concurrence, that no further  response is required to protect  human health or the
environment. After approving a closeout report establishing that all response actions
have been taken or that no action is required,  EPA publishes a deletion notice in the
Federal Register.

emergency response: A removal action that, based on the lead agency's evaluation of
the release or threat of release of hazardous substances, must begin within hours.

environmental justice (EJ):  The fair treatment and meaningful  involvement of all
people—regardless of race,  color,  national  origin, or income—with respect to the
development, implementation, and enforcement of environmental laws, regulations, and
policies.

extramural  cost:  Expenditures made by EPA that are "external" to the Agency,
including contracts, interagency agreements, and cooperative agreements with states.

final NPL site:  A site, usually with a Hazard Ranking  System score of 28.5 or higher,
that has been added to the National Priorities List through the issuance of a final rule in
the Federal Register.  EPA can use Trust Fund monies to pay  for  long-term remedial
actions only at final NPL sites.

Fund-lead action: An action  financed, in whole or in part, and conducted by EPA (often
by the U.S. Army Corps of Engineers, contractors, or state agencies).

Hazard Ranking System (MRS):  The system EPA uses to score potential risks to
human health and the environment from actual or threatened releases of hazardous
NACEPT Superfund Subcommittee Final Report | April 12, 2004                Glossary-Page 111

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substances at a site.  In general, a site must score at least 28.5 to be placed on the
National Priorities List.

intramural costs:   Expenditures  made by EPA  that are  "internal"  to  the  Agency,
including expenditures for payroll, travel, and supplies.

long-term  response  action (LIRA):   Fund-financed operation  of groundwater and
surface water restoration measures, including monitored natural attenuation, for the first
ten years of operation.

mega site: A site with actual or expected total removal and remedial action costs of $50
million  or more.

no further remedial action planned (NFRAP) site: A site that has been removed from
the inventory of Superfund sites and to the best of the  EPA's  knowledge, the Superfund
Program has completed  its assessment and has determined that no further steps need to
be taken to list that site on the NPL.

non-mega site:  A site with actual or expected total removal and remedial action costs of
less than $50 million.

Non-time-critical removal action: A removal action that based on a site evaluation, the
lead agency determines does not need to be initiated within the next six months.

NPL candidates:  A subset of NPL-eligible sites - that the regions send forward to be
considered for NPL listing.

NPL-eligible  sites:  Sites that  EPA regional offices identify  as priorities and  are sent
forward to headquarters for proposed addition to the NPL.

operable unit (OU):  A distinct project of the overall site cleanup.  Sites can be divided
into operable  units based on  the media  to be  addressed  (such as  groundwater or
contaminated soil), geographic area, or other measures.

operations and maintenance (O&M):  Activities required to  maintain the effectiveness
and integrity  of  a remedy, including groundwater pumping and treating,  measures to
restore groundwater or surface water, and maintenance  of landfill caps.

orphan site:  A site where the party or parties responsible for the hazardous substance
contamination are unknown, or are unwilling or unable to pay for a cleanup.

potentially responsible party (PRP): An individual, business, or other organization that
is potentially liable for cleaning up a site. The four types of responsible parties include a
site's present owner(s) and operator(s),  its previous owner(s)  and  operators) during the
time when  it  received hazardous substances, the generators of such substances, and
any waste transporters responsible for choosing the site.
Glossary-Page 112                   NACEPT        Subcommittee Final       |     12,

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preliminary assessment: The first stage of EPA's screening process for investigating
suspected contaminated sites, generally involving review of available documents.

proposed NPL site:  A site that has been proposed for NPL listing through the issuance
of a proposed rule in the  Federal Register.  EPA then accepts public comments on the
site, responds to the comments, and places on the NPL those sites that continue to meet
the requirements for listing.

PRP-lead action: An action conducted and financed by a potentially responsible party or
parties.  A portion of the response action  may be financed by the Trust Fund through a
preauthorized reimbursement under Section 106(b) of CERCLA, a practice referred to as
preauthorized mixed funding.

Record of Decision (ROD):  The public document in which EPA identifies the cleanup
alternative to be used at an operable unit of a site.

remedial action (RA):  The actual construction or implementation of a remedy at a site
or portion thereof.

remedial design (RD):  The engineering  plan for cleaning up a  site or portion thereof.
The actual remedial design document includes the technical drawings and specifications
that will guide implementation of the remedy, referred to as the remedial action.

remedial  investigation  and  feasibility  study (RI/FS):   Site studies  that  involve
gathering data to determine the types and extent of contamination at  a site (or portion
thereof),  establishing  cleanup  criteria,  and  analyzing  the  feasibility and  costs of
alternative cleanup methods.  The study  can  be conducted by EPA, contractors, state
agencies, or potentially responsible parties.

site inspection: The second stage  of EPA's process for screening a contaminated site
to determine whether it warrants inclusion on  the  National Priorities List.   The site
inspection involves collecting and analyzing samples of soil and water.

teenager site:  A site listed on the  National Priorities List that was  proposed  for listing
prior to FY 1987 and that, as  of the end of FY 1999, was not construction-complete. In
other words, the site has been on the NPL and is still not construction-complete  after at
least 13 years, making it a "teenager" site.

time-critical removal action:  A removal action that, based on a site  evaluation, the lead
agency  determines must be initiated within six months.

Trust Fund:  The Trust Fund created by  Congress to finance EPA's implementation of
the Superfund program, officially called the Hazardous Substance  Superfund.
NACEPT                       Report       12,                       Glossary-Page 113

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Glossary-Page 114                     NACEPT Superfund Subcommittee Final Report |  April 12, 2004

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             List  of
Acronyms
This is an EPA approved list of Acronyms as reported in the "Superfund/OH Program
Implementation Manual FY 02/03," July 9, 2001, Change 1, FY 02/03 SPIM, OSWER
Directive 9200.3-14-1G-P and modified.
AA          Assistant Administrator
AMLT       Abandoned Mines Lands Team
ASTSWMO   Association of State and Territorial Solid Waste Management Officials
ATSDR      Agency for Toxic Substances and Disease Registry
CAG        Community Advisory Group
CERCLA     Comprehensive Environmental Response, Compensation and Liability
            Act
CERCLIS     Comprehensive Environmental Response, Compensation and Liability
            Information System
CSTAG      Contaminated Sediments Technical Advisory Group
CWA        Clean Water Act
DoD        Department of Defense
DOE        Department of Energy
DOI         Department of the Interior
DOJ        U.S. Department of Justice
EJ          Environmental Justice
ELI          Environmental Law Institute
EPA        U.S. Environmental Protection Agency
ESI          Expanded site inspection
ESI/RI       Expanded site inspection/remedial investigation
FACA       Federal Advisory Committee Act
FR          Federal Register
FS          Feasibility study
NACEPT Superfund Subcommittee Final     |     12,2004
Acronyms-Page 115

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FTE           Full-time-equivalent (position)
FY            Fiscal year
GAO          U.S. General Accounting Office
GPRA         Government Performance and Results Act
HHS          Health and Human Services
MRS          Hazard Ranking System
IG            Inspector General
LIRA         Long-term response action
NACEPT      National Advisory Council for Environmental Policy and Technology
NCP          National  Contingency  Plan (National Oil and Hazardous Substances
              Pollution Contingency Plan) or National Contingency Plan
NFRAP        No further remedial action planned
NIEHS         National Institute of Environmental Health Sciences
NPL          National Priorities List
OA           Office of the Administrator
O&M          Operations and maintenance
OARM         Office of Administration and Resources Management
OCFO         Office of the Chief Financial Officer
OECA         Office of Enforcement and Compliance Assurance
OEI           Office of Environmental Information
OERR         Office of Emergency and Remedial Response (OSWER)
OIG           Office of the Inspector General
OMB          Office of Management and Budget
OPPE         Office of Policy,  Planning and Evaluation
ORD          Office of Research and  Development
OSC          On-scene coordinator
OSRE         Office of Site Remediation and Enforcement (New name for OERR)
OSWER       Office of Solid Waste and Emergency Response
OU           Operable unit
PRP          Potentially responsible party
RA           Remedial action
RCRA         Resource  Conservation and Recovery Act
RD           Remedial design
Acronyms-Page 116
NACEPT                  Final      |     12,

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RFF          Resources for the Future
Rl            Remedial investigation
RI/FS         Remedial investigation and feasibility study
ROD          Record of Decision
RPM          Remedial project manager
SARA         Superfund Amendments and Reauthorization Act
SAS          Superfund Alternatives Site
SBRP         Superfund Basic Research and Training Program
SI            Site inspection
TAG          Technical assistance grant
WETP         Worker Education and Training Program
USAGE       U.S. Army Corps of Engineers
NACEPT                                12,
Acronyms-Page 117

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Acronyms-Page 118                    NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Attachment A:
Subcommittee Members' Individual
Statements
NACEPT Superfund Subcommittee Final Report | April 12, 2004          Attachment A

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Attachment A                          NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Sue Briggum
                        Environmental Affairs Director
                        Waste Management, Inc.
The Final Report of the Superfund Subcommittee outlines complex discussions that took place over
the course of two years.  The facilitators of the Subcommittee should be commended for their
attempts to find  consensus and for their clarity in  describing the  basis for  disagreement when
consensus was impossible.  It's been an honor to be chosen to participate in these discussions.

The  challenge  was  significant.   Superfund  is  a  highly mature  program  after 23 years  of
implementation  and construction of final remedies at over 900 sites.   Many members of the
Subcommittee  have decades of experience living near Superfund sites, implementing cleanup
plans at sites, or studying the Superfund program on a political or policy level. Although it would be
impossible to articulate the precise views of each of the NACEPT's 32 stakeholders, the drafters of
the report have done an  excellent job of summarizing the substantive points discussed, thus giving
the Agency useful policy  perspectives.

The Final  Report, and many papers  from Subcommittee members submitted to the docket for the
group,  contains  important  information  and perspectives  that should  be helpful to EPA as  it
continues  to refine the Superfund  program.  The Final Report should be  read in its entirety; the
recommendations alone fail to usefully inform the reader of the group's opinions.

There are several aspects of the document  I would like to  emphasize as a Superfund practitioner
for 23 years:

Recognition of Superfund's  place  in the context of many effective remedial programs:  The
report repeatedly acknowledges Superfund's relatively small role in terms of the number of sites
cleaned up across the country.  Superfund sites are  intended to  be only those  of the highest
priority,  and - as we heard from many state program directors - other programs handle far more
sites, including both low and high-risk sites. This is as it should be. I would urge EPA to review the
extensive  materials submitted to the docket by Superfund practitioners and state officials about the
creative, protective and  cost-effective practices of non-Superfund federal and  state remedial and
solid waste post-closure  programs.   Best practices should  flourish.  The recommendations in this
report should push EPA  in the direction  of appreciating and relying upon non-Superfund programs
by improving  coordination  with other agencies, reinforcing  review  and  consideration  of other
remedial and closure  programs before listing a site on the  NPL,  and involving all responsible
parties much earlier in the process in order to incentivize  handling  of sites within non-Superfund
programs. This  appears consistent with Assistant Administrator Horinko's One Cleanup initiative,
and it's  a  sensible recognition that Superfund should work in conjunction with, not as a substitute
for, other programs.

Strong  management of the Superfund program:  The report continually stresses transparency
and adherence to defined  criteria.  A common theme is consistency:  consistent evaluation of the
reasons a site  would be  handled by the Superfund  and not other state or federal programs;
consistent and methodical application of a defined set of factors in listing a site on the NPL and
thereby  committing Superfund staff  or resources; consistent early  outreach to communities and
responsible parties; consistent search for current accurate data on site conditions and impacts.
EPA's Headquarters' initiative to accelerate progress at pre-SARA sites is commended in the report
as an  example  of consistent leadership to bring  old  sites to completion.  EPA's Superfund
Alternative Program,  in  contrast, is  criticized,  and a consensus  recommendation  urges that the
Program be restrained to a small Headquarters-run  pilot because of  its lack of transparency and
consistency; failure to follow the procedures, prioritization and due process  protections afforded
NPL sites  and stressed in this report;  and ad  hoc selection and implementation.

Emphasis on solid,  up-to-date data:  Members from all  perspectives constantly  referenced the
need for accurate, up-to-date information on site and community conditions.  It is impossible to
select for Superfund listing the highest priority sites and to  develop  reliable, effective and sensible
remedial plans  without  accurate current  data  on  health  and environmental  impacts.  For this
reason,  the report repeatedly recommends that EPA seek available data from community members
NACEPT Superfund Subcommittee Final       |      12,2004                  Attachment A-Page 1

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and responsible  parties early and often. The report recognizes the HRS's failure to provide risk
characterization  and  stresses the need for corrective data on actual exposures and site-specific
community conditions.

Fairness and accountability:  The Subcommittee's discussions did not and were  not intended to
address Superfund's liability system,  but a theme underlying our discussions was accountability.
As the report states in the discussion of funding issues, "all Subcommittee members recognized the
importance  and  value of a strong  enforcement program  that targets  all - not  just some -
responsible  parties,  encourages  proactive   efforts  by  cooperative  responsible  parties,  and
discourages recalcitrance."  Superfund is most effective in  practice  and as an  incentive if it
uniformly and fairly holds all parties responsible for their activities and if it encourages accountable
parties to come forward by treating them fairly. This is the premise of EPA's fairness administrative
reforms. They remain vitally important to a successful Superfund program.

Robust public discourse:  The very fact of establishing a NACEPT Subcommittee on the Future
of Superfund demonstrates EPA's commitment to understanding all perspectives and submitting to
even the most critical public comment. All stakeholder groups were enthusiastically represented in
this Subcommittee, and EPA did  not shirk in its support of the group even when discussions were
difficult or  demanding on scarce agency resources. This openness is to be commended, as  is the
Assistant Administrator's commitment at the final Subcommittee meeting to continuing the dialogue
and  exchange   of perspectives.   Particularly  in  an  era  when politics  tends to  stereotype
environmental policy discourse, EPA must have access to substantive, non-polemical dialogue and
advice.  I believe the discussions over the past two years and this Final Report represent just that.
Attachment A-Page 2                   NACEPT          Subcommittee Final       |     12,

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Position Statement of:   Doris Cellar!us
                        Vice Chair, Environmental Quality Strategy Team
                        Sierra Club - Prescott, Arizona
I begin by giving my full endorsement to the comments of Jason White, which include the "Top 10
Issues To Protect Public Health and The Environment atSuperfund Sites", and to the appended
comments of Dolores Herrera,  Lexi Shultz, Aimee Houghton, Vicky Peters, Ken Jock,  and Grant
Cope.

OVERVIEW—Although I fully support the NACEPT Report's excellent recommendations for EPA to
direct increased attention and resources to tribal and environmental justice communities,  I cannot
sign the Report.  It does not send a strong message  about the serious  need for more resources to
address needs  at sites where  cleanup  is stalled  for lack of funds and the needs at  increasing
number of contaminated sites in this country.  At the very least the program needs an  immediate
short-term funding increase of $300 to $800 million to protect communities at sites that  have been
delayed because of insufficient funding.  Sierra Club will continue to advocate for restoration of the
expired Superfund tax on users  of the chemicals that have created Superfund sites by polluting the
environment.  And we will advocate for  larger annual appropriations. If Congress is not provided
with  a list of all sites that qualify  because  of threats  to health  and  the  environment,  it is not
surprising that they don't vote for adequate funding.

I agreed to participate in NACEPT because I understood it was a consensus process and we would
not have to  put our name on anything  we did  not support.  It was most disappointing  that the
Subcommittee almost reached consensus on some very important issues where true collaboration
almost occurred.  Most parties  were willing to give up something for the common  good,  but the
efforts of a few  spoiled it.  Some unidentified industry representatives  could not even agree on a
small temporary funding  increase that would  not involve reinstatement of fees or  the  tax! They
were unwilling to give their names,  a situation  in sharp contrast to the openness of those who were
willing put their names on funding recommendations in the "Top 10 Issues To Protect Public Health
and The Environment at Superfund Sites".

My larger concern about attribution is the possible  misuse of concepts in this Report where ranges
of views are presented with no attribution. It will be impossible for EPA,  as well as other  readers, to
know who or how many  held  these views.   Such  discussions  could be misused to  weaken
programs and prevent qualifying sites from receiving attention. In many cases even  consensus
recommendations are followed by "some say this"  and "some say that",  a very confusing situation.
 An example can  be found in Chapter III. How would anyone know that it was industry "members
that believe the Program's resources should  be guided using assessments of risk  and that EPA
should increasingly use risk as a way to make  decisions about NPL eligibility and to set priorities for
spending"? I  think this is a very bad idea  and I  refer you to the discussion of risk in the comments of
Vicky Peters which point out the inadequacy of this approach.

All sites  that qualify, regardless of the  size  or remoteness  of the community, should be listed.
Tribal residents  and other  affected communities must have early and  genuine involvement, and
financial support to facilitate their participation.  TAG grants should be more easily obtained and
they should also be made available to non-NPL sites. ATSDR and NIEHS should have to do more
to  share information  at other sites and address the overall health impacts in affected communities.
Accurate,  comprehensive site  hazard   assessments,  done  in  consultation  with  the  affected
community, are one of the most  important determinants of what cleanup is needed.

OTHER PROGRAMS and MEGASITES—One of the  most dangerous ideas  discussed in the report
is  deferring sites that qualify for CERCLA oversight to  other federal or state  programs.   I totally
disagree with the industry  view (Chapter III,  "Different views on  risk.") "the Superfund Program
should first prioritize ongoing significant  threats that  require  government funding for cleanup, and
other environmental cleanup programs  should  be  used  to address less  significant  current
threats and potential future threats, and should  administer and oversee cleanups at sites where
there are viable  responsible parties." Leaving management of Superfund sites with viable PRPs to
"other  programs"  that have weaker cleanup and  liability  provisions could  remove  CERCLA
protections and standards from some of our nation's worst sites.
NACEPT Superfund Subcommittee Final       |     12,2004                  Attachment A-Page 3

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Unfortunately,  this dangerous  idea  is one of the  factors listed  under Recommendation  1  for
determining what other programs could be used suggests using redevelopment programs (Chapter
III, "Likely outcomes of activitiem by other programs or PRPs").   It states: "Is  or will another
program appropriately address the  site?  The Agency should not use  scarce Superfund  time,
attention, or funding when another program could appropriately address a site and has the capacity
(funding and  resources) to appropriately  carry out site evaluation and  cleanup or appropriately
provide oversight  of work funded  by responsible parties.   Such  programs might include state or
Tribal environmental programs,  redevelopment programs, and other Federal programs, such as the
Resource Conservation  and Recovery Act program."

Superfund is not, and was not created to be, an economic redevelopment program.  Although such
programs  might provide  resources  for cleanup,  they do  not provide the  oversight, expertise,
cleanup standards and other requirements of a CERCLA cleanup program.   For this reason, NPL
qualifying sites should not be "deferred" to  redevelopment or brownfields programs.  Resources and
partnerships provided by  such  programs,  where they may exist, can be  adjuncts  to the ultimate
reuse of the site.

Early in our subcommittee's studies it was found that generally these other programs do not have
the financial resources  and capabilities to clean up these most serious  sites (Chapter III,  "NPL
Candidate Sites not Proposed for Listing"). States are overburdened with multiple responsibilities
and short on funds; the budget situation shows no sign of improvement.  Funding  programs provide
small amounts of money to address sites that,  in general, are smaller and less complex than  NPL-
caliber sites; although some funding might be available and  appropriate  to augment some  NPL-
caliber cleanups.   In general these  programs provide funding potential only, they  do not  provide
a cleanup process or cleanup standards - these would have to be provided by another program, for
example a state cleanup program.

"Some states may have programs that can better address some cleanups.  However, we neither
comprehensively  assessed the capacities  of state  programs, nor  is it likely that most  state
programs will be more protective of human health and the environment.   In  my own community I
already see major parts of a site with a qualifying MRS score being parceled out to a state program
with  weaker procedures and standards, including those that address liability.  They will  lose EPA
oversight, expanded investigation, and authorities, and the rest of the site  may no longer rank high
enough to be considered under Superfund.  Although the Superfund  NPL program is  not the only
program  capable  of appropriately  cleaning  up  contaminated sites, contrary to the  Report,
("Deliberations  on Ensuring Consideration  of and Coordination  with  Non-NPL  Programs, last
sentence"), under 42 USC 9628(b)(1)(B)(iii)(l),  EPA can only exercise its enforcement authority at
a site being cleaned up under a State response program if, among other unrelated conditions, "a
release or threatened release may  present an imminent and substantial  endangerment to public
health or  welfare  of the environment and  additional response  actions are  necessary."  - not
wherever EPA determines that "non-Superfund programs are not acting appropriately."

States use combinations of voluntary programs, redevelopment assistance,  and often weak  "risk-
based" cleanup standards,  rather than the preference for  permanence  in CERCLA.  They're all
supposed to be "reasonably anticipated' uses, not current, though people don't seem to good at
anticipating. Although EPA has  not required permanence as often as it should, it  is  finding that this
has been a mistake.  Engineered and institutional controls fail, leading to spreading environmental
damage and costly readjustments of the remedies.   Protection of groundwater is also sometimes
weaker.

Megasites need increased attention, comprehensive oversight, expert staff and improved decision-
making. It is not surprising that very large sites have taken a  long time for agreement on remedy
and  implementation of cleanup. The impact  of these sites  on  residents,  businesses  and  local
government is huge in terms of public resources expended, lost tax base, and  community values.

As one view in the Report correctly states, if megasites are  parceled out to other programs instead
of being listed  as  one  large geographic  area, communities will be denied  the unified basis for
participation  in the evaluation and cleanup of all the contaminants and hotspots in the area. The
many benefits of a more  comprehensive investigation, public  visibility, availability  of TAG grants,
implementation of technologies, and support from the businesses in the community will be lost if
the site is divided.
Attachment A-Page 4                   NACEPT         Subcommittee Final       |     12,

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Based upon site-specific data, it might make sense to list releases within a large site separately, as
is sometimes done with operable units within a large Superfund site.  The danger is that dividing a
site might expedite cleanup of simpler problems,  but delay (sometimes indefinitely) cleanup of the
more difficult parcels.

Another reason to not limit clean up to "hotspots"  or small parcels is that this evades EPA's current
policy, which is to  NOT consider incremental reduction  of risk from  removals or PRP cleanup
standards in determining whether a  site  should be  listed on the NPL.   This  provision  is to
ensure that  sites that would qualify  as  a national  priority are cleaned  up  in compliance  with
CERCLA standards, and do not fall off the table  because just  enough clean up occurs to result in
the site no longer scoring 28.5.

Federal facilities sites are generally very large,  with huge risks and costs of cleanup. Effective
public involvement is often difficult to  achieve because of the disempowering  style of the federal
government.  The  progress of  cleanup  is also  significantly   less.    Unique  issues  related to
these facilities warrant a focused dialogue on issues arising since 1996.
NACEPT                           Report       12,                       Attachment A-Page 5

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Attachment A-Page 6                   NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Grant Cope
                        Attorney, Earth Justice
Summary:  I dissent from the report because defects in the process,  precipitated by EPA and
Subcommittee management,  helped to infuse the report with statements that officials may use to
severely weaken Superfund's ability to protect public health and environmental quality.

Since the  beginning of the subcommittee process, the operating policies included a process that
promoted consensus recommendations and an array of five  different ways that a "range of views"
could be represented in the absence of consensus. During the final stages of the process, EPA
and  Subcommittee management dramatically changed these policies.  In the fall of 2003, EPA
began to   express  its   desire  for   non-consensus  statements,   as   well   as   consensus
recommendations,  and stated that the  agency  would seek to  exercise  greater discretion  in
implementing policies  based  on  a "range  of views."   In the final days of the Subcommittee's
existence,  its management chose not to attribute views to individual or groups of representatives.
These changes promoted extremist positions that could weaken vital protections in the Superfund
program.  Therefore, I dissent.

The  following describes proactive policy recommendations that the Administration  should endorse
and work to implement in  order to increase  protections for public health and environmental quality
in the Superfund program.  Consistent with these recommendations, I hereby endorse the "Top Ten
Issue to Protect Public Health and the Environment at Superfund Sites" included in the comments
of Jason White.  I also endorse the views of Lexi Shultz, Doris Cellarius, Aimee Houghton,  Dolores
Herrera, Vicky Peters, and Ken Jock.  I also wish to  thank EPA, other  representatives  on  the
Subcommittee, and individuals who talked with the Subcommittee for contributing their time, talent,
and thoughts during this process.

Make Polluters—Not Innocent Taxpayers-Pay To  Clean Up The Nation's  Most  Heavily
Contaminated Toxic Waste Sites:  The Administration and Congress  should approve and  sign
into law a  reauthorization  of Superfund polluter pays fees, which expired at the end of 1995,  with
increased  authorizations and  appropriations to ensure that public health and environmental quality
are protected at dangerous toxic waste sites across the country. Presidents Reagan, George H.W.
Bush, and Clinton endorsed reauthorization of Superfund's polluter pays fees, but the current Bush
Administration has not supported their reauthorization.

As referenced in the NACEPT,  Congressional, EPA, and independent  reports demonstrate  that
Superfund is currently under-funded by $300 to $800 million dollars per year. This figure does not
include the years of under-funding that have created a  backlog of  needed clean  up activities and
lost opportunities to address threats. Comparing the baseline and high estimates of funding needs
provided by the  Congressionally requested  study written by Resources For the  Future and  the
Superfund  past appropriations, the program has experienced a funding deficit of between $2-3
billion from 2001 to the levels of funding requested in  2005. The end result: public  health  and
environmental quality suffer.

The  purpose of Superfund  is to protect  public health  and the environment  from  hazardous
substances  at highly contaminated toxic waste sites.   In order to accomplish this purpose,  the
Superfund  program needs resources.  When Congress enacted Superfund in 1980, it gave  the
Superfund  program two  methods  of obtaining needed resources.  First,  Superfund has  liability
provisions that make potentially responsible parties ("PRPs") liable for cleaning up a site.  If a PRP
refuses to  clean up a site  and EPA expends money to remediate a site, PRPs are liable for EPA's
clean up costs,  plus,  potential penalties for refusing  to  clean  up the  contamination.   Second,
Congress  enacted fees on the purchase of chemicals often found at toxic waste sites, petroleum,
and a small levy on profits in excess of $2 million for some big corporations.  In exchange for the
fee  on  petroleum sales,  Congress  gave oil  companies  a liability  exemption  for petroleum
contamination  at Superfund  sites, meaning that EPA cannot hold polluters  liable under for
petroleum  contamination.

These "polluter pays fees" provide the foundation for Superfund's ability to protect public heath and
environmental quality in five important ways.  First, the fees provide a stable source of funding that
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is not dependant on uncertain annual appropriations  from taxpayer funds, or "general  revenue."
This point is critical  because,  generally speaking, annual appropriations from general revenue for
domestic programs are capped at certain levels, which means that Congress will only spend a set
amount of money annually on such  programs.   Therefore, Congress  must pay  for increased
appropriations for one program  by  reducing  money  going  to another program.   However, the
polluter pays fees  allow Congress to increase money going  to  Superfund cleanups without
necessarily taking resources away from other programs.  Congress does this by relying on money
from fees that build  up over  time.   This system ensures that the government  can help protect
communities  threatened by toxic waste sites without taking  money away from programs  that
provide people with safe drinking water,  clean air, clean water,  and better enforcement of other
public health and environmental protections.  Stable funding also promotes long-term management
options at Superfund sites, which is critical because EPA may need several decades or longer to
clean up heavily contaminated sites.

Second, the federal government appropriates money from collected fees to pay for  EPA clean up
activities when PRPs refuse to undertake such action, cannot be located,  or are bankrupt.  When
EPA spends resources to clean up a site, the agency can recover such cost from PRPs connected
to that  site. These cost-recovery funds go back into the Superfund program to fund more cleanups.

Third, the fees provide EPA with a stable source of funding that is essential for a strong Superfund
enforcement program.  This enforcement program helps to expedite cleanups at Superfund sites
and increases the capacity of other federal and state clean up programs.  For example, if a PRP is
being intransigent at a Superfund site, EPA can  either clean up the site—if the  agency has the
resources to undertake such an action—or it can  issue a unilateral administrative order to the PRP
directing it to undertake clean  up  activities.  However, the effectiveness of EPA's order authority is
directly tied to the availability of EPA resources, since PRPs know that EPA's order is only as good
as the amount of money behind it. While EPA can also request that DOJ seek judicial enforcement
of an order, there is no guarantee that DOJ will prioritize  such requests over other matters; in
addition, litigation over orders could  delay cleanup for years  as the parties  argue  over the
reasonableness of the selected remedy.

A strong enforcement  program under Superfund also benefits other federal  and  state cleanup
programs.  When PRPs are being intransigent, representatives of other programs can provide the
option of negotiating in  good faith or dealing with EPA's Superfund program. The threat of an EPA
cleanup order or site listing provides polluters with  a powerful incentive to negotiate in good faith.

Fourth, the fees promote pollution prevention activities, by shifting cleanup costs to  industries and
products associated  with the creation of toxic waste sites.   This uses  the  market to  promote
environmentally sensitive products and companies.  Industries can continue to produce polluting
products, but they generally choose to pass those costs onto customers, creating a comparative
advantage  for environmentally sensitive products that  do  not harm the environment  or  public
health.   Additionally,  the fees  also  help  ensure  that  funding  for  other  public  health  and
environmental programs are not reduced, thereby contributing to pollution prevention efforts under
other programs.

Fifth, EPA  also provides states with grants  to increase  the  capacity of state  and tribal clean up
programs.  These resources are critically important to ensuring that states and tribes  can effectively
address toxic waste  sites in communities across the country.  Unfortunately, these resources -
especially for tribes—a have declined in recent years. At the same time,  the economic  downturn
has resulted in budget cuts in state clean up programs.

The Administration's  failure to endorse and  Congress's failure to reauthorize Superfund's polluter
pays fees has contributed  to  a dramatic slowdown in the pace of clean up at the  nation's most
heavily contaminated toxic waste sites. The Report mischaracterizes the GAO's findings on the
interplay between funding levels and taxes.  Rather, as pointed out by the Congressional Research
Service: "[w]hen the taxes expired, the Fund had an unobligated balance of nearly $4 billion, and,
even after expiration of the taxes, money continued to  be added to it from interest payments, costs
recoveries, and other sources. Thus, the  lapse in taxing authority initially had little effect on the
ability to fund the program." Emphasis added. (CRS-3). Once the surplus was depleted, funding
levels began to drop.  In addition, the  agency provided no data or explanation for the precipitous
drop of construction completions from 2000-2001.   It  is worth  noting that  EPA  informed the
Attachment A-Page 8                   NACEPT          Subcommittee Final        |     12,

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Subcommittee that the agency's budget was cut $100 million in that year, and that amount was
never restored.

The  Bush  Administration  should  stop protecting the  profits of polluting  industries  and  start
promoting protections  for public health and environmental quality by calling  for reauthorization of
Superfund's polluter pays  fees.  Congress  should enact  reauthorization  of Superfund's polluter
pays  fees.   The  tens of  millions of Americans—including  millions  of children—who live  near
Superfund sites and millions of other people who work and recreate near sites deserve no less.

Industry's  Orphan Share Funding Proposal Aids Polluters And Weakens Protections:  I fully
supported  a  modest,  compromise recommendation  for short-term funding for  the  backlog  of
remedial actions  that are awaiting  funding. Unfortunately,  industry  representatives  stymied a
consensus. These members insisted that any additional funds be spent only on "orphan snares" at
Superfund  sites.  This restriction would exclude funding for cleanups  in communities  near some
Superfund sites, and  prioritize expenditures of these funds based on the potential financial status
and  availability of PRPs,  not  the threats posed  by toxic waste sites.   It would also  violate
Superfund's existing provisions that  require  EPA to recover costs from PRPs or their insurance
companies, and thereby undermine Superfund's liability provisions (42 U.S.C. § 9622(b)). Lastly, it
would encourage the destructive practice of attaching Congressional "environmental riders" on EPA
appropriation  legislation, and signal a lack of support for the CERCLA liability provisions that form
the foundation of the Superfund program.

Currently, EPA  uses "orphan shares" to describe the amount of money that the agency will credit
(i.e. not seek to recover) to  PRPs at a site  based on EPA's  assessment that certain non-viable
PRPs are or may be  responsible for a set amount  of the contamination.  Industry representatives
wanted  EPA to initiate a new  process of formally designating certain sites or parts  of sites  as
"orphan shares".  This restriction could force EPA to forgo recovering costs against PRPs or their
insurance companies,  in order to use the money to clean up contamination, likely benefiting PRPs
that EPA has not  yet found or intransigent parties who argue that a cleanup is too expensive and
who  point the finger at other entities.  A relatively minor contribution at a large site could fund  an
entire investigation or design at a smaller site. Apart from the fact that such  a practice is contrary
to law, relinquishment of the right to cost recover is bad policy.

Funding And Conflicts Of Interest:  The Subcommittee was correct to examine how the lack of
funding  is adversely affecting EPA's ability to  list and cleanup sites and meet the agency's goals for
the program, and to  attempt  to  remedy the situation.   Some members  of the full NACEPT
Committee   have  questioned  whether  this  examination  was  appropriate,  since   certain
Subcommittee members might indirectly benefit from increased funding. However, members of the
full NACEPT  Committee also expressed interest in the  Subcommittee examining funding issues
early on  in  the Subcommittee's process.  Moreover, the failure to obtain additional funding has a
direct benefit to PRP's on the panel.  An underfunded program poses less risk of enforcement and
less pressure on PRPs to perform thorough and timely cleanups.

Inappropriate Measures That May  Weaken Cleanups:  The Report's appendix inappropriately
includes a  reference to  weak  RCRA-type  measures  to  consider in  measuring  program
performance,   such  as controlling—but  not  necessarily cleaning  up—human  exposure  to
contamination and the migration of contaminated groundwater.  These measures could  weaken
protections  by driving staff to simply contain  toxic waste and use institutional controls,  rather than
directly cleaning up the pollution. These measures could weaken EPA's application of Superfund's
preference  for  permanent treatment and vigorous  application of  strong  clean up  standards.
Moreover,  experts, communities,  and  EPA often  debate  whether contaminated  plumes  of
groundwater are  moving or  all pathways of exposure are closed.  EPA's  measure  of success
should be based  on objectively verifiable steps that are related to EPA's  process of cleaning  up
Superfund sites, such as construction completions.
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Attachment A-Page 10                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:   James Derouin
                        Attorney, Steptoe & Johnson, LLP
I enjoyed the experience of serving on the Superfund Subcommittee and feel that the final report
provides a good discussion of (a) the Superfund Program and (b) the pros and cons of a number of
important issues that relate to it. I think that the Subcommittee leadership was excellent and the
facilitation was very professionally and competently done.  EPA provided a wide variety of useful
information.  In addition,  senior EPA personnel provided excellent insights into the Superfund
Program at smaller, work group  size meetings.  The competence of EPA personnel was impressive
and reassuring.  I do,  however, have some observations about the process  and certain issues
contained in the report.

The Subcommittee Process.

The process started out as a consensus effort; unfortunately, it didn't stay that way.  I have been
involved in the environmental consensus process for  30 years.   To get something done, the
process needs to find areas of  commonality; that's the  challenge.  In  my opinion, several factors
combined to thwart producing a report with a  greater range of consensus recommendations.

    •   The Subcommittee's mandate involved three issues-i.e.,  measuring program progress,
        management of megasites and the role of the National Priorities List.  In the middle of the
        process, the  mandate  was  expanded to include funding.   In my  opinion,  progress had
        been made on the original Subcommittee agenda. When program funding was  added  to
        the agenda, it had a "whip  lash"  effect-i.e.,  it changed the focus of the Subcommittee
        process and consumed its energies  from that point forward.A

    •   The demand/expectation for consensus was eliminated,  perhaps  because of   lowered
        expectations resulting from  what could be viewed  as hostility toward  EPA exhibited by
        some  parties.   Regardless,  this, too,  had a  "whip lash" effect.  Once this decision was
        made,  momentum for  broad consensus stopped  and the process  slid inevitably into
        explaining/validating disparate views.

In  terms  of "lessons learned," the Subcommittee process reaffirmed  my  belief that in order  to
produce consensus, you need to demand it, there has to  be active facilitation and there needs to be
a  commitment to  the  process  by  all parties.  In this case,  there was, in  the beginning, an
atmosphere of  great suspicion about the "agendas" of Subcommittee members.  In addition, some
parties were suspicious of even  the slightest change in the status quo.  But hard work and lots  of
discussion prevailed—and led to  the Subcommittee report.  In my opinion, however, an opportunity
for a broader, useful consensus was lost.

Program Funding.

There is  no agency in the federal government that has  all the money it wants.  The question,
however, is whether an agency has  all the money that it needs.   A  twin issue  is whether it  is
spending efficiently the money entrusted to it.  There is a mentality in some sectors that efficiency
is not applicable to the Superfund Program; that, because of the noble purpose of the Superfund, it
should be funded on a "sum sufficient" basis.  Unfortunately, that is an unrealistic expectation.

Another complicating factor is that an entire  service industry, both inside and outside government,
has built up around the Superfund  Program.  State programs rely on federal funding.  Studying
sites has precedence over remediating sites.  The  mentality  that the Superfund Program is an
entitlement has become prevalent.  EPA is under constant pressure from multiple sources to turn
A For example,  the study done by Resources For the Future ("Superfund's Future:
What Will It  Cost?") was advanced  as  a basis for a recommendation for increased
program funding. That study speaks for itself. There was no reason to "reinvent the
wheel" by imposing a discussion of its findings on the Subcommittee because, except
as background, it was irrelevant to the original charge of the Subcommittee.


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the Superfund Program  into a public works program.  If the Program ever comes to encompass
river and harbor reconstruction, it will become just that—at a cost of multiple trillions of dollars.  In
other words,  there is no amount of money sufficient  to  meet the political, technical  and legal
demands that are being made on the Program.  To cope, therefore, requires a sense of reality
along with efficiency and prioritization.

Expenditures Must Be Prioritized Throughout The Superfund Program.

Sites, or portions of sites, that pose actual human health risks/exposures must be the Superfund
program's top priority. "Worst First" must become a part of the prioritization process regardless of
all pressures to the contrary resulting from the competition for funds from regions and states.  Bona
fide threats to human health must have priority and  must, always,  be provided necessary funding.
If,  in this context,  inadequate funds  exist, emergency, temporary and targeted funding should be
sought.  However, the concept that all sites are created  equal, and that all parts of megasites pose
the same risk, is wrong.  The inability to spend, up front, all the money needed on a project always
creates  inefficiency.  However, there are always limits on funding. The interstate  highway program
was built in steps;  in fact, no highway exists  that has  not been expanded after it was originally
constructed.  The defense department is subject to phased spending. If individuals could afford to
buy their houses without mortgages,  their total cost would be less.   Based on the reality, therefore,
that funds will always be  limited, prioritization of spending is critical.

EPA has, for some time,  had a prioritization system for allocating dollars for remedial actions. That
process should, based on the principles set forth in the report, be applied to prior steps in the
Superfund pipeline, including NPL listing decisions.  The lack of precise and perfect information at
earlier stages  in the Superfund process should not  be  used as an  excuse for the failure to  make
difficult decisions.  I concur with the principle that "perfect should not be made the enemy of better."
The  prioritization process,  however,  should not be  so  cumbersome that decisions  can never be
made. Such gridlock does not invite increased funding.


EPA Headquarters Must Retain  Listing Authority.

EPA must be  accountable for the  funds entrusted to  it. EPA cannot be held accountable, however,
if  it  does  not  retain  authority over  listing  and spending  decisions.   More specifically, EPA
Headquarters must retain final authority to make NPL listing decisions. Those decisions cannot be
delegated to either the regions or to the states. Superfund decisions require complex, balanced
decisions that should not be submitted to a "round table" process in which decisions  are made by
those with a vested programmatic interest in the outcome.  EPA can be held accountable only if it,
at  the  headquarters level,  retains  the authority to  make  final  decisions  to assure national
consistency and the allocation of funds to national priorities.   Part  of management,  oversight and
accountability is the prioritization of funding; and the NPL listing mechanism is an important part of
the management process.

Remediation Must Become Superfund's Priority.

More resources should be directed,  as a  percentage of overall funding, toward  bona fide "bricks
and mortar" remediation. The decline in such funding is unacceptable and should be reversed.  In
addition, although there  are dozens  of studies and initiatives mentioned  in the report, it would be
counterproductive to allocate  significant  resources  to  these  studies while,  at the  same time,
remediation funding is decreasing. The best evidence  for additional  funding is the wise, efficient
use  of  existing funds.   Directing funds  toward personnel  and   studies instead of  the  actual
remediation  of sites,   or  portions  of sites,  that  pose   human  health  risks/exposures  is
counterproductive.  Spending more money is not a measure of program progress; spending money
better is.
Meqasites Must Be Conceptualized Better; Otherwise They Will Sink Superfund.

The  Subcommittee spent considerable time,  unsuccessfully,  discussing  a  definition for what
constitutes a "megasite."  The fact is that some sites confronting EPA cover a large area, include
multiple sources of release and pose funding challenges to the  Program.  Scrutiny of the current
program  demonstrates that  a  large  share  of annual  remediation costs is today consumed by
Attachment A-Page 12                  NACEPT          Subcommittee Final       |     12,

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relatively few sites.  That may be the way that it should  be.  But it also suggests that megasites
require special management and  listing attention.  The mere listing of a geographically large site on
the NPL should not dictate that all portions of the site receive the same priority for funding unless it
can be concluded that they also pose the same degree of risk to human health. Megasites must be
viewed, wherever appropriate, as a composite of multiple release  sources  whose  risk to public
health must be individually assessed.
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Attachment A-Page 14                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Steve Elbert
                        Senior Vice President
                        BP America, Inc.
I appreciate the opportunity to participate in this Superfund Subcommittee, and would like to thank
the other members of the Subcommittee for sharing their experiences and ideas in this process.
EPA graciously responded to our many  requests  for detailed information  about the  Superfund
program, and the facilitators  at Meridian/Ross should be commended for their efforts to identify
consensus where possible, and to summarize the diverse range of views on issues where there
was no consensus.

Throughout these deliberations, we were often reminded that Superfund resources are limited, and
that EPA program managers,  like other business managers, need to accomplish a great deal with a
limited budget.    Recommendations 1, 2, 3 and 7 in this report share  a common theme: they
suggest that EPA could make greater use of private party and other program resources at many
sites.  In these comments I want to expand  on that theme, and suggest a number of steps that EPA
could  consider to implement these recommendations.

As  the report explains,  when a site can be cleaned up in a  timely and  effective manner under
another program, it is not an optimal candidate for the Superfund program. EPA recognized this in
the 1980's, when it stated that cleanup at RCRA permitted sites should be conducted under the
RCRA program to the extent possible. In later guidance, EPA recognized that cleanups in progress
at state sites should continue to be handled by the states to the extent possible.  We believe EPA
should extend this policy to sites where parties seek to begin work under these and other cleanup
programs, and should issue guidance to ensure that regions consistently evaluate and make good
use of the resources available under other  programs.  Rather than using the Superfund program to
address every NPL-caliber site (as some  Subcommittee members  have  suggested), we believe
EPA should  look to the program's original purpose, and use  the Superfund as a "safety-net" to
catch  those  NPL-caliber sites that  cannot be adequately addressed by  other programs and  by
private funds.   To make  maximum  use of  other program resources, we suggest the following
additional steps:

1.   Provide essential information to  interested parties before a site is placed on the NPL.  In our
experience, EPA does not consistently seek input from potentially responsible parties (PRPs) at the
earliest stages of the investigation and cleanup process. As a  result, we see sites where EPA has
used Superfund resources to  perform investigation, removal or  remedial work that could  have been
performed by PRPs with private funds.

In  order to  make maximum use  of available resources,  EPA needs  to  reach out to other
stakeholders earlier in the process, before it places a site on the National Priorities List (NPL), while
there  is still  an opportunity to take  action  under a variety of  cleanup programs and use private
funding to perform the earliest stages of work.  Before proposing  a site for the NPL, we suggest
that EPA should  send each major  PRP  a  detailed notice letter  describing  the  site,  the
contamination, and the names of  other PRPs.  At the same time,  EPA should allow all interested
persons to review and copy detailed information in EPA's files about site conditions, contamination
(type,  location, alleged sources), PRP lists, and each PRP's alleged connection to  the site.  Many
NPL-caliber sites are large, complex sites that involve multiple PRPs who are unaware of the other
parties' activities.  At these sites it  is not realistic to expect one PRP with a  small share of the waste
to voluntarily accept liability for the waste of hundreds or thousands of  other  parties, based on
minimal information.  When  given  sufficient information, however, such PRPs can and in  our
experience usually do form a  group to fund some or all of the work needed at the site.  Sometimes
we've found it difficult to  get essential information before a  site  is placed on the NPL, as it is
common for EPA to withhold information for possible use in future  enforcement litigation, and to
insist that such information be obtained through a Freedom of  Information  Act (FOIA) process that
can take years to complete.  However, these  practices deprive other agencies and PRPs of data at
a critical point in time,  when  they need it to develop a plan  to address the site under another
program, without draining Superfund resources. To  take full advantage of the capacity that resides
in  other  programs and among  groups  of PRPs, EPA needs  to share its  data with  these
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stakeholders.  EPA should automatically and  consistently make the above data available to all
interested persons before placing a site on the NPL.

2.  Establish a reasonable amount of time to develop and consider proposals for voluntary cleanup
or further action.  Once a potential NPL site has been  identified, in our experience it takes several
months to develop a viable proposal to investigate and respond to that site.  Some Subcommittee
members viewed this as  a troubling source of delay.  However, over the last five years the median
time between the date when a site is proposed for NPL listing, and when it is actually  listed on the
NPL, has been about 5 months.6 This suggests that at most sites there is sufficient time for EPA to
evaluate proposals for voluntary cleanup under a variety of programs. If a site requires immediate
action, EPA could conduct emergency work as  a Superfund action, while it continues to evaluate
proposals for additional work under other programs.

3.  Develop consistent criteria to evaluate proposals for voluntary cleanup.  EPA's ultimate goal is a
prompt and effective response action that protects  human health and the environment. In deciding
how to achieve this goal,  we believe that EPA should take full advantage of the resources available
in other cleanup programs,  considering the following factors:
        o   Whether agency staff in another cleanup  program are willing and able to oversee the
            necessary work;
        o   Whether that other cleanup program  has, in the  past, achieved  remedies that protect
            human health and the environment;
        o   Whether funding is available for the proposed work.  Most work will be performed and
            paid for by  private parties, but other funding sources should not be overlooked (such
            as funds for redevelopment or dredging of navigation channels under WRDA);
        o   Whether the proposal will provide  adequate opportunities for public participation and
            comment at those sites where there  is significant public interest.  At many sites the
            parties must comply with the public comment provisions in the  National Contingency
            Plan (NCP) in order to bring a contribution action  against recalcitrant parties  under
            CERCLA Sections 107 and 113.  In addition,  some programs contain their own  public
            comment requirements.  Where  neither of  these conditions  applies, and there  is
            significant public interest in  the site,  our  company has  entered agreements with the
            oversight agency to create a public participation process suited to the specific needs
            of a site.

4.  Consider the use of a  Coordinating Committee or similar group on a pilot basis.  Other agencies
are often in the best position to evaluate proposals to handle  sites under other cleanup programs.
Representatives from other programs are able to draw  on a wide range of program experience and
insight that can  be used to  develop thoughtful and  balanced advice regarding the pros and cons of
each program option.

During the Subcommittee's deliberations, I chaired a Work Group that considered whether a multi-
agency coordinating committee could help EPA  make sound NPL listing decisions.  EPA may want
to consider testing that concept on a pilot basis. Mega-sites are especially good candidates for a
pilot project because they often cover large geographic areas that contain many potential sources
of contamination, and while these might be addressed  as a single mega-site covering hundreds of
square miles,  it might be  better to address  them as a  series  of smaller  sites  tied to  specific
contaminant sources, possibly under more than one cleanup  program. A multi-agency committee
could advise EPA on the cleanup programs that  are  best able to  address  portions  or all of the
proposed mega-site, considering each program's capabilities, funding, staffing and limitations.

Potential  members of a coordinating committee might include staff from federal and state programs
that  have an interest in  the contamination at the proposed mega-site, as well as  at least two
members from EPA headquarters who can provide a national perspective and level of consistency,
and a neutral person to chair or facilitate the discussion.

The  committee  would review relevant data, including  contaminant sources, locations and  levels;
whether there are high risk areas that should be  prioritized for action first, before other areas of
B We ran a quick analysis of the time it took for a site to move from proposal to final
listing for the 146 sites listed on the  NPL between January 1997 and April 2002.  The
average time was 297 days, and the median was 149 days.
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lower risk; and proposals by private parties to perform or pay for some or all of the work.  It would
evaluate a range of cleanup  programs, and consider how those programs  might work together, if
needed.  If the committee could not agree on  a recommended course of action within an allotted
time, it could offer the pros and cons of each option to EPA for consideration, as the Subcommittee
has done in  this report.  It  could  consult a checklist of relevant criteria to ensure  it weighs
appropriate factors and provides a sound analysis of them to the Region for review.  The Region
would then exercise its discretion to decide whether to propose the site for NPL listing,  based on
input from the committee and other stakeholders who file comments.   EPA headquarters  would
continue to review these proposals to bring a national perspective and consistency to the process.
In  all  cases, we  believe the  Assistant Administrator should retain her authority and  discretion to
make the final NPL listing decision.

I believe these proposals would reduce the number and size of sites that end up on the NPL in the
future, and would allow EPA to focus its Superfund resources on a smaller universe of sites that
have no  other options.  This  should allow EPA to spend more money cleaning up those sites that
need to be on the NPL.  If EPA or any other stakeholder is interested in further discussion of these
ideas, or any other issues raised by the Subcommittee's report,  I would be happy to participate in
such discussions.
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Attachment A-Page 18                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Jane Gardner
                        Manager& Counsel, Remediation Programs
                        General Electric Company
GE appreciates the opportunity to have participated in the NACEPT Superfund Subcommittee and
its deliberations on how to improve the Superfund program. GE also appreciates EPA's willingness
to "take stock" of the Superfund program with a view toward identifying changes that would improve
the program and make better use of the significant financial expenditures by EPA and PRPs. While
the Subcommittee's discussions were  often vigorous, most of the participants listened to  other
points of view, considered the views of others in order to reach  compromises, and support this final
Report.  GE's comments are a result of this effort to reach compromises with other stakeholders.
GE thanks  EPA for the opportunity to  participate, and Meridian  and Ross  & Associates for their
helpful direction and mediation.

As  one of  America's  oldest and  largest companies,  GE is,  and has  been,  addressing under
Superfund and other cleanup programs multiple sites that were created long  before Superfund was
enacted.  GE  has spent more  than $1  billion to remediate sites  since  1990, and  now spends
approximately $150 million  dollars  per year on  remediation  activities.   As a result, GE has a
significant interest in making sure that money spent to  remediate sites is spent efficiently and
effectively, and  provides the maximum benefit for the expenditures. In addition, given  the maturity
and size of GE's remediation program,  GE has acquired broad, hands-on experience with virtually
every phase of  remediation  efforts under both Superfund  and  other state and federal  remediation
programs.  The virtually unparalleled depth and  breadth  of GE's experience particularly informs
GE's input on 2 of the 3 questions in EPA's charge to the Subcommittee: (1) the role of the NPL in
the context of other cleanup programs; and (2)  how to  handle the special challenges  posed by
"mega" sites.

Through  experience,  GE has  found that the success of Superfund turns on two fundamental
questions:   what are  the   realistic risks to human  health and the  environment posed by
contaminated sites, and how can those risks be reduced to acceptable levels most efficiently and
effectively? The current risk assessment process does not adequately distinguish between realistic
risks (current and future)  and hypothetical risks (current and future).  Many stakeholders believe
that EPA's  risk assessment practices  rely too frequently on  unwarranted, conservative,  "worst
case" assumptions that distort the outcomes of risk assessments, and do  not result in  an accurate
analysis of the  actual risk posed by a  site.0  EPA should reform the MRS  to adequately identify
actual, realistic risks.  EPA then should  prioritize sites based upon the results of that effort, with the
sites that present  the most serious risks to be addressed first,  and commit both public and private
funds in accordance with that prioritization.

GE has repeatedly observed that cost-effectiveness and  cost-benefit considerations  are virtually
absent from the Superfund program, despite the fact that EPA and other federal and state agencies
routinely  make  decisions  based on those considerations.  To  avoid misinterpretation, it must be
made clear that GE does NOT believe  that only current risks  should  be  addressed under the
Superfund program or elsewhere. To the contrary, GE believes that if sites were evaluated based
on realistic current and future risks, as  opposed to hypothetical current and  future  risks,  more
funding would be available  to address  more sites and  protect  more people and  more  of the
environment.

GE is disappointed that the Subcommittee did not reach consensus on the appropriateness of risk-
based  metrics as the vehicle for decisionmaking and priority-setting  in the Superfund program.
Through the years, policymakers have emphasized how important it is that the Agency use risk-
based approaches to ensure that EPA spends its limited resources wisely, both within and across
programs.   See, e.g.,  Reducing  Risks:  Setting  Priorities  and  Strategies  for Environmental
Protection  (1990)  (Scientific Advisory  Board;  http://www.epa.gov/history/topics/risk/01.htm);
"Setting Priorities, Getting Results:  A  New Direction for EPA",  pp. 2-3(Nat'l Academy of Public
c See generally,  "An Examination of EPA Risk Assessment Principles And Practices",
EPA/100/B-04/001 (Mar. 2004).


NACEPT Superfund Subcommittee Final Report \      12, 2004                  Attachment A-Page 19

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Administration, 1995)("EPA should .  . . [u]se comparative risk analyses to inform the selection of
priorities and the development of specific program strategies").

Despite the Agency's progress in successfully applying risk-based tools to improve environmental
performance in  many programs, the Superfund program remains rooted in the past, relying, as it
does, on an incomplete hazard assessment tool (the MRS) that was developed in the early days of
the program.  EPA's skewed use of inappropriate exposure assumptions, and failure to link actual
exposure to health threats,  has generated a process that addresses all  risks almost equally, and
because of this, EPA rarely makes  decisions in the remedial  process that focus limited funding
(both federal and private) on the realistic expectation that a contaminant will cause near term health
or ecological problems unless  action is taken.  Rather,  EPA assumes that regardless of funding
limits, particularly for privately funded sites,  all risks, realistic and hypothetical, current and future,
must be dealt with simultaneously under the Superfund  program.  This position fails to allocate
money to where it is needed most, fails to consider how to get the most risk reduction with limited
dollars,  and encourages significant dispute and delay with private parties and other stakeholders.
GE recommends that EPA reconsider how risk is evaluated, make tough decisions that recognize
limited budgets,  and commit Superfund dollars  to the most critical sites where there is current
exposure or realistic expectations of additional risk in the short term (i.e.  linked to actual exposure
and  dose), and  then provide an "off ramp" for long term future  risks to be managed under other
federal and state programs better suited to deal with these issues. This approach would preserve
Superfund monies for sites and exposure paths that cannot  be addressed by other programs or by
private parties, and that need immediate action with the full force  of Superfund resources.

GE recognizes that evaluating the relative risks posed by potential Superfund  sites is not an easy
task, nor a non-controversial one. The Agency now has 25 years of experience in undertaking risk-
based  evaluations,  however,  and the Superfund  program  should be  taking advantage of that
experience.  Toward that end,  GE believes that  EPA should revisit the essential  building block of
the Superfund program - the Hazard Ranking System - and make it  a  more meaningful tool for
identifying sites that pose the most serious risks to human health or the  environment.  In addition to
collecting information about the toxicity of materials in potential Superfund sites, a  revised MRS
should identify,  based upon site-specific data, the realistic exposure risks that prospective sites
pose to neighbors and to the environment.

Likewise, EPA should devote additional up-front investments in data gathering and  evaluation of
those "mega" sites  that are threatening to  overwhelm the limited resources of the  Superfund
program. The stakes involved in mega sites are too high to take analytical short-cuts, forcing EPA
to "fly blind" without information regarding which  aspects of  mega sites pose the highest risks and
should be addressed  first under the Superfund program.  Having better information and  "good
science" about  mega sites also will enable EPA to  be more creative  in how these  sites are
addressed. As the Subcommittee's mega  sites work group discussed, it might be more efficient to
address geographically diverse mega sites under a number of authorities  and agencies - whatever
can  get a timely job done  cost-effectively.   It is difficult to sensibly  deploy  alternative cleanup
options, however, in the absence of good information  about the nature and  scope  of the threat
posed by mega sites.

GE would like to emphasize a related point regarding the  increasingly important role  that non-
Superfund programs are playing in the  cleanup of contaminated sites.   When Administrator
Whitman addressed the Subcommittee, she emphasized that today's Superfund  landscape  is far
different than that faced by EPA in  the 1980s, when Congress  launched the Superfund program.
Today,  many cleanups  are proceeding outside the  Superfund program,  under robust federal
programs (such as the RCRA corrective action program; the Department of Defense's multi-billion
dollar cleanup program; Interior's abandoned mines cleanup program; the Brownfields program; the
Corps of Engineers' Great Lakes Initiative, etc.) and state programs (including, in particular, state
oversight  of  many  private,   PRP-financed  cleanups).    Administrator Whitman  asked  the
Subcommittee to put the Superfund program in the context of this new reality,  and to  help the
Agency take full advantage of the multiple cleanup programs that are now handling many cleanups
throughout the nation. GE agrees that many other remediation programs have matured and are
capable of handling sites that are  currently on  the NPL, thus  preserving the limited  Superfund
funding as a "last resort" for those sites that otherwise would not be addressed. The Superfund
program must become the program of last resort,  not remain the program of first resort.
Attachment A-Page 20                  NACEPT          Subcommittee Final        |     12,

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The report's characterization of funding shortages is misleading in at least two important respects.
First, although not acknowledged in the report, an estimated 70 percent of cleanup dollars under
the Superfund program historically are expended by private parties - and not through federal
appropriations. Thus, while federal funding of the program is an important aspect of the Superfund
program, it is not the primary financial driver of cleanup - most cleanup dollars come from PRPs.

Second, the Superfund program no longer "occupies the field" when it comes to cleanups.  Much of
the most interesting  and  innovative cleanup work is  occurring  in  cooperation with community
development projects (brownfields sites), and in the RCRA and DOD cleanup programs - cleanup
programs that appear to be ahead  of Superfund in terms of employing risk-evaluation techniques
and streamlined, but protective, cleanup approaches.  Likewise, as noted above, many states are
overseeing  major,  NPL-caliber cleanups with PRPs. The preference of many states and  PRPs to
proceed outside EPA's Superfund program is evidenced by the substantial cleanup activity that is
occurring under other authorities, and demonstrates that the Superfund program has much to learn
from other cleanup efforts.

GE is hopeful that EPA will take the work of the Subcommittee, and take a fresh look at how EPA
can improve the Superfund program to make it more responsive to our nation's cleanup needs. We
encourage the Agency to  review the full range of views presented  in the Subcommittee's report,
and take advantage of this unique opportunity to  make needed  reforms to the risk assessment
process to maximize benefit to as many people and sites as possible.
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Attachment A-Page 22                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Glenn  Hammer
                        Vice President, Environmental Health and Safety
                        Ashland, Inc.
On behalf of Ashland Inc., I would like to thank Assistant Administrator Marianne  Horinko for her
thoughtfulness and  foresight  in establishing the NACEPT Subcommittee on  Superfund.   Her
attempt to  address  the  problems  with the program and identify  potential solutions through  an
inclusive stakeholder process was a  great idea.  I would  also  like  to  thank  the  Chair of the
Subcommittee, the  facilitators for working through some tough  issues and the EPA staff  for
providing information and insight.  The Subcommittee worked diligently over the  last twenty-two
months to find common ground on extremely difficult Superfund matters. In the end  however, it was
difficult for  some people on the  Subcommittee to keep an open mind  and get to  "real  change" -
change that would have provided for additional funding for specific sites and acceleration of the
pace of cleanup at others. Superfund will be incrementally improved if the recommendations in the
final report are implemented, but  much more could have been accomplished by this  Subcommittee.

The charge  of  the Subcommittee  from  both the  Deputy Administrator  and  the  Assistant
Administrator  was  clear  and  straightforward.    We were  asked   to  deliberate and  make
recommendations on the  role of  the NPL, the  handling  of mega-sites and  improvements in
measures to gauge the  performance  of the program.  We were also encouraged to confine our
discussions to current statutory mandates and not to  discuss or make recommendations that would
require legislative action. While in  the ordinary course of a subcommittee's work it is  normal to
sometimes  stray somewhat from  the charge, this Subcommittee seemed to stray more than I would
consider normal. The facilitators should be commended for their attempts to find consensus.

Superfund - Federal Waste Clean-Up Program of Last Resort
Personally  I think  that enormous progress has  been made in the remediation of hazardous waste
sites in the  nearly  twenty-five years following enactment of the statute.  There are other federal and
state programs that are  now able to assist in either the funding and/or management of these sites.
It is therefor totally  appropriate  for Superfund  to be on  the decline in terms of funding and the
addition of new sites to the program.

Superfund should be the federal waste cleanup option of last resort, a safety net, turned to only
when its stringent liability requirements, complicated remedy selection, continuous oversight and
community  participation are needed and when  other available programs do not suffice.  Assistant
Administrator  Horinko certainly recognizes this  evolution in waste cleanup programs  as evidenced
by her forward thinking One Cleanup Program.  This  program of applying a range of tools available
to federal and state agencies provides cleanup solutions that are less costly and just as effective
and timely in the protection of human health and the environment.

Funding
Having  noted the difficulty in getting to "real change" and  anticipating that some Subcommittee
members will likely continue to ask for increased funding and for a reauthorization of the corporate
and excise  taxes for the  trust fund, it becomes  important to bring some clarity to  any discussion of
funding.

    •   First, well over  seventy percent of the costs  of Superfund cleanups are  paid by private
        responsible parties.  Contrary to what some might think the polluters are  paying, and, in
        many instances, more than their fair share!  In fact, most  of the sites being added to the
        list today are orphan sites.  If there is no viable  responsible  party, it is totally proper for
        these agency lead sites  to be paid for from appropriated funds from general revenues.

    •   Second, there is absolutely no correlation between the size of the annual appropriation for
        the Superfund program  and the revenues residing in the trust fund.  In spite  of what some
        people think surrounding the taxing and funding issues, there  is  no compelling  reason to
        reauthorize the taxes or to substantially increase funding for the program.
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Statutory and Regulatory Reforms Are Needed
While discussions of legislative changes were not part of the Subcommittee's charge,  I would like
to take this opportunity to make several comments pertaining to statutory improvements that should
be considered.

    •   The liability provisions of CERCLA should be amended to provide for fair share allocation
        in which Potentially Responsible Parties (PRPs) only  pay for their fair share of the cost of
        cleanup.

    •   CERCLA should be amended to make Superfund cleanups more risk based. The Hazard
        Ranking System (MRS) should be based on the relative risk posed by a site.  In addition,
        the public should be better educated about the risk assessment process.

In addition to potential legislative reforms, I believe that some significant reforms could be made
under current statutory authority which were not discussed by the NACEPT Subcommittee.

    •   EPA regions differ in their support to PRPs in  pursuing non-cooperating  parties.  Many
        times, EPA finds one or a handful of PRPs and then  ceases to identify other  responsible
        parties leaving the cooperating  PRP to search out and bring costly legal action against the
        recalcitrant parties. Other times, the agency will "pull the rug out" from under cooperating
        PRPs by settling and  providing contribution protection and covenants not to sue to others.
        Both of these actions by the agency result in additional transaction costs going to lawyers
        and consultants and not to cleanups.

    •   Access to orphan share funding is not consistently applied. Most of the time, on "mixed
        funding" sites, EPA will only pay the orphan share of the site costs up to the level of its in-
        kind contribution. This was not what Congress intended and this should be rectified.

Missed Opportunities
It is important to point out topics discussed  by the  Subcommittee where its deliberations did not
result in meaningful recommendations. I will refer to those areas as "missed opportunities".

Program Administration
(1)      Remedy Selection:
        •   Cleanup decisions should be made on the projected future use of the property.
        •   PRPs are forced to pursue outdated Records of Decision (RODs) and spend millions
            of dollars  on   remediation systems that  will  never  adequately  address  the
            contamination problem.

(2)      Early Involvement of PRPs:
        •   EPA should  revise its PRP search guidance to  ensure that responsible parties are
            brought to the table earlier in the process. This will provide efficiencies to the program
            and reduce overall transaction costs.

(3)      Consistency Among Regions:
        •   Sharing of Superfund experiences between regions is spotty at best.  For example,
            EPA regions differ in their support to cooperating PRPs in negotiating  access to sites
            and enforcing access agreements.

(4)      Headquarters review for NPL sites:
        •   The Assistant Administrator is the national program manager for Superfund. As such,
            it is appropriate that a final policy review be made at the headquarters level. I believe
            that this practice  should continue.

Program Funding
(1)      Increase  funding for orphan shares and for actual cleanups. This could be funded in part
        through reductions in  program administrative costs.

(2)      As the Superfund program declines, a review of staffing levels should be conducted.

(3)      Reimbursement of PRPs for orphan share expenditures will result in increased willingness
        of PRPs to come to the table.
Attachment A-Page 24                  NACEPT          Subcommittee Final       |      12,

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(4)      Reform of rigid contract administration procedures and  outmoded  contract vehicles will
        result in increased efficiencies and substantial savings to the program.

In conclusion,  I am grateful for having had the opportunity to participate in this process and wish
the  EPA success in implementing the recommendations.
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Attachment A-Page 26                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Dolores Herrera
                        Senior Advisor, Alianza Ambiental Center
                        Environmental Justice
Thank you to the Taxpayers, EPA, OSWER, Meridien & Ross, and Staff's for your support of this
project. I respectfully acknowledge my colleague's contributions and thank them for their hard work.

PREFACE: When asked to volunteer my time, expertise and service to work with other senior level
managers to advise EPA on specific issues within the Superfund Program I realized that issues and
problems would arise. As a longtime grassroots community activist and public servant I live  in a
neighborhood with two superfund sites. It is within that capacity, and as director of programs and
the community TAG representative that I have come to have a high regard and  respect for EPA
Region 6 and their role in partnership with the community. I debated on signing on to the report that
my colleagues and staff labored over during the last 22. I signed  because I had no set, definitive
expectations. I have been around long enough to know that when you get a group of highly diverse
people together (like  ours)  to discuss monumental issues (like EPA's) to make recommendations
on environmental policy and agency direction that it becomes a struggle to create a product. One
of the community's right of passage is to sit at the table interfacing with policy makers, industry,
environmental groups, academia, government and other stakeholders to tell the people's real story.
I do not want to offend my colleagues, EPA, any organization or group with my position, but just as
hard as they fight for their constituency so shall I. It is a  mistake for EPA to decide to create public
policy from  the total subcommittee report -  any  policy must be based  upon the Consensus
Recommendations only, not on the collected Range of Views. Our colleagues representing industry
cannot be faulted inasmuch as they are  working hard to  protect their  bottom  line,  net profits.
Community  members do the same  thing,  we are on the  front lines  among the  environmental
degradation, protecting the lives, health, social  and economic welfare of real people. We have it
tough lacking the power and resources to make a strong argument for human life. The case must
also be made for the States who carry a tremendous burden and responsibility, without sufficient
resources to be as  effective  as they could  be.  We are  grateful for humanitarian efforts  and
contributions by environmental groups.  On the  other hand,  some communities are still shuddering
from experiences with paid researchers, scientists and  academia coming into our neighborhoods
armed with prestigious credentials,  grant money, and staff to take advantage of people and the
situation.  Some outsiders create a livelihood on the backs of the people. In the interim, we continue
to be disempowered and  workplaces  continue to be  poisoned. The committee  did  not reach
consensus. An old Spanish dicho says: "The only way someone will move is when the fire begins
burning on his or her backs. " Maybe that is when people will get serious and join together, when
America is on fire? Almost twenty-five years ago on June 13, 1979, the EPA issued a press release
that proposed a federal trust fund to clean up the most contaminated, hazardous waste site in our
country. It was a day of promise and hope for people who had bore the ill  health effects of living
near the toxics and poisons and accountability for those who had created the problems. The press
release said, "President Carter (today) proposed legislation to Congress to establish a multi-million
dollar fund to help clean up hazardous waste dump sites which threaten public health or the
environment. The fund, comprised of federal money and fees on the oil and chemical industry,
would be part of a total governmental response to spills  of oil and hazardous  substances  and
problems related to inactive and abandoned hazardous waste disposal sites." The  superfund tax
expired in 1995. The people lost another round as the proactive activity and commotion  to promote
reauthorization was not successful enough to revive it.  On March 11, 2004 when the US Senate
voted 44 to  52 to defeat reinstating the tax.  New Mexico  Senator Jeff  Bingaman voted  for his
constituency, voting for  reinstating the tax. We continue to go, round  and round  while  people,
children are  sick, some have died or are dying from exposures and illnesses directly linked to the
pollution and contamination at the sites. The hills, mountains, rivers, valleys, oceans, forest, plants,
animals and the entire ecological balance are diminishing at an alarming rate. Yet, when we are at
the table we continue to expend tax dollars to argue and hide instead of striving to do what is right.
I wonder  what would  happen if we put our babies' faces on the contamination and  not just dollar
signs? ENVIRONMENTAL JUSTICE: The majority of the toxic dumps are situated among people
of color,  minority, tribal, and poor  disenfranchised  populations.  Human,  civil and  constitutional
rights of  people of color,  minorities, tribal and the  poor have been devalued by unfair, unjust
practices  in  the location and placement of toxic cesspools. The  minority and poor communities
posed the path of least resistance. The community's rights to fairness, equality, equity  and justice
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ended  in  EJ communities when the  profit margins of commerce  and industry  became  more
valuable than decency and human  life. It is morally and ethically wrong to sacrifice a people, a
culture - racism in its lowest degree. EPA must strengthen and reinforce the laws  and mandates
that  protect  people  and  the  environment.  The  White  House  Executive Order  12898  on
Environmental Justice directed federal  departments to protect and prevent and enforce EJ. EPA
should support further expansion of collaboration  with local superfund communities. Partner with
environmental groups; provide funding for innovative onsite programs and other community led EJ
projects. Superfund policy  and Agency direction should address working with local stakeholders
and  practice the  Principles  of  Environmental Justice.   PUBLIC  INVOLVEMENT:  Additional
resources should  be provided  to  the  local,  grassroots  community stakeholders. EPA should
increase funding  and technical support to communities at optimum levels. Superfund communities
should be supported to develop common sense  approaches on technical dialogue, educational
outreach  and  information  toward  meaningful public  participation.  EPA  should  streamline the
process with greater access to public information. They  should be  responsive toward  the local
community working with them in developing acceptable procedures toward  communication, public
outreach, information, education and policymaking  as it affects the community and site. EPA should
provide accounting practices and measures to create and revise internal  management  decision-
making to competently engage the affected stakeholders,  communities, rural, urban,  tribes/tribal
governments. EPA should place special emphasis to honor  and preserve the  unique history,
values, customs, religious ceremony, traditions and values  of the impacted  community. ATSDR &
NIEHS: Many of my colleagues around the country have been and are very upset with treatment
by ATSDR and NIEHS. Both agencies that were created to support superfund communities have
not always  been  effective  or accountable  to  the  primary  stakeholders  and  representative
stakeholder advisors. This must improve. These programs  as well as other projects and  initiatives
at all levels of government  should explore standard options for the local superfund communities to
share  an  equal  partnership to collaborate in the grant  making process. All should  be non-
discriminatory of federal programs.  EPA should establish a requirement to work in full  partnership
with the superfund TAG directly, to  provide acceptable, appropriate services and practices to best
serve the  needs and requirements  of the affected community and not the other way around.  An
honest assessment engaging the local, existing talent pool and expertise should  take precedent
that accompany provisions of funding  and  resources to employ local, grassroots,  experts in the
superfund communities. A  collection of performances should be reinforced using such tools as a
Community  Survey and Performance  Profile, detailed in  an unbiased,  transparent Community
Report Card.  This requirement would be a measurement of reliable information: current, applicable
data directly related to human, public health and the environment at the superfund  sites to provide
notification and  accountability.  HUMAN  AND PUBLIC   HEALTH:  EPA,  other  agencies  and
collaborators must work with the community.  They should  not bring in strangers,  experts  to
implement a plan that doesn't work,  which insults the community and wastes our (too few) precious
resources. Agencies must respectfully listen  to  the people and pay them for their expertise.
Incidences of serious health problems and risk  occur to a greater degree in people  of color,
minority, poor communities, tribal, industrial, and  farm workers, and  at a higher, faster  rate than
affluent, white populations. Present  dangers to human health and future risk are a  reality and are
pre existing conditions that should be the primary factor in the ranking of sites. Ecological impacts
should also be considered.  Superfund communities often go berserk when they hear that additional
health  studies or environmental research  is  being proposed.   For too long,  and too often the
government  and  their representatives have not respected  the rights have  and have not listened
effectively to the people. Many of the data collections provide inconclusive information, which only
bemoans  distraction  with  little  or no  relief to  the  community.  Just   constant employment
opportunities for  "experts." Resources  must be connected to clean-up actions and direct health
services modeled with the  local grassroots community to serve pertinent, existing  (future) health
problems  at  the  superfund  site.  Improving  data collection  and timely delivery to superfund
communities continues to be problematic. EPA should provide  resources within the TAG process
so that the affected superfund stakeholders,  communities build consensus to improve  upon the
strategy, orientation and delivery. All actions should be done protective of  human health and the
environment. SUPERFUND  TAX:  The  tax  must  be  reinstated.  Many  communities  lack the
necessary resources and access to public information and process that is reinforced due to poor
health  that is directly affected by toxics, contamination and pollution, stress, lack of resources,
education, disenfranchisement and  other mitigating factors living with superfund.  There is public
acknowledgement of EPA's problems, fiscal, program management and waste of resources, but it
is  unfair to penalize  impacted neighborhoods, communities and tribes.  The government should
reinforce  and  strengthen  venues  for  partnerships to  restore  and  reinstate the polluter pays
principle.  PROCESS:  The subcommittee did not  achieve consensus on several important issues
Attachment A-Page 28                  NACEPT         Subcommittee Final       |      12,

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due  to  consequences  related  to committee  structure,  process  and direction.  Lacking the
environment of trust, open dialogue with built in measures for accountability consensus was not
achieved. When the preliminary and interim rules were abrupt halted and others were inserted  in
the final stages of the development of the Report the necessity for building consensus became
improbable and a  moot point.  Throughout the process, issues and concerns were communicated.
The facilitation team was amenable to listen, but lacked the proper support to solve the problems.
The inevitable pressing time lines, volatile subject material, the potential for discord and the plan for
solutions among  the diversity and high-level  expertise  of  participants was not addressed  or
presented until the last weeks of the process. When the rules were changed, the undercurrent  of
agendas, communication problems and lack of transparency manifested into grave trust issues
leading to an impasse undermining acceptable  results. LEADERSHIP AND  FACILITATION: The
lack of building "community" among our colleagues and the structure further impacted producing a
consensus  document.   The membership highly qualified was generally  focused,  but at  times
individual  agenda's  were  mired  by lack of  transparency  impairing enough  honest,  fruitful
discussions to provide holistic decisions. As polarization  and dissent of the  committee occurred
some perceived it as being counter productive and offensive,  therefore, the debates that would
have provided the substance needed to build consensus never materialized. The organization and
development of the subcommittee was a challenge,  but the facilitation team did their best in a tough
situation. I am doubtful that their expertise was fully utilized. EPA provided a lot of responsibility to
the Chair with a key element of relationship building missed. Oftentimes, the Chair and facilitation
team worked among themselves in major planning,  and development of content and structure,
which created  an  imbalance of power affecting interactions  and interpersonal relationships that
displaced the committee. It was frustrating when the  documentation of the meetings proceedings
did not capture the  thrust  and synopsis of our  discussion. Another  problem was  that  some
members chose to communicate only to the hierarchy  and not during our meetings or as participant
in-group e-mails. The timeline and challenges of working with such a high level group of peers with
diverse opinions and  self-interests disallowed members access to all of the information in order to
make honest assessments and decisions.  I appreciated when the dialogue and deliberations were
fluid and transparent and took on a life of their own. In order to effect systemic change the process
of change must be transparent. Unfortunately, much of the relevant dialogue  was never captured
and debated to transpire to consensus.  This process left huge gaps - a "non-consensus" report
with various views with limited or no attribution. My greatest fear and anxiety is that the agency and
the public will not  be  able to discern the difference  between the Consensus and the  Broad  Range
of Views in the Report; they are  not interchangeable. The Broad Range of Views should  not be
used to force EPA to create policy that weakens the  program or standards, which would become
disastrous to human health and the environment.   CONCLUSION: The care and protection of our
generation  is no more important than  the  care  and protection of future generations. The present
generation has an obligation to solve these problems  and  not pass them on to future generations.
The ill health effects,  environmental, social, economic issues and stigma of living in contaminated,
polluted communities are real; obscured in  political surroundings, which create social and economic
nightmares  for  citizens,  government  and  elected  officials.  Real  people,  minority,  poor,
disenfranchised populations continue to bare the brunt of the nightmare created by years of abuse
to people, the earth and  natural resources. Many in EPA work hard to protect human life and the
environment. Sufficient resources should be secured  for communities and tribes to  be financially
and technically empowered  to fully participate in the  decision making process to make educated
choices that  affect their families, communities  and  themselves.  There  are  inefficiencies  in
government and at EPA, but that does not alter the fact that additional money is needed for the
superfund program to be functional to clean up all  the sites.  Therefore, I advocate for additional
resources for EPA; supporting a short-term funding increases of $300 to $800 million in order  to
protect communities at sites that have been delayed  because of insufficient funding.  A word  of
caution regarding  Mega  Sites, they are  not Brownfields, a rose garden, or a ball field. They are
mega toxic dumps; clean them up - properly. Industry created the problems; it is unfair to ask the
citizens of this country to pick up the tab for their actions as they reap the rewards and  profits. It is
an outrage to expect the already polluted, contaminated superfund communities to pay and risk
double indemnity  for this crime and environmental injustice.  Where's the America where people
used to  own  up  and  accept responsibility for their actions? Industry must be held  100%
accountable for the restoration and clean up all of their messes.

I  agreed  to sign onto the 2004 NACEPT  Report with comments and reservations.  I provide my
endorsements  to  the:  1.)  "TOP  TEN  THINGS  THAT WOULD  MAKE  SUPERFUND MORE
EFFECTIVE" presented in Jason White's comments;  and the 2.) "Appended  Comments" of: Doris
Cellarius, Grant Cope, Aimee Houghton, Ken Jock, Vicky Peters and Lexi Shultz
NACEPT                          Report       12,                      Attachment A-Page 29

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Attachment A-Page 30                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Aimee Houghton
                        Associate Director
                        Center for Public Environmental Oversight
For numerous reasons that I  will  articulate below I  was  not  able  to  sign on  to  this report.
Personally, this was a difficult  decision  because I  have long been committed to the process of
consensus and I strongly  believe in seeing through what I  have begun.  However, those  two
factors,  by themselves, do not  provide enough  of a reason to endorse,  in full,  a  document that
causes me great concern.

In dissenting I  wish to express  my support for my Subcommittee colleagues who worked so hard
and  so  diligently  for the  protection  of  human health  and  the  environment—particularly
representatives of the tribal and  environmental justice communities.  From experience I  know of the
sacrifices these members must make in order to participate in national policy  dialogues  and their
knowledge, expertise, and commitment are invaluable. I would also  like to  make clear that I concur
with the consensus recommendations and would like to see them implemented.  Finally, I wish to
fully and formally endorse the comments of Jason White, which include "Top 10 Issues To Protect
Public Health and the Environment at Superfund Sites", as well as the  appended comments of
Dolores Herrera, Doris Cellarius, Alexandra Shultz, Vicky Peters, Ken Jock, and Grant Cope.

In closing, I would like to express  my thanks to EPA and all those who took the time to share their
knowledge and expertise with the committee.

The Hindrance of Process

Our initial charge (see Appendices, A-7) was  to  put  forward  consensus recommendations to
address serious issues surrounding the future of the Superfund  program.  Having  served on  two
previous consensus  policy dialogues, I  had  some experience with the process and  more than an
inkling as to what to  expect when  a large and diverse group of people come together in one room,
around one table, to discuss issues where they are bound to disagree. This group was  no different.

What was different was the changing structure of the group and the  timetable. In my experience,  a
consensus dialogue is best served when all members understand  how report recommendations will
be achieved and characterized and what type  of  attribution will take place.  With this type of
foundation  in place, the facilitation team can  move the  process  in a way designed to gain  a
common understanding of the issues,  build  trust among  individuals and often strangers, begin to
develop recommendations, start some sort of negotiation process and  finally begin the process of
compromising which  is essential to achieve consensus.

Time is also immensely important. Committee members must have  enough time to be  briefed on  a
range of topics relevant to the discussions, break the topics up and meet in smaller groups, work
through  controversial issues as a large group and finally begin to craft recommendations.  Once the
crafting begins, the real consensus process begins.  Even with a draft document in the  final stages
it is not unusual for  members to  deliberate  over the fine points  for months.  Ultimately, it is that
deliberation that produces a quality document whose recommendations live and breathe and
whose legacy is beneficial to the public and impacted stakeholders long into the future.

I am sorry to say that is not the process that I have been engaged  in for the last 20 months. While I
have the highest regard for all of  my colleagues who served  on this committee, we were all badly
served  by a process that boxed us in and did not allow us to develop a document of significance.
Initially,  EPA gave the Subcommittee 18 months  to finish our work.  With a charge as enormous as
ours we were bound for failure  from the start.  Based upon prior experience it often takes over  a
year before a first draft  of the  report appears.   Our Subcommittee also went  a year before
producing  a first draft.  Unfortunately that first draft was produced well before we had agreed—even
conceptually—on what we wanted to  do or say.  As  a result,  we focused  on  language before
engaging in creative  problem solving of the issues.

Quite a few Subcommittee members warned that we were not ready to produce a draft but, given
the time constraints, the Chair insisted that we didn't have much of a choice.
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Typically, when that draft finally does appear it gives  members something to  react to  and the
process begins its next evolution—determining the priorities of the members. Up until that  point
most members have been simply "having a dialogue." Once the ideas are put on paper, dynamics
get to be a bit more "real".  As more drafts develop, finer points of the debate are brought to light
and often times the whole structure of the  report will shift once people see their words in  print.
Again, this group was no different.   A little over a year after our first meeting, we had a first draft,
yet we were ending in six months.  The timeframe was impossible.  With that in mind the Chair
pushed us to resolve differences and develop recommendations.

Resolving differences was not the problem.  Resolving differences under immense pressure where
trust was not fully developed became the problem. In September 2004 Ms. Horinko addressed the
Subcommittee and  told us that if we could  not reach consensus  EPA would still like to hear the
discussions we had on those particular topics.  I believe at this moment we began to veer away
from consensus. At the following  meeting in early November,  an  EPA staff member informed the
Subcommittee that if we did end up with a report that contained  some consensus recommendations
and a range of views  on topics where the Subcommittee could not agree,  then EPA would look at
those range of views and take those into consideration as well when developing policy.

At this moment any incentive for consensus, on difficult topics, was effectively eliminated—why
compromise when  all views will be equally considered.  The Subcommittee now engaged in  a
"range of views" process.  The range of views had to be  somehow characterized and we ultimately
ended  up with a  "some  people/some  people"  approach.   Such an  approach  is bound  to
misrepresent the nature of the discussions and confuse the positions of Subcommittee members

Our facilitators,  the Meridian Institute, were  then  stuck with the challenge of trying to represent a
range of views and, not surprisingly, the starkest views are often what appear in the text while the
nuances get  lost.   EPA doesn't need to know  polarized  views.  They are well aware of those
positions.  What they do need to know is how to bring those different views together. The views
that might have reflected some movement in either direction are, for the most part, absent from this
report.  Thus,  the report doesn't ultimately do justice to the complexity of the discussions and views.
Consensus seeks to avoid this dilemma by striking middle  ground. Consensus also demands that
everyone own the entire product, and that the manner in which consensus is achieved is apparent
(or transparent) to all.

Ultimately, ideas that may have had the support of 30 members could end up being vetoed by just
one person, and ultimately represented with equal validity  as an opinion voiced by one.  Readers
won't be able to discern that and,  in some  instances, neither  will Subcommittee members.  The
some people/some people  characterization,  far from  demanding  everyone to  own the entire
product, gives people  a vehicle to hide behind.

As an  example, I  believe the funding discussion  in  the Report  erroneously emphasizes the
disagreement about the source of funding.  In reality, while some of us argued for reinstatement of
the fees, we were all willing to forego such a  recommendation if we could get a temporary increase,
in a reasonable amount (as articulated in three separate  reports by the IG,  GAO and Resources for
the Future) to address backlog sites.  Sufficient, interim  funding is critical to help communities at
sites that have been delayed because of insufficient funds—such as New Bedford Harbor. It was
the placement  of restrictions  on  the use  of the extra funding that  caused the breakdown in
negotiations, not the reinstatement  of the fees. To state otherwise completely misrepresents not
only my position but also, what actually transpired.  (Please see Grant Cope's appended comments
for further details.)

Transparency of Dialogue

At least three of the consensus recommendations deal  with the subject of transparency - both in
EPA's decision-making process and publicly available data on the Superfund program. These are
all recommendations I fully support.  However, in many instances the Subcommittee was unable to
put into practice what it recommends to  EPA.  Due to  the evolving "range of views" format the
nature of consensus recommendations kept changing.  Members would leave a meeting believing
they had consensus on a recommendation only to find out  later that members had not agreed, but
had not spoken up. Often members were in the dark as to where other  members stood on certain
issues  making it difficult to understand all sides and work toward an acceptable compromise.  In
Attachment A-Page 32                  NACEPT         Subcommittee Final       |      12,

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short, I believe we did not have an open and transparent dialogue process.  Indeed, in reviewing
the final report I was often times at a loss as to whose views were being represented by which text.
This  is something I have never before experienced in a FACA dialogue process.

As an example,  in the March 5, 2004 preview draft of the final report the following language was
included in Recommendation 1: Anticipated cleanup costs and the amount of funds available
in the Superfund Program budget should not be criteria used to include or exclude sites
from the NPL.

To my knowledge this recommendation had full consensus as it had appeared in at least two prior
drafts.  In the final version of the report that sentence is no longer included in the recommendation.
Why is it gone and  who objected to  it?  I would imagine that most members, like myself, have no
answer for either question.

Technical Assistance Grants (TAGS)

Another recommendation that  did  not make it  into this report but which  I feel is  crucial  to
communities impacted by Superfund or Superfund candidate sites is one on technical assistance.
In order for communities to be fully engaged in the cleanup process they often need the resources
a  Technical  Assistance  Grant can  provide.    The  Subcommittee was  working  toward  a
recommendation that would  have  provided  grants to community  groups at NPL-eligible  sites.
Current  EPA guidance already allows grants to be awarded for sites that are proposed for listing.
This  type  of assistance  would  only be  made available if TAG funding  exceeded the requests
generated  by community groups at listed sites. Other members on the committee—again, I'm not
certain who—did not support this recommendation.
NACEPT                         Report       12,                     Attachment A-Page 33

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Attachment A-Page 34                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Ken Jock
                        Director, Environment Division
                        St. Regis Mohawk Tribe
In addition to the "Top 10 Issues To Protect the Public Health and The Environment at Superfund
Sites," the statements below reflect positions on important issues addressed in the Report. I also
endorse the comments  of Jason White, Dolores Herrera, Lexi Shultz, Aimee Houghton, Vicky
Peters, and Grant Cope.

Reporting :  Accurate and transparent reporting of site and program progress, anticipated program
costs, listing decisions,  and site conditions at NFRP'd sites,  is critical for evaluating  program
success, and preventing  unacceptable risks.

Increased Management  of Mega and Pre-SARA Sites:  The costs  of these sites in  money, lost
community values and, for the latter, damaged program credibility justify heightened attention, and
creative management to accelerate and improve decision-making at these sites.

Federal facilities:  The Federal facility cleanup program dwarfs the  NPL both in  risks posed and
costs of cleanup.  Tribes have been particularly impacted by  these facilities. The  progress of
cleanup is also significantly less.  Unique Problems related to these  facilities warrant a focused
dialogue on issues arising since 1996.

Protection of the Environment:  The  protection of human health is not more important  than the
protection of the environment. We are just a small part of the environment, and  the law requires
both.

Protection of Future Generations: The protection of our generation is  no more  important than the
protection of future generations.  We have an obligation to solve our own problems and not leave
them for others.  The  Haudenosaunee teachings tell us to consider the environmental effects our
decisions will have on the next seven generations.

Also endorsed  by:

Vicky Peters
Doris Cellarius
Aimee Houghton
Jason White
Dolores Herrara
Niawen/Thankyou,
NACEPT Superfund Subcommittee Final Report | April 12, 2004                  Attachment A-Page 35

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Attachment A-Page 36                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Mayor Frederick M. Kalisz, Jr.
                        City of New Bedford, MA
Serving on the NACEPT for the last twenty months has been a great honor and an excellent
educational experience for me.  The strength of any subcommittee is the quality  of the members
and of the leadership.  In this case, both were outstanding. I  do not know how EPA could  have
brought together a more informed, a more hard working, a more diverse,  a more articulate, or a
more passionately committed group of people to wrestle with the problems of Superfund, than the
subcommittee  it assembled.  Every member brought to the meetings a wealth of experience
dealing with the real problems of identifying and cleaning up hazardous waste sites.

This was not an academic group.   Even the academicians  among us came to the group with
pressing concerns about their own communities. My own City of New Bedford, MA has been  living
with a massive Superfund site in the middle of our Harbor, the economic and in many ways cultural
center of our community, for more than 20 years.  And unless funding is increased we are looking
at another 25  years before the Harbor is made  safe for  our  residents. Of course I brought my
concerns to the NACEPT. To do otherwise  would  have been  irresponsible. In fact, as the only
elected  municipal official on the subcommittee, I  did my best to represent the concerns of  other
cities  whose   residents  are affected  every  day  by the presence  of  a  Superfund  in  their
neighborhood.

My fellow members likewise came to the task at hand with overriding  responsibilities.  Industrial
representatives,  environmental advocates, tribal  spokespersons, community leaders, insurance
company representatives, state regulators, attorneys - all of them brought deeply held convictions,
based  on  their own experiences to the deliberations of the  subcommittee.  Diversity  of views,
experience, and interests was a great strength of the subcommittee.

Because of the group's  real world  orientation, agreements did not come  easily.   Everyone was
acutely aware of the stakes, and of their own responsibility to address the issues that confront them
on a day-to-day basis.

The divisions on the subcommittee reflect the divisions in the country. But with a major difference.
The subcommittee members engaged each  other  and engaged with  the real issues about the
future of the Superfund program with a sort of thoroughness and factual foundation that has  been
mostly missing from the national debate. Readers of the report may not find a comprehensive set of
recommendations, a fact which many of my fellow members and I regret. But they will find a suite
of recommendations aimed at improving the efficiency of the program.   They'll also find a full
statement of the key issues and points of view, and along with an accurate, factual statement of
present conditions.

The subcommittee report, in my view, provides a foundation for national decision-making.

And no  decision is more vital than how to finance the program during  the next five to ten years.
The subcommittee spent many hours on this topic.  While improvements in programmatic efficiency
may reduce the strain  on EPA resources, they won't solve the entire problem.  For this reason,  I
remain steadfast in my belief that the issue of increased funding for Superfund must be considered.
Some have criticized  us for going beyond  the charge. In my  opinion, confronting the funding
question head-on  was  an unavoidable responsibility. The  Superfund  program,  as  its  name
suggests, is at heart a program for financing  the cleanup of abandoned sites. In recent years, the
belief has emerged that the job of cleanup is mostly over, that the program has achieved its major
goals and that  the right approach for the future is to slowly phase it out. The subcommittee report
and the factual materials provided by EPA demonstrate that nothing could be further from the truth.
In fact, the need for a  well-funded program has never been greater. Years of study, investigation
and design have produced a  set of ready-to-go cleanup projects that now languish for  lack of
resources. The fundamental question, in my view, is whether to take on this challenge today, or to
pass it off to the next generation, when the costs  of action and the consequences of past inaction
will both be much greater. The issue could  not be clearer.   Now it is  for Congress and the
Administration to settle it.
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In closing I wish again to thank my fellow subcommittee members, Chairman Raymond Loehr and
Assistant Administrator Marianne Horinko for the opportunity to participate in this important effort.
Attachment A-Page 38                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:   State Superfund Managers - Joint Member Comments
                        Gary King
                        Illinois Environmental Protection Agency
                        Ed Putnam
                        New Jersey Department of Environmental Protection
                        Catherine Sharp
                        Oklahoma Department of Environmental Quality
In  past discussions  relative to the federal Superfund  program, the role  of State environmental
protection  agencies has frequently been downplayed, without an understanding of the critical role
States play across Superfund and all contaminant cleanup  programs.  We, as State Superfund
managers  and  members of the  NACEPT Superfund  Subcommittee, appreciate the thoughtful
consideration that was given to our views by the other  members of the Subcommittee throughout
the  discussions.  We  appreciate  that  the final  report  includes  an  important  consensus
recommendation (Recommendation 8) advocating  a continued  investment in capacity building for
State cleanup programs. Given the array of individual state capacities, and the challenges faced by
state programs (e.g., declining state budgets), and the diminishing resources at the national level,
the Subcommittee's  Final Report urges  EPA to continue its efforts to build the capacity of state
remediation programs.

As the Final  Report recognizes, building  capacity within State programs is essential to maintaining
a strong national Superfund program.   State cleanup programs  are an  important  piece  of the
cleanup  puzzle.  They serve as a complement to the national Superfund Program by  providing for
the cleanup  of  many sites that are  not eligible for the  NPL and, in some cases,  by providing
administrative mechanisms  to  oversee  cleanups  at sites that would  be eligible for the NPL.
Collectively,  state programs have addressed many thousands of contaminated sites -  including
some NPL-eligible sites - and they will continue to do so.

On the other hand, we are disappointed  that at the 11th hour consensus within  the Subcommittee,
which had  held for many months, disappeared with regard to  the role of costs in listing sites on the
NPL. We strongly advocated the inclusion in Recommendation 1 of the following sentence:

"Anticipated  cleanup costs and the amount of funds available  in the Superfund Program budget
should not be criteria used to include or exclude sites from the NPL".

This sentence does not appear  in the  Final Report.  While we acknowledge  that EPA decision
makers may have an awareness of costs and knowledge of likely program funding, we believe that
this knowledge should not be used to limit or expand the number or types of sites listed  on the
NPL. We believe that the NPL should represent true national  priorities-sites that meet the eligibility
criteria and are judged to need the expertise  and  resources that only the Superfund Program can
provide.

EPA should  place sites on the NPL based solely on consideration of a set of consistent factors.
Anticipated cleanup costs and the amount of money in  the Superfund Program budget should not
be criteria  used to include or exclude sites from the NPL.

In 2002, EPA instituted a new national-level process in which officials from the regional offices and
headquarters evaluate all NPL-candidate sites, group them  in  tiers  based  largely on the relative
significance  and urgency of risk  but also taking  into consideration other  program management
factors,  including budgetary constraints, and then  make recommendations  about which NPL
candidate  sites should  be  proposed for NPL listing.    Prior  to  this change, in general, EPA
headquarters provided guidance and oversight to the regions  on national listing  policy  and ensured
that  listing  packages  were appropriate and  legally  defensible.   Most NPL-candidate sites
recommended by regional offices were proposed for listing on the NPL, provided national policy
was  followed and the MRS  score was valid.   Since the advent of this new national-level  review
process, approximately  half of the  NPL-candidate sites sent  forward  by  regional offices to
headquarters have been proposed for NPL listing.  The  remaining NPL candidates sent forward by
NACEPT Superfund Subcommittee Final Report  | April 12, 2004                 Attachment A-Page 39

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the regions  have been  held  over  for reconsideration in future  listing cycles  thus  delaying the
remediation process indefinitely.

While the Subcommittee had  a range of opinions  about this national-level review process,  it did
agree that the national-level review process (if it is continued) should focus on:

•   bringing national consistency and a national perspective and judgment to bear on NPL listing
    proposals,
•   monitoring regional offices' implementation of Program guidance,
•   considering geographic fairness in NPL listings so that one region of the country does not
    inappropriately dominate the NPL, and
•   ensuring that MRS packages are legally defensible and of high quality.

The Final Report recognizes,  as did the Subcommittee, the ongoing and  critical nature of State
cleanup programs in supporting and implementing the federal Superfund program and providing
alternative cleanup  resources to address  non-NPL  sites. Although  States  are critical to the
successful  implementation  of environmental  remediation  programs,  we,  as State  Superfund
managers, recognize that States cannot fund remedial actions at NPL fund lead sites. It is vital to
the health of  our  citizens  and the protection of our environmental  resources for the federal
government to adequately fund the federal Superfund program.  This position is not only supported
by the three States  represented by Superfund Managers on the NACEPT Subcommittee, but by
virtually all States with active Superfund cleanup programs. Some states, like New Jersey, strongly
advocate reinstatement of the  expired Superfund tax to assure the adequate funding of the federal
Superfund program.

We, as State  Superfund managers,  do not believe that the current  funding  level  for  remedial
actions at NPL Fund lead sites is adequate. In our view the deficiencies in funding are creating a
stranglehold  on  EPA's ability  to  move  cleanups  forward  at these  sites.  We   remain  very
disappointed that the Subcommittee was unable  to put aside its differences and reach consensus
on a recommendation for additional funding.
Attachment A-Page 40                  NACEPT          Subcommittee Final       |      12,

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Position Statement of:  Edward C. Lorenz
                        Reid-Knox Professor of History and Political Science-
                        Alma College
                        Pine River Superfund Task Force Member
I find the report reflects well those recommendations about which there was universal agreement
and which specifically respond to the charge  given to the subcommittee.   Also, the  report
accurately discusses a range of other topics  about which  members became aware and  which
supplement the core recommendations.  I would include here especially those relating to ATSDR,
NIEHS, and long-term stewardship in Chapter VI.  The major weakness of the report is the failure
to find agreement on issues related to financing Superfund.  The later drafts of the report, I believe,
addressed well the thoughts of most members of the subcommittee on a  package of financial
recommendations, essential to return the program to dedicated funding wisely spent.

As a resident of a small community with one mega-site and two related Superfund sites, I  find it
unfortunate not to make recommendations related to financial management and needed  interim
levels of funding, especially given the  inclusion  in the  program's name the word fund.  The
subcommittee  seemed very  close to  consensus  on  such issues,  but the spirit of compromise
seemed poisoned by maneuvering for ideological, interest group, and political advantage.  Such
maneuvering reflects one of the worst features of current American  policy-making, the endless
struggle for staging the symbolic fight rather than a desire to practice both restraint in rhetoric and
prudence in policy to produce meaningful progress.

The search for short run ideological or political  benefit frustrated any effort to assess well the past
and current obligation to raise funds responsibly and spend them with  care and maximum impact.
This failure is of special concern to residents of communities such as mine who have seen recent
generations profit from behaviors that leave resources depleted and contaminated without regard to
the impact on our descendants. The failure to fully address funding in this  report, as  happens in so
many of  our political forums, reflects this generation's tendency to ignore  both its stewardship
responsibilities and  our need to pay the price for our mistakes and those of our parents.  Without in
any way favoring  one  mechanism over  another, I   regret that  such  a talented and diverse
subcommittee  could not agree on some means to halt deficit funding of Superfund. As both a
parent and grandparent, as well as a professor of history,  I know current financing of the program
irresponsibly transfers  the  cost of cleaning  our generation's  mess to the  accounts  of  our
descendants.

Perhaps it is too much to expect that the members of the subcommittee could overcome the  habits
of our generation to avoid responsibility. The habits are ingrained in our culture and unable to be
defied by a small group.  Even the charge to the  subcommittee avoided  consideration of funding
increases, despite the clear evidence,  described well in Chapter II, that a  gap is growing between
costs and funds available to on-the-ground clean-ups.  Whatever the explanation or excuse for not
recommending  some  solution to  the  funding  needs of  the program,  the failure  to formally
recommend  both adequate  funding  levels and  mechanisms  that would  improve  controls of
spending is a fundamental flaw of our report.

Despite such regret, I can say that both St. Louis, Michigan, and Alma College have  been honored
that one from among us has been invited to participate on the subcommittee with a group of people
who, as  our chair  has  said  so well, "fulfilled their charge extremely well and have done  so
professionally and positively." Likewise, it has been a  pleasure to work during the  last two years
with  many dedicated  EPA  employees  and  our facilitators who did   so  much  to  bring  our
deliberations to a fruitful conclusion.  Finally,  our chair  has played a model role  in leading  us
through  our deliberations.   I hope the  many recommendations on which we have  come to
agreement outweigh the loss inherent in what we have elected to omit.
NACEPT Superfund Subcommittee Final       |     12,2004                  Attachment A-Page 41

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Attachment A-Page 42                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:   Tom Newlon
                        Attorney, Stoel Rives
I would like to start out by thanking my fellow Subcommittee members, EPA staff and the facilitation
team for their very substantial efforts. I grew to deeply appreciate your professionalism, dedication
and hard work in the face of what proved to be an extremely daunting task. Thank you for allowing
me to participate.

My personal efforts on the Subcommittee focused on megasite issues, specifically the following:
(1) addressing the current backlog of fund-lead megasites that either are or will soon be ready for
remedial  action  implementation;  (2) identifying  factors  that  lead  to potentially-unnecessary
increases in costs and timelines, turning currently-listed sites that would not necessarily need to be
megasites into extremely expensive and difficult  endeavors that cross the  somewhat arbitrary
megasite cost threshold; and (3) recommending approaches to  potential new sites that could lead
to more cost-efficient and efficacious cleanup, thereby avoiding the creation of new megasites.

The megasites subgroup that I worked with over the course of the first year or so of Subcommittee
deliberations (which included representatives of all interests on the Subcommittee) received a great
deal  of highly informative  input from EPA and others, worked  collaboratively in  a non-politicized
environment,  and eventually came up with what nearly all of us viewed  as an important and well-
balanced set  of recommendations to address a variety of megasite-related issues. Although our
efforts were  well received  by  the vast  majority of Subcommittee members, the Subcommittee's
ground rules  requiring absolute consensus resulted in nearly all of our recommendations falling
victim to members who felt strongly that the reforms we were  recommending  might somehow
weaken elements of the program that they held dear.  As a  result, the final Subcommittee report
contains precious few of our subgroup recommendations,  and  the  explanatory text  has been
watered down from a hearty stew to the consistency of chicken  broth.0  In my three pages I will
attempt to  reconstruct some of the thinking that went into the megasite recommendations that were
eliminated in the last weeks of nearly two years of effort.

(1) Addressing the current backlog.  As a maturing program, a significant number of sites have now
reached the stage in the process where major expenditures on remedial  action implementation are
necessary. We saw firsthand the situation in New Bedford, and  learned that just a handful of fund-
lead  sites, if addressed in  the most cost-effective, expeditious fashion (i.e., quickly), would use up
EPA's entire remedial action budget for a number of years.  This  would be an untenable situation,
of course,  as it would shut down all other EPA-lead sites, be they ready for remedial action or at
some earlier stage. So how do we get more funds applied to sites like New Bedford Harbor? The
easy answer  is to recommend more funding for the agency.  However,  actual funding for on-the-
ground (or in the water) remediation efforts  is such a relatively  small  percentage of the overall
program budget that increased funding alone would not guarantee that the backlog of sites would
be effectively reduced.E  So  exploring  possible changes in the way  EPA  does its Superfund
business seemed appropriate,  rather than simply recommending that we throw more money at the
problem and hope for the  best. The funding  recommendation debate is summarized in the report
and very well documented in the record of the Subcommittee's deliberations, but as a megasite
issue, funding is only part of the equation.   How the  money is spent is also  key, and  linking
additional  funding to  an outside review  of the program's approach and expenditures seemed a
sensible approach/

A more fundamental change than  an audit,  however, would be a change in how EPA actually
carries out the work at fund-lead sites where there are no viable PRPs remaining.  Megasites of
D See "Talking  Dust Bowl Blues," Woody  Guthrie  ("Mighty thin stew,  though, you
could read a magazine right through it.")
E See Comments of Mel Skaggs and Lindene Patton for more  detail on  EPA budget
issues.
F See Lindene Patton comments for more detail on audit rationale and a discussion of
contracting and other reforms that  hold  great  promise  for  improving  the cost-
effectiveness of cleanup implementation.
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this type have a very poor record of extremely lengthy timelines and  extraordinary expenditures.
An  alternative approach would be to make use of creative contracting  mechanisms and direct
appropriations for the limited number of sites that currently hamstring the agency's overall program.
For example, the cleanup needed at New Bedford has been identified in a ROD and designed.  The
only thing standing in the way of completion within three years is adequate funding.  EPA's current
approach, however, would drag this cleanup out over 15 or more years. Anyone familiar with major
project construction knows that massive cost overruns and inefficiencies  are likely to accompany
such an attenuated timeline. As an alternative approach, why not put the cleanup out to bid so that
private entities (backed by the appropriate insurance or other financial instruments) could take on
that cleanup obligation  and move it forward expeditiously to completion.  A one-off appropriation
from Congress for this effort would bring new cleanup money directly to implementation of a major
remedial action, without the funds being  watered down in the welter of other obligations that seem
to bleed off Superfund appropriations before they can be applied to  on-the-ground cleanup. Those
in Congress who are normally opposed to additional funding for Superfund due to (in their view) its
nearly-legendary inefficiencies and inequities would be attracted to an alternative approach  that
bypasses much  of the current remedial action implementation  process, giving  funding a much
better chance of success.  Since the final cleanup  measures have already been decided  on  and
designed, EPA and Congress would not be delegating risk decisions to a private party, but rather
would be tapping into a  more efficient way to get the identified work  done.  Creative contracting and
financing of this type must be explored if the agency is to quickly work through the backlog  of sites
that are ready to go. Communities deserve  no less,  and EPA and Congress should be willing to go
outside the  box, at least on a pilot basis, to remedy this backlog.

(2)  Identifying  factors that turn sites that need not be meqasites into  meqasites.   Discussions
around these  issues were difficult due to a lack of common experiences and understanding among
the  Subcommittee  members.  As Empedocles wrote in  the 5th  century B.C., "Each man believes
only his experience."  The experiences, or at least beliefs, represented on the Subcommittee were
widely divergent on the subject of whether  there are megasites currently being addressed by the
program that  could have been handled differently so  as not  to  become  megasites, while still
maintaining an  appropriate  level  of protection to  human health  and the  environment.   Views
regarding how best to define and address risk were expressed in the Subcommittee as  a whole, but
the  final report reflects little on the tie between approaches to risk  and the creation of megasites.
Clearly,  if the  agency is serious about discovering whether current  megasites really needed to be
so expensive, a fresh and objective review of how risk is defined and addressed in the program is
necessary,  with  such a review most appropriately  being  carried out  by  experts from outside  of
EPA.G   Additionally, a review of how the program  makes use of its resources at EPA-lead sites
would be a  good approach, this being a  link to the audit recommendation that did not make it into
the  final report.

The megasites subgroup did  identify  a set of factors that, when present, seemed to correlate  well
with very expensive sites and lengthy timelines.  These were sites that involve large geographic
areas with  a  large  number of  PRPs, multiple  contaminant  sources,  and  widely dispersed
contamination  that tends  to  be  concentrated in  certain  "hotspot"  areas.   Sites with these
characteristics present a great  deal of uncertainty about whether actionable risk is really present
across the entire area (as opposed to the hotspots where the remediation need is likely clear) and
huge transaction costs  associated with decisionmaking, all of which combine to create extremely
lengthy  process timelines and very high  process  costs.   In  the experience  of  many  on the
Subcommittee, sites of this type would frequently be better addressed in smaller units, meaning
that needed cleanup  would be accomplished better,  faster and cheaper, with  no commensurate
diminution  in   environmental  protection.H    The   megasites  subgroup  brought  forward  a
recommendation on this topic which did  not survive due to the objections of a small group on the
Subcommittee that seemed bent on insisting that more  money for  business-as-usual  at EPA  was
the  only viable fix for the megasite problem.
G See Comments of Richard Stewart and Jane Gardner on the need for an updated
approach to risk characterization and prioritization in the Superfund program.
H See Comments of Jim Derouin on addressing large areas of this type  as composites
of smaller areas that each may  or may  not require the  attention  of the  federal
Superfund program.



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(3)  New approaches that could help prevent unnecessary meqasite problems in the future.  The
package of recommendations originally suggested  to  the  Subcommittee  from the  megasites
workgroup  included the "small can be  beautiful" recommendation  described  above, as well as
recommendations on more frequent use of Enhanced Site Assessments and additional early (pre-
listing) input from  all  interests, particularly  at  potential large-area  megasites.1   The enhanced
coordination recommendation survived, but  lost a lot of its power  to effectively streamline the
program when the corollary recommendations  from  our subgroup were eliminated.  Enhanced
collaboration and coordination  with the  community, state,  PRPs, Tribal governments and  others
gives EPA the opportunity to assess potential  risks  and take more of an iterative approach to
certain types of  sites.  "Subdividing" is not  a dirty word if it means that on-the-ground cleanup
happens quicker and is more effective.  Twenty-year process timelines with little or no cleanup may
be useful for those of us who make their living representing parties who participate in that process,
but any process that takes that long and is that  arduous to get through is not serving the broader
community well,  either in  terms of fiscal responsibility or protection  of human  health and the
environment.   Automatically listing large   areas  on  the  NPL,  before exploring all  possible
alternatives to address specifically-identified  risk drivers (i.e.,  sub-areas that are clearly hotspots
that need remediation), is not a viable answer for the  program over the long term. Enhanced site
assessments involving additional data gathering and  analysis should  be employed for early
identification of areas that can be addressed in a more focused,  expedited way prior to  simply
listing an entire large geographic area and letting the chips fall where they may.

Despite the lack  of absolute unanimity on the original  subgroup recommendations on megasites,  I
urge EPA to review them carefully and to be bold in taking creative new approaches that give some
promise  of  streamlining the process  and  getting to decisions  in a more  cost-effective  and
expeditious  fashion.J   As  many  Subcommittee   members  discovered,  being  bold  about
recommending changes to the  Superfund program has its considerable perils and frustrations, no
matter how self-evident the need  for improvement  and no  matter how  promising  different
approaches may be in improving the program's performance.


"It is not possible to achieve certainty in our  knowledge of the empirical world,  but we can  devise
workable approximations and act on them."  John Locke (1632 - 1704)

"In practical life, we must steer a middle course  between demanding  a degree of certainty that we
can never have and treating all possibilities  as  if they were  of equal weight when they are not."
Bryan Magee (20th Century Philosopher)
1 See Comments of Stephen Elbert on the merits of early involvement of all interests
and the potential use of Coordinating Committees on a pilot basis.
1  "He  not busy being born is busy dying."   Bob Dylan "It's Alright Ma (I'm Only
Bleeding)"


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Attachment A-Page 46                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Lindene Patton
                        Vice President & Counsel
                        Zurich Specialties
I appreciated the opportunity to participate as a member of the NACEPT Superfund Subcommittee.
Each  member of the Subcommittee brought a unique perspective to the deliberations and I was
privileged to learn much from each and every member.  I would like to thank the facilitators and
Chair for the work that each performed in the face of an extraordinarily polarized group. I commend
the EPA for initiating the dialogue, and  hope that the Agency will continue to investigate and
explore the many ideas identified in the multitude of discussions, deliberations and written works
prepared by the Subcommittee members during the many months of effort.

I agree with Mr. Derouin's observations with respect to the impact of the expansion of the scope of
the discussions  to  include funding  issues.  In  hindsight, while some  may  have thought  the
discussion of funding would assist in the dialogue, the expansion of the discussion to encompass
funding was extremely destructive, resulting  in the loss of existing consensus and focus.

Missed  Opportunities: Alternative Settlement Strategies, Contract Reform and Independent
Audit of Program Expenditures

Overall,  the breadth of issues encompassed by the charge was such that discussion of complex
issues outside the experience base of the majority of the Subcommittee  members was generally
avoided. The Subcommittee spent the majority of its time obtaining and reviewing information about
the Superfund Program itself,  and testimonials related to  community needs.  The limited number,
schedule and structure of the meetings was  such that no time was provided for expert testimony on
many  issues   of  interest  that  could   have  impacted  deliberations and  yielded   quality
recommendations.  Few, if any,  Subcommittee  members were comfortable  discussing  issues
related to improving the performance of the Superfund Program using  auditing,  insurance,  finance
and contract reform techniques. Several Subcommittee members commented during deliberations
that they needed independent expert  advice to make any recommendation on auditing, finance,
alternative settlements and insurance applications. Ultimately, the exigencies of time, combined
with the  complexity  of the issues resulted in a failure to explore the issues as a group.

I refer any  readers who have interest in  the issues of alternative settlement strategies, contract
reform, and funds leveraging using other programs to the administrative record which supports this
FACA. The record  should include a series of documents developed by individual Subcommittee
members on specific complex  topics, including two documents that I developed and distributed to
members and  the EPA on the subjects of alternative settlement strategies and  contract  reform.
Additionally, prior  drafts  of  the  report  and  transcripts of the  deliberations  include  specific
discussions regarding recommendations  related to auditing  of  the Agency expenditures in  the
Superfund Program over the last five (5) years.

I believe that the US Environmental Protection Agency could  realize significant performance and
financial improvements in the Superfund Program, including  a substantial improvement in  human
health and  environmental conditions,  because funds  could be  spent  more efficiently and needs
would be better justified, if the following specific actions were taken:
1.   Implementation of a comprehensive audit of the Superfund Program appropriations
    and expenditures for the last five years. The purpose of such an audit would be to  identify
    where and how funds are  expended in  detail, especially funds which are  not extramural funds
    used for remedial or removal actions. The Agency must establish a link between  funds spent
    on salaries, other than extramural contracts, and environmental and health improvements at
    Superfund sites. Some argue that such a link would be best  established  using risk based
    techniques to demonstrate performance. From benchmarking  perspective, current ratios of
    Agency administration costs  as compared to the actual dollars  spent on  investigative and
    remedial  action  activities at  Superfund  sites are not  consistent with  private  sector best
    practices.  The  report notes that only approximately 17% of Superfund expenditures go to  site
    investigation and remediation costs.  By implication,  more  than 80% of costs are spent on
    administrative activities. In the private environmental remediation industry world, even a 20%
    administrative cost load might be considered inefficient and non-competitive. In the case of the
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    EPA, the numbers are inverted. An audit would serve to provide the transparency necessary to
    explain the extreme  variance is administrative cost loading. I  recognize that programmatic
    requirements for the Agency are different from anything existing in the private sector, however,
    putting a price with greater description of the work on the specifics of such administrative costs
    would  enable  a much needed policy discussion about prioritization of funding  within the
    Agency. Throughout the deliberations, the Agency employees made great efforts to supply the
    Subcommittee with requested data on expenditures, but despite their valiant efforts, in many
    cases they were unable to supply the data requested because the Agency simply did not track
    expenditures with the detail  necessary to  answer the questions asked. This situation must
    change if the Superfund Program is to continue its success and an audit is one of the activities
    necessary to get there.
2.   Estimation of orphan share liabilities  at Sites on the NPL: Throughout the deliberations,
    many Subcommittee members expressed the  desire to understand  just what true budgetary
    needs  (in private sector terms, this would be called "liabilities") existed within the Agency for
    the Superfund  Program. The  Agency was unable to  provide any idea of multiple year financial
    exposure or budgetary need for the Superfund Program other than those estimated by a study
    conducted by a non-profit several years ago. The only other studies the Agency could point to
    were certain Agency  reports referred to in the text of the report - but such reports only looked
    to single year  program needs  and not multi-year or present value funding requirements.
    Further, when asked  about just how much money the Agency thought it would need to pay for
    clean-up of "orphan sites", especially those that are mega-sites, the Agency not only said it
    was unable to  answer the question  because it did not even have rough  estimates of the
    liabilities (eg costs to clean),  they further indicated that to do so might impact enforcement
    sensitive data.  With all due respect and deference to enforcement sensitive information, when
    pushed in discussions, EPA  staff did acknowledge that the Agency does know when it is
    unlikely to have any  recovery from PRPs - and documents do exist within the Agency which
    acknowledge same.  In an environment where accountability  and  transparency are critical,
    where  FASB standards clearly require disclosure of environmental liabilities for private sector
    business, and  where  developing  GASB  standards  require  the  same  for governmental
    agencies, it is  hard to understand how the  EPA can  continue on without estimating  its
    liabilities. The Departments of Defense and Energy have clearly estimated their environmental
    liabilities. How is it that the EPA can be treated any  differently ? Some complain that the EPA
    cannot afford to use  precious funds to estimate such liabilities. I wonder how they can afford
    not to.  Transparency is required to assure an honest and open dialogue about public policy
    issues  surrounding Superfund -especially budgetary needs;
3.   Mega  Site  Management Reforms:  I  would  recommend implementation of  mega  site
    management reforms far beyond those articulated in  this report. I would recommend that mega
    sites be managed by persons with construction management and cost-engineering experience.
    The softening of the  recommendation text in the report to include the ability to use staff who
    simply  have negotiation skills skirts the  issue and will not serve the Agency well. The  hard
    facts may be  that to implement  such a recommendation,  the Agency may either require
    workforce retraining or  acquisition  of human  resources with  cutting  edge skills,  and
    concomitant elimination of staff with obsolete skills through early retirement programs or other
    initiatives. I do  not make this recommendation lightly. The private sector, including industries in
    which I have worked, learned the hard way through excessive and inefficient expenditures that
    construction management and  cost  engineering expertise  is critical to cost effective and
    performance effective management of complex clean-ups;
4.   Contract Reform: Please look to materials I drafted and placed into the record for suggested
    contract  reforms.  In short,  I  suggest  exploration  of the  use of  guaranteed fixed price
    remediation  contracts,  requirements contracts,   and  indefinite  quantity  with  guaranteed
    minimums  contracts.  Other  agencies have saved  substantial monies implementing such
    reforms.  Lessons  have also been learned in such efforts, and the EPA should learn from the
    efforts of others.
5.   Settlement Reform  Initiatives: Please look to the  administrative record for detailed reports
    which I submitted on  alternative settlement strategies. In short, I suggest that credit risk for the
    EPA and many PRP's increases  over time. Said otherwise, where a PRP  is financially
    unstable, the likelihood that the  entity will declare bankruptcy or become otherwise unable to
    pay its liabilities increases with time. If all or most PRP's on a site become insolvent, the EPA
    will likely be left to pay the bill through the  Superfund Program. In  private industry,  to avoid
    being left with an  insolvent debtor, creditors make professional judgements about when to
    settle disputes  to  avoid  being  left with the entire bill.  I suggest  that  to  avoid  increasing
    insolvency risk  and bad debt risk that the  EPA should, in conjunction with  or as  part of the
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    audit  suggested  above,  perform  a multi-years  needs and credit  risk analysis  for  each
    Superfund Site. Where credit risk is substantial,  the EPA should look to alternative settlement
    strategies, including  fair  share  allocations and  integration  of financial instruments  such as
    insurance, to  minimize future liability  (budget  needs) for  the  program. Such actions can
    proceed in a way to avoid  forfeiture of basic  programmatic liability enforcement schemes,
    consistent with current administrative policy reforms, and in a manner which improves ultimate
    protection and human health and the environment.
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Attachment A-Page 50                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:   Vicky Peters
                        Senior Assistant Attorney General
                        Natural Resources and Environment Section
                        State of Colorado
With Concurrence of Aimee Houghton, Doris Cellarius, Jason White, Ed Lorenz, Dolores Herrera,
Alexandra Shultz, Grant Cope

I also endorse: "Top 10 Issues To Protect Public Health and The Environment at Superfund Sites"
(See  Jason  White's appended statement); State Superfund Managers'  Statement (except the
endorsement of first bullet for national review by headquarters of NPL-candidate sites);   Ed
Putnam's statement on the role of cost in listing; Alexandra Shultz's discussion regarding many of
these same  issues and the importance of pollution  prevention, environmental  compliance and
effective financial assurances.

Regarding the Role of Risk in the Superfund Program

Absent a dramatic paradigm shift, risk assessment will continue to be a necessary but imperfect
tool in the Superfund program, as well as every other pollution control program.  In Superfund, the
question of risk is raised at every stage of the process:  1.) whether the site poses sufficient risk to
warrant listing on the NPL;  2.) what cleanup is necessary to ensure that unacceptable risks are
eliminated, i.e., "how clean is clean?"; 3.) whether risks warrant accelerated response, e.g., through
a removal action, or a higher priority remedial action;   and finally 4.) whether the success of the
Superfund should be measured  by risk reduction achieved. The Subcommittee did not address the
second question and disagreed on the other three.

Consideration of Risk in Listing Decisions

Generally the Subcommittee agreed that the NPL should reflect sites that pose a significant risk to
human health and the environment and  that likely will not be adequately cleaned  up absent the
resources available to sites listed on the NPL. We did not define "significant" riskK.  This is not
surprising. For several years, scores of stakeholders,  lobbyists and Congressional staff attempted
to define  "NPL caliber" sites and exclude them from Voluntary Cleanup Program Agreements and
proposed legislation. The exercise proved futile; instead,  these agreements and the "Brownfields"
statute exclude sites that have entered into the Superfund  assessment process.

I believe that the determination  of "significant risk" should be generally consistent with the level of
risk posed by sites that have been  proposed for listing in the past  10 years or so, (as adjusted
through  implementation of Recommendation 4), and should be based on the  application of a
standard  set of criteria, rather than a comparison among NPL-candidate sites  in any given year. A
site that has been  sent forward by an  EPA region as posing a significant risk should be  listed
regardless of how much it costs and how soon funding can be made available for its cleanups;
otherwise, communities at sites left off the list could actually experience greater threats than some
sites put  on  if the competition for the former was  greater or funding less in the year(s) they are
considered.1

Criticisms that the MRS has not been screening out enough sites fell into two groups":  a.) current
or potential exposures predicted by the MRS could be disproved with site-specific data; and b.) the
K We also did not agree what constituted "adequate" cleanup, but I am not addressing
that issue.
L See also comments submitted on this subject by Ed Putnam.
M Community, environmental, tribal, and State members also questioned whether the
current  listing process has kept pace with  our  growing knowledge  of risks via
pathways such as vapor intrusion and subsistence lifestyles, among other things.
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MRS does not reflect risk, and allows the listing of sites with  "hypothetical potential future risks."N
The prior criticism should be addressed by Recommendation 4.

The terms, "current actual risk" versus "potential  future risk," are themselves confusing, as  risk
inherently refers to the future.  People who are currently exposed and suffering adverse effects are
not "at risk;" they  are injured.  I believe, however, that the term, "potential future risk," is meant to
relate primarily to changes in  land/water use and also,  perhaps, to potential future events and/or
migration.  Examples of the latter, would be a tailing  impoundment that might fail under certain
conditions,  or  buried  contaminated  sediments that could be  disturbed by  certain  natural or
anthropogenic circumstances.   Regarding such cases, I cannot agree to a blanket policy that would
preclude EPA  from listing  such  sites, or  assign  them  a priority so  low  that they  are never
addressed.   Only people  familiar with  the site,  who  could  judge,  with the  input of  other
stakeholders, the  likelihood of such events transpiring,  and the potential for harm, should decide
whether such sites pose a significant risk to human health and the environment.

I do not support spending hundreds of millions of dollars to address contamination that could not
reasonably result  in unacceptable  exposures to humans  or the environment.  Unfortunately, the
Subcommittee cannot  prescribe good judgment.  As long as the event does not occur, of course
society is better off addressing on-going exposures.  If such occurrence does occur, however,  and
results in serious adverse effects,  or  greatly increased cleanup costs,  society is  ill-served.
Therefore, the listing of such sites should not be automatically precluded, but rather, such decisions
should be left to the regions as informed by the outreach suggested in Recommendation 3.

Apart from the future event scenario, as discussed above,  I cannot support precluding the listing of
a site with no current exposure for three reasons: first,  I have seen from personal experience how
quickly land use can change.  Development  moves far faster than Superfund. Houses have been
built on or immediately adjacent to contaminated sites that were not cleaned up a few  years  ago
because residential use was  not "reasonably anticipated" by EPA project  managers.   Second,
allowing contamination to  migrate to human or  ecological receptors  before taking action  is ill-
advised because  cleanup costs would increase,  and greater  injuries to natural resources would
occur in the process.   In either instance, allowing individuals (or ecological receptors) to suffer
exposure before addressing known contamination would,  in my view, be unconscionable.  Third,
even  if exposures could  be  averted  indefinitely, the  resources would  remain  injured   and
unproductive.   CERCLA was  passed not only to protect against on-going threats but also to
mitigate the occurrence of national sacrifice areas.  Regions and stakeholders are best able to
weigh these considerations and determine when listing is appropriate.

Consideration of Risk in Prioritization of Sites on the NPL

Critics have for years admonished EPA and  DOD/DOE to incorporate the  principle of "worst first"
into their cleanup  programs. While cleanup of the most contaminated and dangerous sites first is a
laudable goal, much of such  criticism reflects a lack of understanding of the complexities of the
sites  addressed by these programs, as well as  the  issues  involved in  risk  assessment.   For
example, in ranking risks to human health, how would one decide which is worse, cancer or lupus;
chronic respiratory infections  or  decreased sperm  count?   Toxicity includes not  only  the
concentrations at  which chemicals are found but also the  severity of their effects.  If one site  has
toluene orders of  magnitude over a drinking  water standard and another has  nitrosodimethylamine
(carcinogenic at parts per trillion level) barely above a risk-based level, which site is worse?  What
if the  receptors include an environmental justice  community where certain baseline diseases are
more  prevalent?   Of course, the complexities  would be exponentially  greater if risks to  the
environment and  ecological receptors were  added. Even if such judgments could  theoretically be
made, the resources it would take to evaluate thousands of sites would be enormous.

Although any prioritization  must consider risk in determining priorities,  such  consideration cannot
be reduced to a quantitative ranking but rather might be subjected to broad categories such as  1, 2
N No specific examples of inappropriately listed (or unlisted sites) were discussed by
the Subcommittee.
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and 3°. Category 1 might be sites where acute (i.e., less than 10 days) exposure could result in
severe adverse effects. Category 3 might be mild effects after chronic exposure.  Everything else,
which would be most sites, would likely fall in-between.  Even with such a simplistic approach,
reasonable people could disagree on what are mild versus moderate or moderate versus severe
effects,  and what would  be moderate  for most could be severe  or even  deadly  for sensitive
subpopulations.  Furthermore, the  uncertainties  in  risk assessment render more  quantitative
rankings fruitless; for example, we know virtually nothing about synergistic or antagonistic effects
from multiple chemical interactions, very little about the sensitivities of children and the potential for
endocrine  disruption in pregnant women, and are only now exploring the toxicological significance
of hormesis. The usefulness of the risk assessment tool should not be oversold.

The prioritization approach that the Subcommittee was working toward, and that I endorse, would
require analysis of the likelihood of exposure, (including whether there was current exposure), the
degree of  potential  harm,  including whether exposure would result in acute or chronic toxicity, the
type of toxicity associated with the contaminants at the site, and  the amount of toxic substances
that were  present, among other factors.  All of these factors would be evaluated qualitatively with
active participation of stakeholders from the sites,  and accountability for decisions made.  Such a
rigorous, transparent process is more likely to result in good decisions than one in which arbitrary
numerical  values are assigned to various site characteristics.

The Subcommittee's unwillingness to engage in quantitative relative risk ranking should not come
as a surprise. FFERDCP had five years in which to develop a prioritization approach, (among other
things);  it gave up on relative risk ranking fairly early on. DOD, (glutton for punishment), continues
to "quantify" relative risk in  its  recent Munitions Response Site Prioritization  Protocol and Range
Rule Risk Methodology and continues  to  be  attacked by States because  application of these
models  results in  disparate  and sometimes  nonsensical conclusions.0   DOD  attempted  to
categorize all of its contaminated sites  and were criticized  because virtually all of them  were
designated as high risk. DOE and EPA gave up long ago.R

Consideration of Risk Reduction in Measuring Program Progress (MPP)

        EPA is  also  under pressure to use risk  reduction  measures of program  progress  for
Superfund. Such measures would be difficult if not impossible to develop. In fact, the Work Group
on MPP invested considerable time  and energy in an effort  to develop meaningful, transparent,
clear and simple risk reduction  measures that would not require significant additional  expenditures
to gather and collate data; however,  the group was unable to  satisfy these goals. This is largely
due to the difficulty in defining populations at risk. EPA identifies potential exposure pathways and
receptors;  however,  once identified, EPA does not try to quantify precisely the  number of receptors,
and the exact risk to which they are exposed, both of which can be transient.  Nor can the agency
capture averted threats to future populations because it cannot predict how adjacent  areas will be
developed and uses changed.  What EPA can do is measure when  all threats that are posed by
contamination at a site are adequately addressed - i.e., deletion of the site from the NPL
° Regardless of such categorizations, assignments of risk must be augmented by other
principles and site-specific factors discussed in the body of the  report to ensure a
well-managed and cost-effective program.
p Federal Facilities Environmental Restoration Dialogue Committee
0 See e.g., Superfund Report,  January 5,  2004,  "States Attack  DOD Proposal for
Prioritizing Munitions Cleanups."
R EPA does apply weighting factors to "new starts" each year, but they are not limited
to risk factors, and I and other members did not agree with them.
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Attachment A-Page 54                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Edward Putnam
                        Superfund Program Manager
                        New Jersey Department of Environmental Protection
This statement explains the reasoning behind my decision to disassociate with the report.  A
separate joint statement by the three State Superfund Managers on the committee is also included
in this appendix. I also wish to support the Top 10 Issues To Protect the Public Health and The
Environment at Superfund Sites.

The process used to draft this report had as an objective reaching consensus on a given statement,
in order for it to be  considered a "Bolded Recommendation". This objective is what led to the
substantial  reduction in  the number of recommendations from previous drafts,  including those
made relative to the funding to  the program.  Unfortunately,  this  objective was seemingly
abandoned on the very  last draft of the document. Specifically, Recommendation 1  contained a
statement that if EPA were to institute a Headquarters (HQ) level review of NPL eligible sites  in
order to decide which sites to propose for the NPL, that  review should not consider cost as a
factor. This statement was crucial to my consent of this recommendation.

For background, HQ review of the listing packages  was previously limited to a quality control review
of the HRS, which by rule is the only criteria needed for listing a site. The EPA region and the state
have already determined that the site  requires the resources of Superfund, or  it would  not have
been passed on to HQ. Currently, EPA HQ has developed a tiered ranking of NPL eligible sites.
Once tiered, then several factors including cost, and more particular the cost to the fund,  are used
to  determine how many of these site are actually  listed  in that particular cycle. The  sites not
proposed for listing,  are not rejected, but are held  over for the next cycle.  This could go on
indefinitely putting a particular site into  "limbo".  Since the site is beyond the State's capability, and
EPA HQ is  not listing it, no action then occurs with respect to the site. Such inaction is more than
problematic and I cannot support  a  recommendation that allows it to happen. However, under the
rules established for my concurrence with the document,  I'm precluded  from presenting another
draft to reflect my non-concurrence.  Thus, I am faced with no other option than to disassociate with
the report for the inconsistent rules applied to the way the report was drafted.
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Attachment A-Page 56                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Alexandra Shultz
                        Director, Legislative and Regulatory Affairs
                        Earthworks
I have received the endorsement for these comments in their entirety from Dolores Herrera, Doris
Cellarius, Aimee Houghton and Grant Cope

I am choosing to dissent from the report of the full Subcommittee, for the reasons described below.
In  making this dissent,  however,  I wish to offer my support and thanks to the many people who
worked so hard on this panel to ensure that the Superfund program improves the lives of citizens in
affected communities, as well as the environment.  In particular, I would  like to recognize the efforts
of the tribal and environmental justice representatives, who made many personal sacrifices just to
participate in the often grueling discussions of this  NACEPT Subcommittee.  I also wish to formally
endorse the comments of Jason White, which include "Top 10 Issues To Protect Public Health and
The  Environment  at Superfund Sites", as well as the  appended  comments of Dolores Herrera,
Doris Cellarius, Aimee Houghton,  Vicky Peters, Ken Jock, and Grant Cope.

In  dissenting,  I would also like  to make it clear that there are aspects of the report that I do support,
and that would be very important to see implemented.  These include: improving collaboration with
Tribal nations  and potentially  affected communities (parts of recommendations 2 & 3),  building
capacity for State  and Tribal cleanup programs (recommendation 8), measuring the effectiveness
of Agency coordination with Tribe, state, local and community stakeholders (recommendation 12),
and the release of an EPA annual report that makes public information on program progress and
spending,   and  information on   sites  considered for  listing and  those  not listed  and why.
(recommendations 5 and part of 6).

Unfortunately, the  negatives in this report outweigh the positives - from the flawed process, to the
unacceptable language that was included, to the critically important recommendations that were left
out.  As such, I was unable to endorse the overall report.

Lack of Accountability on the Range of Views
First,  it is extraordinary that this  report has degraded into a so-called "range of views" document,
when those views  are not attributed to any specific Subcommittee members or stakeholders.  If this
were a consensus document,  it would be understood that every Subcommittee member would be
endorsing the recommendations as at least acceptable,  if perhaps not preferable. The final report,
in  contrast, contains views that would leave communities and the environment in harm's way, such
as  using  an  uncharacterized idea  of "present  risk"  as  the  motivating factor  in  listing and
prioritization decisions  by the EPA.  Since I could  not support such views, I  am  extremely
uncomfortable with putting my  name on a document that contains them.

Moreover, because EPA representatives indicated that they might use the disparate views to inform
the agency's course of actions, such unacceptable language could be turned into policy. I cannot
endorse that possibility.  Finally, the  lack of attribution on the views has left a document that lacks
either transparency or accountability while  criticizing the  EPA for  not  being  transparent  or
accountable enough on the underlying Superfund program.

Cost Should  Not Be a Factor in  Making  Listing Decisions
I am also extremely concerned over  the removal of the recommendation that the cost of cleaning
up a particular site NOT be used as a factor in the decision to list or not  list that site on the National
Priorities List.  The  decision to list a site on the NPL involves assessing  which sites most need
federal intervention because of their  severity and the inability of other programs to clean them up.
Cost is not relevant to considerations of the threats a site may pose to  human health and  the
environment, or to the speed with which a site can and should be addressed,  and as such  is not
relevant to listing decisions. Moreover, if the cost of a cleanup is a problem, it is incumbent on the
EPA  to state that  plainly, request that funding,  and  not  let  insufficient funding  jeopardize
communities or the environment.   Not listing a site because of insufficient  funding is abhorrent.  I
also wish to note that in many previous drafts of the report, Recommendation 1 included language
that cost not be used as  a factor in  listing decisions.  Yet,  in the final report,  this language was
removed, without an explanation or any transparency about who objected or why.
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"Risk," "Segmenting Large Sites" and Inaccurate Funding Discussions are Unacceptable
Among  the  other issues that  have prompted  my  inability to endorse the final report  are  the
unattributed, industry-backed language on using present risk in listing and prioritization decisions,
the discussion of the EPA's segmenting large sites; and the flawed description over what prompted
the breakdown  in consensus on the proposed  recommendation to request  more funding for the
sites that need it the most.

Omission of Recommendations:
Short-term Funding to Protect the Communities Most at Risk
Equally objectionable is what the report omits -  including some of the recommendations that could
have gone the farthest towards ensuring a healthy Superfund  program that does an adequate job
of protecting human  health,  communities  and  the  environment.   Chief among these is a
recommendation that more money goes to contaminated sites that are stalled or stopped because
of a  lack of funds.  It is critically  important that communities and the environment impacted by
heavily contaminated sites have the money they need to proceed with timely cleanup.  Anywhere
from $300 million to $800 million per year, as explained in three separate reports from the EPA
Inspector General, the General Accounting Office,  and  Resources for the  Future,  is needed to
make up the shortfall.  Without injecting more money into the process now,  communities will suffer.
Many of the  industry representatives on the panel were  only  willing to  agree  to  such a
recommendation if they could  control where the funding  were to  go -  instead of allowing  the
agency to use additional money to  protect the communities that need it the  most.  The report omits
the recommendation and inaccurately describes  the source of disagreement.

Reinstating the Polluter Pays  Fee to Provide a Stable, Long-term Source of Funding
A separate,  although related, issue that the report  ignores is how to ensure that the Superfund
program has  sufficient long-term funding.    Only  a stable source of funds to  supply  the
appropriations process will enable the program to plan to cleanup severely  contaminated sites in a
timely manner into the future.  Even finding efficiencies in the current Superfund program will at
best free  up 5  -10  percent  (if any) of the program's money, an amount insufficient to ensure
protections for communities and the environment.  The "fund" in "Superfund"  should be reinstated.
That will require reinstating the  polluter pays fee.  It is irresponsible to claim, as the EPA and the
report does,  that megasites are  burdening the program, but  not address how to get the funding that
will ensure that those sites will be cleaned up.

Resources for Communities
Third,  the  report omits  a  recommendation that  communities receive  funding  for Technical
Assistance Grants if their site would have been eligible for inclusion on the NPL and if the TAG
funding  had  not already been consumed by NPL sites. The concept that  new statutory language
would be needed for such a  recommendation  is inaccurate. Instead, the report does not deal with
this important issue.

Pollution Prevention and Corporate Responsibility
Finally,  but  not least importantly to communities  around the country that bear the brunt of the
consequences  of toxic pollution,  are the twin  issues of  pollution prevention and corporate
responsibility. I strongly object to the statement in the  report that pollution  prevention is not part of
the Subcommittee's charge.    The original charge asked the Subcommittee  to address issues
relating  to megasites and to the National Priorities  List. Given that, the single biggest step that the
EPA can take to protect the long-term vitality of  the Superfund program is to ensure that new sites
never get contaminated enough to be considered for  Superfund cleanup.   Barring that, the EPA
should at least attempt to ensure that sufficiently solid industry-provided financial assurances  are
available in order to prevent  any taxpayer-funded from being burdened by cleanup  liabilities. It is
highly disappointing that the report does not include the suggested recommendation on prevention,
especially given how much stronger that recommendation could  have been.  Moreover, the  report
confuses the two issues of pollution prevention vs. corporate responsibility.

Pollution prevention should be the gold standard to which all environmental agencies  and private
companies are held. Once contamination has occurred, it is impossible to put the genie back in the
bottle, and people and wildlife have already been exposed or put at risk of  being exposed to  highly
dangerous contaminants. The  EPA should strive to protect healthy  people  and  environments by
preventing sites from becoming toxic waste sites to  begin with.  There are a number of steps the
EPA can and should take to achieve this goal.
Attachment A-Page 58                  NACEPT         Subcommittee Final       |      12,

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    1.   The  EPA should, for example, strongly enforce existing environmental laws such as the
        Clean Water Act and the Resource Conservation and Recovery Act.
    2.   The  EPA should also take as strong a stance as possible in comments to Environmental
        Impact Statements shepherded by other agencies, using all the knowledge the EPA can
        glean from all its programs.  For example,  in an EIS for a mine site, the EPA could use
        knowledge learned from cleaning up a similar site to ensure that the preferred  alternative
        includes sufficient mitigation measures to prevent acid runoff, or to urge the no  alternative
        option. The EPA has taken steps to  implement this sort of action recently in the EIS for
        the Phoenix mine in Nevada, where the EPA argued for a long-term water treatment trust
        fund  of $33 million,  while the BLM only called for $400,000 - an amount that would not
        begin to address the perpetual pollution predicted for the mine.
    3.   The  EPA should also craft new regulations to stop pollution that is not already covered by
        existing authorities.  For example, while mining operations are exempt from the  hazardous
        waste provisions of RCRA, EPA retains authority to craft regulations to  govern certain
        types of mining wastes.  Yet, the EPA has failed to take action to regulate  hazardous
        mining waste - to the detriment of communities and the environment in the Western U.S.

Corporate responsibility  measures - through requirements for strong  industry-funded financial
assurances -  are another step the EPA can take to ensure that sites do not become burdens on the
Superfund  program.  More specifically, the EPA should exercise  its  authorities, such as those
under section 108(b) of  CERCLA  and through its ability to  comment on the EISs shepherded by
other agencies, to  require companies seeking to open new facilities to put  up a sufficient pot of
funding  in  advance  to  pay  for  any  required  cleanup.   Strictly speaking, financial  assurance
requirements  are  not pollution  prevention measures.   Such  cleanup  money only  becomes
necessary if a site becomes polluted and requires cleanup.  Financial assurance measures simply
ensure that an already contaminated site does not become the liability  of federal,  state or  local
taxpayers.  It is  extremely  important that such financial assurance measures require a secure
source of funding, such as a bond or  letter of credit just to name two.  If a company is  allowed to
simply  promise to  pay out of its own existing resources  -  a so-called "corporate guarantee,"
taxpayers  will be  left out in the cold if the  company later goes bankrupt or makes  its  assets
unavailable in some fashion.  Such "corporate guarantees" are no better than "lOUs."   To date,  a
mixture of corporate guarantees and insufficient bonds have left taxpayers on the hook for as much
as $12 billion  just for cleanup costs at currently operating mine sites, according to "Putting a Price
on Pollution" a 2003 report by Jim Kuipers and the Center for Science in Public Participation.
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Attachment A-Page 60                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Position Statement of:  Mel Skaggs
                        President, InDepth Environmental Associates
I  was honored  to  serve  on  the  Superfund Subcommittee, and I  appreciated the diligent work
performed by the other members  of the Subcommittee and the Chair.  The facilitators also worked
very hard to find consensus in the central issues and concepts that remained as the Subcommittee
finalized its report.  I  also appreciated the efforts of the EPA Superfund staff members, who were
tasked with providing  information on their Program.

Many of the participants provided carefully developed work products throughout the  process that
contributed greatly to  the group's  deliberations. Since many of these work products were prepared
by practitioners, they  often contained insightful information and  creative ideas.  Some of this work
did  not appear in the  final report.  The reader is encouraged to explore these valuable resources,
which are available through the Subcommittee's docket and public records.

These comments offer my individual perspectives on three topics discussed by the Subcommittee.

Expenditures  Must  Be Prioritized.  Information presented to the Subcommittee by EPA suggested
that a backlog exists of construction-ready orphan sites which lack current funding for construction.
Over 70% of site cleanups are paid for with private funds from PRPs,  but EPA's appropriation still
must fund orphan  sites cleanups and, sometimes, orphan shares of  other sites.  However, the
Superfund program today is also funding many additional constituencies and activities unrelated to
field cleanup to be funded out of its annual appropriation.

The Superfund  program  expenditure data provided to the Subcommittee were  not  consistent
throughout the  Subcommittee's process,  nor were these data consistent with  historical  figures
available from  GAO.   These issues were not fully resolved,  but  the fraction  of the  annual
appropriation  allocated to extramural construction  at NPL sites appears to have  been  declining
since approximately 1996. Only about 16.6% of the annual appropriation was spent for extramural
remedial actions during the time period looked at by the Subcommittee  (FY2002).

Using such tools as the deobligation of unspent funds from prior budgetary years, EPA's  current
management  has implemented admirable innovative management approaches during these recent
years.  Nonetheless,  the low percentage (16.6%  of current year appropriation)  being  spent on
extramural remedial actions left me with several lingering questions, including:

    •   What portions of the  Program  budget grew proportionately  as the extramural remedial
        action portion shrank, and what would reverse this eight-year downward trend?
    •   If only  16%  of current year appropriations are being spent for field construction at  NPL
        sites, how could additional  appropriations  ever resolve the orphan site  construction
        backlog that  EPA described to the Subcommittee?

I  never found  a satisfactory answer to either question, and I ultimately concluded that growth in the
non-construction ("programmatic") portions of the  Program must account for this trend.  If the
Program's expenditure priorities were proportionately restored  to those present  in 1996, at  least
$100 MM/year of additional  money would be available for cleanup  at these construction-ready
orphan sites.  Comparing the alternatives of expenditure reprioritization or simple appropriation
increases, I concluded that such  reprioritization would be a superior way to increase construction
funds available for use at these backlogged construction-ready orphan NPL sites.

Recommendations  for Numerous New Studies Will  Divert Resources From Clean Up.   This
understanding of the spending trends raises troubling questions in light of the contents of this
report. The report contains  numerous non-consensus suggestions of different ideas for EPA to
consider, and many of these suggestions individually sound very appealing.  To illustrate this point,
by my count,  this document  contains suggestions  that EPA develop 38 separate  new regulatory
processes/guidances,  conduct up to 47 new studies, conduct 6 formal multiparty "dialogues" on
various topics,  etc.  In  all,  if everything suggested  in this report were  implemented,  99  new
regulatory efforts would be initiated, each drawing  resources from the Program.   I was unable to
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ascertain what the cumulative costs might be to implement such activities, or whether there would
any budget left at all for remedial construction after doing so.

Some of the Subcommittee's suggestions and Recommendations could provide the benefit of more
efficient contracting mechanisms,  improved understanding  of where the Program expends  its
resources, etc., and I  particularly endorse these.  I also generally support the recommendations
which would help the Agency understand how to better prioritize its expenditures to address site-
specific  current   risks.     The   remainder   of  these   studies,   recommendations,   new
guidance/procedures/etc, that do not yield more resources for field construction  generally will not
be helpful and should, in my opinion, be avoided.

I  believe the Subcommittee might have been  more helpful  to the EPA had it instead found  99
current  ongoing Superfund  funded studies,  guidances being  developed,  and   processes  to
recommend be discontinued.  Unfortunately the Subcommittee did not see any information useful
to this task, so I can only voice  support for the  audit recommendation and hope that it will provide
the Agency the information necessary to achieve such a redirection of resources on its own.

Use  Of Other Programs to Cleanup Mega Sites.  I began my Subcommittee service expressing
support for "using all of the tools  in the tool box"  for cleaning up sites, and I saw much good
information to  support this approach.   Two decades of maturation of the remedial  regulatory
processes have given us effective new cleanup "tools" such as the Great  Lakes Legacy Act,
Brownfields Act, experienced state  cleanup programs, RCRA Corrective Actions, and the Water
Resources Development Act (WRDA).

Various practitioners provided the Subcommittee with very detailed information on the successes of
various different state and federal programs in cleaning up sites across the country.  However,  as
noted above, this information often  does not appear in this final report but it definitely  should  be
accessed in the Subcommittee's docket.

One  example of such a  new non-Superfund remediation "tool" is the Urban Rivers Restoration
Initiative (URRI) under WRDA.   In  Section III,  the  report suggests "EPA should explore options
such as  memoranda  of agreement or other  arrangements with  non-NPL  programs  to  further
coordination and ensure that EPA's statutory authority is not impaired." (111-48)  The report contains
a similar statement on 111-52 with regard to other USAGE waterway  programs.

The  EPA and  USAGE have already demonstrated how such an agreement can  be  effectively
utilized in the Urban Rivers Restoration Initiative. The  USAGE and EPA began pilot testing this
alternative approach for the restoration of degraded urban rivers over two years ago.  This program
is discussed in the  final report at page 111-47.   The  program is  currently being tested at eight
national pilot sites, under a Memorandum of Understanding (MOU)  between USAGE  and EPA.
The  July 2, 2002 MOU requires that all of EPA's CERCLA,  RCRA and CWA regulations be met
under  this cooperative  new  program.   Of  course,  USAGE has  already built  considerable
remediation expertise overseeing the design and implementation  of numerous upland Superfund
site remedies for EPA at sites all across the nation.

Alternative cleanup programs such as URRI permit  EPA to leverage both cash and human capital
resources - achieving more  site cleanups with fewer resources.   The urban  rivers restoration
program offers the participants  partial federal funding to address orphan shares in a class of sites
where many hazardous substances dischargers may be unknown or quasi-governmental.

The  USAGE   has   over  100  years  of  experience  in planning,  designing,  and  executing
comprehensive  solutions to complex water and  related  land resource  problems.  The agency's
expertise has  been  developed over that time  from  extensive  watershed  management  work,
including responsibilities for 25,000  miles of commercially navigable waterways,  numerous inland
lakes and reservoirs, and almost 300 deep draft harbors, many of which are located in urban areas.
USAGE statutory authorities overlap geographically and  functionally with  many  non-point source
watershed contamination, NPL-eligible sites, and other problem areas.

In a  precursor to the URRI program, WRDA served an important  role coordinating multi-authority
funding for the Ashtabula Harbor, Grand Calumet/Indiana Harbor and other cleanups. Further, the
Great Lakes WRDA program  alone has  already provided  over $580 million for  contaminated
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sediment response actions  at nineteen different Great Lakes Areas of Concern over the  past
thirteen years.

Much has been  learned about interagency, public-private partnership approaches such  as the
URRI, earlier WRDA-based  programs, and the early years of the URRI program itself.  However,
even more will be learned as the URRI pilots projects move through the partnering process. In my
opinion,  it is critically  important for our society to take advantage of these lessons as we address
mega sites.

Citations are provided below  to give additional detailed information  on this  specific alternative
cleanup  program.  The  reader is encouraged to review them or to discuss the program  with
practitioners such as Dr. Jonathan Deason of George Washington University.

The  development of cooperative  MOUs between  EPA and the  alternative  cleanup programs
obviously can be achieved by following the model of URRI.  Such utilization of "all the site cleanup
tools in the toolbox" is an essential part in freeing Superfund resources to respond more effectively
at the back-logged construction-ready NPL orphan sites where the Program  needs to refocus  it
resources in the coming years.

URRI References
    •   Deason, J.P., "Urban River Restoration  Initiative:  Key to Brownfields  Redevelopment
        Success in  Urban  River Corridors,"  Brownfields  2000 - Research  and Regionalism:
        Revitalizing the  American Community.  Washington, DC:  U.S. Environmental  Protection
        Agency, 2000.
    •   Deason, J.P., "Passaic River  Restoration Initiative: A New Model for Cleaning  Up Our
        Nation's Contaminated  Urban Rivers."  Proceedings of the  EPA Forum on  Managing
        Contaminated  Sediments  at  Hazardous   Waste  Sites.  Alexandria,  Virginia:  U.S.
        Environmental Protection Agency, May 30, 2001.
    •   Deason, J.P., "Cry Me a River: The  Passaic River Restoration Provides a  Nationwide
        Model for Addressing  Polluted Urban Rivers." Pollution Engineering, September 2001.
    •   Deason, J.P., "Natural Resource  Trustee  Partnering  in  the Urban  River Restoration
        Initiative," Federal Facilities Environmental Journal, Volume 14, Number 4 (Winter 2004),
        pp.  45-59.
    •   Fuglevand,  P.P.  and Deason, J.P., "Integration of WRDA  Restoration and CERCLA
        Remedial Processes  at Urban Waterway Superfund Sites."  Invited  presentation to the
        EPA Technical Support Project General Meeting, San Diego, California, May 10, 2001.
    •   Fuglevand, P.P.  and Deason, J.P., "Meeting the Challenge of Contaminated Urban Rivers
        Using an Integrated WRDA/CERCLA Approach." Invited paper presented at the American
        Society of Civil Engineers Conference "Dredging '02", Orlando, Florida, May 7, 2002.
    •   USEPA and  USAGE, Memorandum of Understanding  Between the U.S. Environmental
        Protection Agency and the U. S. Department of the Army, "Restoration  of Degraded Urban
        Rivers," July  2, 2002.
    •   USEPA and  USAGE,  "Urban Rivers Restoration  Initiative,"  July  2003 (announcing
        selection of the second group of four pilot sites).
    •   See also http://www.epa.gov/oswer/landrevitalization/urbanrivers
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Position Statement of:   Richard B. Stewart
                        Professor, Center on Environmental and Land Use Law
                        New York University - School of Law
The  Subcommittee's Report, which I  have joined,  is,  notwithstanding the best  efforts of most
participants, very much a lowest-common-denominator document.3 As a  result, it largely fails to
come to grips with the Subcommittee's charge of helping EPA to frame and resolve the tough
choices presented in setting Superfund program priorities in the context  of limited resources. In
retrospect, it would have been  more helpful to EPA for us not to have sought consensus, and
instead set forth differing views.  Some Subcommittee members believe that the current Superfund
program is basically sound  and the primary need  is more money.  By contrast, I  find that the
program is gravely flawed and  requires fundamental change to achieve its goal of preventing
significant threats to health and the environment.

The  current  Superfund  program suffers  from  pervasive defects  of  both  substance  and
management. As a substantive matter, the program wastes scarce resources and  undermines
health and environmental protection by failing  to target resources effectively on significant risks.
This  substantive failing is rooted  in EPA management failures. EPA has failed  to  develop the
comparative  risk information and  analysis  and the budgeting  and  program  tracking  systems
necessary to ensure that program resources are targeted on cost-effective means for preventing
important threats instead of being wasted on minor or hypothetical risks. r  The failures have been
compounded by lack of transparency in EPA decision-making regarding Superfund priority setting
and  cleanup  policies.  These several failures prevent  meaningful  progress and  disserve the
interests of the  public in effective protection as well  as  the  interests of the  taxpayers and
consumers of business products who ultimately finance the Superfund  program. These failures also
severely handicapped the Subcommittee's ability to carry out its charge, including "Clarify how the
money is used and what you get for it." (Report, p.A-l-4)

Over the past 25 years, EPA has failed to develop basic information,  based on site-specific data
and  realistic analysis,  on the comparative  risks  posed  at  different  sites and  portions  of sites.
Instead, it  has relied  to a considerable extent on default assumptions and  hypotheticals, often
unrealistic  and highly conservative, to screen  sites for NPL listing through the MRS and  make
remedial decisions. It has relied  on measures of construction activity rather than the environmental
"bottom line" - risk reduction - to define program performance. While  risk is not an objective "fact"
that can readily  be measured, the discipline of risk assessment  has progressed to  where  it can
usefully assess the comparative risks posed by  hazardous  substances at different locations and
guide regulatory and  remedial   priority-setting. Increasingly, other  EPA  program  offices have
successfully used risk analysis to set priorities and adopt regulatory standards. OSWER's failure to
follow suit  can not be justified by the notion that risks at hazardous waste sites are  so inherently
complex or difficult as to defy analysis..  The risks in question are not inherently more complex than,
for example, the risks of air pollution,  which  have been analyzed  by the EPA Air Office with
substantial success.
s Jim Derouin's statement explains some of the reasons for this unfortunate result.
T One independent study of Superfund remedial decisions found that nearly  80% of
measured costs  at a sample of sites were incurred for measures to address potential
future risks based on changes in land use as opposed to  current risks created by
current exposures and  land uses. See James T. Hamilton  and W. Kip  Viscusi, The
Magnitude  and  Policy Implications  of Health Risks from Hazardous Waste Sites,  in
Analyzing Superfund, Economic, Science, and Law  55 (Richard Revesz and Richard B.
Stewart, ed.  1995).  [hereinafter Analyzing Superfund].See  also Stephen G.  Breyer,
Breaking the Vicious Circle, Toward  Effective Risk Regulation (1993)  (documenting
unrealistic  and excessively conservative EPA risk assumptions). EPA.  On the other
hand, EPA remedial decisions also often ignore adverse health and environmental
impacts of the remedies chosen.  See, e.g., J. Paul Leigh and Alan Hoskin, Hazards for
Nearby Residents and Cleanup Workers of Waste Sites, 45 J. Envtl. Mgmt. 331 (May
1999)
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In addition to EPA's longstanding failure to develop appropriate measures of comparative site risks,
the Subcommittee's  inquiries disclosed that EPA has failed to  develop adequate accounting  and
program tracking systems for remedial expenditures that would  permit an evaluation of the relative
health and environmental protection benefits achieved by different remedial measures in relation to
expenditures.  Such systems are essential in  order to undertake  intelligent priority setting  and
ensure that consumer  and taxpayer monies are being spent in a cost-effective manner so as to
maximize  health  and  environmental  protection.   Program  accountability  has  been further
undermined  by OSWER's consistent  practice  of  adopting Superfund remedial and  spending
policies almost entirely through guidance and other informal means. It has avoided rulemaking,
which would assure greater decision-making transparency, discipline and  public  accountability
through the  notice and comment  and regulatory  impact analysis  processes. As  a  result,  the
performance of the Superfund program remains extraordinarily opaque and resistant to meaningful
outside review and evaluation, including by the Subcommittee.

Notwithstanding these  management deficiencies, independent academic studies have succeeded
in using comparative risk analysis to evaluate aspects of the Superfund  program. They have found
faulty priority-setting, which results in  serious waste of resources. For example,  studies disclose
that there is a very wide range in the effectiveness of program expenditures in reducing health  and
environmental risks at different sites.u  The information shows  that  if more of  existing Superfund
resources were shifted toward the more  serious  risks  and  spent on remedial  measures  that
provided  greater risk  reductions relative  to  their cost, the Superfund  program could deliver  a
significantly higher level of protection  to the public health and the environment than  it  currently
does.

Past failures do  not excuse  their continuation.  Steps must be taken  to  ensure better program
accountability and begin development  of the information that will enable program resources to be
targeted on those sites or portions of sites  and those remedial measures  that will achieve the
greatest reduction in health and environmental risks. The basic implications for the issues posed to
the Subcommittee are straightforward:

NPL Sites The  MRS  should  be  changed  and focused  on more realistic  measures of  the
comparative  risks posed by different sites, based on site-specific data including exposure data.
Only those sites posing the comparatively more significant risks  should be selected as NPL-caliber,
with a  strong headquarters role to ensure this result. Remediation  of these sites should aim at
addressing the  most important risks,  with priority  on protecting populations  against  current as
opposed to hypothetical future exposures and preventing the  spread of contaminants  that would
pose significant risks to health and the environment. In selecting and funding remedial measures,
priority should  be given to those that  are the  most cost-effective  - i.e.,  those that provide the
greatest reduction in risks relative to their cost. Further, systematic use should be made of other
cleanup programs to remediate NPL-caliber  sites, in order to conserve Superfund resources for
those important risks that can not by addressed by other means/

Meqasites. The need  for risk-based priority setting and use of the most  cost-effective  remedial
measures is especially acute in the case of megasites, which have an  average cost $140 million
as compared to than average cost of $12 million for a non-megasite.  Given the costs involved,
common sense dictates devoting greater resources at megasites to evaluating comparative risks,
u  See. sources cited note 1; Shreekant Gupta, George Van Houtven & Maureen L.
Cropper, Do Benefits and Costs Matter in Environmnetal Regulation? An Analysis of EPA
Decisions  Under Superfund, in Analyzing Superfund; Shreekant Gupta, George Van
Houtven, & Maureen Cropper, Paying for Performance: An Economic Analysis of EPA's
Cleanup Decisions at Superfund Sites, 27(3) RAND Journal of Economics 563 (Autumn
1996) reprinted in Valuing Environmental Benefits 375 (Maureen Cropper ed., 1999);
James T. Hamilton and W. Kip Viscusi, Calculating Risks? -The Spatial and Political
Dimensions of Hazardous Waste Policy (MIT Press 1999); Katherine D. Walker, March
Sadowitz and John D. Graham, Confronting Superfund Mythology:  The Case of Risk
Assessment and Management, in Analyzing Superfund.
v See Mel Skaggs' statement for further discussion of this  issue.
Attachment A-Page 66                 NACEPT Superfund            Final Report  |     12,

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targeting the most significant risks, evaluating alternative remedial strategies, and selecting those
that will achieve the greatest reductions in risk with the resources available.w

Measuring Program Progress. EPA should, similar to what it has  already done in a number of its
other programs, develop measures of the risk reduction benefits  achieved by Superfund and the
costs incurred  in achieving those benefits as the basic measures of program performance. The
measures of performance progress used by the RCRA program would be a beginning.

Program funding is an issue that was not part of our charge but was insistently pressed by many
Subcommittee  members. I am unwilling to support increased program funding at this time, for three
reasons:  (a) the systemic waste in the current Superfund  program,  due to lack of risk-based
priority-setting,; (b) EPA's practice of spending a disproportionate amount of program funds on
administrative staff relative to cleanup; (c) the circumstance, confirmed by EPA's Science Advisory
Board,  that the risks addressed by the  Superfund program are low relative to those addressed by
other EPA programs.

24 years after Congress established the Superfund program, we should know how well it is doing in
actually reducing risks to the  public and the environment.  We should also  know how much risk
reduction it is achieving in relation to the societal resources committed to clean up. EPA has failed
even to begin  to  ask, much  less answer these  bedrock  questions.  It is imperative  to make a
beginning now, and set the Superfund program on track to achieving its important objectives.
w
  See Tom Newlon's statement for further discussion of this issue.
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Position Statement of:   Jason White
                       Environmental Specialist, Office of Environmental Services
                       Cherokee Nation
                               Top 10 Issues to Protect

Public Health & The Environment at Superfund Sites


This document describes pro-active positions of the representatives listed below on key issues on
which the report by EPA's National Advisory Committee on Environmental Policy and Technology's
Superfund Subcommittee report contains a "range of  views."  These members agreed upon the
following  positions that  maintain  or  increase  Superfund's ability to  protect  public  health  and
environmental quality.

I. A Weakened Superfund Cleanup Program

In recent years, the Superfund program has suffered severe funding shortfalls, dramatic declines in
the  pace of cleanups,  and an  inability  to conduct cleanups at  some  of the nation's most
contaminated toxic waste sites. Program funding has declined from $1.7 to $1.3 billion—over 30%
using  inflation adjusted dollars—between  1993 and 2003.  Since  1995, with the expiration  of
Superfund's dedicated funding mechanism, taxpayers have increasingly paid  for the cleanup  of
abandoned Superfund  sites and the running of  the Superfund program.  Now, in 2004, taxpayers,
rather than industries,  will pay 100%  of such costs. The number of annual cleanup completions
has fallen over 50% since the last half the 1990s.  The following list built upon consensus contains
ten concrete steps to address these problems.

II.  Pro-active Initiatives to Protect Public Health and Environmental Quality

1)     Increase Funding and Reauthorize Superfund's Fees: The Administration and Congress
      should agree to  increase funding for the Superfund program by$300-$800 million annuallyx,
      and should support and sign into law a reauthorization of Superfund's polluter pays fees;

2)     List Sites for Clean  Up: EPA headquarters should not consider the potential costs of a
      cleanup or budgetary shortfalls in making  listing decisions.  However,  EPA headquarters
      should generally defer to regional proposals to list toxic waste sites on Superfund's national
      priorities list;
x Three reports provide the factual foundation for this range.  First, Resources For The
Future reported that the Superfund Program would likely need level or increased
funding throughout this decade to adequately fund cleanups. Katherine Probst, et al.,
Superfund's Future; What Will It Cost? (1999).   However,  actual appropriation have
been $300 to $800 million below RFF's inflation adjusted base  and high estimates.
Second,   EPA's  2004  Inspector  General  report  released  agency  documents
demonstrating that the resource needs for activities included in the FY 2002 Remedial
Action Advise of Allowance (i.e. remedial actions;  long-term response actions; five-
year reviews; enforcement  fairness projects;  above-the-base removal actions; and
redevelopment/reuse projects) is nearly three  times the  budgeted amount of $224
million.  (EPA Inspector General, Congressional Request on Funding Needs for Non-
Federal Superfund Sites, Rpt. 2004-P-00001 (Jan. 7, 2004); EPA, Memorandum from
Elaine F. Davies to Superfund National Program  Managers, OSWER 9275.1-04 (Jan. 3,
2002). Third, the General Accounting Office also recently  reported that over the last
ten years the Superfund Program has suffered  a decline  in funding of $672 million
adjusted for inflation.
NACEPT Superfund Subcommittee Final Report \     12, 2004                 Attachment A-Page 69

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3)    Better Integrate Stakeholders: EPA should increase its outreach to affected and impacted
      communities, tribes, states, and  EJ groups during  the  listing process, including providing
      funds for TAGs at non-NPL sites where such funds  do not reduce the availability of funding
      at NPL sites;

4)    Promote Protective Listing Decisions:  The MRS and listing process should capture the
      core value  of tribal concerns and EJ principles, and non-traditional threats such as vapor
      intrusion and explosives;

5)    Strengthen Long-Term Protections:  Bolster the long-term management of toxic waste
      sites by reducing the  reliance  on Institutional Controls  (ICs), including  land use  controls,
      strengthening enforceability and tracking mechanisms,  and expanding resources  for long-
      term stewardship;

6)    Improve Institutional Coordination:   Increase  ATSDR and  NIEHS'  responsiveness,
      accountability,  and funding to address concerns of impacted communities and states, create
      guidance on declaring a  "public  health emergency" that details when citizens can obtain
      health services, and craft community report cards;

7)    Prevent Future Sites: Strengthen  pollution prevention efforts  by creating section  108(b)
      financial assurance  regulations and expanding  prevention activities  at  facilities at  risk  of
      creating NPL sites;

8)    Increase Funding To Other Programs:  The federal government should increase funding
      to state and tribal programs to help  them maintain  and  increase their capacity to  clean up
      toxic waste sites;

9)    Use Effective  Measures of Success:  EPA  should  use  clear, verifiable,  performance
      measures that are based on readily available data and that reflect progress  in the actual
      cleanup of sites not elaborate calculations of exposure control or risk reduction;  and

10)   Quickly Address Threats:  EPA  should  use  Superfund's existing legal  authorities  to
      prevent and clean up contamination threatening public health and the environment,  including
      at Federal facilities.
Signed,

Aimee Houghton
Center for Public Environmental Oversight

Alexandra Shultz
Legislative and Regulatory Affairs
Earthworks (formerly known as Mineral Policy Center)

Dolores Herrera
Environmental Justice

Doris Cellarius
Sierra Club

Ed Putnam
State of New Jersey

Grant Cope
Environmental Attorney

Jason White
Office of Environmental Services
Cherokee Nation
Attachment A-Page 70                  NACEPT          Subcommittee Final        |     12,

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Ken Jock
Environmental Division
St. Regis Mohawk Tribe

Mildred McClain
Harambee House, Inc./Citizens For Environmental Justice

Victoria Peters
State of Colorado
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Attachment A-Page 72                  NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Appendix I:
Revised Charge to the Subcommittee
NACEPT Superfund    Final     12,2004          Appendix I

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Appendix I                             NACEPT Superfund Subcommittee Final Report |  April 12, 2004

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Superfund Subcommittee
National Advisory Council for Environmental Policy and Technology

Charge

REVISED 6-19-02 Following Subcommittee Discussion on 6-18-02


BACKGROUND:

In  July 2001, the  Deputy Administrator directed the  development  of an action plan to
address the recommendations in the Resources for the Future (RFF) report to Congress,
Superfund's Future, What Will It Cost?  Specifically, the plan called for the creation of a
Superfund Subcommittee under the auspices of the Agency's National Advisory Council
for Environmental Policy and Technology (NACEPT).

In  the fall of 2001, the Agency enlarged the  Superfund Subcommittee's scope to reflect
consideration of the Superfund program in context with other federal and state waste
cleanup programs.  This broader focus will consider  how the Nation's waste programs
can work together in a more effective and unified fashion, so that citizens can be assured
that federal, state, tribal and local governments are working optimally to make sites safe
for their intended uses.


STATEMENT OF TASK:

The  overall intent of this effort  is to assist in  identifying the future direction  of the
Superfund program in the  context of other federal  and state waste and site cleanup
programs.   Specifically,   the  Superfund  Subcommittee  will  review  the relevant
documentation  and, to the  extent possible,  provide  answers to the questions that are
attached and that relate to:  a) the  role of the NPL, b) mega sites, and c) measuring
program performance.

During the period of Subcommittee  activity, additional  issues may arise for which the
Agency will seek Subcommittee input.  If this occurs,  EPA will identify specific issues or
questions for which advice is sought and provide appropriate documentation.


LEVEL OF EFFORT:

    1.  The Agency shall furnish the necessary personnel, material, reports, background
       documents and facilities needed for the Subcommittee activities.

    2.   It is expected that the Subcommittee activities  will be accomplished by a series of
        meetings over about an 18 month period.
NACEPT Superfund Subcommittee Final Report |  April 12, 2004                   Appendix l-Page 1

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    3.  It is anticipated that one or a series of consensus reports will result.  However,
       where consensus  cannot be  reached,  a written discussion  of the different
       opinions of Subcommittee members is to be provided.

    4.  The scope of the Subcommittee, as identified in the Statement of Task, will not
       change without agreement of both the Subcommittee and the Agency.

    5.  For additional  issues for which  the Agency will seek Subcommittee input, it  is
       understood  that these  issues would  not replace the  main  focus of the
       Subcommittee as  identified in  the Statement of Task.  For  these  additional
       issues,  the Subcommittee response may be in the form of a "consultation," i.e.,
       dialogue, rather than a formal written report.

    6.  The Subcommittee may, at its discretion, make use  of separate working groups
       to address specific issues.  The Agency will support the  activities  of these
       working groups in  the same manner as will be provided for the  Subcommittee
       itself.

    7.  The Subcommittee will operate  as and be subject to the requirements of a FACA
       Committee.
ROLE OF THE NPL:

The process to  place sites on the NPL has become increasingly contentious since the
Superfund program's inception.  Some stakeholders support the notion that the NPL is
most  appropriately a  "tool  of  last  resort."  Others  believe  the  current  process
inappropriately emphasizes keeping sites off the list.  Perceptions aside, sites placed on
the NPL  are typically those with either recalcitrant or no potentially responsible parties
(PRPs), those where States lack funds to perform cleanup, those considered Federal
facilities,  or where tribal, trustee, or affected community  pressure is applied.  Other
cleanup  avenues  include the  Resource  Conservation  and  Recovery  Act  (RCRA)
program, the relatively new Brownfields program, Federal  agency response programs,
Leaking  Underground Storage  Tank  Program, State deferral  or voluntary  cleanup
programs,  and  EPA's  use  of so-called  "NPL-equivalent" cleanups and large-scale
removals.

Among the issues that will be addressed are the following:

    1.  What should the  role of the  NPL be in addressing waste cleanup and what does
       it mean to be placed on the NPL?
           a.  What should be the  relationship between the NPL and other cleanup
              programs?
           b.  How to best ensure  an adequate level of cleanup?
           c.  How to integrate the NPL with other programs/statutes (NRD, CWA,
              Brownfields, etc.)?
Appendix l-Page 2                   NACEPT Superfund Subcommittee Final Report | April 12, 2004

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           d.   Should the NPL be a "tool of last resort?" In particular, what is the
               appropriate role of non-NPL cleanups and States in addressing sites?
           e.   What are the impacts/implications of placement on the NPL (funding,
               community, etc.)?
           f.   How can EJ concerns be more effectively integrated into the
               implementation of the NPL (e.g. synergistic and cumulative impacts)?
           g.   What is the appropriate use of the NPL in the context of mega sites (e.g.
               river basins)?
           h.   What are the issues associated with the goals of remediation and
               economic redevelopment?

    2.  Who should be involved in  determining what sites are listed (e.g., states, tribes,
       and communities)?
           a.   What should  the nature of their involvement be?
           b.   Should their role differ depending on the site type or risk?
           c.   What is the role of local authorities?
           d.   What is the role of communities (in  listing, risk assessment methodology,
               etc.)?
           e.   How can the  role of ATSDR (or equivalent) be integrated at non-NPL
               sites?

    3.  What kinds of sites belong  on the NPL?
           a.   Should the NPL be used for a more limited range of sites?
           b.   How can Tribal sites be addressed  more  effectively through the NPL?
               (How can cultural and subsistence-living factors be integrated more
               effectively?)
           c.   What is the role of Risk (ecological, human health) in determining which
               sites should be on  the NPL?
           d.   What are the technical criteria for listing a site?
           e.   What should  the interaction be between the removal and the  remedial
               programs?
           f.   What are the broader issues of NPL listing (stigma, etc.)?

Information Needs

  1.    Assess the relative costs of using other cleanup programs as alternatives to the
       NPL.
  2.    Determine whether EPA has used the citizen petition process to add sites to the
       NPL.  If so, how?
  3.    Identify    the    other    remedial/cleanup     alternatives    and    their
       obligations/requirements (RCRA ToSCA, state standards,  etc.).
  4.    Identify other funding sources (non-EPA public sources, private funding).
  5.    Assess the issues behind "recalcitrant parties".
  6.    Understand EPA guidance on the listing process.
  7.    Assess the characteristics  of other cleanup  programs that  have made them more
       or less successful than the NPL. What kind of sites were involved (cost
       complexity  etc.)?
NACEPT                        Report       12,                       Appendix 1-Page 3

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  8.    Gain a better understanding of the MRS and the application of the "magic
       number."
  9.    Assess community acceptance of NPL listing vs. voluntary cleanups.
  10.   Determine what types of sites are typically listed on the NPL. (Is it true that "sites
       placed on the NPL are typically those with either recalcitrant or no potentially
       responsible parties (PRPs), those where States lack funds to perform cleanup,
       those considered Federal facilities, or where tribal, trustee, or affected
       community pressure is applied?)
  11.   Assess the use of 106 Orders (and funding to implement).
MEGA SITES:

The RFF Superfund cost study defined mega sites to be those NPL sites where cleanup
costs  (i.e., total removal and remedial  action costs) exceed $50 million.  Mining  and
contaminated sediment sites are often  considered synonymous with mega sites, although
the majority of mining and sediment  sites are  not  mega  sites, and  vice versa.  RFF
indicated that cleanup costs for mega  sites are among the  major variables driving future
program costs.  Mega site  cleanups,  especially those tied to mining  and contaminated
sediments, are also often difficult and time consuming.

Among the issues that will be addressed are the following:

    1.   Should costs be the determining factor when  designating sites as mega sites or
        should other factors such as complexity or geographic size be considered?

    2.   What are the reasonable policy options for addressing mega sites?
           a.   Are there viable alternatives to placing mega sites on the NPL and/or
               ways of containing their costs (for example,  listing only the highest
               priority portions of the sites)?

    3.   What are the unique aspects of mega sites that might require a different decision
        making process for NPL listing?
           a.   Large geographical distribution (e.g. river basins)
           b.   Slow rate of progress
           c.   Risk management challenges
           d.   Factors specifically relevant to Federal Facilities

    4.   How to integrate long-term stewardship in the cleanup/management of mega
        sites?

Information Needs

    1.   Confirm the  characteristics that drive  the  costs  of mega  sites (quantity of
        material, etc.).
    2.   Confirm the list of all sites defined as "mega sites."
Appendix l-Page 4                    NACEPT Superfund Subcommittee Final Report | April 12, 2004

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    3.  Bring in outside  experts to  help frame the discussion around issues where the
       committee may be missing expertise.
    4.  Clarify the federal budgeting process and how mega sites are funded.
    5.  Summary of RFF study.
    6.  Clarify EPA's  position on  liability/cleanup responsibility for  state/private/other
       ownership.
    7.  Determine the impact of PRPs protecting their assets.
MEASURING PROGRAM PROGRESS:

For  approximately  the  last  seven years  of the Superfund  program,  construction
completion has been  the  program's key measure of progress for sites on the NPL.
However,  this  milestone only reflects the final outcome  of years of analysis,  cleanup
work, and effort  at  NPL sites.   Construction  completion  neither measures  nor
characterizes the impacts of cleanup  efforts  on human health and the environment.
Furthermore,  construction completions do  not  correlate  as milestones for  non-NPL
cleanups or with efforts at other hazardous waste cleanups.  In  the past few years, the
Resource  Conservation  and  Recovery Act (RCRA) program developed indicators to
gauge the impact of its efforts on human health and the environment.  The Superfund
program  has capitalized  on RCRA's efforts and conceptualized  similar  indicators for
Superfund work.   Nonetheless, there  still are few cross-program  metrics to capture
comprehensive outcomes for interim work.  This void impedes the Agency's  ability to
communicate work at  hazardous waste sites to the public, Congress, States,  and the
regulated  community.  The Agency expects  to share new measure proposals with the
panel and will seek feedback from the Subcommittee on those proposed measures.

Among the issues that will be addressed are the following:

    1.  What criteria should be used to  measure progress?
           a.   Should environmental   indicators be  established  that are consistent
               among environmental programs?
           b.   Review the definition of construction  completion and the relationship
               between that and "really being done."
           c.   Determine the role of public/community values in  determining  progress
               (e.g. cultural, social, subsistence lifestyles).
           d.   How to address and respond to remedy failures?

    2.  Who should be involved in measuring progress and defining success?
           a.   What is the role of communities and other parties?

    3.  What  is  the  long-term  effectiveness  of institutional  controls (particularly
       enforcement),  containment and  natural attenuation?

    4.  How to integrate long-term stewardship into the goals of the Program?
           a.   How to assure responsibility?
           b.   How to fund for long-term stewardship?
NACEPT                        Report      12,                       Appendix 1-Page 5

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Information Needs

    1.  Clarify how the money is used and what you get for it.
    2.  Determine how communities feel about the program.  Is there consensus about
       what communities identify as success and progress?
    3.  Assess the impacts/implications of economic redevelopment vs. remediation.
    4.  What are the timing assumptions for construction completion (speed of cleanup)?
    5.  What  are  the institutional  controls  available  for  monitoring  and  long-term
       stewardship?
    6.  What environmental indicators do other cleanup programs use?
    7.  What factors influence whether a resource is useable (cultural  factors, factors
       influencing subsistence lifestyles etc.)?
    8.  Determine the steps for communities to assess their own measures of success.
    9.  Determine how to measure long-term treatment scenarios for those sites that do
       not reach construction completion.
    10. Identify Congressional perspectives on success.
Appendix l-Page 6                   NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Appendix II:
Original Charge to the Subcommittee
NACEPT Superfund    Final     12,2004          Appendix II

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Appendix II                            NACEPT Superfund Subcommittee Final Report  | April 12, 2004

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Superfund Subcommittee
National Advisory Council for Environmental Policy and Technology

Draft Charge
BACKGROUND:

In July 2001, the Deputy Administrator directed the development of an action plan to address
the recommendations in the Resources forthe Future (RFF) reportto Congress, Superfund's
Future, What Will It Cost? Specifically, the plan called  for the creation of a Superfund
Subcommittee under  the  auspices  of  the  Agency's  National  Advisory Council  for
Environmental Policy and Technology (NACEPT).

In  the fall of 2001, the Agency enlarged the Superfund Subcommittee's scope  to reflect
consideration of the Superfund program in context with other federal and state waste cleanup
programs. This broader focus will consider how the Nation's waste programs  can work
together in a more effective and unified fashion, so that citizens can be assured that federal,
state, tribal and local governments are working optimally to make sites safe fortheir intended
uses.
STATEMENT OF TASK:

The overall intent of this effort is to assist in identifying the future direction of the Superfund
program in the context of other federal and  state waste and site  cleanup programs.
Specifically, the Superfund Subcommittee will review the relevant documentation and, to the
extent possible, provide answers to the questions that are attached and that relate to:  a) the
role of the  NPL, b) mega sites, and c) measuring program performance.

During the  period of Subcommittee activity, additional issues may arise for which the Agency
will seek Subcommittee input. If this occurs, EPA will identify specific issues or questions for
which advice is sought and provide appropriate documentation.
LEVEL OF EFFORT:

    1.  The Agency shall furnish the necessary personnel, material, reports, background
       documents and facilities needed forthe Subcommittee activities.

    2.  It is expected that the Subcommittee activities will be accomplished by a series of
       meetings over about an 18 month period.

    3.  It is anticipated that one or a series of consensus reports will result. However, where
       consensus cannot be reached, a  written discussion of the different opinions of
       Subcommittee members is to be provided.
NACEPT Superfund           Final       |     12,2004                  Appendix 11-Page 1

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    4.  The scope of the Subcommittee, as identified in the Statement of Task, will not
       change without agreement of both the Subcommittee and the Agency.

    5.  For additional issues  for which the Agency will seek Subcommittee input, it is
       understood that these issues would not replace the main focus of the Subcommittee
       as  identified in  the  Statement of Task.   For these  additional  issues,  the
       Subcommittee response may be in the form of a "consultation," i.e., dialogue, rather
       than a formal written report.

    6.  The Subcommittee may, at its discretion, make use of separate working groups to
       address specific issues.  The Agency will support the activities of these working
       groups in the same manner as will be provided for the Subcommittee itself.

    7.  The Subcommittee will operate as and be subject to the requirements of a FACA
       Committee.
Role of the NPL:

The process to place sites on the NPL has become increasingly contentious since the
Superfund program's inception. Some stakeholders support the notion that the NPL is most
appropriately  a "tool of last resort."  Others believe the current process inappropriately
emphasizes keeping sites off the list.  Perceptions aside, sites placed on the NPL are
typically those with either recalcitrant or no potentially responsible parties  (PRPs), those
where States  lack funds to perform cleanup, those considered Federal facilities, or where
tribal, trustee, or affected community pressure is applied. Other cleanup avenues include the
Resource Conservation and Recovery Act (RCRA) program, the relatively new Brownfields
program, Federal agency response programs, Leaking Underground Storage Tank Program,
State deferral or voluntary cleanup programs, and EPA's use of so-called "NPL-equivalent"
cleanups and  large-scale removals.

    1.  What should be the role of the NPL in addressing waste cleanup given other cleanup
       options? Should it be a "tool of last resort?" In particular, what is the appropriate role
       of non-NPL cleanups and States in addressing sites?
    2.  What parties (e.g., states, tribes, and communities) should have formal consultation
       roles in NPL listing? Should this role differ by site type or risk?
    3.  What kinds of sites belong on the NPL? Should the NPL be used for a more limited
       range of sites (for example, only sites where human health is at risk, not ecological
       risk)? If so, how might other major risks be addressed?
Appendix Il-Page 2                   NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Mega Sites:

The RFF Superfund cost study defined mega sites to be those NPL sites where cleanup
costs  (i.e., total  removal and  remedial action  costs) exceed $50 million.  Mining  and
contaminated sediment sites are often considered synonymous with mega sites, although the
majority of mining and sediment sites are not mega sites, and vice versa. RFF indicated that
cleanup costs for mega sites are among the major variables driving future program costs.
Mega site cleanups, especially those tied to mining and contaminated sediments, are  also
often difficult and time consuming.

    1.   Should cost be the determinant when designating sites to be mega or should other
        factors such as complexity or geographic size be considered?
    2.   Are there viable alternatives to placing mega sites on the  NPL and/or ways of
        containing their costs (for example, listing only the highest priority portions of the
        sites)?
    3.   What are the feasible and reasonable policy options for addressing mega sites?
    4.   Should mega sites have a unique decision process for NPL listing?  If so, what
        supplemental processes are suggested?
Measuring Program Progress:

For approximately the last seven years of the Superfund program, construction completion
has been the program's key measure  of progress for sites on the  NPL.  However, this
milestone only reflects the final outcome of years of analysis, cleanup work, and effort at NPL
sites.  Construction completion neither measures nor characterizes the impacts of cleanup
efforts on human health and the environment. Furthermore, construction completions do not
correlate as milestones for  non-NPL cleanups or with efforts at other hazardous waste
cleanups.  In the past few years, the Resource Conversation and Recovery Act (RCRA)
program developed indicators to gauge the impact of its efforts on human health and the
environment. The Superfund program has capitalized on RCRA's efforts and conceptualized
similar indicators for Superfund work. Nonetheless, there still are few cross-program metrics
to capture comprehensive outcomes for interim work. This void impedes the Agency's ability
to communicate work at hazardous waste sites to the public,  Congress, States, and the
regulated community.

For this  particular issue, EPA is not posing specific questions to the Subcommittee.  Rather,
the Agency expects to share new measure proposals with the panel and will seek feedback
from the Subcommittee on those proposed measures.
NACEPT Superfund Subcommittee Final Report  | April 12, 2004                  Appendix 11-Page 3

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Appendix 11-Page 4                     NACEPT Superfund Subcommittee Final Report |  April 12, 2004

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Appendix III:
Memo from Elliott P. Laws Concerning Remedial Action
Priority Setting
NACEPT Superfund Subcommittee  Report   12,2004
Appendix III

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Appendix III                            NACEPT Superfund Subcommittee Final Report | April 12, 2004

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JfiN-21-2003  13:20       ROSS & flSSOC.                       206 447 0956  P.03/12
         \      UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
         I                 WASHINGTON. D.C. 20460
                              JAN  19 1996
                                                              OFFICE OF
                                                        SOLID WASTE AND EMERGENCY
                                                              RESPONSE
     MEMORANDUM

     SUBJECT:  Remedial Action  Priority Setting

     FROM:     Elliott P. Law
               Assistant
     TO:       Regional Administrators
               Regions I-X


         Thank you for your  participation in our conference call  on
     January 16, 1996 regarding the impact of potential budget cuts on
     the Superfund program.   I  asked my staff to prepare the three
     enclosed attachments in response to our discussions, and request
     that you provide any comments  on them to Steve Luftig, Director
     of OERR by February 2,  1996.

         The first attachment is a  summary of Congressional action  on
     our FY 1996 Superfund appropriation.  Under any scenario proposed
     so far, the Superfund program  will face severe reductions from
     the 1995 Operating and  1996 President's Budget resource levels.
     OSWER is currently using the following principles for our FY 1996
     resource planning:

             o Emergency removals will be funded at 1995 levels to  the
               extent possible,

             o Core Cooperative Agreements and the Brownfields
               initiative should be maintained at the 1995 level

             o A very -limited number of front-end pipeline activities
               will be funded.

             o Fund-lead remedial actions will absorb a significant
               cut.
                                      inns or 100% RocyOW Paper (as*.
 JPM-10-2003 136:33             703 603 9100                  97*          P.05

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JfiN-21-2003  13:20       ROSS & flSSOC                       206 447 0956  P.04/12
                                   -2-

        The second attachment is a summary of what I believe  to be a
    sound policy course with regard to managing the Superfund program
    in light of weighing our discussions with Agency commitments and
    existing policy.  In this context, we need to be aware  of the
    continued Agency commitment to national risk-based priority
    setting and the success we are demonstrating by completing
    construction at NPL sites.

        The third attachment is a detailed summary of practices we
    will employ for priority setting on a national basis with regard
    to funding new Superfund cleanup projects while keeping in mind
    our discussions regarding the need to support ongoing projects.
    I trust we will continue to work together through these
    challenging circumstances.  Please call on me if you have any
    questions, -and continue to call on Steve Luftig for support in
    addressing Superfund issues as they arise.

    Attachment
JRN-10-2803  06:33             703 603 9103                   97x.          P.06

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JflN-21-2003  13=20       ROSS & fiSSOC.                       206 447 0956  P.05/12
                               Attachment 1

                      FY  1996 Superfund Budget Sunsnary
     The accompanying chart depicts1 Congressional action  to-date on
     the Agency's FY 1996 Superfund Appropriation.   The chart  shows
     five major budget functions for the Superfund program:  Response,
     Enforcement, Research and Development, Management and Support,
     and Other Federal Agencies.  It is important to remember  that the
     resources shown for the five budget functions are the result of
     Congressional report language, not Bill  language.  Therefore,
     while the Agency may at some point receive  a total Superfund
     appropriation, any additional details  shown in  Congressional
     report language accompanying our  appropriation  may be changed,
     subject co Congressional approval.

     The chart is intended for informational  purposes only.  The
     function subtotals are subject to change resulting  from
     Congressional or Agency decisions.
     Note:   FY 1995 column equals enacted Operating Plan  less  $1CO
     million rescission.
 IfiM-10-2003  06=33             703 603 91B0                  97X          P.07

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 13
 I
 C-l
u
'JD
-J
    1/19/96

 Superfund
 FY 1 996 Superfund Congressional Action
 (Dollars in Millions)
Category
Response
   Response Action
   Response Support - OAR
Enforcement
Research and Development
Management and Support
   Management and Support
   Inspector General Transfer
Other Federal Agencies
   ATSDR
   NJEHS
   OOJ
   USCG
   NOAA
   FEMA
   DO I
   OSHA

Gulf Coast  Haz Sub Res Ctr
General Reduction
             Appropriation Total
FY
Enacttd
Op Plan
4805.11
isoi.es
13,42
$169.71
*ei.2s
* 126.62
1111.22
515.40
$168.50
$ea,8G
$58.70
S32.20
14. SO
12.20
IQJQ
io.eo
SO, 30
11,331.20
FY
President's
RiQUist
fssi.is
IS32.i3
13.42
I1S2U74
IS1.22
• 150.23
1136.16
114,01
• 165.79
168.00
I54.S3
533.94
H.SO
12,21
11.20
10.76
1036
• 1.562.94.
FY
Mouse
i»vaf
te«.»i

13,08
•77.74
• 13.22
• 115.73
$110.73
18,00
$t47.10

M9.SO
127.16
I4.3S
12.00
11.10
w.ea
10.32


ft, 003.40























rr
Senate
L»w9l
'
1827.87
13.42
1127.74
$18.22
I97,ii
I86.t'5
1 1 1 .70
1125.79
414,00
I34.S3
127.84
$4,80
12,21
11.20
*0.76
I0.3S
42.SO

11,003.40























FY
Nov0mit§r
Confe/meo


S3.08
i 127.0Q
10,00
1122.00
$ 1 1 1 .00
111,00
1 140.96
liS.OO
$48, §0
$25.00
I4,3i
42,00
11.10
10.68
10,32
$0,00
1130,001
I1.1S3.40
<-H


 I

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 I
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                                                                                                                                             cs
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                                                                    TF96CUT2.XLS
                                                                                                                                             \
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JRN-21-2003  13:21        ROSS & flSSOC.                       206 447 0956   P.07/12




                               ATTACHMENT 2

                  DRAFT PRIORITY  SETTING POLICY SUMMARY



    Criteria  for  Defining  Existing Cleanup Work.:

         o   in  general existing work should  be  given priority over
              new work.

         o   Completion of construction activities  at NPL sites
              continues to be a high priority  for the Agency.

    Existing  or ongoing cleanup work at a  site,  in contrast to new
    work at that  same site, is not of a separable and discrete
    nature.   Work considered as existing or  ongoing  is exempt from
    national  ranking by thei National Risk-Based  Priority Panel, and
    in  general  exhibits one of the following characteristics:

         •   The work consists of existing  continuous operations
              conducted under a single construction  contract
              mechanism.

         •   The work supports a Long Term  Response Action (LTRA)
              for example, a ground-water  pump and treat remedy.

         •   Discontinuing the work would result in imminent
              endangerment of human health or  the environment.

         •   The cost of  the work element is  relatively low,  for
              example, less than  $100,000  and  is integral to the
              overall cleanup of  the site.

    In  addition,  Regions have identified several EPA/PRP mixed
    funding  and mixed work projects which may  require funding  in
    FY  96-  These projects will be considered  separately for funding.


    criteria for  Defining New Cleanup work:

         o   New,  Fund-financed  cleanup work is subject to priority
              ranking by the National Risk-Based Priority Panel, with
              the exception of "emergency" and "time critical"
              response actions.

         o   All new  cleanup work is  funded  in sequence of national
               ranking, unless the Assistant Administrator of OSWER
              grants an exception.

          o    Determinations on whether a project represents new or
               existing work will be made by the National Risk-Based
               Priority Panel.
 JflN-10-2003  06=34             703 603 9100                  97X          P.03

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JflN-21-2003  13:21       ROSS & fiSSOC                       206 447 0956   P.08/12
    New cleanup work  consists of large removal actions which, exceed
    funding  levels  available within a Region's baseline removal
    budget,  as well as cleanup activities at sites where no  previous
    actions  have taken place.  In addition, activities at  sites are
    considered new  work  if they constitute "separarable and  discrete"
    elements of existing site activities.

    Separable and discrete implies an element of work associated with
    the overall cleanup  of a site that may be considered on  an
    independent pathway  with regard to timing and implementation.
    The National Risk-Based Priority Panel is scheduled to meet on
    January  30 & 31,  1996, in Crystal City, Virginia to complete the
    ranking  of new  work  scheduled to begin in FY 96.


    Criteria for Cessation of work at Ongoing Projects;

        o    There may  be situations where work can be discontinued
             and the recovered funds used to support other  national
             priority projects.  These actions require prior
             consultation with Headquarters.

    AS noted, maintaining our ongoing projects remains a top
    priority.  This is particularly true for ongoing remedial action
    projects.  These projects are intended to mitigate an  identified
    risk and we should follow through on our commitments to  the
    States/Tribes and the communities to complete this work-

   Also,  it can be very costly to terminate a construction  project
   under a  fixed price contract,  with specific costs incurred for
    securing the site and demobilization, as well as claims  for costs
    already  incurred by the contractor (e.g.  long lead time
    equipment),  other costs incurred in shut-down, and potential
    impact claims for lost profits.   Additional costs could  be
    incurred later  if the project is restarted.  These facts weigh
   heavily against stopping projects through contract terminations.

   However,  situations may occur where stopping a project or work at
   a site should be considered as a viable option-
   criteria:
             Changed field conditions at a site have been identified
             and win result in a substantial cost increase to
             implement the remedy as defined in the ROD calling into
             question the rationale for the remedy selection
             decision.

             Evidence has been uncovered .which demonstrates that
             maintaining an ongoing long term remediation effort
             (e.g. ground water pump/treat, soil vapor extraction,
             bioremediation) will not result in a significant
JflN-10-2083  06=35             703 693 9108
                                                                   P. 10

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 JflN-21-2003 13:21        ROSS & flSSOC.                      206 447 0956  P.09/12
             additional reduction in residual waste concentration  or
             risk.

        «    Consultation with the State or PRP group indicates that
             another party is prepared to take over the work.

   Regional proposals to terminate ongoing projects will require
   consultation with OERR prior to initiating the action.  Also, the
   Region must coordinate closely with the affected State/Tribe, and
   involve the community in the decision process.

   Funds recovered from stopping work at an ongoing project must go
   through the deobligation process and be recertified by the
   Comptroller back to the national superfund program-  These  funds
   will be used to start new projects based on the national risk-
   based priorities -


   Criteria for_Eeopening RODs;

        o    Records of Decision should not be reopened to select
             cheaper remedies simply based on diminished
             availability of Federal remedial action funds,

        o    Under the Superfund reforms, EPA has committed to
             evaluating earlier decisions where new scientific
             information or technological advancements indicate that
             another remedial strategy would be more effective or
             appropriate for the site (while maintaining
             protect iveness) .  The principal focus of this effort  is
             to reassess older ground-water decisions which did not
             consider the potential presence of dense nonaqueous
             phase liquids (DNAPLs) or may benefit substantially
             from newly available remediation technologies".

        o    Records of Decision may be modified whenever
             significant new information persuades EPA that the
             selected remedy is no longer the most appropriate
             solution for the site.  Procedures for making such
             modifications are outlined in CERCLA section 117 (c) and
             (d) ,  the NCP,  and the ROD guidance.

   A selected remedy represents EPA's judgment as to the most
   appropriate solution for a superfund site — that protective
   ARAR-cotnpliant option which achieves the best balance of
   tradeoffs between remedial alternatives with respect to the
   remedy selection criteria, including cost.
   Remedies .are selected for individual sitps such that they  satisfy
   the requirements of CERCLA and the NCP Without consideration  of
   who will pay for the cleanup or their financial capability.
   Therefore, variations in available Federal funding should  have no
JAN-10-2903  06=35             703 503 9100

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JftN-21-2003  13:22       ROSS & RSSOC.                      206 447 0956   P.10/12
    bearing on our judgments regarding whether the remedy is the most
    appropriate solution for a site, although other information may.


    Deobligated Funds:


         o    Use of deobligated funds is subject to all established
              provisions of national Superfund program funding
              criteria.

    The Office of the Comptroller has been leading the 1994 and 1995
    deobligation effort.  Historically we have tried to assure
    Regions would receive a portion of the funds they deobligate for
    reprogramming in the Region of origin.  As a result of the budget
    situation in 1996 we will need to establish procedures and
    guidelines for deobligations during this fiscal year.  Any
    reprogramming of funds would still be subject to the national
    priority setting scheme.


    Additionally,  the processing of Superfund State Contract funds
    will be a higher priority than the deobligation of other funds
JflN-10-2003 06=35             703 603 9100                   97X           P. 12

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     JflN-21-2003  13=22       ROSS & ftSSOC.                      206 447 0956  P.11/12
 /"^                                  Attachment 3
                           National Risk-Based Priority Panel

                 In response to funding shortfalls and  an agreement between
            superfund Senior Managers  and  Congress, a change  from a regional
            prioritization  system to a national prioritization system was
            implemented in  Fiscal Year 1995  for all large dollar removals  and
            new start remedial action  projects where funding  was requested
            during Fiscal Year 1996.  This system involves  employment  of a
           .ranking  scheme  that prioritizes  projects based  on the  following
            principles:
                 *    Protection  of human  health

                 *    Protection  from  significant environmental  threats

                 *    Potential human  health or environmental threats  based
                      upon  current site  conditions.

                Five  criteria  and associated weighting  factors (below)  are
          used  to classify threats that contaminants may pose.  These include
          risks to human population exposed,  contaminant stability,
          contaminant  characteristics, threat to a significant  envircnment
          and program  management considerations.  Each criteria is ranked on
          a scale of one to five.   The highest score for any criteria is  five
          representing a current risk-current exposure scenario posi_ng.risk
          to human health  and the environment.   The lowest score  for  a factor
          is one representing a  future risk-future exposure  scenario.

                A national  prioritization  panel comprised of  national  program
          experts from Regional  offices and Headquar,-rs ranks  projects.   The
          panel met  for  the first, time in August 1995  to finalize the
i          protocol for ranking projects on  a national  level  and to begin
!          voting on  projects  that were ready for funding during Fiscal Year
j          1996.

                The Superfund  program  in the 1990s has  shifted from a  program
          with the largest percentage of  projects in  a study phase to a
          program in which the largest percentage of  sites have at least
          started remedial design. A national priority list is seen as a way
j          for  each Region  to  list its priority projects in order  of
          importance a.id rank these projects against  priority projects from
          other Regions ensuring that scarce resources are allocated to the
          projects posing  the most risk to human health and the environment.
      .TfiN-10-2003  06 = 36            7036039100

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     JflN-21-2003  13:22       ROSS & RSSOC.                       206 447 0956   P.12/12
                               Criteria Factors and Weights
           Weight                   Factors
             5        A.  Risks to 'Human Population Exposed:  Population  size,
                     proximity to contaminants,, likelihood of exposure,

             5        B.  Stability: Mobility of Contaminant, Site Structure  and
                     Effectiveness of any Institutional or Physical Controls.

             3        C.  Contaminant Characteristics:  Concentration,
                     Toxicity an<3'Volume.       !

             3        D.  Threat to a Significant Environment: Endangered
                     Species or their Critical Habitats, Sensitive
                     Environmental Areas.

             4        E. Program Management Considerations: Innovative
                      Technologies, Cost Delays, High Profile Projects,
                      Environmental Justice, State involvement,
                      BrownfieIds/Economic Redevelopment.

           The raw score for each factor is multiplied as follows to obtain the
           maximum score.
                                                    Raw      Weight     Total
                                                    Score    Factor     Score
                 Factor  A   Population Exposed  1-5    x    5    »    2,5

                 Factor  B   Stability            1-5    x    5    -25

                 Factor  C   Contaminant Char     1-5    x    3    «    15

                 Factor  D   Threat  to  a Significant
                           Environment         1-5    x    3    =15
i
|                Factor  E   Program Management
!                           Considerations.      1-5    x    4    -

I                                                    Total          -  100
     JAN-10-2903  0S:36             703
                                                                       TOTflL P.12

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Appendix IV:
Memo from Henry L. Longest II Concerning Guidance on
Setting Priorities for NPL Candidate Sites
NACEPT Superfund Subcommittee  Report   12,2004
Appendix IV

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Appendix IV                            NACEPT Superfund Subcommittee Final Report  | April 12, 2004

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                                                            PB93-963333
             UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
                          WASHINGTON Q,C. 20460
                                                          OFFICE OF
                                                  SOLID WASTE AHO § IWEFKJEHCY
                                            OSWSE Directive 9203,1-06
 MEMORANDTOj

 SUBJECT:   Guidance on Setting Priorities for NPL Candidate sites

 FROM;      Henry L.  Longest II,  Director
           Office of Emergency and Remedial

 TO:        Director,  Waste Management Division
             Regions I „  IV, v, VII
           Di reset or,  Emergency and Remedial Response Division
             Rrjgion 11 -
           D.3r«;ctor,  Hazardous Waste Management Div. sior:
             Regions HI,  '-/I,  VIII,  IX
           D i r •:= c tor,  Ha za r dous Was c e D i v i s i on
             Region X
           Director,  Environmental  Services Division
             R-egions I,  VI, VIZ

.PURPOSE

     The purpose of this  directive is to transmit  interim final
guidance on  "Setting Priorities for NPL Candidate  Sites"  for  use  in
Superfund  site assessment.
     Many of  the  regions  have substantial backlogs of sites  for
which site  inspections (Sis)  have been completed" Each  of  tJiese
sites needs  additional staff  work to support a decision to list  the
Site on the  KPL or  to refer the site to the scate or other
authorities  ;or appropriate action.

OBJECTIVE

     Ali participants  in  the  Superfund program  should set priorities
for National  Priorities List  (MPL)  candidate  sites in  a consistent
manner. Proper  use  of the guidance  will  help  to achieve this  aoal
The Supeirfuno Accelerated Cleanup Model Regional  Decision Team
     can helj> set priorities  and ensure technical quality.

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                                 -2-

IMF LEHBHTA TH3.W

     Superfund site assessment personnel should Immediately begin
incorporating this priority-sett ing guidance  into  ongoing
operat ions,

     If you  ne ad furc'her information on priority setting,  contact
the Hazardous Site Evaluation Division, Barbara Vandermer  at  FTS
703-603-8812 <: r David Guderkirk  at  FTS  703 -603 - 6721 .

Attachment

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             SETTING PRIORITIES FOR ¥PL CA1TOIDATE SITSS

PURPOSE

     This guidance document: identifies factors that will help EPA
regions decide the order  in which  they should consider  sines with
completed si til: inspections  (Sis) for  inclusion on  the National
Priorities Limt  (KPLJ pursuant  Co  section 105 fa) (8) (B!  of  the
Comprehensive Environmental Response, Compensation, and Liability
Act of: 199D  i^EHCLA) - Stressing risk-based decisionmalcing,  this
•guidance should be used as s.  tool  to  increase the  consistency of
the process fur setting priorities, conserve program  resources, and
advance Superiiuad' s  worst- sites- first policy. Regions should use
the factors in this  directive  to determine which sites  receive  the
most expedited consideration  for early action or NFL  listing, noc
to remove sitiis from further  consideration altogether.

     This directive  is intended to be used on sites with newly
completed Sis and older sices  for  which no decision on  priority has
been made. Th 2 guidance does  not recommend that  regions reconsider
earlier priority determinations on siies  in  their  backlogs,
although they may choose  to dc  so.

     The procedures  set Eotth  in this document are intended as
guidance to Employees o£  EPA,  States, and other government
agencies, EPA officials may decide whether or not  Co  follow ihc
guidance bas€;d on analysis of  specific site  circumstances.  EPA  m&y
modify this guidance at any time without  public notice.  This
guidance does not constitute  EPA r vie making  and  cannot  be  relied on
to create any rights enforceable by any party in litigation with
the United States.



     Many o£ the regions  have substantial backlogs of sites for
which S±3 have been  completed.  Each of these sites needs additional
staff worJc to support a decision to list  the site  or.  the MPL or to
refer the site to the State,  CERCLA early-action authorities, or
other author j ties as appropriate.

GniDELINES_Fi;iR _SETTING _
     Each region should use the following two-step process Co
establish the relative priority of  sites. The process is designed
to make site priority evaluations quick  ano simple; decisions
should require no more information  than  is routinely included  in
site inspection reports. To avoid duplicative efforts, site
priority decisions  should not be reassessed unless significant  new
information becomes available.

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jjjtep 1;  _C_cm^.ij:|gLJLj5g|ljer.a.l  Factors

     For each. site assigned  a projected  Hazard  Ranking  System i.HRS)
score at or above  28.5,  regions  should consider Che general
factors  discussed  below.  However,  these  factors do r.ot  constitute
an exhaustive .,ist ;  regions  have the  flexibility to consider
additional fadiors  they  deem appropriate,

     Hazard Ranking  System Score.  The projected HRS  score -nay
provide  one measure  of a site's  risk:  zn  evaluating sites under the
HRS,  regions should  ordinarily project  the  score based  on
evaluating eac:i  site's RIOSC  significant  pathways.  Ones  a projected
HRS score  {developed from  the SI worksheet  or PREseore)  at or above
23,5 is  determined,  regions  should consider whether there are risks
not reflected in the projected score.

     Environmental Factors.  Although most  of  the  following factors
will  have been considered when determining  the  projected HRS score,
they should a:, so be  evaluated qualitatively for" both,  scored and
unscored pathways  to the extent  that  appropriate data are available
in the SI reprrt, Regional staff should  evaluate any  unscored
pathways subjectively by using their  best professional  judgement,

          Has  an  observed release been documented? Has Level  1
          (exposure to humans or  sensitive environments  above  a
          health-based or ecological  benchmark) or 2  (exDosure
          below benchmarks)  contamination been documented?  Has  the
          si to caused the closure of  a drinking water supciy?

         How  far is  the  target population from the site sources?
          Is t:he  population potentially or actually exposed under
         current land use  conditions  (both onsite and. off site) ?
         Whai: is the likelihood  that  exposure has occurred?

         Has the Agency  for  Toxic  Substances and" Disease Registry
          {AT,i!DR)  issued  a  health advisory?  Is it planning  to?

         Whai: are  the risks  associated with contaminants found in
         air,  soil,  ground water,  and surface water?  Are the
         hazardous substances, pollutants,  or contaminants at the
         sit<; highly toxic?  Are  large quantities of these
         substances  present?

    -    i'lha; is the effect  of any removal/ remedial work at the
         sit-5? Are conditions deteriorating? Is contamination.
         sprsading?  what effect  will  tile delay of any remedial
         ace ion have at  the  site?

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      -     Are  hazardous substances,  pollutants,  or contaminants at
           the  site mobile? If so,  how mobile'?  Are any containment
           features in place to mitigace risks? If so, how effective
           are  they? Are these substances likely to be released in
           the  future?

      -     Are  any nearby sensitive environments or endangered
           species threatened? How  fragile or  how important is the
           sensitive environment? How far is  it from*the site
           sotr-ces? Are major impacts iikelv?

      CERCLA Removal Actions, Are  EPA removal  actions complete,
 underway, ^or scheduled? Will proposed or ongoing EPA removal
 actions significantly reduce risks?

      Other Regulatory Involvement- Is the sits being addressed by
 sotne  other authority?

           Is there active  State or nor.-CERCLA  Federal response
          action  complete,  ongoing,  or scheduled at  the site? Will
          all  pathways of  concern  be evaluated?  Are  resources
          adequate to address L'ne  site?

           Is the  site subject to regulation pursuant  co subtitle c
          cf the  Resource  Conservation and Recovery Ace (RCRA)? If
          tlw:  RCRA deferral  policy is  applicable,  the site "should
          not:  receive further considers tier: for  placement  on the
          N'PL .  If  RC.HA deferral is not appropriate, any complete,
          ongoing,  or scheduled response" action  taken under'RCRA'
          should be considered in  priority setting,

          Are  other regulatory agencies,  such  as  local  and county
          health departments, undertaking response action  at  the
          sije? Can they provide adequate oversight?  Is such  action
          lively to continue?

     PRP Response  Actions,   Has the  potentially  responsible partv
 (PRP) completed,  scheduled,  or undertaken response action at" the'
site? is such  action  likely  to continue?

     Degree af Public Concern.  Has  the  State  recommended  this git-
for the *PL pursuant  to  CERCLA 103(a} (a) IB)?  Is  there community
interest in the site? Are  community  groups aware of plans  for
characterization/remediation, and  do they approve?  is there
congressional  interest?

51ep 2 ;	_J3^jjAana^js	Priori_ti_es.

     After evaluating  the general   factors listed  above,  each region
shoula  divide  its candidate  MPL  sites  into  high or low  priority
Particular factors should be  considered in makincf this determination-

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     High priority  generally should  be given  to  any  site:

     -    where people are currently exposed  to  hazardous
          substances, pollutants, or contaminants;

     -    where actual contamination has been documented,
          espsicially at or above a health-based  benchmark;

     -    where a large potentially affected  target  population  is
          nea::by;

     -    whe::e contamination to a sensitive  environment or  fishery
          has been documented;

     -    whe::e tJie State has recommended the site be  listed on the
          KPL pursuant to CERCLA I05(a)(8)(B); or

          where the ATSDR has issued a health advisory or  is
          pla in ing Co .

However, in  considering  the  totality of  circumstances  consistent
with the wors; t-s ites-first policy, regions  may  determine that a
particular s.its may  not  merit  high priority.  Such  a  situation might
occur when significant  response  actions  are being  undertaken =t a
site by the  State,  other  governmental  authority,  or  a  PRP

     Low priority generally  should be given to all sites nou
exhibit-ing ar.y of the above  factors. Once again,  however,  after
viewing the  :-otality of  factors  present,  regions may conclude that
a given site having none  of  these factors should nonetheless be
assigned higl: priority.

     Within each category, priorities should  be  set  consistent  with
SPA's worst-^ites-first policy.  This guidance does not present
specific factors for determining which of several  sites  should  be
addressed fi;;st within  each  category. Guidance may be  provided  in
the future iJ: appropriate.

PE5H REVIEW .PROCESS

     To help set priorities  &s well as to ensure technical quality,
the Superfwnd Accelerated Cleanup Model  (SACM) Regional  Decision
Team (RDT)  may opt  to use some form of peer review process.  Peer
reviews can be an important  step in  ensuring  technical accuracy and
promoting consistency.   In addition to site  assessment  staff, the
peer review group could include program  management staff,  remedial
project managers,  on-scene coordinators,  technical staff  (e.g.,
chemist, hyd.rogeologist toxicologist} , and  possibly  representatives
o£ non-Super£und SPA

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programs such, f..$  air,  water,  and toxic  substances.  Regions may
tailor these suggestions  to  their own needs  or  choose  not to
implement peer review.

POCTJKElgATlOU

     Regions should informally document the  factors which
determined each site's  priority.  This record should, aot  be made
public. The Freedom of  Information Act  (FOIAj exempts  from
mandatory release preliminary documents reflecting  the Agency's
deliberative processes  [5  DSC 552{bj (5)],

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Appendix V:
Performance Profile
NACEPT Superfund    Final    12,2004         Appendix V

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Appendix V                            NACEPT Superfund Subcommittee Final Report | April 12, 2004

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Superfund Site Report Card Mock Up
General Background
Region
State
EPA ID
Site Name
N PL Status
Federal Facility
Population 1 Mile
Population 4 Miles
Media Contaminated
Primary Contaminants
1
MA
MAD001026319
ATLAS TACK CORP.
F
N
5,000-10,000(6,688)
100,000-150,000(114,601)
Soil, Groundwater, Surface
Water, Sediments
Too numerous to list
Administrative
Date of Site Assessment
Date of Proposal to NPL
Date Final on NPL
Date Construction Complete
Date Deleted from NPL
How Long on NPL (NPL Listing to date, CC, or
deletion)
"Year Class" Comparison

06/24/1988
02/21/1990


13.0 years
70% of sites listed
concurrently or prior to Atlas
Tack are construction
complete
Major Cleanup Milestones
Final ROD at Site
Human Exposure Under Control
Contaminated Groundwater Migration Under Cont
Construction Complete
Y
Y
N
N
Cleanup Progress
RIFS Status
ROD Status
RD Status
RA Status
LR Status
Removal at Site
ROD at Site
Status of "Leading" OU
RIFS All OU Complete
ROD All Complete
RD 1 or More OU Underway
RA No OU Underway
National Average






5,000-10,000(8,025)
75,000-100,000(77,226)








12. 2 years


74% have final ROD
80% are under control
61 % are under control
54% are CC

69% have All RIFS Complete
74% have All RODs Complete
15% have 1 or More RD
Underway
29% have no RAs Underway
or More Planned Not Underway
Y
Y
Design Underway
Durations of Current Cleanup Activities
Longest RIFS Ongoing Duration
Longest RD Ongoing Duration
Longest RA Ongoing Duration
Date of Last Completed Cleanup Action
N/A
N/A
N/A
Remedial Design 07/23/02
Construction Completion Status
CC Site RIFS Planned or Underway
CC Site RD Planned or Underway
CC Site RA Planned or Underway
CC Site LR Planned or Underway
CC Site Five Year Review Completed
N/A
N/A
N/A
N/A
N/A
Scope of Contaminated and Cleanup Progress
RME Cancer Risk
Non-Cancer Hazard Index
Known Area of Contamination
% Where Cleanup Goals are Met
% With Residual Contamination
Selected Remedy - Treatment Component
Selected Remedy - Containment Component
Estimated Volume of Contaminated Material
% of Estimated Volume Addressed
Institutional Controls In Place
Institutional Controls Not Required
Institutional Controls Required But Not In Place
Five Year Review Protective
Total Report Card Points















5x 10(-3) (PAHs, PCBs, Arsenic)
<1
54,000 cubic yards


6,000 cubic yards
48,000 cubic yards





N/A













37.5
Year Group
Comparison (1988-
1992)






5,000-10,000(8,833)
75,000-100,000
(74,399)









60% of sites are
construction complete

76% have final ROD
84% are under control
68% are under control
60% are CC

3.7
2.7
3.3
3.2





























41
Site Report
Card Points



















10
10
0
0

4
3
2
1





























30

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Appendix VI:
Additional Elements of Comprehensive Reporting
NACEPT Superfund Subcommittee  Report  12,2004          Appendix VI

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Appendix VI                            NACEPT Superfund Subcommittee Final Report |  April 12, 2004

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Appendix VI
Additional Elements of Comprehensive Reporting
As was stated in Chapter V of the body of the report, the Agency has flexibility in terms of
the  reporting  format used  for measures  of  progress and   performance.   The
Subcommittee  recommends that the Agency track additional measures  (for which data
currently exist) and,  in the future, add additional measures  for which  data does not
currently exist but can reasonably be obtained. Consensus did not exist regarding which
additional  items  should  be tracked.   Many  suggestions were  offered by  individual
members as data that could increase the effectiveness of the Performance Profiles or
provide valuable information for other purposes. The group felt it was important to move
the ideas forward as an Appendix in an effort to provide more comprehensive feedback to
the Agency. By not including this level of detail, the richness of the discussion would be
lost.  The following items were discussed as data that could be helpful to track in order to
more comprehensively understand the progress of the  Program.  They do not reflect
consensus among members, rather they are ideas put forth by individual Subcommittee
members to which other members may object.

    -* Human exposure under control (from land and/or groundwater contamination)
    -* Contaminated groundwater migration under control
    -* Site cost information [total cost to-date  and projected total   (EPA data on past
       costs and projections of future costs if this is determined to be available for a
       sufficient number of sites to make reporting reliable). For example, cost spent on
       RA. Cost spent to get to construction complete and RA costs as a percentage of
       total costs)
    -* Community involvement  indicator (Existence of a  TAG   - Y/N,  Existence of a
       CAG - Y/N)
    -* Total number of Operable Units
    -* Number  of sites  where  all  cleanup  goals  have  been  achieved  (Some
       Subcommittee members understood this number to  be  slightly different than
       "sites deleted from the NPL" and felt it would  be useful to track both - with an
       explanation of the difference.)
    -* Performance Profile (report card) score from previous year
    -* Site cleanup lead (fund, PRP, mixed)
    -* Number,  description and effectiveness of institutional controls and  long-term
       stewardship efforts (this information could  be used to indicate the percentage of
       ROD'S  requiring institutional controls at a national level)
    -* Sites that reached construction complete but have  been reopened (with  an
       explanation of the reason why the remedy has  been reconsidered. For example,
       improved technology has become available or the remedy failed)
    -* Acre feet (or gallons)  of  restored water (specify amount restored  for drinking
       water vs. cleaned up to pose no unacceptable  risk to ecological receptors, or
       cleaned up for restricted use)
NACEPT Super-fund Subcommittee Final Report \    12, 2004
Appendix Vl-Page 1

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    -* Acres of land returned to beneficial use (specify amount cleaned up for restricted
       vs. unrestricted  use and  acres  cleaned up to pose  no unacceptable risk to
       ecological receptors)
    -* Acres of sediment restored for beneficial use (restricted versus unrestricted and
       acres safe for ecological receptors)
    -* Contaminants of concern at each site by medium
    -* Number of  sites (specifically  NPL sites)  completing  each major  step  in the
       Superfund   process:  remedial  investigations  completed,  feasibility  studies
       completed, ROD'S issued,  remedial designs completed, constructions completed,
       five year reviews completed and sites deleted from the NPL.
    -* Sensitive Environments Protected  (This was address  in the  context of the
       national  priority  measures.  The Agency has not  yet  proposed  a measure for
       sensitive environments. The Subcommittee recognizes that it is complex and
       difficult, that it is important, and that when  a measure is  developed  it should be
       thoroughly reviewed by stakeholders before implementation.)
    -* Consistent site type definitions (i.e. SIC codes)
    -* Current land use (private/commercial)
    -* Exposure pathways (e.g. consumption, ingestion,, subsistence fishing, etc.)
    -* Cooperation at site with other cleanup programs
    -* Risk Reduction Measures
    -* Remedy effectiveness measures
    -* The Hazard Ranking Score for the Site
    -* The date EPA expects construction to be complete
    -* Implementation  of  administrative  reforms  (e.g.  orphan  share  funding,
       groundwater strategy, special  account, land use,  remedy review board, revisit
       remedies to update approach)
    -* PRP costs
    -* Human  Health risks
    -* Ecological risks
    -* Remedy failure - In addition to the 5-year review data that is currently included in
       the Performance Profile, additional data should be collected to report on the
       effectiveness of  remedies  relative to state  and national cleanup standards and
       community expectations.
    -* Acres of land covered by operable units at a site
    -* Demographics information  (race, ethnicity, income, etc.)
    -* Number of removal actions and population protected
    -* Acres of land (now) available for industrial or other reuse and acres  predicted to
       be available.
    -* Economic, recreational or environmental benefits derived from reuse.
    -* Number of sites  or operable units at which  risk based cleanup  goals have  been
       attained
    -* Use of resources from or cooperation with other cleanup programs
    -* Use of contract reforms

The Subcommittee recognizes that in some cases, EPA currently does  not have the data
to track all of these measures  or they  do not  have consistent data to  do so accurately.
Appendix Vl-Page 2                   NACEPT        Subcommittee Final       |     12,

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The Subcommittee suggests that EPA consider developing the capacity to collect and
track these data so that they can be reported accurately at the site and national level in
the future.

Many members oppose certain  items  included on the list.   In particular,  a  range of
perspectives on the Subcommittee felt that the RCRA measures were inappropriate to
include  for Superfund.  While  it may be  appropriate for  the  RCRA  program to use
"groundwater contamination under control" as a national measure of performance [since
all other chemical releases (air emissions, discharges to surface water, etc.) are tightly
controlled  at the RCRA facilities] Some Subcommittee members believe that this is not a
good measure of performance for all Superfund sites, many of which were created and
abandoned before RCRA was enacted.  Superfund sites typically suffer from uncontrolled
releases into  the  air,  surface water,  sediments and  soil,  as well as  groundwater.
Therefore, if the performance of EPA staff is measured by whether they have controlled
groundwater (but not other types of) contamination at  a site, the fear is that will have the
undesirable  effect  of driving  EPA  to  place its top priority on controlling groundwater
contamination  at sites first, even if other problems are more urgent.   These members
believe that a more balanced national measure would ask whether contamination from a
list of relevant sources (air, soil, surface water and groundwater) is under control at a site,
meaning that it is not spreading.  This would allow  EPA to set the right priorities, seeking
to control the most pressing types of contamination first, and  getting credit for achieving
such control.

Additionally, some  members believe that stopping contamination from spreading, while
generally beneficial, is not a good indicator of cleanup progress.1 These Subcommittee
members  believe the RCRA measures are inappropriate  because they might prioritize
and reward  the use of containment and  institutional controls,  rather than permanent
treatment, and because they may be difficult to objectively verify.

Some members of the Subcommittee believe that  some of these measures (particularly
health risk related) are very controversial and may need outside expertise to develop if
they are to be reliable.  Some  members felt that the critical factor in measuring program
progress is reduction of risk to human health and the environment at NPL sites.  They felt
that it was vitally important for the  agency to monitor and calibrate  risk reduction using
risk assessment techniques as the  basis for such a measure.  Where human exposures
are under control, communities and the public should know  this fact.  Other members
also believe that risk reduction  measures would be difficult if not impossible to develop in
an objective way that accurately reflects the progress  of the program. Furthermore, critics
of risk reduction measures  argued that  such  measures  have the potential to trigger
unintended consequences that outweigh the benefits. The Work Group on Measuring
Program Performance  devoted considerable time and  effort in attempting to  develop
meaningful, transparent, clear and simple measures that would not require significant
additional  expenditures to gather and collate data. However, the group was unable to
1 Subcommittee member Richard Stewart believes that these RCRA measures are appropriate measures of
performance  in reducing  risks at sites, pending  development of more truly risk  based measures. See
Attachment I for his individual statement.
NACEPT                       Report      12,                      Appendix Vl-Page 3

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satisfy these goals. This is largely due to the difficulty in defining the population at risk.
EPA identifies exposure pathways and potential receptors.  However, once unacceptable
exposures are identified, EPA does not expend  resources trying to quantify the actual
numbers of receptors, and the exact risk to which they are exposed. Nor can the agency
capture averted risks to future populations because it cannot predict how adjacent areas
will be developed.

Similar to the statement made with respect to national priority measures in the main body
of the report,  some members believe that mega sites may need to be  distinguished from
other sites covered by the performance profiles  in order to reflect the  expectation that
progress on such sites will likely take longer.
Appendix Vl-Page 4                  NACEPT         Subcommittee Final       |     12,

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Appendix VII:
Community Satisfaction Survey
NACEPT Superfund Subcommittee Final Report April 12, 2004          Appendix VII

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Appendix VII                           NACEPT Superfund Subcommittee Final Report  | April 12, 2004

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                                                          OMB Control No: 2050-0096
                                                          Expiration Date 10/31/04
             What Do You Think About EPA's Community
                Involvement Efforts at the               Site?
      The U.S. Environmental Protection Agency (EPA) is cleaning up the toxic wastes at the
      	Superfund site in your community. EPA believes the active, meaningful
involvement of community members is critical to the success of a cleanup effort. This survey is
an opportunity for you to tell us how well we are doing at listening to your concerns about the
cleanup and making it possible for you to participate in the planning and decision making
process. Please take a few minutes to answer the questions. Your views are important and will
help us to be more responsive to your needs and interests.

       This survey is being conducted in accordance with the Federal Paperwork Reduction Act
Information Collection Request # 1463.05.  You will need about 15 minutes to answer the
questions.
Directions:
- Do NOT put your name, address, or phone number on this form.
- Please use the postage paid envelope provided to return this form to our contractors.
- Do NOT put your return address on the envelope.
1.  How do you rate EPA at each of the following?  (Circle one number for each question)
                                         Very Bad                         Very Good
 a. Providing the information you need           123456
 b.  Giving you accurate information       123456
 c. Making the information easy to understand     123456
 d. Earning your trust                          123456
 e. Making it easy to get involved                123456
 f. Understanding your concerns                 123456
 g. Responding to your concerns                 123456
 h. Treating you  courteously                    123456
 i. Having a fair decision making process         123456
 j. Using your input                           123456
 k. Explaining decisions                       123456
 1. Cleaning up the  site                         123456
                                                          OMB Control No: 2050-0096
                                                          Expiration Date 10/31/04

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2.  Before cleanup of the site began, how concerned were you about the site being harmful
to  each of the following?  (Circle one number for each question)
                                  Not Concerned             Very Concerned
 a. My family's health                   123456
 b. The environment                    123456
 c. Property values                      123456
 d. Jobs in the community               123456
 e. Business in the community            123456

3.  How concerned are you about the site being harmful to each of the following once the
cleanup work is finished? (Circle one number for each question)
                                  Not Concerned             Very Concerned
 a. My family's health                   123456
 b. The environment                    123456
 c. Property values                      123456
 d. Jobs in the community               123456
 e. Business in the community            123456

4.  How have you have learned about EPA's work at the site?  (Check all that apply)
 	 EPA mailings (other than this survey)
 	Newspaper articles
 	 Radio or TV news
 	 Community member
 	 Family or friends
 	 EPA's web page
 	 Public meeting or information session held by EPA
 	 Direct conversation with someone from EPA
 	 Information about the site is "common knowledge"
 	 Know someone who worked at the site
 	 Participation on one or more citizen groups

5.  How would you prefer to receive site information?  (Check the ONE you most prefer)
 	 Monthly "News Brief: project updates,  contacts, calender of events, and new documents
 	 Short (1-2 pages), very focused (issue-specific) mailings, sent frequently
 	 Longer, general informational mailings,  sent periodically
 	Newspaper articles
 	 Radio or TV news
 	 A knowledgeable person in your community
 	 The EPA web site
 	 Short, very  focused meetings, held frequently
 	 Longer, general informational meetings, held periodically
 	 A direct conversation with an EPA representative
 	 Presentations at local clubs  and organizations
 	 Other	
                                                           OMB Control No: 2050-0096
                                                           Expiration Date 10/31/04

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6.  How interested are you in obtaining information about the following topics? (Circle one
answer for each question)
                                        Not Interested                     Very Interested
 a. EPA's Superfund program                   123456
 b. Toxic wastes at the site                      123456
 c. How the site might affect human health        123456
 d. How the site might affect the environment      123456
 e. Site cleanup decisions                       123456
 f.  Other
7.  What is the best way to get your participation?  (Check the ONE you most prefer)
 	 Through opportunities for you to give written comments.
 	 Through public meetings where you can voice your comments.
 	 Through opportunities for you to meet and talk informally with EPA staff.
 	 Through a toll free telephone number you can  call with your comments.
 	 Through a community group which discusses issues and concerns with EPA.
 	 Through opportunities for you to talk with independent experts.
 	 Through a web site for you to communicate with us.
 	 Other	

8.  Please tell us whether you  have ever: (Circle your answer for each question)
 a.  Provided information to EPA about the project and its history.        Yes   No
 b. Expressed your concerns about the project to EPA.                  Yes   No
 c.  Offered cleanup suggestions or advice to EPA.                      Yes   No
 d. Given EPA comments on materials available for public review.       Yes   No
 e.  Requested information from EPA about the site.             Yes    No

       If "no" to all of the above, why not?
9.  Can you accept the decisions EPA has made so far about the site cleanup? (Check one)
 	 Yes
 	 No
 	 I am not aware of any decision EPA has made
                                                           OMB Control No: 2050-0096
                                                           Expiration Date 10/31/04

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10. Is there anything else you would like to tell us about EPA's community involvement
efforts or about this cleanup project?
Thank you for taking the time to share your views with us!  To get on the EPA's existing
mailing list, please contact	.
EPA estimates the individual burden for completing this survey to be 15 minutes.  On average there will
be about 300 respondents to the survey, for an overall public reporting burden of 75 hours.

Burden means the total time, effort, or financial resources expended by persons to generate, maintain,
retain, or disclose or provide information to or for a Federal agency. This includes the time needed to
review instructions; develop, acquire, install, and utilize technology and systems for the purposes of
collecting, validating, and verifying information, processing and maintaining information, and disclosing
and providing  information; adjust the existing ways to comply with any previously applicable instructions
and requirements; train personnel to be able to respond to a collection of information; search data
sources; complete and review the collection of information; and transmit or otherwise disclose the
information. An agency may not conduct or sponsor, and a person is not required to respond to, a
collection of information unless it displays a currently valid OMB control number. The OMB control
numbers for EPA's regulations are listed in 40 CFR Part 9 and 48 CFR Chapter 15.

Send comments on the Agency's need for this information, the accuracy of the provided burden
estimates, and any suggested methods for minimizing respondent burden, including through the use of
automated collection techniques to the Director, Collection Strategies Division, U.S. Environmental
Protection Agency (2822), 1200 Pennsylvania Ave., NW, Washington, D.C. 20460; and to the Office of
Information and Regulatory  Affairs, Office of Management and Budget, 725 17th Street, NW, Washington,
DC 20503, Attention: Desk Officer for EPA.  Include the EPA ICR number and OMB control number in
any correspondence.

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