905R01015

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     United States  Environmental Protection Agency, Region 5
                   Corrective Action Conference
                      January 17  and 18, 2001
                         Chicago,  Illinois

Section I - Presentation Summaries

Section II - Action Items from Meeting

Appendix 1 - Presentation Slides

Appendix 2 - Meeting Handouts
                             .«t.,t
                   U.S. Environmental

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                Section I  -  Presentation Summaries

 Day  1  -  January 17,  2001

 Welcome  and Introductory  Remarks  -  Robert Springer,  Director,
 Waste, Pesticides  and Toxics  Division,  United States
 Environmental Protection  Agency  (U.S. EPA),  Region 5

 We have  made much  progress  in the RCRA  program during  the  past
 two  years.  Achieving Environmental  Indicator determinations  (Els)
 has  been our main  priority.   For  the  State programs:   Illinois  -
 has  been the standard bearer  for  Region 5 States;  Indiana  -  Our
 Memorandum  of Agreement (MOA)  for their voluntary  program  is
 almost final, it may be a model  for the country to follow;
 Michigan -  Region  5  recently  signed a MOA with the State;
 Minnesota - Has only two  CA 725  (human  health)  and only  three CA
 750  (groundwater)  determinations  left to complete.   They also
 have only two facilities  that have  CA 999 determinations
 (termination of Corrective Action process) left to complete;
 Ohio - Has  a large number of  facilities in their universe  to
 address.

 Projections - Our  goal  is to  keep pace  while working on  our
 streamlining.

 Streamlining -  Fewer deliverables required;  New Orders will  be
 performance-based; and  our goal will be to streamline  existing
 orders.

 Region 5  RCRA corrective  action strategy:  Where we were, are, and
 where we  are going.   Future goals will  be to get voluntary
 agreements  with all  of  the states,  meet Government Performance
 and  Results  Act  (GPRA)  goals  for  Environmental  Indicators and
 complete  the Corrective Action process  (CA 999) .

 National  Perspective - Michael Shapiro,  Deputy  Assistant
 Administrator,  Office of  Solid Waste and Emergency Response,
 U.S.  EPA

 Region 5  is  leading  the country.  Region  5 entered into  the  first
 Memorandum  of Understanding to recognize  a State voluntary
 program  (Illinois  in July 1997).  The Region  has also issued five
 streamlined  Corrective Action Orders that  implement cleanup with
 a minimum of process.  They have  also reached voluntary
 agreements with six  facilities.

This  meeting is an invaluable opportunity  for dialog and is a

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model for other Regions to follow.  This is the second such
meeting here in Region 5 and we are urging other Regions and
States to have similar stakeholder meetings.  The States are the
key to reaching GPRA goals as 38 states have authorized
Corrective Action Programs in place.  Also key to meeting GPRA
goals is cooperation between U.S. EPA, the States and facilities
(private-sector).  Other key components are to continue the
momentum of Reforms II, site reuse and redevelopment.

The first set of RCRA Corrective Action reforms (July 1999)
focused on environmental results over process, enhanced public
participation and flexibility.  These reforms led to a
significant increase in program accomplishments.  Nationally,
facilities meeting El determinations increased  tenfold since
1997.  Last month, in Pontiac, Michigan, General Motors
Corporation and EPA celebrated the 500th facility to meet both
Environmental Indicator Measures.

In the future cleanups will be more challenging.  Last August
Assistant Administrator Tim Fields announced that EPA needed to
renew our commitment under Corrective Action to achieving our
cleanup goals be developing a second round of RCRA Cleanup
Reforms that would build upon the 1999 Cleanup Reforms and that
would ensure all stakeholders had a voice.  Last week at the
BP Amoco facility in Wood River, Illinois, U.S. EPA announced the
RCRA Cleanup Reforms II.

The 2001 Cleanup Reforms focus on several themes.   These include:
Pilots to ground-test innovative and protective approaches to
cleanup; Cultural change, Changing the way people interact and
implement the program in the field; Information, Effective access
to timely information to increase public awareness and
opportunity for involvement at Corrective Action sites; and
Redevelopment and reuse of sites.  Capitalizing on redevelopment
potential at sites can motivate interested parties in expediting
cleanup and help to revitalize communities.

Some of the highlights of the 2001 RCRA Cleanup Reforms include:
At least 25 innovation pilots, at least one in each Region for
2001.  The new pilot program will support State and Regional
offices in their efforts to use innovative, results-oriented and
protective approaches to speed up El determinations and final
cleanups; U.S. EPA will take actions to accelerate culture change
in implementing the program including hosting a stakeholder
meeting, provide the public with more access to information  (El
forms and site summaries on-line)  and encourage stakeholders top
to capitalize on brownfields reuse.

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 Industrv  Perspective,  John  Quarles, Esq., Counsel, RCRA
 Corrective Action Project

 Key  to program  success is the  application of  concepts and
 spending  funds  OR cleanups  versus  studies.  In  April 1997,  the
 RCRA Corrective Action Program was in  need  of reform. There were
 too  many  sites  stuck  in the study  phase.  There was a need  to
 communicate  recommendations to U.S. EPA  for program changes and
 both U.S. EPA and industry  were in agreement  that  reforms to the
 RCRA Corrective Program should be  made.  There  were two
 categories of reforms  in 1999,  change  in process and change in
 approach.  The  original Corrective Action process  was very  rigid.
 The  reforms  were implemented to change the  program to a results-
 based approach.  Oversight  was tailored  to  speedup the  process.
 A  holistic approach was used to look at  the entire facility (not
 one  solid waste management  unit at a time).   Procedural
 flexibility  was stressed.   U.S.  EPA was  to  set  performance
 standards (define objective) and leave it up  to industry how to
 get  there. Data collection  was targeted  to  that which the agency
 felt was  really needed and  only go back  if  more data were
 required.

 The  government  should  address  the  issue, "how clean is  clean."  A
 relationship between  cost and  benefits must be  considered.   The
 cost effectiveness of  the cleanup  must take into account future
 land use  (industrial  standards versus  residential).  Use of
 Institutional controls at sites.   Groundwater standards need to
 be reevaluated.

 State Perspective. William  Child,  Chief Bureau  of  Land,  Illinois
 Environmental Protection Agency

 In the State of Illinois, Corrective Action is  a subset of  the
 Illinois  Cleanup Program.   Illinois goals are to properly
 remediate Solid Waste  Management Units.  Illinois  has a flexible
 process for  cleanups.   We negotiate with industry  to reach
 mutually  acceptable goals.   Illinois expects  to meet the GPRA
 goals for 2005.

 Illinois  uses a tiered approach  to Corrective Action referred to
 as "TACO" (Tiered Approach  to  Cleanup  Objectives).  It  is a  risk
 based standard  (10 -6)  and  used  in all our  cleanup programs.
 There are three tiers  (I -  Residential, II  -  Site  Specific
 Calculations and III -  Risk Modeling).

Another component of the Illinois cleanup program  is the
 groundwater management  zone.   This consists of  source removal and
managing remaining waste in a  defined  zone.

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 Corrective Action Management Units  - there are three facilities
 in  Illinois  that have  consolidated  wastes into one unit.

 Remedial Action Plan Permit - To  date Illinois has issued three
 final and five draft permits.   Illinois was able to issue the
 draft permits within 90 days.   This approach allows for faster
 and more cost effective cleanups.

 Illinois has learned the  following  lessons from our past
 experiences.  First, the  command  and control that we had used in
 the past were not the  best option.  We will accomplish more by
 offering cleanup incentives to  facilities.  We need to tie our
 other cleanup programs to the RCRA  Corrective Action Program.

 Illinois is  currently  working on  an Ecological TACO.  We should
 have this finished by  the end of  the year.  We also plan on
 continued teamwork and open communication with the stakeholders.
 We  also want to continue  looking  for new and innovative ways to
 manage the program.  We are open  to new ideas from industry.

 Voluntary Efforts by the  Private  Sector, Robert Johnson,
 Executive Vice President, Wildlife Habitat Council

 The Wildlife habitat Council (WHC) was established in 1988.  Our
 main objective is to work with  companies and Federal and State
 agencies to  increase wildlife habitat through improvement of
 marginal or  unused portions of  property.  To date, WHC has
 assisted its members to plan wildlife enhancement opportunities
 at more than 750 facilities.  These programs encompass more than
 1.5 million  acres.  The WHC works with and encourages industry to
 work with WHC on sites involving  RCRA and Superfund program
 cleanups.  WHC believes it is possible to achieve acceptable risk
 levels.  WHC focuses on results and innovation.  Two cleanup
 sites that WHC has provided assistance to were the
 Bridgestone/Firestone Woodlawn  Landfill in Cecil County, Maryland
 and the Lime Lakes project at PPG in Barberton, Ohio.  The PPG
 Barberton site consisted of six above ground waste impoundments
 containing more than 33 million metric tons of lime wastes.
 Initial cost estimates indicated  remediation would take more than
 fifty years  to complete at a cost of more than $100 million.  The
 final decision was to use land  treatment and ecological
 enhancements where sewerage sludge was used to amend the lime
 wastes to produce a soil that sustained a vegetative cover
 stimulating wildlife habitation.

 Benefits to  industry include enhanced wildlife habitat,  increased
 employee morale and productivity,  better community relations,
maintenance cost savings and improved relationships with
governmental agencies.

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WHC will be holding a sequel conference to our June 2000
conference.  It will be held on July 10 and 11, 2001 in
Washington, D.C.

Performance-Based Orders, Jean Caufield, Remediation Group,
General Motors Corporation and Gerald Phillips, Corrective Action
Process Manager, Region 5

Drawbacks of the traditional order were that it had an unlimited
scope of work, negotiation was a  lengthy process delaying
cleanups, the work was too detailed and focused on minutiae and
generated ill-will between the facility and government.

U.S. EPA's objectives to streamlining include less oversight and
more owner/operator response.   Achieving Environmental
Indicators are still a priority.

The positive features of the new  streamlined order include:
•    Enforceable deadlines, recourse for disputes and penalties
     stop accruing until U.S. EPA notifies.
•    The facility has more responsibility.
•    Innovative technologies are welcomed.
•    It features a risk basis for remediation.
•    Reduced time in completing the cleanup is achieved due to
     less review time.

The streamlined order has the following key legal provisions:
•    Delay of one year for dispute resolution proceedings to
     allow for negotiation between the project managers.
•    Feature the same work products but the process is different:
     There is a team approach,  steps are eliminated,  the team
     meets in lieu of approvals.
•    The order requires two meetings per year.

Results:
•    The facility and the Agency are working more informally
     (team approach to work product review).   It has  eliminated
     detailed review of planning documents.
•    The facility seeks EPA approval even when not required by
     the order for comfort.
•    EPA has been responsive to requests for meetings which has
     helped with coordination with TSCA.
•    The speed of the process has increased dramatically.
•    All of General Motors Corporation's facilities are on
     schedule.

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Voluntary Agreements, Hak Cho, Chief, Corrective Action Section,
Waste Management Branch, U.S. EPA, Region 5 and Monica Satrape,
Environmental Action Manager, Hoover Company

Hak Cho:

A voluntary agreement is performance-based.  There is a minimized
oversight involvement by U.S. EPA.  The owner/operator does not
have to wait for formal U.S. EPA approval to begin the cleanup.
Key points that are noted in the agreement are Environmental
Indicators  (CA725 - human health and CA750 - groundwater) and the
final remedy.  The voluntary agreement is a non-enforceable
document, there are no penalties and either party can terminate
the agreement with or without cause.  The goal is to achieve
Environmental Indicator determinations and to achieve final site-
wide cleanup.  Enhanced public participation is required and is
critical to the process. The facility must submit and maintain
all documentation required.  The facility is required to act in a
timely manner.  There are currently six voluntary agreements
signed in Region 5.

Monica Satrape:

The facility (Hoover Company) is in the middle of a small town
(North Canton,  Ohio).  Closure issues were addressed by the Ohio
Environmental Protection Agency (OEPA).  OEPA did not have the
resources to address corrective action issues.  Hoover Company
chose a voluntary agreement because there was trust and a sense
of partnership and the company is concerned with the people and
the community.   Hoover Company wanted a shorter process than with
the traditional Corrective Action Order.  Hoover Company received
support from OEPA with an extension for their closure plan
execution.  The agreement required commitment from both U.S. EPA
and Hoover Company.  U.S. EPA increased the facility from a
medium priority to a high priority facility and Hoover Company
committed to the agreement.  Hoover Company plans to achieve
their El determinations by August 2001, which is 22 months after
the agreement was signed.  The final remedy is planned to be
finished by December of 2003.  The agreement features focused
deliverables.   Implementing the plan included starting at the
perimeter of the facility to address community concerns.   Hoover
Company has completed interim measures.  The on-site
investigation is currently ongoing.  Achieving El determinations
may be challenging because Hoover Company has only two
construction seasons.   This requires a constant strategy and
focus on the Els.   The voluntary agreement is more efficient
because it is less prescriptive and it has a maximum term of five
years.   Hoover Company is saving money with this process.   The
community is being supportive,  and Hoover Company gained the

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 support of a previously skeptical environmental group.

 Streamlining Under Existing Instruments.  Tammy Ohl,  Corrective
 Action Project Manager, Region 5; Roger Schumer, Project Manager.
 International Paper; Richard Menozzi,  Director of Environmental
 Remediation, U.S.  Steel; Gale Hruska,  Corrective Action Project
 Manager,  Region 5; and Douglas Bley,  Senior Projects Coordinator,
 Bethlehem Steel Company

 Tammy Ohl and Roger Schumer:

 U.S.  EPA  negotiated a new order for the remedy implementation.
 The  impetus  for streamlining  came from International Paper's
 upper management.   They separated the  Solid Waste Management
 Units by  priority  and set time goals.   They then planned what
 work  they could achieve in that time  span.   The preset  schedule
 made  the  process less formal.   All  decision-makers were present
 at all meetings to prevent delays needed  for consulting.
 They  completed the remedies on time.   The motivation for adhering
 to this process was that it is more efficient and it saves money.
 Fewer documents were necessary to prepare formally.   Documents
 were  conditionally approved rather  than going through a round  of
 revisions.   The catalyst for  action was schedule constraints,  the
 aggressive schedule meant that there wasn't  time to  argue, the
 atmosphere encouraged problem solving.  In  return, there was
 quick turnaround for reply.

 Tammy Qhl and  Richard Menozzi.  U.S. Steel Streamlining:

 Previous negotiations  were "stop  and go." There was  an attempt
 to develop a MOA and then to modify the existing order.   Neither
 option  was achieved.   US Steel agreed  to  set  a  schedule to
 expedite work  at the site.

 Pitfalls of the  negotiations:   The  current order may  have already
 had the flexibility required,  if  both  parties agreed  on the
 goals,  the order can be  amended.  If the  parties  disagree, no
 progress will be made  regardless  of the type  of  order.   If we
 intend  to renegotiate  an order, go  on  a parallel  track  with the
 old order to maintain progress.   The negotiations can be used to
 establish trust.  Both parties  should  align their objectives and
 understanding each  other's goals  is important.   Both parties
 should identify their "must haves."  Setting a schedule was also
 important.  Key decision-makers should be at all meetings so a
steering committee was established to include project managers
and management.

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Gale Hruska and Douglas Bley, Bethlehem Steel streamlining:

The facility had a permit for underground injection which
included corrective action.  The permit was not specific about
work to be performed.  It required development of a corrective
action plan, and implementation of that plan.  The permit is
about to expire.  The new permit will include the specifics and
flexibility that were missing.  Partnership is important to speed
up communications.  There must be a smooth transition from the
expiring permit with incorporation of past work,  such as the
Quality Assurance Project Plan.  The new instrument must
incorporate flexibility and be less process oriented.  There is a
citizen's advisory committee that is interested in the South
Landfill Area at the site.  The interest in this area makes it a
high priority and the facility wants to remediate it quickly.
The South Area will be addressed first.  The rest of the facility
will then be addressed to expedite the cleanup.

Property Reuse, David Kalet, Environmental Business Manager, BP
Amoco, Whiting Refinery and Keith West, Remediation Group,
General Motors Corporation

David Kalet:

Establish a vision for the future use of the property.  The
future use of the property will be market driven.  Identifying
the stakeholders (community and external market)  is important.
Identify the positive and negative attributes of the site.  What
aspects of the site will be attractive to outside sources and
investors.  Investors will be concerned about risks of
environmental liability.  Stakeholders  (users, community and
investors) will be more involved than the regulator agencies or
property owners.  Relevant user needs such as access, community
concerns such as creation of jobs,  taxbase and additional
greenspace.  The Brownfield's equivalent of a RCRA Conceptual
Site Model is the site master plan.

Keith West:

In smaller towns, the facility may be the major employer.
Assessment of impact to communities must be considered.
Redevelopment of the facility should be included in corrective
action to create jobs after the facility is gone.  The Corrective
Action process should mirror the business process.  The approach
was to create a redevelopment strategy.  This included discussing
future plans for the site with stakeholder including
decommissioning the buildings, performing the environmental site
assessment and, and prioritizing the environmental issues (do the
interim measures first,  and then address the larger problems at

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 the site) .

 From the beginning the development of a current conditions report
 that identifies  environmental  concerns at the site and sets the
 tone of  the remediation.   For  example: Centerpoint Business
 Campus which was formerly a General Motors Corporation truck
 plant.   One production building was decommissioned and scaled
 down to  an  office building. U.S.  EPA had identified 28 SWMUs,  GM
 found 43 more.   Interim measures  were used extensively to get the
 work started.  The new uses for the plant are:  GM offices,  GM
 plant, hotels, restaurants and commercial businesses.
 Keys for success are the  facility must be proactive and trust
 EPA.  Address  immediate issues with interim measures and finally,
 be  flexible.   Realize that the requirements of  the developer may
 be  more  stringent than EPA's requirements.

 Alternative Remedy (Phvtocover),  Martin Hamper, Principal
 Scientist:,  Arcadis,  Geraghty and Miller and Dr. David Tsao,
 Environmental  Research Engineer,  BP Amoco

 Martin Hamper:

 Phytoremediation provides containment and removal of water
 content  from a site  through evapotranspiration  and degradation  of
 the hazardous  waste  constituents.   A 25-year-old tree  can
 transpire 5 gallons  per day.   The  system needs  to be designed to
 meet  RCRA regulations.  A conservative design concept  was
 developed.   Water balance analysis  is crucial for success.   The
 benefits are that the regulatory  requirements can be met in a
 cost-effect manner.   The  phytocover provides greenspace.
 Operation and maintenance costs decrease over time.

 David Tsao:

 During the  mid-1990's,  properties  adjacent to the Mississippi
 River such  as BP  Amoco's  Closed Disposal Facility (CDF)  in  Wood
 River, Illinois,   were subjected to  inundation as  the river
 reached  500-year  flood  stages.  As  the waters eventually receded,
 the potentiometric gradient between the inside  and outside  of the
 CDF began to build.   Concerns  were  raised that  this  gradient
 could potentially push  the  contained hydrocarbons  (petroleum
 wastes in the form of hydrocarbon sludge)  through  the  containment
 wall  surrounding  the  CDF.    In  order to remedy this  situation, BP
 Amoco, in cooperation with  Illinois EPA,  investigated  the use of
 phytoremediation  for  its  abilities  to  evapotranspire significant
 volumes  of water   from the subsurface.   Initially, plant  screening
 experiments were  conducted  in  the greenhouse  using hydrocarbon
material  acquired from the  CDF.  These  experiments provided
 valuable  insights into the  potential species  that could be used

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to send their roots into the subsurface of the CDF, possibly
encounter hydrocarbons, survive, and transpire out the contained
moisture.  Both groundcover species as well as trees were tested.
Once a list of candidate species was developed, three-year field
trials were initiated which included planting several plots of
groundcover plants as well as stands of different tree species.
The groundcover plots were designed to intercept incoming
rainfall and prevent further infiltration into the subsurface
while the trees were designed to provide a slow pressure release
of the existing subsurface moisture.  When used in conjunction
with one another, the combined vegetative cover should lead to a
reduction in liquid levels v/ithin the CDF.  The site had ponding
due to flooding of the Mississippi River which was contained in
the site by a previously-installed slurry wall.  The pump and
treat option was not feasible due to the lack of an electric
utility.  Water would have to be collected and trucked away.  The
cost was estimated at around two million dollars.  The second
option was phytocover which would not require utility
connections.  The estimated cost was $250,000 to $500,000.

Day 2 - January 18, 2001

Opening Remarks, David Ullrich, Deputy Regional Administrator,
U.S. EPA, Region 5

This year and the next several years will continue our efforts to
improve the effectiveness of RCRA Corrective Action.  Yesterday
you heard about some new initiatives and some successful new
tools for program implementation.  Today we will have a chance to
get State perspectives on Corrective Action in their Breakout
sessions.  I support the streamlining efforts that have been
implemented and I encourage continued efforts to reform RCRA.
I want to stress that the Corrective Action program is key to
achieving both agency and regional priorities.   These include
reducing toxics, Brownfield redevelopment, protecting people at
risk, especially children and environmental justice communities
and protecting and restoring ecosystems.

I want to encourage you to provide your suggestions, insights and
experience today during this afternoon's open discussion.
I believe that it is through effective communication that
improvements in the way we all work together can be achieved.
We look forward to working with you and thank you for coming to
our second conference on RCRA Corrective Action.

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 State Breakout Sessions  -  Individual  States with  Industry

 Illinois

 Joe  Zlogar, URS Corporation  -  Industry  will encourage
 streamlining in Illinois.  Creative ideas, trust,  and
 communication are  needed.  Innovative programs  such  as  RAPs  and
 CAMU are also needed.  Perceived  barriers  include failed
 promises,  lack of  progress,  site  specifics in discussions  and
 State interpretation  of  U.S. EPA  guidance.

 Indiana

 Tom  Linson, Indiana Department  of Environmental Management -
 Indiana's  Risk Integrated  System  of Closure(RISC)  (consistent
 clean up standards) was  adopted last  Wednesday.   It  allows for
 more flexibility in their  cleanup program.  RCRA  reforms when
 permits and orders appropriate  (site  specific issues were
 discussed).  Other discussion  topics  during their break out
 session were the Corrective  Action Program organizational
 structure, Groundwater Rule  (currently  under development), land
 use  restrictions especially  industrial  closure  scenarios'  (more
 agency authority to enforce  and transition)(implementation of
 RCRA reforms).

 Michigan

 De Montgomery, Michigan  Department of Environmental  Quality
 (MDEQ) - Michigan's cleanup  criteria  is land use  risk based
 (1995), their Part 201 cleanup  program.  In November 2000, U.S.
 EPA  recognized Michigan's  cleanup standards and they now have a
 recognized Voluntary Action  Program with U.S. EPA.   MDEQ will be
 training their personnel on  the Part  201 cleanup  standards.
 Project managers will also adopt  streamlining.  MDEQ has
 formulated a strategy to complete Corrective Action  in  Michigan.
 Michigan identified "pilot"  issues -  waste identification  (listed
 waste classification versus  risk-based  cleanup criteria),
 bioavailability determination  (as opposed to more  traditional
 analytical procedures for  identification of risk-based  pathways),
 and  PCB Federal process  (Michigan wants to pursue  site  specific
 standards).  Waste classification listed vs. risk  based clean or
 still listed.  On May 1,  2001,  MDEQ will host a Corrective Action
 conference in Troy, Michigan with Michigan facilities.

Minnesota

Bruce Brott,  Minnesota Pollution Control Agency - There were no
facilities attending the conference from Minnesota.  Minnesota is
just about through with GPRA Corrective Action work.   GPRA

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necessitated the issuance of a few additional permits with CA
agreements to address all sites.

Ohio

Dave Sholtis, Ohio Environmental Protection Agency - Overview of
Corrective Action is at 85 GPRA baseline facilities, almost an
even split between U.S. EPA versus State lead  (work sharing is
ongoing).  Concerns are that there is a smooth transition from
U.S. EPA to State lead.  A lot of coordination will be required
as well as work sharing and getting the State involved early in
the transition process.  Perceived barriers to streamlining
include getting ideas across and focusing on new methods, putting
things in writing at State level.  Facilities with units subject
to closure rules sometimes want to be more flexible and move
ahead with site-wide cleanups, but run into authorization
problems.  Closure requirements can get in the way of site-wide
cleanup  (e.g., groundwater monitoring in cleanup areas to comply
with closure regulations).  State requirements' conflict with
Federal requirements.  Need to engage U.S. EPA on how to deal
with these types of scenarios.

Wisconsin

Mark Gordon, Wisconsin Department of Natural Resources - Pilot
projects expand liability exemption for government and lenders.
It expands EPA's area of contamination policy.  Also, request an
MOU with Region 5 to recognize Wisconsin's voluntary program.

Federal

Cultural changes are needed to convert from process-based to
performance-based Corrective Action Program.  October 13, 2000,
Region 5 Guidance on performance-based Corrective Action is key
to implementation of these changes.  The Corrective Action
Program is in transition and we need to maintain the momentum of
the past few years.  We need to concentrate on useful data
collection at sites (only collect data that is needed).  Use an
iterative nature to collect data.  Paula Williams, Region 5 is
working on risk-based guide (clean facility to risk point then
manage risk on a site specific basis).  For all programs in
Waste,  Pesticides and Toxics Division, involvement with all
stakeholders (community,  citizens and local officials)  as well as
facility. It is  important to identify stakeholders at the
beginning of the process.  Owner/operator cooperation and
communication (need a level of cooperation to develop a
partnership).   A strong partnership with the States is  also
critical.  Make  the process transparent.  Encourage innovation and
skip steps as appropriate.   Working on exit process and how clean

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 is clean.   The El determinations are a key step in the process,
 but we need to finish the cleanups and terminate the process
 before we  are really finished at a site.   We are currently
 revising the Exit strategy.   We still need to finish 162 GPRA
 facilities and 1,600 sites that haven't been started yet (non-
 GPRA facilities).  U.S.  EPA role in permit-driven Corrective
 Action will be replaced by States over time as we transition from
 Federal to State  lead.

 Superfund's sharing of  information (set up exchange of ideas and
 informal communication  between project managers).  Waste,
 Pesticides and Toxics Division wants to incorporate that among
 RCRA Corrective Action  Project Managers.

 U.S.  EPA needs to mirror the performance-based approach to
 encourage  States  to embrace  RCRA reforms  as well.  Headquarters
 assistance and support  will  help dealing  with non-cooperative
 sites.

 Corrective Action Awards,  Presented by Robert: Springer and
 Karl Bremer,  Chief,  Waste Management Branch,  Region 5

 Leadership Award   -  Hoover  Company,  accepted by Monica Satrape,
 Environmental Action Manager.   Recognized for outstanding
 facility leadership in  the Corrective Action Program and the
 development and implementation of a model Voluntary Agreement.

 Progress Award -   Argonne National Laboratory East,  accepted by
 Greg  Borland and  Angela  Harvey,  United States Department of
 Energy.  Recognized for  outstanding facility progress in the
 Corrective  Action Program in streamlining and completing work at
 its  facility.

 Special  State Commendation - State of Illinois,  Environmental
 Protection  Agency,  accepted  by William Child,  Chief,  Bureau  of
 Land.  Recognized for outstanding leadership  and support of
 streamlining  the  Corrective  Action Program and efforts  in
 completing  Environmental  Indicator determinations.

 Honorable Mentions  -  Industry:   Safety-Kleen  and State:  Michigan
 Department  of  Environmental  Quality.

 The New  RCRA  Reforms, Steve  Heare,  Director,  Permits  and State
 Programs Division, Office  of Solid Waste, U.S. EPA

 U.S. EPA Headquarters wants to thank  the  Region,  States  and
 facilities  for the progress achieved  in the Corrective Action
program.  Review of past reforms HPV  to GPRA,  stabilization  to El
determinations.  Environmental Indicator  determinations  are  our

-------
                               -14-

top priority.  2005 is the deadline imposed by GPRA.  We have
tools in place, regulations and policy to allow programs to take
off and meet these challenges.  The RCRA Corrective Program will
be different in the future.  It will be results not process that
will be stressed.  Creativity and innovation by the Regions,
States and facilities will be key.  RCRA Cleanup Reforms II
center around making cultural changes on how to do business.
Pilot innovative approaches.  Twenty-five pilot projects for 2001
is our goal.  We need to accelerate changes in culture in all
Regions.   It is important to have these kind of conferences
where the stakeholders are present.  Training, Corrective Action
workshops and partnering with industry to assist with training
are things we would like to see.  Internet web-based
communication also linked to State sites to foster information
exchange.  A summary pamphlet to summarize web information for
the public is another.  Indoor air issues and such related to El
determinations, connecting communities to clean ups (TOSC grants
to help communities understand problems and options for cleanup).
Brownfields and TSE targeted sites are issues that could hold
things up (chance to work thru barriers).  Outreach and training
(success of cleanup stories) should be communicated to
stakeholders.  Also, comf6rt letters to keep U.S. EPA out of the
loop.  Guidance and letter drafted and coming out soon.
The latest round of guidance coming out will be groundwater and
exit strategy.  Most likely no new national policy but clarity is
needed.  There are no current plans to issue perspective
purchaser policy/guidance.  The Region plans to pursuing
voluntary program MOUs to recognize State programs rather than
issuing "comfort letters" on a case by case basis.

Open Issues Discussion. Steve Heare, John Quarles and Gerald
Phillips (moderated by Robert Springer)

Ground rules for pilots have not yet been published.  The way
U.S. EPA currently envisions the process is to register them with
U.S. EPA Headquarters for information purposes (what it is, what
will it achieve and what we learned from the pilot).  No formal
approval will be required from Headquarters.  The pilot project
should demonstrate streamlining.  We are looking at one per State
as a good idea.  Headquarters would encourage the pursuit of a
pilot if it is something that makes sense and the company,  State
and Region agree on it.  Wisconsin is looking-at some sort of
lender liability protection pilot.  We need to use pilots to test
new concepts to see if something will really work.  The RCRA
Corrective Action Program is run on the basis of existing
guidance.  The challenge is to find flexibility that currently
exists and to take the general framework of the guidance and
successfully applying it in practice,  achieving results and
reporting out on successes.

-------
                                -15-

 Brownfields are part  of managing property.   Reuse  is part  of  the
 decision making process for  an  owner.  What  is  it  about
 Brownfields that RCRA Corrective Action project managers should
 be paying attention to?  The business process is the leading
 issue.  When is the corrective  action process done at a site?
 Property developers and managers want the  corrective action
 process to be out of  their way.  Does the  absence  of a proactive
 Brownfields program in the RCRA arena restrict  business activity?
 The answer is yes.  Companies will warehouse contaminated
 property and not use  it or sell it due to  the liability risks.
 It is a manageable burden for the company, but  a devastating
 burden to society because it is keeping that property out  of
 active use.  U.S. EPA needs  better tools and training to deal
 with this problem.

 Headquarters as part  of Reforms I committed  to  do  a handbook  of
 groundwater policies.  What  was envisioned was  a compilation  of
 existing policies.  Into the process it was  found  that it  was
 contrary to the kind  of things  they were trying to promote with
 the reforms.  It has  since been significantly rewritten and has
 been distributed for  comment.   Some of the comments dealt  with
 cleaning up a site to drinking  water standards  where the' existing
 use is industrial.  There needs to be some interim steps.  For
 example, the cleanup  level for  a facility  that  is  operating may
 not be the same once  it closes.  There needs to be continuing
 dialogue, perhaps in  some sort  of setting.   The current draft
 will be out in a couple of weeks for Region  and State review.

 Exit Strategy. George Hamper, Corrective Action Section,
 Enforcement and Compliance Assurance Branch, U.S. EPA, Region 5

 Region 5 is developing a Corrective Action Completion Guide to
 help Region 5 staff recognize the successful completion of RCRA
 corrective action work at any individual facility, and describe
 the situation accurately in  the Agency's information database,
 RCRAInfo.  A draft is  available for review and  comment.  It
 explains that the "Statement of Basis" and the  "Final Decision
 and Response to Comments" are the key documents for public
 participation and remedy selection.   The "Final Decision and
 Response to Comments"  for each corrective action project should
 explain what needs to be done to complete the corrective action
 work for that facility.  Recently,  a workgroup  has been formed to
 try to adapt the Corrective Action Completion Guide  for use by a
wider audience,  including industry representatives and the staff
of state agencies.   The goal  is to have the document finalized by
about the end of April 2001.

-------
                               -16-

Risk Management Strategy, Paula Williams, Toxicologist,
Corrective Action Section, Enforcement and Compliance Assurance
Branch, U.S. EPA, Region 5

Corrective action decisions are largely based on risk.  This
strategy is designed to unify risk managers' professional
judgement and to take a holistic approach to the process.  The
strategy includes considerations of the big picture  (i.e.,
wetlands, public interest, El determinations), data quality,
ecological concerns, and groundwater use concerns.  Using this
guidance, project managers will make site specific, risk-based
decisions that are consistent with other decisions made in the
Region.

Persistent Bioaccumulative and Toxic Chemical Reduction Strategy,
Greg Rudloff, Corrective Action Project Manager, Corrective
Action Section, Waste Management Branch, U.S. EPA, Region 5

My discussion will be about PBT pollutants and what they are.
They are bioaccumulate in the food chain.  They are toxic and
pose risks to human health and ecosystems.  Examples include the
following chemicals: cadmium, lead, mercury, PAHs,
dioxins/furans, pentachlorophenol, heptachlor, chlorobenzene.
The GPRA goal is by 2005 to reduce by 50% of PBT chemicals as
compared with a baseline year of 1991.  Recovering PBT chemicals
that have been released into environment is a key component of
the strategy.   The RCRA program plans to track and document
these chemicals at ten U.S. EPA lead sites.

Performance Based Guide, Gerald Phillips

The Region's Performance-based Corrective Action Guide became
effective in October 2000.  The purpose of the Guide is to
provide a summary of the philosophy behind the Region's efforts
to streamline RCRA Corrective Action.  The focus of the Guide is
on the use of flexibility and prioritized decision making to
ensure that the cleanup efforts take precedence over
administrative steps.  The Guide discusses the use of risk
management tools,  iterative data collection and decision making
as well as the role of the interested stakeholders.  The Guide is
intended to summarize the cultural changes being implemented by
the RCRA Corrective Action program in Region 5.

-------
                                -1-

                    Section II - Action Items

1.   Illinois Environmental Protection Agency will develop
     Ecosystems-Tiered Approach to Cleanup Objectives  (ECO-TACO)
     guidance.

2.   Michigan Department of Environmental Quality will hold a
     Corrective Action Conference in May 2001.  They have offered
     to share their efforts with the other States.

3.   Indiana Department of Environmental Management will finalize
     its State Risk Guidance  (RISC).

4.   Region 5 will send some staff to Indianapolis, Indiana for
     RISC training.

5.   Region 5 will send some staff to Lansing, Michigan for State
     Cleanup Standards "Part 201" training.

6.   Region 5 will work with the States to coordinate transition
     of permitted sites from Federal lead to State lead.

7.   Indiana Department of Environmental Management and Wisconsin
     Department of Natural Resources will request Memoranda of
     Understanding with Region 5 for acknowledgment of State
     Voluntary Cleanup Programs.

8.   Region 5 will further test streamlining pilot projects with
     States using approaches such as:
     a.  Achieving cleanup goals more effectively;
     b.  Improving stakeholder involvement; and
     c.  Enhancing the use of accountable State non-RCRA cleanup
     programs.

     Region 5 will develop as many as six pilots under RCRA
     Reforms II,  through collaboration with each State.

9.   Region 5 will provide more public access to information by
     publishing Environmental Indicator forms and site summaries
     on-line.

10.   Region 5 will examine common approaches for industry
     sectors.

11.   Stakeholders will resolve property reuse issues.

-------
                                -2-

12.  U.S. Environmental Protection Agency Headquarters will issue
     revised draft groundwater policy (further dialogue with
     stakeholders will be provided).

13.  Region 5 will begin to make property re-use,  such as
     Brownfields, part of the CA approach used by the Region.
     Links between the two efforts will include how Els fit,
     release of property, timing, exit.

14.  Region 5 has a workgroup developing a RCRA Corrective Action
     completion and exit plan.  Tied to this,  is consideration of
     alternative institutional controls, available at various
     levels of government.

15.  Region 5 is working to develop consistent risk guidance.

16.  Region 5 will pilot test measuring Persistent
     Bioaccumulative and Toxic chemical reductions at Federal
     lead sites.

-------
            Appendix 1 - Presentation Slides

Robert Springer - Welcome and Introductory  Remarks
(13 slides)
William Child - RCRA Corrective Action, A State's
Perspective  (10 slides)
Robert Johnson - Voluntary Efforts by the Private Sector
(39 slides)
Jean Caufield - Streamlined Corrective Action Order  (12
slides
Hak Cho - Voluntary Agreements  (4 slides)
Monica Satrape - Voluntary Agreements  (22 slides)
Richard Menozzi - Streamlining  (U.S. Steel)(1 slide)
Douglas Bley - Streamlining  (Bethlehem Steel)(8 slides)
David Kalet - Property Reuse  (19 Slides)
Keith West - Property Reuse  (47 slides)
Martin Hamper - Phyto-Cover at a RCRA Site  (23 slides)
David Tsao - Phytoremediation at Wood River  (25 slides)
George Hamper - Exit Strategy (2 slides)
Paula Williams - Risk Management Strategy  (2 slides)
Gregory Rudloff - PBT Strategy  (7 Slides)

-------
Welcome and  Introductory Remarks

           presentation by

      Robert Springer, Director
Waste, Pesticides and Toxics Division
         U.S. EPA,  Region  5

-------

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Streamlining Under Existing  Instruments

              presentation by

              . Richard Menozzi
    Director of Environmental Remediation
                 U.S. Steel

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     CORRECTIVE ACTION - U.S.STEEL GARY WORKS
                     OVERVIEW
• 3008 (h) Order: signed                      May 1998

• Current Conditions Report: Submitted         January 1997
                           Revised            February 1999

• Facility Wide RFI Workplan:  Submitted        July 1999
                  Response to Comments        December 2000

 • Environmental Setting:
    •  4000 acre site
    •  7 miles long x Imile wide
    •  Operational for nearly 100 years
    •  RFA identified nearly 500 SWMU's
    •  CCR identified 251 SWMU's and 42 AOC's
    •  3 Interim Status Hazardous Waste Units
    •  RFI identified 10 SWMA's & 3 Facility Wide Investigations

 • Completed 2nd round of Groundwater sampling and analysis
  at 55 perimeter groundwater wells

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Streamlining at  Bethlehem Steel

          presentation by

            Douglas Bley
    Senior Projects  Coordinator
    Bethlehem Steel  Corporation

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                  UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
                                      REGIONS
                               230 SOUTH DEARBORN ST.
                               CHICAGO, ILLINOIS  60604
                                                 REPLY TO ATTENTION OF:

               UTC3EKGROUND INJECTION CONTROL PERMIT
              CLASS I HAZARDOUS PERMIT MODIFICATION
                                   X
 Permit Number:  IN-127-1W-0003   x     EPA ID Number:  IND0039113423

      Pursuant to the Underground Injection Control regulations of the
 United States Environmental Protection Agency codified at Title 40 of the
 Code of Federal Regulations, Parts 124, 144, 146, 147, and 148, Bethlehem
 Steel Corporation, Burns Harbor Plant, of Chesterton, Indiana is hereby
 authorized to operate a Class I injection well located at Indiana, Porter
 County,  T37N, R6W, Section 30, SE Quarter Section.

      The injection zone, or zone which will contain the hazardous
 constituents, for this well is the lower Eau Claire Formation and the Mt.
 Simon Sandstone.   Injection is permitted only into the lower Mt.  Simon
 Sandstone between the depths of 2730 and 4298 feet,  upon the express condition
 that the permittee meet the restrictions set forth herein.   The designated
 confining zone for this injection well is the upper Eau Claire Formation.

      All references to Title 40 of the Code for Federal Regulations are to all
 regulations that  are in effect on the date that this permit is effective.  The
 following attachments are incorporated into this permit:  A,  B, C,  D,  E,
 and F.

      This permit  is a modification of an existing permit which has an
 expiration date of nddnifgHt-,  October 30,  1990.   This modified permit shall
 become effective  on    U U I  _ f>  (8JtJ      and shall supersede the existing
 permit upon issuance.   This permit shall remain in full force and effect
 during the life of the permit, unless:   1)  the statutory provisions of Section
 3004 (f),  (g)  or (m)  of the  Resource Conservation and Recovery Act ban or
 otherwise condition the authorizations in this permit;  2) the Agency
 promulgates rules pursuant  to these Sections which withdraw or otherwise
 condition  the authorization in this permit; or 3)  this  permit is  otherwise
 revoked, terminated, modified or reissued pursuant to 40  CFR  144.39  or 144.40.

     This permit and the authorization to inject shall  expire at  midnight,
October 30,  1990, unless terminated.
                     -*i             	
     Signed this   O    day of   far^^ , 1990.
                                               Dale S. Bryson
                                               Director, Water Division
                                                                    Printed on Racyded Paoer

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                                     56
     SWMU -     resource  recovery or conservation of any solid waste (as

                defined in 40 CFR §261.2).  It includes any uni.t a£ the

                facility  from which hazardous, constituents might migrate,

                irrespective of whether the units were intended for the

               management of solid and/or hazardous wastes.

B.  Implementation of Corrective Action

The process of implementing Section 300.4(u) will  take place in three

stages,'with each stage consisting of several  specific steps,  as follows:

 1. Preliminary Assessment.   Assessment of confirming re-leases is  required
    for all permits issued after November 8,  1984.   If any of  the  requested
    information has been previously submitted  to  the Director, include
    the original source as a reference on the  copy  provided in the required
    report.  The permittee is  required to submit  the following information
    45  -(forty-five) days from the effective date  of the permit. Failure
    to  submit the required information or falsification!-of. arty submitted
    information is grounds for the termination of this permit  (40  CFR
    §144.40).   All information submitted trust be certified as required
   "by  40 CFR §144.32.


        a.     Topographic Maps  -  Provide niap(s)  showing  the facility  and a
              distance of 1,000 feet  around the property  line  at a scale of
              one inch equal to not more  than  200 feet.   In addition to
              showing the location  of the permitted  hazardous  waste
              facility and management unit;., the  permittee must  locate on
              the map each existing and former soltd waste management
              unit (SWMU), regardless  of  its permitting  status.

       b.     Description of Units  -   For ;ach SWMU,  provide a history of
              construction, including engileering drawings, foundations,
              materials  of construction,  dimensions,  capacity  and  ancillary
              systems.  Include location,  design» construction,, and description
              Of all  monitoring systems (air,  surface  water, ground water,
              etc.).   If  the SWMU  is  not  in use,  describe'  the  methods
              utilized to close the facility and  all  construction  related
              to  closure.

       c.     Description of Operation  -   For each SWMll, provide a  history
              of  the  unit s function  and  all of the wastes processed or

-------
               disposed of  at the  unit.   Include the hazardous waste,
               processed  or disposed  of,  the time frames of operation,  and
               quantities handled  during  those time frames.
        d.     Description  of Releases  -  For each SMW, describe an>y,_       .
               or potential  release originating at each SW4U.   IncTjwte the
               suspected  date of  release, the type o-f haziardouts vtasjte or
               hazardous  waste constituent, the quantity released-., the
               environmental media affected, the nature of- the  release and
               present migration, arvd the circumstances and- cause af the release.
               Provide any  available data which would quant-tfy the nature and
               extent of  any environmental contamination including the
               results of air, soil, surface and. ground, water samp:ling; and
               analysis.  Provide  any available data; which wou.ld. indicate that
               no releases  are present, if applicable.
2. Remedial Investigations and Corrective Action Plan Development.  If

hazardous wastes or constituents have been released, no later than six

(6) months after the effective date of this permit, the permittee shall

conduct remedial Investigations, develop a proposed corrective action

plan, and submit a report on the investigations to the Director

as follows:


          (a)  Site investigation, including but not limited to,

          hydrological data, both surface and sub-surface sampling,

          and identification of background prior to cantami nati on ;


          (b)   Remedial investigations by owner/operator to

          identify /characterize releases;


          (c)   Develop an appropriate proposed corrective .action plan

          and  cost estimate; and


          (d)   Provide a financial  assurance  mechanism to cover the cost of

          implementing the corrective action  plan.

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                                    5 8                    ' A '••  " WL-^^ rlO Q'!>3
 3.  Corrective Action Plan Implementation.   Within thirty-six (36) months

 after the  Director's approval, the permittee sha)l  iiapTefaeifrt th
                                                                  *•»
 action plan as follows:

  *
           (a)  6 months  after approval  - Complete eng-ineering design;

           (b)  6 months  after approval  - Prepare  contract documents and

           award construction bids  or equivalent in-hou.s.e, action.

           (c) 18 months  after approval- Complete  corrective, act-ton  p.lan

C.  Permit  Modification

The Director  may modify  this permit  to include additonal  requirements or

modify the  Schedule  of Compliance  as  appropriate  in accordance with 40 CR?

§270.41 and Section  212  of HSW.   If major,permit modification  fs receded,

USEPA will  publish a  public  notice and allow for  pubTfc  review  and  comment.

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                                             Table 2
                                       Summary of Phase 2
                       Bethlehem Steel Corporation, Burns Harbor Division
     Investigation Area
                                                       Phase 2 Activities
IA 1
Wastewater   pump   station
No. 2 surface impoundment
                            (1)  Collect 2 upgradient hydropunch samples to confirm that  there are no
                            upgradient sources of benzene

                            (2) Install downgradient monitoring well and sample for benzene quarterly for
                            one year

                            (3) Sample storm ditch and Outfall quarterly for benzene to verify no off-site
                            discharge.

                            (4) Perform a risk analysis using data obtained in Phases 1 and 2 to document
                            no risk to human health or the environment based on site-specific industrial
                            exposures and potential for off-site migration.	
IA3
Rectangular and circular tar
impoundments
                            (1)  Perform voluntary corrective measure

                            (2)  Install 3 new groundwater monitoring wells

                            (3)  Perform quarterly  groundwater  monitoring for  one year  to show
                            effectiveness of corrective measure.

                            (4) Perform a risk analysis as described for IA 1, above.
                            \ -_/_ ______ 	 _	 ~	"*   _ —	     ~._—~------- -~_.._   —           	  	      	
                            (1) Re-sample existing wells 5-OW-3 and 5-P-2 quarterly for one year for
                            benzene

                            (2) Perform a risk analysis as described for IA 1, above.	
IA5/7
Cokemaking by-products
recovery area
IA12
COG collection container
                            (1) Install one monitoring well immediately downgradient

                            (2) Perform quarterly groundwater monitoring for benzene for one year.

                            (3) Perform a risk analysis as described for IA 1, above.	
IA15
COG collection container
                            (1) Install one monitoring well immediately downgradient

                            (2) Perform quarterly groundwater monitoring for benzene for one year.

                            (3) Perform a risk analysis as described for IA 1, above.
IA27
COG collection container
                            (1) Install one monitoring well immediately downgradient

                            (2)  Perform  quarterly   groundwater   monitoring   for   benzene   and
                            benzo(a)pyrene for one year.

                            (3) Perform a risk analysis as described for IA 1, above.
IA30
COG collection container
                            (1) Install one monitoring well immediately downgradient

                            (2) Perform quarterly groundwater monitoring for benzene and toluene for
                            one year.

                            (3) Perform a risk analysis as described for IA 1, above.
                            (I) Perform quarterly sampling for one year in each area of potential off-site
                            migration (discharge channel, 001 outfall, and harbor)

                            (2) Perform a risk analysis as described for IA 1, above.	
Dibenz[a,h]anthracene Study

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       Property Reuse

       presentation by

         David Kalet
Environmental  Business Manager
  BP Amoco,  Whiting  Refinery

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              Exit Strategy

             presentation by

           George Hamper, Chief
         Corrective Acton Section
Enforcement and Compliance Assurance Branch
            U.S. EPA, Region 5

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  Corrective Action Completion Guide
                    Decision  Tree
 Is it likely that
  hazardous
constituents have
been released to
 e environmen
                                                  Send Exit letter #1
                                                   and enter CA070
                                                  NO, CA725 YE and
                                                     CA750 YE
  Did all of the
releases originate
 from regulated
 T/S/D units that
 are subject to
  CRA closure
                           Enter CA070 NO
                            and direct the
                           owner/operator to
                           complete RCRA
                               closure
Was RCRA
  closure
successfully
completed?
    Is the
 owner/operator
  bankrupt or
  recalcitrant?
                                                 Refer the facility to
                                                 CERCLA and enter
                                                    CA210 SF
                       Impose a RCRA
                           Facility
                         Investigation
                          (CA100)
Has the nature and
  extent of the
  contamination
been determined?
                       Figure 1

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                                Figure  1  (Continued)
 Would the contamination pose
  any human health risk if the
  land use was residential, or
  any unacceptable ecological
 risk, or does the groundwater
  quality need to be restored?
       Select "No
       Further Action"
       Remedy
           Send Exit Letter
            #2 and enter
           CA999, CA725
           YE and CA750
                YE
              (any 1)
       Have all current
      human health risks
       and migration of
        contaminated
      groundwater been
         controlled?
    Enter CA725YE
     and CA750YE
 Select remedy to abate future
human health risks, unacceptable
  ecological risks, and restore
     groundwater quality.
  Enter CA550 upon completion
  of construction of the remedy
     Monitor operation and
      maintenance of the
           remedy
 teve the Final"
   Decision
   cleanup
objectives been
  achieved?
Yes
          Send Exit Letter #3
           and enter CA999

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       Risk Management  Strategy

              presentation by

       Paula Williams,  Toxicologist
         Corrective Acton Section
Enforcement and  Compliance Assurance Branch
            U.S. EPA,  Region  5

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Introduction
*•  Risk assessment is the primary tool used to direct
    remedy selection.

•#•  EPA policy established the continuum for risk
    managers to work with, such as the cancer risk range
    of 10-4tolO-6

&  Risk managers apply their professional judgement to
    each case to arrive at a final remedy decision.

^  The purpose of this guidance is to unify the thinking
    of the project managers and unify their professional
    judgement, therefore ensuring consistent risk-based
    remedy selections.

The big picture
^  Primary remedy driver
        wetlands
        large amount of public interest
        Environmental Indicator determination

*  Influence of other statutes or programs
        TSCA
        UST

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The art of the risk assessment
%•  Confidence level for the sampling data
        Sufficient samples
        Use of historic data
        Background levels
        Data gaps

^  Confidence and certainty in the risk assessment
        Calculations are based on sampling results
        Reasonably conservative assumptions if land use
            is not certain.  A conservative assessment is
            flexible.
        If risk assessment is not reliable or conservative,
            a more conservative remedy may be merited

^  Use of the NCP cancer risk range
        Confidence in risk estimations will influence
            final acceptable estimated risk within the
            range

Other corrective action goals
    Ecological receptors or sensitive ecosystems
    Reduction of toxicity, mobility or volume of wastes,
       especially for PBTs
    Groundwater restoration
        "Maximal beneficial use"

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                  PBT Strategy

                 presentation by

Gregory Rudloff,  Correction Action  Project Manager
            Corrective Action Section
             Waste Management Branch
                U.S.  EPA,  Region  5

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             Appendix 2 - Meeting Handouts

October 13, 2000, Guide to Performance-Based RCRA Corrective
Action

January 2001, RCRA Cleanup Reforms II

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      ^£0 sr47.               UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
      *        * .                                     REGION  5
                z                         Waste, Pesticides and Toxics Division
                ?                    77 W. Jackson Blvd, Chicago, Illinois 60604-3590
   Date:       October 13, 2000

     To:       RCRA Corrective Action Staff

   From:      Robert Springer, Director (signed)
              Waste, Pesticides and Toxics Division

 Subject:     Guide to Performance-Based RCRA Corrective Action

 Introduction

 The Waste, Pesticides and Toxics Division (WPTD) initiated an effort to streamline and accelerate
 RCRA corrective action in October 1998. We had concluded that corrective action should be efficient
 and less process-driven.  WPTD has implemented a series of changes and intends to continue its
 streamlining initiative.  This  initiative has had several successes and has led us to an understanding of
 how corrective action can be made more efficient. Our goal is to ensure that facilities control risks to
 human health and the environment as quickly and effectively as possible, and continue the effort through
 the completion of corrective  action.  The purpose of this Guide is to express a set of implementation
 principles that will form the foundation for all of our RCRA corrective action decisions.

 This Guide builds on the foundation of program flexibility that has been encouraged through national
 guidance and the 1999 RCRA Reforms. The RCRA corrective action program has matured to the point
 where review and approval of implementation  activities conducted by many facility owner/operators
 (O/O) can be made simpler and more efficient.  The U.S. Environmental Protection Agency Region 5
 (Agency) has provided extensive policy and guidance to enable the regulated community to understand
 what level of implementation performance is  expected.  For selected facilities, we believe formal
 Agency involvement can be limited to a few crucial decision points. By reducing time-consuming and
 repetitive formal document reviews, revisions and approvals, the Agency and O/Os can devote more
 resources to improve communications and to expedite corrective action.

 A performance-based approach will provide more implementation  flexibility throughout corrective
 action. This approach should also foster an effective professional working relationship between WPTD,
 the O/O  and their consultant(s).  We are confident  that a performance-based approach to RCRA
 corrective action, using real time practical decision making, will not only reduce the time needed to
 complete corrective action, but also will increase the  efficiency and cost effectiveness of the overall
 RCRA corrective action process.

Elements of the Performance-Based Process

To date our efforts to evaluate corrective action have identified certain essential elements:

       •      Development  of a concise history and status report  for the facility in the form  of a

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                                            -2-

              Current Conditions Report

       •      Development of a Conceptual  Site Model, that is a constantly  evolving working
              hypothesis of potential sources, risks, data needs, cleanup objectives and corrective action
              solutions that can be used as an effective implementation tool

       •      Information and Data Collection Planning based on the above two elements, in order to
              focus the overall corrective action effort on those releases that may pose an unacceptable
              risk to human health and the environment

       •      Facility Investigation to confirm what is known about a facility and to fill data gaps

       •      Development and implementation of appropriate Interim Measures while final Corrective
              Measures are established

       •      Evaluation of Corrective Measures and Selection of a remedy to address the identified
              environmental risks presented by the facility

       •      Implementation of the Selected Corrective Measure(s) including appropriate operation
              and maintenance of the remedy

       •      Confirmation and certification of successful completion of RCRA corrective action

We have determined that, even though all of these essential elements must be completed, four regulatory
decision points are central to satisfactory completion of RCRA corrective action. These decision points
are:

       •      Determination that the  two  Government Performance and  Results  Act  (GPRA)
              Environmental Indicators have been successfully achieved

       •      Evaluation of Corrective  measure alternatives and selection of the Final Corrective
              Measure(s)

       •      Planning and scheduling implementation of the selected Corrective Measure(s)

       •      Determination and certification of successful completion of the RCRA corrective action

In order to ensure these four corrective action decisions have a solid foundation, Agency or state staff
must have confidence in the quantity and quality of the data collected, and in particular, that sampling
and data analysis under the essential element of facility investigation have been conducted with adequate
quality assurance. WPTD intends, except as discussed in the Selection Criteria Section below, to limit
its formal decision making to the above four decision points. It is therefore critical that the O/O ensure
that the data provided to the Agency meets the WPTD QA/QC Policy.  Corrective measure alternatives
must be based on a thorough understanding of releases to the environment and any contaminant migration
that may have occurred.  Because the Agency has transferred greater responsibility and flexibility to the
O/O by removing many of the traditional approval requirements, this understanding can best be achieved

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                                             -3-

through use of the conceptual site model and effective information exchange established through a
relationship built on trust and mutual respect.

Implementation of Corrective Action Elements

RCRA corrective action is primarily environmental risk management.  It is intended to identify and
confirm current and potential environmental risks, to gather data through facility investigation, and then
to select a remedy that will eliminate, to the extent possible, the hazards to human health and the
environment. Several important features of performance-based corrective action are cross-cutting in
nature and therefore affect all stages of the process. These features are:

       1.     Iterative Nature:  It must be  recognized that the various  elements  or  phases of
             corrective action should be implemented in an iterative manner. This is in contrast to
             the more traditional system which calls for a series of clearly defined steps that are often
             carried out in a rigid order.  Thus, for example,  under  the traditional system, a) all
             investigative work would be performed during the RCRA Facility Investigation (RFI)
             which often ends with a formal risk assessment, b) the process would move to the
             Corrective Measures Study (CMS), which in turn c) would lead to the selection of the
             entire facility remedy, d) then move to the design and construction of the remedy in the
             Corrective Measures Implementation (CMI) phase, and e)  any  Interim  Measures
             identified during the process would require formal proposal, design and approval.

             A performance-based approach recognizes that corrective action projects can benefit
             from more flexible implementation.  Corrective action  will be more efficient if the
             various steps are performed in an  iterative way, sometimes with overlapping process
             elements and time frames. For example, the development of a conceptual site model
             early in the process and the implementation of data collection activities based on this
             conceptual site model  is encouraged.  In addition, the performance-based process
             encourages the implementation of corrective measures as early in the process as
             possible. This may result in corrective measures being implemented at a portion of the
             facility while investigation is continuing at a different portion.   Likewise, some
             investigative tasks might be reserved until after the implementation of interim corrective
             measures in order to determine the need for further cleanup activity or to  verify the
             success of the interim  measure.   In order to make appropriate corrective measures
             decisions at any one time, we  have determined that data should be gathered and
             decisions made on an iterative basis to allow flexibility, encourage prompt action and
             select practical solutions.

      2.     Risk Based Decision-Making:  Performing risk analysis is by its  nature an iterative
             process and an example of how corrective action can benefit from fully incorporating
             these  principles. A deliberate objective  of risk-based decision-making is to bring
             forward,  as appropriate, risk criteria decisions in order to include them as early as
             possible  in the corrective action  process. This practice would enable the project
             manager, who functions as the risk manager, to make initial risk  criteria decisions based
             on data and information available at the outset in order to guide the nature and extent
             of the investigative work.  Communication among the risk manager, risk assessor, and

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                                      -4-

       other interested stakeholders must occur throughout the corrective action effort. Risk
       analysis and risk management decisions will  be conducted throughout the entire
       corrective action effort. Therefore,  a traditional risk assessment, in the sense  of
       preparing a single comprehensive document that once and for all provides a full risk
       analysis to be used in making all the final remedy decisions, may not be necessary.
       Making risk criteria decisions early, and as quickly as the data allow for an appropriate
       choice, will help to focus the corrective action effort on those factors that present the
       potential threat(s) to human health and the environment.

3.     Data Collection: The collection of information and data, whether in an initial survey
       to prepare a conceptual site model or in a formal investigation to evaluate the conceptual
       site model, should be carried out in stages that most efficiently match the conditions and
       needs of each particular facility. The planning and performance of investigative work
       commonly occurs as in a series of actions, with each phase of the investigation building
       upon and governed by the results of earlier phases. The facility investigation should be
       organized to carry out a series of often separate efforts that best fits the conditions of the
       facility and  ensures that an adequate facility-wide investigation is completed.  The
       investigation of  one portion of a facility should  not necessarily wait for the rest of the
       current phase of an investigation to be completed for the whole facility. Data collection
       should proceed to a logical conclusion for each portion of the facility.  It is critical for
       data collection to be focused on those factors that present, or have the potential  to
       present, a risk. Risk management decision-making needs should be the primary driver
       for all data collection. Therefore, only data that  support the corrective action decision
       process should be collected.

       The  greatest opportunities to achieve the benefits of streamlining RCRA corrective
       action occur during the facility investigation, in particular, in the area of data collection.
       In many instances it is not necessary or beneficial to exercise all of the prescriptive
       Agency oversight  called for in existing permits and orders for the investigation  of
       contamination at a facility. By balancing Agency oversight activities with an increased
       responsibility on the O/O to do the data collection and to do it right, WPTD believes it
       is possible to expedite cleanups and focus limited Agency resources.

4.     Stakeholder involvement: Stakeholders should be identified at the beginning of the
       corrective action process. Properly managed stakeholder involvement will address the
       Agency's public participation requirements and  enhance the relationship between the
       facility's O/O, the surrounding community and other individuals or groups that have  an
       interest in the corrective action.  Stakeholders should be involved throughout the
       process, with a communications plan that addresses the needs and circumstances of the
       stakeholders and O/O of the facility.  The communications plan should be modified  as
       needed to reflect developments that occur during the corrective action in order to ensure
       prompt and accurate information exchange.  Stakeholders in the performance-based
       process include not only representatives of the community surrounding the facility, but
       also regulatory agency representatives and others who may be impacted by the corrective
       action.

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                                             -5-

        5.      Owner/Operator responsibility: Successful implementation  of corrective action
               requires that an effective level of confidence and cooperation be established between the
               affected O/O's,   the regulatory  officials responsible for the facility, and other
               stakeholders.  One of the key assumptions implicit in this Guide is that the responsible
               O/Os have sufficient  knowledge, competence and  integrity to assume expanded
               responsibility and  the flexibility  to implement RCRA corrective action  without
               compromising the results.  The O/O's ability to implement corrective action with
               significantly reduced oversight depends on whether the ultimate standards that govern
               the effort are clearly established or can be effectively determined for the facility. On an
               iterative basis, the  O/O  should evaluate, investigate and remediate a contaminated
               facility in accordance with a functionally driven process and schedule appropriate to the
               facility conditions.

               WPTD recognizes that not all policy issues related to RCRA corrective action have been
               resolved.  We intend to continue our efforts  to resolve these remaining  issues.
               Nevertheless,  the key  to effective  performance-based corrective action is continued
               effort on the part of O/Os and regulatory officials to  establish practical solutions to
               implementation issues.

        6.      Transparent  and Definitive Process: It is critical that the corrective action decision
               process be  obvious to the point it is transparent and definitive with no hidden agendas.
               Determinations made by the O/O or by U.S. EPA should, whenever possible, provide
               closure to an issue. RCRA corrective action can be a lengthy process. Because GPRA
               Environmental Indicators determinations are based on current facility conditions, and
               can be modified to address changes in facility status, they provide an excellent interim
               decision stage in the corrective action process. The Indicators are achieved when the
               Agency determines that the facility no longer presents a current risk to human health and
               when migration of contaminated ground water is controlled. This interim success point
               will provide assurance that a facility presents no current environmental threat while the
               RCRA corrective action is completed.  A final RCRA corrective action completion
               determination is particularly important when the facility as a whole, or as determined
               by  the Agency, portions of the facility  have achieved the cleanup action levels
               established for the facility.    Similarly, if institutional controls are used as part of
               corrective action, those controls must be clear, effective and enforceable.

Selection Criteria for Performance-Based Corrective Action

WPTD has developed a performance-based model consent order and voluntary agreement.  We are
currently using these performance-based models to initiate corrective action at remaining facilities
subject to RCRA corrective action. However, we recognize that not all facilities subject to RCRA
corrective action will benefit from a change in process. In addition, not all facility O/Os have the
interest or capability to implement a performance-based approach. For these facilities a traditional
consent or other type of order will be utilized.

WPTD is also evaluating facilities that have already initiated corrective action under a traditional order
or permit issued by the  Agency to  determine which facilities could  benefit from a shift to  a

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                                            -6-

performance-based approach. In order to ensure O/Os have the knowledge, competence and other
factors necessary to effectively participate in this performance-based approach to corrective action,
WPTD  staff will evaluate each facility scheduled for  corrective action to determine the most
appropriate implementation mechanism. If identified by the Agency as a potential candidate for this
performance-based approach, the O/O of the facility will be contacted to discuss the option of a
streamlined  approach.   WPTD staff will then  recommend a mechanism to management for final
selection.

O/Os of a facility under a federal traditional order or permit who have an interest in switching to a
performance-based approach should contact their proj ect manager. The O/O must define for the project
manager why they feel corrective action at their facility would benefit from a change in approach.

 WPTD management will then select facilities where this performance-based approach could be used
based on appropriate, including criteria:

              •      The current status of the corrective action mechanism based on: a) how much of
                    the process has been completed, and b) how the change in approach would result
                    in implementation improvements.

              •      The implementation improvements that will result from the change in approach.

              •      The facility O/O's demonstration  of financial and technical capability to
                    implement a performance-based approach.

              •      The compliance and corrective action performance history of the facility' s O/O.

              •      The O/O's degree of commitment to expedite corrective action.
Conclusion

Effective implementation of a corrective action that promptly  addresses environmental concerns
requires the Agency to provide adequate tools for implementation.  We now have two approaches to
corrective action implementation:!) the traditional process and 2) the performance-based approach
outlined in this Guide. This Guide establishes an alternative to the traditional approach to corrective
action for those facilities administered by WPTD.  It also reinforces the direction of the RCRA
Corrective Action Reforms issued by OS WER Assistant Administrator Tim Fields in July 1999 to instill
greater flexibility and practicality in our overall implementation of RCRA corrective action.  We
recognize that program improvement is an ongoing effort. We intend to monitor this approach and to
modify it as appropriate in order to continue our efforts to streamline RCRA corrective action.
cc:     Steve Heare, OSW
       RCRA State Division Directors
       RCRA Regional Division Directors
       John Quarles, RCAP, Morgan, Lewis and Bockius

-------
                           United States Environmental
                           Protection Agency
Solid Waste and Emergency
Response (5305W)
EPA530-F-01-001
January 2001
httpVAwww.epa.gov/osw
                           Office of Solid Waste
       vc/EPA       RCRA  CLEANUP  REFORMS

                           Reforms II:  Fostering Creative Solutions

                           The U.S. Environmental Protection Agency (EPA) is implementing a second set of administrative
                           reforms to accelerate the cleanup of hazardous waste facilities regulated under the Resource
                           Conservation and Recovery A ct (RCRA). EPA 's 1 999 Reforms promoted faster, focused, more
                           flexible cleanups. The 2001 Reforms reinforce and build upon the 1999 Reforms and will pilot
                           innovative approaches, accelerate changes in culture, connect communities to cleanup, and
                           capitalize on redevelopment potential, while maintaining protection of human health and the
                           environment.
Why Is EPA Reforming the  RCRA

Corrective Action Program?

The goals for the RCRA Corrective Action program remain
very challenging. To more effectively meet these goals and
speed up the pace of cleanups, EPA introduced RCRA
Cleanup Reforms in 1999 and is implementing additional
Reforms in 2001. The 1999 and 2001 Reforms build upon
actions taken by EPA and the states in recent years to
accelerate cleanups. EPA believes mat the 1999 Reforms
remain central to successful implementation of the program.
The 1999 Reforms were designed to:

    •   Focus the program more effectively on achievement
       of environmental results, radier than fulfillment of
       steps in a bureaucratic process.

    •   Foster maximum use of program flexibility and
       practical approaches to achieve program goals.

    •   Enhance public access to cleanup information and
       improve opportunity for public involvement in the
       cleanup process.

The 1999 Reforms set the near-term focus of the program
on attainment of the two Environmental Indicators and
established an environment for program implementors to be
innovative and results-oriented. The 1999 Reforms have
successfully led the program toward faster, focused, more flexible
cleanups. An example of progress since 1997 is that the
number of RCRA cleanup facilities meeting both
Environmental Indicators has increased from 47 to 504.
  What are the Goals of the RCRA Corrective Action
  Program?
  EPA has established two fleae-term goals, leaned
  "Environmental Indicators," for the RCRA Corrective Action
  ptogtaou These goals, undei the Govftttiment Petfottnance and
  Results Act {GPKA}, a*e that by 2005, jfee states aod EPA wiE
  verify wd4ocnmeat t)pat 95 percent ofti^s 1^4 RCRA
  cleanup facilities under GPRA focus wfll have "current human
  exgoiBites under control," and 70 percent of these fadliJes wfll
  have "raigratJott of coatamiaated gtoundwater uadet conttol."
  TJbs J0ag-te«s gwdof Su; pregpiMs 
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    •   Pilot innovative approaches.

    •   Accelerate changes in culture.

    •   Connect communities to cleanups.

    •   Capitalize on redevelopment potential.

 The 2001 Reforms include just some of the innovative
 approaches that have been identified by program
 implementors and stakeholders.  EPA intends to continue
 work in other areas critical to meeting program goals. In
 particular, we seek to: continue a dialogue with interested
 parties on groundwater cleanup and other issues relating to
 final cleanup; provide guidance for cleanup at facilities with
 limited resources to pay for cleanup; and, continue to work
 with federally-owned facilities  to meet their Environmental
 Indicator goals.  Similarly, we encourage program
 implementors and stakeholders to use approaches that
 improve the program yet are not specifically included in the
 RCRA Cleanup Reforms.

 I. Pilot innovative approaches.

 The RCRA Cleanup Reforms Pilot Program will support
 state and EPA Regional Offices in dieir efforts to use
innovative, results-orientated and protective approaches to
 speed achievement of Environmental Indicator goals and
 final cleanup. Stakeholders are encouraged to contact state
and EPA Regional Offices with their pilot ideas.

EPA has set a target of 25 pilot projects to be launched in
2001.  EPA expects at least one pilot project in each EPA
Region, administered by the state or EPA.  EPA will
showcase pilot projects to share successes and lessons
learned and to promote use of similar approaches at other
facilities. EPA recommends that stakeholders consider pilot
projects in one or more areas.  For example, pilots that:

    —   Achieve program goals most effectively at
        companies with multiple facilities
    —   Improve stakeholder involvement and
        communication to resolve issues where cleanup
        progress is slow
    -   Use site characterization technologies or strategies
        that efficiently assess Environmental Indicators
    -   Enhance the use of protective and accountable state
       non-RCRA Cleanup programs to achieve program
       goals
    —   Establish EPA Regional  or state "corrective action
       expediters" to focus on cleanups that are stalled or
       delayed
    -   Expedite achievement of program goals at
       federally-owned facilities
    -   Use Superfund or emergency authorities at RCRA
       sites for bankrupt or unwilling facilities
 What is the RCRA Corrective Action Program?

 In 1980, when die RCRA law and regulations went into effect,
 thousands of facilities became subject to hazardous waste
 maaageaaeot teguMoas- These regulations have helped ensure
 that hazardous waste generated from industrial operations is
 properly managed and does not contribute to a future
 generation of toxic waste sites. However, many of these
 facilities had soil and groundwater cotttartuflatioa resulting
 from their waste management practices prior to 1980- The
 RCRA Corrective Action program addresses cleanup of
 contamination at these operating industrial facilities,

 Who Runs the RCRA Corrective Action Program?

 The RCRA Corrective Action program is tutthy both EPA and
 the states, witfe 38 states and territories authorized to        :
 implement the program. Corrective action is conducted under
 RCRA .permits, orders and other approaches.
II. Accelerate changes in culture.

EPA will help program implementors and stakeholders
accelerate changes in culture in how they implement the
program by: focusing on results over process; encouraging
frequent, informal communication among stakeholders;
partnering in training; promoting methods of information
exchange; and, using new approaches to meet
Environmental Indicator and long-term cleanup goals.  EPA
will:

*   Promote nationwide dialogue among program impkmentors and
    stakeholders on RCRA cleanups.  EPA Regional Offices will
    work with states in an effort to hold at least one meeting
    in 2001 in each EPA Region, open to all stakeholders
    who wish to interact, provide input, or learn more about
    the RCRA Corrective Action program.  Discussion
    topics could cover local, regional or national topics
    relevant to corrective action.
    Conduct targeted training in partnership with program
    implementors and stakeholders.  EPA will work with
    interested parties to deliver targeted training, depending
    upon the needs of those requesting the training and
    available resources. Training topics could cover, for
    example: innovative technical and administrative
    approaches to cleanup; success stories and lessons
    learned from implementation of the 1999  Cleanup
    Reforms; Corrective Action program basics; and use of
    performance-based approaches to corrective action.

    Use web-based communication to share successes and lessons
    learned and promote innovative approaches. EPA will support
    the establishment of a web-based interactive tool to
    promote the sharing of successes and lessons learned
    and to provide for frequent exchange of ideas among all

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    stakeholders on any corrective action topic, including
    those that are technical, policy-oriented or site-speci6c.

    Overcome barriers to achieving Environmental Indicators. EPA
    will clarify the relationship between Environmental
    Indicators and final cleanups, and how Environmental
    Indicators can be met within the context of existing
    orders and permits. EPA will answer "Frequently Asked
    Questions" about Environmental Indicators, and issue
    technical guidance on ways to assess the impacts of
    contaminated groundwater on surface water and indoor
    air quality. In addition, EPA will demonstrate new uses
    of enforcement tools to achieve Environmental
    Indicators.
  Focus on Results

  The JtC&A Qeaaup Reforms foster creative, practical, resales-
  based approaches to corrective action. la die field, this means:

  «   TfrwiMngiaikmloversight, E&ttinateadministrativeor
     technical steps where not needed to assure effective
     performance.
  *   Using bolistit approaches. Evaluate facilities for overall risk
     and apply laoBty-wide corrective: actioa measures.
  »   Exerstfingprv&durafj&xtUStjr. Emphasize results over
     mechanistic process steps and eliminate unproductive
     activities,
  -   Stttittgpttfiamnxx standards. Establish clear protective
     standards the owner/operator must fuJfiEto complete
     corrective action.               .    .
  *   I'argtiitgdatatalketion. Examine actual conditioas at each
     corrective action decisions.
 III.  Connect communities to cleanups.

 EPA will provide the public with more effective access to
 cleanup information. EPA seeks to increase public interest
 in and awareness of cleanup activities, and to further
 enhance the public's ability to become more involved in
 decisions about cleanups in communities.  EPA will:

 •   Clarify principles and expectations for public involvement in
    corrective action cleanups.  EPA will set out general
   principles and expectations for providing the public with
    the opportunity to become involved at corrective action
    sites. EPA also will share examples of successful public
   involvement approaches that have been used at RCRA
   cleanup sites and lessons learned.

•  Increase support of Technical Outreach for Communities (TOSQ.
   The TOSC program provides communities with
   technical and educational assistance from universities on
   issues associated with cleanup of hazardous sites. EPA
   will provide resources to the TOSC program for
   community involvement at RCRA cleanup sites and
   advertise the availability of this  program.
•   Place Environmental Indicator evaluation forms and site
    summaries on EPA web sites. EPA will place
    Environmental Indicator evaluation forms and
    summaries of site cleanup activities of 1,714 RCRA
    facilities on the web sites of EPA Regional Offices. The
    evaluation forms and site summaries will provide readily
    available information on the status of cleanup at these
    sites.

•   Publicise and promote the use of readily accessible cleanup
    information sources. EPA will produce and distribute a
    pamphlet for the general public that explains how to
    access RCRA Corrective Action program information
    and site-specific cleanup information.


IV. Capitalize on redevelopment

potential.

EPA encourages program implementors and stakeholders to
capitalize on the redevelopment potential of RCRA cleanup
sites. Many of these sites are located in areas that are
attractive for redevelopment and are poised for community
revitalization. These factors can
motivate interested parties to pursue an expedited cleanup,
sometimes with additional resources. EPA will:

•   Initiate Additional RCRA Krownfields Pilots. EPA will
    launch 4-6 additional RCRA Brownfields pilot projects
    in 2001.  These pilots will be designed to showcase the
    flexibility of RCRA and the use of redevelopment
    potential to expedite or enhance cleanups. Pilot
    applicants could be program implementors or
    stakeholders. Pilot participants also benefit from
    technical assistance. Limited funding may become
    available for public meetings and related activities.

•   Initiate the Targeted Site Effort (TSE) Program to spur cleanup
    at RCRA sites with significant redevelopment/reuse potential.
    EPA will ask each Regional Office to identify two sites
    for the TSE in 2001. The TSE program will apply to
    sites that have significant redevelopment/reuse potential,
    and require a limited amount of extra EPA support to
    help spur cleanup. The TSE program will provide
    participants with focused attention, access to RCRA
    brownfields expertise, and limited funding for EPA to
    conduct public meetings and related activities.

•    Provide training and outreach to program implementors on using
    redevelopment potential to meet program goals. EPA will
    provide training and outreach to program implementors
    and stakeholders to promote the environmental and
    community benefits that can be gained by integrating
    brownfields redevelopment opportunities and RCRA
    facility cleanups.

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•  Promote cleanup and redevelopment with RCRA
   "Comfort/Status" Letters. "Comfort/status" letters
   provide information regarding EPA's intent to exercise
   its RCRA corrective action response and enforcement
   authorities at a cleanup site. EPA will issue examples of
   letters that have been used to spur cleanup and
   redevelopment at RCRA facilities.


How Will EPA  Measure the  Results

of the  Reforms?

Measuring and recording the results of the RCRA Cleanup
Reforms is a priority for EPA and the states to ensure
continued improvement of the Corrective Action program.
EPA will measure progress in putting the reforms into
practice. EPA recognizes program implementors are using
new approaches that may or may not be highlighted in the
Cleanup Reforms, and will measure progress under these
approaches as well.  While the ultimate goal of the
Corrective Action program is to achieve final cleanups, EPA
will continue to measure the near-term success of the
program against its Environmental Indicator goals for
controlling human exposure and migration of contaminated
groundwater.                 v ,


How Will EPA  Involve

Stakeholders in  Implementing the

Reforms?

EPA will provide periodic updates on the RCRA Cleanup
Reforms and solicit input from stakeholders through several
means, including focus meetings, Federal Register notices,
the RCRA Corrective Action Newsletter, Internet postings,
and press releases.

EPA seeks continuous feedback from all stakeholders on the
need for additional reforms beyond those already underway.
EPA values and appreciates the feedback and interest of all
stakeholders.  However, limited resources may not allow us
to respond individually. Based on stakeholder input and our
ongoing assessment of the program, we will continue to
refine and add to the RCRA Cleanup Reforms, as needed,
and will communicate program changes.

If you would like to provide written comments on the
RCRA Cleanup Reforms, please mail your comments to:
RCRA Information Center (5305W), U.S. Environmental
Protection Agency, Ariel Rios Building, 1200 Pennsylvania
Avenue, NW, Washington, DC, 20460-0002, or send an
email to the RCRA docket at rcra-docket@epa.gov. Please
include the following number on all correspondence, written
or e-mailed, to the RCRA Information Center: F-2001-CRII-
FFFFF.
For More Information

For information on corrective action cleanups, please visit
state and EPA Regional web sites, which can be linked via
the EPA corrective action web site at
http://www.epa.gov/correctiveaction. The EPA corrective
action web site has the latest and more detailed information
on the RCRA Cleanup Reforms.

If you have questions regarding the RCRA Cleanup
Reforms, please call the RCRA Hotline at 800-424-9346 or
TDD 800-553-7672, or visit their web site at
http://www.epa.gov/epaoswer/hotline/index.htm.

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