Lessons Learned
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   The Pacific Northwest Hazardous Waste Advisory Council's
  Approach to Regional Coordination and Policy Development
                  Prepared for U.S. EPA Region 10
                        February 1991

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                    LESSONS LEARNED






 THE PACIFIC NORTHWEST HAZARDOUS WASTE ADVISORY COUNCIL'S




APPROACH TO REGIONAL COORDINATION AND POLICY DEVELOPMENT
                        prepared by:




                    ROSS & ASSOCIATES
                        prepared for:




                      EPA REGION 10









                        February 1991

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                                           Table of Contents

 INTRODUCTION & EXECUTIVE SUMMARY  	  Page 1
             Lessons Relating to tfre Regional Nature of the Process
 LESSON 1:  Clearly Perceived Common Interests 	  Page 5
 LESSON 2:  Focus on the Right Questions	  Page 7
 LESSON 3:  Confidence in Process & Evidence of Political Will	  Page 9
 LESSON 4:  Adequate Representation of All Stakeholders	  Page 12
             Lessons Relating to the Process Itself
 LESSON 5:  Agreement on Analytical Framework	  Page 15
 LESSON 6:  Finality to the Process	   Page 18
 LESSON 7:  Sufficient Resources	   Page 20
             Lessons Relating to Information Requirements
 LESSON 8:  Objective Information that Meets the Group's Needs 	  Page 22
 LESSON 9:  Flexible Information Process	  Page 24

 APPENDIX A: The Council Itself	   Page 25
 APPENDIX B: Review of Meeting Content	  Page 28
 APPENDIX C: List of All Council Members	  Page 31
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INTRODUCTION AND EXECUTIVE SUMMARY

In August 1988, at the behest of the governors of Alaska, Oregon, Idaho, and Washington and the Administrator
of EPA Region 10, the 22-member Pacific Northwest Hazardous Waste Advisory Council met for the first time.
Its charge was to examine the long-term implications of the emerging hazardous waste  management system in
the Northwest and to make  recommendations to the governors and EPA Region 10 on ways to strengthen that
system.  The impetus for the Council's creation was a growing awareness of the interdependencv that exists in
the Pacific Northwest for hazardous waste management. As an adjunct to each state's efforts to assure sufficient
and  appropriate management capacity for its in-state waste generation,  the  Capacity Assurance Plan process
mandated by the Superfund Amendments and Reauthorization Act, the states and EPA Region 10 decided that
they should also collectively explore the issues raised by this interdependence

Council members represented industry,  academia, public and  environmental  interest groups, local elected
officials, and state legislators.  Five members each were appointed by the  governors of Washington and Oregon,
the two states in which most of the hazardous waste in the region is generated  and managed.   Four members
each were appointed by the governors of Idaho and Alaska. The EPA Region 10 Administrator appointed four
members,  representing  the Province  of  British  Columbia, federal  facilities, the  military, and  Indian  tribes.
Attending all Council meetings were the directors of the environmental agencies of each of the states, the EPA
Region 10 Administrator, and the Deputy Minister of the Environment for the Province of British Columbia.

The Pacific Northwest Hazardous Waste Advisory Council met eight times between August 1988  and June 1990.
It developed clear  recommendations for the states on how they should  approach hazardous waste decisions
within their scope of responsibility.  The Council's recommendations are captured  in the Council's 1988 and 1989
Annual Reports.  While the Council did meet once more after the 1989 report was released in March 1990,  the
last meeting dealt with the development of a Memorandum of Understanding between the government entities
that  would promote continued cooperation among  the states, EPA, Environment Canada,  and the  Province of
British Columbia on hazardous waste issues.
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 The Council was considered by most observers to be a successful regional coordination and policy development
 effort because it shaped the public debate on hazardous waste management in two important ways:  it established
 a regional  context  for  decision-making  about capacity and waste reduction programs;  and it  established the
 overarching importance  of waste reduction as the "capacity" option of choice.

 This report outlines the lessons that were learned from the Council process, so that policymakers  and others who
 embark on similar efforts can learn from the experience of the Council.  In general, this experience showed that,
 in order for a regional planning process  to succeed, it is necessary to have:  participants  in the process who are
 willing to attend, work, discuss and  agree; governmental  agencies whose management is involved and who are
 willing to  act  on  the  recommendations  generated by  the  process; and,  finally, staff  who  provide timely
 information, frame the issues clearly, and coordinate input to and  from the participants in the process. In some
 cases,  lessons were  learned from  shortcomings in the Council process, while  most were learned from what was
 done to ensure the level of success that the Council did achieve.  In general, these lessons fall into three groups:
 those pertaining to regional processes; those  pertaining to policy-oriented processes; and finally, those pertaining
 to the information requirements of any  regional/policy-oriented process.   Each  of these lessons is summarized
 below.

                    Lessons relating to the regional nature of the process

 Lesson 1:           Regional  efforts work best when there are  clearly perceived common interests and/or
                    interdependencies.

 Lesson 2:           Regional efforts work best when the process  focuses on the significant questions and issues
                    which the participating entities face.

 Lesson 3:           Regional efforts  work best when there  is a process  in which all participants are confident
                    of being heard and  there is clear evidence of political will (including support of key federal
                    agencies) to make progress.

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Lesson 4:
Lesson 5:


Lesson 6:

Lesson 7:
Regional  efforts  work  best  when  there  is  adequate  representation  of  all  potential
stakeholders, including those that may not yet have made their interests known.

Lessons relating to the process itself
                         «

A policy-oriented process works  best  when there  is  agreement  on a clear agenda and
analytical framework.

A policy-oriented process works best when there is a sense of eventual finality to the process.

A policy-oriented  process works best when there are sufficient resources to meet the basic
requirements of the process and to move initiatives forward.
Lesson 8:
Lesson 9:
Lessons relating to the information required to move the process forward

A policy-oriented process works best when information is perceived as objective, reasonable,
and sufficient to meet the needs of the group's decision-making process.

A policy-oriented  process works best when it is flexible enough to meet the specific data
and information needs of individual stakeholders.
Each of these lessons  is described more fully in this  report,  illustrated with observations from the Council's
experience. At the end of this report are two appendices, one which briefly describes the logistics of the Council
process and one which shows how the content of Council meetings evolved over time.
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 This regional effort  was recognized  by EPA  Headquarters  as  one  of the most successful regional efforts
 associated with the Capacity Assurance  Plan requirement.  By working through the Council to focus attention
 on regional issues and solutions in an atmosphere of cooperation and reasoned deliberation,  the governmental
 entities  in this region have been able  to avoid the animosity  and discord that affected some other parts of the
 country.  EPA Region 10 requested this report about the Council process so that these lessons might be shared
 with others responsible for conducing regional policy-making processes.
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LESSON 1:   REGIONAL EFFORTS WORK BEST WHEN THERE ARE  CLEARLY PERCEIVED  COMMON
             INTERESTS AND/OR INTERDEPENDENCES.

       For a group of counties, states, or countries to develop policy as a "region," they first must see themselves
       as  part of a  "region."  Regional  identity results from  common interests or problems, interdependent
       economies, or shared geographic boundaries.   Regional identity cannot be imposed on  a group  of
       jurisdictions for the purposes of a policy process.  If these common  interests are lacking, the group may
       splinter easily  when trying to address substantive issues.
                                              *.
       The Council process was built on a strong sense of  regional identity arising from a combination of three
       factors:

             The states of Washington,  Idaho, and Oregon are geographically isolated from the rest  of the
             country by the Rocky Mountains to the east and by desert to the south.  (As well, the Rockies
             isolate  British Columbia from the  rest of Canada.)  Alaska is  geographically isolated from the
             continental U.S.,  but its major economic and social ties are with the Pacific Northwest states.

             There  is a long history of regional governmental cooperation on environmental issues, such  as
             environmental protection of the Columbia River.

             The economies of the states are interrelated and similar:

                    Boeing is  a major employer in Washington  and Oregon.
                    Both Oregon and Washington have significant aluminum and high technology industries.
                    Idaho, Washington, and Oregon have similar agricultural and forest products interests, and
                    Oregon and Washington are outlets for agricultural exports.
                    Spokane serves as the major hub for Eastern Washington and Northern Idaho, just as
                    Seattle is a major hub for Alaska.

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       Even as a  strong sense of regional identity existed on many  other issues, the full extent of regional
       interdependence  for hazardous waste  management became clear as a  result of a preliminary two year
       scoping process.  This scoping process  developed an initial understanding of waste movements throughout
       the region which resulted in recommendations to  create a Council to address specific regional concerns.
       This scoping process involved two symposia attended by 700 opinion leaders in the Northwest, culminating
       in a report  prepared by Dr. Lee Stokes of Boise State University which clearly  documented  the flows of
       wastes among the Pacific Northwest states:

              Washington is the region's largest generator of hazardous waste; much of this waste is managed
              at facilities in Oregon and Idaho.

              Oregon is the  second  largest  generator of hazardous  waste and ships some wastes to  both
              Washington and Idaho for management.

              British Columbia is both an importer and exporter of hazardous waste from and to the  Pacific
              Northwest states.

              In most years, Alaska generates relatively little hazardous waste and has no commercial hazardous
              waste  management  facilities;  it  relies  primarily  on  facilities  in  the Pacific  Northwest  for
              management  of  its  wastes.   Alaska's dependence on  Washington and Oregon facilities was
              highlighted last year, as  management facilities in both  states received  tons of oil-contaminated
              waste generated from oil spill cleanup  activities.

       This scoping process made  clear that  common  interests would  be served by analyzing hazardous waste
       management issues in a  regional context.
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LESSON 2:   REGIONAL EFFORTS WORK BEST WHEN THE PROCESS FOCUSES ON THE SIGNIFICANT
             QUESTIONS AND ISSUES WHICH THE PARTICIPANTS FACE.

       Three criteria determine what might be appropriate questions for a regional process:

             Is it a policy level question?  Ultimately there has to be agreement on the policy level first, before
             discussion of implementation issues can proceed.

             Can the question be answered given the time and resources that can be devoted to it?  An agenda
             that is too broad sets the process up for failure because of the need to make  too many trade-offs
             on decisions and the need to involve too many stakeholders.  An agenda that is too narrow may
             allow the group to detour from a policy focus and become entangled in details or busy work, either
             of which may cause the participants to lose interest in the process.

             Can the question be. answered with credibility by those charged with finding an answer?    Just as
             a  group of laypeople  might not  be  perceived  as  credible if they were to address policy issues
             requiring complex, technical analysis, a group of scientists alone might not be a credible body to
             voice the values and concerns of the body politic.

       In addressing the evolution  of the hazardous waste management system in  the  Pacific Northwest, the
       Council chose to  focus on two policy questions:

             Does the  region have a responsibility to foster evolution of a waste management system that  is
             consistent with a preferred hierarchy of management options (in order of decreasing preference:
             waste reduction; recycling/reuse;  treatment;  and then incineration or land disposal of residuals),
             or should  the  development of the management  system be left exclusively to generators and TSDs,
             making choices  in the context of national  regulatory  priorities  and local, regional,  or national
             market opportunities?

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              Does the region have a responsibility to its generating industries to ensure access to the types of
              capacity necessary to manage  wastes  according to this hierarchy of preferred management,  or
              should capacity decisions be left solely to the private market?

       In both cases, the Council's answer was yes, the states in the region do have a responsibility to go beyond
       national regulatory priorities  for  hazardous  waste  management  and  to ensure  access  to  appropriate
       capacity for the waste streams generated in the region.

       Because these were policy questions, and  because the Council was comprised of people who spoke for
       a broad range of constituencies and were perceived as credible, the Council work served to  shape the
       discussion  in  the  Pacific Northwest about how  the  hazardous waste management  system  should  be
       modified to achieve these policy goals.

       The Council was able to provide first-level answers to both these questions.  Regarding waste reduction
       and  the preferred  hierarchy, the Council was able to go  beyond the first-level  answers and recommend
       a series of activities to the states regarding how to foster waste reduction, the first option in the preferred
       hierarchy, throughout the region.  However, the Council was less unified in providing its recommendation
       on the need for or  desirability of in-region incineration capacity due to  disagreement among stakeholders
       as to the level of analysis needed  to make a decision.  The majority of the  Council concluded that there
       was  sufficient information upon which to make  a recommendation  and that making  more detailed
       recommendations regarding capacity went beyond  the scope of the process because the analysis required
       became too technical and too site-specific.
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LESSON 3:   REGIONAL  EFFORTS  WORK  BEST WHEN  THERE  IS  A  PROCESS  IN  WHICH ALL
             PARTICIPANTS ARE  CONFIDENT OF BEING  HEARD  AND THERE IS CLEAR EVIDENCE
             OF POLITICAL WILL (INCLUDING  SUPPORT OF KEY  FEDERAL AGENCIES) TO MAKE
             PROGRESS.

      It is not  enough for the entities in a region to  acknowledge their common interests.  In order  for a
      regional policy process to work well, there needs  to be both broad agreement on the questions that the
      process will address and an evidence of political will to implement the recommendations.  Because these
      are intangible qualities, the best way to assess whether this agreement and support exists is to gauge the
      participation of the government entities in the process - through creation of the process itself, attendance
      by concerned officials at meetings, cooperation and support of the analytical aspects of the process, and/or
      interest in receiving and implementing recommendations arising from the process.

      All these  factors were present to support the work of the  Council,  as evidenced by the active involvement
      of the EPA Regional Administrator, the state directors, and their key staff people.

             The  decision  by the EPA  Regional Administrator  to launch  the  Council process and provide
             funding for the process throughout its life showed clearly the value that EPA placed on this
             dialogue.   EPA's leadership was the foundation for the success of this effort and demonstrated a
             good model for federal support in  assisting regional discussions of this type.

             Participating in the Council process was a  clear priority for the EPA Regional Administrator and
             each of the four state environmental agency directors and their counterpart from British Columbia.
             Most were in attendance at  each meeting,  absent  only  when  the  call of state  business was
             particularly pressing  (e.g., to address the Exxon Valdez disaster).  In  addition, as a result of the
             Council process, the state directors  met prior to each Council meeting to discuss  the progress of
             the Council and the issues it was  confronting.  Their direct involvement was important because it
             allowed the Council  to speak directly to the audience that  would act - one way or the other - on

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              their recommendations.  It also allowed the state directors to clearly articulate the policy questions
              on which they sought the guidance of the Council.

              Staff from each of the states, the province, and EPA Region 10 provided invaluable  support  in
              providing  data and other input for the various  Council  analyses and in reviewing documents for
              accuracy and completeness.  This commitment of time was a clear indication of how important the
              state directors considered this process, especially  as the states' staff were already fully occupied with
              the mechanics of completing the states' Capacity  Assurance-Plans.

              The leadership of EPA, the commitment of the state directors, and the support of the relevant
              agency staff created a positive  dynamic which encouraged the active attendance and involvement
              by Council members and their constituencies, because they recognized that their views would be
              heard and that the Council's  recommendations would  considered by the EPA  and the  states
              directors as important policy guidance.

       The existence of  the Council process helped focus attention on hazardous waste legislation in each of the
       four states.  During the life of the Council, Oregon adopted a toxic use and waste reduction law which
       mandated waste reduction planning on the part of  regulated hazardous waste generators.  In its following
       session, Washington passed a similar bill, one which included the Council's goal of a  50 percent  waste
       reduction target.   Alaska  adopted the preferred  hierarchy  of hazardous  waste  management options  to
       guide its  hazardous waste management efforts.   Finally,  similar legislation  was introduced  in  Idaho,
       although it did not pass.   In each case,  one of the sponsors of each state's legislative initiative was also
       a member of the  Council.  As well, legislation was introduced in Washington to incorporate regional need
       as a criteria for permitting  new capacity in the state; that legislation was not successful.

       After the cessation of Council activities, EPA Region 10,  the states, and the  province  entered  into a
       Memorandum of Understanding to structure their relationship and to sustain  the benefits of regional
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       communication and coordination that  were derived from the Council process.  This  MOU is further
       evidence of the political support that the Council enjoyed.
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 LESSON 4:  REGIONAL EFFORTS WORK BEST WHEN THERE IS ADEQUATE REPRESENTATION OF
             ALL POTENTIAL STAKEHOLDERS, INCLUDING THOSE THAT MAY NOT YET HAVE MADE
             THEIR INTERESTS KNOWN.
       The  credibility of a regional process rests on  having heard from those on all sides  of an  issue.  This
       includes both those who are clearly affected by the issues under discussion, as well as  those who may be
       affected but who are not yet actively involved in shaping the issue.

       The  Council was successful because its members represented a wide range of opinions on  how best to
       ensure appropriate hazardous waste management in the Pacific Northwest.   Members were encouraged
       to communicate with their constituencies about the  issues facing the  Council so that those interests could
       be well represented in this effort.   Financial assistance was provided, in some instances, to ensure  that
       members could communicate  effectively  with  their consistencies.   The Council also welcomed  public
       input and outside review of its documents and materials.

       The following interests were represented on the Council:

             federal agencies,  because they are both major generators and managers of hazardous  waste in the
             Pacific Northwest;

             Indian tribes, because they need access to  management capacity as a  result of cleanup activities
             that are occurring  on their  lands and because  Indian lands are often sought as sites for  new
             commercial management facilities;

             the Province of British Columbia, because waste currently moves between the Northwest states and
             British Columbia;
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             the  environmental  community,  because  the  proper  management of  hazardous waste  is  an
             environmental issue, as well as an economic and political one;

             state and local elected officials, because of their hands-on understanding of and responsibility for
             the policy and political issues involved;

             hazardous  waste generators, because it  is their behavior that any hazardous waste policy would
             attempt to change.

       A list of all Council members and their affiliations is found in Appendix C.

       The  hazardous waste management industry was not represented on the Council.   However, throughout
       the Council process, the industry was  kept involved in reviewing and commenting on the full range of
       Council activities.

       To encourage the public's interest in this process, an extensive mailing list was maintained both by the
       contractor  and  EPA Region 10.  Individuals on the contractor's list received Council packets and other
       information prepared for Council members.  Individuals on the  EPA list received periodic updates on the
       Council's activities.  As well, each Council meeting was announced in the  major newspapers serving the
       host  state about a week in advance; all meetings were open to the public.  At the meetings, opportunities
       provided  for public comment were frequently used by various interest groups.
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 LESSONS:  A POLICY-ORIENTED PROCESS  WORKS  BEST WHEN  THERE IS AGREEMENT  ON A
             CLEAR AGENDA AND ANALYTICAL FRAMEWORK.
       A clear agenda and  analytical framework precludes  unplanned divergences which may or may not be
       productive.  It is not imperative that a clear  agenda be established in advance.  However, it is important
       that developing such an agenda become the first task of the group.

       The Council did not  start with a clear agenda.  It developed both its  agenda and analytical framework
       over the course of its first three meetings.

       The Council's agenda evolved into two issues:

             Assuming that  management  of  hazardous  waste  should be done according to the preferred
             hierarchy, to what types of capacity do the  wastes generated in the region need access in order
             for this to occur?

             How  can the  Council  foster waste  reduction, the  most  preferred  alternative  on  the  waste
             management hierarchy?

       With respect to assessing the need for capacity, the Council adopted a six step process:

             formally affirming a regional approach to capacity assessment;

             analyzing the hazardous wastes generated in the Pacific Northwest;
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             developing generic criteria under which it might be appropriate to provide any type of TSD capacity
             within the region (e.g., it  meets environmental standards, it is appropriately sized to meet regional
             needs after maximum waste reduction);
                     4

             adopting a preferred management hierarchy (including waste reduction) and assessing the capacity
             needs of Pacific Northwest waste streams if they were to be managed according to that hierarchy;

             determining which in-region capacity may be needed; and

             designating conditions under which any needed capacity should be sited in the region.

       The issue of waste reduction lent itself to a different approach.  After reviewing various attempts to model
       waste reduction  potential for various industries in the Pacific Northwest, the Council concurred with the
       Office of Technology Assessment (OTA) that waste reduction potential was too unpredictable  at this
       time,  given the extent of regulatory change affecting generators.  Thus, the Council decided to adopt the
       OTA approach to waste reduction which set policy targets of 10 percent reduction each year. Over a five
       year period, such reduction results in a greater than 50 percent reduction from starting volumes.  Given
       the waste reduction initiatives already implemented  in the Pacific Northwest, the  Council agreed that an
       additional reduction from 1987 volumes was an ambitious but achievable target.   Adopting a policy goal
       shifted the   deliberations to focus on what policies  and programs  the states could implement to help
       generators meet  this goal; the Council adopted 13 recommendations for waste reduction activities.

       A strength of the Council was in  its ability to achieve consensus as  it moved through the analytical process.
       In its  capacity assessment process, the Council was unanimous in:

             endorsing a regional perspective for capacity analysis;

             recommending a preferred hierarchy of management options;

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              adopting a 50 percent goal for waste reduction;

              recommending a series of waste reduction measures to the states; and

              endorsing ten generic criteria to guide capacity decisions in the region.

       However, the Council  did not achieve unanimity in addressing the issue of whether incineration capacity
       was needed to meet the needs of the region's waste streams, and whether that capacity should be provided
       in-region rather than out-of-region.  On this issue the  Council  split, 13-4, in favor of a resolution stating
       the need for such capacity and the preference for having that capacity in-region.  The dissenting Council
       members felt  it was premature to  support the conclusions contained in Resolution 5 because the Council
       has not yet addressed  the full range of potential capacity needs (i.e. for recycling  and metals recovery);
       because the Council has not analyzed whether incineration met  the environmental and health criteria (and
       other generic  criteria) established by  the  Council;  and  because  specific  conditions  for developing
       incineration and any  other  in-region  capacity  had not been  developed by  the  Council  to  minimize
       environmental and  health impacts.  There also  was concern that the resolution  could be interpreted as
       endorsing a particular  project. The majority of the Council believed that its resolution did not endorse
       any particular project;  that there was sufficient information upon which to make  a  recommendation; that
       the Council's generic criteria were  sufficient  to provide policy guidance on any specific project; and that
       making  more detailed recommendations went  beyond  the  scope of the process because the analysis
       became too technical and too site-specific.

       The vote  on  this issue was a clear diversion from the Council's record of consensus  on all previous
       resolutions.  In addressing the incineration capacity issue, the Council made a major commitment to tackle
       a serious and controversial regional and,  indeed,  national issue.  As such, perspectives of Council members
       were influenced by  a broader array of information  than that generated  by and for the Council itself. As
       well, the level of additional analysis necessary to address the concerns  of the minority Council members
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       exceeded what most  Council members believed was either necessary or within the scope of a regional
       advisory body which met quarterly.

       The failure to achieve consensus on this issue was  not viewed by Council members as a fatal  event in the
       life of the Council, nor did  it detract from a positive  assessment of the Council's  overall progress or
       accomplishments.  It  did, however, point out the fact that groups such as the Council do face limits on
       both the type and depth of issues which they can successfully address.  Again, this fact highlights the need
       for an agenda and analytical framework  that is  as clearly defined as possible  at  the  beginning  of the
       process.  Then, when the group reaches this "limit" on an issue, it can either shift its energy to other issues
       within its purview, or  recognize explicitly that its mission on this issue has been completed.
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 LESSON 6:  A POLICY-ORIENTED PROCESS WORKS BEST WHEN THERE IS A SENSE OF EVENTUAL
             FINALITY TO THE PROCESS.
       A policy-oriented process works best when it has a clearly-defined termination point.  The  importance
       of finality is best illustrated by the potential effects of operating without some deadline:

             There may be a tendency to postpone action until there is "sufficient" data or analysis.  However,
             since  there  is rarely  "enough" information for  most decisions, decisions  are made on the best
             available information.  If both the policy process and data requirements are open-ended, there is
             never a point when the group can be asked to "fish or cut bait."

             There may be a tendency  to assume that the group which  has been constituted to address the
             policy questions  should also be the group that addresses implementation issues.  This is not often
             the case.  It is important that follow-up processes evolve as necessary and involve the stakeholders
             that have an interest in the implementation of policy.

             There may be a  risk of burnout and/or the loss of enthusiasm on the part  of participants and staff
             for what ultimately is a voluntary process.

       Just as the Council began without a clearly-defined agenda, it also began without a time frame in which
       to complete  its analysis and  recommendations.   While  the need  for an agenda was met during the first
       three meetings, the Council struggled somewhat because it lacked a fixed termination point.

       The Council's first meeting was held in August 1988.   Its meetings in October  and December of 1988
       were organizational in  nature,  during which the Council's  agenda and operating mode was  established.
       In these meetings, it became clear that the states could best benefit  from the Council's  input  and
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       recommendations prior to the October 17,  1989, deadline for submissions of hazardous waste  Capacity
       Assurance Plans as required under the Superfund Amendments and Reauthorization Act.

       In 1989, the Council held two meetings (including a two-day meeting in July) which dealt with substantive
       aspects  of its analysis  of  need  for capacity.   At  its September meeting,  the  Council  concluded its
       recommendations on the capacity issue,  so  that the states could incorporate the  Council's findings into
       their Capacity Assurance Plans due on October 17.

       The continued role of the Council became  less clear at that point.  The future of the Council  was first
       discussed at the  September meeting.  Two additional meetings followed, in December of 1989 and in June
       1990, which also focused on the future  of  the Council.  Because Council members and state  directors
       agreed that the  process  had  been useful, there was reluctance to disband the process, even though the
       majority of the Council and the state directors felt that the Council's substantive regional policy agenda
       had been completed.

       The Council's experience illustrates the importance of having some well conceived, and clearly understood,
       notion of how the transition between a  policy and an implementation orientation will take place.  The
       willingness of governmental entities to enter into  an MOU enabled the Council to disband knowing that
       its policy recommendations would be considered, even  in the absence of the continuation of the  Council.
       In addition, the MOU provided a mechanism by which a formal, regional body (such as the Council) could
       be constituted in order to address a serious regional policy issue, should one arise.
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                                                            Pacific Northwest Hazardous Waste Advisory Council
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 LESSON 7:   A  POLICY-ORIENTED   PROCESS  WORKS  BEST  WHEN  THERE  ARE   SUFFICIENT
              RESOURCES TO MEET THE  BASIC REQUIREMENTS OF THE  PROCESS AND  TO  MOVE
              INITIATIVES FORWARD.
       The Council was funded by EPA Headquarters and Region 10 as part of the SARA Capacity Assurance
       Process.   Throughout the Council  process,  there were  sufficient resources  to  provide the level  of
       information and support needed to keep the process moving forward.

       Sufficient resources are necessary to generate needed information; the notion of "sufficient" is obviously
       related to the agenda and the duration of the process.  Resources are required  if the existing staff of the
       government entities would be overburdened by  taking on the full responsibility of an additional process.
       Also, if the  coordinative  and analytical activity is assigned  to existing government  staff  with other
       substantive governmental  responsibilities (i.e.,  management or  permit  issuance), it is likely that  the
       regional process will not be the first priority; this may cause delays and lead to disinterest in the process.

       EPA Region 10,  in consultation with  the  states, chose to hire a consultant  to staff  the Council.   A
       consultant was chosen in order to avoid:  any problems with perceived biases on hazardous waste issues;
       potential conflicts with regulatory and permitting decisions  that are within the purview of state staff; and
       any institutional biases.  As well,  the consultant was able to provide logistical support without burdening
       state staff people who were enmeshed in meeting the CAP deadline.

       State and EPA Region 10 staff supplemented the consultant support in two ways: they assisted with some
       logistical activities (e.g., contracting with the hotel when their state hosted a meeting); and they provided
       substantive  contributions to the capacity assessment information analysis.

       EPA Region  10  also  provided sufficient  resources to pursue Council recommendations with respect to
       development of a Memorandum  of Understanding  to sustain the  progress of  the Council among EPA

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      Region 10, the  states, and British  Columbia.   Implementation of the  MOU will be  supported  by
      contributions from each of the signatories.  Ensuring that this MOU was developed was important to the
      process, so that regional coordination by the government entities would continue after the Council ended
      its activities.
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 LESSON 8:   A POLICY-ORIENTED PROCESS WORKS BEST WHEN  INFORMATION IS  PERCEIVED AS
              OBJECTIVE,  REASONABLE, AND SUFFICIENT TO MEET THE  NEEDS OF THE GROUPS
              DECISION-MAKING PROCESS.

       For a policy process, it is important that information is both objective and  is seen as being sufficient to
       address the issue.  Information which is not seen as objective serves to fragment and  divide a process.
       At a minimum, the group must trust that, while maybe not complete or as  fully detailed as some would
       like, the information does not contain any biases which distort the conclusions drawn from it.  As  well,
       it  is important  that the group agree on the appropriate range  of tolerance  about the information put
       before it   Generally, this tolerance is dictated by the nature of  the decision being made.  Technical
       decisions about the type  of pollution controls for a specific facility, for  example,  require quite different
       types  of information than policy decisions  about how to  foster implementation of a preferred waste
       management hierarchy.   While policy decisions  will lead to  subsequent technical and implementation
       decisions,  the level and  type  of  information necessary to make  technical decisions is not necessarily
       required at the time that the implementation decisions are to be made.

       The Council chose to use  a "reasonableness" test in assessing the need  for capacity.

             It was clearly acknowledged up front that hazardous waste management practices were undergoing
             enormous change,  driven in large part by implementation of new federal regulations (notably, the
             Land Disposal Restrictions). These regulations were seen as driving up the cost of waste disposal,
             thus providing an economic incentive for waste reduction.  Compounding the problem of change,
             the Council  recognized that it was relying on data already two years old and, hence, it was unsure
             how many changes in waste management practices had already occurred.

             On the  other hand,  imminent  regulatory changes,  such as  planned adoption of  the  Toxicity
             Characteristic  Leaching Procedure  to  replace the Extraction Procedure Toxicity Test, were  seen
             as expanding the universe of hazardous waste in ways that could not be predicted at the time.

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              In  the face of  this dynamic  reality, the Council considered whether estimating future waste
              reduction potential for  each generating industry was reasonable.  It decided that such an approach
              was unreasonable because of the large number of regulatory, technical and economic assumptions
              required and the significant uncertainty that existed around each assumption.

              Instead, the Council believed that the amount of waste reduction that occurred would be the result
              of federal and state efforts to encourage such  reduction (e.g., directly through technical assistance
              programs, or indirectly through higher waste management  costs occasioned by, for instance, the
              Land  Disposal Restrictions).  Thus, the  Council chose to work backwards:  instead of trying to
              'predict' waste reduction, it adopted an ambitious and hopefully feasible target for waste reduction,
              and then recommended to the states  the types of activities they would need to implement to help
              generators reach that target. This target was then factored into the need for capacity analysis.

       Almost any process could generate vast quantities of relevant information.  However,  it is important for
       information to be tailored to  the decision being made (summarized, reformatted, etc.) so that the group
       does not need to sort through extraneous information. On the other hand,  the process also needs to be
       flexible enough to address specific information requests, when it appears that those requests are necessary
       to build confidence or would further progress.

       The Council's process was stymied under  the weight  of the questions raised regarding the next level of
       detail in its deliberations on the need for incineration capacity:  should incineration be on-site? offsite?
       in-region?  out-of-region?   The  questions  proved  too  difficult to  answer given information-gathering
       capabilities of the process.
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                                                          Pacific Northwest Hazardous Waste Advisory Council
                                                                                        Lessons Learned
 LESSON 9:  A POLICY-ORIENTED PROCESS NEEDS TO  BE  FLEXIBLE ENOUGH  TO MEET THE
             SPECIFIC DATA AND INFORMATION NEEDS OF INDIVIDUAL STAKEHOLDERS.
       Information  needs cannot be fully projected, and thus,  there may be a  need to respond to specific
       information concerns of various participants.

       This was clearly the Council experience.  As the analysis unfolded, specific questions emerged which had
       not been foreseen at the start of the process, including an analysis of the need for metals recovery capacity
       in the region and a discussion of the feasibility of promoting waste exchanges in the region as part of
       regional waste reduction efforts.  As well,  to ensure objectivity of the analysis of the  waste streams in
       terms of the application  of the preferred hierarchy for those waste  streams, some  Council  members
       requested outside peer review of the analysis.  In each instance,  information was provided to assist in
       the deliberation about the specific questions posed, and the process moved forward.
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APPENDIX A:            THE COUNCIL ITSELF

In 1986, recognizing the regional  nature of the hazardous waste management challenge, the directors of the
environmental agencies  of Washington,  Oregon, Alaska, and  Idaho, and the Administrator of EPA Region 10
began to  work together to' understand  the region's  hazardous waste streams and discuss  the potential for a
regional response to the challenge of reducing the volume of hazardous waste and managing the remainder safely.
It seemed then that a consistent and coordinated regional response would not only be appropriate, but desirable.

In 1987, a four-state  steering committee  was created by EPA and the states to organize two symposia which laid
the ground work for understanding regional flows of various types  of hazardous waste and for identifying  the
issues this waste flow raises  for policymakers.  One of the recommendations emerging from these symposia was
the creation  of a council, to advise on appropriate  regional approach to these regional concerns.  Thus,  the
Pacific Northwest Hazardous Waste Advisory Council was formed as an advisory body charged with examining
the hazardous waste management issues facing the Pacific Northwest.

There were 22 members of the Council.  The  governors of Idaho and Alaska each approached four members
and the governors of Oregon and Washington each appointed five members.  The EPA Region 10 Administrator
also appointed four Council members.  (See Appendix C for a full list of Council members and their affiliations.)

Council Logistics

A brief review of the logistics of the Council meetings:

       one-day meetings were held approximately each quarter;

       the meeting site rotated among the states, except during the legislative sessions when the need to minimize
       travel  time dictated that the meeting be in Seattle;
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        each Council member participated  in  one or  more  committees which met either  in  person or  by
        conference call between meetings;

        prior to each Council meeting, meeting  packets were distributed a week in  advance which provided the
        reports of the various subcommittees and analyses requested at the prior meeting;

        at the close of each meeting there was agreement on the general agenda for the next meeting;

        most work between  meetings was done by the contractor, with environmental agency staff from the host
        state responsible for  arranging the place of the next meeting, etc.;

        each state was provided a fund with which to pay for meeting expenses when it hosted a Council meeting,
        as well as to pay for  the travel of its Council members to all meetings;

        each meeting  was  advertised one or two weeks prior to the meeting in  the major papers serving the host
        state;

        substantive support on issues was  provided by staff from all states; and

        each state was also responsible for  selecting a hazardous waste reduction award winner; the winners were
       provided a plaque  from the Council at the meeting.


The Council's Structure

       The Council was guided by two  co-chairs, one from Oregon and one  from Washington.  Responsibility
       for chairing  the meetings was rotated  between the two, both sat on the Strategic Planning Committee, and
       each took responsibility for one of the two committees that addressed substantive issues.

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       The  Strategic  Planning Committee provided guidance to the chairs on meeting agenda and procedural
       issues, and reviewed substantive information prepared for the Council, as necessary, between full Council
       meetings.

       Two committees were formed,  dealing with waste reduction and the need for capacity.  Each committee
       was  responsible  for  reviewing  information developed for  the Council  and  developing  drafts  of
       recommendations and reports on which the full Council acted.

       The  state  directors  and EPA Region 10 Administrator attended the meetings and  sat at one end of the
       table, facing the  Council  members.   At every meeting,  the  state directors updated the  Council on the
       hazardous waste management activities in  their states.  They were available throughout the meetings to
       answer questions posed by Council members and to offer  their observations on the issues facing the
       Council.   The presence of the directors  helped the Council focus on relevant  issues.   As well, the
       participation of the directors signified the political will behind the Council process  and elevated the
       importance of its deliberations.
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                                                            Pacific Northwest Hazardous Waste Advisory Council
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 APPENDIX B:      REVIEW OF MEETING CONTENT
 Seattle. August 1988  The Seattle meeting was primarily an information and organization meeting.  Each state
 environmental agency director provided an overview of the status of hazardous waste management issues in
 his/her state.  This was followed by a discussion of the Council's statement of purpose and the adoption of such
 a statement.  The Council also brainstormed in two areas:  what are the components of a regional hazardous
 waste management plan and  what are the  components of a waste reduction strategy.  Two committees were
 formed to structure these ideas for the next meeting.

 Boise. October 1988  The Boise meeting built  on the groundwork laid in the Seattle meeting, clarifying how
 the Council would operate and identifying some of its objectives with regard to waste reduction.  The Council
 also began  to focus on how hazardous waste should be defined in the context of its activities.  The Council
 indicated  that its focus should be broader than simply the legal definition of hazardous waste.

 As well, the Council was briefed on EPA's draft  guidance document for the states to use in completing their
 SARA CAPs.  The Council endorsed the cooperative,  inclusive process  by which EPA developed this guidance
 document but refrained from endorsing the document, per se, because of insufficient time to study it.

 The Council formed two standing committees to address the issues of waste reduction and  the regional need for
 TSD  capacity.  The Strategic  Planning Committee handled  any administrative concerns of the  Council.  Each
 of the standing committees was charged with  returning to the Council with a proposed workplan.

 Portland.  December 1988  In  Portland, the Council adopted a set of working definitions  of hazardous waste to
 guide  its  activities in waste reduction  and its analysis of the  region's need for TSD capacity.   In addition,  it
 adopted a formal affirmation of a regional approach to hazardous waste management in the  Pacific Northwest.
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                                                            Pacific Northwest Hazardous Waste Advisory Council
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The Council also adopted the workplans of its two standing committees.  In the coming year, the Council agreed
to focus its efforts in  two primary areas of  concern:  fostering and  supporting efforts in waste reduction,  and
advising the states and EPA on the TSD capacity needed to manage wastes generated in the region.

Seattle. March 1989  The Council adopted a preferred hierarchy of hazardous waste management options. The
Council adopted  a list of 10 generic criteria  against which the location of any  capacity in the region should be
evaluated.  In addition, it reviewed and deliberated on an analysis of the waste generated in the Pacific Northwest

Anchorage. July  1989    The Council  reviewed and deliberated on an analysis of the capacity implications of
managing the  region's waste streams  in relation to the  preferred hierarchy.   The  Council  passed a motion
recognizing the need for incineration in the Pacific Northwest, based  on an analysis of the demands that  would
be placed on capacity if there were both a 50 percent waste reduction by 1995 and the management of residuals
in accordance with the preferred hierarchy.

Portland. September 1989  At this meeting, the Council adopted two resolutions:  one recommended the states
and EPA take a comprehensive approach to waste reduction; the other recognized the need  for hazardous waste
incineration capacity in the  region and recommended to the states the conditions under  which  that capacity
should be considered for  siting in the  region.  In addition, the Council passed  a resolution  urging the states to
include waste reduction in their CAPs  as a source of capacity and that they do so in a way  that fosters reliance
upon waste reduction  as  the management option of choice.   Finally, the Council submitted a letter to EPA
Administrator Reilly, asking him to recognize  the regional efforts of the Pacific Northwest states.

As  well, the Council  adopted  a discussion paper which explained how the Council's goal  of  50 percent  waste
reduction by 1995 was determined  and how the Council hoped  this goal would be used to influence decisions.

Coeur d'Alene. December 1989   At this meeting,  the Council discussed its future and recognized that it was
moving into a period of consolidating  its gains and broadening public awareness about its work.  The Council
recognized that there appeared to be  no major additional regional policy issues outstanding at the time  which

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 would benefit from Council analysis and  recommendations.  The Council saw four specific  tasks on its  1990
 agenda:

       to investigate the possible need for additional metals recovery capacity in the region;

       to continue to support and promote the Pollution Prevention Research Center;

       to describe for nationwide use by EPA the development of the Pacific Northwest framework for addressing
       regional hazardous waste issues (in the form of this Lessons Learned report); and

       to develop a statement concerning the institutionalization of the Council's goals by the government entities
       in the region.

 Portland. June 1990    The Council deliberated on the  issues that should be addressed in a Memorandum of
 Understanding among the states, the province, and EPA Region  10. The Council indicated that, by passing the
 baton to others through the MOU, its work was completed.
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                                                          Pacific Northwest Hazardous Waste Advisory Council
                                                                                       Lessons Learned
APPENDIX C:
LIST OF  COUNCIL MEMBERS  (Individuals marked  with  an * were  appointed  to  fill
vacancies on the Council.)
Alaska
Kay Brown
Don Oilman
Tony Knowles

Tom Painter
Julie Petro*
Mark Tumeo*

Idaho
Joan Cloonan

Denton Darrington
Leanna Lasuen
William Saul

Oregon
Ron Cease
Frank Deaver
William Hutchison (Co-Chair)
Laura Pryor
Ann Wheeler
             Alaska State Representative
             Mayor, Kenai Peninsula Borough
             former Mayor of Anchorage (resigned from the Council to run for political
             office)
             Conoco (resigned from the Council due to a job transfer)
             NANA Regional Corporation, Inc. (Appointed - Spring 1990)
             University of Alaska, Fairbanks  (Appointed - Spring 1990)
             J.R. Simplot Company

             Idaho State Senator
             Idaho State Representative
             Dean, College of Engineers, University of Idaho
             Oregon State Representative
             Corporate Environmental Services, Tektronix, Inc.
             Tooze,  Marshall, Shenker,  et. al., also chair of the Oregon Environmental
             Quality Commission which  oversees the activities of the Oregon Department
             of Environmental Quality
             Gilliam Country Judge
             Attorney representing environmental groups
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                                                           Pacific Northwest Hazardous Waste Advisory Council
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 Washington
 Pam Crocker-Davis

 Ron Kendall (Co-Chair)
 Pat Murnmey
 Nancy Rust
 Liz Tennant*
 Kirk Thomson

 EPA Appointees
 Earle Anthony

 John Barry
 Richard DuBey
 Raymond Jones*
 Rear Admiral J.R. Reason
Washington Toxics Coalition  (resigned  upon  assuming  a job  with  the
Washington Department of Ecology)
Professor, Western Washington University (resigned because of a job transfer)
Spokane County Commissioner
Washington State Representative
Seattle Audubon Society (Appointed - January 1989)
Boeing
Environment Canada (originally appointed to the Council when an official of
the Province of British Columbia)
U.S. Department of Energy, Idaho National Engineering Laboratory
DuBey Law Firm, representing Indian tribal interests
Admiral, U.S. Navy (appointed - August 1989)
Admiral, U.S. Navy (resigned from the Council due to a job transfer)
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