Collingwood Harbour PAC Sfl/ of Quinte PAC
Port Hope Local Advisory Croup	^
Metro Toronto PAC
Monroe Country Water
Quality Management Committee
\ Hamilton Harbour
\ Stakeholders
y	BAIT
^	BARC
'st. Clair River BPAC _
Saginaw Basin Alliance
Saginaw Basin Natural
Resources Steering Committee
Muskegon Lake PAC
Clinton River PAC
Detroit River BPAC
Friends of the Detroit River
Friends of the Rouge
Rouge RAP Advisory Council
River Raisin PAC
Jackfisb Bay PAC
Institutional Frameworks to
Direct the Development and Implementation
of Remedial Action Plans
Peninsula Harbour PAC
St. Marys BPAC
Spanish River PAC
St. Lawrence
River PAC
St. Lawrence
River RAC
Oswego River RAP
Advisory Committee
Niagara River PAC
Niagara River Action Committee
Friends ot the Buffalo River
Buffalo River Citizen* Committee
Buffalo River RAC
Prtsqu* IsU Bay PAC
Ashtabula River RAP Advisory
Council
Maumee River PAC
Cayaghoga River Commodity
Planning Organization
Cuyahoga River RAP
Coordinating Committee
Black River Coordinating
Committee
Co-sponsored by Environment Canada and U.S. Environmental Protection Agency
in cooperation with Wayne State University (Detroit, Michigan)
Canada
1993
\
12EZ. °
Wayne Skate University

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Institutional Frameworks to
Direct the Development and Implementation
of Remedial Action Plans
Based On a March 1993 Roundtable Co-sponsored by Environment Canada
and U.S. Environmental Protection Agency, in cooperation with Wayne State University
(Detroit, Michigan)
John H. Hartig
and
Neely L. Law
Wayne State University
Department of Chemical Engineering
Detroit, Michigan 48202
1993

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TABLE OF CONTENTS
TABLE OF CONTENTS		i
LIST OF TABLES		ii
LIST OF FIGURES		ii
ACKNOWLEDGEMENTS		iii
EXECUTIVE SUMMARY		1
I INTRODUCTION		3
H SYNOPSIS OF WORKSHOP DISCUSSIONS 		7
A.	Essential Characteristics of RAP Institutional Frameworks to Ensure Use
of an Ecosystem Approach to Use Restoration 		8
1.	A Watershed Perspective		8
2.	Broad-Based Participation to Achieve Implementation		10
3.	Clear Responsibility and Sufficient Authority		11
4.	Human and Financial Resource Support		12
5.	Flexibility and Continuity to Achieve an Agreed-Upon Road Map
to Use Restoration		13
6.	Education and Outreach		15
7.	Commitment to Action Planning within a Strategic Framework ...	16
B.	Guidance to Ensure Linkages to Other Related Plans and To
Ensure Complementary and Reinforcing Actions		17
C.	Embracing New RAP Institutional Frameworks to Ensure a Smooth
Transition from RAP Development to Implementation		20
m CONCLUDING REMARKS AND RECOMMENDATIONS 		24
IV	APPENDIX I - LIST OF ROUNDTABLE PARTICIPANTS 		26
V	APPENDIX D - INSTITUTIONAL FRAMEWORK CASE STUDIES		30
VI	LITERATURE CITED		49
i

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LIST OF TABLES
Table 1. Remedial Action Plan institutional frameworks established in Great Lakes Areas
of Concern		5
Table 2. Activities and functions being performed by nonprofit RAP institutional
frameworks in the Great Lakes Basin		14
LIST OF FIGURES	
Figure 1. Forty-three Areas of Concern identified in the Great Lakes Basin 		4
Figure 2. The institutional framework for implementation of the Hamilton Harbour
RAP 		31
Figure 3. A general framework for the development of the Detroit River Stage II
Remedial Action Plan		33
Figure 4. Cuyahoga River institutional framework for development of a Stage I RAP. ...	37
Figure 5. Cuyahoga River institutional framework for development of a Stage II RAP. . .	38
Figure 6. St Lawrence River Remedial Action Plan institutional framework for the
development of the joint goal and problem statement 		41
Figure 7. Lake Champlain Project		43
Figure 8. Major committees in the Chesapeake Bay Program		46
ii

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ACKNOWLEDGEMENTS
The roundtable and report were made possible by a grant from Environment Canada and
U.S. Environmental Protection Agency to Wayne State University in Detroit, Michigan. We
would like to extend our appreciation to the speakers who provided informative presentations (M.
Donahue, S. Benzie, D. Gaudenzi, G. Mills, J. Beeker, M German, G. Mikol, L. Borre, S.
Funderburk, and M. Binns), the roundtable participants identified in Appendix I whose knowledge
and practical experiences inspired a thorough assessment and dialogue on institutional
frameworks, and S. Lefleur who arranged the roundtable facilities at the Windsor Public Library.
Further acknowledgement must be given to the reviewers of the manuscript (D. Epstein, K.
Fuller, M. Brooksbank, T. Coape Arnold, M. German, D. Dodge, B. Fredrickson, J. Letterhos,
P. Johnson, G. Mikol, J. Beeker, G. Knaap), whose thoughtful comments improved the final
report. Finally, we would like to especially thank D. Epstein (project officer from Environment
Canada) and K. Fuller (project officer from the U.S. Environmental Protection Agency) for their
continued support and encouragement for this project.
iii

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EXECUTIVE SUMMARY
The Great Lakes Water Quality Agreement requires use of a systematic and
comprehensive ecosystem approach in development and implementation of remedial action plans
(RAPs), and requires that the public is consulted in all actions undertaken pursuant to RAPs. To
accomplish this will require greater cooperation, coordination, and integration among all
stakeholders throughout the RAP process. Locally-designed, RAP institutional frameworks have
proven to be effective mechanisms to facilitate a coordinated and integrated approach to resource
management and ensure meaningful public participation.
In March 1993, a Canada-United States roundtable discussion on institutional frameworks
was held to learn from nine institutional framework case studies from within and outside the
Great Lakes Basin, and develop guidance on RAP institutional frameworks to help achieve
implementation. Three areas of discussion were highlighted at the roundtable: essential
characteristics for RAP institutional frameworks; guidance to ensure linkages to other related
plans and to ensure complementary and reinforcing actions; and ways to embrace new
institutional frameworks to ensure a smooth transition from RAP development to implementation.
Based upon the roundtable discussions, recommendations include:
•	RAP institutional frameworks should be empowered to pursue their mission of restoring
impaired uses. Empowerment of RAP institutional frameworks would be demonstrated
by: a focus on watersheds or other naturally-defined boundaries to address upstream
causes and sources, and attain watershed "buy-in" for implementation; an inclusive and
shared decision-making process; clear responsibility and sufficient authority to identify
and pursue a road map to use restoration; an ability to secure and pool resources
according to priorities for action using nonprofit organizations or other creative
mechanisms; flexibility and continuity in order to achieve an agreed-upon road map to
use restoration; a strong commitment to broad-based education, and public outreach; and
an open and iterative RAP process that strives for continuous improvement.
•	Governments must adopt and reward a cooperative (rather than competitive) approach to
working with other stakeholders, agencies, and organizations. It is farther recommended
that open communication and information networks be developed across and within public
agencies and organizations, and existing or new RAP institutional frameworks be used as
mechanisms for coordinating and integrating planning and program functions at the local
level. This "bottom-up" approach to coordination through RAP institutional frameworks
should be complemented with "top-down" efforts to ensure intra- and interagency
initiatives are complementary and reinforcing by: explicitly recognizing the need for
coordination and integration of interrelated programs in agency mission statements; and
incorporating institutional arrangements necessary for desired coordination and integration
into agency program plans.
•	Governments need to recognize the value of RAP institutional frameworks as a means to
an end. RAP institutional frameworks can help build the capacity of government agencies
1

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to achieve their goals. Therefore, governments should adopt long-term, visionary goals
for Areas of Concern and commit to a customer-driven and value-added RAP process of
continuous improvement that shares decision-making power. It is further recommended
that RAP institutional frameworks consider establishing a partnership agreement for Stage
II RAPs to help empower stakeholders, capitalize on resources, clarify roles, ensure
integration, and increase communication. Such partnership agreements are consistent with
an ecosystem approach and could serve as an important milestone to be celebrated in the
Stage II RAP process. Such partnership agreements can also initiate the development of
local roundtables, similar in function to the Ontario Round Table on the Environment and
Economy, to help governments build consensus that will lead to the necessary
commitments and endorsements to achieve full RAP implementation and use restoration.
2

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I INTRODUCTION
The Great Lakes Remedial Action Plan (RAP) Programs of Canada and the United States
were initiated by a 1985 recommendation of the International Joint Commission's Great Lakes
Water Quality Board and formalized in the 1987 Protocol to the Great Lakes Water Quality
Agreement (GLWQA). The purpose of RAPs is to restore impaired beneficial uses in the 43
Areas of Concern in the Great Lakes Basin (Figure 1) through a three-staged planning process
(Stage I includes problem definition and description of causes; Stage II requires selection of
remedial and preventive measures; and Stage HI confirms restoration of impaired uses).
RAPs are unique in that the GLWQA states that RAPs shall embody a systematic and
comprehensive ecosystem approach (i.e. accounting for the interrelationships among land, air,
water, and all living things, including humans; and involving all user groups in management) and
that the Parties (i.e. the U.S. and Canadian federal governments), in cooperation with State and
Provincial Governments, shall ensure that the public is consulted in all actions undertaken
pursuant to RAPs (United States and Canada 1987). To say the least, this is a noble and
challenging charge to governments.
It can be argued that to ensure RAPs embody an ecosystem approach and achieve
meaningful public participation will require new approaches to management in Areas of Concern.
These new approaches will require greater cooperation, coordination, and integration among the
involved participants to transcend politically defined boundaries. For the purposes of this report
a hierarchy distinguishes these three forms of interaction. Cooperation needs to exist before
coordination can occur to integrate various agreed-upon functions or activities. Cooperation is
defined as a process whereby two or more parties agree to interact for mutual benefit. It should
be used as a means, not an end to itself Coordination can be both a process and a state whereby
two or more parties harmonize their decisions to collectively take action for a shared resource
or interest (DeLoe 1990). Integration is both a state and an end product achieved through
cooperation and coordination. Each process, state, or end result may be achieved through either
formal or informal mechanisms. The synergy created through cooperation, coordination and
integration would enable RAP institutional frameworks to incorporate an ecosystem approach to
remediation and prevention.
Indeed, RAPs are already achieving greater cooperation, coordination, and integration
through RAP institutional frameworks in Areas of Concern. Currently, 39 of the 43 Areas of
Concern have either a stakeholder group, basin committee, coordinating committee, public
advisory council, or comparable institutional framework broadly representative of environmental,
economic, and social interests in Areas of Concern (Table 1). In essence, each of these RAP
institutional frameworks is working to implement a locally-designed ecosystem approach in their
Area of Concern (Hartig and Vallentyne 1989).
Despite the progress that has been made toward institutional cooperation and coordination,
continued efforts are needed to ensure integration and full implementation of remedial and
preventive actions. The media-specific, command-and-control approach of traditional Great
3

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Figure 1. Forty-three Areas of Concern identified in the Great Lakes Basin.
Nlpigon Bay(
¦ThunderBayj
t Jacklish Bay
Peninsula
Harbour
<:-^pER IO
uPERlOfi\
'SI. Lotiii Bay/River
Torch Lake
Deer Lake-Carp Creek / River
Manistique River |
0
Menominee River (
Fox River /
| Southern Green Bay
Sheboygan River/ ^
V
Milwaukee EstuaryS
Waukegan Harbor I
O
s
* 0
V-
SI Maryt River
.Spanish River Mouth

)up°n
St. Lawrence River
(Cornwall I Massena)
I Severn Sound
Collingwood Harbour
Bay ol Quinle
Port Hope
Metro Toronto i
I White Lake
Saginaw River / Saginaw Bay
(Muskegon Lake
L.
oNtarjo_
'Oswego River
Hamilton Harbour I
SI. Clair River £ Wheatley Harbour
Clinton River
Rochester Embayment |
Eighteen Mile Creek
! Niagara River
Buffalo River
Detroit Rfverj
I Kalamazoo River Rouge River^
/"Grand Calumet River / R|W Ra)lin|
Indiana Harbor Canal
Maume* Riverl

Bit
"x£_.
Black River
- Presque Isle Bay
rAshtabula River
''Cuyahoga River

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Table 1. Remedial Action Plan institutional frameworks established in Great Lakes Areas
of Concern.
Area of Concern
Institutional Framework
1. Peninsula Harbour
Peninsula Harbour Public Advisory Committee
2. Jackfish Bay
Jackfish Bay Public Advisory Committee
3. Nipigon Bay
Nipigon Bay Public Advisory Committee
4. Thunder Bay
Thunder Bay Public Advisory Committee
5. St. Louis River
St. Louis River Citizens Advisory Committee
6. Torch Lake

7. Deer Lake-Carp Creek-Carp
River

8. Manistique River
Manistique River Partnership Council
9. Menominee River
Menominee River Remedial Action Plan Citizens Advisory Committee
10. Fox River/ Southern
Green Bay
Green Bay Remedial Action Plan Public Advisory Committee
North East Wisconsin Waters of Green Bay Tomorrow, Inc.
11. Sheboygan River/Harbor
Sheboygan County Water Quality Task Force
12. Milwaukee Estuary
Milwaukee Estuary Remedial Action Plan Citizens Advisory
Committee
13. Waukegan Harbor
Waukegan Harbor Citizens Advisory Committee
14. Grand Calumet River/
Indiana Harbor Canal
Citizens Advisory for the Remediation of the Environment Committee
(CARE)
15. Kalamazoo River
Kalamazoo River Public Advisory Council
16. Muskegon Lake
Muskegon Lake Remedial Action Plan Public Advisory Council
17. White Lake
White Lake Remedial Action Plan Public Advisory Council
18. Saginaw River/ Saginaw Bay
Saginaw Basin Natural Resources Steering Committee
Saginaw Basin Alliance
19. Collingwood Habour
Collingwood Harbour Remedial Action Plan Public Advisory
Committee
20. Severn Sound
Severn Sound Remedial Action Plan Public Advisory Committee
21. Spanish River
Spanish River Public Advisory Committee
22 Clinton River
Clinton River Remedial Action Plan Public Advisory Council
23. Rouge River
Rouge Remedial Action Plan Advisory Council
Friends of the Rouge
5

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Table 1 continued.
24. River Raisin
River Raisin Public Advisory Council
25. Maumee River
Maumee River Remedial Action Plan Advisory Committee
26. Black River
Black River Remedial Action Plan Coordinating Committee
27. Cuyahoga River
Cuyahoga Remedial Action Plan Coordinating Committee
Cuyahoga River Community Planning Organization
28. Ashtabula River
Ashtabula River Remedial Action Plan Advisory Council
29. Presque Isle Bay
Public Advisory Committee for the Presque Isle Bay Remedial
Action Plan
30. Wheatley Harbour

31. Buffalo River
Buffalo River Citizens Committee
Buffalo River Remedial Advisory Committee
Friends of the Buffalo River
32. Eighteen Mile Creek

33. Rochester Embayment
Monroe County Water Ouality Management Committee
34. Oswego River
Oswego River Remedial Action Plan Remedial Advisory Committee
35. Bay of Quinte
Bay of Quinte Public Advisory Committee
36. Port Hope
Port Hope Harbour Local Advisory Group
37. Metro Toronto
Metro Toronto Public Advisory Committee
38. Hamilton Harbour
Hamilton Harbour Stakeholder Group
Bay Area Implementation Team (BAIT)
Bay Area Restoration Council (BARC) _
39. St Marys River
St. Marys Binational Public Advisory Council
40. St. Clair River
St. Clair River Binational Public Advisory Council
41. Detroit River
Detroit River Binational Public Advisory Council
Friends of the Detroit River
42. Niagara River (Ontario)
Public Advisory Committee for the Niagara River Remedial Action
Plan
42. Niagara River (New York)
Niagara River Action Committee
43. St. Lawrence River
(Cornwall, Ontario)
St. Lawrence Public Advisory Committee
43. St. Lawrence River
(Massena, New York)
St Lawrence Remedial Advisory Committee
6

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Lakes management (e.g. separate programs for water quality, fish, wildlife, land, air, etc.) has
often led to "empire building" within disciplines and institutional gridlock. The Canadian and
United States commitment, through the GLWQA, to incorporate the ecosystem approach in the
RAP process has provided the catalyst for new, integrative approaches to management and a
greater impetus to overcome institutional gridlock. Remedial action planning is a cooperative
learning process that accounts for interrelationships among programs and organizations in an
attempt to accelerate the implementation of remedial and preventive actions to restore impaired
uses. RAP stakeholder groups, public advisory councils, and citizen committees can be viewed
as new institutionalized frameworks for social learning, opinion formation, and decision-making
for use restoration in Areas of Concern (Milbraith 1989).
In an effort to learn from different experiences with institutional frameworks, Environment
Canada and U.S. Environmental Protection Agency initiated a survey of selected institutional
frameworks within the Great Lakes Basin (i.e. Hamilton Harbour, Detroit River, The Greater
Toronto Bioregion, Canadian Healthy Communities Program, Cuyahoga River, St. Lawrence
River) and outside the Great Lakes Basin (i.e. Lake Champlain, Chesapeake Bay, Puget Sound).
Information on the case studies was compiled into a background report for a March 1993
Canada-U.S. roundtable discussion in Windsor, Ontario on RAP institutional frameworks (see
Appendix II for summaries of the nine institutional framework case studies). For the purposes
of this report, the term institutional framework refers to the organization and mechanism of
achieving cooperative and coordinated (and where necessary integrated) planning and action
among different entities and organizations whose mission impacts or is impacted by uses or users
in Areas of Concern.
The purpose of the roundtable discussion was to learn from the case studies and develop
guidance on RAP institutional frameworks to help achieve plan implementation. The roundtable
approach provided an open forum in which stakeholders within and outside the basin were able
to express collectively their ideas and experiences in a cooperative and mutually reinforcing
process. Approximately fifty people participated in the roundtable discussion (see Appendix I
for a list of roundtable participants). Presentations on the nine case studies provided insight on
the mechanisms used to facilitate cooperation, coordination, and integration within the
institutional frameworks. Later, two concurrent breakout sessions were used to discuss in greater
detail the case studies and answer questions pertaining to: essential characteristics for RAP
institutional frameworks; guidance to ensure linkages to other related plans and to ensure
complementary and reinforcing actions; and suggestions to help embrace new RAP institutional
frameworks to ensure a smooth transition from RAP development to implementation. This
report presents a synthesis/synopsis of the roundtable discussions and information on the nine
institutional framework case studies in an effort to help RAP practitioners learn from each others'
experiences.
n SYNOPSIS OF WORKSHOP DISCUSSIONS
In an effort to summarize the roundtable discussions, all information and recommendations
are organized and presented in three subsections consistent with the questions asked in the
7

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breakout sessions. These include: essential characteristics for RAP institutional frameworks;
guidance to ensure linkages to other related plans and to ensure complementary and reinforcing
actions; and suggestions to help embrace new RAP institutional frameworks to ensure a smooth
transition from RAP development to implementation.
A. Essential Characteristics of RAP Institutional Frameworks to Ensure Use of an Ecosystem
Approach to Use Restoration
For the purposes of this report, roundtable discussions on essential characteristics of RAP
institutional frameworks are summarized into seven categories. These essential characteristics
include: a watershed perspective; broad-based participation to achieve implementation; clear
responsibility and sufficient authority; human and financial resource support; flexibility and
continuity to achieve an agreed-upon road map to use restoration; education and outreach; and
commitment to action planning within a strategic framework. These characteristics are inherent
in both development and implementation of RAPs.
1. A Watershed Perspective
To incorporate an ecosystem approach in RAPs will require an ability to transcend
politically defined boundaries and address causes and effects of use impairments within
watersheds or other defined natural systems. Consistent with an ecosystem approach, roundtable
participants identified two strategies to overcome limitations imposed by political boundaries and
achieve a more coordinated and integrated approach to RAPs: watershed planning; and
delineation of "effects" and "source" Areas of Concern.
The watershed approach to planning provides a framework to evaluate natural resource
problems using a natural systems' approach (Water Environment Federation - Water Quality 2000
Steering Committee 1992). This approach respects the natural boundaries delineated by the
watershed within the larger bioregion to holistically account for: upstream and downstream
sources and effects of pollution in a systematic and comprehensive strategy for remediation and
prevention; and sustainable management of human activities within the Great Lakes Basin
Ecosystem.
A watershed perspective encourages a sense of stewardship from people living, working,
and recreating within the watershed. Crombie (1992) notes that this sense of stewardship can
emerge when people are prepared to back a common vision that takes into account the long-term
health and well-being of the watershed. The adoption of a watershed perspective enables a RAP
institutional framework to recognize upstream stakeholders in watershed planning as equal
partners. RAP institutional frameworks can be valuable mechanisms to communicate with other
upstream communities and organizations to attain watershed "buy-in". A commonality of
geography and economic activity links one community to the next, and communities may come
to realize that there will be certain problems that only can be solved collectively. Consequently,
the watershed approach can serve as an incentive to overcome inter-jurisdictional fragmentation
and gridlock through consensus-building within the watershed.
8

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The Rouge River, Rochester Embayment, and Hamilton Harbour are three examples of
Areas of Concern where a watershed approach to RAP development and implementation is
practiced. Each Area of Concern has recognized the value, both monetary and non-monetary,
in delineating the watershed as the unit for remedial action planning. It became evident after
years of independent clean-up activities in the lower Rouge River that downstream actions alone
would not improve water quality. The Rouge River adopted a comprehensive watershed
approach to urban runoff and combined sewer overflow remediation that covers the entire 1,210
km2 (467 square miles) watershed. Subsequently, this watershed approach to planning and
management has been recommended for the entire State of Michigan, including establishment of
watershed organizations in cooperation with local governments to implement water quality
management measures (Michigan Department of Natural Resources 1990). The Rochester
Embayment Area of Concern has placed emphasis on multi-media watershed planning and has
not one, but four separate plans for clean-up. The RAP is made up of a plan for the Rochester
Embayment proper and watershed plans for each of the three major tributaries that flow into the
Rochester Embayment. Similarly, the Hamilton Harbour RAP addresses the entire watershed and
endorses an ecosystem approach to planning and action.
Depending upon the range of authority, legislative mandates, and relationships among
stakeholders, the watershed approach may not be the most feasible approach to use restoration
and prevention. No one agency has unilateral authority over an entire watershed, therefore
attempting to get buy-in from the entire watershed may be an onerous task as not all political
jurisdictions are necessarily willing to involve themselves (Donahue 1988). A RAP institutional
framework may need to define smaller geographic units for management as noted above for the
Rochester Embayment.
Delineation of "effects" and "source" Areas of Concern by RAP institutional frameworks
is another way of accounting for upstream contributions to use impairments. The "effects" Area
of Concern would consist of that portion of the tributary/harbor/nearshore Great Lakes that
manifests use impairments. The "source" Area of Concern would consist of that portion of the
entire watershed from which pollutants were entering and contributing to use impairments in the
"effects" Area of Concern.
This two-staged approach factors in the upstream contributions to the impaired uses within
the Area of Concern. However, a weakness to this approach may be the reluctance from
upstream communities and users to buy-into a process that did not initially account for them.
Some upstream communities may also have a lack of interest or information on how upstream
actions impact the downstream areas and the relationship to the RAP. This may hinder
implementation of the RAP and limit the extent of remediation that can be accomplished. To
offset this weakness, it will be important to secure upstream stakeholder involvement as soon as
possible in Stage II RAP development to ensure accountability for implementation. The Detroit
River RAP is one example of where this approach is being applied (Michigan Department of
Natural Resources and Ontario Ministry of the Environment 1991).
9

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Each approach to planning and action has merit. The challenge is to comprehensively
address all significant sources and effects of pollutants in order to sustain long-term ecosystem
health for an Area of Concern. Management mandates must recognize watershed boundaries in
order to achieve a more coordinated and integrated strategy for remediation and prevention.
2. Broad-Based Participation to Achieve Implementation
The RAP process is intended to build consensus about the necessary remedial and
preventive actions to restore uses by seeking broad-based public participation. Each RAP
stakeholder group, basin committee, coordinating committee, public advisory council, or citizen
committee is made up of individuals broadly representative of environmental, economic, and
social interests in an Area of Concern (Table 1). Such RAP institutional frameworks must be
inclusive to be able to take advantage of the knowledge and expertise stakeholders possess about
their Area of Concern and create the political will for plan implementation.
Important in the multi-stakeholder, multi-sectoral RAP process is the approach taken by
the lead government agency to involve stakeholders. While traditional, top-down, command-and-
control actions may be necessary to regulate specific sources of pollution, the RAP process might
be better based upon a facilitation/management approach, and not just control. The Worldwatch
Institute (1993) notes that prescriptive, media-specific, regulatory tools have proven to be
ineffective and unlikely to spur the breadth of changes necessary to achieve full use restoration.
Such a control approach may be seen as telling stakeholders that they are not to be directly
involved in determining the future of their communities. On the other hand, the
facilitation/management approach steers or guides the process to ensure it stays on track and
encourages a partnership with stakeholders in restoring uses. Roundtable participants emphasized
that lead governments are more likely to succeed if they demonstrate a strong emotional
commitment to RAPs and a facilitation/management approach. Commitment to this
facilitation/management approach has greater potential of assuring community ownership of the
RAP as it permits distribution of responsibilities and shares decision-making power. Eiger and
McAvoy (1992) have concluded that one element of a successful RAP process is the presence
of a community leader or organizer with primary responsibility for forming a broad-based RAP
institutional framework and ensuring public participation and outreach.
Such inclusive RAP processes which share decision-making power should be viewed as
helping to design local institutional frameworks that build bottom-up support for plan
implementation. A bottom-up approach can also help adapt top-down initiatives to local
situations and serve as a catalyst for action. RAP institutional frameworks that are inclusive and
share decision-making power can:
•	provide a forum for mutual understanding and new perspectives;
•	help establish trust among stakeholders which is essential for plan implementation; and
•	help orient decision-makers to the process of an ecosystem approach to use restoration.
10

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The New York State Department of Environmental Conservation and the Federation of Lakes
Associations, Inc. (1990) also prescribe an inclusive planning process as it may serve as a
catalyst in building political and social coalitions which are needed to sustain a positive, long-
term management effort. Further, sharing decision-making power within a multi-stakeholder,
RAP institutional framework can also be a good mechanism of getting organizations/entities/
communities to do what might not be in their own parochially-defined self-interest. Christie et
al. (1986) have described this as enlightened self-interest (e.g. enlightenment that because all
stakeholders in a watershed share a common problem, they must be committed in their own
interest to its solution).
It should be recognized that each stakeholder in the RAP process not only has a
responsibility to their RAP institutional framework, but a responsibility to go back to their
constituency or sector and educate and elicit support from them. An important goal for the RAP
process would be for each stakeholder in an Area of Concern to become a partner in remediation
and prevention. Roundtable participants thought it is particularly valuable to have local elected
officials represented on RAP institutional frameworks. Such broad-based participation and shared
decision-making power are viewed as critical success factors in the Hamilton Harbour and
Cuyahoga RAPs, and in Puget Sound, Chesapeake Bay, and Lake Champlain.
3. Clear Responsibility and Sufficient Authority
Broad-based participation that is brought about by an inclusive, shared, decision-making
process must result in each stakeholder having a meaningful role in the RAP process.
Meaningful participation is dependent on the clear delineation of responsibilities of all
stakeholders, and sufficient authority to fulfill RAPs' mission and goals for restoring impaired
uses. Roundtable participants noted that RAP institutional frameworks must also be free of
gnve.rnme.ntal bureaucratic processes to ensure effectiveness and timeliness. Care must be taken
to ensure that the RAP process is responsive to the legitimate public agencies who are legally
responsible and empowered to act.
To achieve use restoration, the plan should be viewed as a road map sufficiently detailed
to ensure accountability of implementing organizations, and yet concise enough to ensure broad
communication of the critical path to use restoration. Priority elements for identifying the road
map to use restoration include:
•	broad-based agreement on goals, objectives, indicators, and benchmarks to measure
progress and confirm use restoration;
•	identification of key actions, responsibility, and sequencing of actions to restore each
impaired use;
•	demonstration of commitments and endorsements (e.g. formal or informal agreements)
from responsible parties and stakeholders; and
11

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description of important activities to resolve issues that delay remediation or prevention.
Once a clear road map to use restoration has been laid out, RAP institutional frameworks
n o compare the recommended actions with the existing authorities and regulatory and non-
OI^ m^c'ian'sms to identify any gaps. If gaps exist, RAP institutional frameworks should
power to recommend or help create new authorities, statutes, enforcement mechanisms,
r o er means to. implement RAP recommendations; monitor the progress of implementation;
• en®ure responsible parties are held accountable. Such empowerment can increase individual
r,	(^Water Environment Federation - Water Quality 2000 Steering
• p.-1 66	Partnership agreements and other cooperative initiatives, like financial
.. IVCS an tec^D'ca^ assistance, can also serve as effective mechanisms to facilitate and
n„up^.rem iatl0n and prevention. If cooperation cannot achieve the necessary remediation or
j, . ,T:regU a|Pry or ot^er enforcement mechanisms will be needed to ensure implementation.
_t . ?"?! noAted that some roundtable participants expressed concern for liability of RAP
nnnrna°h ^ • combination of a "carrot" (i.e. incentives) and "stick" (i.e. disincentives)
tn L / t0.1™P1®mentation has proven to be effective (Hartig and Zarull 1992). There needs
t .• nancia ai^ technical resource incentives to encourage action and penalties or sanctions
to discourage lack of action.
4. Human and Financial Resource Support
• ^eac*erskip 's essential to the RAP process that includes demonstrated
nirvw^w ^ semor management and a clear understanding of the lead agency role in the
_„ *. owe^®r> government alone is not capable of providing all the resources necessary to
diversitv f mU	r process is effective and timely. Current fiscal strain and the
aovemL !	" WltWn government cal,s for cooperative initiatives among
become nnrtn ^' st®te^Prov™c^a^ atK* local), private industry, and communities alike to
become partners in remediation and prevention.
activities'1^^°St	Syfem	a govemment agency is the budget, as it controls what
develonmentm^'ahT^ ^	and WhCD (0sborae aad Gaebler 1992). Expedient RAP
operations anT? b!a|c)lieved throuehgreater autonomy in RAP institutional frameworks' fiscal
resou ^T m * !?1 t0 PTUe innovative	mechanisms. Pooling of financial
remSoi W3tershed may better account for the cumulative effects of pollution and
sustained^m^h80^??	is equally important as financial resource development A
rfpvpinn a ¦ mCn °	participation will elicit a diverse range of expertise to help
fl992WW 11111)161116111 RAPs- ^ * consistent with the recommendation of Eiger and McAvoy
age!lcies must recognize the importance of efforts that effectively
imolementntm . signiftcantly engage a wider segment of the general public in RAP
mpl mentation, and support those efforts. RAP institutional frameworks are mechanisms by
which to organize the areas of expertise into specific work groups or functions.
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Ideally, RAP coordinators should be senior level staff, rather than junior level staff, in
order for RAPs to obtain a higher profile within an agency or ministry, thus ensuring greater
authority in accessing technical staff/resources and making necessary decisions to expedite the
RAP process. An alternative would be to follow the approach taken by the Grand Calumet
River/Indiana Harbor Canal Citizens Advisory for the Remediation of the Environment (CARE)
Committee which has had a junior level RAP coordinator, but the senior Commissioner of
Indiana Department of Environmental Management chairing the CARE Committee. Roundtable
participants recognized the unique interjurisdictional and interagency difficulties of binational
connecting channel RAPs and suggested that the federal governments consider hiring independent
facilitators to further develop or update their Stage II documents. Whatever approach is taken,
roundtable participants noted the importance of using local staff within the Area of Concern or
watershed to assist in the organization of institutional frameworks. Consistent participation from
technical governmental staff is needed in all RAP processes.
The use of nonprofit organizations has proven to be a catalyst for RAP activities, which
complement governmental efforts. Eiger and McAvoy (1992) have recommended that local and
state RAP coordinators should give serious consideration to helping establish a nonprofit
organization, if one does not exist in their Area of Concern, to increase their ability to leverage
additional resources and provide greater flexibility in organizing public activities. The Cuyahoga
River Community Planning Organization (CRCPO) is a nonprofit organization that has played
a pivotal role in moving the RAP forward by providing technical, educational, and staffing
resources that augment staff support provided by regional and state agencies (Beeker et al.
1991). The Bay Area Restoration Council (BARC) for Hamilton Harbour not only promotes and
assesses RAP implementation, but solicits and acquires donations, gifts, and legacies in
furtherance of RAP goals. Other examples of nonprofit organizations established to complement
RAP institutional frameworks are summarized in Table 2. Such initiatives are invaluable
components of local RAP programs.
Securing financial and human resource support for the RAP throughout the watershed
recognizes that everyone who contributes to the problems must also be part of the solution.
Many RAPs have already acted as a catalyst for action and initiated partnerships among
government, industry, and local public interest groups (Hartig and Law 1992). RAP institutional
frameworks should be empowered to help secure and pool resources according to priorities for
action.
5. Flexibility and Continuity to Achieve an Agreed-Upon Road Map to Use
Restoration
RAP institutional frameworks can be instrumental in achieving broad-based agreement on
the road map to use restoration. As planning and implementation are pursued simultaneously
throughout the RAP process, there needs to be flexibility to accommodate change (i.e. as a result
of new knowledge or information), and continuity to ensure progress and accountability for
action. In some cases, broad-based agreement on the path to use restoration may not always be
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Table 2. Activities and functions being performed by nonprofit RAP institutional
frameworks in the Great Lakes Basin.
Nonprofit Organization
Purpose
Activities and
Functions
North East Wisconsin
Waters of Green Bay
Tomorrow, Inc.
To provide information for decisions related to
water quality in the Lower Green Bay, Fox, and
Wolf River watersheds in conjunction with the
implementation of the Lower Green Bay RAP.
•	independent
analysis
•	fund raising
•	research
Saginaw Basin Alliance
To promote the preservation, restoration, resource
management, planning, and responsible
development through basin-wide citizen
involvement, education, and cooperation.
• public education
and outreach
Friends of the Rouge
To promote/advocate the restoration of the Rouge
River through participation and education of
citizens in cooperation with agencies, private
interests, and governments concerned.
•	public education
and outreach
•	fund raising
Cuyahoga River Community
Planning Organization
To support the goals of the Cuyahoga River RAP
with additional technical and financial resources
for planning, and to develop support for programs
in public involvement, education, and research.
•	fund raising
•	public education
and outreach
•	planning
coordination
•	research
Friends of the Buffalo River
To promote, preserve, protect, and take action
where necessary for the natural and historical
environment of the Buffalo River and the environs
for the benefit of the local community.
•	fund raising
•	public education
and outreach
Bay Area Restoration Council
To provide an advisory function to the
implementation of the Hamilton Harbour RAP that
oversees the coordination and monitoring of
implementation measures.
•	independent
auditing
•	public outreach
and education
•	fund raising
Friends of the Detroit River
To provide and encourage public participation in
the Detroit River RAP and to promote the social,
economic and environmental health of the Detroit
River ecosystem.
•	fund raising
•	public education
and outreach
achieved, therefore guidelines to resolve conflict or conflict resolution techniques may be
necessary and minority opinions should be accepted.
A greater understanding of Area of Concern ecosystems has rendered the need for more
flexible and adaptable forms of institutional frameworks to account for the interrelationships
among different organizations, agencies, and entities. RAP institutional frameworks should be
flexible to coordinate the specific spheres of expertise and pursue simultaneously
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remediation/prevention and necessary investigations. The RAP process is intended to be iterative
and to accommodate new data/information and stakeholders.
The traditional command-and-control approach practiced by governments does not readily
support coordinated efforts due to the independent nature of government agencies and the
separate approval mechanisms required to take action. A RAP institutional framework that
encourages collaboration, particularly among public management agencies at all levels of
government, can help remove obstacles and embrace a mission-driven approach to better
coordinate the decision-making process. A mission-driven institutional framework is a more
flexible management structure as it informs stakeholders what needs to be accomplished, but does
not dictate how it should be accomplished (Osborne and Gaebler 1992). This reinforces the need
for a facilitation/management approach for RAPs.
Continuity in both the RAP process and its' membership is essential to identify the critical
path to use restoration. To achieve continuity, a common understanding of the RAP process and
path to use restoration must be achieved and sustained, and institutional memory ensured.
Empowered RAP stakeholder groups, coordinating committees, and public advisory councils are
essential institutional frameworks to keep the RAP process on track and ensure continuity, as
there has often been a high turn over rate of government RAP coordinators in some Areas of
Concern. Such institutional frameworks can also provide continuous and vigorous oversight to
ensure progress toward remediation and prevention.
6. Education and Outreach
The RAP process is a learning process for all stakeholders. Through a RAP institutional
framework, stakeholders practice cooperative learning through listening, sharing, discussion, and
participating in RAP development and implementation. To facilitate the RAP process and
provide support to a RAP institutional framework, governments can ensure that priority is placed
on stakeholder education by: clarifying and documenting roles and responsibilities; emphasizing
education/training that meets the needs of all stakeholders; ensuring strong linkages between
scientific institutions and non-scientific, non-technical stakeholders in the RAP process; allocating
sufficient resources for education and training; performing periodic "reality checks"; empowering
people; and adopting a positive reinforcement system. Because the success of a RAP institutional
framework hinges on interaction and cooperation among all stakeholders, priority should be
placed on cooperative learning and education.
However, equally important are the public education and outreach activities that create
the necessary political will for remediation and prevention. RAP institutional frameworks can
be instrumental in establishing community outreach strategies and ensuring broad distribution of
responsibilities among stakeholders. Education, from primary school children to business
professionals, is essential to bring about the societal changes necessary to ensure prevention and
remediation. Through education, citizens can take immediate actions to begin restoration and
practice pollution prevention within their community. The Saginaw River/Bay and Rouge River
Areas of Concern have both benefitted from the incorporation of water quality educational
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projects within the areas' school systems (i,e. Saginaw River Journal Project and the Rouge River
Interactive Water Quality Project) (IJC 1991a). RAP educational programs can extend to
agricultural and industrial practices, urban (redevelopment, land-use planning, resource
management, etc. to achieve stewardship of water and land resources in Areas of Concern.
RAPs have also initiated public outreach activities to complement educational programs.
Annual cleanup days have spurred environmental citizenship and elevated the profile of RAPs
(e.g. Rouge River, Green Bay, Buffalo River, Cuyahoga River, Clinton River, Metro Toronto,
etc.). The Cuyahoga River Community Planning Organization (CRCPO) has played a major role
in education and outreach activities within its Area of Concern, specifically coordination of
Riversweep, public opinion polling, and nonpoint source education. Roundtable participants
concluded that RAP institutional frameworks, like the Cuyahoga River Coordinating Committee
and Hamilton Harbour's Bay Area Restoration Council, should be empowered to host annual
"State-of-the-RAP" events and/or prepare annual RAP progress reports to measure and celebrate
progress in restoring uses.
7. Commitment to Action Planning within a Strategic Framework
Remedial action planning is a three-staged iterative process that is guided by broad-based
participation and a flexible, but agreed-upon road map to restoration. RAPs, specifically Stage
II, are composed of action-oriented strategies that identify responsible parties and the key
sequencing of actions to attain full use restoration in Areas of Concern. Strategic planning, like
remedial action planning, strives for continuous improvement. Strategic planning focuses
decisions and actions that shape and guide the mission and activities of an organization (Bryson
1988).
As planning and implementation proceed simultaneously throughout the RAP process,
identification of what can be done and what needs to done is pursued simultaneously. Simply
put, RAPs should be recognized as an open and iterative process in which remediation/prevention
and investigation should proceed in tandem, incrementally. The Hamilton Harbour Stage II RAP
is one example of this strategic approach to planning through the development of Stage HA and
Stage IIB reports. Stage HA identifies recommendations on what is being done and what needs
to be done, when, and who is responsible, while Stage IIB secures the commitments to implement
remedial and preventive actions.
Driven by a mission, rather than rules or functional mandates, strategic planning enables
RAP institutional frameworks to have a futures-thinking capability that can identify critical issues
affecting the successful implementation of RAPs (Milbraith 1989). A mission tells an
organization where it wants to be, rather than a mandate that tells an organization what it should
be doing at the present time. This is precisely the intent behind the 14 use impairments
identified in the GLWQA These use impairments are intended to help drive the RAP process,
help stakeholders and organizations pursue their mission of restoring uses, and achieve greater
accountability. Long-term commitment to, and attainment of, a mission are achieved through the
implementation of a series of short-term strategies that are monitored, reported, and celebrated
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as the RAP progresses toward use restoration. As a management tool, strategic planning alerts
RAP institutional frameworks to externalities - opportunities and threats that may help or hinder
implementation. Threats can be addressed and opportunities pursued by involving parties who
have an interest in the outcome, thus potential obstacles can be overcome in order to build
consensus among stakeholders (Kaufman and Jacobs 1987). Continued emphasis must be placed
on accelerating implementation of existing remedial and preventive programs, while identifying
the schedule and sequencing of actions beyond existing programs to fully restore beneficial uses
(IJC 1991a).
B. Guidance to Ensure Linkages to Other Related Plans and To Ensure Complementary and
Reinforcing Actions
Cooperation, coordination, and integration of key functions and activities need to take
place at all levels of government, with local communities, and with the private sector to ensure
a systematic and comprehensive ecosystem approach is taken to restore impaired uses within
Areas of Concern. An ecosystem approach to remediation and prevention requires explicit
linkages between and among current media-specific programs and agencies. Such linkages are
accomplished on a systematic and incremental basis in order to serve immediate needs. Multi-
sectoral, multi-stakeholder RAP institutional frameworks provide a mechanism to form linkages
to other related programs and ensure actions are complementary and reinforcing.
Cooperation and coordination should be viewed as processes by which to account for
media-specific mandates and programs, and form linkages between RAPs and other related
planning efforts (e.g. land use, fishery management, etc). To re-orient government processes
from a competitive culture to one that encourages integration, a commitment to cooperative
management for a shared resource is required (Mitchell 1990; Donahue 1988; Francis et al.
1979). Communication among and across organizations and agencies is primary to initiate
cooperation and coordination. Further, communication facilitates working relationships to
integrate planning functions and helps prevent management actions from being at odds with one
another.
For a RAP to be accepted on a broad scale and be effective, its mission needs to be
broadly communicated to all stakeholders that impact or are impacted by use impairments. RAP
institutional frameworks must ensure communication channels are open and accessible to increase
the flow of information to generate a common understanding throughout the Areas of Concern.
By creating awareness through cooperative learning, a RAP's mission is reinforced and additional
support is acquired for implementation of remedial and preventive actions. This is particularly
important where the RAP may not be a priority and cannot be realistically implemented on its
own. The more people and plans that explicitly acknowledge interrelated problems and reinforce
common goals, the more support there will be for a systematic and comprehensive ecosystem
approach to remediation and prevention (IJC 1991b).
Linkages among interrelated planning initiatives can be best accomplished at the local
level where community values, priorities for action, and accountability can be readily determined.
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Roundtable participants suggested that there is greater will at the local level to implement RAPs.
This can be partially attributed to the direct impact use impairments has on the quality of life
within communities and the perceived future benefits derived from remediation and pollution
prevention. Thus, there is generally more incentive at the local level to establish linkages and
account for interrelationships.
The focus on remediation or other reactive measures should not result in losing sight of
other problems - specifically anticipatory planning activities for pollution prevention. Roundtable
participants emphasized that an ounce of prevention is worth a pound of remediation.
Roundtable participants suggested that partnership agreements, Memoranda of
Understanding, or other mechanisms of empowerment of new or existing river/harbor/watershed
boards, authorities, or councils are effective mechanisms to coordinate and integrate planning
functions within a watershed or other identified ecological management units (e.g. bioregion).
Indeed, empowerment of communities to meet their basic needs and care for their local
ecosystem is what was called for in the '92 Global Forum held in conjunction with the United
Nations' Conference on Environment and Development held in Rio de Janeiro during 1992 (The
Centre for Our Common Future and the International Facilitating Committee 1992). The success
of such empowerment initiatives depends on: the capacity of local communities to organize
themselves and participate in projects; integration of local knowledge and environment; access
to natural and financial resources; environmentally sound technology; government support; access
to information and public accountability; external support; and a capacity to influence
development priorities.
Solving the persistent environmental problems found in urban/industrial complexes located
in many Areas of Concern will require strong linkages with urban planning and design.
Therefore, it is critical that RAP efforts are integrated with municipal and regional planning.
Greater emphasis must be placed on ensuring stakeholder representation from municipal and
regional planning in the RAP process, and translating RAP findings and recommendations into
regional and local land use plans and zoning by-laws/ordinances.
The "bottom-up" approach to ensuring linkages needs to be complemented with "top-
down" management to ensure agency programs and initiatives are complementary and reinforcing.
"Top-down" support for coordination and integration can be demonstrated by senior management
acknowledging the need for coordination/integration in program mission statements, and by
assigning staff via annual work plans to promote coordination/integration. Federal, state, and
provincial commitment to a facilitation/management approach is needed to adapt larger planning
initiatives to local, site-specific problems. As an example, the Puget Sound Growth Management
Act directs all affected jurisdictions to plan at a multi-jurisdictional level where issues are of
regional significance. This approach enables the jurisdictions to accommodate local values by
integrating planning functions through local governments, rather than implementing broad policy
statements or programs developed by centralized state, provincial, or federal staff,
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Roundtable participants suggested that high ranking local agency representatives be
involved in the process of coordination and integration. This would help ensure "bottom-up" and
"top-down" support for inter- and intra-agency cooperation and coordination through the provision
of technical resources and seed money. This approach is reflected in the development and
implementation of RAPs along the north shore of Lake Superior through the Lake Superior
Program Office. The staff is composed of representatives from several provincial and federal
agencies who work together on integration and program delivery. The end result is partnerships
among government, industry, and local interest groups that coordinate and catalyze the programs
and actions. Another example of effective cooperation and coordination is among the Ontario
Ministry of the Environment RAP coordinators for the upper connecting channels (i.e. St. Marys
River, St. Clair River, Detroit River) who are located in the same office and have close working
relationships among themselves and with Canada-Ontario Agreement management. In the United
States, the federal and state governments are incorporating RAPs into each state water quality
management plan which helps ensure an integrated approach across media-specific program areas.
Knaap (1993) offered an another mechanism to ensure actions among government
agencies are complementary and reinforcing. He suggested the generation of coordination
statements that are developed cooperatively by state and local agencies to indicate how agency
rules, regulations, and activities affect RAP implementation. Three possible avenues to ensure
development of such coordination statements include: legislation by provincial or state
governments; grant incentives; or withhold revenues from those local governments and state or
provincial agencies whose rules, regulations, or activities are found to inhibit RAP
implementation.
A cooperative, facilitation/management approach to integration promotes common goals
and desired outcomes, yet does not threaten individual authority of agencies. However, trade-offs
are inevitable to achieve effective linkages among and between agencies and other
organizations/entities/individuals to overcome obstacles. To achieve full use restoration, RAP
institutional frameworks will need to address a number of obstacles to developing linkages with
other planning efforts. Obstacles include:
•	limited, media-specific, and single objective agency mandates that restrict incorporation
of an ecosystem approach;
•	perceived loss of jurisdictional control;
•	insufficient priority for RAPs; and
•	interagency competitiveness for resources.
These obstacles present a challenge to RAP institutional frameworks, but also justify the need
to link RAPs to other related planning efforts. Successful implementation of RAPs is dependent
upon the generation of socially acceptable, economically feasible, and politically viable solutions
(Hartig et al. 1992). The benefits of linking RAPs to other related planning efforts outweigh the
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disadvantages. The benefits include:
•	pooling resources to accomplish common ends;
•	achieving a common understanding of problems, causes, and solutions;
•	determining priorities for action;
•	achieving long-term sustainability through use of a comprehensive ecosystem approach,
and
•	generating added public support and stewardship as other stakeholders become part of the
planning process.
The complementary and reinforcing actions that are generated as a result of coordinating
and integrating planning functions can only increase the credibility of RAPs within the Great
Lakes Basin. Roundtable participants suggested that RAPs must be seen as part of a larger Great
Lakes management effort To help ensure a Great Lakes Basin Ecosystem perspective, RAPs
need to recognize larger planning efforts that impact the implementation of RAP
recommendations (e.g. lakewide management plans, coastal management plans, fishery
management plans, land use/official plans, economic development plans, etc.). Periodic review
of plans will be needed to ensure the process stays on track and coordination and integration are
achieved. Roundtable participants noted that multi-disciplinary workshops and roundtables for
each Great Lake might be useful tools for tracking progress and ensuring coordination and
integration.
C. Embracing New RAP Institutional Frameworks to Ensure a Smooth Transition front RAP
Development to Implementation
Colborn et al. (1990) suggest that RAPs represent the major test of the ecosystem
approach and are the means through which the ecosystem approach will involve and affect large
numbers of people and organizations. Governments are now being asked to be inclusive, account
for interrelationships among agencies, departments, and organizations, and share decision-making
power. To say the least, this is an enormous challenge. One frequently asked question is: "What
can be done to help governments embrace/endorse new institutional frameworks as we move
from RAP development to implementation?"
The introduction of RAPs into the management of the Great Lakes Basin eight years ago
required governments to embrace a new way of thinking and a new way of doing business. As
a result of the commitment to an ecosystem approach, governments are learning to work in
partnership with local citizens - the beneficiaries of and contributors to remedial action planning.
The success of RAPs depends upon continued public involvement; effective communication and
cooperation; resource commitments; addressing research needs; building a record of success;
effective use of an ecosystem approach and progress toward sustainable development; and
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recognition of personal responsibility (Hartig and Zarull 1992). These key success factors
emphasize the need for governments to adopt long-term, visionary goals and commit to a
customer-driven and value-added process of continuous improvement that shares decision-making
power. Value-added means using human and financial resources in a complementary fashion to
help produce a desired outcome. Currently, 39 of the 43 Areas of Concern have a stakeholder
group, public advisory council, basin committee, or coordinating committee to complement and
enhance the efforts of governments in the development and implementation of RAPs. In
addition, nonprofit organizations have also been established in seven Areas of Concern (Table
2).
Such RAP institutional frameworks are essential to building strong coalitions to create the
political will for implementation. Governments need to recognize the value of RAP institutional
frameworks as a means to an end. These institutional frameworks can help build the capacity
of government agencies to achieve their goals. This concept of building the capacity of
government agencies to achieve RAP goals has been a working principle in the Cuyahoga River
RAP, the Cuyahoga River Community Planning Organization, the Hamilton Harbour RAP, the
Bay Area Implementation Team, and Bay Area Restoration Council. Benefits include:
establishing private/public partnerships; pursuing alternative funding sources and pooling
resources; building grassroots/community support; augmenting special projects with additional
technical resources; and building community pride by celebrating successful community activities.
A facilitation/management approach to the RAP process will help ensure a smooth
transition from development to implementation. Roundtable participants suggested that RAP
institutional frameworks be free of governmental, bureaucratic processes to help ensure a smooth
transition from RAP development to implementation. Guided by a common mission rather than
rules, RAP stakeholders can work cooperatively toward reaching agreement on the critical path
to use restoration, yet can achieve the flexibility necessary to adapt to changing circumstances
as new ideas, issues, or partners emerge. Further, long-term commitment to the mission provides
continuity in the RAP process. A RAP workshop at the International Joint Commission's 1989
Biennial Meeting emphasized the need to sustain meaningful involvement of all stakeholders in
the RAP process - based on a cooperative, rather than an adversarial approach (Hartig et al.
1991). Sustaining meaningful public participation from RAP development through
implementation is viewed as essential.
Roundtable participants suggested that partnership agreements are an effective mechanism
to unify the diversity of stakeholders to embrace a common vision and new institutional
structures, and help ensure a smooth transition from RAP development to implementation. A
partnership agreement is typically a succinct vision statement and a set of principles that is used
to address and resolve a problem. Partnership agreements do not ignore federal, state, or
provincial solutions, but rather rely first on community stakeholders and organizations closest to
the problem to determine what solutions are needed. The number of partners who sign the
agreement is unlimited. For example, the partnership agreement for the Grand Traverse Bay
Watershed Initiative has over 100 businesses, agencies, organizations, and citizen groups as
signatories (Johnson and Stifler 1993). Emphasis is placed intentionally on identifying common
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ground among partners in a cooperative, positive, and reinforcing fashion. Experience has shown
that this approach increases trust among stakeholders. Further, signing the partnership agreement
creates a sense of empowerment to personally work on solving the problems. Othef benefits of
partnership agreements include: serving as a tool for capitalizing on existing programs and
pooling resources; serving as an instrument to demonstrate watershed 1 buy-in coalition
support in various grant applications to private foundations and government agencies; clarifying
roles and responsibilities of various partners to ensure coordination and integration; and
increasing communication and education among all parties. RAP institutional frameworks should
consider establishing a partnership agreement for Stage II RAPs to help empower stakeholders,
capitalize on resources, clarify roles, ensure integration, and increase communication. Such
partnership agreements are consistent with an ecosystem approach and could serve as an
important milestone to be celebrated in the Stage II RAP process.
Partnership agreements can also serve as a mechanism to initiate the development of local
roundtables in Areas of Concern. Roundtables provide an opportunity for all stakeholders in the
RAP process to become more active partners in the transition from development to
implementation. A roundtable is defined as a tool to guide/assist the decision-making process
that:
•	ensures balanced, multi-sectoral, multi-stakeholder representation in a non-hierarchial
forum;
•	provides an opportunity to generate a mutual understanding of problems,
•	helps re-orient decision-makers to the goals and principles of the ecosystem approach; and
•	strategizes about the means for implementation and serves as a catalyst for action (Ontario
Round Table on Environment and Economy 1991).
The roundtable approach does not challenge existing management authorities, rather it seeks out
broad-based input for the decision-making process to build consensus for action.^ It emphasizes
a "win-win" outcome through a continual two-way communication link between top-down and
"bottom-up" management. The Ontario Round Table for the Environment and Economy (1992)
actively promotes this approach in local communities throughout Ontario as it. deals more
effectively with conflict between disparate interests; makes more efficient use of scarce resources,
allows for an inclusive decision-making process; results in broad-range acceptance to decisions,
and increases accountability throughout the planning process.
The experiences gained and lessons learned through all RAP institutional frameworks must
be broadly communicated to help embrace new approaches and mechanisms for implementation.
For example, in New York Areas of Concern, Citizen Advisory Committees (CACs) were
replaced with Remedial Advisory Committees (RACs) for Stage II RAPs. In Hamilton Harbour,
BARC and BAIT were developed to comprehensively implement and track remedial an
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preventive actions for Stage II (see Figure 2 in Appendix II). Continued emphasis on cooperative
learning within and among Areas of Concern is needed.
To sustain the momentum from development to implementation, RAP institutional
frameworks will need to build a record of success by celebrating milestones. Both short-term
and long-term milestones and benchmarks should be identified and celebrated when met.
Examples of milestones and benchmarks include: government management actions; remedial and
preventive actions by identified sources; changes in discharge quality; reductions in contaminant
loadings; changes in ambient air/water/sediment concentrations; reductions in bioaccumulation
rates; biological recovery; use restoration; or increased human use of resources. RAP institutional
frameworks publishing annual or biennial RAP progress reports or hosting annual or biennial
"State-of-the-RAP" events are two successful mechanisms of measuring progress and celebrating
successes in a positive and reinforcing fashion.
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Ill CONCLUDING REMARKS AND RECOMMENDATIONS
The GLWQA charge to incorporate a systematic and comprehensive ecosystem approach
in RAPs, has led federal, state/provincial, and local governments, along with industry, public
organizations, and private citizens, to adopt new approaches for management in Areas of
Concern. Meeting this institutional challenge requires greater cooperation, coordination, and
integration of planning activities and program functions pertaining to remediation and prevention.
RAP institutional frameworks have proven to be effective mechanisms to facilitate this integrated
approach to resource management and ensure meaningful public participation.
RAP institutional frameworks are working to implement locally-designed ecosystem
approaches which address site-specific needs in a process of restoring impaired uses. The RAP
process is most effective if it is mission-driven and not rule-driven. Therefore, it is
recommended that each RAP institutional framework be empowered to pursue its mission of
restoring impaired uses. Empowerment of RAP institutional frameworks would be demonstrated
by: a focus on watersheds or other naturally-defined boundaries to address upstream causes and
sources, and attain watershed "buy-in" for implementation; an inclusive and shared decision-
making process; clear responsibility and sufficient authority to identify and pursue a road map
to use restoration; an ability to secure and pool resources according to priorities for action using
nonprofit organizations or other creative mechanisms; flexibility and continuity in order to
achieve an agreed-upon road map to use restoration; a strong commitment to broad-based
education, and public outreach; and an open and iterative RAP process that strives for continuous
improvement.
RAP institutional frameworks represent a forum for cooperative learning to generate a
common understanding of problems and build consensus for action throughout a watershed. To
ensure linkages of RAPs to other related planning efforts, it is recommended that governments
must adopt and reward a cooperative (rather than competitive) approach to working with other
stakeholders, agencies, and organizations. It is further recommended that open communication
and information networks be developed across and within public agencies and organizations, and
existing or new RAP institutional frameworks be used as mechanisms for coordinating and
integrating planning and program functions at the local level. This "bottom-up" approach to
coordination through RAP institutional frameworks should be complemented with "top-down"
efforts to ensure intra- and interagency initiatives are complementary and reinforcing by:
explicitly recognizing the need for coordination and integration of interrelated programs in agency
mission statements; and incorporating institutional arrangements necessary for desired
coordination and integration into agency program plans.
Government agencies will undoubtedly have to embrace/endorse new RAP institutional
frameworks to ensure a smooth transition from RAP development to implementation. For this to
occur, governments need to recognize the value of RAP institutional frameworks as a means to
an end. These institutional frameworks can help build the capacity of government agencies to
achieve their goals. Therefore, it is recommended that governments adopt long-term, visionary
goals for Areas of Concern and commit to a customer-driven and value-added RAP process of
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continuous improvement that shares decision-making power. It is further recommended that RAP
institutional frameworks consider establishing a partnership agreement for Stage II RAPs to help
empower stakeholders, capitalize on resources, clarify roles, ensure integration, and increase
communication. Such partnership agreements are consistent with an ecosystem approach and
could serve as an important milestone to be celebrated in the Stage II RAP process. Such
partnership agreements can also initiate the development of local roundtables, similar in function
to the Ontario Round Table on the Environment and Economy, to help governments build
consensus that will lead to the necessary commitments and endorsements to achieve full RAP
implementation and use restoration.
Considerable progress has been made in re-orienting decision-makers to a more inclusive
planning process that shares decision-making power with all stakeholders to become partners for
action. Continued emphasis should be placed on binational sharing of RAP experiences on the
nature and effectiveness of remedial and preventive actions in order to ensure progress in
restoring and maintaining health of the Great Lakes Basin Ecosystem.
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IV
APPENDIX I - LIST OF ROUNDTABLE PARTICIPANTS
Lisa Arcand
International Joint Commission
Great Lakes Regional Office
Cathy Bean
Michigan Department of Natural Resources
Surface Water Quality Division
John Beeker
Northeast Ohio Areawide Coordinating Agency
Susan Benzie
Michigan Department of Natural Resources
Surface Water Quality Division
Mary Beth Binns
Northeast Ohio Areawide Coordinating Agency
Lisa Borre
Lake Champlain Basin Program
Murray Brooksbank
Environment Canada
Great Lakes Environment Office
Valerie Cromie
Niagara River RAP Public Advisory Committee
Carla Davidson
Southeast Michigan Council of Governments
Lillian Dean
Environmental Planning Consultant
Erich Ditschman
Clinton River Watershed Council
Douglas Dodge
Ontario Ministry of Natural Resources
Great Lakes Operations
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Michael Donahue
Great Lakes Commission
Danny Epstein
Environment Canada
Great Lakes Environment Office
George Francis
University of Waterloo
Faculty of Environmental Studies
Brian Fredrickson
Minnesota Pollution Control Agency
Kent Fuller
U.S. Environmental Protection Agency
Great Lakes National Program Office
Steve Funderburk
U.S. Fish and Wildlife Service
Chesapeake Bay Estuary Program
Dan Gaudenzi
Ontario Ministry of the Environment
Murray German
Ontario Ministry of the Environment
Ann Gertler
St. Lawrence River Public Advisory Committee (Cornwall)
Mary Ginnebaugh
Great Lakes United
Moyra Haney
Ontario Public Advisory Council (RAPs)
John Hartig
Wayne State University
Pat Hartig
Downriver Center for Environment and Development
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Scott Holmgren
Landscape-Environmental Planner
Wayne State University
Peggy Johnson
Clinton River Watershed Council
Madhu Kapur Malhotra
Environment Canada
Great Lakes Environment Office
Steve Klose
Ontario Ministry of the Environment
Metro Toronto and Region RAP Coordinator
Rimas Kalinauskas
Environment Canada
Great Lakes Environment Office
Gerrit Knaap
University of Illinois
Department of Urban and Regional Planning
Belinda Koblik-Berger
Ontario Ministry of the Environment
Niagara River RAP Coordinator
Joe Koonce
Case Western Reserve University
Neely Law
Wayne State University
Sally Lerner
University of Waterloo
Faculty of Environmental Studies
Lesley Lovett Doust
University of Windsor
Biological Sciences
Tim Lozen
St Clair River RAP Binational Public Advisory Council
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Luciano Martin
Watershed Ecosystem Technologies
Grant Mills
Waterfront Regeneration Trust
Gerald Mikol
New York State Department of Environmental Conservation
Division of Water
Lois New
New York State Department of Environmental Conservation
Division of Water
Jeanna Paluzzi
East Michigan Environmental Action Council
Lee Pfouts
Toledo Metropolitan Sewerage District
Lou Quintan
St Marys RAP Binational Public Advisory Council
Anne Redish
Bay Area Restoration Council
G. Keith Rodgers
National Water Research Institute
Mike Santavy
Ontario Ministry of the Environment
Robert Sweet
Michigan Department of Natural Resources
Surface Water Quality Department
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V APPENDIX II - INSTITUTIONAL FRAMEWORK CASE STUDIES
Presented below are synopses of the nine case studies of institutional frameworks for
comprehensive water resource management. These case studies represent a range of practical
experiences from within and outside the Great Lakes Basin Ecosystem.
Hamilton Harbour (Ontario)
A broad-based institutional framework for Hamilton Harbour RAP development was
established in 1986 with the formation of a Stakeholder Group. This Stakeholder Group was
made up of representatives from agencies, organizations, institutions, governments (municipal,
regional, provincial, federal), industries, environmental groups, recreational groups, and private
citizen groups who make use of, who wish to make use of, or in some manner have jurisdictional
interests in the Harbour. The purpose of the Hamilton Harbour Stakeholder Group was to
provide input and advice to a technical, governmental writing team on: public education and
outreach; the process of developing the RAP; problem definition and use impairments; principles
an goals relating to the RAP; the review of remedial options; and the selection of preferred
remedial actions.
At the outset, the Hamilton Harbour Stakeholder Group had 49 members. After four
years, membership was 43, with 38 of the original groups or agencies represented. To ensure
t at t ere was adequate coordination, continuing public involvement, and that government
agencies remained publicly accountable for implementation, the Hamilton Harbour Stakeholder
roup recommended formation of a management group named the Bay Area Implementation
an<^ 3 Pu^'c consultative organization named the Bay Area Restoration Council
(BARC). Secretariats and a number of committees would be set up for each group. The
structure of these two groups and their relationships to the Canada-Ontario Agreement (COA)
Committee are depicted in Figure 2.
BAIT is made up of a core group of implementing agencies. The responsibilities of BAIT
src!
to facilitate the development of local arrangements for implementation of the RAP and
to coordinate the implementation of remedial actions for which commitments exist;
to provide consolidated reporting of actions and progress in implementing the RAP;
to consult with the BARC, with the general public, and with other stakeholders on issues
related to implementation of the RAP;
da?316 3nd dirCCt technical committees as required to support the implementation of the
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*	to liaise directly with the BARC on a regular basis, including referral of progress reports
and other RAP documentation for their review;
*	to evaluate the effectiveness of remedial actions on an ongoing basis; and
*	to report on status of the RAP to the COA Review Board through its RAP Steering
Committee.
BARC uses a "roundtable" model to achieve public consultation on restoration of
Hamilton Harbour as outlined in the RAP. Specifically, the purposes of BARC are to: assure
protection and appreciation of Hamilton Harbour; promote and assess RAP implementation;
assess public perceptions of ecosystem status; provide advice to governments on restoration;
coordinate the activities of the association with those of other organizations with complementary
objectives; and solicit and acquire donations, gifts, and legacies in furtherance of the objectives
of the association. BARC was incorporated by law and is managed by a Board of Directors.
Figure 2. The institutional framework for implementation of the Hamilton Harbour RAP
(Hamilton Harbour Stakeholder Group 1991).
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Detroit River (Michigan and Ontario)
The Detroit River, a 31 mile (51 km) international boundary linking Lake St. Clair and
Lake Erie, is the lowest link of the upper Great Lakes connecting channels. In 1985, the
Governor of Michigan and the Premier of Ontario signed a "letter of intent" committing their
jurisdictions to a binational approach to developing their shared connecting channel RAPs. For
the Detroit River Area of Concern (AOC), the Michigan Department of Natural Resources
(MDNR) was designated as the lead agency responsible for preparing the RAP and ensuring
adequate public participation. In 1988, a Binational Public Advisory Council (BPAC) was
established to facilitate public participation in RAP development. The BP AC had 20 members
from Michigan and 20 members from Ontario.
The Stage I Detroit River RAP was completed in 1991 by a Detroit River RAP Team with
input from the full BP AC. The RAP Team consists of representatives from MDNR, Ontario
Ministry of the Environment (OME), U.S. Environmental Protection Agency, Environment
Canada, Ontario Ministry of Natural Resources, Canada Department of Fisheries and Oceans, and
four representatives from the BPAC. The development of the Stage II Detroit River RAP
expands the multi-stakeholder partnership created in Stage I using a new cooperative and
interactive approach (Figure 3).
The RAP Team agreed that the Stage n RAP should be developed jointly by members
of the RAP Team, BPAC, and technical experts. Four planning workgroups consisting of
selected RAP Team members, BPAC members, and technical experts have been established to
develop individual reports for four major issue areas identified by the RAP Team (i.e. habitat,
contaminated sediments, point and nonpoint sources, combined sewer overflows). Cross-
representation of members is needed to ensure adequate communication and coordination with
the RAP Team and BPAC. Each of the four technical workgroups will develop their own report
which will include an assessment of completed and in-place remedial and regulatory measures
as related to impaired beneficial uses in the Detroit River, a list of potential remedial and
preventive options, and recommendations for preferred remedial and preventive actions. The four
technical workgroup reports will become the foundation of the Stage II Detroit River RAP.
Communication, cooperation, and coordination among the technical workgroups, the RAP Team,
and BPAC is critical to the acceptance and success of the plan. In general, the Detroit River
RAP Team and BPAC meet quarterly. Each of the four technical workgroups meet once every
six weeks on average. It is expected that the four planning committee reports will be developed
by April 1994, a draft Stage II RAP developed by August 1994, agency review by October 1994,
public review by February 1995, and final sign-off by June 1995.
As mentioned earlier, both Michigan DNR and OME are committed to cooperate fully on
the development of the Stage II Detroit River RAP in the most timely manner possible while
ensuring high quality technical documents that both agencies support. Several initiatives have
been taken to resolve and avoid conflicts that arise due to differences in agency philosophies and
program procedures, and to facilitate planning. In addition, both MDNR and OME are strongly
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Figure 3. A general framework for the development of the Detroit River Stage Et Remedial
Action Plan.
Michigan
Department of Natural Resources
(Lead Agency)
Abbreviations
DNR - Dept. of Natural Resources
OME - Ontario Ministry of
the Environment
EPA - Environmental Protection
Agency
EC - Environment Canada
0MNR - Ontario Ministry of
Natural Resources
DFO - fnnaHiMl Dept Of
Fisheries and Oceans

RAF Team.


(Michigan DNR, OME,
U.S. EPA, EC, OMNR,
DFO, BPAQ
\
Four
Technical Workgroup*
i
k
\
^ Habitat

r
\

Bimtionai Public

^ Contaminated Sediments
Advisory Council
(BPAC)

^ Combined Sewer Overflows
^ Point/Nonpolnt Sources
1
t

Technical
/

Experts

I
Four Topic Report!
I
Draft Stage II RAP
committed to actively seeking advice and input from the public through: local public
participation programs in the Detroit metropolitan area and the greater Windsor area; and
statewide and province-wide programs pertaining to all RAPs in Michigan and Ontario.
The Greater Toronto Bioregion (Ontario)
In 1988, the federal government of Canada appointed the Honourable David Crombie to
act as Commissioner for the Royal Commission on the Future of the Toronto Waterfront The
Commission's three-and-a-half year mandate was to make recommendations regarding the future
of the Toronto Waterfront, and to seek the concurrence of affected authorities in such
recommendations, in order to ensure that, in the public interest, federal lands and jurisdiction
serve to enhance the physical, environmental, legislative, and administrative context governing
the use, enjoyment, and development of the Toronto Waterfront and related lands (Crombie
1990).
The problems of making Toronto Harbour publicly accessible, fishable, drinkable, and
swimmable are enormous. Currently, governance in the Greater Toronto Bioregion is shared by
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five regional municipalities, 30 local municipalities, and numerous federal and provincial
ministries, departments, boards, agencies, and commissions. The result has been bureaucratic and
political paralysis - a situation in which almost any agency can stop projects and no one can do
anything (Crombie 1992). Because lines of accountability are completely distorted or hidden by
this jurisdictional fragmentation, the citizen is left without any means of recourse. The
jurisdictional gridlock throughout the Greater Toronto Bioregion is the single biggest obstacle to
its environmental and economic regeneration - and this is not unique to Toronto.
Crombie (1992) advocates that each city region in the world develop its own institutional
framework/adaptation to implement an ecosystem approach to planning. Each institutional
framework/adaptation should reflect the history, culture, traditions, habits, and customs unique
to that city. An ecosystem approach requires that economic development patterns, resource
policies, consumer trends, and public attitudes must all be considered in terms of their actual or
potential effects on the integrity of the system. This will require greater emphasis on setting
goals in common, changing attitudes, coordinating plans and actions across jurisdictions,
coordinating mechanisms for allocating and using resources, and planning cooperatively (Crombie
1990).
Nine principles have been recommended to guide the regeneration of Toronto Waterfront:
clean, green, useable, diverse, open, accessible, connected, affordable, and attractive (Crombie
1990). Implementing an ecosystem approach and restoring Toronto Waterfront cannot be
accomplished by any one agency or government in isolation. Rather, a wide range of
organizations and government agencies must cooperate to implement the ecosystem approach and
apply the nine principles presented above.
Features of an institutional framework/adaptation to implement an ecosystem approach
to planning include:
*	the recognition of the primacy of natural boundaries and processes;
*	the integration of land use with environmental planning in public process and law;
*	the integration of urban and rural planning to link the city with its region;
*	the creation of concurrent, rather than consecutive, planning processes;
*	the integration of capitol budgets of all government departments and agencies to ensure
coherence, economies, and financial strength; and
*	the recognition of the increasing importance of designing places and spaces that allow
people to feel a part of nature while they take advantage of the pleasures that cities can
offer (Crombie 1992).
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The recommended strategy for developing the Toronto Waterfront, planning and building
for sustainability, implementing environmental imperatives, and regenerating historic and social
places involves six basic steps:
1)	adopt the ecosystem approach and the nine waterfront principles (i.e. clean, green,
useable, diverse, open, accessible, connected, affordable, attractive);
2)	establish or adjust waterfront plans to ensure they reflect the ecosystem approach and
principles like sustainability;
3)	secure intergovernmental cooperation, agreements, and commitments on what needs to be
done, the priorities, who does what, and the time-frames for design, construction, and
delivery;
4)	consolidate capital budgets and pool resources as necessary to move projects forward;
5)	create the framework and conditions for private sector involvement, and capitalize on its
enterprise, initiative, creativity, and capability for investment; and
6)	establish partnerships among governments and between the public and private sector in
accordance with planning and project requirements (Crombie 1992).
Crombie (1992) argues that the roundtable process is the key to the public administration of the
waterfront - one that brings together all parties at the appropriate time, publicly and openly, so
that public values can be debated and determined, and various agencies made accountable.
Canadian Healthy Communities Program
The concept of "healthy communities" originated in Toronto, Ontario and was endorsed
by the World Health Organization to help cities develop and practice a healthy approach to
working on the elements that make up a community. The definition of a "healthy community"
is more than physical health, it recognizes the complex interactions and holistic nature of the
determinants of health, including social, mental, economic, and environmental well-being. In a
background paper, the World Health Organization defines a healthy city as: one that is
continually developing those public policies and creating those physical and social environments
which enable its people to mutually support each other in carrying out all the functions of life
and achieving their full potential. The goal of this program is to make cities the healthiest
communities possible.
The healthy communities program is more about process than a product. It recognizes
that the process of improving the health of a community is slow and complex; that the necessary
changes in human values and attitudes are the result of a long-term commitment to a multi-
faceted and broad-based process of social change; and that many of the challenges of health are
interrelated and require a holistic approach for resolution.
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Proponents argue that city government as a whole and the community-at-Iarge must
become involved in every effort to make a city the healthiest community possible. This calls for
a broad, multi-sectoral, and community-based initiative which can be initiated by public health
departments and boards, but cannot be implemented alone.
Much of what government does affects health, directly or indirectly. Therefore, it is
argued that local government should make a commitment to create a healthy community and help
establish mechanisms to achieve that goal. Some essential elements of a healthy community
include:
*	a City Council resolution of political commitment to a broad public policy approach to
health;
*	a commitment to an interdepartmental and intersectoral healthy community strategy;
*	a commitment to full community participation in the Healthy Community Project; and
*	a commitment to undertaking an evaluation of local projects/programs to ensure
consistency with the Healthy Community Project goals.
Each local government department is asked to identify ways in which they presently contribute
to health, and ways they could contribute to better health in the future. In addition, local
governments involve local citizen groups and neighborhood associations in planning and
implementation of local projects, and encourage resource support for projects from business,
labor, churches, volunteer groups, etc.
A Healthy City Program is being comprehensively carried out in Toronto, Ontario.
Toronto City Council established a Healthy City Office to be responsible for developing the City-
wide Healthy City Initiative as outlined in the report "Healthy Toronto 2000" under the direction
of an inter-departmental Healthy City Work Group (Healthy Toronto 2000 Subcommittee 1988).
The Healthy City Office is an official office within Toronto city government and has a staff of
six. The inter-departmental Healthy City Work Group is charged with coordinating the activities
of various city departments under the Healthy City Initiative. This institutional structure
addresses specific issues utilizing key stakeholders in a "roundtable" fashion.
Cuyahoga River (Ohio)
The Cuyahoga River Remedial Action Plan Coordinating Committee (CCC) was
established by the Ohio Environmental Protection Agency (EPA) in 1988 to provide local, state,
and federal public agencies, industries, and citizen groups an opportunity to fully participate in
a partnership in all aspects of the RAP planning process. It is argued that this broad-based
participation will broaden and deepen community ownership of the RAP and heighten prospects
for implementation (Beeker et al. 1991).
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The CCC is comprised of 35 members or stakeholders. From the outset, it was given a
plan development role, not simply a public advisory role. The CCC and the committees under
its direction provided the institutional framework for developing the Stage I RAP.
Much of the detailed planning work was carried out by four committees: Steering
Committee; Technical Committee; Community Involvement Committee; and Plan Drafting
Committee (Figure 4). Broader public participation was also actively pursued on a routine basis
in all committee work.
Figure 4. Cuyahoga River institutional framework for development of a Stage I RAP
(Cuyahoga River Remedial Action Plan Coordinating Committee 1992).
The primary role of the Steering Committee was to facilitate the CCC's oversight effort
by setting meeting agendas and providing a forum for shaping issues for CCC consideration,
debate, and decision. The Technical Committee coordinated ongoing field investigations of
public and private entities participating in the RAP and initiated additional studies to fill data and
information gaps. The Community Involvement Committee was responsible for ensuring broad
public involvement in the RAP process. Much of the work of researching and writing the
Cuyahoga River Stage I RAP was carried out by the Plan Drafting Committee. This committee,
in turn, formed six subcommittees (Biota Impairments, Toxics Consumption, Recreation
Impairments, Socio-economic, Point Sources, and Nonpoint Sources) which were responsible for
preparing background on problems/causes which eventually provided the foundation for the Stage
I RAP. Staff support to the Cuyahoga RAP process is provided by the Northeast Ohio Areawide
Coordinating Agency (NOACA) and Ohio Environmental Protection Agency (Ohio EPA).
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With the encouragement of the Ohio EPA, the CCC created a nonprofit organization under
Ohio law named the Cuyahoga River Community Planning Organization. The purpose of this
nonprofit organization is to support the goals of the RAP with additional resources for planning,
and to develop and support programs on public involvement, education, and research. Financial
support for the Cuyahoga River Community Planning Organization was obtained through grants
from the George Gund Foundation, the Cleveland Foundation, and the U.S. EPA Operating
expenses during 1991 and 1992 were $152,000 and $100,000, respectively. These grants,
combined with both member and nonmember contributions, provided the support for the
following: a full-time environmental planning coordinator to augment staffing of NOACA and
Ohio EPA; a part-time public involvement coordinator; a study investigating the direct and
indirect benefits of river cleanup; a public opinion poll; public workshops; and an urban nonpoint
source education program. The CCC and its committees are viewed as a successful institutional
framework for developing the Cuyahoga River Stage I RAP. Full endorsement for the Stage I
RAP was obtained from the CCC in 1992.
This inclusive, participatory, community-based planning process is now being used to
develop the Cuyahoga River Stage II RAP (Figure 5). Overall direction is provided by the CCC
Figure 5. Cuyahoga River institutional framework for development of a Stage II RAP.
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and Steering Committee, in cooperation with the Cuyahoga River Community Planning
Organization. Under their direction, the Community Involvement and Technical Committees
continue to function. However, the efforts of these committees are complemented with Stage II
Work Groups on land uses/institutions, stormwater management, habitat, education/pollution
prevention, and recreation/access, and a separate work group to update the Stage I RAP.
St. Lawrence River (New York and Ontario)
The St. Lawrence River is a binational connecting channel linking Lake Ontario to the
Atlantic Ocean. This binational Area of Concern includes waters shared by New York State, the
Provinces of Ontario and Quebec, and the Mohawks at Akwesasne. Two separate RAP processes
are being undertaken - one by the New York State Department of Environmental Conservation
(NYSDEC) at Massena, New York, and the other by Environment Canada and Ontario Ministry
of the Environment (OME) for the Cornwall/Lake St. Francis area in Ontario. Binational
activities by the NYSDEC and OME have increased the coordination of the two separate RAP
processes. The Governments of Akwesasne were officially recognized as a supporting third party
in February 1989 by the United States, Canada, Quebec, Ontario, and New York State to
participate in the St. Lawrence River RAP process.
The institutional framework guiding the development and implementation of the St
Lawrence River RAP at Cornwall is led by a RAP Team made up of representatives from
Environment Canada, Ontario Ministry of the Environment, Ontario Ministry of Natural
Resources, the Mohawks at Akwesasne, and the Cornwall Public Advisory Committee (PAC).
The RAP Team has been working since 1986 to analyze and complete a data base on the
environmental conditions and causes of use impairments. The technical component of the RAP
process is balanced with a formal public participation program that stems from the RAP Team.
A Cornwall PAC was formed in November 1988, which subsequently initiated the formation of
four subcommittees: Goals; Public Outreach; Technical; and Remedial Options. The Cornwall
PAC holds monthly meetings and is attended by more than forty members, including Massena
RAP participants. In addition, a Steering Committee consisting of the PAC Executive provides
direction for the PAC.
The public participation process is further encouraged through the Public Outreach
Subcommittee that develops and implements both independent and joint projects with
Environment Canada in support of the RAP public involvement program. This subcommittee has
been instrumental in involving and receiving feedback from the community on RAP activities.
Other subcommittees are responsible for the development of the PAC's goals (Goals
Subcommittee), reviewing and providing feedback on technical information (Technical
Subcommittee), and the development of remedial options in cooperation with the RAP Team and
the PAC throughout Stage II (Remedial Options Subcommittee).
The NYSDEC was the lead agency in the development of the RAP for Massena, New
York. A Citizen Advisory Committee (CAC) was established in 1987 and was the primary
means for the public to participate in the Stage I RAP process. The CAC was comprised of
39

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j'ff_rpnt interest eroups and advised NYSDEC on all aspects of the
thirty members &OIVp Technical and Public Outreach Subcommittees had been formed to
development of th .	development. A Steering Committee was also formed to direct
deal with	activities of the CAC and the NYSDEC. Members of the
RAP development	NYSDEC program and communication staff, the executive members
Steering CommitteefuU committee, and the chairs of the Technical
o£ CAC, the chair and ^	was chaired by ^ msmc od
and activities of the CAC and Us subcommittees. It set agendas for the
CAC^s approval fnd was the forum for discussion on poltcy matters.
„	s £ =r tsss
tacS tetS fact sheets and newsletters, presenting information to community groups,
havinga display at sportsmen's shows and festivals, and sponsoring a poster and song wrmng
contest in schools.
A Remedial Advisory Committee (RAC) was established in 1991 to assist the NYSDEC
.. , • i .	thp stape II RAP and assess RAP progress and recommend actions.
^em^SnTnutty in the RAP process, original members of the CAC have been appoint^ to
remittee as well as elected and appointed government officials, and representatives from
public toterest groups (non-economic interests), economic intents, and private citizens The
NYSDEC Division of Water Quality will provide the general coordination for the implementation
of the remedial strategy.
Proness toward RAP institutional cooperation has been made through an agency
agreement to develop a taint goal statement and joint problem statement A citizen's group
called the St. Lawrence River Restoration Council (1989-1991) was accepted by the PAC and
CAC as a mechanism for communication among the three groups on RAP development. The
Council was composed of representatives from the Cornwall PAC, the Massena CAC, and the
"Mohawks Agree on Safe Health" group. It was a forum for formation exchange and: Medas
an intermediary between the two institutional structures, the PAC and CAC. This was a
consistent link established between the two RAP processes. In 1991, the Cornwall PAC
withdrew its support due to internal difficulties with representation on Council Other
mechanisms for binational communication are informal, for example attending Cornwall PAC or
Massena CAC meetings.
The Governments of Mohawk Akwesasne (the Mohawk Nation Council of Chiefs, the
Mohawk Council of Akwesasne, and the St. Regis Mohawk Tribal Council) are parttctpants m
both RAP processes. They participate in the preparation of the RAP, provide expertise and
information, provide an important perspective on the St Lawrence River, and participate in the
evaluation and implementation phase of the RAP. Mechanisms for the involvement of
Environment Quebec have also been established to liaison with the St Lawrence River RAP
processes.
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The goal of a cooperative approach to RAP development between Ontario and New York
was partially achieved in May 1988 with an agreement between Environment Canada, Ontario
Ministry of the Environment, and the NYSDEC to develop joint statements on environmental
problems and goals for the Cornwall-Massena Areas of Concern. The Canadian and United
States RAP teams have outlined a process for the development of these joint statements which
requires input from Environment Canada, the Mohawk People of Akwesasne, and the Canadian
and United States publics (Figure 6). A joint goal statement has received the approval of the
Figure 6. St Lawrence River Remedial Action Plan institutional framework for the
development of the joint goal and problem statement (Environment Canada et al. 1992).
Continue RAP
Development
Continue RAP
Development
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Cornwall PAC, Massena CAC, Mohawk People through the St. Lawrence River Restoration
Council, as well as Environment Quebec. This goal statement includes the following:
The goal of the Cornwall and Massena Remedial Action Plans is
to restore, protect, and maintain the chemical, physical and
biological integrity of the St. Lawrence River ecosystem, and in
particular, the Akwesasne, Cornwall-Lake St. Francis and Massena
Area of Concern in accordance with the Great Lakes Water Quality
Agreement.
The goal of the Cornwall and Massena Remedial Action Plans
includes protecting the downstream aquatic ecosystem from adverse
impacts originating in the Akwesasne, Cornwall-Lake St. Francis,
and Massena Area of Concern (St. Lawrence River RAP Team
1991).
In addition, a joint summary statement of use impairments has also been prepared. The joint
summary report outlines conclusions on the description of problems in the Area of Concern with
evaluation of the Great Lake Water Quality Agreement 14 indicators of use impairment. The
separate processes of both RAPs are also described.
In 1992, a binational monitoring workshop was also held to share ideas and approaches
for the continued education on monitoring in the Area of Concern during remedial activities.
This joint workshop was a result of the cooperative institutional framework established by the
RAP process.
Lake Champlain (New York, Vermont, Quebec)
Lake Champlain, situated at the border of New York, Vermont, and Quebec, is the sixth
largest freshwater lake in the United States. It has considerable economic and social significance,
both regionally and internationally.
In recognition of the value of Lake Champlain and the need to strengthen and consolidate
efforts to preserve and protect it, the Lake Champlain Management Conference was formed and
authorized under the Lake Champlain Special Designation Act of 1990 to serve as an institutional
framework for developing a Comprehensive Pollution Prevention, Control, and Restoration Plan
for the Lake. The Plan will provide a framework for managing the various, and sometimes
divergent, uses of the Lake so that its environmental integrity is maintained, while social and
economic concerns are reflected.
In order to accomplish its goal, the Lake Champlain Comprehensive Pollution Prevention,
Control, and Restoration Plan will identify corrective actions and compliance schedules for
minimizing the threat from existing point and nonpoint sources, and a strategy for pollution
prevention which will reduce the amount of pollution generated within the Lake Champlain
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Basin. This will be accomplished by clarifying the duties of responsible parties, especially
federal and state agencies, in pollution prevention and control activities, incorporating
environmental management concepts established and implemented through other existing
programs, and describing methods and schedules for funding of programs, projects, and activities
identified in the Plan. The Management Conference can incorporate additional recommendations
in order to fulfill its mission.
The Lake Champlain Management Conference, which represents a broad-based group of
interests, shares in common a goal of developing a management program to protect and enhance
the integrity of the Lake and its basin, taking into account social and economic benefits.
Through the Management Conference, federal agencies (i.e. U.S. Environmental Protection
Agency, U.S. Department of Agriculture, U.S. Department of Interior) work together with
state/provincial governments, local communities, academic institutions, and public interest groups
in development and implementation of the Management Plan (Figure 7).
Figure 7. Lake Champlain Project (Pearson 1992).
Lake Champlain is managed for multiple uses (e.g. commerce, swimming, fishing,
boating, drinking water supply, wildlife habitat) through the Management Conference. The uses
are to be balanced to minimize stresses on any part of the lake system. Maintaining a vital
economy is an integral part of managing the Lake and its basin. The Management Plan is to
43

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ensure that the Lake and its basin will be protected, restored, and maintained so that future
generations will enjoy its full benefits.
Funding for the Lake Champlain Management Conference is provided from the Lake
Champlain Special Designation Act of 1990. These funds are used to facilitate the Management
Conference and support research efforts, surveys, demonstration projects, modelling, technical
support work, and public education for developing the Management Plan. The Management
Conference allocates funds to these purposes. Authorized funds to carry out this work are $2
million for each of fiscal years 1991 through 1995. In addition, complementary resource support
is obtained through designation of Lake Champlain as a special project under the U.S.
Agricultural Conservation Program. This provides technical and financial resources in support
of the agricultural nonpoint source component of the Management Plan.
Chesapeake Bay (Maryland, Virginia, and Pennsylvania)
Chesapeake Bay and its tributaries, wetlands, and dependent natural resources make up
an ecosystem shared and used by the State of Maryland, the Commonwealth of Virginia, and
Commonwealth of Pennsylvania. Chesapeake Bay is the largest estuary in the United States.
Considerable degradation of Chesapeake Bay has occurred as a result of human activities in the
watershed. As a result, there has been substantial concern for rehabilitating and protecting the
Bay, particularly as the population in the watershed is expected to grow by 20 % to over 15
million people by the year 2020.
In recognition of the degradation of Chesapeake Bay and the need for wise use,
conservation, and management of Chesapeake Bay, the Chesapeake Bay Commission was created
in 1980 by the General Assemblies of Maryland and Virginia (Chesapeake Bay Commission
1991). The legislation was amended by mutual consent in 1985 to include Pennsylvania as a full
member of the Commission.
The membership of the Chesapeake Bay Commission consists of seven representatives
from each of the three states. Each state's delegation includes two Senators, three Delegates of
Representatives, the Governor or his/her designee, and a citizen representative. The Commission
has a small staff with offices in Annapolis, Maryland; Richmond, Virginia; and Harrisburg,
Pennsylvania. Current funding for the Chesapeake Bay Commission is approximately $125,000
annually from each state.
The primary purpose of the Chesapeake Bay Commission is to encourage and assist in
achieving cooperative, coordinated planning and action among the executive agencies and
legislatures of the three states (Chesapeake Bay Commission 1991). To accomplish its purpose,
the Chesapeake Bay Commission:
* identifies specific management concerns requiring interjurisdictional coordination and
cooperation;
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*	recommends to all levels of government the legislative and administrative actions which
are needed to achieve effective and coordinated management of the Bay;
*	collects, analyzes, and disseminates data and information about the watershed for the
General Assemblies:
*	represents the common interests of the states as they are impacted by activities of the
federal government;
*	monitors federal activities; and
*	provides a forum for discussion and resolution of interstate conflicts.
Since the Commission was formed it has been instrumental in sponsoring legislative and
budgetary actions in the three states to promote restoration of Chesapeake Bay. The Commission
also actively reviews executive agency actions to ensure that programs are implemented
expeditiously and effectively. The range of interests of the Commission is broad and far reaching
including:
fisheries and living resources management;
agricultural nonpoint source pollution;
sediment control;
stormwater management;
nutrient control strategies;
sewage treatment;
toxic pollutants;
population and land use;
institutional arrangements;
water use activities; and
shoreline erosion.
The Chesapeake Bay Commission works with other organizations which have been created
to coordinate management, particularly the Chesapeake Bay Program which consists of the
Chesapeake Bay Liaison Office of U.S. Environmental Protection Agency, the Chesapeake
Executive Council composed of the Governors of Pennsylvania, Maryland, and Virginia, the
Mayor of the District of Columbia, and the Administrator of the U.S. Environmental Protection
Agency, its Implementation Committee of state and federal resource management agency
representatives, and its Citizens and Scientific and Technical Advisory Committees (Figure 8).
The Chesapeake Bay Liaison Office of the U.S. Environmental Protection Agency helps
coordinate cleanup activities of federal and state agencies, and is authorized by the 1987
Amendments of the Clean Water Act to spend up to $ 13 million a year on Bay activities, with
most of that money going into matching grants that help fund state programs (U.S. Environmental
Protection Agency 1989). The Chesapeake Bay Liaison Office also provides administrative and
*
*
*
*
*
*
*
*
*
*
*
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technical support to the network of regional committees, subcommittees, and work groups which
run the Chesapeake Bay Program under the direction of the Chesapeake Executive Council.
Figure 8. Major committees in the Chesapeake Bay Program (Chesapeake Bay Commission
1991).
Citizen*
Advisory Committee
Local Government
Advisory Committee
—iH Technical
Advisory Committee
8 Subcommittees
Living
Rcaourcet
Toxic*
Otfumpoatf
Executive Committee
Principal!1 Staff
Committee
Implementation
Committee
Budget and
Workplan Steering
Committee
1991 Nutrient
Reevaluation
Workgroup
Federal Agencies
Monitoring
Modeling
Nonpoint
Source
Public
Access
Growth and
Development
Public
Information
and Education
.Water Quality.
The signing of the Chesapeake Bay Agreement in 1987 represented a significant milestone
in the evolution of the multijurisdictional effort to restore Chesapeake Bay. The Agreement
committed the U.S. Environmental Protection Agency, Maryland, Virginia, Pennsylvania, the
District of Columbia, and the Chesapeake Bay Commission to work together to achieve a set of
specific goals in a specific timeframe. All parties are working together, for the first time, to
develop and implement mutually agreed-upon programs to achieve a healthier and more
productive Chesapeake Bay ecosystem. Activities of the Parties to the Agreement are directed
by goals and priority commitments for: living resources; water quality; population growth and
development; public information, education and participation; public access; and governance.
The 1987 Chesapeake Bay Agreement has spawned numerous interjurisdictional working
groups which involve all interested parties in a partnership to find acceptable solutions to
common problems. Figure 8 presents the post-Bay Agreement organizational structure for the
46

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Chesapeake Bay Program.
Commitments related to governance in the Chesapeake Bay Agreement cover a broad
array of issues dealing with the overall administrative structure and function of the Chesapeake
Bay Program. Specific commitments include:
*	developing an annual Chesapeake Bay work plan which is endorsed by the Chesapeake
Bay Council;
*	continuing to support Bay-wide environmental research and monitoring to support
management decisions;
*	strengthening the Chesapeake Bay Liaison Office by assigning staff persons from the
signatories to assist with technical support functions;
*	developing and implementing a comprehensive research plan in support of the Chesapeake
Bay Program;
*	developing a Bay-wide monitoring plan for selected commercially, recreationally, and
ecologically valuable species;
*	establishing a local government advisory committee to achieve local participation in the
Chesapeake Bay Program;
*	reviewing the feasibility of establishing an independent Chesapeake Bay Board; and
*	ensuring that the U.S. Environmental Protection Agency develops a coordinated federal
workplan which identifies specific federal programs to be integrated in support of the
Chesapeake Bay Program.
A Local Government Advisory Committee was formed to focus attention on issues of
concern to local governments such as infrastructure funding, development standards, and
immediate response to hazardous substance spills. It consists of 20 members representing local
governments from each of the signatory jurisdictions. As the states begin to address human
population growth and development, and attempt to develop growth management strategies, it is
expected that the Local Government Advisory Committee will play an increasing role.
Puget Sound (Washington)
Puget Sound is located in the northwestern portion of the State of Washington along the
coast of the Pacific Ocean. Puget Sound is an extraordinary national resource which supports
considerable international commerce, abundant commercial and recreational fisheries, and varied
wildlife habitats. The area also provides recreation to 3.2 million people. By the year 2010, the
population of the Puget Sound Region is expected to increase to 4.4 million.
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In response to growing public concern for the health and well-being of Puget Sound, the
Washington State Legislature created the Puget Sound Water Quality Authority in 1985 to
prepare, adopt, and oversee the implementation of a comprehensive, coordinated plan (i.e. the
Puget Sound Water Quality Management Plan) to clean up and protect Puget Sound (Puget Sound
Water Quality Authority 1991). The Puget Sound Water Quality Management Plan is a
comprehensive estuary management plan that addresses: municipal and industrial discharges;
nonpoint source pollution; shellfish protection; contaminated sediments; stormwater and combined
sewer overflows; wetlands protection; monitoring and research; education and public
involvement; and household hazardous waste. Over 500 jurisdictions and public agencies have
some responsibility related to Puget Sound, therefore, one of the principal roles of the Authority
is to ensure that there is regional coordination and cooperation in protecting and rehabilitating
Puget Sound.
The Authority is an independent state agency governed by an eleven member board
representing a broad range of interests and geographic areas around the Sound. Nine members
are appointed by the Governor of Washington (i.e. one representative from each of the six
congressional districts surrounding the Sound and one representative from cities, counties, and
tribes). In addition, the Director of the Washington Department of Ecology and the
Commissioner of Public Lands or their respective designees serve as ex-officio members. The
Director of the Department of Ecology serves as the Authority's chairperson.
The Governor of Washington also appoints an executive director for the Authority, who
selects, supervises, and manages the work of the Authority's staff! The mandate of the Authority
currently extends to 1995. Funding for implementation of the Puget Sound Water Quality
Management Plan was approximately $24 million during the 1987-1989 biennium and
approximately $36 million during the 1989-1991 biennium. Additional state, federal, and local
funds are needed and being sought under the direction of a Puget Sound Finance Committee.
The Puget Sound Water Quality Authority, in cooperation with U.S. EPA, Washington
Department of Ecology, and the Puget Sound Estuary Program Management Committee,
coordinates implementation of the Puget Sound Water Quality Management Plan. Specifically,
the Authority: informs federal and state agencies and local and tribal governments of their
responsibilities under the Plan; participates in committees and work groups; provides formal and
informal guidance; and assists in obtaining funding. Authority staff act as facilitators, working
closely with each federal agency, state agency, tribal government, and local government given
responsibilities under the Plan. As part of the Authority's coordination responsibilities, it
continuously reviews and amends program tasks as necessary to ensure Plan implementation.
In addition to the Puget Sound Water Quality Authority, a Puget Sound Foundation was
established in 1991 by the Authority as a public nonprofit corporation to ensure continuity toward
long-term goals of the Plan and ensure sufficient priority is given to education and research
programs.
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Nipigon BayP^*
Thunder Bay PAC

St. Louis River CAC
M»nistW h
Partnership \
Menominee River CAC
N.E. Wisconsin Waters
of Green Bay Tomorrow, Inc.
Green Bay PAC
Sheboygan County Water
Quality Task Force
Milwaukee Estuary CAC
Waukegan Harbor CAC
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