CHESAPEAKE
BAY:
The
Chesapeake Bay Program provides an interesting model for large-scale
ecosystem restoration. Many of the ecosystem's challenges
are similar to those of other ecosystems across the United
States, such as how to involve multiple states, combine federal
and state interests, and address the problems of a large water
body with multiple tributaries, multiple problems, population
growth and development issues, and important economic interests.
To
meet these challenges, the Chesapeake Bay Program depends
on stakeholder involvement and cooperation. The federal and
state governments all are members of the Chesapeake Executive
Council and signatories to the 1987 and 2000 Chesapeake Bay
Agreements, which contain sections on government participation
and responsibility, as well as community involvement and engagement.
In addition, the program's restoration goals are designed
to address not just the ecosystem needs, but also the sustainability
of the Bay economies that depend on local resources (e.g.,
recreational and commercial fisheries). The Chesapeake Bay
Program also is an example of the success that can be achieved
when the states have a key role in initiating, developing,
and leading the process, rather than simply being directed
by the federal government. Finally, cost-sharing between the
federal government and the states has been crucial for the
success of Bay restoration efforts.
Recent
criticisms of the slow rate of water quality improvement in
the Chesapeake Bay have focused attention on the voluntary
nature of the program's agreements. Some have called for a
more regulatory approach to ensure that agreements and commitments
are met.
COASTAL
LOUISIANA:
Although
restoration efforts in coastal Louisiana involve only one
state and are directed at many challenges and problems endemic
to the Mississippi gulf region, the Coast 2050 Plan for large-scale
restoration provides a fascinating model for other regions
of the country. First, coastal Louisiana's restoration and
conservation efforts have involved local, state, and federal
entities under various guises for many decades. The Coast
2050 Plan is an ambitious attempt to coordinate these efforts
into one initiative, with the goal of sustaining a coastal
ecosystem that supports and protects the environment, economy,
and culture of southern Louisiana, and also contributes greatly
to the economy and well-being of the nation.
In
addition, Coast 2050 is locally driven and extremely well
organized. At a very early stage in the process, it was endorsed
by scientists, business and industry groups, environmental
groups, civic organizations, and the general public - as well
as federal, state, and local government - even though it will
cost billions of dollars and take decades to be carried out.
Finally,
the Coast 2050 Plan details the problems facing coastal Louisiana,
including both ecosystem and economic consequences. Using
the latest scientific information, the plan forecasts what
will happen if it is not implemented. This information - both
the statistics provided and the detail of potential devastation
in realistic, understandable terms-has a tremendous impact.
For example, it shows that every year, a chunk of Louisiana's
coast the size of Manhattan crumbles and sinks into the sea;
if the current land loss rates continue unabated, by the year
2050, the Gulf of Mexico will move inland more than 30 miles.
Information like this makes the restoration effort a necessity,
not a luxury, and unites all of the region's constituencies
in the common goal of restoring coastal Louisiana.
COLUMBIA
RIVER:
Although
the Columbia River system is similar to other ecosystems across
the United States in that it encompasses numerous states,
two countries, various tribal and local entities, and industry
authorities, restoration efforts in the basin should not be
considered as a model. The lack of a single, comprehensive
restoration plan is a definite obstacle for restoring the
Columbia River system. To the detriment of restoration efforts
in the region, the four primary restoration programs currently
operating in the basin function independently of each other,
and in some cases have historically been at loggerheads.
Together,
the four primary restoration programs have resulted in multiple
restoration goals and objectives, numerous court actions and
appeals, significant delays in restoration actions, uncertain
timelines, and continuous implementation problems and issues.
Perhaps the two most important factors impeding restoration
efforts in the Columbia River are the apparent lack of a lead
federal agency charged with overseeing and implementing all
federal restoration efforts, and the lack of a holistic, system
wide approach to restoration. Other unresolved issues in the
Columbia River basin include lack of strong public will, the
absence of a stable source of funding; no specific, uniform
set of restoration goals and objectives; fragmentation of
responsibility; and unclear direction for interagency obligations.
SOUTH
FLORIDA EVERGLADES:
The
South Florida ecosystem restoration initiative, as implemented
by the Comprehensive Ecosystem Restoration Plan (CERP), is
the largest restoration effort led by the U.S. Army Crops
of Engineers to date, and potentially the largest ecosystem
restoration effort in the United States. As the South Florida
effort continues to evolve and be implemented, close attention
should be paid for lessons relevant to other initiatives across
the country.
The
South Florida initiative differs from many other efforts in
that it involves only one state and one country. Its types
of ecosystems, impacts, stakeholders, and potential issues
and user concerns arising from restoration and development
also differ markedly.
However,
as its name suggests, CERP is a comprehensive plan involving
all stakeholders of the region, including local, state, and
federal agencies and entities. Most, if not all of the government
agencies and entities involved in the Florida effort are expected
to play some role in other efforts.
The
scale of the project also is considered to be analogous to
other initiatives, as well as its levels of funding and degree
of commitment from both state and federal governments. The
timeline needed to undertake the vast number of projects for
large-scale ecosystem recovery elsewhere also will be similar
to the Everglades. Further, other efforts will be conceptualized
through a dire need for whole ecosystem recovery.
In
addition, comparable endeavors are expected to be based on
overarching principles similar to those in South Florida,
including restoration, preservation, and protection requirements
while providing for the needs of all stakeholders in the region;
use of best-available science, technology, and independent
scientific review; unanimous cooperation and facilitation
of the restoration agenda from stakeholders and all involved
entities (including full partnership with federal, tribal,
state, and local agencies); and development and implementation
of a flexible plan that engages adaptive assessment and provides
for ongoing maintenance and monitoring.
Possible
issues of contention arising during CERP implementation include
stakeholder assurances for water allocation; agency and entity
coordination; technological uncertainties; plan success; and
funding.
GREAT
LAKES:
The
Great Lakes ecosystem presents many of the challenges involved
in other large-scale restoration initiatives nationally, including
how to involve multiple federal, state, and tribal interests;
how to tie together existing strategies and program activities;
and how to holistically address multiple ecosystem problems
while accommodating important economic interests. Because
the Great Lakes Regional Collaboration is a recent initiative
charged with developing a coordinated, comprehensive plan
for the long-term conservation and restoration of the Great
Lakes, it is uncertain how these challenges will be overcome.
However, the Great Lakes have more than 30 years of effective
joint cooperation through the Canada-U.S. Great Lakes Water
Quality Agreement and other forums to build on.
One
important detail of the Collaboration that is yet to be determined
is the type of role that the Canadian federal agencies and
the provinces of Ontario and Quebec will have. Nor has the
role of the tribes and first nations - large landowners with
special legal status in the Great Lakes basin - been determined.
As in the rest of the country, it is important that any holistic
approach to restoration in the Great Lakes basin fully include
its neighbors - Canadian federal agencies, the provinces of
Ontario and Quebec, and tribes and first nations - at a high
level. The problems of the Great Lakes basin do not end at
the U.S. border and need to be addressed through a shared
vision and complementary restoration actions.
One
positive outcome of the Collaboration is the involvement of
the mayors and cities of the Great Lakes in restoration planning
through the Great Lakes Cities Initiative. Long-term restoration
in the Great Lakes must have the commitment of all levels
of government and all stakeholders, and this seems to be recognized
in the Great Lakes Regional Collaboration. It is hoped this
commitment will not only be in the form of support for the
restoration effort, but also for providing resources and helping
with plan implementation. Specifically, it is essential that
any restoration initiative incorporate specific ways that
all constituencies of a healthy ecosystem (industrial, municipal,
and public) can participate in achieving the desired outcome
- for example, by transforming the region's human systems
that impact the natural system.
SAN
FRANCISCO BAY DELTA:
Unlike
many other initiatives across the country, restoration of
the Bay-Delta involves only one state and one ecosystem. However,
numerous lessons can be drawn from the CALFED Bay-Delta Program
when considering the most successful pathway for developing
and implementing a long-term comprehensive restoration plan.
First,
a federal commitment to both authorization and funding is
crucial during comprehensive plan development and comprehensive
plan implementation. Although the CALFED Bay-Delta Program
received adequate state and federal resources and funding
during its development phases, plan implementation was severely
delayed for many years while the program awaited federal reauthorization.
This delay not only affected restoration actions on the ground,
but also saw the decline of federal funding dollars and overall
agency support for the program.
Between
2001 and 2004, a handful of bills were introduced in both
the House and Senate to reauthorize the CALFED Bay-Delta Program.
To gain support from lawmakers outside California, many of
the bills included provisions addressing water development
issues in other Western states. All the bills advanced a dialogue
over reauthorization of the CALFED Bay-Delta Program, but
to its detriment some bills also caused debate among the program's
stakeholders. Finally, after four years of negotiation and
several ill-fated attempts, bipartisan consensus resulted
in successful passage of legislation reauthorizing the CALFED
Bay-Delta Program in September of 2004. However, it is yet
to be determined if Congress will appropriate the authorized
program funding levels.
It
is also imperative that restoration program funding be scheduled
into all participating state budgets, and be authorized in
state statute. Initially the CALFED Bay-Delta Program was
not displayed as a program element in the governor's budget
or scheduled in the budget bill, and the state legislature
was slow in statutorily authorizing the program's governance
framework. Both of these factors produced hiccups in the program's
structure in the state and affected its overall functioning.
UPPER
MISSISSIPPI RIVER:
Along
with other parts of the United States, the UMR basin is geographically
diverse and complex, with many competing economic and political
interests. The challenges and accomplishments of restoration
efforts in the UMR basin should be a source of significant
insight to other initiatives across the country.
Although
the UMR basin has no single restoration plan or funding strategy,
there are a number of significant and complementary ecosystem
restoration and environmental protection initiatives underway
within the river system and the broader watershed. Together,
the Environmental Management Program (EMP), UMR-Illinois Waterway
navigation study, Hypoxia Action Plan, and USDA conservation
programs represent long-term, interagency, and multi-stakeholder
efforts to direct billions of federal, state, and private
dollars toward the restoration of critical ecosystems in the
UMR basin.
Within
the river and floodplain system, the EMP has provided a scientific
and practical basis for future restoration efforts. An important
set of long-term monitoring data, design and construction
methods, information on habitat response, models of interstate
and interagency coordination, and public input mechanisms
have evolved through nearly twenty years of program implementation.
The 50-year, $5.72-billion ecosystem restoration plan proposed
recently by the Corps of Engineers in the UMR-Illinois Waterway
Navigation Study builds on these findings and lessons.
Within
the broader watershed-most of which consisting of private
lands in agricultural production-the Action Plan for Reducing,
Mitigating, and Controlling Hypoxia in the Northern Gulf of
Mexico (called the Hypoxia Action Plan) and the U.S. Department
of Agriculture conservation programs constitute the primary
landscape-level efforts to improve environmental management
of private agricultural lands. The Hypoxia Action Plan has
initiated a planning process, but the degree of federal and
state support needed to move it forward has yet to materialize.
At the same time, spending has increased significantly through
the U.S. Department of Agriculture conservation programs reauthorized
in the 2002 Farm Bill. Over the life of the current Farm Bill,
several billion dollars will be invested in voluntary conservation
efforts on private agricultural lands in the UMR basin. Because
these investments are not coordinated or evaluated on a large-scale
basis, it is unclear what level of basin-wide impacts they
will have.
In
ecological terms, the division of the UMR into two basic components--the
river system (river and floodplain) and the broader watershed--is
an arbitrary distinction, since the two components are internally
and dynamically connected. Moreover, with respect to particular
environmental problems such as nutrient and sediment runoff,
policy and management responses need to be formulated in a
cross-cutting fashion. Owing to the size and complexity of
the UMR - as well as to the jurisdictional reach and institutional
proficiencies of different federal agencies-it remains a great
challenge to move beyond piecemeal efforts to restoration.
Very significant steps toward an integrated approach toward
restoration of the river and floodplain system have taken
through the Environmental Management Program and the Navigation
Study. Hopefully these initial successes will form a basis
for a more comprehensive basin-wide approach to land stewardship
and ecosystem restoration.
COMPARING
CASE HISTORIES:
Effects
of Competing Demands
First and foremost, all of the ecosystems have historically
suffered from the effects of competing demands on ecosystem
resources. This competition has led to the development of
socio-economic systems and infrastructure that depends on
particular uses, including dams and levees for flood control
and power production; channels and canals for navigation,
irrigation, and wastewater discharge; and fish stocking and
farming for recreational and commercial activities. As a result,
any attempt to restore the ecosystem must also transform these
historically significant socio-economic systems, and modify
their dependent infrastructure. Therefore, large-scale ecosystem
restoration is a sensitive process. It takes money, time,
and resources away from other priorities, and requires shifts
in historical thinking.
Ecosystem
Impacts
Another commonality is the similar ecosystem impacts of reduced
water quality; water quantity issues; declining fish and wildlife
populations; destruction and loss of habitat - particularly
wetlands; and invasive species problems. Because of these
common problems and concerns, the restoration initiatives
should look to one another for guidance, lessons, and technologies
that work best to address these issues.
For
example, conversion of land for agriculture has resulted in
the loss of up to 95 percent of wetlands in the Iowa and Illinois
portions of the Upper Mississippi River basin. More than 1.2
million acres of coastal land has been lost in Louisiana -
accounting for 80 percent of the nation's coastal land loss.
And in the San Francisco Bay-Delta, over 88 percent of the
estuary's wetlands have been eliminated or altered.
In
the Chesapeake Bay, nutrient enrichment and algal blooms combined
with sediment runoff have resulted in decreased dissolved
oxygen and water clarity. Declining water quality through
soil erosion and increased levels of polluted runoff, nutrients,
and contaminants is also prolific in the South Florida Everglades.
The discharge of pollutants - such as pesticides, fertilizers,
oil and grease, metals, nutrients, and sediments from farms,
ranches, and cities - have similarly produced inadequate water
quality in the San Francisco Bay-Delta. Industrial and municipal
discharges, combined sewer overflows, and urban and agricultural
nonpoint source runoff also have seriously reduced water quality
in the Great Lakes basin and resulted in the accumulation
of contaminants in lake sediments.
Endangered,
Rare, and Invasive Species
All seven ecosystems also provide habitat for listed endangered
and rare species. The South Florida Everglades has 68 plant
and animals species listed as threatened or endangered - more
than any other state. Two species of freshwater mussel listed
as endangered and another five species listed as rare are
found in the Upper Mississippi River basin. In the Columbia
River, 12 major salmon and steelhead runs are listed as endangered,
and several species are extinct.
The
ecosystems also share the problem of invasive species. In
the Upper Mississippi River basin, Asian carp, round gobies,
and zebra mussels are particularly destructive. Over 1.5 million
acres of the South Florida Everglades are infested with invasive
species and exotic plants. More that 140 non-native aquatic
species have colonized the Great Lakes since the 1800s resulting
in costly damage to ecology and water infrastructure.
Federal
and State Leadership
All seven initiatives have a designated federal and state
agency leading the restoration efforts. In most cases, priority
issues and restoration actions have determined these lead
agencies. For example, the Florida Everglades and Coastal
Louisiana restoration efforts both are co-led by the U.S.
Army Corps of Engineers because they involve extensive engineering
and replumbing. Because the Chesapeake Bay initiative centers
on water quality issues, it is managed by the U.S Environmental
Protection Agency.
Government
and Stakeholder Coordination
These restoration efforts require unprecedented levels of
federal, state, local, and stakeholder coordination and commitment
throughout both development and implementation phases. For
that reason, the restorations have established numerous task
forces, citizen advisory panels, and coalitions to oversee,
coordinate, and facilitate the restoration process. For example,
in the San Francisco Bay-Delta a group of more than 30 citizen-advisor
stakeholders are charted under the Federal Advisory Committee
Act as the Bay-Delta Advisory Council. In recognition of the
threats to the Mississippi River Delta and the Chenier Plain,
a unique mix of local and national environmental groups, civic
organizations, businesses, industry groups, local governments,
and concerned individuals have created the Coalition to Restore
Coastal Louisiana.
In
the Great Lakes, principal conveners - including the U.S.
Environmental Protection Agency's Administrator, Great Lakes
governors, mayors, tribal officials, and congressional delegation
members - recently established the Great Lakes Regional Collaboration
to prepare short- and long-term restoration goals and strategies.
In the Chesapeake, the Chesapeake Bay Commission - comprising
delegations from Maryland, Virginia, and Pennsylvania - assists
the state legislatures by promoting intergovernmental cooperation
and coordination for resource planning and uniformity of legislation,
among other functions.
Costs
Large-scale restoration in all the regions is also expected
to cost an average of $10 billion and take decades to achieve.
The federal government is expected to pay the more than half
the costs, with states providing funding through some form
of cost-share arrangement. For example, the total cost of
restoring the South Florida Everglades is estimated at $7.8
billion, half of which will be provided by the federal government
and the other half by the state of Florida. The effort is
also expected to take four decades.
CONTRASTING
CASE HISTORIES:
Geographic
Size
In terms of geographical coverage and population size, the
Great Lakes is the largest ecosystem restoration initiative
in the United States. At 200,000 square miles, the Great Lakes
watershed is more than three times the size of the Chesapeake
Bay, and more than ten times the size of the Florida Everglades.
The Great Lakes also has the distinction of being only one
of two restoration efforts to transcend international borders,
and encompasses more states than any of the other initiatives.
Taken as a whole, any large-scale restoration effort in the
Great Lakes must assimilate 10 different legislative bodies,
two federal governments, and many tribes and first nations-an
immense and complex undertaking. With territory in seven states
and the Canadian province of British Columbia, more holistic
approaches to restoring the Columbia River will similarly
need to assimilate eight legislative bodies, two federal governments
and many tribes and first nations.
Population
At 667 people per square mile, the South Florida Everglades
is the most densely populated restoration area, followed by
the Chesapeake Bay (250 people per square mile), San Francisco
Bay-Delta (179 people per square mile), the Great Lakes (170
people per square mile), the Upper Mississippi River (157
people per square mile); Coastal Louisiana (111 people per
square mile), and finally, the Columbia River (42 people per
square mile). However, the total population of the Great Lakes
basin, home to 34 million people, is nearly three times larger
than that of the Florida Everglades, and five times larger
than the San Francisco Bay-Delta population.
Ratio
of Land Area to Water
The Chesapeake Bay is unique among coastal and inland bodies
of water in that it has the largest land area to water volume
ratio of any system in the world - equal to 1,059 square miles
of land for every square mile of water. This is five times
the ratio of the next closest waterbody; the Gulf of Finland.
The principal reason for this is the Chesapeake's extreme
shallowness; its average depth is less than 21 feet. The shallowness
of the Bay however exacerbates its vulnerability to degradation
from actions that take place on land hundreds of miles from
its shores. This vulnerability is further compounded by the
dense population within the Bay's watershed.
Source
of Drinking Water
Several of the ecosystem restoration areas are a source of
drinking water for large populations. The Great Lakes--which
hold 95 percent of the nation's surface fresh water supply-provides
drinking water to more than 25 million people, the San Francisco
Bay-Delta provides drinking water to 22 million people and
the South Florida Everglades provides drinking water to 6
million people. This demand for clean freshwater not only
catalyzes the need for restoration and protection efforts,
but also determines the level of environmental quality these
efforts must achieve.
* * * * *
Each
of the seven ecosystems is nationally and globally unique
in its biological and habitat diversity, socio-economic dependencies,
and a whole range of other distinguishing characteristics.
This fact alone warrants a national commitment to conserving
and restoring these systems. Many of the systems already have
local and regional consensus for protection and restoration,
but all of them need national support to successfully garner
state and federal attention, program authorization, and funding.