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The Rewilding Institute
Criteria for Ecological Wilderness
This outline summarizes the draft guidelines
for Wilderness Area Identification and Selection, Design, and
Prioritization developed by The Rewilding Institute’s EcoWild
Working Group. Comments are welcome. To generally endorse these
guidelines and this approach,
Click Here.
These guidelines will continue to be revised. Further details are
forthcoming. Some Rewilding Institute Fellows are available to give
conservation groups presentations on these guidelines.
This outline includes the historic criteria used by federal
wilderness-managing agencies (particularly the Forest Service and
Bureau of Land Management) and by conservation groups for comparison
with the ecological criteria.
IDENTIFICATION
of lands for wilderness study, and SELECTION of particular
wilderness study areas for proposal as designated wilderness areas.
Traditional
Criteria by Agencies and Conservationists:
Roadless
Over 5,000 acres
Federal lands
Offer outstanding opportunities for primitive recreation and
travel
Offer solitude for the visitor
Scenic in the classic “Crown Jewel” model
Habitat for big game and sport fish
Resource conflicts absent or limited, seen as “reasonable”
Exclude “redundant” areas
Ecological
Criteria:
Roadlessness is good, but not essential (nor is it required by the
Wilderness Act)
roads
should be measured within cultural and economic context
roads are
“puncture wounds” that should be closed to heal
roadlessness nurtures more hot spots of biodiversity
lightly
roaded areas can be used to link Wilderness Areas
Areas of
less than 5,000 acres qualify as Wilderness, but bigger is always
better
scale is
important for ecosystem processes and species
Placement
in landscape for wildlife movement connectivity and permeability
accommodate migration routes, winter range, and other dynamic
processes
core
Wilderness may lie in a matrix of federal, state, and private land
Geological, educational, scenic, historical, and primitive
recreational values
Areas that
protect and restore the diversity of life
unusual
and underrepresented ecosystems and landforms
habitat
for rare, sensitive, imperiled, and highly interactive species
riparian
and wetland habitats
Resource
conflicts may exist; “reasonable” has been replaced by ecological
criteria
Natural
vegetation (present or restorable) including ancient forests
Use
precautionary principle
DESIGN of
proposed wilderness areas, and drawing boundaries for proposed
wilderness areas and identification of units to be included or not
included
Agency
Criteria:
Topographically “defensible” boundaries
Exclude
areas with resource conflicts
Exclude
flat areas or areas without vegetative screening (“lack of
solitude”)
Exclude
areas with fading signs of roads and other human use (“purity”)
Exclude
“unmanageable” areas
Exclude
areas agency perceives are of “lower quality”
Exclude
areas with limited recreational appeal
Exclude
“redundant” areas
Traditional
Conservationist Criteria:
Extend
boundaries out to surrounding roads
Exclude
some major resource conflicts
Generally
exclude signs of human impact but to lesser degree than do
agencies
Cherrystem
roads and other human intrusions
Ecological
Criteria:
Design to
accommodate components of varied ecosystems and landforms
May
include areas where resource conflicts exist and where
management will be challenging if of high ecological value
Include
areas showing some sign of human use if ecologically important
such as riparian, wetland, natural vegetation, habitat for focal
species
Design with rounded boundaries whenever possible to maximize
internal area and minimize edges
Do not
cherrystem roads and other human intrusions that can be closed or
restored
close
roads or gate roads for permit holders’ access only
Implement
connectivity within wildlands network
bring
boundaries of separate units closer together
extend
boundaries to roads and suitable buffers
Consider
landscape dynamics
changes in vegetation over time
influenced by changing fire regimes and exotic
species
affected by scale and connectivity
Use
precautionary principle
Consider defensible boundaries
for management purposes but not necessarily based on
“topographical” landmarks
Bigger is
always better
PRIORITIZATION
of proposed wilderness areas: determining relative priority for
designation of proposed wilderness areas in a region
Agency
Criteria:
Scenic in
the classic “Crown Jewel” model
Exclude
areas with resource conflicts
Exclude
areas of controversy and opposition
Exclude
areas perceived as “too much” or unreasonable
Traditional
Conservationist Criteria:
Follow
agency criteria but to a lesser degree
Areas with
a strong constituency
Exclude areas perceived as “too much” or unreasonable (but more
liberal than agencies)
Areas
palatable to members of Congress
Areas that
without protection would be vulnerable to degradation
Ecological
Criteria:
Consider
placement in landscape to function as part of a wildlands network
including areas with potential for restoration as core Wilderness
Ecological
value for sustaining and restoring biodiversity
particularly focal species such
as large carnivores or highly interactive species that serve as an
umbrella for ecosystem protection
also “hot
spots” of biodiversity
Larger areas, though not
exclusively, which are more manageable and more self-regulating
also consider islands and small areas within cultural and
ecological context
Areas that
offer fire restoration opportunities
Areas with plant communities and landforms not well represented in
protected area systems
Areas with
potential core habitat for large carnivores
Use
precautionary principle
Note: In
some cases, ecological criteria replaces agency and traditional
conservationist criteria; in other cases, it modifies or adds to
agency and traditional conservationist criteria. Ecological
criteria are not in conflict with, nor do they denigrate, scenic and
recreational (experiential) values. Since the 1980s,
conservationists have been generally moving in the direction of
ecological criteria. Keep in mind that this is an outline and not a
detailed discussion.
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