Introduction
This summary of the draft Environmental Impact
Statement (DEIS) describes 4 alternatives that represent
different approaches to grizzly bear recovery and management in
the Bitterroot Ecosystem (BE) of central Idaho and western
Montana. The process used to develop alternatives, and the
environmental consequences of implementing each alternative are
described. Two alternatives involve reintroducing grizzly bears
from other areas in the U. S. and Canada to the BE: Alternative 1
- Reintroduction of a Nonessential Experimental Population
(Proposed Action); and Alternative 4 - Reintroduction of a
Threatened Population with Full Protection of the Endangered
Species Act (ESA). Alternative 2 - The No Action Alternative:
Natural Recovery, encourages natural recovery of grizzly bears in
the BE through range expansion from existing populations. And
Alternative 3 - The No Grizzly Bear Alternative, prevents grizzly
bear recovery. These alternatives were developed in response to
public comments and represent a full range of alternatives for
consideration. All issues and concerns identified by the public
were considered and the most significant were analyzed in detail.
The potential effects of each alternative on human health and
safety, source grizzly bear populations, land-use activities,
wildlife populations, public access and recreational use, social
aspects, and regional economies are described.
Important
In order to be considered in the development
of the final plan, comments on the DEIS must be received by
September 30, 1997. Public comments will not be available for
public review until after the DEIS comment period ends. Copies of
the DEIS have been sent to public libraries in Montana and Idaho,
and those cities where open houses were held. In addition,
several hundred copies of the DEIS were sent to organizations or
individuals who represent people who may be significantly
impacted by any decision. The DEIS summary document is also
available on the internet at:
http://www.r6.fws.gov/endspp/grizzly. Those wishing to review the
complete draft Environmental Impact Statement, or needing further
information should contact:
Dr. Christopher Servheen, Grizzly Bear Recovery Coordinator / Bitterroot EIS Team Leader
U. S. Fish and Wildlife Service
P.O. Box 5127
Missoula, Montana 59806
Phone: (406) 243-4903, Fax: (406) 329-3212
PURPOSE OF AND NEED FOR THE ACTION
Purpose. Grizzly
bears (Ursus arctos horribilis) are a part of America=s
rich wildlife heritage and once ranged throughout most of the
western United States. However, distribution and population
levels of this species have been diminished by excessive
human-caused mortality and loss of habitat. Today, only 800 to
1000 grizzly bears remain in a few populations in Montana
(Northern Continental Divide, Yellowstone, and Cabinet-Yaak
Ecosystems), Idaho (Yellowstone, Cabinet-Yaak, and Selkirk
Ecosystems), Wyoming (Yellowstone Ecosystem), and Washington
(Selkirk and North Cascades Ecosystems). Wildlife species, like
grizzly bear, are most vulnerable when confined to small portions
of their historical range and limited to a few, small
populations. Expansion of the range of the species will increase
the number of bears within the lower 48 states and increase
habitat size and extent, and further conservation of the species.
The Bitterroot Ecosystem (BE) is one of the
largest contiguous blocks of federal land remaining in the lower
48 United States. The core of the ecosystem contains two
wilderness areas which make up the largest block of wilderness
habitat in the Rocky Mountains south of Canada. Of all remaining
unoccupied grizzly bear habitat in the lower 48 States, this area
in the Bitterroot Mountains has the best potential for grizzly
bear recovery, primarily due to the large wilderness area. As
such, the BE offers excellent potential to recover a healthy
population of grizzly bears and to boost long-term survival and
recovery prospects for this species in the contiguous United
States.
The U. S. Fish and Wildlife Service (USFWS),
with support of the Interagency Grizzly Bear Committee (IGBC is a
group of high-level administrators that represent the federal and
state agencies involved in grizzly bear recovery, and coordinate
agency efforts in implementing the Grizzly Bear Recovery Plan),
proposes to recover the grizzly bear and restore this component
of the BE by reestablishing the species within this portion of
its historical range. The USFWS has determined that there are no
grizzly bears in the BE at this time, that recovery of grizzly
bears in the BE would facilitate conservation and recovery of the
species in the lower 48 States, and that recovery of grizzly
bears in the BE would require reintroduction of bears from other
areas (USFWS 1993, 1996). The action proposed in this DEIS (USFWS
1997) is to reintroduce a minimum of 25 grizzly bears over a
5-year period from which a population could grow over time.
Need. The grizzly
bear was listed as a threatened species in the lower 48 States
under the Endangered Species Act (ESA) in 1975 (Federal Register,
V.40, No.145, Part IV-3173-4). As such, the U.S. Fish and
Wildlife Service was mandated by Congress to conserve listed
species and the ecosystems upon which they depend.
The USFWS is the primary agency responsible
for recovery and conservation of threatened species, including
grizzly bears in the U.S. The Revised Grizzly Bear Recovery Plan
(USFWS 1993) and the Bitterroot Ecosystem Recovery Plan Chapter -
Supplement to the Grizzly Bear Recovery Plan (USFWS 1996)
identify actions necessary for conservation and recovery of the
species. The ultimate goal of the plan is removal of the species
from threatened status in the conterminous 48 States.
LOCATION OF THE PROPOSED ACTION
This project involves the area defined as the
Bitterroot Ecosystem of central Idaho and western Montana in the
northern Rocky Mountains. The analysis area considered in this
draft EIS is referred to as the Bitterroot Grizzly Bear Primary
Analysis Area (PAA) and includes USDA Forest Service lands
potentially affected by grizzly bear recovery in the BE of Idaho
and Montana (Figure S-1). The heart of the PAA is centered around
Wilderness Areas of central Idaho, while a small portion extends
over the crest of the Bitterroot Mountains into western Montana.
The PAA includes about 16,686,596 acres
(26,073 square miles) of contiguous national forest lands
including all or parts of the Bitterroot, Boise, Challis,
Clearwater, Lolo, Nez Perce, Payette, Sawtooth, Salmon, and
Panhandle National Forests. The center of the area is
characterized by 3 large wilderness areas covering a contiguous
area of almost 4 million acres (6,250 mi2). These
include the Frank Church-River of No Return (2,361,767 acres;
3,690 mi2), the Selway-Bitterroot (1,340,681 acres;
2,095 mi2), and the Gospel Hump (200,464 acres; 313 mi2)
Wilderness Areas. The area contains 3 major mountain ranges; the
Salmon River Mountains (south of the Salmon River), the
Clearwater Mountains which extend from the Salmon River north to
the upper Clearwater River drainage, and the Bitterroot Mountains
which form the eastern border of the PAA along the Montana-Idaho
state line.

Table S-1 presents the basic information about the Bitterroot Ecosystem PAA. It describes the area and may be useful in understanding potential impacts of grizzly bear reintroduction. This information represents the situation that currently exists without grizzly bears in the BE.
Table S-1. A summary of the key characteristics of the Bitterroot Ecosystem Grizzly Bear Primary Analysis Area (PAA) which could potentially be affected by grizzly bear recovery. |
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Characteristic |
Central Idaho |
Western Montana |
||
Land (in the 14-county area that encompasses the PAA) |
||||
Acres |
22,687,424 |
5,740,560 |
||
% Federal Ownership |
80 |
59 |
||
% Private ownership |
15 |
38 |
||
% National Park, Wilderness, or Wildlife Refuge |
17 |
trace |
||
Public land usesa |
||||
Recreational visits/year to national forest lands in the PAA |
8,576,995 |
4,691,400 |
||
Acres open to grazing on national forests included in the PAA |
4,467,571 |
348,400 |
||
Acres suitable for timber harvest in national forests included in the PAA |
4,387,831 |
1,602,331 |
||
Acres of timber projected for harvest annually on national forests included in the PAA |
44,368 |
13,618 |
||
Total miles of system roads on national forest lands in the PAA |
17,111 |
9,053 |
||
Miles of year-round open system roads on national forest lands in the PAA |
7,448 |
4,114 |
||
Miles of closed or restricted access system roads on national forest lands in the PAA |
9,664 |
4,939 |
||
Total miles of recreational trails on national forest lands in the PAA |
12,439 |
2,350 |
||
Miles of recreational trails open to motorized vehicles in the PAA |
6,073 |
1,474 |
||
People/Land Economy (in the 14-county area) |
||||
Population (numbers) |
103,380 |
115,681 |
||
Population (people/mi.2) |
3.2 |
11.6 |
||
Total personal income for Idaho and Montana portions of the PAA (billions of dollars) |
||||
Average per capita income for Idaho and Montana portions of the PAA ($) |
||||
Farm income for Idaho and Montana combined (% of total personal income) |
||||
Local services income for Idaho and Montana combined (% of total personal income) |
||||
Other Industry income for Idaho and Montana combined (% of total personal income) |
||||
Other non-earnedb income for Idaho and Montana combined (% of total personal income) |
|
|||
Livestock |
||||
Numbers of cattle in the 14-county area (spring) of the PAA |
295,500 |
72,300 |
||
Number of sheep in the 14-county area (spring) of the PAA |
49,045 |
6,645 |
||
Number of livestock on national forest allotments in the PAA (May through October) |
||||
Adult cattle and calves |
64,589 |
4,222 |
||
Adult sheep and lambs |
229,188 |
0 |
||
Horses |
939 |
9 |
||
Total livestock |
294,716 |
4,231 |
||
Estimated current livestock mortality in the PAA and surrounding counties from all causes per year based upon spring cattle and sheep numbersc: cattle |
12,314 3.3% loss (69% calf) |
|||
sheep |
9,366 16.8% loss (~72% lambs) |
|||
horses |
unknown, very low |
|||
Ungulate Populations (postharvest estimates) |
||||
Elk |
82,293 |
4,861 |
||
Deer (mule & white-tailed) |
>159,575 |
21,750 |
||
Moose |
1,700 |
- |
||
Bighorn Sheep |
1,666 |
337 |
||
Mountain goat |
2,017 |
160 |
||
Total ungulate population |
247,251 |
27,108 |
||
Ungulate Annual Harvest |
||||
Elk |
13,366 |
934 |
||
Deer (mule & white-tailed) |
19,953 |
3,480 |
||
Moose |
161 |
14 |
||
Bighorn sheep |
37 |
16 |
||
Mountain goat |
35 |
11 |
||
Total ungulate harvest |
33,552 |
4,455 |
||
Percent of ungulate population harvested |
14 |
16 |
||
Estimated ungulates dying/year (all causes)d |
182,509 |
16,977 |
||
Percent of mortality attributable to hunting |
19.0 |
26.0 |
||
a A wide variety of land-use restrictions (seasonal and permanent) are employed on public lands throughout the PAA for protection of natural resources and public safety including: on motorized vehicles, construction of structures, Animal Damage Control activities, big game winter range, calving areas, security and migration habitat, raptor nest sites, endangered species, erosion control, wetland protection, to provide a variety of outdoor experiences (motorized or nonmotorized, wilderness or developed, etc.). b Non-earned income represents investments, entitlements, and retirement income that often does not depend on where a person lives. The growth of this segment of the economy over the last 2 decades results from people with this type of income moving into central Idaho and western Montana because these areas are perceived to have a lifestyle that people want to participate in (wild spaces, abundant wildlife, less crowding, low crime, clean air, etc.). c Source: U.S. Fish and Wildlife Service. 1994. The reintroduction of gray wolves to Yellowstone National Park and central Idaho. Final Environmental Impact Statement. U.S. Fish and Wildlife Service, Helena, MT. d Including hunting, crippling loss, poaching, road kill, predation, disease, starvation, drowning, winter kill, accidents, fighting, etc. |
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THE PLANNING PROCESS
One of the first steps in the planning process
was to develop a public participation and interagency
coordination program to identify issues related to grizzly bear
recovery in the BE and alternatives to be considered in the
National Environmental Policy Act (NEPA) process. Natural
resource and public use information was gathered. Previous plans
and reports dealing with grizzly bear recovery were reviewed. The
USFWS is solely responsible for the DEIS, although
representatives from the USDA Forest Service, Idaho Department of
Fish and Game, Montana Department of Fish, Wildlife, and Parks,
and Nez Perce Tribe assisted in preparation. Participation and
review by representatives of other agencies does not imply
concurrence, endorsement, or agreement to any recommendations,
conclusions, or statements in the DEIS.
Issue Scoping
Seven public scoping sessions, in the form of open houses were held in Grangeville, Orofino, and Boise in Idaho; Missoula, Helena, and Hamilton in Montana; and Salt Lake City, Utah; from July 5 to 11 with a 45-day public comment period on the proposal ending July 29, and extended to August 21, 1995. Written comments on preliminary issues and alternatives were received from more than 3,300 individuals, organizations and government agencies. About 80 percent of written responses were from residents of counties in Idaho and Montana adjacent to the proposed recovery areas. All issues were considered, organized into 46 separate headings, and addressed by the USFWS as follows. (Further explanation of the issues/impacts and how they were addressed is provided in the DEIS.)
Twenty-six issues and impacts were addressed / included as part of one or more alternatives:
Management Strategies
Strategies to Control Nuisance Bears
Illegal Killing of Grizzly Bears
Recovery Area (Boundaries, Size, & Range)
Recovery Time
Monitoring and Evaluation
Nonessential Experimental Population & Area
Private Property Rights
Endangered Species Act (ESA)
Ecosystem Management
Grizzly Bears as a Missing Component of the
Ecosystem
Definition of Population Viability for Grizzly Bears
Travel Corridors & Linkages (Range of Grizzly Bears)
Habitat Protection Requirements
Laws, Restrictions, Rights, Authority
Federal, State, Local, and Tribal Authority
Compliance with Forest Plans
Are Grizzly Bears Native to the Bitterroot Ecosystem
Effects on Grizzly Bears from Human Incursions
Outside Wilderness
Population Corridor Linkages
Effects Ato@ Grizzly Bears (Genetics, Disease,
Colonization, etc.)
Habitat Security
Cost of Program to Taxpayer
Education
Political Influence
Enjoyment of Grizzly Bears (Viewing, etc.)
Eleven issues/impacts (consolidated into 7 areas) were analyzed in detail in the DEIS because they could be potentially impacted by grizzly bear recovery strategies:
Effects of Grizzly Bear Recovery on Human Health and Safety
Effects of Grizzly Bear Recovery on Source Populations of Grizzly Bears
Effects of Grizzly Bear Recovery on Land-Use Activities - to include Timber Harvest,
Minerals Extraction, and Livestock Grazing
Effects of Grizzly Bear Recovery on Wildlife
Effects of Grizzly Bear Recovery on Public Access and Recreational Use
Social Effects of Grizzly Bear Recovery
Economic Effects of Grizzly Bear Recovery
Nine issues/impacts were not evaluated further in the DEIS because they were not significant to the decision being made: (Although these issues, as identified by the public (see DEIS Chapter 1 ), were not used to formulate alternatives or analyze effects, most are addressed within the DEIS and Appendices).
Consultation with Fish & Wildlife Service
Interagency Grizzly Bear Committee Guidelines
State or Private Bear Management Specialist
Wilderness Act
Effects of Grizzly Bear on Other Endangered
Species
Effects of Grizzly Bear on Other Animals,
Fish, Birds, etc.
Spiritual/Cultural
Visitor Use
Miscellaneous
Alternative Scoping
The USFWS used preliminary issues identified from public comments received during scoping meetings for the BE Recovery Plan Chapter, and the Notice of Intent to complete an EIS for Recovery in the BE, to formulate three preliminary alternatives. Prior to conducting formal scoping meetings and a comment period, the USFWS proposed these three preliminary alternatives for consideration and published them in a Scoping of Issues and Alternatives brochure that requested ideas and comments from the public. The alternatives were: Alternative 1 - No Action (Natural Recolonization); Alternative 2 - Reintroduction of an Experimental Population (Proposed Action); and Alternative 3 - Accelerated Reintroduction of a Standard (Fully Protected) Population.
Two new alternatives were suggested during the
public scoping period. The first proposed alternative entitled
The Citizen Management Committee Alternative was submitted by the
National Wildlife Federation, Defenders of Wildlife, the Resource
Organization on Timber Supply, and the Intermountain Forest
Industry Association (USFWS 1995). The second alternative
identified was the Alliance for the Wild Rockies Alternative,
which was proposed by the Alliance (USFWS 1995).
Alternatives Identified During Scoping, but not Evaluated Further
Alternative 3 that was identified in the
scoping document, AAccelerated
Reintroduction of a Standard Population@ is not
evaluated in this DEIS. Securing 10 non-nuisance grizzly bears
per year from similar habitat in the lower 48 States or southern
British Columbia is not feasible because of a lack of a suitable
number of bears from existing source populations. For this reason
the alternative was eliminated.
ALTERNATIVES ANALYZED IN THE DEIS
Four alternatives that represent different
approaches to grizzly bear recovery and management were developed
for evaluation in the DEIS because they encompass public concerns
raised during scoping, and they represent a full range of
alternatives. Two alternatives (Alternatives 2 and 3) do not
necessarily meet the purpose of and need for action, but were
included in the DEIS to be responsive to public comments, to
provide a full range of alternatives for consideration, and to
meet the requirements of NEPA. All four alternatives reflect
public comments and suggestions identified through issue and
alternative scoping. The alternatives considered in this DEIS
are:
Alternative 1. Reintroduction of a Nonessential Experimental Population Alternative (Proposed Action):
The goal is to accomplish grizzly bear
recovery by reintroducing grizzly bears designated as a
nonessential experimental population to central Idaho and by
implementing provisions within Section 10(j) of the ESA, conduct
grizzly bear management to address local concerns. A Citizen
Management Committee (CMC), created under a special rule to be
published in the federal register, would be tasked with
management of this grizzly bear population.
Alternative 2. The No Action Alternative - Natural Recovery:
The goal is to allow grizzly bears to expand
from their current range in north Idaho and northwestern Montana
southward into central Idaho and western Montana, and to
recolonize the BE. The ultimate goal is natural recovery of
grizzly bears in the BE.
Alternative 3. The No Grizzly Bear Alternative:
This alternative would prevent grizzly bear
recovery in the BE.
Alternative 4. Reintroduction of a Threatened Population with Full Protection of the ESA Alternative:
The goal is to achieve recovery through
reintroduction and extensive habitat protection and enhancement
to promote natural recovery. The grizzly bear would have full
status as a threatened species under the provisions of the ESA.
Description and Impacts of the Proposed
Action and Alternatives
Alternative 1. Reintroduction of a Nonessential Experimental Population (Proposed Action):
Summary.-- The purpose of this alternative is to accomplish grizzly bear recovery by reintroducing grizzly bears designated as a nonessential experimental population to central Idaho and implementing provisions within Section 10(j) of the ESA to conduct special management to address local concerns. Section 10(j) provides for reintroduction of experimental populations under special regulations. "Experimental population" designation gives the USFWS more flexibility because such populations can be treated as "a species proposed to be listed" rather than "threatened or endangered". If a reintroduced population of grizzly bears is designated "experimental" and "nonessential" (refers to an experimental population whose loss would not likely reduce the survival of the species in the wild) under the ESA 10(j) amendment, other federal agencies are required only to confer with USFWS on federal activities that are likely to jeopardize the species. Management of a nonessential experimental population can thus be tailored to specific areas and specific local conditions, including meeting concerns of those opposed to reintroduction. Because reintroduced grizzly bears would be classified as a nonessential experimental population, the Service=s management practices can reduce local concerns about excessive government regulation on private lands, uncontrolled livestock depredations, excessive big game predation, and lack of State government and local citizen involvement in the program. A Citizen Management Committee (CMC) would be authorized management implementation responsibility for the Bitterroot grizzly bear experimental population.
The Bitterroot Grizzly Bear Experimental Population Area (experimental population area), which includes most of central Idaho and part of western Montana (Figure S-2), would be established by the USFWS under authority of Section 10(j) of the ESA. This would include the area bounded by U.S. Highway 93 from Missoula, Montana to Challis, Idaho; Idaho Highway 75 from Challis to Stanley, Idaho; Idaho Highway 21 from Stanley to Lowman, Idaho; Idaho Highway 17 from Lowman to Banks, Idaho; Idaho Highway 55 from Banks to New Meadows, Idaho; U.S. Highway 95 from New Meadows to Coeur d=Alene, Idaho; and Interstate 90 from Coeur d=Alene to Missoula, Montana. The experimental population area encompasses approximately 25,140 square miles. The best scientific evidence available indicates there are no grizzly bears in the experimental population area at this time (USFWS 1996). Ongoing grizzly bear monitoring efforts would continue. The USFWS would designate the Bitterroot Grizzly Bear Recovery Area (recovery area) to consist of the Selway-Bitterroot Wilderness and the Frank Church-River of No Return Wilderness (Figure S-2). The recovery area contains approximately 5,785 square miles.
The first year of implementation would be a Aphase-in@
year where sanitation equipment would be installed in key areas,
and information and education outreach programs would be
initiated. Grizzly bears would be reintroduced into the
Selway-Bitterroot Wilderness portion of the recovery area during
the second year of implementation. Specific reintroduction sites
would be recommended by the management agencies to the CMC. The
recovery area would be identified as the area of recovery
emphasis. Bears moving outside the recovery area would be
accommodated through management provisions in the proposed
special rule and through management plans and policies developed
by the Citizen Management Committee, unless potential conflicts
were significant and could not be corrected.
The CMC would be authorized management
implementation responsibility by the Secretary of Interior (in
consultation with the governors of Idaho and Montana) for the
Bitterroot grizzly bear nonessential experimental population. The
CMC would be comprised of local citizens and agency
representatives from federal and state agencies and the Nez Perce
Tribe. Grizzly bear management would allow for resource
extraction activities to continue without formal Section 7
consultation under Section7(a)(2) of the ESA. The CMC would be
responsible for recommending changes in land-use standards and
guidelines as necessary for grizzly bear management. People could
continue to kill grizzly bears in self-defense or in defense of
others. Following issuance of a permit by the USFWS, the public
would be allowed to harass a grizzly bear attacking livestock
(cattle, sheep, horses, and mules) or bees. A livestock owner may
be issued a permit to kill a grizzly bear killing or pursuing
livestock on private lands if it has not been possible to capture
such a bear or deter depredations through agency efforts. If
significant conflicts occurred between grizzly bears and
livestock within the experimental area, these could be resolved
in favor of the livestock by capture or elimination of the bear
depending on the circumstances. There would be no federal
compensation program, but compensation from existing private
funding sources would be encouraged. Toxicants lethal to bears
are not used on public lands within the recovery and experimental
population areas. It is anticipated that ongoing animal damage
control activities would not be affected by grizzly bear
recovery. Any conflicts or mortalities associated with these
activities would result in review by the CMC and any necessary
changes would be recommended by the CMC.

Implementation of Alternative 1 would
involveImplementation of
Alternative 1 would involve.-- The Endangered Species Act
Proposed Special Rule 10(j) for Establishment of a Nonessential
Experimental Population of Grizzly Bears in the Bitterroot Area
that is being published in the Federal Register simultaneously
with the release of the DEIS, describes what this alternative
would involve. This summary includes only highlight points from
the proposed rule.
The proposed special rule would:
- Designate much
of central Idaho and part of western Montana (see description
above) as the Bitterroot Grizzly Bear Experimental Population
Area for grizzly bear reintroduction. Designate the Bitterroot
Grizzly Bear Recovery Area for recovery emphasis to consist of
the Selway-Bitterroot Wilderness and the Frank Church-River of No
Return Wilderness (Figure S-2). Bears would only be released in
the Selway-Bitterroot Wilderness, unless the Citizen Management
Committee determines that reintroduction in the River of No
Return Wilderness is appropriate. Specific relocation sites would
be recommended by the management agencies to the CMC.
- Authorize a 15
member Citizen Management Committee (CMC) to be appointed by the
Secretary of Interior in consultation with the governors of Idaho
and Montana, and the Nez Perce Tribe. This committee would
implement the Bitterroot Chapter of the Grizzly Bear Recovery
Plan (USFWS 1996) and would be authorized management
implementation responsibility by the Secretary of Interior, in
consultation with the governors of Idaho and Montana, for the
Bitterroot grizzly bear experimental population. The CMC would
develop management plans and policies, as necessary, for
management of grizzly bears in the Experimental Area. All
decisions of the CMC must lead to recovery of the grizzly bear in
the BE and minimize social and economic impacts. Members would
serve six-year terms and would consist of seven individuals
appointed by the Secretary of the Interior based on the
recommendations of the governor of Idaho, five members appointed
by the Secretary of the Interior based on recommendations of the
Governor of Montana, one member appointed by the Secretary based
on the recommendation of the Nez Perce Tribe, one member
representing the USDA Forest Service appointed by the Secretary
of Agriculture or his/her designee, and one member representing
the USFWS appointed by the Secretary of the Interior or his/her
designee. Members recommended by the Governors of Idaho and
Montana would be based on recommendations of interested parties
and would include at least one representative each from the
appropriate state fish and wildlife agencies. If either governor
failed to make recommendations, the Secretary would accept
recommendations from interested parties on the Governor=s
behalf. The CMC is to consist of a cross-section of interests
reflecting a balance of viewpoints, be selected for their
diversity of knowledge and experience in natural resource issues,
and for their commitment to collaborative decision-making. The
CMC would be selected from communities within and adjacent to the
recovery and experimental population areas. The CMC would
continue until recovery objectives were met and the Secretary of
Interior completed delisting. Management authority would then
revert to the state wildlife agencies.
- Direct the Secretary of the Interior to review two-year work plans submitted by the Committee which outline directions for the Bitterroot reintroduction effort. If the Secretary determines, through his/her representative(s) on the Committee, that decisions of the Committee, management plans, or implementation of those plans are not leading to recovery of the grizzly bear within the experimental population area, the Secretary's representative on the Committee shall solicit from the Committee a determination whether the decision, the plan, or implementation of components of the plan are leading to recovery. Notwithstanding a determination by the Committee that a decision, plan, or implementation of a plan are leading to recovery of the grizzly bear within the experimental population area, the Secretary, who necessarily retains final responsibility and authority for implementation of the ESA, may find that the decision, plan, or implementation of a plan are inadequate for recovery and may resume management responsibility. In such case the Committee would be disbanded and all requirements identified in this rule regarding the Committee would be automatically nullified.
- Emphasize
grizzly bear recovery in the Recovery Area, but bears moving
outside the recovery area would be accommodated through
management provisions in the special rule and through management
plans and policies developed by the CMC, unless potential
conflicts were significant and could not be corrected, in which
case the CMC would develop strategies to discourage grizzly bear
occupancy in portions of the experimental area. Grizzly bear
management would allow for resource extraction activities to
continue without formal Section 7 consultation. All Section 9 Atakings@
provisions under the ESA for the nonessential experimental
population of grizzly bears in the BE are included in the special
rule. The CMC would be responsible for recommending changes in
land-use standards and guidelines as necessary for grizzly bear
management. The special rule would continue to allow a person to
take a grizzly bear in self-defense or defense of others,
provided that such taking is reported within 24 hours to
appropriate authorities. Livestock owners would be allowed to
take a grizzly bear once a permit has been obtained, the response
protocol established by the CMC has been satisfied, and efforts
by the wildlife agency personnel to capture depredating bears
have been unsuccessful.
- Establish a
tentative recovery goal of approximately 280 grizzly bears (bears
distributed over 5,785 mi2 of designated wilderness
and adjacent lands) occupying suitable habitat within the
wilderness and adjacent lands (USFWS 1996). The CMC could
recommend a refined recovery goal for the Bitterroot Chapter of
the Grizzly Bear Recovery Plan, based on scientific advice, once
grizzly bears were reintroduced and sufficient information was
available. The recovery goal for the Bitterroot grizzly bear
population would be consistent with habitat available within the
recovery area and the best scientific and commercial data
available. Any revised recovery goals developed by the CMC would
require public review appropriate for the revision of a recovery
plan. Grizzly bears outside the recovery area would contribute to
meeting the recovery goal if there were reasonable certainty of
their long-term occupancy in such habitats outside the recovery
area. The CMC would develop a process for obtaining the best
biological, social, and economic data, which would include an
explicit mechanism for peer-reviewed, scientific articles to be
submitted to and considered by the CMC, as well as periodic
public meetings (not less than every two years) in which
qualified scientists could submit comments to and be questioned
by the CMC.
- Allow for
reintroduction of a minimum of 25 grizzly bears into the recovery
area over a period of 5 years, until a colony of bears has been
established. Using the best scientific evidence available, and
standards and criteria developed by the agencies and the CMC, the
CMC would determine if bear reintroduction was successful after a
period of at least 10 years. If based on these criteria and
recommendations by the CMC, the Secretary after consultation with
the CMC, states of Idaho and Montana and their fish and game
agencies, and the Nez Perce Tribe concludes reintroduction has
failed, no more bears would be reintroduced. Any remaining bears
would retain their experimental status.
- Authorize Idaho
Department of Fish and Game (IDFG), Montana Department of Fish,
Wildlife, and Parks (MDFWP), and the USDA Forest Service (USFS),
in consultation with the USFWS and the Nez Perce Tribe, to
exercise day-to-day management responsibility within the
experimental population area while implementing the BE Grizzly
Bear Recovery Plan Chapter, and the special rules, policies, and
plans of the CMC.
The USFWS, USFS, states of Idaho and Montana,
and Nez Perce Tribe in consultation with the CMC would release a
minimum of 25 grizzly bears into the recovery area over a period
of 5 years. Procedures would include:
- Necessary
permits, agreements, and archeological site clearances would be
obtained, and activities conducted for a scientifically based
grizzly bear reintroduction program.
- Subadult
grizzly bears of both sexes would be trapped, each year for 5
years, from areas in Canada (in cooperation with Canadian
authorities) and the United States that presently have healthy
populations of grizzly bears living in habitats that are similar
to those found in the Bitterroot Ecosystem. Three sources of
grizzly bears for the BE have been identified: southeast British
Columbia, the Northern Continental Divide Ecosystem (NCDE)
population in northwest Montana, and the Yellowstone Ecosystem
(YE) population. Specific numbers of bears that could be obtained
yearly from potential source populations is unknown at this time.
Some undetermined level of mortality is expected among
transplanted bears. Every effort would be taken to minimize this,
but mortalities are expected to occur. Any transplanted bears
that died or were removed as a result of human action could be
replaced. Such replacements would be in addition to the original
minimum of 25 bears.
- Grizzly bears
would be captured and reintroduced at the best time of year to
optimize their survival. This would likely occur when grizzly
bear food supplies in the BE are optimum. Each individual
reintroduced grizzly bear would be radio collared and monitored
to determine their movements and how they use their habitat, and
to keep the public informed of general bear locations and
recovery efforts.
Expected actions and effects of Alternative 1.-- See Tables S-2 and S-3 for a comparison of expected actions and effects of this alternative. The tentative recovery goal of this alternative is approximately 280 grizzly bears (USFWS 1996). Realistically, grizzly bear recovery in the BE could take a minimum of 50 years (4% growth rate), and given potential conflicts, could likely take more than 110 years (2% growth rate). Total annual implementation cost during the 5-year reintroduction period would be approximately $393,632/year, and the total 5-year implementation cost would be approximately $1,968,160. Annual costs for monitoring and citizen management would be approximately $168,000 for each year beyond the 5-year reintroduction period.
A brief summary of effects: A recovered grizzly bear population would kill about 6
cattle (4-7) and 22 sheep (0-44) and up to 504 ungulates per
year. This would not measurably impact ungulate populations or
hunter harvest. Nuisance bear incidents could be up to 59 (0-118)
per year. There would be no anticipated impacts to land use
activities on public or private land to include timber harvest,
mining, and public access/recreational use. Changes to hunting
seasons could occur due to conflicts. Risk to human health and
safety from a recovered grizzly bear population would be less
than 1 injury per year and less than 1 human mortality every few
decades. Economic analyses indicate grizzly bear recovery in the
BE would lead to total net economic benefits of 40.4-60.6 million
dollars per year. Annual cost would include an implementation
cost of $168,000 and livestock loss value of $2,260-$8,000, for a
total cost of $170,260-$176,000 per year (cost during the initial
5-year reintroduction phase would be $395,892-$401,635 per year).
Alternative 2. The No Action Alternative - Natural Recovery:
Summary.-- The
purpose of this alternative is to allow grizzly bears to expand
from their current range in north Idaho and northwestern Montana
southward into central Idaho and western Montana, and to
recolonize the BE. The ultimate goal is natural recovery of
grizzly bears in the BE. Grizzly bears would be allowed to expand
their current range in north Idaho and northwestern Montana
southward into central Idaho and western Montana. The likelihood
of recovery of grizzly bears in the BE through natural
recolonization appears remote because grizzly bears do not move
far to colonize distant, disjunct areas. If grizzly bears did
disperse, they would be protected as a threatened species under
the Endangered Species Act wherever they occurred. Because
grizzly bears would be fully protected as threatened under the
ESA, Section 7(a)(2) would apply upon implementation of this
alternative and all federal actions within the recovery zone
would be subject to Section 7 consultation with the USFWS. The
Interagency Grizzly Bear Committee (IGBC) nuisance grizzly bear
management guidelines (IGBC 1986) would be implemented to address
conflicts that occur between grizzly bears and humans. The USFWS
would have management authority for all aspects of grizzly bear
recovery. It is unknown whether this alternative would result in
recovery of grizzly bears in the BE. It was the opinion of the
Bitterroot Ecosystem Technical Committee that recovery of grizzly
bears in the BE through recolonization is considered a remote
possibility because of lack of movement or dispersal by grizzly
bears in the northern Rocky Mountains (USFWS 1996). If recovery
was achieved, grizzly bears would be removed from ESA protection
and the states of Idaho and Montana would continue to manage
bears.
Implementation of Alternative 2 would involve:
- The USFWS would designate the Bitterroot
Grizzly Bear Recovery Zone as delineated in Figure S-3, and
consistent with the 5,500 square mile Bitterroot Grizzly Bear
Evaluation Area (BEA) as defined in the Bitterroot Ecosystem
Recovery Plan Chapter - Supplement to the Grizzly Bear Recovery
Plan (USFWS 1993, 1996).
- The USFWS would
establish a tentative long-term recovery goal of approximately
280 grizzly bears (bears distributed over 5,500 mi2 of
designated wilderness and adjacent lands) within the recovery
zone (USFWS 1996) (Figure S-3).
- Primary grizzly
bear management responsibility would reside with the USFWS and
include active participation by federal land management agencies,
the states of Idaho and Montana, and the Nez Perce Tribe.
- The USFWS would
conduct an extensive and objective public education and
information program to inform the public about grizzly bears and
their management under the ESA.
- The USFWS would
continue to evaluate reported sightings of grizzly bears in the
BE to determine their presence. The USFWS would also coordinate a
monitoring program within the recovery zone to determine the
status of recolonization.
- The national
forests within the recovery zone would continue to manage habitat
to meet or exceed their existing Forest Plan standards for big
game habitat management. ESA Section 7 would apply upon
implementation of this alternative and all federal actions within
the recovery zone would be subject to Section 7 consultation with
the USFWS.
- The USFWS would
coordinate research to further study adequacy of land-use
restrictions to protect suitable grizzly bear habitat within the
Bitterroot recovery zone and within potential linkage zones to
other occupied recovery zones. The USFWS would also evaluate
adjacent wilderness areas for their suitability as additions to
the recovery zone (to include the portion of the Frank
Church-River of No Return Wilderness south of the Salmon River).
- The USFWS, in
cooperation with IDFG and MDFWP would apply the IGBC nuisance
grizzly bear management guidelines (IGBC 1986) to grizzly bears
in conflict with humans or domestic animals.
- Land-use
restrictions could be implemented when necessary if illegal
killing threatens grizzly bear recovery.
Expected actions and effects of Alternative
2.-- See Tables S-2 and S-3 for a
comparison of the expected actions and effects of this
alternative. The tentative recovery goal of this alternative is
approximately 280 grizzly bears (USFWS 1996). Optimistically, it
could take at least 50 years for reproducing populations of bears
from the Cabinet-Yaak Ecosystem (80 miles distance) to reach the
BE. If this occurred, it would conservatively take an additional
50-110+ years to population recovery. Thus, estimated time to
recover grizzly bears in the BE under this alternative is at
least 100-160 years. Since this alternative relies on natural
recolonization to recover grizzly bears in the BE, there would be
no cost associated with reintroduction of bears. Costs for
ongoing monitoring and management activities would be
approximately $140,000 per year. There could be additional costs
associated with proposed research projects.
A brief summary of effects: If population recovery occurred, a recovered grizzly
bear population would kill about 2 cattle (1-3) and 3 sheep (0-6)
and up to 504 ungulates per year. This would not measurably
impact ungulate populations or hunter harvest. Nuisance bear
incidents could be up to 59 (0-118) per year. Ongoing land-use
activities (including timber harvest, minerals extraction, and
public access and recreation) could be altered solely for grizzly
bears if proposed research determines that current habitat
management is not adequate to maintain suitable grizzly bear
habitat, or that linkage zone restrictions are necessary to
promote grizzly bear recolonization. It is estimated that
reductions in timber harvest on affected currently roaded
national forest lands would be between 6.6 and 39.7 million board
feet per year over the next decade. Mineral extraction could be
altered due to grizzly bear concerns in and by themselves.
Changes to hunting seasons could occur due to conflicts. Risk to
human health and safety from a recovered grizzly bear population
would be less than 1 injury per year and less than 1 human
mortality every few decades. Economic analyses indicate that
there is no net economic benefit from this alternative because it
is essentially a continuation of the status quo for the
foreseeable future. Total costs would be $140,000 for
implementation, and the potential net loss of 44-264 jobs from
reduced timber harvest.
Alternative 3. The No Grizzly Bear Alternative:
Summary.-- The
purpose of this alternative is to prevent grizzly bears from
naturally re-establishing in Bitterroot Ecosystem. Changes to the
ESA proposed under this alternative would require intensive
lobbying, changes in public attitudes, and years to implement.
Actions of this magnitude would cost millions of dollars.
Congress would need to pass legislation to remove grizzly bears
in central Idaho and portions of western Montana from the list of
threatened species. The USFWS would stop all funding and
management activity toward bear research, education, and
management in central Idaho. Furthermore, the states of Idaho and
Montana would remove grizzly bears from the protection of state
law within the BE (central Idaho and west-central Montana).
Unregulated killing by the public and extirpation or removal by
agencies would likely prevent any possible grizzly bear recovery
in this area.
Implementation of Alternative 3 would involve:
- Federal
legislation would be passed to remove grizzly bears from the list
of threatened species in the BE.
- State
legislation would be passed to remove grizzly bears from
protection of Idaho and Montana state law in the BE.
- Agencies and
the public would be allowed to kill grizzly bears at any time
without restriction. This would prevent any natural recovery of
bears.
Expected actions and effects of Alternative
3.-- See Tables S-2 and S-3 for a
comparison of the expected actions and effects of this
alternative. The only estimated costs of this alternative are
management costs necessary to develop required legislation to
change existing laws and regulations. Total cost is estimated at
a minimum of $2,000,000 spread over several years. No measurable
benefits have been associated with this alternative. There would
be no other measurable impacts from this alternative.
Alternative 4. Reintroduction of a Threatened Population with Full Protection of the ESA:
Summary.-- The purpose of this alternative is to use reintroduction and extensive habitat protection and enhancement to promote natural recovery of grizzly bears in the BE. Primary grizzly bear management responsibility would reside with the USFWS and include active participation by the states and the Nez Perce Tribe. A ten member Scientific Committee would be appointed by the Secretary of the Interior in cooperation with the National Academy of Sciences to define needs for additional research, develop strategies for reintroduction of bears, and monitor results of the program. Grizzly bears would be reintroduced into the Selway-Bitterroot Wilderness and roadless areas north of the Lochsa River through methods determined by the Scientific Committee. They would be fully listed as threatened with all the protections under the ESA (including Section 7(a)(2)), and all federal actions within the recovery zone would be subject to ESA Section 7 consultation with the USFWS. Management Situation designation would reflect a high priority for recovery on all federal lands within a 21,645 square mile recovery zone.
Grizzly bear populations would take a minimum of 65 years, and likely more than 125 years to recover to a population of 300-500 individuals (bears distributed over 21,645 mi2 of wilderness, non-wilderness, and private land). No logging or road building would be permitted on roadless lands within the recovery zone. The Magruder Road would be reclaimed and converted to a pack trail from Magruder crossing 23 miles west to Sabe Saddle. The Hells Half Acre Mountain Road would be reclaimed over the entire eight mile length. The Lolo Restoration Area (219 square miles) and a Corridor Special Management Area (1,380 square miles) would be designated for road density reduction through reclamation. Road densities on roaded lands within the Restoration Area and the Corridor Special Management Area would be reduced to an average of no more than 0.25 miles per square mile.
Interagency Grizzly Bear Committee nuisance
grizzly bear management guidelines (IGBC 1986) would be applied
to bears killing livestock. The Scientific Committee would review
and modify these guidelines if necessary. If losses occurred on
nearby private lands, bears would be moved. Agency response to
reported livestock losses from grizzly bears must occur rapidly.
Grizzly bears could be killed in defense of life, but not in
defense of property. Use of toxicants lethal to bears on public
lands within the recovery zone and areas used by bears would be
subject to Section 7 consultation and could be prohibited by
existing ADC policy and EPA labeling instructions. Backcountry
users would be required to make food, garbage, and livestock feed
unavailable to grizzly bears. Front country campgrounds would
install bear resistant garbage containers as soon as possible. An
intensive education campaign regarding food storage and garbage
handling would be instituted for all residents and visitors. A
request for elimination of hunting of black bears with dogs and
bait within the wilderness areas designated for reintroduction of
grizzly bears would be made to the State of Idaho. The Scientific
Committee would recommend whether this ban would need to be
extended if conditions warrant. Intensive hunter education
efforts regarding bear identification and recreation in grizzly
bear habitat would be undertaken.
Implementation of Alternative 4 would involve:
- The USFWS would designate the Bitterroot Grizzly Bear Recovery Zone along boundaries described in Figure S-4. The Recovery Zone would include all of the Selway-Bitterroot, Frank Church-River of No Return, Sawtooth, and Gospel Hump Wilderness Areas, surrounding inventoried roadless lands, and other National Forest lands comprising approximately 21,645 square miles. The area is located on portions of the Clearwater, Bitterroot, Lolo, Panhandle, Payette, Boise, Sawtooth,

Challis, and Salmon National Forests.
Specifically, the northern boundary of the recovery zone would be
the northern boundary of the Mallard-Larkins inventoried roadless
area on the Clearwater and Panhandle National Forests and the
northern boundary of the Sheep Mountain inventoried roadless area
on the Lolo National Forest. The western boundary of the recovery
zone would be the western boundary of the Clearwater National
Forest; the westernmost boundaries of the Nez Perce and Payette
National Forests west of U.S. Highway 95 and Idaho Highway 55;
the westernmost boundaries of the Boise National Forest east of
Idaho Highway 55. The southern boundary of the recovery zone
would be the southern boundaries of the Boise, Sawtooth, and
Challis National Forests north of U.S. Highway 20. The eastern
boundary of the recovery zone would be the eastern boundaries of
the Challis and Salmon National Forests west of U.S. Highway 93;
the Bitterroot National Forest west of Lost Trail Pass northwest
to Trapper Peak; the eastern boundary of the Selway-Bitterroot
Wilderness Area to Lolo Peak and to include Lost Horse and
Blodgett Canyons out to the mouth; the Lolo National Forest from
Lolo Peak northwest to Garden Point; from Garden Point northwest
to Rivulet Peak; from Rivulet Peak northwest to Sunrise Point;
from Sunrise Point northwest to Blacktail Mountain.
- The USFWS would establish proactive interagency grizzly bear recovery programs in the BE (similar to those existing in other ecosystems) to conduct monitoring, research, education, and information programs.
- A Scientific
Committee would be established to define needs for additional
research, develop strategies for reintroduction of bears, and
monitor results of the program.
- A recovery goal
of between 300-500 (average of 400) grizzly bears (bears
distributed over 21,645 mi2 of wilderness,
non-wilderness and private land) would be established within the
recovery zone. The Scientific Committee would recommend a refined
recovery goal once grizzly bears are reintroduced and information
is obtained on their use of the habitat.
- The USFWS would
reintroduce a minimum of 25 bears over a period of 5 years into
the Selway- Bitterroot Wilderness and roadless areas north of the
Lochsa River following recommendations of the Scientific
Committee. Subadult grizzly bears of both sexes would be trapped,
each year for 5 years, from areas in Canada (in cooperation with
Canadian authorities) and the United States that presently have
healthy populations of grizzly bears living in habitats that are
similar to those found in the Bitterroot Ecosystem. Three sources
of grizzly bears for the BE have been identified: southeast
British Columbia, the Northern Continental Divide Ecosystem
(NCDE) population in northwest Montana, and the Yellowstone
Ecosystem (YE) population. The specific number of bears that
could be obtained yearly from the potential source populations is
unknown at this time. Bears would be reintroduced at the best
time of year to optimize their survival. Reintroduced bears would
be radio collared and monitored to determine their movements and
how they use their habitat, and to keep the public informed of
general bear locations and recovery efforts.
- Some
undetermined level of mortality is expected among the
transplanted bears. Every effort would be taken to minimize this,
but mortalities are expected to occur. Any transplanted bears
that died or were removed as a result of human action could be
replaced. Such replacements would be in addition to the original
minimum of 25 bears.
- Within the
recovery zone (Figure S-4), the USFS and Bureau of Land
Management (BLM) in cooperation with USFWS would: not approve
logging or road building within roadless areas; use road closures
and road reclamation to reduce road densities to no more than
0.25 miles per square mile within the recovery zone, habitat
restoration areas and habitat linkage corridors; designate
management situations as per the Interagency Grizzly Bear
Guidelines (IGBC 1986); and implement sanitation programs to
assist recovery of grizzly bears.
- USFWS, in cooperation with other federal agencies, the states, the Nez Perce Tribe, and private groups would use federal funding to enhance grizzly bear habitat through acquisitions or easements.
- USFWS, in
cooperation with IDFG and MDFWP would apply the IGBC nuisance
grizzly bear management guidelines (IGBC 1986) to grizzly bears
in conflict with humans or domestic animals.
- IDFG in
cooperation with the USFWS could be requested to eliminate the
use of dogs and bait for black bear hunting within the area
designated for release of reintroduced bears.
Expected actions and effects of Alternative
4.-- See Tables S-2 and S-3 for a
comparison of expected actions and effects of this alternative.
The tentative recovery goal of this alternative is approximately
400 (300-500) grizzly bears. Under this alternative, grizzly bear
recovery in the BE could take a minimum of 65-70 years (4% growth
rate), and given potential conflicts, would likely take more than
125 years (2% growth rate). Total annual implementation cost
during the 5-year reintroduction period would be approximately
$393,632/year, and total 5-year implementation cost would be
approximately $1,968,160. Annual costs for monitoring and citizen
management would be approximately $168,000 for each year beyond
the 5-year reintroduction period.
A brief summary of effects: A recovered grizzly bear population would kill about 17
cattle (12-22) and 178 sheep (0-355) and up to 720 ungulates per
year. This would not measurably impact ungulate populations or
hunter harvest. Nuisance bear incidents could be up to 84 (0-168)
per year. Because grizzly bears would be listed as a fully
protected threatened species, all federal actions within the
recovery zone would be subject to ESA Section 7 consultation with
the USFWS. Road building and timber harvest would not be allowed
on federal lands within the recovery zone that are presently
roadless. Grizzly bear habitat management would also likely
restrict to some degree timber harvests on currently roaded areas
within the recovery zone It is estimated that reductions in
timber harvest on national forest lands would be between 43 and
194 million board feet per year over the next decade. Minerals
extraction activities could be altered due to grizzly bear
concerns in and by themselves. Public access could be negatively
impacted due to proposed road closures, however, backcountry
recreation opportunities could be enhanced by the road closures.
Changes to black bear hunting seasons (elimination of baiting and
hound hunting) could occur. Risk to human health and safety from
a recovered grizzly bear population would be less than 1 injury
per year and less than 1 human mortality every few decades.
Economic analyses indicate grizzly bear recovery in the BE would
lead to total net economic benefits of 40.4-60.6 million dollars
per year. Annual cost associated with grizzly bear recovery would
be: $288,700 for the value of hunting losses; $6,780-$45,090 for
the value of livestock losses; and $168,000 annual cost for
monitoring and management after the reintroduction phase
($393,632 annual implementation cost for the first 5-year
reintroduction phase). Thus, the total cost would be
$463,480-$501,790 per year (costs during the initial 5-year
reintroduction phase would be $689,112-$727,422 per year). In
addition, there would potentially be a net job loss of 138-1,136
jobs from reductions in timber harvest due to implementation of
this alternative.
Literature Cited
Interagency Grizzly Bear Committee. 1986. Interagency grizzly bear guidelines. U.S. For. Serv., Washington, D.C. 100 pp.
U.S. Fish and Wildlife Service. 1993. Grizzly bear recovery plan. U.S. Fish and Wildlife Service, Missoula, Montana. 181 pp.
__________. 1995. Summary of public comments on the scoping of issues and alternatives for grizzly
bear recovery in the Bitterroot Ecosystem. U. S. Fish and Wildl. Serv., Missoula, Mont.
__________. 1996. Bitterroot Ecosystem recovery plan chapter - supplement to the grizzly bear recovery plan. U.S. Fish and Wildlife Service, Missoula, Montana. 27 pp.
__________. 1997. Grizzly bear recovery in the Bitterroot Ecosystem, Draft Environmental Impact Statement. U.S. Fish and Wildlife Service, Missoula, Montana. 464 pp.
Table S-2. Alternatives and expected actions associated with them.
|
What is the risk to human safety? |
Land-uses altered solely for grizzly bears? |
Cost estimate for implementation?
|
How are linkage zones addressed? |
Are habitat quality/size sufficient for recovery? |
How would grizzly bears and their habitat be managed? |
Where would grizzly bears be obtained and recovered? |
Legislation needed to implement? |
Alternatives |
||||||||
Alternative 1 - Reintroduction of a Nonessential Experimental Population (Proposed Action) |
Minimal before recovery. At recovered grizzly popn. levels, less than 1 injury per year and less than 1 human mortality every few decades. |
None expected. To be determined by the Citizen Management Committee (CMC), if need for land-use restrictions arises. |
Reintroduction phase (first 5 years) = $1,968,160. Annual monitoring and management thereafter = $168,000 per year. |
No linkage zones designated. |
Yes |
IDFG/MDFWP in consultation with USFWS and the Nez Perce Tribe would manage and implement rules, policies, plans of CMC. Current land management agencies would continue to manage habitat. |
Bitterroot Grizzly Bear Recovery Area (Figure S-2) = 5,785 square miles. Bears likely moved from existing popns. in U.S. and Canada and released into Selway-Bitterroot Wilderness. |
Publish special rule in Federal Register to establish nonessential experimental population. |
Alternative 2 - The No Action Alternative - Natural Recovery |
No risk unless bears move from other ecosystems to occupy the BE. Minimal risk until recovery, then same as Alt. 1. |
Few expected. To be determined by USFWS, if illegal killing, research, or ESA Section 7 consultation warrants. |
Annual cost of monitoring and management for natural recovery = $140,000 per year. |
No linkage zones designated. |
Yes |
Federal (USFWS) would have authority for grizzly bear recovery. Current land management agencies would continue to manage habitat. |
Bitterroot Grizzly Bear Recovery Zone (Figure S-3) = 5,500 square miles. No bears would be moved or released. |
None |
Alternative 3 - No Grizzly Bear |
Nonexistent. |
None for grizzly bears. |
Minimum total cost to develop legislation = $2,000,000. |
No linkage zones designated. |
N/A |
No agency management for recovery of grizzly bears. |
Nowhere |
Modify state (MT & ID) and federal laws. Change ESA. |
Alternative 4 - Reintroduction of a Threatened Population with Full Protection of the ESA |
Minimal before recovery. At recovered grizzly bear population levels, less than 1 injury per year and less than 1 human mortality every few decades. |
No timber harvest or road constructn. in roadless areas of recovery zone. Road densities reduced to <0.25 mi/sq.mi. in recov. zone. Other restrictions per Science Committee recommendation, and ESA Section 7 consultation. |
Reintroduction phase (first 5 years) = $1,968,160. Annual monitoring and management thereafter = $168,000 per year. |
Linkage zone designated between Bitterroot Ecosystem and Cabinet- Yaak Ecosystem. |
Yes |
Federal (USFWS) with active participation by IDFG, MDFWP and the Nez Perce Tribe, and in consultation with Scientific Committee. Current land management agencies would continue to manage habitat. |
Bitterroot Grizzly Bear Recovery Zone (Figure S-4) = 21,645 square miles. Bears likely moved from existing populations in U.S. and Canada and released into Selway-Bitterroot Wilderness or roadless areas north of Lochsa River. |
None |
Table S-3. Expected impacts of a recovered grizzly bear population by alternative.
Alternatives |
|
|
||
Impact |
||||
Impact on human health and safety |
Minimal risk of injury before recovery (50-110+ years). At recovery (280 bears), less than 1 injury per year, and less than 1 mortality every few decades. |
If bears recolonize, risk minimal until recovery (150+ years), then same as Alternative 1. |
No impact. |
Same as Alternative 1, except time to recovery is minimum 65-70 years, and likely more than 125 years. |
Impact on source grizzly bear populations |
Removal of bears from source populations would adhere to all management guides to protect source popn. health. Thus no impact to source popn. health. |
Bears would not be relocated under Alternative 2. No impact. |
Bears would not be relocated under Alternative 3. No impact. |
Same as Alternative 1. Thus no impact to source population health. |
Impact on land-use activities to include: timber harvest, domestic livestock, and minerals extraction |
No expected impacts to timber harvest or mining. At recovered population level (280 bears), 4-7 cattle and 0-44 sheep lost per year. Nuisance incidents = 0-118 per year. |
Sectn. 7 consultation could reduce timber harvest and mining. At population of 280 bears, 1-3 cattle & 0-6 sheep lost per year. Nuisance incidents = 0-118 per year. |
No impact. |
ESA Section 7 consultation required. No road building or timber harvest on USFS roadless areas. Timber harvest & mining reduced. At 400 bears, 12-22 cattle & 0-355 sheep lost per year. Nuisances = 0-168 per year. |
Impact on wildlife populations |
Minimal impacts to wildlife. At recovered population levels, 280 bears would kill approximately 504 ungulates per year. |
If recolonization occurs, minimal impact until recovery, then same as Alternative 1. |
No impact. |
Minimal impacts to wildlife. At recovered population levels, 400 bears would kill approximately 720 ungulates per year. |
Impact on public access and recreational use |
No road/trail closures expected. Changes to hunting seasons could occur due to possible conflicts. |
Possible road/trail closures due to Section 7. Hunting season changes could occur also. |
No impact. |
Closure and reclamation of 3500 miles of roads. Other closures likely due to Sectn. 7. Hunting season changes, especially black bear. |
Social impacts |
Hardship due to nuisance incidents and sanitation reqs. Mixed impact due to knowledge of grizzly presence. Positive impact to Native American culture by recovering grizzlies. |
If recolonization occurs, then same as Alternative 1. Also negative impact of jobs lost to local communities. |
No impact to local communities. Negative impact to Native Americans. |
Same as Alternative 1. Additional negative impact of lost jobs to local communities. |
Economic impacts |
Livestock loss: $2,260-$8,003/yr. Grizzly existence value: $40.5-$60.6 million/yr. Reintroduction cost: $393,632/year for first 5 years. Management cost: $168,000/year after first 5 years. |
Possible loss of 44-264 timber jobs. No existence value. Management cost until recovery = $140,000 per year. |
Total cost of $2 million over several years to change federal and state laws. |
Hunting loss: $288,700/yr. Livestock loss: $6,780-$45,090/year. Jobs lost: 138-1,136. Existence value: $40.5-$60.6 million/year. Reintrod. cost: $393,632/yr. for first 5 years. Managemt. cost: $168,000/year after first 5 years. |
How You Can Become Involved:
Written Comments on the Draft EIS
In order to be considered in development of the final plan,
comments on the draft EIS must be received by September 30, 1997.
For your convenience, a Response Form is provided with this
summary. Mail your comments to: Bitterroot Grizzly Bear EIS, P.O.
Box 5127, Missoula, Montana 59806.
Public Hearings
Six public hearings have been scheduled for officials to
gather testimony regarding the draft EIS for Grizzly Bear
Recovery in the Bitterroot Ecosystem. The public will have the
opportunity to provide oral and/or written testimony at these
hearings. The schedule follows:
Wednesday August 27, 1997 Salmon, Idaho
Wednesday August 27, 1997 Hamilton, Montana
Thursday August 28, 1997 Lewiston, Idaho
Thursday August 28, 1997 Missoula, Montana
Friday August 29, 1997 Boise, Idaho
Friday August 29, 1997 Helena, Montana
Draft EIS Response Form
Mail comments to: Bitterroot Grizzly Bear EIS, P.O. Box 5127, Missoula, Montana 59806.
Comments will be accepted from July 1, 1997,
through September 30, 1997.
Alternative 1. Reintroduction of a Nonessential Experimental Population. |
Alternative 2. The No Action Alternative - Natural Recovery. |
Alternative 3. The No Grizzly Bear Alternative. |