Endangered and Threatened Wildlife and Plants; Designation of Critical Habitat for the Sierra Nevada Bighorn Sheep (Ovis canadensis sierrae) and Taxonomic Revision, 45534-45604 [E8-16813]
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Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[FWS–R8–ES–2008–0014; 92210–1117–
0000–B4]
RIN 1018–AV05
Endangered and Threatened Wildlife
and Plants; Designation of Critical
Habitat for the Sierra Nevada Bighorn
Sheep (Ovis canadensis sierrae) and
Taxonomic Revision
Fish and Wildlife Service,
Interior.
ACTION: Final rule.
AGENCY:
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SUMMARY: We, the U.S. Fish and
Wildlife Service (Service), are
designating critical habitat for the Sierra
Nevada bighorn sheep (Ovis canadensis
sierrae) under the Endangered Species
Act of 1973, as amended (Act). In total,
approximately 417,577 acres (ac)
(168,992 hectares (ha)) fall within the
boundaries of the critical habitat
designation. The critical habitat is
located in Tuolumne, Mono, Fresno,
Inyo, and Tulare Counties, California.
We also are finalizing the revision of
taxonomy of the listed entity from a
distinct population segment (DPS) of
California bighorn sheep (Ovis
canadensis californiana) to subspecies,
Ovis canadensis sierrae, based on recent
published information.
DATES: This rule becomes effective on
September 4, 2008.
ADDRESSES: The final rule, economic
analysis, and maps are available at
https://www.regulations.gov and at
https://www.fws.gov/nevada. Supporting
documentation we used in the
preparation of this final rule is available
for public inspection, by appointment,
during normal business hours, at the
Nevada Fish and Wildlife Office, 1340
Financial Boulevard, Suite 234, Reno,
NV 89523; telephone 775–861–6300;
facsimile 775–861–6301.
FOR FURTHER INFORMATION CONTACT:
Robert D. Williams, U.S. Fish and
Wildlife Service, Nevada Fish and
Wildlife Office (see ADDRESSES section).
If you use a telecommunications device
for the deaf (TDD), call the Federal
Information Relay Service (FIRS) at
800–877–8339.
SUPPLEMENTARY INFORMATION:
Background
It is our intent to discuss only those
topics directly relevant to the
designation of critical habitat in this
rule. For more information on the Sierra
Nevada bighorn sheep, refer to the final
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listing rule published in the Federal
Register on January 3, 2000 (65 FR 20)
and the proposed critical habitat rule
published in the Federal Register on
July 25, 2007 (72 FR 40955).
The bighorn sheep (Ovis canadensis)
is a large mammal in the family Bovidae
described by Shaw in 1804 (Shackleton
1985, p. 1). Cowan (1940, pp. 519–569)
recognized several subspecies based on
geography and skull measurements.
Recent genetic (Ramey 1993, pp. 62–86;
1995, p. 432–434; Boyce et al. 1996, pp.
423–426, 429; Gutierrez-Espeleta et al.
1998, pp. 7–9, 11) and morphological
data (Wehausen and Ramey 1993, pp. 4–
8; 2000, pp. 148–153), and review and
reanalysis of Cowan’s data (Ramey 1993,
p. 83), do not support Cowan’s original
subspecies differentiations.
Ramey (1993, pp. 71–72; 1995, p. 432)
found, based on mitochondrial DNA
(mtDNA), bighorn sheep from the Sierra
Nevada to be more allied with sheep
occupying the adjacent desert area than
those to the north. Ramey (1993, pp. 67–
68; 1995, pp. 433, 435) also found Sierra
Nevada bighorn sheep to be a distinctive
group in the desert region extending
east to Utah and New Mexico and south
to northern Mexico. Ramey (1993 p. 54)
used mtDNA as a genetic marker to help
understand the evolutionary history of
North American mountain sheep. From
the 116 individuals included in the
surveys, 16 different mtDNA haplotypes
were identified in North America and
four in Asia (Ramey 1993, p. 62). Two
major mtDNA lineages of mountain
sheep were indicated in North America
(Ramey 1993, p. 63). Within the
northern Alaska and western North
America clade, three mtDNA lineages
were identified (Ramey 1993, p. 72).
One lineage included bighorn sheep in
the desert ranges of the southwestern
United States and Mexico and the Sierra
Nevada (Ramey 1993, p. 72), where the
Sierra Nevada population was found to
be more closely related to the desertdwelling sheep than those from the
Cascade Ranges or Rocky Mountains
(Ramey 1993, p. 72). Within the desertdwelling sheep populations, Sierra
Nevada bighorn sheep differed (Ramey
1993, p. 73). Ramey (1995 p. 429) used
mtDNA as a genetic marker to help
understand the evolutionary history of
North American mountain sheep in the
southwest United States. Ten mtDNA
haplotypes were identified in the
southwest, with a common one being
found in most populations (Ramey
1995, pp. 431–432). The distribution of
mtDNA variants in the southwest did
not support the recognition of O. c.
cremnobates, O. c. mexicana, and O. c.
nelsoni as distinct and separate
subspecies, but the mtDNA analysis did
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show a unique fixed haplotype for O. c.
californiana from the Sierra Nevada
(Ramey 1995, p. 433). Based on this
finding, bighorn sheep from the Sierra
Nevada could be distinguished from
populations of other subspecies of
bighorn sheep (Ramey 1995, p. 433).
Results indicated that significant
differences in mtDNA haplotype
frequencies can be found among
populations that are adjacent to one
another and separated by short
distances (Ramey 1995, p. 435). A few
rare haplotypes were limited in
distribution and found in only single
populations. One of these populations
included the Sierra Nevada (Ramey
1995, p. 433).
Wehausen and Ramey (2000, pp. 148–
153) used univariate and multivariate
statistical methods to examine the
geographic variation in horn and skull
characters of 694 bighorn sheep (Ovis
canadensis) from the Great Basin to
British Columbia and Alberta. California
bighorn sheep (O. c. californiana) from
Washington and British Columbia were
not distinguishable from Rocky
Mountain bighorn sheep (O. c.
canadensis); however, they did differ
from Sierra Nevada bighorn sheep
populations considered to be O. c.
californiana. Extirpated populations
from northeastern California, Oregon,
and southwestern Idaho shared a hornrelated character with Nelson bighorn
sheep (O. c. nelsoni) from the Great
Basin; this shared character was
different from Rocky Mountain bighorn
sheep. Individuals from the Sierra
Nevada were distinguishable from
bighorn sheep from the Great Basin.
These results agree with geographic
patterns identified with the mtDNA
studies of Ramey (1993, 1995)
(Wehausen and Ramey 2000, p. 156).
Wehausen and Ramey (2000, pp. 153–
157) synonymized the extinct Audubon
subspecies, O. c. auduboni, from east of
the Rocky Mountains in eastern
Montana and Wyoming, North Dakota,
South Dakota, and western Nebraska
with O. c. canadensis. They also
assigned extinct and extant native
populations of O. c. californiana from
Washington and British Columbia to O.
c. canadensis and the extinct native
populations of O. c. californiana from
northeastern California, northern
Nevada, southwestern Idaho, and
Oregon to O. c. nelsoni of the Great
Basin desert form. Based on genetic and
morphometric data, Wehausen and
Ramey (2000, p. 156) concluded that
bighorn sheep in the Sierra Nevada
should be recognized as a separate
subspecies of O. canadensis, but they
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did not recommend a change in
nomenclature at that time.
In a recent investigation of the
taxonomy of Sierra Nevada bighorn
sheep, Wehausen et al. (2005)
reexamined the history of bighorn sheep
nomenclature. Grinnell (1912, p. 144)
recognized bighorn sheep from the
Sierra Nevada of California as a distinct
subspecies, Ovis cervina (= canadensis)
sierrae, designating a 5-year-old ram as
the type specimen. Cowan (1940, p. 556)
did not recognize the subspecies O. c.
sierrae as valid, but included animals
from the Sierra Nevada as O. c.
californiana. Wehausen and Ramey
(2000, pp. 153–157) reassigned
specimens from north of the central
Sierra Nevada to O. c. nelsoni and O. c.
canadensis. They kept the name O. c.
californiana for bighorn sheep in central
and southern Sierra Nevada (Wehausen
and Ramey 2000, p. 156), raising the
question of the correct subspecific name
for animals inhabiting this area. Based
on this investigation of the taxonomy of
Sierra Nevada bighorn sheep and by the
Principle of Typification (International
Commission on Zoological
Nomenclature 1999), cited in Wehausen
et al. (2005, p. 217), Wehausen et al.
(2005 p. 217) concluded, based on
Grinnell’s original type specimen, that
the correct nomenclature for native
sheep in the central and southern Sierra
Nevada of California is Ovis canadensis
sierrae (Grinnell). Therefore, with the
publication of this final rule designating
critical habitat for the Sierra Nevada
bighorn sheep, we formally revise its
taxonomy from DPS of California
bighorn sheep (Ovis canadensis
californiana) to subspecies Ovis
canadensis sierrae.
Sierra Nevada bighorn sheep inhabit
portions of the Sierra Nevada located
along the eastern boundary of California
in Tuolumne, Mono, Fresno, Inyo, and
Tulare Counties. Habitat occurs from the
eastern base of the range as low as 4,790
feet (ft) (1,460 meters (m)) to peaks
above 14,100 ft (4,300 m) (Wehausen
1980, pp. 3, 82).
Based on recent modeling efforts,
discussed further in the Criteria Used
To Identify Critical Habitat section,
Sierra Nevada bighorn sheep habitat, as
well as areas necessary to provide
connectivity between winter and
summer ranges, occur as low as 4,000 ft
(1,219 m) in the southern portion of its
range (Johnson et al. 2005). Sierra
Nevada bighorn sheep inhabit open
areas where the land is rocky, sparsely
vegetated, and characterized by steep
slopes and canyons (Wehausen 1980, p.
81; Sierra Nevada Bighorn Sheep
Interagency Advisory Group 1997, p. 5).
Wehausen (1980, pp. 18–25) provides a
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detailed description of Sierra Nevada
bighorn sheep habitat throughout its
range. They prefer open ground to better
detect predators and allow enough time
to reach steep, rocky terrain (escape
habitat) (Wehausen 1980, p. 81). Forests
and thick brush are usually avoided if
possible (65 FR 21; January 3, 2000).
Most of the sheep live at higher
elevations (10,000–14,000 ft (3,050–
4,270 m)) in subalpine and alpine areas
during the summer (65 FR 21; January
3, 2000). During winter, these sheep
occupy high-elevation, windswept
ridges and tend to prefer south-facing
slopes where snow melts more readily
(Jones 1950, pp. 44–45; McCullough and
Schneegas 1966, p. 71; Wehausen 1980,
pp. 86–87) or migrate to lower
elevations (4,800 ft (1,460 m)) in
sagebrush-steppe areas to avoid deep
snow and to find forage.
Sierra Nevada bighorn sheep are
gregarious, with group size and
composition depending on gender and
season. Spatial segregation by gender
occurs outside of the mating season.
Bighorn sheep ewes generally remain
with the same band in which they were
born (Cowan and Geist 1971, pp. 80–
81). Males older than 2 years of age
remain apart from females and younger
males for most of the year (Jones 1950,
p. 50; Cowan and Geist 1971, p. 65;
Wehausen 1980, p. 109). During the late
fall and winter, the groups come
together and concentrate in suitable
winter habitat.
Breeding takes place in late fall,
generally November and December
(Jones 1950, pp. 63–64; Cowan and
Geist 1971, p. 64; Wishart 1978, p. 165).
Lambing occurs between late April and
early July (Wehausen 1996, p. 475) on
safe, precipitous, rocky slopes
(Wehausen 1980, p. 95); most lambs in
the Sierra Nevada are born in May and
June (Wehausen 1980, p. 94; 1996, p.
475). Ewes and lambs often occupy
steep terrain that provides a diversity of
exposures and slopes for escape cover
(65 FR 21; January 3, 2000). The lifespan
for both Sierra Nevada bighorn sheep
males and females has been observed as
8 to 12 years (Wehausen 1980, p. 76;
Stephenson 2008, p. 1).
Bighorn sheep are primarily diurnal
(Jones 1950, pp. 54–57). They are
primarily grazers; however, they may
browse woody vegetation at times.
Plants consumed include various
grasses, browse, and forbs, depending
on season and location (Wehausen 1980,
pp. 80–93). Naturally occurring and
mineral licks provide necessary
minerals for bone and muscle growth.
While distribution of bighorn sheep is
naturally fragmented on the landscape,
the maintenance of migration corridors
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(space) is important to allow genetic
exchange between Sierra Nevada
bighorn sheep herds. The population
ecology of bighorn sheep has been
described as a metapopulation with
geographically distinct herds interacting
in a network (Schwartz et al. 1986, p.
184; Bleich et al. 1990, pp. 384–388).
The movements of rams between herds
can counteract the effects of inbreeding
that can develop with small, isolated
populations (Schwartz et al. 1986, pp.
182–185).
Previous Federal Actions
On April 20, 1999, we published an
emergency rule listing the Sierra Nevada
DPS of the California bighorn sheep as
endangered (64 FR 19300), providing
emergency protection to the DPS until
such time that we could complete the
normal listing process. We also
published a proposed rule to list the
DPS as endangered on the same date (64
FR 19333). On January 3, 2000, we
published a final rule listing the Sierra
Nevada bighorn sheep as endangered
(65 FR 20). The emergency rule stated
that the designation of critical habitat
was not determinable due to lack of
information sufficient to perform the
required analysis of impacts of the
designation. In the final listing rule, we
stated our revised determination that
there is sufficient information to
perform the required impact analysis
and that the designation of critical
habitat is prudent.
During the process of designating
critical habitat for the Sierra Nevada
bighorn sheep, we noticed that the final
listing rule published in 2000 (65 FR 20)
inadvertently listed this entity as a DPS
rather than as a subspecies. While the
listing rule addressed the DPS question,
we failed to include the DPS language
in the table found in the regulatory
section of the rule. However, as stated
above, based on the work of Wehausen
and Ramey (2000, p. 156) and
Wehausen et al. (2005, p. 217), the
Sierra Nevada bighorn sheep is
recognized as a subspecies, and the
correct nomenclature is Ovis canadensis
sierrae. Therefore, we are formally
providing a taxonomic revision herein
to amend the final listing rule to
subspecies Ovis canadensis sierrae.
On July 30, 2003, we made available
the Service’s Draft Recovery Plan for the
Sierra Nevada Bighorn Sheep (Ovis
canadensis californiana) (68 FR 44808).
On October 9, 2003, we reopened the
comment period for the draft Recovery
Plan (68 FR 58355). On February 13,
2008, we published a Notice of
Availability for the final recovery plan
(73 FR 8345).
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On December 8, 2005, the Center for
Biological Diversity filed a complaint
based on the Service’s failure to
designate critical habitat for this
subspecies within the time mandated
under the Act (Center for Biological
Diversity v. U.S. Fish and Wildlife
Service, et al. Case No. 2:05–CB–02492–
DFL–KJM). On June 6, 2006, the Service
entered into a settlement agreement
with the Center for Biological Diversity
to submit a proposed critical habitat
designation for this subspecies for
publication in the Federal Register by
July 17, 2007, and to submit a final
determination on the proposed critical
habitat designation for publication by
July 17, 2008.
Our proposed critical habitat rule and
taxonomic revision for the Sierra
Nevada bighorn sheep was published in
the Federal Register on July 25, 2007
(72 FR 40956). A notice of availability
of the draft economic analysis (DEA) of
the proposed critical habitat designation
was published in the Federal Register
on February 5, 2008 (73 FR 6684). This
final rule satisfies the June 6, 2006,
settlement agreement with respect to
Sierra Nevada bighorn sheep.
For more information on previous
Federal actions concerning Sierra
Nevada bighorn sheep, refer to the final
listing rule published in the Federal
Register on January 3, 2000 (65 FR 20).
Summary of Comments and
Recommendations
We requested written comments from
the public on the proposed designation
of critical habitat for the Sierra Nevada
bighorn sheep published on July 25,
2007 (72 FR 40956). The 60-day
comment period for the proposed rule
closed on September 24, 2007. A request
for a comment period extension was
received from a private organization on
August 20, 2007, and on October 9,
2007, the comment period was reopened
until November 23, 2007 (72 FR 57276).
A 30-day comment period was opened
on the DEA and the proposed rule on
February 5, 2008, and closed on March
6, 2008 (73 FR 6684). Comments and
new information received in response to
the proposed rule and the DEA were
incorporated in the final rule as
appropriate and summarized below.
During the comment periods for the
proposed rule, we received a total of
28,181 (28,153 in support, 12 opposed,
and 16 neutral) comments from Federal,
State, and local governments, nongovernmental organizations and private
individuals. We received two requests
for public hearings. The Inyo County
Board of Supervisors made a request for
a public hearing on August 7, 2007, as
did two private individuals on August
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29, 2007. A public hearing was held in
Bishop, California, on October 25, 2007
(72 FR 57276). We received 12 oral
testimonies from 12 individuals. Of
these commenters, three who provided
oral comments also submitted
duplicative written comments. A
request was made for a public workshop
by the Mono County Board of
Supervisors on September 5, 2007. We
held two public meetings in Bridgeport
and Bishop, California, on October 24
and 25, 2007, respectively (72 FR
57276).
Peer Review
In accordance with our policy
published July 1, 1994 (59 FR 34270),
we solicited expert opinions from three
knowledgeable individuals with
scientific expertise that included
familiarity with the species and
conservation biology principles. We
received responses from two peer
reviewers. In general, the peer reviewers
concurred with our methods and
conclusions and provided suggestions to
improve the final critical habitat rule.
We reviewed all comments received
from the peer reviewers and the public
for substantive issues and new
information regarding critical habitat for
the Sierra Nevada bighorn sheep,
addressed them in the following
summary, and incorporated them into
the final rule as appropriate.
Peer Reviewer Comments
(1) Comment: Both peer reviewers
raised concern that the proposed
designation did not adequately protect
Sierra Nevada bighorn sheep from the
possible introduction of disease from
domestic sheep and goats. One
suggested that the ‘‘absence of risk of
disease transmission’’ should be
explicitly included as a primary
constituent element (PCE) as pneumonia
caused by contact with domestic sheep
or goats can be an overriding factor
affecting habitat suitability.
Our Response: Conservation of the
Sierra Nevada bighorn sheep depends
on addressing both habitat and nonhabitat related threats. In terms of the
consultation process under section
7(a)(2) of the Act, the Service is required
to analyze both the threats to the
individuals within a population and the
threats to the PCEs of its designated
critical habitat. Under the Special
Management Considerations or
Protection section, we have indicated
that management of domestic livestock
grazing practices that result in
overgrazing or forage competition
between these domestic species and
Sierra Nevada bighorn sheep can be a
threat. The concern for overgrazing or
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competition is a habitat-related threat
associated with the PCEs (i.e., PCE 2).
The potential for contact and the
possible transmission of disease to
bighorn sheep exists when domestic
sheep or goats are present in critical
habitat. Management of the threat of
disease transmission between domestic
sheep and goats and Sierra Nevada
bighorn sheep is needed to conserve this
species; however, this threat is not
strictly a habitat-related threat. The
potential effects of disease transmission
will be addressed through section 7
consultation with Federal agencies
under the jeopardy standard and
through the section 9 prohibitions of the
Act to the extent applicable. There
would be no benefit gained from a
critical habitat designation with respect
to the effects of disease on individual
Sierra Nevada bighorn sheep because
the regulatory effects of critical habitat
designations apply to adverse
modification or destruction of habitat,
not to effects that result in the mortality
of individual Sierra Nevada bighorn
sheep. Because the disease threat faced
by the species is not habitat-based, there
would be no practical benefit to
including it as a PCE.
(2) Comment: One peer reviewer
suggested that buffer zones be
established around designated critical
habitat for management of domestic
sheep and goats because activities that
could pose a risk of disease
transmission do not need to occur
directly within critical habitat to affect
that habitat.
Our Response: The units designated
as critical habitat for the Sierra Nevada
bighorn sheep contain the features
essential for the conservation of this
subspecies. It is not our practice to
establish buffers around an area
designated as critical habitat. As
indicated under the Special
Management Considerations or
Protection section, domestic sheep and
goat grazing may require management
modifications to protect Sierra Nevada
bighorn sheep in critical habitat in
certain units. Any buffer distance
recommended or suggested in a
Federally proposed action involving
domestic sheep or goat grazing adjacent
to a designated critical habitat unit to
reduce the potential threat of disease
transmission to Sierra Nevada bighorn
sheep would be taken into consideration
during the jeopardy analysis of the
consultation process under section 7 of
the Act.
(3) Comment: One peer reviewer
raised concern for an elevated risk of
disease transmission with domestic
sheep grazing on U.S. Forest Service
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(USFS) lands as Sierra Nevada bighorn
sheep wander between units.
Our Response: We are aware of the
potential risk of disease transmission
due to contact between domestic sheep
(and goats) and Sierra Nevada bighorn
sheep. If a disease outbreak were to
occur in a Sierra Nevada bighorn sheep
population, it could be passed to other
populations (units) because of, most
likely, ram forays. This risk will
increase if Sierra Nevada bighorn sheep
numbers increase as expected due to
continuing recovery actions. While we
believe that this is an issue of
management concern, we do not believe
that this critical habitat designation
necessarily affects the issue in any
significant way. Please also see our
response to comment (1).
(4) Comment: Both peer reviewers
raised concern that the proposed critical
habitat designation did not provide
biologically based corridors or linkage
zones for movements among Sierra
Nevada bighorn sheep subpopulations.
They were unclear how genetic
exchange or colonization would be
allowed with unconnected units of
critical habitat.
Our Response: Connectivity, within a
critical habitat unit, is a PCE for the
Sierra Nevada bighorn sheep (i.e., PCE
1). The current critical habitat
configuration provides for long-term
connectivity between groups within a
particular unit. We recognize the
importance of migration between
critical habitat units, as discussed under
Metapopulaton Structure in the Space
for Individual and Population Growth
and for Normal Behavior section.
However, due to the current isolation of
occupied herd units and extremely
limited knowledge of various migration
paths that Sierra Nevada bighorn sheep,
especially rams, may have taken
historically between units, we did not
develop criteria that would capture
migration corridors between units.
(5) Comment: One peer reviewer was
concerned about the fine-scale mapping
resulting in ‘‘finger-like’’ habitats for
Units 1, 2, 3, 4, and 9. The concern was
related to possible difficulties in
managing such areas. The reviewer
suggested the boundaries be redrawn to
reduce sinuosity, possibly along
watershed and or drainage boundaries.
Our Response: The critical habitat
units have been developed to be
consistent with the herd units that the
Sierra Nevada bighorn recovery plan
identifies as essential for recovery of the
subspecies. Those herd units were
originally developed using expert
opinion and information on current and
historical bighorn sheep locations in the
Sierra Nevada. Those units were later
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refined using a habitat selection model
developed by University of California
Davis and the California Department of
Fish and Game (CDFG) (Johnson et al.
2005). Based on our analysis of the
biological needs of the subspecies, we
believe that the herd units developed for
the recovery plan capture those areas
that contain the physical and biological
features arranged in the appropriate
quantity and spatial arrangement for the
conservation of the subspecies.
It is important to remember that these
critical habitat units are not being
established as Sierra Nevada bighorn
sheep preserves or management zones.
These are regulatory designations of
areas that contain the features essential
to the conservation of the subspecies.
Critical habitat would serve its
regulatory role when analyzing a
particular Federal action in the
consultation process under section
7(a)(2) of the Act to determine if that
action would adversely modify or
destroy critical habitat by impacting the
essential features within that unit to
such a degree that the unit no longer
serves its function for conservation.
It is possible that a Federal action
immediately adjacent to these units
(e.g., between ‘‘fingers’’) could
indirectly adversely modify critical
habitat within the units. In such a
situation, the action would be analyzed
through the consultation process under
section 7(a)(2) of the Act against the
adverse modification standard.
However, because our analysis has not
identified essential features in these
locations, unit boundary modification
and designation of critical habitat
therein would not be appropriate.
(6) Comment: One peer reviewer
commented that the indicated 9 to 11
year lifespan for bighorn sheep seemed
short.
Our Response: We have modified the
Background section of the final rule to
more accurately reflect the observed
lifespan for male and female bighorn
sheep in the Sierra Nevada.
Comments From State Agencies
(7) Comment: California Department
of Fish and Game (CDFG) suggested a
PCE that identifies a ‘‘disease-free zone’’
because of the risk to Sierra Nevada
bighorn sheep in proximity to domestic
sheep.
Our Response: Please see our
response to Comment 1.
(8) Comment: CDFG recommended
establishment of a buffer that excludes
domestic sheep to ensure the integrity of
the critical habitat for Sierra Nevada
bighorn sheep and provide additional
protections.
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Our Response: Please see our
response to Comment 2.
(9) Comment: CDFG recommended
more emphasis be placed on the use of
fire to maintain critical habitat because
fire is an integral part of the landscape.
Our Response: The Special
Management Considerations or
Protection section identifies activities of
Federal agencies or those with a federal
nexus that may impact Sierra Nevada
bighorn sheep and their habitat. The
section is not meant to promote or
discourage any particular activity. We
indicated that it may be necessary in
some of the critical habitat units to
reduce forest cover to make habitat more
suitable for Sierra Nevada bighorn
sheep. Prescribed fire can be used as a
tool to do this. Johnson et al. (2005, p.
34) indicate Sierra Nevada bighorn
sheep could gain additional habitat with
a reduction in forest cover. In addition,
the final recovery plan (Appendix H,
Genetic Management of Sierra Nevada
Bighorn Sheep) provides a specific
recommendation to use fire in addition
to other methods to enhance habitat
within herd units (Service 2007, p. 174).
This would improve unit carrying
capacity, as well as connectivity with
adjacent herd units, providing better
opportunities for genetic exchange
between herds.
(10) Comment: California Department
of Food & Agriculture (CDFA)
commented that there is ‘‘still
incomplete agreement in the scientific
community’’ about disease transmission
from domestic sheep to bighorn sheep,
in general, such as how often it occurs
and its role in disease epizootics in
bighorn sheep. The CDFA agrees that a
reasonable approach is to keep the two
species separated. How such separation
occurs and what measures are used to
prevent possible contact are important
to both the survival of Sierra Nevada
bighorn sheep and the domestic sheep
industry in Inyo and Mono Counties,
California. The CDFA commented that
further scientific findings will improve
understanding of the true nature of
respiratory disease in bighorn sheep, in
general, and that interested parties
should cooperate on common interests.
They also noted that at the 111th
Annual Meeting of the United States
Animal Health Association (USAHA) in
October 2007, a joint resolution passed
recommending additional research and
formation of a subcommittee. The
College of Agriculture, Biotechnology
and Natural Resources at the University
of Nevada Reno (UNR) similarly
mentions the USAHA resolution.
Our Response: We are aware that
disagreement continues regarding the
potential for disease transmission to
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occur between domestic livestock,
especially sheep and goats, and bighorn
sheep, in general, under range
conditions. We have reviewed
Resolution No. 15 that reads, ‘‘The
United States Animal Health
Association (USAHA) urges the United
States Secretary of Agriculture and the
United States Secretary of the Interior to
seek resources through the President’s
budget to fund research to better
elucidate the epidemiology and
pathogenesis of bighorn/domestic sheep
disease interactions so informed and
effective management decisions can be
made.’’ We, along with others, continue
to seek answers to questions related to
this disease transmission issue. We
support continuing research efforts to
address uncertainties and to assist in the
decision-making process.
(11) Comment: The CDFA
recommends consideration of the
Western Association of Fish and
Wildlife Agencies’ (WAFWA)
document, ‘‘Recommendations for
Domestic Sheep and Goat Management
in Wild Sheep Habitat’’, dated June 21,
2007, and the University of California—
Davis’ ‘‘Quantifying the Risk of Disease
Transmission from Domestic Sheep to
Bighorn Sheep in the Sierra Nevada’’ in
future determinations of effectively
preventing the possibility of disease
transmission between domestic sheep
and Sierra Nevada bighorn sheep, in
addition to working with livestock
industry representatives.
Our Response: We are aware of these
documents and consider information
contained within them during section 7
consultations, as appropriate. Other
documents also support the effective
separation of domestic sheep from
bighorn sheep, in general, as a
management tool to reduce the risk of
contact and possible disease
transmission (Wyoming State-wide
Bighorn/Domestic Sheep Working
Group 2004, pp. 7, 11; U.S. Forest
Service 2006, pp. 18–19). Also, an
expert science panel (U.S. Geological
Survey and Bureau of Reclamation
2006) was convened in 2006 to discuss
a risk analysis of disease transmission
between domestic and bighorn sheep on
the Payette National Forest in Idaho.
The panel focused on science-based
concerns raised by the risk analysis
document, specifically the disease/
mortality category, and developed six
statements. References to concerns
about domestic sheep also apply to
domestic goats. Three of these key
statements follow: ‘‘(1a) Scientific
observation and field studies
demonstrate that ‘‘contact’’ between
domestic sheep and bighorn sheep is
possible under range conditions. This
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contact increases risk of subsequent
bighorn sheep mortality and reduced
recruitment, primarily due to
respiratory disease; (1b) The complete
range of mechanisms/causal agents that
lead to epizootic disease events cannot
be conclusively proven at this point;
and (1c) Given the previous two
statements, it is prudent to undertake
management to prevent contact between
these species’’ (U.S. Geological Survey
and Bureau of Reclamation 2006, p. 1).
One panelist dissented and preferred
‘‘can increase risk’’ in statement 1a
because it did not imply that any
contact will result in disease
transmission (U.S. Geological Survey
and Bureau of Reclamation 2006, p. 1).
(12) Comment: The California
Department of Transportation
(CalTrans) states that roads are
inconsistently addressed and that it is
inappropriate to include state highway
right-of-ways (ROWs) and facilities
within critical habitat. It is
recommended by CalTrans that State
Route (SR) 120 in Unit 1 and SR 158 in
Unit 2 be excluded from critical habitat.
Our Response: When determining
critical habitat boundaries for Sierra
Nevada bighorn sheep, we made every
effort to avoid including developed
areas such as lands covered by
buildings, paved areas, and other
structures that lack PCEs for the Sierra
Nevada bighorn sheep. The scale of the
maps prepared under the parameters for
publication within the Code of Federal
Regulations may not reflect the
exclusion of such developed areas. Any
such features and the land under them
inadvertently left inside critical habitat
boundaries shown on the maps of this
final rule have been excluded by text in
the final rule and are not designated as
critical habitat. Therefore, Federal
actions limited to these areas would not
trigger section 7 consultation, unless
they may affect the species or PCEs in
adjacent critical habitat.
We have determined, however, that
the unpaved road right-of-ways of SR
120 from Unit 1 and SR 158 from Unit
2 do contain the features essential to the
conservation of the Sierra Nevada
bighorn sheep, and therefore meet the
definition of critical habitat. CalTrans
did not provide, nor are we aware of any
additional information of the benefits of
excluding ROWs based on ongoing or
planned management of these ROWs, or
how any on-going or planned
management of the ROWs would benefit
the conservation of the Sierra Nevada
bighorn sheep or the sheep itself.
The Secretary may exclude an area
from critical habitat under section
4(b)(2) of the Act after taking into
consideration the economic impact, the
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impact on national security, and any
other relevant impact if he determines
that the benefits of such exclusion
outweigh the benefits of designating
such area as critical habitat, unless he
determines that the exclusion would
result in the extinction of the species
concerned.
Because we are not aware of any
information describing the benefits of
excluding ROWs based on ongoing or
planned management of these ROWs, or
how any existing or planned
management provides the same or better
level of protection from adverse
modification or destruction than that
provided through a consultation under
section 7 of the Act, we have
determined that exclusion of these lands
from the final designation of critical
habitat pursuant to section 4(b)(2) of the
Act is not appropriate at this time.
(13) Comment: CalTrans states that no
bighorn sheep collisions with vehicles
are listed in their accident database.
This is contrary to a statement made in
our proposed rule that a bighorn sheep
collision with a vehicle had occurred in
the past.
Our Response: A CDFG employee was
made aware of the collision we
referenced in the proposed rule (72 FR
40956) through a third party. The
employee contacted the motorist to
obtain information about the November
2003 collision. The Sierra Nevada
bighorn sheep ram was monitored after
the collision by CDFG, and it
subsequently died in January 2004. No
formal report was made by CDFG to
CalTrans (Stephenson 2008, p. 1).
(14) Comment: CalTrans indicates
references to SR 190 should be corrected
as SR 190 does not occur in or adjacent
to critical habitat.
Our Response: We erroneously
indicated SR 190 occurred in or
adjacent to Unit 10 in the Proposed
Critical Habitat Designation and the
Special Management Considerations or
Protection sections. The road should
have been indicated as Forest Route
16S02. This has been corrected in both
sections.
(15) Comment: CalTrans states that,
although an alignment has not been
selected for the proposed Olancha/
Cartago U.S. 395 project, an alternative
might occur on the west side of Los
Angeles aqueduct.
Our Response: We appreciate this
information. If the location for this new
road construction occurs within
designated critical habitat or may
impact the Sierra Nevada bighorn sheep
or its designated critical habitat,
consultation under section 7 of the Act
will occur as appropriate.
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(16) Comment: The Nevada
Department of Agriculture (NDOA)
stated that the disease transmission risk
assessment model by Clifford et al.
(2007) is ‘‘questionable’’ as a tool for
management and is a problem when
serving as the basis of a critical habitat
designation. The College of Agriculture,
Biotechnology and Natural Resources at
the University of Nevada Reno (UNR)
similarly recommends that the disease
risk assessment by Clifford et al. (2007)
should not be used as the basis for
designating Sierra Nevada bighorn
sheep critical habitat.
Our Response: We agree. Critical
habitat as defined in section 3 of the Act
is; the specific areas within the
geographical area occupied by a species
at the time it is listed in accordance
with the Act, on which are found those
physical or biological features essential
to the conservation of the species and
which may require special management
considerations or protection; and
specific areas outside the geographical
area occupied by a species at the time
it is listed, upon a determination that
such areas are essential for the
conservation of the species. Designation
of critical habitat is not based on a
single management issue and, in this
case, the concern for transmission of
diseases from the grazing of domestic
sheep or goats in proximity to Sierra
Nevada bighorn sheep did not serve as
the foundation for this critical habitat
designation. Domestic sheep grazing is a
management issue that is properly
addressed through the consultation
process under section 7(a)(2) of the Act.
(17) Comment: The NDOA
recommended that the critical habitat
designation be suspended until the
scientific basis has been established for
disease transmission between domestic
sheep and Sierra Nevada bighorn sheep.
Our Response: We are designating
critical habitat for Sierra Nevada
bighorn sheep in accordance with the
deadlines established by a courtapproved settlement agreement. We
agreed to submit to the Federal Register
a final determination of critical habitat
for Sierra Nevada bighorn sheep by July
17, 2008. We based our designation of
critical habitat on the best scientific and
commercial data available as required
by Section 4 of the Act. Further, our
Policy on Information Standards Under
the Endangered Species Act (published
in the Federal Register on July 1, 1994
(59 FR 34271)), the Information Quality
Act (section 515 of the Treasury and
General Government Appropriations
Act for Fiscal Year 2001 (Pub. L. 106–
554; H.R. 5658)), and our associated
Information Quality Guidelines provide
criteria, establish procedures, and
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provide guidance to ensure that our
decisions are based on the best scientific
data available. We used published
scientific literature and the expertise of
Recovery Team members (including
scientists from a variety of federal and
state agencies, and other publics). We
also solicited peer review from
individuals familiar with bighorn sheep,
in general, and related issues. We
solicited new biological data, invited
public participation during multiple
comment periods, conducted a public
hearing, and held informational
meetings on the proposed rule. We have
considered peer review, agency, and
public comments received during the
preparation of this final rule.
Accordingly, we have used the best
scientific and commercial information
available in this designation.
Designation of critical habitat is not
based on a single management issue
and, in this case, the concern for
transmission of diseases from the
grazing of domestic sheep or goats in
proximity to Sierra Nevada bighorn
sheep did not serve as the foundation
for this critical habitat designation.
(18) Comment: The NDOA stated that
uncertainties in general about bighorn
sheep epizootics exist per the USAHA
meeting in October 2007.
Our Response: Please see our
response to Comment 10.
(19) Comment: The NDOA stated that
the occurrence of bighorn sheep disease
and die-offs can be associated with
bighorn sheep reaching peak numbers
(Monello et al. 2001). Stagnant bighorn
sheep population numbers have
occurred in association with predation
by wolves and mountain lions. These
factors affect bighorn sheep populations
‘‘permanently,’’ not just ‘‘temporarily’’
like domestic sheep grazing.
Our Response: Bighorn sheep
mortalities can be attributed to various
factors as discussed below in the
‘‘Mortality Factors’’ section of this rule.
These mortality factors may or may not
affect bighorn sheep populations
‘‘permanently,’’ depending on
numerous variables. Die-offs from
diseases possibly transmitted from
domestic sheep can have long-lasting
effects by influencing subsequent
population recruitment. Lambs born to
surviving ewes can experience low
survival rates for 3 to 5 years after the
initial outbreak (Foreyt 1990, p. 100;
Coggins and Matthews 1992; Ward et al.
1992; Foreyt 1995; Hunter 1995a, as
cited in Schommer and Woolever 2001,
p. 3). We have added a short discussion
in the Physical and Biological Features
section related to these long-lasting
impacts of pneumonia in bighorn sheep
populations.
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(20) Comment: The NDOA and UNR
stated that climate and geographical
factors play a role in the recovery of a
species and that the ‘‘northern recovery
unit’’ is neither suitable nor essential
habitat in terms of winter range for the
Sierra Nevada bighorn sheep due to its
higher elevation and greater snow
depths than more southern units.
Our Response: As indicated in the
Criteria Used to Identify Critical Habitat
section, we used the following criteria
to select areas occupied by the Sierra
Nevada bighorn sheep at the time of
listing for inclusion in critical habitat:
(a) Those areas occupied by the Sierra
Nevada bighorn sheep at the time of
listing (1999–2000) as indicated in the
final listing rule (65 FR 20; January 3,
2000). In the final listing rule, we
identified five subpopulations of Sierra
Nevada bighorn sheep that existed: (1)
Lee Vining Canyon (Mount Warren and
Mount Gibbs Herd Units), (2) Wheeler
Crest (Wheeler Ridge Herd Unit), (3)
Mount Baxter (Sawmill Canyon and
Mount Baxter Herd Units), (4) Mount
Williamson (Mount Williamson Herd
Unit), and (5) Mount Langley (Mount
Langley Herd Unit) in Mono and Inyo
counties, California (Wehausen 1999,
pp. 1–7; 2000, pp. 1–6);
(b) Areas that are representative of the
distribution of the Sierra Nevada
bighorn sheep throughout the
geographical range occupied at the time
of listing with the goal of maintaining
the subspecies’ range of habitat and
genetic variability; and
(c) Areas that allow for the continued
existence of viable subpopulations
under varying environmental conditions
and that can serve as locations for
source populations. The locations of all
five subpopulations identified in the
original listing rule continue to remain
occupied today.
We have determined that the areas
occupied at the time of listing continue
to be occupied, contain features
essential to the conservation of the
subspecies (possess one or more PCEs
such that the area supports one or more
of the Sierra Nevada bighorn sheep’s life
processes) that may require special
management, and provide sufficient
habitat to protect these populations.
Units 1 (Mount Warren) and 2 (Mount
Gibbs) of the northern recovery unit
meet these criteria.
More specifically, essential habitat is
available for Sierra Nevada bighorn
sheep in Units 1 (Mount Warren) and 2
(Mount Gibbs). This is not only based
on historical data indicating their
presence as far north as Sonora Pass
(Grinnell and Storer 1924, as cited in
Service 2007, p. 14), but also on the fact
that these units also currently support
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Sierra Nevada bighorn sheep herds.
Mount Warren has a population of
approximately 26 individuals, and
Mount Gibbs has a population of
approximately 8 individuals (Wehausen
and Stephenson 2006, p. 7). The Mount
Gibbs herd spends almost the entire
year at elevations above 11,000 ft (3,353
m). In 2007, all ewes gave birth, and
their lambs are known to have survived
through at least September. This herd
continues to survive and reproduce,
expanding in numbers, although this
alpine environment is no doubt harsher
than lower-elevation areas. It is
expected this herd will outgrow its
carrying capacity of the alpine winter
ranges and begin using lower-elevation
winter ranges in the future (California
Department of Fish and Game 2007, p.
2). Surveys (ground and aerial
observations) of the Mount Warren herd
conducted during the period from 2003
to 2007 indicate individuals are using
this unit during every month of the year
(California Department of Fish and
Game files—monthly reports, Service
files). In addition, a Resource Selection
Probability Functions model was
developed for summer and winter
habitat and indicates an estimated 20.2
square kilometers (sq km) (7.8 square
miles (sq mi)) and 9.4 sq km (3.6 sq mi),
respectively, are available for Sierra
Nevada bighorn sheep in the Mount
Gibbs and Mount Warren units (Johnson
et al. 2005, p. 31). As discussed under
the Primary Constituent Elements for
Sierra Nevada Bighorn Sheep section of
this rule, not all life history functions
require all the PCEs, therefore, not all
areas designated as critical habitat
contain all of the PCEs. Units are
designated based on sufficient PCEs
being present to support one or more of
the subspecies’ life history
requirements. This applies to both the
occupied and unoccupied units
designated.
(21) Comment: The NDOA and UNR
noted that a memorandum to the
Director of the Service from the U.S.
Department of the Interior’s Assistant
Secretary for Fish and Wildlife and
Parks, dated April 28, 2004, stated that
critical habitat adds little additional
conservation benefit to a listed species
and designations must not be based on
speculation or determinations that lack
supporting data. Therefore, the
designation of critical habitat is of
‘‘dubious value’’ as identified by your
own agency.
Our Response: Section 4(A)(3) of the
Act requires that the Service identify
those lands on which are found the
physical or biological features essential
to the conservation of the species that
may require special management
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considerations or protection, and those
areas outside the geographical area
occupied by the species at the time of
listing that are essential to the
conservation of the species. In
identifying those lands, the Service
must consider the recovery needs of the
species, such that, on the basis of the
best scientific and commercial data
available at the time of designation, the
habitat that is identified, if managed,
could provide for the survival and
recovery of the species.
The identification of those areas that
are essential for the conservation of the
species and that can, if managed,
provide for the recovery of a species is
beneficial. The process of proposing and
finalizing a critical habitat rule provides
the Service with the opportunity to
determine the physical and biological
features essential to the conservation of
the species within the geographical area
occupied by the species at the time of
listing, as well as to determine other
areas essential for the conservation of
the species. The designation process
includes peer review and public
comment on the identified physical and
biological features and essential areas.
This process is valuable to land owners
and managers in developing
conservation management plans for
identified areas, as well as any other
occupied habitat or suitable habitat that
may not have been included in the
Service’s determination of essential
habitat.
The consultation provisions under
section 7(a) of the Act constitute the
regulatory benefits of critical habitat. As
discussed above, Federal agencies must
consult with us on discretionary actions
that may affect critical habitat and must
avoid the destruction or adverse
modification of critical habitat. Federal
agencies must also consult with us on
discretionary actions that may affect a
listed species and refrain from
undertaking actions that are likely to
jeopardize the continued existence of
such species. The analysis of effects to
critical habitat is a separate and
different analysis from that of the effects
to the species. Therefore, the difference
in outcomes of these two analyses
represents the regulatory benefit of
critical habitat. For some species, and in
some locations, the outcome of these
analyses will be similar, because effects
on habitat will often result in effects on
the species. However, the regulatory
standard is different: The jeopardy
analysis looks at the action’s impact on
survival and recovery of the species,
while the adverse modification analysis
looks at the action’s effects on the
designated habitat’s contribution to the
species’ conservation. This may, in
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many instances, lead to different results
and different regulatory requirements.
Thus, critical habitat designations may
provide greater regulatory benefits to the
recovery of a species than would listing
alone.
Another benefit of including lands in
critical habitat is that designation of
critical habitat serves to educate
landowners, State and local
governments, and the public regarding
the potential conservation value of an
area. In general, critical habitat
designation always has educational
benefits; however, in some cases, they
may be redundant with other
educational effects.
(22) Comment: The NDOA states that
listing of Sierra Nevada bighorn sheep
as an endangered species, subspecies, or
even distinct metapopulation lacks
scientific merit.
Our Response: Please refer to our final
rule listing the Sierra Nevada bighorn
sheep published on January 3, 2000 (65
FR 20), which outlines our rationale for
listing.
(23) Comment: The UNR stated
designating critical habitat for Sierra
Nevada bighorn sheep will lead to
grazing allotment closures.
Our Response: The designation of
critical habitat for Sierra Nevada
bighorn sheep does not automatically
lead to closing allotments. For those
areas on Federal lands, consultation
under section 7 of the Act may be
required to examine the effects of
grazing on critical habitat. Specific
actions by the managing Federal agency
could include the elimination of, or
restrictions on, livestock grazing in
areas that overlap with critical habitat.
Please also see our responses to
Comments 24, 40, 41, and 42.
(24) Comment: UNR states that shortterm, high intensity grazing by domestic
sheep helps maintain forage production
and fuel load accumulation. The
regrowth of vegetation is more palatable
and nutritious for Sierra Nevada bighorn
sheep during the growing season as well
as during winter. The removal of
domestic sheep will lead to poorer
forage production and an accumulation
of fuels.
Our Response: Regardless of any
effects of grazing on fuel loads and
forage quantity and quality, domestic
sheep in some locations may pose a
disease risk to Sierra Nevada bighorn
sheep. The Service will recommend the
removal of domestic sheep from
allotments where contact with Sierra
Nevada bighorn sheep cannot be
prevented through section 7 of the Act.
The Service has proposed actions in the
recovery plan for Sierra Nevada bighorn
sheep to maintain and enhance the
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integrity of habitat through the careful
use of fire and other habitat
manipulations that do not involve
domestic sheep grazing. These actions
would include maintenance and
enhancement of habitat in areas where
domestic sheep may be removed to
prevent contact with Sierra Nevada
bighorn sheep.
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Comments From Other Federal
Agencies
(25) Comment: Yosemite National
Park raised a concern about any
reduction in the proposed critical
habitat and protection of the Sierra
Nevada bighorn sheep in the ‘‘northern
recovery units’’ which would constitute
the ‘‘Yosemite herd.’’ Sierra Nevada
bighorn sheep in the northern areas are
the ones most likely to reoccupy habitat
in Yosemite, filling an ecological void
and offering park visitors the
opportunity to observe these animals.
Our Response: We have not reduced
the area of designated critical habitat for
the two units (Mount Warren and
Mount Gibbs) that occur within the
northern recovery unit because they
meet our criteria for identifying critical
habitat. These units contain the features
essential to the conservation of the
Sierra Nevada bighorn sheep and
require special management. We also
did not identify any areas within these
units where the benefits of exclusion
outweighed the benefits of inclusion.
Please also see our response to
Comment 20.
(26) Comment: Yosemite National
Park supports the proposed critical
habitat designation and taxonomic
revision but recommends expanding
critical habitat to cover all areas
currently occupied by Sierra Nevada
bighorn sheep, accommodate further
range expansion, and provide buffers
between domestic sheep and Sierra
Nevada bighorn sheep to prevent
disease transmission.
Our Response: As indicated in our
response to Comment 2, it is not our
practice to establish buffers around an
area designated as critical habitat. A
buffer distance indicated in a Federally
proposed action involving domestic
sheep or goat grazing near designated
critical habitat would be considered
during the consultation process under
section 7 of the Act. As indicated in our
response to Comment 36, critical habitat
should not include the entire area that
can be occupied by the species. We
based our designation on the Recovery
Team’s delineation of essential habitat
and as indicated in our final approved
recovery plan (Service 2007, p. 41). For
a more thorough discussion of these
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topics, please see our responses to
Comments 2 and 36.
(27) Comment: Sequoia and Kings
Canyon National Parks indicated their
commitment to preserving and restoring
natural ecosystems. They view Sierra
Nevada bighorn sheep as an essential
component that has been lost from
much of its historical range within the
Parks. By policy and law there is a
commitment to working with the
Service and other agencies to help
restore the Sierra Nevada bighorn sheep
to their former range and abundance.
Sequoia and Kings Canyon National
Parks fully support the proposed critical
habitat designation.
Our Response: We appreciate the
support and look forward to continuing
to work with the National Park Service
and others to conserve the Sierra
Nevada bighorn sheep.
(28) Comment: The USFS suggested
that designating critical habitat does not
provide any additional benefit to a
species and that it unnecessarily adds to
USFS workload and may lead to reinitiation of section 7 consultation for
critical habitat where a consultation has
already been completed.
Our Response: Designating critical
habitat identifies those areas that
contain the features that are essential to
the conservation of a particular species,
thus signaling to Federal agencies to
consider the species’ conservation in the
design and implementation of their
management actions. The designation
provides guidance on why these areas
need special management
considerations or protection and
indicates activities that are likely to
adversely modify or destroy critical
habitat. The designation of critical
habitat assists the recovery process by
providing information on how actions
might impact the species’ habitat.
Including USFS lands as critical habitat
is significant because this will assist in
maintaining the Service’s role in
reviewing potential future impacts to
areas that are important for the
conservation of Sierra Nevada bighorn
sheep populations. Lands administered
by the USFS contain a substantial
portion of habitat that is essential for the
conservation of Sierra Nevada bighorn
sheep. Designation of critical habitat
may also provide protection for
unoccupied habitat that may not
otherwise undergo the section 7
consultation process due to species’
absence. Considering whether proposed
future projects will result in the
destruction or adverse modification of
critical habitat in addition to the
jeopardy analysis will require some
additional analysis during the section 7
consultation process.
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(29) Comment: The USFS indicated
the 2001 Record of Decision for the
Ansel Adams, John Muir, and Dinky
Lakes Wilderness Plans considered
various impacts on Sierra Nevada
bighorn sheep and their habitats.
Our Response: We appreciate this
information and have reviewed this
document. Only one item was found
directly related to management of the
Sierra Nevada bighorn sheep. This
addressed the closure of Sierra Nevada
bighorn sheep habitat to dogs. As
indicated in the Special Management
Considerations or Protection section,
dogs (with their associated recreation
activities) are a potential threat to Sierra
Nevada bighorn sheep critical habitat.
At issue are the effects of Wilderness
Plans, associated Forest Land and
Resource Management Plans, and
ongoing activities on USFS lands on
federally listed species, including the
Sierra Nevada bighorn sheep. The goal
of these plans is to describe a strategic
direction for the management of the
wilderness areas over a long period of
time (15–20 years). The plans do not
make any decisions regarding USFS
site-specific project proposals for
implementing the land management
plans nor do they require managers to
implement any specific conservation
activities.
(30) Comment: The USFS stated that
management direction was established
to restrict dogs in Sierra Nevada bighorn
sheep habitat located in the Mt. Baxter
and Mt. Williamson California Bighorn
Sheep Zoological Areas on the Inyo
National Forest.
Our Response: Please see our
response to Comment 29. These
statements also apply to FS Order No.
04–81–3 which established these
zoological areas in 1981.
(31) Comment: The USFS commented
that the proposed critical habitat
designation does not establish migration
corridors between the units though
migration is identified as important.
While paths that rams may take between
units or groups may be unpredictable,
the final designation would be
strengthened if it were to identify
dispersal and movement corridors that
are integral to the habitat elements.
Our Response: Please see our
response to Comment 4.
(32) Comment: The USFS requests
clarification on why disease
transmission from domestic livestock
grazing is included as a stochastic event.
Our Response: This has been
corrected. We have removed those
references specifically identifying the
risk of disease transmission from
domestic livestock from (3) of the
Criteria Used To Identify Critical
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Habitat section. The remaining reference
addresses various diseases of North
American wild sheep.
(33) Comment: The USFS suggested
that the proposal is not as clear as it
should be regarding the effects of
disease transmission on Sierra Nevada
bighorn sheep populations.
Incorporating disease-associated risks
into a PCE would strengthen the
proposal.
Our Response: We have added some
additional information in the biological
background of the Primary Constituent
Elements section of this rule. Please also
see our response to Comment 1.
(34) Comment: The USFS stated that
while it is important to decrease the
degree of habitat fragmentation in the
Sierra Nevada, the designation of
critical habitat does not actually do that.
Our Response: Designation of critical
habitat offers protection from various
impacts which may be proposed on the
landscape. We believe designating
critical habitat in 12 units ranging from
22,037 ac (8,918 ha) to 80,966 ac (32,766
ha) does reduce potential habitat
fragmentation. Providing protections for
currently unoccupied areas that
decrease the distances between
occupied areas also assists in reducing
habitat fragmentation. The protection of
these unoccupied habitats will allow for
future establishment of herds in these
habitats through translocation or natural
colonization, which will help to
increase gene flow between populations.
The ability to establish and maintain
regular gene flow between populations
of Sierra Nevada bighorn sheep is
essential to their recovery. Reducing
habitat fragmentation through
protection of these currently
unoccupied habitats under a critical
habitat designation is essential to the
subspecies’ conservation.
(35) Comment: The USFS
recommended that the section
discussing wildfire be clarified to
resolve apparent contradictions
identifying which management actions
and stochastic events are considered
potentially beneficial or detrimental to
critical habitat.
Our Response: Fires can have
beneficial, as well as detrimental, effects
depending on the situation including
location, severity, and extent. As
indicated in the Special Management
Considerations or Protection section,
management actions such as the
suppression of wildfires over the past
decades has allowed for encroachment
of forested habitat into Sierra Nevada
bighorn sheep habitat. This has been
detrimental to the Sierra Nevada
bighorn sheep by increasing habitat for
predator concealment. Management
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actions such as prescribed fires are
carried out in a planned, controlled
manner in a specific area and can be
beneficial to Sierra Nevada bighorn
sheep by reducing selected forested
habitat that can conceal predators.
Stochastic events such as wildfires can
be beneficial or detrimental. For
example, in July 2007, lightning sparked
fires in Sierra Nevada bighorn sheep
habitat in the Mount Baxter herd unit.
The Seven Oaks Fire burned the
majority of the low elevation winter
range [<8,000 ft (2438 m)] (California
Department of Fish and Game 2007, p.
5). The fire may benefit Sierrra Nevada
bighorn sheep by opening up forested
areas. The fire also scorched the above
ground vegetation. With appropriate
moisture levels gained over the winter,
sufficient forage may become available.
The CDFG personnel intend to evaluate
the effects of this fire on forage
availability and quality and habitat
selection by Sierra Nevada bighorn
sheep in this area (California
Department of Fish and Game 2007, p.
6).
(36) Comment: The USFS mentioned
that the Mount Warren unit may not
extend northward enough to encompass
currently occupied habitat as a few
Sierra Nevada bighorn sheep have
occurred in the northern areas.
Our Response: According to 16 U.S.C.
1532(5)(C), ‘‘critical habitat should not
include the entire geographic area that
can be occupied by the threatened or
endangered species’’ absent a finding of
exceptional circumstances by the
Secretary of the Interior. We based our
critical habitat designation on the
Recovery Team’s delineation of
essential habitat and as indicated in our
final approved recovery plan (Service
2007, p. 41). The Recovery Team did not
include all areas that have documented
historical and current use by Sierra
Nevada bighorn sheep, but only those
areas regarded as essential for the
recovery of the Sierra Nevada bighorn
sheep. We used the Recovery Plan to
assist in the preparation of the proposed
and final critical habitat designations.
Integration of these processes
strengthens the scientific basis and
minimizes the potential discrepancies
between the two. Please refer to the final
recovery plan for a more detailed
discussion of the recovery strategy. The
basis for the critical habitat delineation
is described in the Criteria Used to
Identify Critical Habitat section of this
rule. We did not include the areas to the
north of Mount Warren or the Bubbs
Creek area as critical habitat as these
areas did not meet our criteria for
inclusion as critical habitat for Sierra
Nevada bighorn sheep. Not including
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these areas within the critical habitat
designation does not preclude the
continued occupancy or expansion of
Sierra Nevada bighorn sheep into these
areas. We believe the units designated
as critical habitat contain sufficient
PCEs to support the behaviors we have
determined are essential for the
conservation of the subspecies and
population criteria as identified in the
final recovery plan. Therefore, we have
not included these additional areas as
critical habitat in the final rule.
(37) Comment: The USFS stated there
appear to be some biological
contradictions among units that were
included and those that were
‘‘excluded’’ in the critical habitat
designation. For example, the Bubbs
Creek Herd Unit is currently occupied
yet is excluded; and the Mount Warren
area does not provide access to low
elevation winter range yet is included.
Our Response: No areas were
excluded from the final critical habitat
designation. We did not designate four
herd units that were mentioned in the
Sierra Nevada bighorn sheep final
recovery plan as they were not
considered essential in the plan. Please
refer to the Criteria Used to Identify
Critical Habitat section for our detailed
rationale for not designating these areas.
Please also refer to our responses to
Comments 36 and 50.
(38) Comment: The USFS suggested
that the ramifications of global climate
change be considered in the proposal.
Our Response: As indicated in the
final recovery plan (Service 2007, p. 41),
two northern herd units, Mount Warren
and Mount Gibbs, are included as
essential to the conservation of the
Sierra Nevada bighorn sheep, in part, to
protect this subspecies and its habitat
across a range of latitudes. Climate
change may induce ecological changes
in the essential herd units in the south.
Populations in the northern latitudes
can help guard the rangewide
population against loss of populations
in areas that occur further south.
General Comments
Comments Related to Designation and
Sierra Nevada Bighorn Sheep Biology
and Management
(39) Comment: A few commenters
stated concern for the areas of overlap
between proposed critical habitat and
Federal domestic sheep grazing
allotments. The commenter requested
that these areas of overlap (six areas
with an estimated 1,000 ac (405 ha) be
excluded from the critical habitat
designation. If these areas are not
excluded, the commenter requested
specific justification and evaluation of
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the habitat including what contribution
these areas make to Sierra Nevada
bighorn sheep and why their
elimination would be detrimental to
recovery efforts.
Our Response: We have determined
that there are seven areas of overlap
between designated critical habitat and
Federal domestic sheep grazing
allotments [Bureau of Land Management
(BLM) or USFS], not six as the
commenter stated. These allotments
include: (1) Dunderberg; (2) Copper
Mountain; (3) Bloody Canyon; (4)
McGee; (5) Sherwin; (6) Round
Mountain; and (7) Rock Creek-Hilton
Unit. The overlap areas total
approximately 2,209 ac (894 ha). At the
time critical habitat was proposed, all of
these allotments were considered
vacant, inactive, or unalloted with the
exception of the Rock Creek-Hilton
Unit. The Rock Creek-Hilton Unit is the
only active domestic sheep grazing
allotment that overlaps with designated
critical habitat. This overlap is 0.9 ac
(0.4 ha).
In our proposed rule and this final
rule, we included domestic livestock
grazing as a threat to the essential
features that may need special
management considerations or
protection within designated critical
habitat units. Consultation under the
Act by Federal agencies may be
necessary if proposed actions may
adversely affect the Sierra Nevada
bighorn sheep or its critical habitat. We
have determined that all seven overlap
areas are essential to the Sierra Nevada
bighorn sheep because they contain the
features essential to the conservation of
the subspecies and meet the definition
of critical habitat. Please see the Criteria
Used To Identify Critical Habitat section
for more information. One of our
objectives is to provide consistency
between critical habitat designation and
the essential habitat indicated in the
final recovery plan (Service 2007, p. 41).
The Secretary may exclude an area
from critical habitat under section
4(b)(2) of the Act after taking into
consideration the economic impact, the
impact on national security, and any
other relevant impacts if he determines
that the benefits of such exclusion
outweigh the benefits of designating
such area as critical habitat, unless he
determines that the exclusion would
result in the extinction of the species
concerned.
We have previously consulted with
the USFS on grazing issues in Units 1,
2, and 4 and have determined that those
activities were either not likely to
adversely affect the Sierra Nevada
bighorn sheep or were not likely to
jeopardize the continued existence of
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the subspecies. Since critical habitat has
not been previously proposed or
designated for this subspecies, it is
anticipated that Federal agencies will
initiate section 7 consultation as
appropriate, for any activities that may
affect Sierra Nevada bighorn sheep or its
critical habitat. These consultations
would include an analysis of
destruction or adverse modification of
critical habitat as well as a jeopardy
analysis. Considering whether proposed
future projects will result in the
destruction or adverse modification of
critical habitat in addition to the
jeopardy analysis will require some
additional analysis during the section 7
consultation process. We do not believe
that the additional analysis to determine
whether an action will result in the
destruction or adverse modification of
critical habitat constitutes a substantial
burden.
According to the final EA, postdesignation baseline costs for grazing
are estimated at $12.5 million
(undiscounted) over the next 20 years,
$9.6 million applying a 3 percent
discount rate, or $7.1 million applying
a 7 percent discount rate. Postdesignation incremental costs for
grazing consultations are estimated to be
$97,600 (undiscounted) over the next 20
years, $74,800 applying a 3 percent
discount rate, or $55,300 using a 7
percent discount rate.
These impacts are primarily due to
the predicted yearly formal section 7
consultations between the Service and
the USFS on allotments in proximity to
critical habitat in Unit 1. There are no
forecasted post-designation incremental
impacts for the other critical habitat
units. Thus, costs are not considered to
be disproportionate. We will continue to
work with the USFS, BLM, and
permittees to address concerns related
to the Sierra Nevada bighorn sheep
during the section 7 consultation
process as appropriate.
Units 1, 2, and 4 all contain the
features essential to the conservation of
the Sierra Nevada bighorn sheep. The
benefits of including these units in
critical habitat include access to areas
for foraging (summer and winter),
mating, lambing, bedding, predator
avoidance, seasonal elevational
movements, and mineral licks.
We have considered the request by
the commenters to exclude the areas
listed above and the relevant impacts of
designation. Based on this record, we
have chosen not to exclude these areas.
(40) Comment: Domestic sheep
producers have been working with
Federal agencies informally to prevent
contact between domestic sheep and
Sierra Nevada bighorn sheep. These
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practices should be formalized by the
grazing permit process.
Our Response: Federal agencies that
issue grazing permits that may affect
federally listed species consult with the
Service as required under section 7 of
the Act, as appropriate, even in the
absence of critical habitat. The purpose
of the section 7 consultation process is
to analyze the effects of an action (e.g.,
the issuance of a grazing permit) to
determine if the action will jeopardize
the continued existence of the listed
species, to provide reasonable and
prudent measures to avoid and
minimize the impact of incidental take,
and, if necessary, to provide reasonable
and prudent alternatives to avoid
jeopardy. With the designation of
critical habitat, Federal agencies will
also determine whether the proposed
action will adversely modify or destroy
critical habitat under this process. The
Service has, and will continue to, work
with Federal agencies and grazing
permittees to address concerns related
to the Sierra Nevada bighorn sheep
during the section 7 consultation
process, as appropriate. Outside of the
section 7 consultation process, the
Service has the ability to provide
comments to other Federal agencies
during National Environmental Policy
Act (NEPA) review.
(41) Comment: Some commenters
urged the continued authorization of
domestic sheep grazing on lands
designated as critical habitat. Others did
not support domestic sheep grazing
within these areas.
Our Response: The designation of
critical habitat does not automatically
eliminate or place restrictions on
domestic sheep grazing or other land
use activities in areas that overlap with
critical habitat. For those areas on
Federal lands, consultation under
section 7 of the Act may be appropriate.
Please also see our response to
Comments 23 and 39.
(42) Comment: A concern was raised
that elimination of cattle grazing at
higher elevations may occur due to the
designation of critical habitat.
Our Response: There are several
Federal cattle grazing allotments (USFS
and BLM administered lands) that
overlap with critical habitat designation
in both occupied and unoccupied units.
The designation of critical habitat does
not automatically eliminate or place
restrictions on cattle grazing or other
land use activities in areas that overlap
with critical habitat. To date, we have
not conducted section 7 consultations
with other Federal agencies related to
impacts of cattle grazing to Sierra
Nevada bighorn sheep. However, if the
Federal agencies determine that
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issuance of grazing permits may affect
Sierra Nevada bighorn sheep or its
critical habitat, they will request
consultation under section 7 of the Act.
(43) Comment: One commenter
recommended that managed cattle
grazing be ‘‘protected,’’ or retained,
within critical habitat as a recovery tool.
Our Response: There are currently
several Federal cattle grazing allotments
located within designated critical
habitat. We do not know the amount of
private lands where cattle grazing may
also occur within critical habitat, but
the total amount is not more than 1,005
ac (407 ha). Cattle grazing on Federal
allotments within critical habitat should
be reviewed under section 7 of the Act
if it may affect Sierra Nevada bighorn
sheep or its critical habitat. In addition,
the suggestion that Federal domestic
sheep grazing allotments could be
converted to cattle grazing allotments to
reduce the potential impacts of disease
transmission from domestic sheep to
Sierra Nevada bighorn sheep has been
raised. Allotment conversion would
require Federal agency involvement, as
well as willingness and ability on the
part of the permittee. This suggestion
has been included in the final recovery
plan for the Sierra Nevada bighorn
sheep (Service 2007, pp. 64 and 70).
(44) Comment: Habitat protection and
disease issues are different and should
be treated separately.
Our Response: These issues are
treated differently as indicated by the
definition of critical habitat stated in
this rule under the Critical Habitat
section and the activities addressed
under the Special Management
Considerations or Protection section.
(45) Comment: Why is 417,000 ac
(168,757.6 ha) needed for 400 Sierra
Nevada bighorn sheep?
Our Response: The critical habitat
designation of 417,577 ac (168,992 ha)
is not only for the estimated 400 Sierra
Nevada bighorn sheep’s current
population. The area of critical habitat
is also for the additional animals that
are needed for the recovery of the
species and to provide sufficient area for
their life history requirements.
According to the final recovery plan,
there should be an estimated minimum
total of 305 females at least 1 year of age
throughout the four recovery units at the
time of delisting (Service 2007, p. 47).
Based upon a natural adult sex ratio of
about 70 males:100 females, the
minimum total population (both sexes)
is estimated to be 520 adults at
delisting. Since this number is based on
a minimum requirement for each
recovery unit, the total population is
likely to be higher. This number would
be higher still with young of the year
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also included in the total (Service 2007,
p. 44).
(46) Comment: Why is it necessary to
have critical habitat if section 7 is
already being used?
Our Response: Under section 7(a)(2)
of the act, Federal agencies must consult
with the Service to ensure that their
actions do not jeopardize the continued
existence of listed species. By
designating critical habitat, section 7 of
the Act also protects the recovery needs
of the species by requiring Federal
agencies to ensure that their actions will
not result in the destruction or adverse
modification of designated critical
habitat. For additional information,
please also refer to our response to
Comment 28.
(47) Comment: Several comments
were received related to recreational
activities and what the designation of
critical habitat signifies now and in the
future. Some commenters recommended
that snowmobiles and off-road vehicles
be prohibited in critical habitat and
existing routes be closed. Others
thought it was appropriate to ‘‘exclude’’
dogs or require them to be on leashes at
all times. Others recommended that no
new off-road vehicle trails be built in
critical habitat. Others expressed
support for our ‘‘exclusion’’ of
particular recreational areas from the
designation. Others requested no
restrictions on backcountry use. Others
wondered if public use would continue
as it does currently. Others
recommended that any restrictions
apply to both guided and non-guided
public alike. A few commenters
suggested that the rule be changed to
state that most, if not all, types of
recreation were non-threatening to
Sierra Nevada bighorn sheep, especially
when bighorn sheep are not overtly
threatened and have access to escape
terrain. Some suggested continued
monitoring of both Sierra Nevada
bighorn sheep and the effects of
people’s interaction with them as
recreation is an important component of
the economy.
Our Response: Proposed and final
rules designating critical habitat do not
automatically eliminate or place
restrictions on any recreational
activities or opportunities within
critical habitat. This rule did not
‘‘exclude’’ any particular recreational
area from the critical habitat
designation; these areas were not
included because they did not meet our
criteria for designating critical habitat
for Sierra Nevada bighorn sheep. For
more information on the criteria used to
delineate critical habitat please see the
Criteria Used to Identify Critical Habitat
section in this rule. The designation of
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critical habitat is not a management
plan, nor does it put in effect or restrict
management activities. The Special
Management Considerations or
Protection section of this final rule lists
actions that may impact the PCEs for
Sierra Nevada bighorn sheep and serves
as a guide to Federal agencies that may
conduct or permit actions within
designated critical habitat. The USFS
and National Park Service may have
restrictions (e.g., quotas, seasonal
closures, dog prohibitions or leash
requirements) already in place in some
areas to address resource concerns, as
well as to reduce impacts to wildlife,
including Sierra Nevada bighorn sheep.
Due to areas of rugged terrain and
inaccessibility, as well as wilderness
designations, some recreational
activities (e.g., snowmobiling, off-road
vehicle use) are not possible within
portions of the designated critical
habitat. Other activities, such as rock
and ice climbing and peak bagging, are
specific to these rugged areas. We
encourage the public to enjoy the Sierra
Nevada while treating it with respect.
With proper management, recreational
activities can or may be compatible with
Sierra Nevada bighorn sheep
conservation and recovery. It is the
responsibility of the Federal agencies to
review the various kinds of recreational
activities currently allowed, where they
are allowed, and the seasonal use of
these areas among other things, to
determine if these activities may result
in the destruction or adverse
modification of critical habitat. Federal
agencies will review all proposed
actions in accordance with section
7(a)(2) of the act in light of possible
increases of sheep-human interaction
due to both increasing Sierra Nevada
bighorn sheep and human populations,
and subsequent habitat use changes. We
will continue to work with Federal
agencies and those who need Federal
permits through the section 7
consultation process to address
recreational activities that may affect
Sierra Nevada bighorn sheep habitat.
We have added some additional
information related to bighorn sheep
and human interactions in the Special
Management Considerations or
Protection section in this rule. As
previously stated, we will continue to
recommend that studies be
implemented to clarify any potential
impacts of different recreational
activities on Sierra Nevada bighorn
sheep and their habitat to assist with
decision-making processes.
(48) Comment: While several
commenters expressed support for the
critical habitat designation as proposed,
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a majority of commenters expressed a
desire that additional lands be included.
Some offered a general statement to
expand the critical habitat designation
while others provided more specific
statements of additional areas to be
included. These recommendations were
to include: (1) All historical and
currently occupied areas; (2) areas north
of Mount Warren; (3) all occupied and
unoccupied habitat essential for
survival and recovery; (4) all areas
identified as of recovery value in the
recovery plan; and (5) the Bubbs Creek
area.
Our Response: Please see our
response to Comment 36.
(49) Comment: Many ranchers have
lost faith in the Service’s ability to
implement Sierra Nevada bighorn sheep
recovery and re-introduction efforts
while protecting ranching operations.
For example, ‘‘a rancher lost his Bloody
Canyon USFS Allotment, although
previously promised that Sierra Nevada
bighorn sheep recovery would not
require any changes in the use of [the
Bloody Canyon] allotment.’’
Our Response: The ‘‘promise’’
referred to in the comment above relates
to two letters, one written by the CDFG
dated August 27, 1984, and addressed to
the Inyo National Forest, and the other
written by the Forest Service dated
December 20, 1989, and addressed to
the permittee. It is important to note
that these letters were written by other
agencies prior to the Federal listing of
the Sierra Nevada bighorn sheep in
2000, and prior to the Service’s
involvement with this subspecies. Since
the listing of the subspecies and
development of the recovery plan,
substantial new information has been
gathered regarding areas used by Sierra
Nevada bighorn sheep. The Service has
and will continue to coordinate with
individual ranchers, the State of
California, and other Federal agencies to
promote the recovery of Sierra Nevada
bighorn sheep while balancing the
needs of affected permittees and
conservation of the subspecies through
the section 7 consultation process. Also,
please refer to our response to Comment
40.
(50) Comment: The areas of Twin
Lakes, Green Creek, Coyote Ridge, and
Bubbs Creek should not be ‘‘excluded’’
from critical habitat designation.
Our Response: These four areas were
not ‘‘excluded’’ from the critical habitat
designation. These four areas were not
included within our critical habitat
designation because they were not
determined to be essential for the
conservation of the Sierra Nevada
bighorn sheep. Please see the Criteria
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Used to Identify Critical Habitat section
for our rationale.
(51) Comment: Some commenters
agreed that the four existing plans
[Sierra Nevada Bighorn Sheep Recovery
and Conservation Plan (Sierra Nevada
Bighorn Sheep Interagency Advisory
Group 1984); the Bighorn Sheep
Management Plan (National Park
Service 1986); the Inyo National Forest
Resource & Management Plan (U.S.
Forest Service 1988); and A
Conservation Strategy for Sierra Nevada
Bighorn Sheep (Sierra Nevada Bighorn
Sheep Interagency Advisory Group
1997)] should not result in the
exclusions of lands covered by these
plans from critical habitat designation.
One commenter thought we should
exclude these lands because the plans
already exist and there are recovery
projects in place.
Our Response: We have indicated our
rationale for not excluding areas
covered by these four plans as indicated
in the Application of section 4(b)(2) of
the Act section of this final rule. These
plans are general in nature and reflect
our knowledge at that time. All plans
were prepared prior to the listing of the
subspecies. Specific recovery projects
and actions are a result of the draft and
final recovery plans, not these four
documents.
(52) Comment: Does the designation
of critical habitat allow for management
of mountain lions?
Our Response: The designation of
critical habitat will not affect the
management of mountain lions as their
control is not a habitat-based threat. The
encroachment of vegetation that
provides cover for predators of the
Sierra Nevada bighorn sheep is a
habitat-based threat, and actions to
manage the vegetation encroachment
may require special management
considerations or protection as
discussed in this rule. We, along with
CDFG, recognize the role that mountain
lions have played in the status of the
Sierra Nevada bighorn sheep. Beginning
in 2000, CDFG began placing radio
collars on mountain lions near Sierra
Nevada bighorn sheep ranges and
monitoring them to assist in the removal
of selected individuals to benefit Sierra
Nevada bighorn sheep. Mountain lions
are a necessary and important part of
the Sierra Nevada ecosystem; Sierra
Nevada bighorn sheep have evolved
with this predator on the landscape. As
the numbers of Sierra Nevada bighorn
sheep increase with recovery, the need
for mountain lion control specifically
for the benefit of Sierra Nevada bighorn
sheep should be reduced and eventually
eliminated.
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(53) Comment: One commenter
questioned whether land use managers
would be allowed to use prescribed
burning and logging within critical
habitat.
Our Response: Prescribed burning and
logging would be considered habitatbased activities that could affect the
PCEs. Federally proposed actions would
be analyzed during the section 7
consultation process as appropriate. As
indicated in the rule, prescribed burning
can benefit Sierra Nevada bighorn sheep
by increasing visibility of the landscape.
These activities may be able to proceed
as determined during the section 7
consultation process.
(54) Comment: Sierra Nevada bighorn
sheep deaths due to tranquilization and
horns being ripped off during research
activities are a management problem.
Our Response: Since 2001, when
CDFG’s Sierra Nevada Bighorn Sheep
Recovery Program was established,
there have been 44 deaths (2 rams, 2
ewes) among the approximately 150
captures conducted to date (2.7 percent)
(Stephenson 2008, p. 1). Sierra Nevada
bighorn sheep are not tranquilized. One
ewe is known to have broken a horn
sheath (not horn) during capture
activities. Documentation of injuries or
deaths occurring during capture
activities must be provided to the
Service under CDFG’s section
10(a)(1)(A) recovery permit issued
under the Act. The reporting
documentation must describe in detail
the circumstances that led to the injury
or mortality and include a description of
the changes in activity protocols that
will be implemented to reduce the
likelihood of such an injury or mortality
from occurring again. All incidents are
reviewed by the Service and capture
procedures are changed, if necessary, to
reduce subsequent injuries or deaths.
The recovery permit allows for a
determined level of incidental take to
occur on an annual basis that will not
jeopardize the continued existence of
the species. In addition, the importance
and recovery value of information
obtained during these activities and
subsequent monitoring of Sierra Nevada
bighorn sheep is utilized in our
population management and rangewide
recovery management decisions.
Although we acknowledge that certain
levels of take may occur when
conducting authorized activities for
Sierra Nevada bighorn sheep, we make
every effort to minimize take to the
maximum extent practicable.
(55) Comment: The Special
Management Considerations and
Protection section provides no
assurances that existing development
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activities, livestock grazing, mining,
recreation, etc. can continue.
Our Response: The Special
Management Considerations or
Protection section of this rule identifies
the types of activities that could impact
the PCEs in the designated critical
habitat units. It is not meant to provide
assurances but to identify areas of
concern for Federal agencies to
determine if a proposed action may
affect Sierra Nevada bighorn sheep
habitat and should be addressed under
the section 7 consultation process.
Please also refer to our response to
Comment 28.
(56) Comment: Explicit management
recommendations for off-road vehicles
and domestic sheep grazing should be
included in the final rule.
Our Response: In the Special
Management Considerations or
Protection section, we indicate various
management activities that may affect
designated critical habitat. We
purposefully do not provide explicit
management recommendations for the
various activities so that the action
agency and the Service can determine
appropriate measures on a case-by-case
basis during the section 7 consultation
process.
(57) Comment: The purchase of
private lands should be a priority to
reduce the concern of disease
transmission from domestic to Sierra
Nevada bighorn sheep.
Our Response: There is little private
land (1,005 ac (407 ha)) within the units
designated as critical habitat. We do not
know the extent of private acreage, if
any, that provides domestic sheep or
goat grazing. The purchase of private
lands for the purposes of critical habitat
is not within the scope of this final rule;
however, purchase of private lands from
willing sellers would be an option for
recovery purposes and could, in some
areas, reduce the potential of disease
transmission from domestic to Sierra
Nevada bighorn sheep.
(58) Comment: One commenter stated
there is little definitive information or
predictive ability regarding avalanches
in almost all areas recommended as
critical habitat. The rule should reflect
real and practical activities not
speculative ones such as avalanche
control.
Our Response: We agree that it is
difficult to predict and manage
avalanche danger in many areas of the
Sierra Nevada, and we are not proposing
a comprehensive plan for control of
avalanches to protect Sierra Nevada
bighorn sheep. However, opportunistic
management of avalanche danger in
some locations may be possible (e.g., SR
120 corridor). Mortality of Sierra
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Nevada bighorn sheep from avalanches
is a real and documented threat that can
result in losses of large numbers of
individuals. We are working to buffer
the subspecies against these stochastic
losses by establishing additional
populations that spread the risk across
a larger area. We are also working to
improve winter range habitat, to reduce
winter range predation, and to increase
population sizes. The goal of these
activities is to increase use of winter
range by Sierra Nevada bighorn sheep,
so that they are not at high elevation
locations during the season of highest
avalanche danger. However, we do not
rule out the possibility of
recommending avalanche control in
areas where we believe it might be
effective in protecting some populations
that are not utilizing winter range.
(59) Comment: Sheep crossing signs
should be installed in the Tioga Pass
and June Lake Loop areas for the safety
of motorists as well as the Sierra Nevada
bighorn sheep.
Our Response: Sign placement is
outside the scope of this rule. However,
the Service is supportive of continuing
efforts to increase public awareness of
Sierra Nevada bighorn sheep.
(60) Comment: The critical habitat
overlaps existing wilderness
designations creating another layer of
bureaucracy.
Our Response: Some of the critical
habitat units do overlap portions of
wilderness; however, these two
designations do not achieve the same
goals. The Wilderness Act of 1964
created a National Wilderness
Preservation System. Federal lands
designated by Congress as ‘‘wilderness
areas’’ are to be ‘‘administered for the
use and enjoyment of the American
people in such manner as will leave
them unimpaired for future use as
wilderness, and as to provide for the
protection of these areas, the
preservation of their wilderness
character, and for the gathering and
dissemination of information regarding
their use and enjoyment as wilderness.’’
A wilderness designation prohibits
commercial enterprises; permanent
roads (with some exceptions); use of
motorized vehicles, equipment, and
boats; aircraft landing; temporary roads;
and structures or installations (with
some exceptions). It does not prohibit
activities such as some mining and
associated activities, water resource and
development and their associated
support facilities, grazing, and
recreational activities. The Wilderness
Act also did not affect the ‘‘jurisdiction
or responsibilities of the several States
with respect to wildlife and fish in the
national forests.’’ The stated purpose of
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the ESA, as amended, is, in part,
‘‘ * * * to provide a means whereby the
ecosystems upon which endangered
species and threatened species depend
may be conserved, to provide a program
for the conservation of such endangered
species and threatened species.’’ Some
activities that are permissible under the
Wilderness Act may affect the
conservation of the Sierra Nevada
bighorn sheep as indicated in our
Special Management Considerations or
Protection section. Therefore, the
designation of critical habitat provides
protections to the Sierra Nevada bighorn
sheep that a wilderness designation
does not.
(61) Comment: Manage ‘‘all suitable
historic range’’ for Sierra Nevada
bighorn sheep as events such as fire may
create landscape changes that may
encourage use in areas of historic range
not currently suitable.
Our Response: Please see our
response to Comment 36.
Comments Related to Criteria and
Methods
(62) Comment: Critical habitat should
not be reduced to avoid potential
difficulties with conflicting uses such as
domestic sheep grazing in the northern
units.
Our Response: We have not reduced
the amount of designated critical habitat
in this final rule compared to the
proposed rule due to potential conflicts
with domestic sheep grazing. Please
review the Criteria Used to Identify
Critical Habitat section, as well as our
response to Comment 39. The two herd
units in the northern area, Twin Lakes
and Green Creek, were not included in
the critical habitat designation because
they did not meet our criteria and are
not considered essential to the
conservation of the Sierra Nevada
bighorn sheep. There is scientific
uncertainty regarding whether these two
herd units can support viable herds.
There is a lack of historical evidence
indicating numbers and uncertainty
about connectivity between summer and
winter ranges. Potential conflict with
domestic sheep grazing was not a factor
for not including these two areas in the
designation.
(63) Comment: A concern was raised
regarding the use of a road in proximity
of critical habitat boundaries.
Our Response: Existing roads and the
lands under them are not considered
critical habitat. Please also refer to our
response to Comment 12.
Comments Related to Taxonomy
(64) Comment: The taxonomic
revision should not be included in a
rule on critical habitat.
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Our Response: While this rule is
primarily to designate critical habitat for
the Sierra Nevada bighorn sheep, the
Service legally and appropriately
determined to use this rulemaking
process to address and correct related
issues. The final listing rule published
on January 3, 2000 (65 FR 20),
inadvertently listed this entity as a DPS
rather than as a subspecies. We sought
to use our limited resources most
efficiently by proposing the taxonomic
revision to the Sierra Nevada bighorn
sheep with our proposed critical habitat
designation. We are revising the
scientific name for the Sierra Nevada
bighorn sheep from Ovis canadensis
californiana to Ovis canadensis sierrae
based on the current understanding of
this subspecies’ taxonomy.
(65) Comment: The taxonomic issue
was not adequately addressed in the
proposed rule.
Our Response: We have provided a
more thorough discussion of the genetic
and morphometric studies supporting
the distinctness of Sierra Nevada
bighorn sheep as compared with other
bighorn sheep populations in the
Background section of this final rule.
(66) Comment: One commenter stated
that the taxonomic question of whether
the Sierra Nevada bighorn sheep is a
unique subspecies should be answered
before proceeding with the critical
habitat designation.
Our Response: The Sierra Nevada
bighorn sheep, at listing, was thought to
be part of a larger California bighorn
sheep subspecies, Ovis canadensis
californiana. However, based on the
best scientific information available,
genetic and morphologic research now
indicates it should be classified as a
separate subspecies, O. c. sierrae. Please
see additional information provided in
the Background section of this rule. We
are aware of an unpublished
preliminary analysis performed by the
NDOA suggesting that Sierra Nevada
bighorn sheep may be part of a
continuous population of Nevada desert
bighorn sheep. This analysis is based on
microsatellite markers of samples
collected from approximately 100 desert
bighorn sheep from Nevada and
California and one Sierra Nevada
bighorn sheep from California. These
results are preliminary and limited due
to the single sample for Sierra Nevada
bighorn sheep. This analysis has not
been presented as a technical paper or
published in a peer reviewed scientific
publication. We cannot consider this as
substantial new information at this time.
Until further research is conducted
either supporting or rejecting the
suggestion that Sierra Nevada bighorn
sheep is a part of a continuous
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population of Nevada desert bighorn
sheep, we will use the best scientific
information currently available
indicating that Sierra Nevada bighorn
sheep should be classified as a separate
subspecies, O. c. sierrae.
(67) Comment: The animals found
north of Mammoth Lakes should be
declared Nelson bighorn or Nelson/
Sierra Nevada bighorn sheep hybrids.
Our Response: The commenter did
not provide any data to support this
statement, nor do we have any data to
support this statement. Please refer to
our response to Comment 66.
(68) Comment: Sierra Nevada bighorn
sheep genetic material should be
released to a third party so additional
analyses can be conducted to determine
whether this is a distinct subspecies.
Our Response: To conduct research
on a listed species, such as involving
genetic material (considered a body
part), a section 10(a)(1)(A) of the Act
permit application must be submitted to
the Service. The permitting process is
described in 50 CFR 17.22, Permits for
scientific purposes, enhancement of
propagation or survival, or for
incidental taking. Currently, only one
entity has applied for and been issued
a permit under section 10(a)(1)(A) of the
Act for research activities involving
Sierra Nevada bighorn sheep; this
permit covers several individuals and
institutions specifically listed in the
permit.
Comments Related to Legal and
Procedural Issues
(69) Comment: There is public
frustration that a lawsuit is instigating
designation of critical habitat at this
time.
Our Response: The Act requires
designation of critical habitat at the time
of listing unless not prudent or
undeterminable. We are complying with
a court approved settlement agreement
to designate critical habitat for Sierra
Nevada bighorn sheep. As indicated by
the settlement agreement, we are
required to submit to the Federal
Register a final determination of critical
habitat designation by July 17, 2008.
Please see our Previous Federal Actions
section of the rule for further details.
(70) Comment: A commenter was
concerned that the final critical habitat
designation could be expanded in the
future.
Our Response: Section 4(a)(3)(B) of
the Act provides that critical habitat
designations may, from time-to-time, be
revised. A revision can propose an
expansion or contraction of the
boundaries. Any such revision would
again be published in the Federal
Register as a proposed rule with an
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opportunity for public comment before
any such revision is made final.
(71) Comment: Why was the
designation for critical habitat for the
Sierra Nevada bighorn sheep not
completed sooner?
Our Response: Please refer to the
Previous Federal Actions section of this
final rule for additional information on
this topic.
(72) Comment: The Service must
designate sufficient critical habitat to
support the ‘‘conservation’’ and
‘‘recovery’’ of the Sierra Nevada bighorn
sheep, not just survival.
Our Response: The process of
designating critical habitat as described
in the Act requires that the Service
identify those lands on which are found
the physical or biological features
essential to the conservation of the
species that may require special
management considerations or
protection, and the areas outside the
current range of the species that are
essential for its conservation. In
identifying those lands, the Service
must consider the recovery, as well as
the survival, needs of the species. Once
critical habitat has been designated,
Federal agencies must consult with the
Service under section 7(a)(2) of the Act
to ensure that their actions will not
destroy or adversely modify designated
critical habitat or jeopardize the
continued existence of the species. As
noted in the Ninth Circuit’s Gifford
Pinchot decision, the jeopardy and
adverse modification standards are
distinct. Through the section 7(a)(2)
consultation process, critical habitat
designations provide recovery benefits
to species by ensuring that Federal
actions will not result in the destruction
or adverse modification of designated
critical habitat.
This final designation of critical
habitat identifies units that are identical
to those herd units that the recovery
plan for the Sierra Nevada bighorn
sheep identifies as necessary for
recovery. Therefore, we believe we fully
considered the recovery and survival
needs of the Sierra Nevada bighorn
sheep in this designation of critical
habitat.
(73) Comment: The four herd units
not included in the critical habitat likely
qualify as a significant portion of the
range for Sierra Nevada bighorn sheep.
If Sierra Nevada bighorn sheep are
recovered in the critical habitat, the
subspecies would still be considered
threatened or endangered in a
significant portion of its range due to
the four units not being included. The
designation ignores recommendations of
scientists that indicate that the Northern
Recovery Unit is needed for recovery
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and does not meet the recovery plan’s
objectives for reintroducing animals to
vacant herd units or for increasing the
number of herds by increasing
geographic distribution and numbers.
Our Response: The determination of a
significant portion of a species range is
not relevant to the designation of critical
habitat. Rather, it applies in the context
of listing or delisting a particular
species; therefore, we do not consider
what constitutes a significant portion of
a species range in this final designation
of critical habitat.
The recovery plan identifies four
specific measurable criteria for
delisting. Delisting Criterion B2
indicates that Sierra Nevada bighorn
sheep must occupy 12 herd units. The
recovery plan specifies 12 essential herd
units that would likely contribute to
recovery by receiving Sierra Nevada
bighorn sheep through translocation or
natural migration. The plan also
identifies four non-essential herd units
as locations that Sierra Nevada bighorn
sheep could occupy based on historical
Sierra Nevada bighorn sheep locations
and habitat characteristics. However,
the recovery plan did not identify these
four herd units as essential to recovery
because of uncertainty over whether
viable populations could persist in these
locations long-term. Three of the four
non-essential herd units are currently
unoccupied.
Because the critical habitat units and
essential herd units have the same
boundaries, we can achieve population
size and distribution recovery goals for
this species if we can establish and
maintain populations within them.
These critical habitat units are
consistent with the recovery plan’s goal
of establishing new herds in currently
unoccupied suitable habitat. Five of the
critical habitat units are currently
unoccupied, but we have designated
them as critical habitat because these
areas are essential to the establishment
of herds that are necessary for recovery
of the species.
Therefore, the recommendation for
retaining the Northern Recovery Unit
has been addressed through
identification of the Mount Gibbs and
Mount Warren essential herd units in
the recovery plan and designation of
critical habitat encompassing these two
units.
(74) Comment: The rule should be
suspended until the ‘‘required
determinations’’ have been made.
Our Response: As stated in the
proposed rule, we indicated we would
wait on the draft economic analysis to
respond to various determinations. On
February 5, 2008 (73 FR 6684), we
published the notice of availability of
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our draft economic analysis, which also
included our amended required
determinations based on the draft
economic analysis. This final rule
contains our final required
determinations which are based on the
final economic analysis of this critical
habitat designation. Please see the
Required Determinations section for
more information.
(75) Comment: The Service did not
have resumes for the peer reviewers.
Our Response: The Service solicits
opinions of independent peer reviewers
to ensure that our designations are
based on ‘‘scientifically sound data,
assumptions, and analyses.’’ Our
longstanding practice does not require
resumes to be submitted by peer
reviewers.
(76) Comment: A commenter noted
that one of the solicited peer reviewers
was included in the literature citations
for the proposed rule and questioned
whether the peer reviewer had input
during preparation of the proposed
critical habitat.
Our Response: The citation is for a
document published by the peer
reviewer in 2002. The peer reviewer did
not have input during the preparation of
the proposed critical habitat
designation. Like the public, it is
appropriate for a peer reviewer to
provide input for a final critical habitat
designation through comments on the
proposed designation.
(77) Comment: An Environmental
Impact Statement (EIS) should be
required for any proposed project which
may affect critical habitat.
Our Response: Requiring an EIS is
beyond the scope of a critical habitat
designation. The Federal action agency
will be responsible for the appropriate
level of NEPA compliance with respect
to any future proposed project. The
level of such compliance would be
determined by the action agency at that
time.
(78) Comment: A few comments were
received related to the two public
meetings and one hearing held on the
proposed critical habitat designation.
While some people expressed
appreciation of the Service’s time and
the opportunity to review maps, obtain
hand out materials, and ask questions of
Service employees one-on-one, others
wanted a formal presentation with an
opportunity to ask questions in a group
setting. One commenter objected that
public speaking time at the hearing was
limited when few people had signed up
to speak.
Our Response: Although we have
complied with the appropriate legal
requirement, we appreciate this
feedback and will continue to seek
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opportunities to share information on
Sierra Nevada bighorn sheep with the
public.
(79) Comment: Critical habitat
boundary maps should have been
overlaid on a topographic map.
Our Response: Maps published in the
Federal Register must be printed in a
simplified format. In addition, due to
the remote locations of the units, the
number of landmarks available to assist
with location descriptions is limited.
The boundary descriptions in the
Regulation Promulgation section of the
final rule indicate the specific critical
habitat unit boundaries.
(80) Comment: One commenter stated
that the Service was moving too quickly
and without having documents peer
reviewed before citing them in the
proposed critical habitat rule and DEA.
The study by Clifford et al. (2007) was
used as an example.
Our Response: As indicated in the
Critical Habitat section of this rule, we
are legally required to use the best
scientific and commercial data available
when designating critical habitat. Under
our Policy on Information Standards
Under the Endangered Species Act and
the Information Quality Act, we are able
to use information available to us as
publications in peer-reviewed scientific
journals, agency documents, reports,
etc. Many of these documents are not
peer reviewed. Our use of Clifford et al.
(2007) is not the basis for our
designation of critical habitat for this
subspecies; rather, we used it to provide
information related to assessing the risk
of and potential for a respiratory
outbreak in Sierra Nevada bighorn
sheep due to contact with domestic
sheep. Addressing the presence of
domestic sheep and grazing activities
within critical habitat relates to the
Special Management Considerations or
Protection section. Please see our
response to Comment 17.
Comments Related to Economic Issues
(81) Comment: It was requested that
the Pine Creek Mine be excluded from
the critical habitat designation for
economic, national security, and safety
issues.
Our Response: When determining
critical habitat boundaries for Sierra
Nevada bighorn sheep, we made every
effort to avoid including developed
areas such as lands covered by
buildings, paved areas, and other
structures that lack PCEs for the Sierra
Nevada bighorn sheep. The scale of the
maps prepared under the parameters for
publication within the Code of Federal
Regulations may not reflect the
exclusion of such developed areas. Any
such features and the land under them
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inadvertently left inside critical habitat
boundaries shown on the maps of this
final rule have been excluded by text in
the final rule and are not designated as
critical habitat. Therefore, Federal
actions limited to these areas would not
trigger section 7 consultation, unless
they may affect the species or PCEs in
adjacent critical habitat.
We consider activities such as new
road construction, maintenance
activities, road widening, and mining
and construction of associated facilities
as potentially impacting additional
lands not within the footprint of
existing facilities. These activities may
affect the features that may need special
management considerations or
protection within designated critical
habitat units. Federal agencies consult
under section 7 of the Act to ensure that
their proposed actions do not jeopardize
the continued existence of the Sierra
Nevada bighorn sheep or result in the
destruction or adverse modification of
its critical habitat. We have determined
that undeveloped areas of the Pine
Creek Mine are essential to the Sierra
Nevada bighorn sheep as they contain
the features essential to the conservation
of the subspecies and meet the
definition of critical habitat. Please see
the Criteria Used To Identify Critical
Habitat section for more information.
One of our objectives is to provide
consistency between critical habitat
designation and the essential habitat
indicated in the final recovery plan
(Service 2007, p. 41).
The Secretary may exclude an area
from critical habitat under section
4(b)(2) of the Act after taking into
consideration the economic impact, the
impact on national security, and any
other relevant impact if he determines
that the benefits of such exclusion
outweigh the benefits of designating
such area as critical habitat, unless he
determines that the exclusion would
result in the extinction of the species
concerned.
We have considered this request by
the commenter. We appreciate the
commenter’s willingness to continue to
work with California Department of
Game and Fish and the Service and
provide access and use of mine roads,
the helipad, and parking lots to assist
with Sierra Nevada bighorn sheep
monitoring activities. We are aware of
the revegetation of tailings piles during
the mine’s idle years which have
subsequently been used by Sierra
Nevada bighorn sheep during winter
months. We have previously consulted
with the USFS on mining associated
activities related to this mine and
determined that those activities were
not likely to adversely affect the Sierra
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Nevada bighorn sheep. Since critical
habitat has not been previously
proposed or designated for this species,
it is anticipated that the USFS will
initiate section 7 consultation as
appropriate for any new activities
proposed by the mine operators for
which action agency authorization is
required. These new activities may
include construction or modification of
escapeways and other safety facilities
and surface stations and reworking of
existing tailings piles. We will continue
to work with the USFS and the
permittee to address concerns related to
the Sierra Nevada bighorn sheep during
the section 7 consultation process as
appropriate.
According to the final EA, postdesignation baseline (due to listing)
undiscounted costs for habitat
management of which Pine Creek Mine
is a portion is estimated at $14.8 million
over the next 20 years (including
$267,000 for impacts due to mining
consultations). Post-designation
incremental undiscounted costs (due to
the designation of critical habitat) for
mining consultations are estimated to be
$14,640 over the next 20 years. These
impacts are due to the predicted section
7 consultations by the USFS to address
mining activities. Thus, costs are not
considered to be disproportionate and
we are not excluding these lands based
on economic impacts.
The commenter also requested lands
be excluded based on national security
concerns. The National Defense
Authorization Act for Fiscal Year 2004
(Pub. L. 108–136) amended section
4(a)(3)(B) of the Act (16 U.S.C.
1533(a)(3)(B)(i)) to state that the
Secretary shall not designate as critical
habitat any lands or other geographical
areas owned or controlled by the
Department of Defense, or designated
for its use, that are subject to an
integrated natural resource management
plan (INRMP) prepared under section
101 of the Sikes Act (16 U.S.C. 670a), if
the Secretary determines in writing that
such plan provides a benefit to the
species for which critical habitat is
proposed for designation. The land in
question is not Department of Defense
land and does not have an INRMP.
While the commenter provided
information on use and application of
tungsten in military applications, we do
not believe that the designation of
critical habitat will preclude the
continued operation of the Pine Creek
Mine. Additionally, a designation of
critical habitat is not likely to preclude
further development or exploration at
the mine. Any future consultations
under section 7 of the Act will include
an analysis of adverse modification of
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critical habitat as well as a jeopardy
analysis. We will continue to work with
the USFS and permittee to address
concerns related to the Sierra Nevada
bighorn sheep during the section 7
consultation process as appropriate.
Therefore, we are not excluding these
lands based on national security
concerns.
In conclusion, based on the record
before us, we are not excluding those
USFS lands on which the Pine Creek
Mine occurs that meet the definition of
critical habitat for Sierra Nevada
bighorn sheep.
(82) Comment: The economic analysis
should be conducted in a timely
manner.
Our Response: Pursuant to 50 CFR
424.19, we are not required to conduct
an economic analysis at the time critical
habitat is proposed. It would be ideal to
provide the draft economic analysis
with the proposal. However, due to the
short time frame to complete the
proposal, we were unable to do so. We
published the proposed critical habitat
designation on July 25, 2007 (72 FR
40956), invited public comment, and
held one hearing and two informational
meetings. We reopened the public
comment period on the draft economic
analysis and the proposed critical
habitat designation for 30 days
beginning on February 5, 2008 (73 FR
6684). We believe we provided adequate
time for the public to provide comment
on the proposed rule as well as the
economic analysis consistent with the
court-approved deadline for this
determination. Comments received
during the two open comment periods
and during the public hearing and
informational meetings were reviewed
and incorporated into our decision
making process as appropriate.
(83) Comment: The economic analysis
for the critical habitat designation
should show the cumulative impacts
since listing the species.
Our Response: In the economic
analysis, costs were developed as predesignation baseline, post-designation
baseline, and post-designation
incremental impacts. The predesignation baseline and the postdesignation baseline indicate the costs
of the impacts of listing of the Sierra
Nevada bighorn sheep. The postdesignation incremental impacts are
differentiated from the baseline as they
are specifically related to the critical
habitat designation. Thus, the economic
analysis does provide a cumulative
analysis of the economic impacts of
actions taken to protect the Sierra
Nevada bighorn sheep since its listing.
Please refer to the final economic
analysis for details.
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Comments Related to the Draft
Economic Analysis
Policy Issues
(84) Comment: One commenter states
that the DEA does not state that while
nearly half of the estimated economic
impacts from proposed critical habitat
are from the Mount Warren and Mount
Gibbs habitat units, the northern herd
units contain less than five percent of
the total Sierra Nevada bighorn sheep
herd population. The comment also
states that incurring these impacts
would be a futile, huge waste of money
and that the DEA should draw the same
conclusion.
Our Response: As described in the
framework of the economic analysis
(Chapter 1), the purpose of the analysis
is to estimate the economic impacts of
Sierra Nevada bighorn sheep
conservation measures as
comprehensively as possible with
publicly available data. A judgment
concerning effectiveness or efficiency of
the conservation measures that may be
required by critical habitat designation
is beyond the scope of the economic
analysis.
(85) Comment: One commenter is
concerned that the DEA does not
calculate the costs of regulatory takings.
Our Response: In accordance with
E.O. 12630 (‘‘Government Actions and
Interference with Constitutionally
Protected Private Property Rights’’), we
have analyzed the potential takings
implications of designating critical
habitat for the Sierra Nevada bighorn
sheep in a takings implications
assessment. Critical habitat designation
does not affect landowner actions that
do not require Federal funding or
permits, nor does it preclude
development of habitat conservation
programs or issuance of incidental take
permits to permit actions that do require
Federal funding or permits to go
forward. The takings implications
assessment concludes that this
designation of critical habitat for the
Sierra Nevada bighorn sheep does not
pose significant takings implications.
(86) Comment: A commenter stated
that there was not enough time provided
in the comment period. Instead of
designating critical habitat, the Service
should set up a pilot program in order
to get insight from the ranchers and
biologists together. Information from the
pilot program could then be used for
designating critical habitat.
Our Response: On October 9, 2007 (72
FR 57276), we extended the time period
for public comment on the proposed
critical habitat designation to gather
additional information. A second
comment period was opened for
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comments on the DEA and the proposed
rule on February 5, 2008 (73 FR 6684).
In our proposed rule we asked for ways
that we could improve or modify our
approach to designating critical habitat.
This could include ways to provide
greater public participation or ways to
better accommodate public concerns
and comments. We appreciate the idea
about establishing a pilot program for
public participation. We welcome
details from the commenter on the
specifics of how that could be
implemented.
(87) Comment: A few commenters
stated that the DEA does not quantify
any benefits. These benefits could be
consumptive, non-consumptive or
scenic.
Our Response: In the context of a
critical habitat designation, the primary
purpose of the rulemaking (i.e., the
direct benefit) is to designate areas that
contain the physical and biological
features that are essential to the
conservation of listed species. The
designation of critical habitat may result
in two distinct categories of benefits to
society: (1) Use; and (2) nonuse benefits.
Use benefits are simply the social
benefits that accrue from the physical
use of a resource. Visiting critical
habitat to see endangered species in
their natural habitat would be a primary
example. Non-use benefits, in contrast,
represent welfare gains from the
knowledge that a particular listed
species’ natural habitat is being
specially managed for the survival and
recovery of that species. Both use and
non-use benefits may occur
unaccompanied by any market
transactions.
A primary reason for conducting this
economic analysis is to provide
information regarding the economic
impacts associated with a proposed
critical habitat designation. Section
4(b)(2) of the Act requires the Secretary
to designate critical habitat based on the
best scientific data available after taking
into consideration the economic impact,
and any other relevant impact, of
specifying any particular area as critical
habitat. Economic impacts can be both
positive and negative and, by definition,
are observable through market
transactions.
Under Executive Order 12866 (E.O.
12866), Office of Management and
Budget (OMB) directs Federal agencies
to provide an assessment of both the
social costs and benefits of proposed
regulatory actions. OMB’s Circular A–4
distinguishes two types of economic
benefits: Direct benefits and ancillary
benefits. Ancillary benefits are defined
as favorable impacts of a rulemaking
that are typically unrelated, or
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secondary, to the statutory purpose of
the rulemaking. In the context of critical
habitat, the primary purpose of the
rulemaking (i.e., the direct benefit) is to
assist in the conservation of the species.
The published economics literature has
documented that social welfare benefits
can result from the conservation of
endangered and threatened species. In
its guidance for implementing E.O.
12866, OMB acknowledges that it may
not be feasible to monetize, or even
quantify, the benefits of environmental
regulations due to either an absence of
defensible, relevant studies or a lack of
resources on the implementing agency’s
part to conduct new research. Rather
than rely on economic measures, the
Service believes that the direct benefits
of the proposed rule are best expressed
in biological terms that can be weighed
against the expected cost impacts of the
rulemaking.
Critical habitat designation may also
generate ancillary benefits. Critical
habitat aids in the conservation of
species specifically by protecting the
primary constituent elements on which
the species depends. Critical habitat
designation can result in maintenance of
particular environmental conditions
that may generate other social benefits
aside from the preservation of the
species. Management actions
undertaken to conserve a species or
habitat may have coincident, positive
social welfare implications, such as
increased recreational opportunities in a
region. While they are not the primary
purpose of critical habitat, these
ancillary benefits may result in gains in
employment, output, or income that
may offset the direct, negative impacts
to a region’s economy resulting from
actions to conserve a species or its
habitat.
It is often difficult to evaluate the
ancillary benefits of critical habitat
designation. To the extent that the
ancillary benefits of the rulemaking may
be captured by the market through an
identifiable shift in resource allocation,
they are factored into the overall
economic impact assessment in the EA.
Where data are available, the analysis
attempts to capture the net economic
impact (i.e., the increased regulatory
burden less any discernable offsetting
market gains) of species conservation
efforts imposed on regulated entities
and the regional economy.
General Methodology
(88) Comment: A commenter states
that it is not feasible to do an economic
analysis without preparing
environmental impact statements
because the inability of the DEA to
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predict future restrictions makes the
report too vague.
Our Response: The best predictions
possible concerning conservation efforts
and their impacts have been provided,
based on multiple interviews with key
stakeholders and review of the publicly
available data. Legally, an EIS is not
required for this purpose.
(89) Comment: One commenter states
that the DEA does not estimate the true
cost of not allowing grazing on a Federal
grazing allotment and deliberately
understates the value of an AUM. The
commenter asserts that provided
documentation proves that this is true.
Our Response: Additional detail has
been added to the DEA to address the
concerns raised in this comment.
Section 2.1.4 has been substantially
extended; the section now provides a
more detailed explanation of how
valuing public grazing AUMs at the
market rate is the most appropriate
economic methodology and is the
method that is most commonly used as
well. A more recent value of grazing
value (the 2007 market rate of $16.50) is
provided; the economic estimates have
been updated to include this new
information. Section 2.1.4 also discusses
other AUM valuation methodologies
(cited in the provided information
referenced in the comment) and shows
how these methodologies do not
measure the resource value (which the
market rate does), how estimates based
on these methodologies are highly
dependent on the specific sample that is
used to create them, and how different
assumptions and different studies can
produce substantially different
estimates of AUM values for ranches in
the same general vicinity. Exhibit 2–3
shows that the value of an AUM from
these studies, using the same
methodology, generates values from
$2.41 to $84 per AUM. Section 2.6 has
been added to address the limitations of
the valuation methods in Chapter 2. A
technical appendix (Appendix D) has
also been added to the DEA to provide
greater detail on how the grazing
impacts were calculated, and to explain
why some information in the
documentation referenced in the
comment was not used in the writing of
Chapter 2.
(90) Comment: A commenter states
that if formerly available Federal
allotments are not able to be grazed,
then the rancher will have to sell the
band of sheep and will not be able to
ranch anymore. The commenter asserts
that the grazing restrictions may drive
the rancher out of business. The
commenter asserts that provided
documentation proves that this is true.
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Our Response: Additions to Section
2.1.4 address this concern. The last four
paragraphs of Section 2.1.4 explain how
one of the research papers listed in the
provided documentation provides
information that finds that reductions of
up to 30 percent in Federal grazing
AUMs can be sustained by Northern
Nevada ranches without affecting ranch
profitability. The ranch experiencing
Federal grazing AUM reductions, as
discussed in Section 2.1.4, has a
maximum estimated reduction of 11
percent.
(91) Comment: Several comments
state that the DEA does not present an
analysis of how the grazing restrictions
will affect the larger economy. One of
these comments states that
documentation provided for the analysis
shows what these impacts would be.
This comment states that the DEA does
not properly account for the
expenditures of the rancher that grazes
in areas proximate to the Sierra Nevada
bighorn sheep and that the analysis does
not address the impact of how smaller
herd sizes would affect the economies of
Mono and Inyo Counties. One comment
specifically asks where IMPLAN has
been used in the analysis.
Our Response: To address the
concerns raised by these comments, a
regional analysis of the impacts of Sierra
Nevada bighorn sheep related
reductions in Federal grazing is
provided in Section 2.5. This analysis
uses IMPLAN, a widely used
methodological tool (called an ‘‘InputOutput’’ model) used for regional
economic analysis to perform the
analysis for Mono and Inyo Counties.
The results indicate that the $261,000
yearly loss of grazing value in Mono
County results in additional losses of
$70,696 per year in that county. The
$14,000 grazing value reductions in
Inyo County results in an additional
yearly $4,445 of indirect and induced
impacts to be lost. Section 2.5 also
explains how the results of the regional
analysis represent a change in the
distribution of economic activity but do
not measure the net effect on that
activity (adjustments are made to
behavior following the grazing
restrictions that regional analysis can
not measure). The section explains that
while the IMPLAN results are valid for
a distributional analysis, they are not
measures of economic welfare change
and, therefore, are inappropriate to
include with the welfare analysis
measures that are the main subject of
the DEA. This issue is also discussed in
Section 1.2.2.
(92) Comment: One commenter states
that the DEA does not forecast the
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impacts of grazing restrictions far
enough into the future.
Our Response: Section 1.3.5 of the
analysis explains that the standard for
the analysis is to forecast land uses that
are reasonably foreseeable, which is
within a 20-year span. This forecasting
period is applied equally to all parts of
the report.
(93) Comment: One commenter states
that not all impacts that were listed in
supplied documents are included in the
DEA.
Our Response: Appendix D has been
added to clarify what information was
used in the grazing chapter estimation
and how the information was used.
Section D–1 provides information about
how conservation effort impact
information in the provided
documentation was used and how
calculations were made. Section D–2
discusses information from the provided
documentation that was not used
because it was either unuseable (as
detailed in Exhibit D–2) or because the
DEA already estimates the impacts
provided in the documentation.
(94) Comment: One commenter states
that the DEA should quantify the
benefits to users of the watershed,
consumers of water from the watershed,
and the costs that Federal Agencies
incur in managing the grazing if grazing
is discontinued in the Forest Service
allotments.
Our Response: The economic impacts
discussed in Section 2.3 are those
impacts that would be due to a
continuation of the policies that are
currently in place; no estimation of
benefits for additional closures is
warranted.
(95) Comment: A commenter stated
that the opportunity cost of forage
values are incorrectly measured. The
commenter stated that the public
grazing price ($1.35 per AUM) should
be used to measure the lost opportunity
cost of grazing on allotments instead of
the private market price. The comment
then states that the DEA should have
used the Nevada private market grazing
price.
Our Response: Section 2.1.4 has been
expanded to address this concern. More
details on the use and rationale for
market rate valuation are provided, as
well as citations concerning the use of
the methodology by other Federal
agencies. The estimates for grazing have
been updated with the 2007 average
grazing value in California from the
National Agricultural Statistics Service.
Since the grazing allotments are in
California, and not Nevada, it is more
appropriate to use the California AUM
price.
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(96) Comment: Several comments
expressed concern that the DEA did not
provide more information or estimates
about future potential restrictions on
recreation activities that may result from
critical habitat designation. These
comments stressed the importance of
recreation activities to the local
economies.
Our Response: Section 4.1 explains
how no public agency (Federal or State)
that is involved with the management of
Sierra Nevada bighorn sheep habitat can
predict any potential restriction on
recreational activities at this time.
Section 4.1.1 has been added to address
the importance of recreation and
tourism to the counties where proposed
critical habitat is located. Exhibit 4–1
has been added to provide specific
information about the number and size
of recreation and tourist businesses and
the percentage of employment in these
industries. Section 4.5 has been added
to address the uncertainty that is part of
the analysis because no predictions
about restrictions can be made at this
time.
(97) Comment: One commenter stated
that only one packer was contacted and
asked about the impacts of permitting
on pack operations. The comment asks
for more details on who was contacted
and questions whether a representative
sample of each area was questioned.
The comment states that there is only
one pack outfitter in Virginia Lakes.
Our Response: To respond to the
concerns raised in this comment, an
additional source was contacted. This
source confirmed that no direct impacts
of Sierra Nevada bighorn sheep
conservation on pack outfit permitting
could be estimated. This source also
provided information on the revenues of
pack outfit operations in Inyo and Mono
counties, which have been included in
Section 4.1.1.
(98) Comment: One commenter stated
that the estimated impacts in Chapter 4
(recreation) do not specify a caveat that
the estimates of total forecast impacts
could be wrong by orders of magnitude
if some currently unanticipated
restriction is put in place.
Our Response: The DEA cannot
provide economic impact estimates for
events that cannot be predicted.
However, to respond to the concerns of
the commenter, Section 4.1.1 was added
to include recreation related
employment and revenue statistics for
the potentially affected counties. The
chapter now provides information that
shows the importance of recreation to
the local economy. Section 4.5 has also
been added to address how the
uncertainty about future conservation
measures is a limitation to the analysis.
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(99) Comment: One commenter states
that the Avocet Tungsten Mine has
clearance to resume mining operations
this year and plans to do so. The
comment reiterates the value of the ore
and its strategic importance.
Our Response: This comment
contains new information. In response
to the comment, Service Field Office
personnel were contacted and potential
conservation measures were forecast.
Section 3.1.3 now includes a discussion
of these measures, estimates of the costs
of their implementation, and estimates
of the costs for predicted consultations.
(100) Comment: Several commenters
asked for more details on the grazing
portion of the economic analysis, and
how it was performed. More
information on the streams of costs and
benefits was requested.
Our Response: Appendix D has been
added to address these concerns. This
appendix describes the data sources and
explains the calculations in great detail.
(101) Comment: One commenter
asked for the basis of the discount rates
used.
Our Response: The discount rates
used are those suggested by the Office
of Management and Budget Circular A–
4 which provides guidance on
performing economic regulatory
analysis. This information is now
included in Appendix D.
(102) Comment: One commenter
stated that ‘‘actions that eliminate
ranchers as residents of these
rangelands’’ would increase risks
because illegal activity would spread
and grow in the forest if the sheep
ranchers were not there.
Our Response: There are no publicly
available models or data to show that an
economic loss may result in increased
illegal activity in that area. If there are
minimal impacts on ranch profitability,
as suggested in the conclusion to
Section 2.1.4, such results are less
likely.
(103) Comment: One commenter
stated that Mono County is concerned
that a grazing allotment lease they have
may be affected.
Our Response: The DEA includes
information on all of the grazing
restrictions that can be predicted at this
time. No Mono County leases are known
to be considered for restrictions at this
time. These allotments occur on County
lands. They would not be affected by
the critical habitat designation unless a
Federal nexus applies, such as where a
landowner requests Federal agency
funding or authorization of an action.
Please see the Critical Habitat section of
this rule.
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(104) Comment: One commenter
asked how many AUMs are restricted in
the grazing chapter.
Our Response: This information is
provided in Exhibit 2–2. Appendix D
has been added to explain how the
AUM forage values foregone were
calculated.
(105) Comment: One commenter
stated that the incremental impacts of
potential yearly consultation on grazing
for Humboldt-Toiyabe (HT) National
Forest allotments over-estimate the true
impacts because there are likely to be
fewer consultations, and HT may decide
to close grazing on those allotments
regardless.
Our Response: As discussed in
Section 2.1.3, there have been yearly
section 7 consultations for grazing in HT
each year from 2004 to 2007. These
yearly consultations are not expected to
stop. Contact with the HT officials
indicates that yearly consultation is the
most probable outcome, rather than
allotment closure (see footnote 31). The
basis for allocating a portion of the
section 7 consultation costs as
incremental impacts is described in
Section 1.3.2 and illustrated in Exhibit
1–2.
(106) Comment: One commenter
stated that the research costs and
litigation costs incurred by the sheep
grazers should not be included in the
analysis.
Our Response: The legal and research
costs discussed in Section 2.1.3 are
indirect costs associated with the
species listing. Quantification of
indirect impacts is discussed in section
1.3.2. Appendix D has been added to
provide information about which
conservation related expenditures for
grazing were used in the analysis and
which were not.
(107) Comment: A commenter stated
that there is no basis for the
‘‘administrative costs for complying
with regulations’’ provided.
Our Response: This information was
based on reported activity levels by the
affected sheep raiser. This sheep raiser
reported the effort level and wage, and
reported a total that did not correspond
to the effort level and wage. The
estimate is provided in Exhibit 2–1, and
the explanation in Note #2 provides
details about how this estimate was
calculated. Appendix D has been added
to provide information about which
conservation related expenditures for
grazing were used in the analysis and
which were not.
(108) Comment: One commenter
stated that there is no reference or
explanation given for stress induced
weight loss among lambs.
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Our Response: Section 2.1.3 discusses
this problem, but does not specify how
it is calculated or what the source is.
Appendix D has been added to provide
information about which conservation
related expenditures for grazing were
used in the analysis and how they were
used.
(109) Comment: One commenter
asked that all computer software used
that is more extensive than simple Net
Present Value calculations be provided.
Our Response: The economic analysis
also uses ArcGIS, and IMPLAN, which
are both commercially available
software packages.
dwashington3 on PRODPC61 with RULES2
Summary of Changes From Proposed
Rule
In preparing the final critical habitat
designation for Sierra Nevada bighorn
sheep, we reviewed and considered
comments from peer reviewers and the
public on the proposed designation
published on July 25, 2007 (72 FR
40956), and the draft economic analysis
published on February 5, 2008 (73 FR
6684). This final rule differs from the
proposed rule in that we made changes
in the following sections of the
proposed rule: Background, Previous
Federal Actions, Primary Constituent
Elements, Special Management
Considerations or Protection, Criteria
Used to Identify Critical Habitat, Critical
Habitat Designation, and Regulation
Promulgation. These changes included
corrections, new information, or
clarifications. Changes included
clarifying Sierra Nevada bighorn sheep
biology; adding information on bighorn
sheep taxonomy; updating information
about the latest Federal actions related
to Sierra Nevada bighorn sheep;
updating reference to the Service’s final
recovery plan and its information;
clarifying the Primary Constituent
Elements for Sierra Nevada bighorn
sheep; adding information related to the
effects of disease transmission to
bighorn sheep; including cattle in
livestock grazing issues; adding
information on recreational activities
and possible habituation by bighorn
sheep; deleting unsuitable references
related to disease issues; correcting a
landmark used in unit descriptions;
clarifying language used with PCEs and
special management considerations or
protection; and changing the indicated
historic range from U.S.A. (western
conterminous States), Canada, (southwest), Mexico (north) to U.S.A. (CA)—
Sierra Nevada due to the change from its
range as a DPS of the subspecies Ovis
canadensis californiana to its range as
its own subspecies Ovis canadensis
sierrae.
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Critical Habitat
Critical habitat is defined in section 3
of the Act as:
(i) The specific areas within the
geographical area occupied by a species
at the time it is listed in accordance
with the Act, on which are found those
physical or biological features
(a) Essential to the conservation of the
species and
(b) Which may require special
management considerations or
protection; and
(ii) Specific areas outside the
geographical area occupied by a species
at the time it is listed, upon a
determination that such areas are
essential for the conservation of the
species.
Conservation, as defined under
section 3 of the Act, means the use of
all methods and procedures that are
necessary to bring any endangered or
threatened species to the point at which
the measures provided under the Act
are no longer necessary. Such methods
and procedures include, but are not
limited to, all activities associated with
scientific resources management such as
research, census, law enforcement,
habitat acquisition and maintenance,
propagation, live trapping,
transplantation, and in the
extraordinary case where population
pressures within a given ecosystem
cannot otherwise be relieved, may
include regulated taking.
Critical habitat receives protection
under section 7 of the Act through the
prohibition against Federal agencies
carrying out, funding, or authorizing the
destruction or adverse modification of
critical habitat. Section 7(a)(2) of the Act
requires consultation on Federal actions
that may affect critical habitat. The
designation of critical habitat does not
affect land ownership or establish a
refuge, wilderness, reserve, preserve, or
other conservation area. Such
designation does not allow the
government or public to access private
lands. Such designation does not
require implementation of restoration,
recovery, or enhancement measures by
private landowners. Where a landowner
requests federal agency funding or
authorization for an action that may
affect a listed species or critical habitat,
the consultation requirements of section
7(a)(2) would apply.
For inclusion in a critical habitat
designation, the habitat within the
geographical area occupied by the
species at the time of listing must
contain the physical or biological
features that are essential to the
conservation of the species, and be
included only if those features may
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require special management
considerations or protection. Critical
habitat designations identify, to the
extent known using the best scientific
data available, habitat areas that provide
essential life cycle needs of the species
(i.e., areas on which are found those
physical and biological features laid out
in the appropriate quantity and spatial
arrangement for the conservation of the
species). Under the Act, we can
designate critical habitat in areas
outside the geographical area occupied
by the species at the time it is listed as
critical habitat only when we determine
that those areas are essential for the
conservation of the species.
Section 4 of the Act requires that we
designate critical habitat on the basis of
the best scientific and commercial data
available. Further, our Policy on
Information Standards Under the
Endangered Species Act (published in
the Federal Register on July 1, 1994 (59
FR 34271)), the Information Quality Act
(section 515 of the Treasury and General
Government Appropriations Act for
Fiscal Year 2001 (Pub. L. 106–554; H.R.
5658)), and our associated Information
Quality Guidelines provide criteria,
establish procedures, and provide
guidance to ensure that our decisions
are based on the best scientific data
available. They require our biologists, to
the extent consistent with the Act and
with the use of the best scientific data
available, to use primary and original
sources of information as the basis for
recommendations to designate critical
habitat.
When we are determining which areas
should be designated as critical habitat,
our primary source of information is
generally the information developed
during the listing process for the
species. Additional information sources
may include the recovery plan for the
species, articles in peer-reviewed
journals, conservation plans developed
by States and counties, scientific status
surveys and studies, biological
assessments, or other unpublished
materials and expert opinion or
personal knowledge.
Habitat is often dynamic, and species
may move from one area to another over
time. Furthermore, we recognize that
critical habitat designated at a particular
point in time may not include all of the
habitat areas that we may later
determine are necessary for the recovery
of the species. For these reasons, a
critical habitat designation does not
signal that habitat outside the
designated area is unimportant or may
not promote the recovery of the species.
Areas that support populations, but
are outside the critical habitat
designations, will continue to be subject
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to conservation actions. They are also
subject to the regulatory protections
afforded by the section 7(a)(2) jeopardy
standard, as determined on the basis of
the best available scientific information
at the time of the federal agency action.
Federally funded or permitted projects
affecting listed species outside their
designated critical habitat areas may
still result in jeopardy findings in some
cases. Similarly, critical habitat
designations made on the basis of the
best available information at the time of
designation will not control the
direction and substance of future
recovery plans, habitat conservation
plans (HCPs), or other species
conservation planning efforts if
information available at the time of
these planning efforts calls for a
different outcome.
dwashington3 on PRODPC61 with RULES2
Primary Constituent Elements
In accordance with section 3(5)(A)(i)
of the Act and the regulations at 50 CFR
424.12, in determining which areas
occupied by the species at the time of
listing to designate as critical habitat,
we consider the physical or biological
features essential to the conservation of
the species that may require special
management considerations or
protection. We consider the physical or
biological features to be the PCEs laid
out in the appropriate quantity and
spatial arrangement for the conservation
of the species. The PCEs include, but are
not limited to:
(1) Space for individual and
population growth and for normal
behavior;
(2) Food, water, air, light, minerals, or
other nutritional or physiological
requirements;
(3) Cover or shelter;
(4) Sites for breeding, reproduction,
and rearing (or development) of
offspring; and
(5) Habitats that are protected from
disturbance or are representative of the
historic, geographical, and ecological
distributions of a species.
We derive the specific PCEs required
for Sierra Nevada bighorn sheep from its
biological needs.
Space for Individual and Population
Growth and for Normal Behavior
In general, Sierra Nevada bighorn
sheep inhabit open areas where the land
is rocky, sparsely vegetated, and
characterized by steep slopes and
canyons (Wehausen 1980, p. 81; Sierra
Nevada Bighorn Sheep Interagency
Advisory Group 1997, p. 5). In the
Sierra Nevada, these bighorn sheep
occur within a wide range of elevations,
from alpine peaks in excess of 14,100 ft
(4,300 m) to the base of the eastern
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escarpment as low as 4,790 ft (1,460 m)
(Wehausen 1980, pp. 3 and 82). Recent
modeling efforts (Johnson et al. 2005)
have clarified and supported our
knowledge that Sierra Nevada bighorn
sheep habitat occurs as low as 4,000 ft
(1,219 m) in the southern portion of its
range. Within this elevational range, a
variety of vegetation communities
exists, including: (1) Great Basin
sagebrush-bitterbrush-bunchgrass scrub;
(2) pinyon-juniper woodland and
mountain mahogany scrub; (3) midelevation and subalpine forests,
woodlands, and meadows; and (4)
alpine meadows and other alpine
habitats varying from cliffs to plateaus
(Service 2007, p. 3). Sierra Nevada
bighorn sheep prefer Great Basin scrub
and alpine communities due to their
visual openness. Because of the aridity
of the eastern slope of the Sierra
Nevada, many of the mid-elevation
vegetation communities have some
locations near precipitous rocks with
sparse plant cover that allow use by
bighorn sheep (Wehausen 1980, pp. 18–
25, 80–100). The extreme visual
openness and the steep, rocky nature of
alpine environments in the Sierra
Nevada provide large expanses of
habitat broken by canyons containing
forests and willow stands. These areas
of forests and willow stands are unlikely
to be used by bighorn sheep. In contrast,
low elevation winter habitat has been
limited to small areas where
topographic and visual features are
suitable (Riegelhuth 1965, pp. 34–38;
McCullough and Schneegas 1966, pp.
71–72, 74–75; Wehausen 1979, pp. 36–
53; 1980, pp. 81–88). Large expanses
lacking precipitous escape terrain can
represent substantial barriers to
movement (Sierra Nevada Bighorn
Sheep Interagency Advisory Group
1997, p. 5).
Male and female bighorn sheep
commonly live in separate groups
during much of the year, and often
occupy different habitats (Geist and
Petocz 1977, pp. 1,802–1,803; Bleich et
al. 1997, pp. 7–14, 22–34, 36–42;
Wehausen 1980, p. 109). In the Sierra
Nevada, both sexes may share common
winter ranges, but they become more
segregated as spring nears (Wehausen
1980, pp. 112–113). During winter,
bighorn sheep occupy high, windswept
ridges if forage is available or move to
lower elevation sagebrush-steppe
habitat (as low as 4,790 ft (1,460 m)) to
escape deep winter snows and find
nutritious forage. In winter, they show
a preference for south-facing slopes
where snow melts more readily (Jones
1950, pp. 44–45; McCullough and
Schneegas 1966, p. 71; Wehausen 1980,
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pp. 86–87). During summer, the two
sexes utilize different habitats, with
females restricted largely to alpine
environments along the crest and males
often at somewhat lower elevations in
subalpine habitats (Wehausen 1980, pp.
112–113). Males again join females
during the breeding season in late fall.
Both males and females will inhabit
open slopes where the area is rough,
rocky, sparsely vegetated, and
characterized by steep slopes and
canyons (Wehausen 1980, p. 81; Sierra
Nevada Bighorn Sheep Interagency
Advisory Group 1997, p. 5).
An indication of winter and summer
range size for male and female Sierra
Nevada bighorn sheep was provided by
Wehausen (1980) and Chow (1992).
Wehausen (1980, p. 84) determined
winter and summer range sizes for the
Baxter and Williamson herds. He
estimated that total winter range was 4.1
sq mi (10.65 sq km) and 5.1 sq mi (13.32
sq km), respectively. Summer range for
ewes, lambs, and yearlings was
estimated at 20.3 sq mi (52.63 sq km)
and 5.9 sq mi (15.41 sq km),
respectively. Fall range was estimated at
17.3 sq mi (44.81 sq km) and 5.1 sq mi
(13.12 sq km), respectively. Chow (1992,
p. 37) estimated home range size for the
Lee Vining herd (winter/spring and
summer/fall for rams and ewes) using
the minimum convex polygon method
(i.e., completely enclose all data points
by connecting the outer locations in
such a way as to create a convex
polygon) from 1986 to 1989. During this
period, ewes covered an area of 1.6 to
7.0 sq mi (4.2 to 18.1 sq km) during
winter/spring, and rams covered an area
of 4.6 to 10.8 sq mi (11.9 to 28.0 sq km).
During this same period, ewes covered
3.7 to 8.6 sq mi (9.5 to 22.4 sq km)
during summer/fall while rams covered
5.7 to 13.7 sq mi (14.7 to 35.4 sq km).
The mean minimum convex polygon
home range was 12.1 sq mi (31.4 sq km)
for ewes and 32.8 sq mi (84.9 sq km) for
rams from Mount Warren/Mount Gibbs,
Wheeler, Sawmill, and Baxter herds
(Sierra Nevada Bighorn Sheep Recovery
Program 2004, pp. 9, 17).
Bighorn sheep have developed
philopatric behaviors (reluctance to
disperse from their home range) such
that they are slow to colonize
unoccupied habitat (Geist 1971, pp. 98–
99; Cowan and Geist 1971, p. 81). This
is likely an adaptation to the naturally
fragmented habitats that bighorn sheep
occupy. Both male and female Sierra
Nevada bighorn sheep demonstrate
seasonal philopatry (Sierra Nevada
Bighorn Sheep Recovery Program 2004,
p. 7). While both males and females
show a tendency to use the same ranges
year after year, males show exceptions
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and demonstrate long-distance
movements (Sierra Nevada Bighorn
Sheep Recovery Program 2004, p. 7).
Annual home range diameter provides
an indication of the extreme distances
bighorn sheep can travel. Maximum
diameters for home ranges for female
Sierra Nevada bighorn sheep from the
Mount Warren/Mount Gibbs, Wheeler,
and Baxter herds ranged from 3.95 to
10.41 mi (6.35 to 16.75 km); males from
the Mount Warren/Mount Gibbs,
Wheeler, and Sawmill herds ranged
from 5.5 to 36.9 mi (8.9 to 59.4 km)
(Sierra Nevada Bighorn Sheep Recovery
Program 2004, pp. 9, 17).
Bighorn sheep exhibit a variety of
behavioral adaptations to avoid
predation. Bighorn sheep are primarily
diurnal (Jones 1950, pp. 54–57;
Krausman et al. 1985, pp. 24–26).
Coupled with their strong reliance on
keen eyesight to detect predators,
diurnal behavior minimizes predation
risks. Due to their keen eyesight and
agility on rocky slopes, bighorn sheep,
in general, select open habitats that
allow predator detection at distances
great enough to allow time to reach
steep, rocky terrain (escape habitat)
(Wehausen 1980, p. 81). This
precipitous, rocky terrain is generally
near foraging and resting areas. Bedding
areas are needed for resting or sleeping
purposes. During the day, bedding areas
are generally wherever the individual is
feeding. Bedding areas are made in the
open but not necessarily in a place with
a view of the surrounding area; during
the night, bedding areas are generally
among or near rugged, chuted cliffs
(Jones 1950, p. 49). Bighorn sheep may
venture a short distance away from
rocky escape terrain to feed; the
distance they venture from safer habitat
varies and is apparently influenced by
visual openness, wind, gender, season,
and abundance of predators (Service
2007, p. 5).
Sites for Breeding, Reproduction, and
Rearing of Offspring
In the Sierra Nevada, ewes and rams
come together in late fall or early winter
(November and December) (Jones 1950,
pp. 63–64; Cowan and Geist 1971, p. 64;
Wishart 1978, p. 165) to breed, usually
at high elevations. Bighorn sheep
generally give birth to single young
(Wishart 1978, p. 165). Most bighorn
sheep births in the Sierra Nevada occur
in May and June (Wehausen 1980, p. 94;
1996, p. 475). Lambing habitat is in
areas of precipitous rocks away from
trees (Wehausen 1980, p. 95), providing
safe areas from predators. Ewes with
newborn lambs are solitary for a short
period of time before joining nursery
groups.
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Mortality Factors
Bighorn sheep die from a variety of
causes including predation, disease, and
accidents. Various predators, including
wolves (Canis lupus), mountain lions
(Felis concolor), coyotes (Canis latrans),
bobcats (Lynx rufus), and golden eagles
(Aquila chrysaetos) kill wild sheep in
North America (Cowan and Geist 1971,
p. 75; Bleich 1999, p. 283). Jones (1950,
pp. 67–68) listed golden eagles,
mountain lions, coyotes, wolverines
(Gulo luscus), bobcats, and ravens
(Corvus corax) as likely predators of
Sierra Nevada bighorn sheep, but
thought none of these predators caused
anything except small losses on the
population under normal
circumstances. He thought predation
overall was light except during
abnormally unfavorable winters. In
recent years in the Sierra Nevada,
mountain lions have been the primary
predator of bighorn sheep, accounting
for 96 percent of losses attributed to
predation (Service 2007, p. 9). Of 147
bighorn sheep deaths recorded in the
Sierra Nevada from 1975 to 2000, a
minimum of 54.5 percent could be
attributed to predation (Service 2007, p.
9).
Numerous diseases of bighorn sheep
have been documented (Bunch et al.
1999, pp. 209–237). Bighorn sheep show
a high susceptibility to pneumonia,
usually caused by bacteria of the genus
Pasteurella (some species now called
Mannheimia) (Post 1971, pp. 98–101).
Pneumonia caused by Pasturella alone,
or with other pathogens, is an important
disease threat for bighorn sheep (Bunch
et al. 1999, p. 210). Lungworms of the
genus Protostrongylus can be important
contributors to pneumonia and
mortality in bighorn sheep in the Rocky
Mountains (Forrester 1971, p. 158;
Woodard et al. 1974, pp. 773–774).
Bighorn in the Sierra Nevada carry
Protostrongylus lungworms, but parasite
loads have been too low to be
considered a management concern
(Wehausen 1980, p. 191).
Although die-offs of bighorn sheep
due to disease have occurred unrelated
to domestic sheep (Miller et al. 1991,
pp. 534–540), a substantial amount of
circumstantial evidence is available that
indicates that contact with domestic
sheep is associated with respiratory
disease outbreaks resulting in
significant morbidity and mortality in
wild bighorn sheep (Martin et al. 1996,
pp. 72, 74). The history of bighorn sheep
in the United States provides numerous
examples of major die-offs following
believed contact with domestic sheep
(Foreyt and Jessup 1982, pp. 163–164,
166; Singer et al. 2001, p. 1,352; Coggins
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45555
2002, pp. 166–170), and these
pneumonia epizootics can extirpate
entire populations (Martin et al. 1996,
pp. 72, 75). Experimental evidence
indicates that bighorn sheep can suffer
mortality from pneumonia after being in
contact with domestic sheep (Foreyt
1989, p. 342; Callan, et al. 1991, pp.
1,054–1,055). Diseases transferred
through contact with domestic sheep are
suspected to have played a major role in
the disappearance of certain bighorn
sheep herds in the Sierra Nevada
beginning about 1870 (Wehausen 1988b,
p. 100).
The outcome of contact between the
two species likely depends on the
exposure history and immunity status of
both species. The onset of pneumonia in
affected bighorn sheep may be delayed
by days or weeks after the initial contact
with domestic sheep, and the problem
may not be detected for months after
infection in isolated bighorn sheep
herds. Those individuals that survive,
especially wandering rams, can transmit
pathogens to nearby populations. Lambs
born to surviving ewes can experience
low survival rates for 3 to 5 years after
the initial outbreak (Foreyt 1990, p. 100;
Coggins and Matthews 1992, Ward et al.
1992, Foreyt 1995, Hunter 1995a cited
in Schommer and Woolever 2001, p. 3).
It is not possible to predict which
contacts with domestic sheep might
result in disease transmission to bighorn
sheep, nor which bighorn sheep
individuals could be susceptible.
Contact can occur due to stray domestic
sheep entering bighorn sheep habitat, or
bighorn sheep coming into contact with
domestic sheep.
Many early die-offs of bighorn sheep,
including some in the Sierra Nevada,
were attributed to scabies contracted
from domestic sheep (Jones 1950, p. 69;
Buechner 1960, p. 111). In 1987, Clark
et al. (1988, p. 13) found scabies in three
desert bighorn sheep in California east
of the Sierra Nevada. In a large sampling
of 50 populations of bighorn sheep in
California between 1980 and 1990, 25
populations were designated as scabiespositive because at least one
seropositive animal occurred at the low
or high cutoff values, though no clinical
evidence of scabies was noted (Mazat et
al. 1992, pp. 543–545).
Other infectious diseases may be of
concern for bighorn sheep in selected
instances. Domestic goats are
occasionally used as pack animals in the
back country or for brush control. This
use could cause concern if it occurs in
or near bighorn sheep habitat. For
example, a recent outbreak of infectious
keratoconjunctivitis (inflammation of
the eye) linked to domestic goats
resulted in blindness and several deaths
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(exacerbated by the blindness) in
bighorn sheep in Arizona,
demonstrating the risk of disease
outbreak in bighorn sheep from
interactions with domestic goats
(Heffelfinger 2004, cited in Sierra
Nevada Bighorn Sheep Recovery
Program 2004, p. 2).
Sierra Nevada bighorn sheep
remaining at high elevations year-round
likely contributed to population losses
over winter (Wehausen 1996, pp. 474–
477). Those losses included losses in
snow avalanches (Service 2007, p. 10).
A survey of the Wheeler Ridge herd
during the heavy winter of 1995 found
12 sheep had died in a single snow
avalanche (Torres et al. 1996, p. 28).
Metapopulation Structure
Within mountain ranges like the
Sierra Nevada, bighorn sheep habitat is
patchy and the population structure is
one of natural fragmentation (Bleich et
al. 1990, p. 384). This fragmentation has
led to the application of a broad
landscape approach to their population
ecology which groups geographically
distinct herds into metapopulations, or
networks of interacting herds (Schwartz
et al. 1986, pp. 182–183; Bleich et al.
1990, p. 386). This approach considers
long-term viability not of individual
herds but rather of entire
metapopulations; thus, both genetic and
demographic factors are considered.
Decreasing population sizes, over time,
can lead to decreasing levels of
heterozygosity (presence of different
forms of a gene at a particular location
on a chromosome) that may have
negative demographic effects through
inbreeding depression (Lande 1988, p.
1,456) and loss of adaptability. A small
amount of genetic exchange among
herds by movements of males can
counteract inbreeding and associated
increases in homozygosity (presence of
identical forms of a gene at a particular
location on a chromosome) that might
otherwise develop within small,
isolated populations (Schwartz et al.
1986, p. 185). Males have a much
greater tendency than females to explore
new ranges. This tendency is likely
attributed to males searching for females
with which to breed. If geographic
distances between female groups within
metapopulations are not great, gene
migration by males occurs readily. In
the absence of such a metapopulation
structure, populations will be isolated.
Because the distribution of bighorn
sheep in the Sierra Nevada is naturally
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fragmented, maintenance of migration
corridors is important to allow for
genetic exchange between herd units. In
the Sierra Nevada this exchange may be
more difficult because the
metapopulations occur mostly in a
linear geographic distribution pattern;
thus, fewer populations may have
provided sources of colonists (Service
2007, p. 34).
Substructuring also can occur within
what are often thought of as single herds
of bighorn sheep (Festa-Bianchet 1986,
pp. 327–330; Andrew et al. 1997, pp.
74–75; Rubin et al. 1998, pp. 543–548).
Such substructuring is defined by
separate home range patterns. Although
demonstrated more with females, it can
occur in both sexes. For example, what
was once considered the Mount Baxter
herd is now recognized as two herds,
Mount Baxter and Sawmill Canyon.
Another important long-term process
in metapopulation dynamics is the
balance between rates of natural
extinction and colonization among
populations. Colonization rates must
exceed extinction rates for a
metapopulation to persist (Hanski and
Gilpin 1991, pp. 8–9). This balance has
not occurred for Sierra Nevada bighorn
sheep since about 1850 due to the high
rate of local extinctions resulting in an
increasingly fragmented distribution. In
addition to fragmentation from past
extinctions, remaining herds are small,
isolated groups of bighorn sheep.
Because of their small population size,
these small groups are more vulnerable
to extirpation due to random, naturally
occurring events, disease, or predation
(Shaffer 1987, pp. 71–73; Meffe and
Carroll 1994, pp. 190–197; Service 2007,
p. 7).
Food and Nutritional Requirements
Bighorn sheep are ungulates that
consume a wide variety of plant species.
Due to a large rumen and reticulum
relative to body size, they have
flexibility in the plants they consume
which include graminoids (grasses,
sedges, and rushes) in different
phenological stages (Hanley 1982, p.
148). Bighorn sheep consume a wide
variety of plant species. While they
prefer grasses, sedges, and forbs,
different browse species become
important food during the fall and
winter (Wishart 1978, p. 167).
Bighorn sheep exhibit seasonal
changes in habitat use due to seasonal
changes in resource availability, habitat
and resource requirements. Sierra
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Nevada bighorn sheep rarely utilize
surface water; instead, these bighorn
sheep generally obtain moisture from
their forage or the occasional
consumption of snow. Altitudinal
migration by Sierra Nevada bighorn
sheep allows them to maximize nutrient
intake during the year (Wehausen and
Hansen 1988, pp. 256–257, 265–267;
Wehausen 1996, pp. 476–477), as the
relationship between elevation and
temperature (Major 1977, pp. 44–45)
influences plant growth (Wehausen
1980, p. 86–91, 133–135). In general,
temperatures decrease with increasing
altitude (Major 1977, p. 44). In the
Sierra Nevada, every 56 ft (17 m) of
elevation gain causes a 1 day delay in
the onset of plant growth (Wehausen
and Hansen 1988, p. 257). Bighorn
sheep are able to take advantage of early
spring growth (usually cold-season
grasses) and then later change their diet
to include warm-season plants that may
have higher nutrient concentrations
than grasses (Wehausen and Hansen
1988, p. 257). Sierra Nevada bighorn
sheep use low-elevation ranges
extensively in winter and early spring,
alpine ranges in summer and fall, and
some intermediate ranges during
transition periods (Wehausen 1980, pp.
80–100).
In the following section plant
nomenclature has been updated to
conform to treatments in Hickman
(1993). Common names generally
conform to those given in Hickman
(1993) or Abrams et al. (1923–1960).
Cited scientific names are retained in
brackets for ease of reference. The
following plant species were found to be
important winter/spring forage for
Sierra Nevada bighorn sheep:
Achnatherum speciosum [Stipa
speciosa] (desert needlegrass),
Eriogonum fasciculatum (California
buckwheat), Artemisia tridentata
(sagebrush), Ephedra viridis (green
ephedra), Keckiella breviflora (gaping
keckiella), Purshia glandulosa (Mojave
antelope bush), P. tridentata (northern
antelope bush), and Ceanothus
cordulatus (mountain whitethorn)
(Wehausen 1980, p. 87). McCullough
and Schneegas (1966, p. 72) and
Riegelhuth (1965, p. 38) provide similar
lists of plant species observed
consumed by Sierra Nevada bighorn
sheep during winter or summer (Table
1). Wehausen (1980, pp. 124–126)
provides a list of plants consumed by
both sexes in summer (Table 1).
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TABLE 1—PLANT SPECIES OBSERVED CONSUMED BY SIERRA NEVADA BIGHORN SHEEP DURING SUMMER AND FALL
MONTHS
[McCullough and Schneegas 1966, p. 72; Riegelhuth 1965, p. 38; Wehausen 1980, p. 124–126]
Sex
Season
Scientific name
Ewes and Lambs .......
Summer and fall .......
Polemonium eximium .......................................................................
Hulsea algida ...................................................................................
Carex helleri .....................................................................................
C. rossii ............................................................................................
C. leporinella ....................................................................................
Elymus elymoides ssp. elymoides [Sitanion hystrix] .......................
Phacelia hastata [frigida] .................................................................
Silene sargentii ................................................................................
Aquilegia pubescens ........................................................................
Ivesia pygmaea ................................................................................
Juncus parryi ...................................................................................
Achnatherum [Stipa] pinetorum .......................................................
Lupinus formosus ............................................................................
Sky pilot.
Alpine hulsea.
Heller’s sedge.
Ross’ sedge.
Sierra hare sedge.
Bottlebrush squirreltail.
Timberline phacelia.
Sargent’s campion.
Coville’s columbine.
Dwarf ivesia.
Parry’s rush.
Pine needlegrass.
Summer lupine.
Rams .........................
Summer and fall .......
Juncus parryi ...................................................................................
Carex filifolia var. erostrata [exserta] C. rossii ................................
C. aurea ...........................................................................................
Luzula comosa .................................................................................
Poa cusickii ssp. epilis [epilis] .........................................................
Elymus elymoides ssp. elymoides [Sitanion hystrix] .......................
Danthonia intermedia .......................................................................
Achnatherum lemmonii [Stipa columbiana] .....................................
Eriogonum lateens ...........................................................................
Trifolium monanthum .......................................................................
Parry’s rush.
Ross’ sedge.
Golden-fruited sedge.
Hairy wood rush.
Mountain bluegrass.
Bottlebrush squirreltail.
Mountain oatgrass.
Lemmon’s stipa.
Onion-flowered eriogonum.
Carpet clover.
Both sexes .................
Summer ....................
Holodiscus microphyllus ..................................................................
Jamesia Americana .........................................................................
Ribes montigenum ...........................................................................
Potentilla fruticosa ...........................................................................
Small-leaved cream bush.
Cliff bush.
Alpine prickly currant.
Shrubby cinquefoil.
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In addition to forage needs, mineral
licks are specific sites where bighorn
sheep have access to important minerals
to meet nutritional needs. These licks
contain minerals such as sodium,
calcium, iron, and phosphorus. Sites are
generally found in granite outcroppings
in the Sierra Nevada. Some known areas
occur in the vicinity of Gilcrest Peak
and Tioga Road (Chow 1992, p. 52),
Baxter Pass (Jones 1950, p. 63; Hicks
and Elder 1979, p. 911; Wehausen 1980,
p. 151), and Mayfield Canyon
(Stephenson 2007, p. 1).
Historical and Geographic Distribution
of the Species
Historically, the range of the Sierra
Nevada bighorn sheep included the
eastern slope of the Sierra Nevada, and
for at least one subpopulation, a portion
of the western slope, from Sonora Pass
in Mono County to Walker Pass in Kern
County, a total distance of
approximately 215 mi (346 km) (Jones
1950, pp. 33–35; Wehausen 1979, p. 1).
The extant range of the Sierra Nevada
bighorn sheep begins in the Lee Vining
area in Mono County and extends south
to the Mount Langley area in Inyo
County. This is a linear distance of
approximately 110 mi (177 km).
All currently occupied units that are
designated were occupied at the time of
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listing and contain the physical and
biological features essential to the
conservation of the subspecies and may
require special management
considerations or protection. The areas
designated as critical habitat that are
currently unoccupied were also not
occupied at the time of listing; however,
these areas are representative of the
historical and geographical distribution
of the Sierra Nevada bighorn sheep and
were all historically occupied (Ober
1914, p. 125; Ober 1931, p. 32; Jones
1950, pp. 35, 38–40; Buechner 1960, p.
69; Barrett 1965, p. 43; Riegelhuth 1965,
p. 35; Dunaway 1971, p. 19; Wehausen
et al. 1987, p. 66; Wehausen 1988a, pp.
100–101; Wehausen 1988b, p. 100;
Berger 1990, p. 94). Furthermore, we
have determined that all designated
unoccupied habitat is essential for the
conservation of the subspecies and will
decrease the degree of fragmentation
within the current geographic
distribution of the subspecies. For
further information on occupancy status
see Table 3 and the Unit Descriptions
sections below.
Primary Constituent Elements for Sierra
Nevada Bighorn Sheep
Under the Act and its implementing
regulations, we are required to identify
the known physical and biological
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Common name
features within the geographical area
occupied by Sierra Nevada bighorn
sheep at the time of listing that are
essential to the conservation of the
species and which may require special
management considerations or
protection. The physical and biological
features are those primary constituent
elements (PCEs) laid out in a specific
spatial arrangement and quantity to be
essential to the conservation of the
subspecies. All areas designated as
critical habitat for Sierra Nevada
bighorn sheep are within the
subspecies’ historical geographic range,
and contain sufficient PCEs to support
at least one life history function.
Based on the above needs and our
current knowledge of the life history,
biology, and ecology of the subspecies,
we have determined that the Sierra
Nevada bighorn sheep’s PCEs are:
(1) Non-forested habitats or forest
openings within the Sierra Nevada from
4,000 ft (1,219 m) to 14,500 ft (4,420 m)
in elevation with steep (greater than or
equal to 60 percent slope), rocky slopes
that provide for foraging, mating,
lambing, predator avoidance, and
bedding and that allow for seasonal
elevational movements between these
areas.
(2) Presence of a variety of forage
plants as indicated by the presence of
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grasses (e.g., Achnanthera spp.; Elymus
spp.) and browse (e.g., Ribes spp.;
Artemisia spp., Purshia spp.) in winter,
and grasses, browse, sedges (e.g., Carex
spp.) and forbs (e.g., Eriogonum spp.) in
summer.
(3) Presence of granite outcroppings
containing minerals such as sodium,
calcium, iron, and phosphorus that
could be used as mineral licks in order
to meet nutritional needs.
We determined that these PCEs
contained within the designated critical
habitat units discussed below provide
for the physiological, behavioral, and
ecological requirements of the Sierra
Nevada bighorn sheep. The first PCE
provides for the general biotic
communities that are known to support
Sierra Nevada bighorn sheep habitat in
the Sierra Nevada of California. Sierra
Nevada bighorn sheep are not known to
occur outside of the communities and
elevations described in this PCE. This
PCE further provides the components
necessary for foraging (summer and
winter), breeding, lambing, predator
avoidance, and bedding, and allows for
seasonal elevational movements among
these areas.
The second PCE describes the types of
food necessary to meet the biological
needs of the Sierra Nevada bighorn
sheep related to seasonal range
movements. Altitudinal migration by
Sierra Nevada bighorn sheep allows
them to maximize nutrient consumption
during the year (Wehausen and Hansen
1988, pp. 256–257, 265–267; Wehausen
1996, pp. 476–477), as the relationship
between elevation and temperature
(Major 1977, pp. 44–45) influences plant
growth (Wehausen 1980, pp. 86–91,
133–135), as discussed earlier.
Wehausen (1980, p. 86) found winter
diet quality was improved with warmer
winter temperatures that aided plant
growth; summer diet quality was
improved, apparently, by the amount of
snowfall the previous winter, which
may influence soil moisture for alpine
plants (Wehausen 1980, p. 133).
The third PCE provides for additional
nutritional needs. Mineral licks provide
necessary nutrients, important in
meeting dietary requirements.
This final designation is designed for
the conservation of the PCEs necessary
to support the life history functions of
the subspecies and the areas containing
those PCEs in the appropriate quantity
and spatial arrangement essential to the
conservation of the subspecies. Some
units contain all of these PCEs and
support multiple life processes, while
some units contain only a portion of
these PCEs, those necessary to support
the species’ particular use of that
habitat. Because not all life history
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functions require all the PCEs, not all
critical habitat units will contain all the
PCEs.
Special Management Considerations or
Protection
When designating critical habitat, we
assess whether the areas occupied by
the subspecies at the time of listing
contain the features that are essential to
the conservation of the subspecies, and
whether these features may require
special management considerations or
protection. As described in more detail
in the unit descriptions below, we find
that the PCEs within the units occupied
at the time of listing (Units 1, 2, 4, 6,
7, 8, and 10) may require special
management considerations or
protection due to threats to the Sierra
Nevada bighorn sheep or its habitat. All
of these units occur almost exclusively
on Federal lands managed by the Forest
Service, National Park Service, and the
Bureau of Land Management.
Management considerations and
protection of the essential features may
include review of various activities
proposed in Sierra Nevada bighorn
sheep habitat that are authorized,
funded, or carried out by these agencies.
These activities can include habitat
enhancement projects to reverse fire
suppression effects, development
activities, livestock grazing, mining
actions, and recreational activities. In
addition, because all of the herds are
relatively small, management actions to
protect Sierra Nevada bighorn sheep
habitat from catastrophic, naturally
occurring events (e.g., wildfires,
avalanches) may be necessary.
Fire suppression can modify the
structure of Sierra Nevada bighorn
sheep habitat by allowing taller
vegetation, such as trees, to become
established, resulting in cover for
predators. Mountain lions, a primary
predator of Sierra Nevada bighorn
sheep, use vegetative cover and terrain
to conceal themselves prior to attacks.
Fires may have burned more frequently
in the past in bighorn sheep habitat. Old
ground and aerial photographs show
habitats in the eastern Sierra Nevada
had little vegetation tall enough to
obstruct the vision of bighorn sheep;
pinyon pine woodlands have mostly
developed since 1860 (Miller and
Tausch 2001, pp. 15–16). Continued
suppression of fires in Sierra Nevada
bighorn sheep range is a threat, as
habitat succession alters the abundance
of suitable bighorn sheep habitat and
increases bighorn sheep vulnerability to
mountain lion predation (Torres et al.
1996, p. 29). Performing habitat
enhancements, such as prescribed
burning, or enabling ‘‘let burn’’ policies,
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helps to provide open habitats. Open
habitats will help to reduce predation
by decreasing the effectiveness of
ambushing by predators (such as
mountain lions) from cover. Providing
more open habitat will allow more
opportunity for connectivity among
herd units and likely promote greater
gene flow to conserve genetic diversity.
According to Johnson et al. (2005, p.
34), all of the herd units would benefit
from forest reduction in winter range;
those units that would incur the highest
benefit are Units 8 and 10. Thus, the
PCEs in all of the units occupied at the
time of listing (Units 1, 2, 4, 6, 7, 8, and
10) may require special management
considerations or protection to reverse
the impacts of fire suppression.
There is limited development within
Sierra Nevada bighorn sheep habitat
because most habitat occurs on Federal
lands; however, there is some
recreational development (e.g., resorts).
There are several paved and unpaved
roads that access Federal lands within
Sierra Nevada bighorn sheep habitat.
For example, State Highway 120 is
located primarily between Units 1 and
2, but some sections lie within Unit 1.
Bighorn sheep have been killed due to
collisions with vehicles on this road (65
FR 28; January 3, 2000). State Route 158
and Road 16S02 occur in or adjacent to
portions of Units 2 and 10, respectively.
The PCE’s in Units 1, 2, 4, and 10
require special management
considerations or protection to address
the impacts from development
activities, including road construction
and maintenance within Sierra Nevada
bighorn sheep habitat.
Management of domestic livestock
(sheep, goats, cattle) grazing practices
that result in overgrazing or allow for
contact between domestic sheep,
domestic goats, and Sierra Nevada
bighorn sheep is a threat. Domestic
livestock could compete with Sierra
Nevada bighorn sheep for forage at some
level in designated critical habitat units.
As the number of Sierra Nevada bighorn
sheep is still limited, this may not be a
concern currently on those allotments
within or near critical habitat. However,
some areas can be especially important
foraging areas for Sierra Nevada bighorn
sheep during winter. After domestic
livestock grazing has been completed
and they have been removed from the
allotment, regrowth of forage at higher
elevations can be a slow process. This
may result in less forage being available
for Sierra Nevada bighorn sheep during
the winter at these higher elevations.
Although die-offs of bighorn sheep
due to disease have occurred unrelated
to domestic sheep (Miller et al. 1991,
pp. 534–540), a major contributing
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factor responsible for the decline of
Sierra Nevada bighorn sheep
populations over the years is thought to
be the introduction of diseases by
domestic livestock (Sierra Nevada
Bighorn Sheep Interagency Advisory
Group 1997, p. 5; 65 FR 25, January 3,
2000).
Clifford et al. (2007) used available
spatial, demographic, and disease data
to assess the risk for and potential
impact of a respiratory disease outbreak
in Sierra Nevada bighorn sheep due to
contact with domestic sheep. They
evaluated the risk of disease
transmission between the two species
by determining the probabilities of
interspecies contact from Sierra Nevada
bighorn sheep monitoring data and
domestic sheep grazing data. A
prediction of short-term populationlevel impacts of a respiratory disease
outbreak was made using an
epidemiologic simulation model. While
acknowledging the study’s limitations,
Clifford et al. (2007, p. 18) indicate
concern for the probability of a
respiratory disease case occurring from
disease transmission between domestic
sheep and Sierra Nevada bighorn sheep,
especially in the northern part of
bighorn sheep range.
Domestic grazing allotments within
the vicinity of Sierra Nevada bighorn
sheep habitat should be reviewed and
activities should be modified as
necessary to prevent competition and
contact between the domestic livestock
(sheep and goats) and bighorn sheep.
These modifications could include such
variables as the number of domestic
livestock allowed on an allotment,
where the domestic livestock may graze
on an allotment, and the length and
timing of the grazing period. These
variables can assist in reducing resource
competition as well as reducing contact
between domestic sheep (and goats) and
bighorn sheep. The PCEs within Units 1,
2, and 4 may require special
management considerations or
protection to address the potential
impacts of domestic sheep and goat
grazing within Sierra Nevada bighorn
sheep habitat. The PCEs within Units 1,
2, 3, 4, 5, 8, 10, and 12 may require
special management considerations or
protection to address the potential
impacts of cattle grazing within Sierra
Nevada bighorn sheep habitat. While we
are addressing the potential for contact
and the possible transmission of disease
to Sierra Nevada bighorn sheep due to
the presence of domestic sheep or goats
within critical habitat, it is not strictly
a habitat-related threat. The concern for
disease transmission from domestic
sheep and goat grazing in proximity to
Sierra Nevada bighorn sheep did not
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serve as the foundation for this critical
habitat designation.
Patented mining claims occur within
habitat used by the Sierra Nevada
bighorn sheep, but the area of the claims
is small. Mining activities and
associated facilities threaten bighorn
sheep by causing the loss of vegetation
structure required for foraging activities;
the destruction of habitats used for
escape, bedding, lambing, or
connectivity between ranges; and the
disturbance due to ongoing mining
activities. Disturbance could modify
bighorn sheep behavior or cause them to
flee an area. Mining occurs within the
habitat of Sierra Nevada bighorn sheep
in Unit 4. These mines are underground,
thus reducing some impacts of habitat
loss. PCEs within this unit may require
special management considerations or
protection to address mining and
associated facility development impacts
within Sierra Nevada bighorn sheep
habitat.
It remains unclear how significantly
Sierra Nevada bighorn sheep may be
affected by human disturbance (Jones
1950, pp. 71–72; Dunaway 1971, p. 19;
Wehausen et al. 1977, p. 31; Hicks and
Elder 1979, p. 914; Wehausen 1980, pp.
200–201; MacArthur et al. 1982, p. 356;
Papouchis et al. 2001, pp. 579–580).
Additional investigations are needed to
identify areas of conflict as situations
arise where the increased presence of
humans could be detrimental to the
Sierra Nevada bighorn sheep or its
habitat. These areas of use could
displace Sierra Nevada bighorn sheep
from important habitats.
Increases in human uses of bighorn
sheep habitat, including recreational
activities such as rock and ice climbing,
mountaineering, ski touring, hiking,
camping, pack station establishment,
snowmobiling, and off-road vehicle use
may disturb Sierra Nevada bighorn
sheep in key areas. This could result in
abandonment of these areas or
disruption of feeding, resulting in
reduced nutrient intake. A cost in
biological energetics could also occur
due to flight. These losses could
translate into reduced reproductive
success. Impacts to the habitat could
occur through trampling and reduced
vegetation structure due to grazing by
pack animals. The presence of dogs
accompanying recreationists is also a
concern in bighorn sheep habitat as
dogs may cause strong alarm reactions
by bighorn sheep (MacArthur et al.
1982, p. 356).
Bighorn sheep can be conditioned or
habituated to human activities such as
trail hiking, where bighorn sheep are
able to watch humans approaching from
a distance and from below (Hicks and
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Elder 1979, p. 914), road traffic
(Papouchis et al. 2001, p. 580), or
predictable activities such as
photographers taking pictures near a
road (MacArthur et al. 1982, p. 356).
This conditioning can minimize alarm
reactions. Other individuals have shown
avoidance of roads (Papouchis et al.
2001, p. 580). Particular groups (e.g.,
ewe-lambs) may demonstrate a more
extreme alarm reaction at a greater
distance than other groups when
encountered from above as their path is
blocked (Wehausen et al. 1977, p. 31).
Review of recreational activities should
take into account various factors such as
location, ground disturbance, timing of
year, duration, and noise level to
determine if impacts may occur to
Sierra Nevada bighorn sheep and its
habitats.
The PCEs within the units occupied at
the time of listing (Units 1, 2, 4, 6, 7,
8, and 10) may require special
management considerations or
protection to protect Sierra Nevada
bighorn sheep and its habitat from
recreational activities. While recreation
could be a threat factor throughout an
occupied herd unit, it is more likely in
some portions of units due to their
inclusion of these higher use areas or
their proximity to these areas. These
areas include the Virginia Lakes, the
Lundy Lake, the Saddlebag Lake, and
the Lee Vining Canyon recreational
areas associated with Unit 1; the Lee
Vining Canyon recreational area
associated with Unit 2; the Rock Creek
recreational area associated with Unit 4;
the Baxter Pass and Onion Valley
recreational area associated with Unit 7;
and the Whitney Portal and Trailhead
and the Cottonwood Lakes recreational
areas associated with Units 8 and 10.
Management actions to protect Sierra
Nevada bighorn sheep habitat from
catastrophic, naturally occurring events
may be necessary. Events such as
wildfires and avalanches could
temporarily destroy large areas that
provide summer or winter foraging
habitat.
Criteria Used To Identify Critical
Habitat
We are designating critical habitat in
areas that were occupied by the
subspecies at the time of listing and that
contain PCEs in the quantity and spatial
arrangement to support life history
functions essential for the conservation
of the subspecies. Some lands contain
only a portion of the PCEs necessary to
support the particular use of that habitat
during that portion of the life process.
We are also designating critical habitat
in specific unoccupied areas that were
not occupied by the subspecies at the
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time of listing. We have determined that
these areas, which were historically
occupied, are essential to the
conservation of the subspecies.
In our analysis, we reviewed existing
data to determine the distribution of
areas occupied by the subspecies at the
time of listing. We also reviewed
available information related to the
habitat requirements of the subspecies.
We used information from literature
cited in the final listing rule (65 FR 20;
January 3, 2000), the final recovery plan,
site records, reports prepared by CDFG,
and other published scientific literature.
We used the following criteria to
select areas occupied by the Sierra
Nevada bighorn sheep at the time of
listing for inclusion in critical habitat:
(a) Areas occupied by the Sierra
Nevada bighorn sheep at the time of
listing (1999–2000) as indicated in the
final listing rule (65 FR 20; January 3,
2000). In the final listing rule, we
identified five subpopulations of Sierra
Nevada bighorn sheep that existed: (1)
Lee Vining Canyon (Mount Warren and
Mount Gibbs Herd Units), (2) Wheeler
Crest (Wheeler Ridge Herd Unit), (3)
Mount Baxter (Sawmill Canyon and
Mount Baxter Herd Units), (4) Mount
Williamson (Mount Williamson Herd
Unit), and (5) Mount Langley (Mount
Langley Herd Unit) in Mono and Inyo
counties, California (Wehausen 1999,
pp. 1–7; 2000, pp. 1–6);
(b) Areas that are representative of the
distribution of the Sierra Nevada
bighorn sheep throughout the
geographical range occupied at the time
of listing with the goal of maintaining
the subspecies’ range of habitat and
genetic variability; and
(c) Areas that allow for the continued
existence of viable subpopulations
under varying environmental conditions
and that can serve as locations for
source populations. The locations of all
five subpopulations identified in the
original listing rule continue to remain
occupied today.
Current population estimates of the
Sierra Nevada bighorn sheep in 2006
indicate 350 to 400 individuals occur
throughout its range (Wehausen and
Stephenson 2006, p. 7); this is an
increase from the 125 individuals
estimated at the time of listing (65 FR
20; January 3, 2000). Current individual
herd numbers in the different
subpopulations range from 8 to 113
individuals (Wehausen and Stephenson
2006, p. 7). Current occupancy of these
herd units is supported by agency
reports (Wehausen and Stephenson
2004, pp. 2–10; 2005, pp. 2–6; 2006, pp.
2–6); status reports (Wehausen 1999, pp.
1–7; 2000, pp. 1–6); and monthly CDFG
monitoring reports based on GPS,
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telemetry, and monitoring data collected
during 2001 through 2006. We have
determined that the areas occupied at
the time of listing continue to be
occupied, contain the features essential
to the conservation of the subspecies
(possess one or more PCEs such that the
area supports one or more of the Sierra
Nevada bighorn sheep’s life processes),
and provide sufficient habitat to protect
these populations.
In addition, we are designating
critical habitat on lands that were
historically occupied by the Sierra
Nevada bighorn sheep, but were not
occupied at the time of listing and are
not currently occupied. These areas
were all historically occupied within
the past 90 years (Jones 1950, pp. 33–
35) and are essential to the conservation
of the subspecies. Based on the best
available information, we have
determined that without protection and
management of these unoccupied areas,
conservation of the subspecies will not
be possible.
We applied each of the following
criteria to select areas historically
occupied, but not known to be occupied
at the time of listing by the Sierra
Nevada bighorn sheep, for inclusion in
critical habitat:
(1) Areas where habitat contains
sufficient PCEs (e.g., characteristics
such as non-forested, steep, rocky slopes
and foraging areas) to support life
history functions.
(2) Areas where habitat has been
occupied by the subspecies. In some
areas this was as long ago as 90 years
(Jones 1950, pp. 33–35). In all of the
areas the habitat has not changed
appreciably in size or quality during
that time.
(3) Areas where appropriate habitat
for Sierra Nevada bighorn sheep has
been predicted by CDFG based on
Resource Selection Probability
Functions modeling (Johnson et al.
2005) (i.e., contains habitat with the
PCEs and additional, more specific
characteristics that allow for a range of
the subspecies’ biological needs, such as
sites for feeding).
(4) Areas where there is potential for
reoccupation by the subspecies, either
through natural means of dispersal from
currently occupied areas or by future reintroduction efforts.
(5) Areas that are geographically
separated from currently occupied units
by approximately 0.5 to 8 mi (0.8 to 12.9
km) to provide redundancy of habitat in
the event of a natural catastrophe
removing habitat (PCEs) from currently
occupied units.
The designation of these unoccupied
areas would decrease the degree of
fragmentation within the current
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geographic distribution of the Sierra
Nevada bighorn sheep. We believe that
the designation of these additional areas
is essential for the conservation of the
subspecies because:
(1) Population increases, either
through natural means or
reintroductions into the additional
units, are expected to increase the
viability of the herds within occupied
areas, as well as the existence of the
Sierra Nevada bighorn sheep as a whole
(i.e., increase the likelihood of
persistence at the local population level
and of this subspecies rangewide).
(2) The Sierra Nevada bighorn sheep
is recognized as a unique subspecies
(Wehausen and Ramey 2000, p. 156;
Wehausen et al. 2005, p. 217), and the
additional units will serve to decrease
the degree of fragmentation of the
current geographic distribution of the
sheep (i.e., increase connectivity
between areas known to be currently
occupied). Fragmented distribution
across the landscape reduces the
connectivity between subpopulations. If
small populations are isolated and
remain small, there is an increased risk
of genetic drift and risk to persistence
due to naturally occurring events
(Gilpin and Soule 1986, pp. 25, 33).
Maintenance of genetic variation is
important in reducing inbreeding
depression and the ability to respond to
environmental changes over time,
especially in small populations
(Schwartz et al. 1986, pp. 180–186;
Lande 1988, pp. 1,456–1,457).
Establishing additional units or
subpopulations in unoccupied areas
would fill in range gaps between the
other occupied units and/or
subpopulations. All of the unoccupied
units lie within 8 mi (12.9 km) of an
occupied area. This would reduce
migration distances and increase the
opportunity for genetic exchange
between the subpopulations. The
addition of these unoccupied units
would ensure the full geographic
distribution of the Sierra Nevada
bighorn sheep is represented.
(3) The current overall population
size of the Sierra Nevada bighorn sheep
is small, and it must increase to ensure
the long-term survival of this
subspecies, as small populations are
more vulnerable to extinction (Meffe
and Carroll 1994, pp. 190–197; Shaffer
1987, pp. 71–73). While the occupied
units provide habitat for current
populations, additional units would
provide habitat for population growth
either through natural means or through
reintroductions. Population increase in
the additional units would assist in
reducing the risk of extinction of the
subspecies through stochastic events,
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such as wildfire, disease (Bunch et al.
1999, pp. 209–237), or avalanches
(Torres et al. 1996, p. 28), as the current
isolated populations are few in number,
small in size, and at risk from such
stochastic events. Establishing
additional subpopulations, increasing a
subpopulation’s size, and increasing the
overall distribution of subpopulations
across the landscape are fundamental to
reducing the significance of losing any
single subpopulation.
We have determined that the
unoccupied Twin Lakes, Green Creek,
and Coyote Ridge Herd Unit areas, as
identified in the final recovery plan
(Service 2007, p. 41), are not essential
for the conservation of the Sierra
Nevada bighorn sheep. During the
recovery team’s efforts to finalize the
recovery plan, an additional herd unit,
Bubbs Creek, was included in the final
recovery plan due to bighorn sheep
occupying this area (Wehausen and
Stephenson 2004, p. 5; Benz 2007, p. 1;
Service 2007, p. 41). Though these four
herd units are mentioned in the final
recovery plan they were not considered
to be essential in the plan. These four
herd units are considered not essential
for the following reasons:
(1) We believe that the 12 units we are
designating as critical habitat provide
the necessary habitat and area to ensure
the viability and long-term survival of
the Sierra Nevada bighorn sheep at the
local and subspecies levels, as well as
provide for sufficient resiliency,
representation, and redundancy of the
subspecies.
(2) There is uncertainty regarding
whether viable Sierra Nevada bighorn
sheep herds can become established in
the Twin Lakes, Green Creek, and
Coyote Ridge Herd Unit areas due to the
lack of historical evidence regarding the
number of animals that may have
occurred in these areas and our limited
understanding of the availability and
connectivity between foraging habitats
in these areas. Thus, there is a question
as to whether there is a potential for
reoccupation by the subspecies, either
through natural means of dispersal or by
future reintroduction efforts. As a result,
these three herd unit areas do not meet
our criterion number 4 for identification
of critical habitat outlined above.
Therefore, the Twin Lakes, Green Creek,
and Coyote Ridge Herd Unit areas are
not considered essential for recovery.
(3) Bighorn sheep were discovered in
the Bubbs Creek Herd Unit area in 2001
and were likely a result of a recent
colonization. This herd unit area is west
of the crest of the Sierra Nevada where
snowfall is much greater than the east
side of the range. Because there are no
historical records of bighorn sheep
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winter range in the Bubbs Creek area,
there is uncertainty as to the long-term
viability of this herd unit. Consequently,
the Bubbs Creek Herd Unit area is not
considered essential for recovery.
Further, our concern for disease
transmission from domestic sheep to
Sierra Nevada bighorn sheep is reduced
because we are not including the
unoccupied herd units as essential to
the recovery of the subspecies. Twin
Lakes and Green Creek overlap with
portions of a few currently active
domestic sheep allotment boundaries.
Bubbs Creek and Coyote Ridge Herd
Units do not occur near domestic sheep
allotments. While the potential for
disease transmission from domestic
sheep and goat grazing in proximity to
Sierra Nevada bighorn sheep is a
management concern, it did not serve as
the foundation for this critical habitat
designation.
We delineated polygon boundaries for
each unit for critical habitat designation
within the Sierra Nevada bighorn
sheep’s historical range and around
areas occupied at the time of listing, or
known to have been historically
occupied and considered essential for
the conservation of the subspecies. We
based our boundary delineation on the
knowledge that bighorn sheep are
naturally philopatric and fit a
metapopulation model. Separate female
groups tend to be geographically
segregated, and these groups can be
defined by separate home range
patterns. The existing herds provided
information related to home range and
habitat use patterns. Low-elevation
winter range habitat is an important,
and apparently limiting, factor in the
Sierra Nevada that occurs in disjunct
patches. We defined unit boundaries
around those patches and
geographically connected habitat that
provides visually open habitat on
steeper slopes (Wehausen 2006, p. 1).
We also considered factors such as
knowledge of the range of elevations
used by Sierra Nevada bighorn sheep,
topographic features known to be
needed by the subspecies, sighting
records, published literature, and the
expertise of bighorn sheep biologists
regarding local conditions (high
elevation, snow-free winter habitat;
lower elevation, south or east-facing
habitat; visual openness; and high
elevation, summer habitat) during
boundary delineation. In addition, a
Resource Selection Probability
Functions model for winter and summer
habitat was developed that can
quantitatively evaluate habitat
conditions (Johnson et al. 2005). This
modeling effort was used to support and
refine unit boundaries (Wehausen 2006,
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p. 2) which contain the PCEs and
additional, more specific characteristics.
The model included variables such as
elevation, slope, aspect, hillshade,
terrain ruggedness, distance to escape
terrain, and vegetation to determine
visibility (Johnson et al. 2005, pp. 8–9).
Pixels (smallest element of an image
that can be individually processed in a
video display system) in the study area
that received a relative winter and
summer probability of use value in the
90–100 percent quartile were
considered winter and summer ranges.
Each unit boundary surrounds the areas
we consider to be winter and summer
range, as well as areas necessary to
provide connectivity between these
ranges. These boundary lines translate
onto the ground by roughly following
elevation and geomorphic features. As
one progresses from south to north
along the Sierra Nevada, the lower
boundary elevation of the units
increases. The elevation of the boundary
lines begins at a low of 4,000 ft (1,219
m) for Unit 12 (Olancha Peak) at the
southern end of the Sierra Nevada. From
this unit northward, the remaining units
begin at a low elevation of 4,500 ft
(1,372 m) or higher.
When determining critical habitat
boundaries for this rule, we made every
effort to avoid including developed
areas such as lands covered by
buildings, paved areas, and other
structures that lack PCEs for the Sierra
Nevada bighorn sheep. The scale of the
maps prepared under the parameters for
publication within the Code of Federal
Regulations may not reflect the
exclusion of such developed areas. Any
such structures and the land under them
inadvertently left inside critical habitat
boundaries shown on the maps of this
final rule have been excluded by text in
the final rule and are not designated as
critical habitat. Therefore, Federal
actions limited to these areas would not
trigger section 7 consultation, unless
they may affect the subspecies or its
PCEs in adjacent critical habitat.
We designate critical habitat (7 units)
on lands that we have determined were
occupied at the time of listing that
contain the physical and biological
features essential for the conservation of
the subspecies that may require special
management considerations or
protection, and additional areas (5
units) not occupied at the time of listing
that we have determined to be essential
to the conservation of the subspecies.
The 12 units that we designate as
critical habitat encompass about
417,577 ac (168,992 ha) within
Tuolumne, Mono, Fresno, Inyo, and
Tulare Counties, California. The
designated units contain habitat that
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supports biological and population-level
functions of the Sierra Nevada bighorn
sheep. A brief discussion of each unit
designated as critical habitat is provided
in the unit descriptions below.
Units both occupied and unoccupied
at the time of listing are designated
based on sufficient PCEs being present
to support Sierra Nevada bighorn sheep
life processes. Some units contain all
PCEs and support multiple life
processes. Some units contain only a
portion of the PCEs necessary to support
the Sierra Nevada bighorn sheep’s
particular use of that habitat.
Section 10(a)(1)(B) of the Act
authorizes us to issue permits for the
take of listed species incidental to
otherwise lawful activities. An
incidental take permit application must
be supported by a HCP that identifies
conservation measures that the
permittee agrees to implement to
minimize and mitigate the impacts of
the taking on the species. We often
exclude from designated critical habitat
non-Federal public lands and private
lands that are covered by an existing
operative HCP and executed
implementation agreement under
section 10(a)(1)(B) of the Act, where we
determine that the benefits of exclusion
outweigh the benefits of inclusion in
accordance with section 4(b)(2) of the
Act. There are no existing operative
HCPs within the areas designated as
critical habitat.
described below constitute our best
current assessment of areas determined
to be occupied at the time of listing, that
meet the definition of critical habitat for
the Sierra Nevada bighorn sheep, and
those additional areas that were not
occupied at the time of listing but were
found to be essential to the conservation
of the Sierra Nevada bighorn sheep. The
12 areas designated as critical habitat
are: Mount Warren, Mount Gibbs,
Convict Creek, Wheeler Ridge, Taboose
Creek, Sawmill Canyon, Mount Baxter,
Mount Williamson, Big Arroyo, Mount
Langley, Laurel Creek, and Olancha
Peak.
The approximate area encompassed
within each designated critical habitat
unit is shown in Table 2.
Final Critical Habitat Designation
We are designating 12 units as critical
habitat for the Sierra Nevada bighorn
sheep. The critical habitat areas
TABLE 2—DESIGNATED CRITICAL HABITAT UNITS FOR SIERRA NEVADA BIGHORN SHEEP
[Area estimates reflect all land within critical habitat unit boundaries]
Size of unit in acres
(hectares)
Critical habitat unit
Land ownership by type
1. Mount Warren ..............................................................
Federal ............................................................................
Private .............................................................................
Local Government ...........................................................
Federal ............................................................................
Federal ............................................................................
Private .............................................................................
Federal ............................................................................
Private .............................................................................
Federal ............................................................................
Federal ............................................................................
Federal ............................................................................
Private .............................................................................
Federal ............................................................................
Federal ............................................................................
Federal ............................................................................
Federal ............................................................................
Federal ............................................................................
2. Mount Gibbs ................................................................
3. Convict Creek ..............................................................
4. Wheeler Ridge .............................................................
5. Taboose Creek ............................................................
6. Sawmill Canyon ...........................................................
7. Mount Baxter ...............................................................
8. Mount Williamson ........................................................
9. Big Arroyo ....................................................................
10. Mount Langley ...........................................................
11. Laurel Creek ..............................................................
12. Olancha Peak ............................................................
35,279
568
165
29,702
36,497
17
80,568
398
28,805
30,508
32,198
22
32,560
24,987
32,845
22,037
30,421
(14,277)
(230)
(67)
(12,020)
(14,770)
(7)
(32,605)
(161)
(11,657)
(12,346)
(13,030)
(9)
(13,177)
(10,112)
(13,292)
(8,918)
(12,311)
Subtotal .....................................................................
Federal ............................................................................
Private .............................................................................
Local Government ...........................................................
416,407 (168,518)
1,005 (407)
165 (67)
Grand Total * .....................................................
..........................................................................................
417,577 (168,992)
* Columns may not sum exactly due to rounding of values.
TABLE 3—OCCUPANCY OF SIERRA NEVADA BIGHORN SHEEP BY DESIGNATED CRITICAL HABITAT UNIT
dwashington3 on PRODPC61 with RULES2
Unit
Occupied at time of listing?
Currently
occupied?
Size of unit in acres
(hectares)
1. Mount Warren ............................................................
2. Mount Gibbs ..............................................................
3. Convict Creek ............................................................
4. Wheeler Ridge ...........................................................
5. Taboose Creek ..........................................................
6. Sawmill Canyon .........................................................
7. Mount Baxter .............................................................
8. Mount Williamson ......................................................
9. Big Arroyo ..................................................................
10. Mount Langley .........................................................
11. Laurel Creek ............................................................
12. Olancha Peak ..........................................................
Yes ....................................
Yes ....................................
No ......................................
Yes ....................................
No ......................................
Yes ....................................
Yes ....................................
Yes ....................................
No ......................................
Yes ....................................
No ......................................
No ......................................
Yes ....................................
Yes ....................................
No ......................................
Yes ....................................
No ......................................
Yes ....................................
Yes ....................................
Yes ....................................
No ......................................
Yes ....................................
No ......................................
No ......................................
Total * ......................................................................
............................................
............................................
* Columns may not sum exactly due to rounding of values.
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36,012
29,702
36,514
80,966
28,805
30,508
32,220
32,560
24,987
32,845
22,037
30,421
(14,574)
(12,020)
(14,777)
(32,766)
(11,657)
(12,346)
(13,039)
(13,177)
(10,112)
(13,292)
(8,918)
(12,311)
417,577 (168,992)
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We present brief descriptions of all
units, and reasons why they meet the
definition of critical habitat for Sierra
Nevada bighorn sheep, below.
Universal Transverse Mercator (UTM)
coordinates and more precise legal
descriptions of each unit are provided
in the Regulation Promulgation section.
Sierra Nevada bighorn sheep
throughout their range utilize elevations
from about 4,790 ft (1,460 m) to above
14,100 ft (4,300 m) (Wehausen 1980, pp.
3, 82). As described in the Criteria Used
to Identify Critical Habitat section
above, we used modeling to further
refine and clarify our knowledge of
those areas that may be essential to the
conservation of the subspecies. Based
on these modeling efforts, Sierra Nevada
bighorn sheep habitat is known to be
available as low as elevation 4,000 ft
(1,219 m) in the southern portion of its
range (Johnson et al. 2005). Within this
elevational range, a variety of vegetation
communities occur including (from
lowest to highest elevations): Sagebrushbitterbrush-bunchgrass scrub; pinyonjuniper woodland and mountain
mahogany scrub; mid-elevation and
subalpine, meadows, forests, and
woodlands; and alpine meadows and
other habitats from cliffs to plateaus
(Service 2007, p. 3). All units contain
one or more of these habitat types in
varying amounts.
Unit 1: Mount Warren
Unit 1 consists of approximately
36,012 ac (14,574 ha) in Tuolumne and
Mono Counties. Unit 1 is generally
located within an area bounded on the
east by U.S. Highway 395 (located about
1 mi (1.6 km) away), on the south by SR
120, on the north by Green Creek, and
on the west by the ridge connecting
Ragged Peak in the south to Camiaca
Peak in the north. It is located northwest
of the town of Lee Vining. Land
ownership within the unit includes
approximately 35,279 ac (14,277 ha) of
Federal land, 165 ac (67 ha) of Los
Angeles Department of Water and Power
lands, and 568 ac (230 ha) of other
private land. The Federal land is
administered by the Humboldt-Toiyabe
and Inyo National Forests, Yosemite
National Park, and Bureau of Land
Management.
Unit 1 begins at a low elevation of
about 7,500 ft (2,286 m) on the eastern
slope and rises to about 12,000 ft (3,658
m) on the west. It encompasses some
areas from 12,000 to over 14,000 ft
(3,658–4,267 m). It is the northernmost
unit designated as critical habitat for the
Sierra Nevada bighorn sheep. This unit
was occupied at the time of listing (65
FR 20, January 3, 2000; Wehausen 1996,
p. 477; Sierra Nevada Bighorn Sheep
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Interagency Advisory Group 1997, pp.
6–7; Wehausen 1999, pp. 6, 8; 2000, pp.
5–7) and is currently occupied with a
minimum population estimate of 26
individuals (Wehausen and Stephenson
2006, p. 7). Unit 1 contains all of the
features essential to the conservation of
the Sierra Nevada bighorn sheep. It
contains steep, rocky terrain which
provides for foraging (summer and
winter), mating, lambing, predator
avoidance, and bedding and also allows
for seasonal elevational movements;
contains a range of vegetation types
(PCE 1 and PCE 2) (Johnson et al. 2005,
pp. 4–14, 31–32, 34, 37–38; Service
2007, pp. 3–5); and contains mineral
licks (PCE 3) (Chow 1992, p. 52). This
unit has good high- and low-elevation
winter habitat in the area north of Lee
Vining Canyon. Mount Warren has a
minimum winter range elevation of
about 7,546 ft (2,300 m), while Tioga
Crest has this type of habitat at 9,515 ft
(2,900 m). In the Lundy Canyon area
there is good low-elevation south-facing
winter range near 8,038 ft (2,450 m).
Dunderberg Peak can provide large areas
free of snow in the winter. It does not
connect to low-elevation winter range
but does connect to summer range in
Lundy Canyon; visual winter range
condition is mixed to open (Service
2007, pp. 127, 129).
The essential features found within
Unit 1 may require special management
considerations or protection to
ameliorate the threats of overgrazing.
Additionally, the PCEs within this unit
may require special management
considerations or protection to reverse
the impacts of fire suppression which
would provide more open habitat and
potentially reduce predation, and to
protect against the impacts of recreation
(e.g., Virginia Lakes, Lundy Lake, Lee
Vining Canyon) and development
activities (Sections of State Highway
120 are located in this unit).
Furthermore, PCEs within Unit 1 may
require special management
considerations or protection in the form
of avalanche control to protect against
catastrophic events.
Unit 2: Mount Gibbs
Unit 2 consists of approximately
29,702 ac (12,020 ha) in Tuolumne and
Mono Counties. Unit 2 is generally
bounded on the north by SR 120 with
U.S. Highway 395 located
approximately 4 mi (6.4 km) to the east.
State Route 158 lies along a portion of
the southeastern boundary of this unit.
The unit is bounded on the west, in
part, by Lyell Canyon. It is immediately
south of Unit 1 (Mount Warren) and is
located southwest of Lee Vining. Land
ownership within the unit includes
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45563
approximately 29,702 ac (12,020 ha) of
Federal land administered by the Inyo
National Forest and Yosemite National
Park.
Unit 2 begins at a low elevation of
about 7,500 ft (2,286 m) on the eastern
slope and rises to 9,000–12,000 ft
(2,743–3,658 m) on the west. It
encompasses areas from 12,000 to over
14,000 ft (3,658–4,267 m). Unit 2 was
occupied at the time of listing
(Wehausen 1996, p. 477; Sierra Nevada
Bighorn Sheep Interagency Advisory
Group 1997, pp. 6–7; Wehausen 1999,
pp. 7–8; 2000, pp. 6–7; 65 FR 20,
January 3, 2000) and is currently
occupied, with a minimum population
estimate of 8 individuals (Wehausen
and Stephenson 2006, p. 7). Unit 2
contains all of the features essential to
the conservation of the Sierra Nevada
bighorn sheep. It contains steep, rocky
terrain which provides for foraging
(summer and winter), mating, lambing,
predator avoidance, and bedding and
also allows for seasonal elevational
movements; contains a range of
vegetation types (PCE 1 and PCE 2)
(Johnson et al. 2005, pp. 4–14, 31–32,
34, 37–38; Service 2007, pp. 3–5); and
contains mineral licks (PCE 3) (Chow
1992, p. 52). An area between Mount
Dana and Mount Wood provides
considerable high-elevation habitat that
is blown free of snow in the winter and
connects to south-facing slopes that
decline to lower elevations. Winter
habitat occurs at a minimum elevation
of 9,105 ft (2,775 m) around Mount
Gibbs; 8,859 ft (2,700 m) around Mount
Lewis; and 7,546 ft (2,300 m) around
Mount Wood. Visual winter range
condition is open (Service 2007, p. 127).
The south-facing side of Mount Lewis is
steep and supports little snow in winter.
The slopes above Silver Lake offer lowelevation east-facing winter range to
7,599 ft (2,316 m). This area may
provide birthing habitat in spring during
some years (Service 2007, p. 129).
The essential features found within
Unit 2 may require special management
considerations or protection to
ameliorate the threats of overgrazing.
Additionally, PCEs within this unit may
require special management
considerations or protection to reverse
the impacts of fire suppression which
would provide more open habitat and
potentially reduce predation, and to
protect against the impacts of recreation
(e.g., Lee Vining Canyon) and
development activities (sections of SR
120 are located along the northern
boundary of this unit; SR 158 lies along
a portion of the southeastern boundary
of this unit). Furthermore, PCEs within
Unit 2 may require special management
considerations or protection in the form
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of avalanche control to protect against
catastrophic events.
Unit 3: Convict Creek
Unit 3 consists of approximately
36,514 ac (14,777 ha) in Mono and
Fresno Counties. Unit 3 is generally
located within an area bounded on the
northeast by U.S. Highway 395 (located
about 2 mi (3.2 km) away), by Fish
Creek and the boundary between Inyo
and Sierra National Forests on the west,
and by Mono Creek on the south. This
unit is located about 3 mi (4.8 km) south
of Mammoth Lakes. Land ownership
within the unit includes approximately
36,497 ac (14,770 ha) of Federal land
and 17 ac (7 ha) of private land. Federal
land is administered by the Inyo and
Sierra National Forests.
Unit 3 begins at a low elevation of
about 7,500 ft (2,286 m) and rises to
about 10,500–12,000 ft (3,200–3,658 m).
The unit encompasses areas from 12,000
to over 14,000 ft (3,658–4,267 m). This
unit was not occupied at the time of
listing and is not currently occupied,
but is essential to the conservation of
the Sierra Nevada bighorn sheep. The
unit contains steep, rocky terrain which
provides for foraging (summer and
winter), mating, lambing, predator
avoidance, and bedding and also allows
for seasonal elevational movements, and
a range of vegetation types (PCE 1 and
PCE 2) (Johnson et al. 2005, pp. 4–14,
31–32, 34, 37–38; Service 2007, pp. 3–
5). Mineral licks (PCE 3) may or may not
occur in this unit. This unit contains
south-facing winter habitat above
Convict Lake that descends down to
7,874 ft (2,400 m). This habitat is
connected to high-elevation windswept
patches on Laurel and Bloody
Mountains. McGee Mountain has southfacing winter habitat down to about
8,005 ft (2,440 m) but only a small
amount of high-elevation habitat.
Nevahbe Ridge has windblown habitat,
but it is east-facing and habitat occurs
down to 8,530 ft (2,600 m) (Service
2007, pp. 127, 130). Visual winter range
condition is open (Service 2007, p. 127).
While this unit was not occupied at
the time of listing, Sierra Nevada
bighorn sheep occupied the area
historically (Ober 1931, p. 32; Jones
1950, p. 40; Buechner 1960, p. 69;
Barrett 1965, p. 43; Dunaway 1971, p.
19; Wehausen et al. 1987, p. 66;
Wehausen 1988a, p. 100). This unit is
essential to the conservation of the
Sierra Nevada bighorn sheep for
increasing the number of herds to
reduce the significance of losing any
particular herd, increasing population
viability, decreasing the degree of
fragmentation of the current geographic
distribution between this unit and Units
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13:15 Aug 04, 2008
Jkt 214001
4 (Wheeler Ridge) and 2 (Mount Gibbs),
increasing opportunities for genetic
exchange between these units, and
increasing overall herd numbers to
reduce extinction risk from stochastic
events. Conservation of this unit is
necessary to achieve the long-term
viability of this subspecies within its
range.
Unit 4: Wheeler Ridge
Unit 4 consists of approximately
80,966 ac (32,766 ha) in Fresno, Inyo,
and Mono Counties. Unit 4 is generally
located within an area bounded by U.S.
Highway 395 (located about 5–17 mi (8–
27.4 km) to the east; Evolution Creek on
the south; Pavilion Dome, Pilot Nob,
and Mills Creek on the west; and Mono
Creek on the north. This unit is located
about 12 mi (19.3 km) west of Bishop.
Land ownership within the unit
includes approximately 80,568 ac
(32,605 ha) of Federal land and 398 ac
(161 ha) of private land. Federal land is
administered by the Inyo and Sierra
National Forests, Kings Canyon National
Park, and the Bureau of Land
Management.
Unit 4 begins at a low elevation of
about 5,500 ft (1,676 m) on the eastern
slope and rises to about 12,000 ft (3,658
m) on the west. It encompasses
numerous areas from 12,000 to over
14,000 ft (3,658–4,267 m). This unit was
occupied at the time of listing
(Wehausen 1996, p. 477; Sierra Nevada
Bighorn Sheep Interagency Advisory
Group 1997, pp. 6–7; Wehausen 1999,
pp. 5–6, 8; 2000, pp. 3–5, 7; 65 FR 20,
January 3, 2000) and is currently
occupied with a minimum population
estimate of 113 individuals (Wehausen
and Stephenson 2006, p. 7). Unit 4
contains features that are essential to the
conservation of the Sierra Nevada
bighorn sheep. It contains steep, rocky
terrain which provides for foraging
(summer and winter), mating, lambing,
predator avoidance, and bedding and
also allows for seasonal elevational
movements; contains a range of
vegetation types (PCE 1 and PCE 2)
(Johnson et al. 2005, pp. 4–14, 31–32,
34, 37–38; Service 2007, pp. 3–5); and
contains/provides mineral licks (PCE 3)
(Stephenson 2007, p. 1). The area
around Wheeler Ridge provides
minimum elevation winter habitat at
5,578 ft (1,700 m) and is visually open
(Service 2007, p. 127). Mount Tom is
located south of Wheeler Ridge and
provides an open winter visual
condition and winter habitat at a
minimum elevation of 6,398 ft (1,950 m)
in Elderberry Canyon (Service 2007, p.
127, 129–130). High-elevation winter
habitat is extensive on the west side of
Mount Tom’s north ridge. Narrow ridges
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on the south side can be snow free.
Between Basin Mountain and Mount
Humphreys, the plateau remains snow
free and is accessible to sheep traveling
ridge lines from Mount Tom by Four
Gables and along the crest.
The essential features found within
Unit 4 may require special management
considerations or protection to
ameliorate the threats of overgrazing.
Additionally, PCEs within this unit may
require special management
considerations or protection to reverse
the impacts of fire suppression which
would provide more open habitat and
potentially reduce predation. Finally,
PCEs within Unit 4 may require special
management considerations or
protection for the threats due to mining,
development, and recreation (e.g., Pine
Creek area), and avalanche control may
be needed to protect against
catastrophic events.
Unit 5: Taboose Creek
Unit 5 consists of approximately
28,805 ac (11,657 ha) in Inyo and Fresno
Counties. Unit 5 is generally located
within an area bounded on the north by
Big Pine Creek and on the south by
Taboose Creek. U.S. Highway 395 is
about 8.5 mi (13.7 km) to the east, and
Marion and Observation Peaks are
located to the west. This unit is located
about 5 mi (8 km) southwest of Big Pine.
Land ownership within the unit
includes approximately 28,805 ac
(11,657 ha) of Federal land administered
by the Inyo National Forest and Kings
Canyon National Park.
Unit 5 begins at a low elevation of
about 6,000 ft (1,829 m) on the eastern
slope and rises to 12,000 to over 14,000
ft (3,658–4,267 m) on the west. This unit
was not occupied at the time of listing
and is not currently occupied, but the
unit is essential to the conservation of
the Sierra Nevada bighorn sheep. The
unit contains steep, rocky terrain which
provides for foraging (summer and
winter), mating, lambing, predator
avoidance, and bedding and also allows
for seasonal elevational movements, and
a range of vegetation types (PCE 1 and
PCE 2) (Johnson et al. 2005, pp. 4–14,
31–32, 34, 37–38; Service 2007, pp. 3–
5). Mineral licks (PCE 3) may or may not
occur in this unit. High windblown
areas (9,187 ft (2,800 m)) occur on Birch
and Kid Mountains that may support
bighorn sheep. There appears to be
limited low-elevation south- or eastfacing habitat unless animals move
south to Red Mountain or Taboose
Creeks. Taboose Creek offers patches of
high-elevation winter habitat and southfacing, low-elevation habitat where it
occurs as low as 6,398 ft (1,950 m). The
northeast side of Kid Mountain provides
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some low habitat near 7,218 ft (2,200 m)
(Service 2007, pp. 128, 132). The winter
range visual condition is open in these
areas (Service 2007, p. 128).
While this unit was not occupied at
the time of listing, Sierra Nevada
bighorn sheep occupied the area
historically (Ober 1914, p. 125; Jones
1950, p. 38; Buechner 1960, 69;
Dunaway 1971 p. 19; Wehausen et al.
1987 p. 66; Wehausen 1988a, p. 101;
Berger 1990, p. 94). This unit is
essential to the conservation of the
Sierra Nevada bighorn sheep for
increasing the number of herds to
reduce the significance of losing any
particular herd, increasing population
viability, decreasing the degree of
fragmentation of the current geographic
distribution between this unit and Units
6 (Sawmill Canyon) and 4 (Wheeler
Ridge), increasing opportunities for
genetic exchange between these units,
and increasing overall herd numbers to
reduce extinction risk from stochastic
events. Conservation of this unit is
necessary to achieve the long-term
viability of this subspecies within its
range.
Unit 6: Sawmill Canyon
Unit 6 consists of about 30,508 ac
(12,346 ha) in Fresno and Inyo Counties.
Unit 6 is generally located within an
area bounded on the east by U.S.
Highway 395 (located about 3 mi (4.8
km) away), on the south by Unit 7
(Mount Baxter) and Sawmill Pass and
Creek, on the west by Woods Creek and
the South Fork of Woods Creek, and on
the north by Taboose Creek. Land
ownership within the unit includes
approximately 30,508 ac (12,346 ha) of
Federal land administered by the Inyo
National Forest and Kings Canyon
National Park.
Unit 6 begins at a low elevation of
about 4,500 ft (1,372 m) on the eastern
slope and rises to about 10,500 to over
14,000 ft (3,200–4,267 m). Unit 6 was
occupied at the time of listing
(Wehausen 1996, p. 477; Sierra Nevada
Bighorn Sheep Interagency Advisory
Group 1997, pp. 6–7; Wehausen 1999,
pp. 4–5, 8; 2000, pp. 3, 7; 65 FR 20,
January 3, 2000) and is currently
occupied with a minimum population
estimate of 36 individuals (Wehausen
and Stephenson 2006, p. 7). Unit 6 has
features that are essential to the
conservation of the Sierra Nevada
bighorn sheep. It contains steep, rocky
terrain which provides for foraging
(summer and winter), mating, lambing,
predator avoidance, and bedding and
also allows for seasonal elevational
movements, and a range of vegetation
types (PCE 1 and PCE 2) (Johnson et al.
2005, pp. 4–14, 31–32, 34, 37–38;
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13:15 Aug 04, 2008
Jkt 214001
Service 2007, pp. 3–5). It is not known
if mineral licks (PCE 3) occur on this
unit. Unit 6 provides foraging habitat at
the northern boundary near Mount
Pinchot (Service 2007, p. 132). In
addition, minimum elevations of winter
habitat occur in the Goodale Creek area
at 6,890 ft (2,100 m) and in the Sawmill
Creek area at 4,922 ft (1,500 m); winter
visual condition is open (Service 2007,
p. 128).
The essential features found within
Unit 6 may require special management
considerations or protection to reverse
the impacts of fire suppression which
would provide more open habitat and
potentially reduce predation. The PCEs
in Unit 6 may also require special
management considerations or
protection for threats due to recreation,
and avalanche control may be needed to
protect against catastrophic events.
Unit 7: Mount Baxter
Unit 7 consists of approximately
32,220 ac (13,039 ha) in Fresno and Inyo
Counties. Unit 7 is generally located
within an area bounded on the east by
U.S. Highway 395 (located about 3 mi
(4.8 km) away); on the south by Bubbs
Creek and Forest Route 13S17 to
Independence; on the west by Mount
Bago, Gardiner Lakes, and Mount
Clarence King; and on the north by Unit
6 (Sawmill Canyon) and Sawmill Pass
and Creek. This unit is located about 6
mi (9.7 km) west of Independence. Land
ownership within the unit includes
approximately 32,198 ac (13,030 ha) of
Federal land and 22 ac (9 ha) of private
land. Federal land is administered by
the Inyo National Forest and Kings
Canyon National Park.
Unit 7 begins at a low elevation of
about 4,500 ft (1,372 m) on the eastern
slope and rises to about 10,500 to 12,000
ft (3,200–3,658 m) on the west. It
encompasses areas from 12,000 to over
14,000 ft (3,658–4,267 m). Unit 7 was
occupied at the time of listing
(Wehausen 1996, p. 477; Sierra Nevada
Bighorn Sheep Interagency Advisory
Group 1997, pp. 6–7; Wehausen 1999,
pp. 3–4, 8; 2000, pp. 2–3, 7; 65 FR 20,
January 3, 2000) and is currently
occupied with a minimum population
estimate of 69 individuals (Wehausen
and Stephenson 2006, p. 7). Unit 7
contains features that are essential to the
conservation of the Sierra Nevada
bighorn sheep. It contains steep, rocky
terrain which provides for foraging
(summer and winter), mating, lambing,
predator avoidance, and bedding and
also allows for seasonal elevational
movements; contains a range of
vegetation types (PCE 1 and PCE 2)
(Johnson et al. 2005, pp. 4–14, 31–32,
34, 37–38; Service 2007, pp. 3–5); and
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contains mineral licks (PCE 3) (Jones
1950, p. 63; Hicks and Elder 1979, p.
911). This unit provides foraging habitat
along the ridges and in drainages of
Mount Baxter. Minimum elevations of
winter habitat in the Thibaut-Sand
Mountain area occur at 5,003 ft (1,525
m), and in the Onion Valley area at
7,546 ft (2,300 m); winter visual
condition is open (Service 2007, p. 128).
In addition to containing the features
essential to the conservation of the
Sierra Nevada bighorn sheep, Unit 7 has
additional conservation value as it
served as a source population, due to its
size and productivity, for
reintroductions to the Wheeler Crest
area (1979, 1980, 1982, 1986, 1988),
Mount Langley (1980 and 1982), and
Lee Vining Canyon area (1986, 1988)
(Sierra Nevada Bighorn Sheep
Interagency Advisory Group 1997, p. 6).
Individuals from this population may be
used for future translocations within the
range.
The essential features found within
Unit 7 may require special management
considerations or protection to reverse
the impacts of fire suppression which
would provide more open habitat and
potentially reduce predation. PCEs
within Unit 7 also may require special
management considerations or
protection for threats due to recreation
(e.g., Baxter Pass and Onion Valley), and
avalanche control may be needed to
protect against catastrophic events.
Unit 8: Mount Williamson
Unit 8 consists of about 32,560 ac
(13,177 ha) in Inyo and Tulare Counties.
Unit 8 is generally located within an
area bounded on the east by U.S. 395
(located about 9 mi (14.5 km) away); on
the south by Tulainyo Lake; on the west
by the Kern River (located about 3.5
miles (5.6 km) away); and on the north
by Forest Route 13S17 to Independence
(located about 1.5 mi (2.4 km) away).
This unit is located southwest of
Independence and northwest of Lone
Pine. Land ownership within the unit
includes approximately 32,560 ac
(13,177 ha) of Federal land administered
by the Inyo National Forest and Sequoia
and Kings Canyon National Parks.
Unit 8 begins at a low elevation of
about 6,000 ft (1,829 m) on the eastern
slope and rises to 12,000 to over 14,000
ft (3,658–4,267 m) on the west. Unit 8
was occupied at the time of listing
(Wehausen 1996, p. 477; Sierra Nevada
Bighorn Sheep Interagency Advisory
Group 1997, pp. 6–7; Wehausen 1999,
pp. 2–3, 8; 2000, pp. 1–2, 7; 65 FR 20,
January 3, 2000) and is currently
occupied with a minimum population
estimate of 20 individuals (Wehausen
and Stephenson 2006, p. 7). Unit 8
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contains features that are essential to the
conservation of the Sierra Nevada
bighorn sheep. The unit contains steep,
rocky terrain which provides for
foraging (summer and winter), mating,
lambing, predator avoidance, and
bedding and also allows for seasonal
elevational movements, and a range of
vegetation types (PCE 1 and PCE 2)
(Johnson et al. 2005, pp. 4–14, 31–32,
34, 37–38; Service 2007, pp. 3–5). It is
not known if mineral licks (PCE 3) occur
in this unit. The Shepherd Creek-Pinyon
Creek area in this unit offers winter
habitat at a minimum elevation of 6,808
ft (2,075 m); the George Creek-North
Bairs Creek provides this habitat at
6,234 ft (1,900 m) (Service 2007, p. 128).
The winter visual condition is mixed
(Service 2007, p. 128).
The essential features found within
Unit 8 may require special management
considerations or protection to reverse
the impacts of fire suppression which
would provide more open habitat and
potentially reduce predation. This unit
could provide an estimated additional
2.2 sq mi (5.8 sq km) of winter range
with a relative probability of equal to or
greater than 10 percent use if forests
were reduced by burning (Johnson et al.
2005, p. 34). PCEs within Unit 8 may
require special management
considerations or protection to
ameliorate the possible threat of
overgrazing due to the proximity of this
unit to Federal grazing allotments.
Furthermore, PCEs within Unit 8 also
may require special management
considerations or protection for threats
due to recreation (e.g., Whitney Portal
and Trailhead), and avalanche control
may be needed to protect against
catastrophic events.
Unit 9: Big Arroyo
Unit 9 consists of approximately
24,987 ac (10,112 ha) in Tulare County.
Unit 9 is generally located within an
area bounded on the east by the Kern
River; on the north by Kern-Kaweah
River, Junction Meadow, and Wallace
Creek area; and on the west and south
by the Big Arroyo Creek. Land
ownership within the unit includes
approximately 24,987 ac (10,112 ha) of
Federal land is administered by Sequoia
National Park.
Unit 9 begins at a low elevation of
about 6,500 ft (1,981 m) on the eastern
slope and rises to about 12,000 ft (3,658
m) on the west. The northern boundary
encompasses areas from 12,000 to over
14,000 ft (3,658–4,267 m). This unit was
not occupied at the time of listing and
is not currently occupied, but is
essential to the conservation of Sierra
Nevada bighorn sheep. The unit
contains steep, rocky terrain which
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provides for foraging (summer and
winter), mating, lambing, predator
avoidance, and bedding and also allows
for seasonal elevational movements, and
a range of vegetation types (PCE 1 and
PCE 2) (Johnson et al. 2005, pp. 4–14,
31–32, 34, 37–38; Service 2007, pp. 3–
5). It is not known if mineral licks (PCE
3) are located within this unit. This unit
contains no high-elevation wind-swept
areas (Service 2007, p. 134). Winter
habitat is provided at a minimum
elevation of 6,890 ft (2,100 m) with a
mixed visual condition due to scattered
trees (Service 2007, pp. 128, 134). From
the upper end of the Big Arroyo
drainage, sheep could find access to
alpine habitat on Kaweah Peaks.
While this unit was not occupied at
the time of listing, Sierra Nevada
bighorn sheep occupied the area
historically (Jones 1950, p 35; Buecher
1960, p. 69; Barrett 1965, p. 43;
Riegelhuth 1965, p. 35; Wehausen
1988b, p. 100). This unit is essential to
the conservation of the Sierra Nevada
bighorn sheep for increasing the number
of herds to reduce the significance of
losing any particular herd, increasing
population viability, decreasing the
degree of fragmentation of the current
geographic distribution between this
unit and Units 8 (Mount Williamson),
and 10 (Mount Langley), increasing
opportunities for genetic exchange
between these units, and increasing
overall herd numbers to reduce
extinction risk from stochastic events.
Conservation of this unit is necessary to
achieve the long-term viability of this
subspecies within its range.
Unit 10: Mount Langley
Unit 10 consists of approximately
32,845 ac (13,292 ha) in Inyo and Tulare
Counties. Unit 10 is generally located
within an area bounded on the east by
Forest Route 16S02 located from
immediately adjacent to the unit to 7 mi
(11.3 km) away, on the south by Muah
Mountain, on the west by Cirque Peak
and the Perrin Creek area, and on the
north by Lone Pine Creek. This unit is
located about 7 mi (11.3 km) southwest
of Lone Pine. Land ownership within
the unit includes approximately 32,845
ac (13,292 ha) of Federal land
administered by the Inyo National
Forest, Sequoia National Park, and
Bureau of Land Management.
Unit 10 begins at a low elevation of
about 4,500 ft (1,372 m) on the eastern
slope and rises to 9,000 to 12,000 ft
(2,743–3,658 m) on the west side. It
encompasses areas between 12,000 and
14,000 ft (3,658–4,267 m). Unit 10 was
occupied at the time of listing
(Wehausen 1996, p. 477; Sierra Nevada
Bighorn Sheep Interagency Advisory
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Group 1997, pp. 6–7; Wehausen 1999,
pp. 1–2, 8; 2000, pp. 1, 7; 65 FR 20,
January 3, 2000) and is currently
occupied with a minimum population
estimate of 90 individuals (Wehausen
and Stephenson 2006, p. 7). Unit 10
contains features that are essential to the
conservation of the Sierra Nevada
bighorn sheep. The unit contains steep,
rocky terrain which provides for
foraging (summer and winter), mating,
lambing, predator avoidance, and
bedding and also allows for seasonal
elevational movements, and a range of
vegetation types (PCE 1 and PCE 2)
(Johnson et al. 2005, pp. 4–14, 31–32,
34, 37–38; Service 2007, pp. 3–5). It is
not known if mineral licks (PCE 3) occur
in this unit. The unit provides low
elevation (5,742 ft, 1,750 m) mixed
winter range in the Carroll Creek-Turtle
Creek area. It also provides lowelevation (4,757 ft, 1,450 m), open
winter range in the Slide CanyonCottonwood Creek area (Service 2007,
pp. 128, 133). From this area, it is
possible that bighorn sheep could cross
a short distance of the open south-facing
forest by Wonoga Peak to access the
large open plateau country. It is also
possible that bighorn sheep using the
Cottonwood Creek area use summer
range to the southeast of the Kern
Plateau where elevations are about
10,000 ft (3,048 m) (Service 2007, p.
130).
The essential features found within
Unit 10 may require special
management considerations or
protection to reverse the impacts of fire
suppression which would provide more
open habitat and potentially reduce
predation. This unit could provide an
estimated additional 1.8 sq mi (4.7 sq
km) of winter range with a relative
probability of equal to or greater than 10
percent use if forests were reduced by
burning (Johnson et al. 2005, p. 34).
PCEs within Unit 10 may require special
management considerations or
protection to ameliorate the possible
threat of overgrazing due to the
proximity of this unit to Federal grazing
allotments. PCEs within Unit 10 may
also require special management
considerations or protection for threats
due to recreation (e.g., Whitney Portal
and Trailhead) and development (Forest
Route 16S02 crosses a portion of this
unit). Furthermore, PCEs within Unit 10
may require special management
considerations or protection in the form
of avalanche control to protect against
catastrophic events.
Unit 11: Laurel Creek
Unit 11 consists of approximately
22,037 ac (8,918 ha) in Tulare County.
Unit 11 is generally located within an
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area bounded on the east by the Kern
River; on the south by Pistol, Laurel,
and Golden Trout Creeks; on the west
by a portion of Little Kern River; and on
the north by Soda Creek. Land
ownership within the unit includes
approximately 22,037 ac (8,918 ha) of
Federal land administered by the
Sequoia National Forest and Sequoia
National Park.
Unit 11 begins at a low elevation of
about 6,500 ft (1,981 m) on the eastern
slope and rises to 10,500 to 12,000 ft
(3,200–3,658 m) on the west. It includes
a few small areas from 12,000 to over
14,000 ft (3,658–4,267 m). This unit was
not occupied at the time of listing and
is not currently occupied, but the unit
is essential to the conservation of Sierra
Nevada bighorn sheep. The unit
contains steep, rocky terrain which
provides for foraging (summer and
winter), mating, lambing, predator
avoidance, and bedding and also allows
for seasonal elevational movements, and
a range of vegetation types (PCE 1 and
PCE 2) (Johnson et al. 2005, pp. 4–14,
31–32, 34, 37–38; Service 2007, pp. 3–
5). It is unknown whether mineral licks
(PCE 3) occur in this unit. This unit
contains no high-elevation wind-swept
areas (Service 2007, p. 134). Winter
habitat is provided at a minimum
elevation of 6,808 ft (2,075 m) with a
mixed visual condition due to scattered
trees (Service 2007, pp. 128, 134).
Laurel Creek provides access to summer
range.
While this unit was not occupied at
the time of listing, Sierra Nevada
bighorn sheep occupied the area
historically (Buechner 1960 p. 69;
Barrett 1965, p. 43; Wehausen 1988b, p.
100). This unit is essential to the
conservation of the Sierra Nevada
bighorn sheep for increasing the number
of herds to reduce the significance of
losing any particular herd, increasing
population viability, decreasing the
degree of fragmentation of the current
geographic distribution between this
unit and Unit 10 (Mount Langley),
increasing opportunities for genetic
exchange between these units, and
increasing overall herd numbers to
reduce extinction risk from stochastic
events. Conservation of this unit is
necessary to achieve the long-term
viability of this subspecies within its
range.
Unit 12: Olancha Peak
Unit 12 consists of approximately
30,421 ac (12,311 ha) in Tulare and Inyo
Counties. Unit 12 is generally located
within an area bounded on the east by
U.S. Highway 395, on the south by Falls
and Walker Creeks, on the west by a
portion of the Pacific Crest National
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Scenic Trail, and on the north by Muah
Mountain. This unit is located west of
the towns of Cartago and Olancha. Land
ownership within the unit includes
approximately 30,421 ac (12,311 ha) of
Federal land administered by the Inyo
National Forest and Bureau of Land
Management.
Unit 12 begins at a low elevation of
about 4,000 ft (1,219 m) on the eastern
slope and rises to about 9,000 to 10,500
ft (2,743–3,200 m) on the west. It is the
southernmost unit designated as critical
habitat for the Sierra Nevada bighorn
sheep. This unit was not occupied at the
time of listing and is not currently
occupied, but is essential to the
conservation of the Sierra Nevada
bighorn sheep. The unit contains steep,
rocky terrain which provides for
foraging (summer and winter), mating,
lambing, predator avoidance, and
bedding and also allows for seasonal
elevational movements, and a range of
vegetation types (PCE 1 and PCE 2)
(Johnson et al. 2005, pp. 4–14, 31–32,
34, 37–38; Service 2007, pp. 3–5). It is
not known if mineral licks (PCE 3) occur
within this unit. This unit provides
bighorn sheep habitat in the areas of
Ash, Braley, Cartago, Olancha, and Falls
Creeks. Cartago, Olancha and Falls
Creeks connect by Olancha Canyon to
Olancha Peak (12,123 ft, 3,695 m) which
provides some alpine summer habitat
(southernmost in the Sierra Nevada)
(Service 2007, p. 133). Winter range
occurs as open, low-elevation (4,757 ft,
1,450 m), south-facing slopes (Service
2007, pp. 128, 133).
While this unit was not occupied at
the time of listing, Sierra Nevada
bighorn sheep occupied the area
historically (Jones 1950, p. 39;
Wehausen et al. 1987, p. 66; Wehausen
1988a, p. 101). This unit is essential to
the conservation of the Sierra Nevada
bighorn sheep for increasing the number
of herds to reduce the significance of
losing any particular herd, increasing
population viability, decreasing the
degree of fragmentation of the current
geographic distribution between this
unit and Unit 10 (Mount Langley),
increasing opportunities for genetic
exchange between these units, and
increasing overall herd numbers to
reduce extinction risk from stochastic
events. Conservation of this unit is
necessary to achieve the long-term
viability of this subspecies within its
range.
Effects of Critical Habitat Designation
Section 7 Consultation
Section 7(a)(2) of the Act requires
Federal agencies to ensure that actions
they fund, authorize, or carry out are not
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likely to jeopardize the continued
existence of a listed species or destroy
or adversely modify designated critical
habitat. Decisions by the Fifth and
Ninth Circuit Courts of Appeals have
invalidated our definition of
‘‘destruction or adverse modification’’
(50 CFR 402.02) (see Gifford Pinchot
Task Force v. U.S. Fish and Wildlife
Service, 378 F. 3d 1059 (9th Cir 2004)
and Sierra Club v. U.S. Fish and
Wildlife Service et al., 245 F. 3d 434,
442F (5th Cir 2001)), and we do not rely
on this regulatory definition when
analyzing whether an action is likely to
destroy or adversely modify critical
habitat. Under the statutory provisions
of the Act, we determine destruction or
adverse modification on the basis of
whether, with implementation of the
proposed Federal action, the affected
critical habitat would remain functional
(or retain the current ability for the PCEs
to be functionally established) to serve
its intended conservation role for the
species.
Under section 7(a)(2) of the Act, if a
Federal action may affect a listed
species or its critical habitat, the
responsible Federal agency (action
agency) must enter into consultation
with us. As a result of this consultation,
we document compliance with the
requirements of section 7(a)(2) through
our issuance of:
(1) A concurrence letter for Federal
actions that may affect, but are not
likely to adversely affect, listed species
or critical habitat; or
(2) A biological opinion for Federal
actions that are likely to adversely affect
listed species or critical habitat.
When we issue a biological opinion
concluding that a project is likely to
jeopardize the continued existence of a
listed species or destroy or adversely
modify critical habitat, we also provide
reasonable and prudent alternatives to
the project, if any are identifiable. We
define ‘‘Reasonable and prudent
alternatives’’ at 50 CFR 402.02 as
alternative actions identified during
consultation that:
• Can be implemented in a manner
consistent with the intended purpose of
the action,
• Can be implemented consistent
with the scope of the Federal agency’s
legal authority and jurisdiction,
• Are economically and
technologically feasible, and
• Would, in the Director’s opinion,
avoid jeopardizing the continued
existence of the listed species or
destroying or adversely modifying
critical habitat.
Reasonable and prudent alternatives can
vary from slight project modifications to
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extensive redesign or relocation of the
project. Costs associated with
implementing a reasonable and prudent
alternative are similarly variable.
Regulations at 50 CFR 402.16 require
Federal agencies to reinitiate
consultation on previously reviewed
actions in instances where we have
listed a new species or subsequently
designated critical habitat that may be
affected and the Federal agency has
retained discretionary involvement or
control over the action (or the agency’s
discretionary involvement or control is
authorized by law). Consequently,
Federal agencies may sometimes need to
request reinitiation of consultation with
us on actions for which formal
consultation has been completed, if
those actions with discretionary
involvement or control may affect
subsequently listed species or
designated critical habitat.
Federal activities that may affect the
Sierra Nevada bighorn sheep or its
designated critical habitat will require
section 7(a)(2) consultation under the
Act. Activities on State, Tribal, local or
private lands requiring a Federal permit
(such as a permit from the U.S. Army
Corps of Engineers under section 404 of
the Clean Water Act (33 U.S.C. 1251 et
seq.) or involving some other Federal
action (such as funding from the Federal
Highway Administration, Federal
Aviation Administration, or the Federal
Emergency Management Agency) or a
permit from us under section 10(a)(1)(B)
of the Act) are examples of agency
actions that may be subject to the
consultation process under section
7(a)(2) of the Act. Federal actions not
affecting listed species or critical
habitat, and actions on State, Tribal,
local or private lands that are not
Federally funded, authorized, or carried
out, do not require section 7(a)(2)
consultations.
Application of the ‘‘Adverse
Modification’’ Standard
The key factor related to the adverse
modification determination is whether,
with implementation of the proposed
Federal action, the affected critical
habitat would remain functional (or
retain the current ability for the PCEs to
be functionally established) to serve its
intended conservation role for the
species. Activities that may result in the
destruction or adverse modification of
critical habitat are those that alter the
physical and biological features to an
extent that appreciably reduces the
conservation value of critical habitat for
Sierra Nevada bighorn sheep. Generally,
the conservation role of Sierra Nevada
bighorn sheep critical habitat units is to
support viable core area populations.
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Section 4(b)(8) of the Act requires us
to briefly evaluate and describe in any
proposed or final regulation that
designates critical habitat, activities
involving a Federal action that may
result in the destruction or adverse
modification of such habitat, or that
may be affected by such designation.
Activities that, when carried out,
funded, or authorized by a Federal
agency, may affect critical habitat and,
therefore, should result in consultation
for Sierra Nevada bighorn sheep
include, but are not limited to:
(1) Actions that would significantly
reduce ongoing management and
conservation efforts that benefit the
Sierra Nevada bighorn sheep on public
lands. Such activities could include, but
are not limited to, the sale, exchange, or
lease of lands managed by the USFS or
other Federal agency. These activities
could reduce the amount of space that
is available for individual and
population growth and normal behavior,
as well as reduce or eliminate the
number and extent of sites for foraging,
breeding, reproduction, and rearing of
offspring. These activities could also
reduce the opportunities available to
Federal agencies to exercise their
section 7(a)(1) authorities to carry out
programs to conserve listed species.
(2) Actions that would significantly
reduce the availability of or accessibility
to summer and winter ranges. Such
activities could include, but are not
limited to, grazing, mining, and road
construction activities. These activities
could degrade, reduce, fragment or
eliminate available foraging resources or
alter current foraging activities of Sierra
Nevada bighorn sheep.
(3) Actions that would result in the
significant expansion of tall, dense
vegetation, such as timber, within
bighorn sheep habitat. Such activities
could include, but are not limited to,
fire suppression. These activities could
allow expansion of vegetation cover
such that movement patterns of bighorn
sheep are altered by avoidance of these
areas. Tall, dense vegetation provides
cover for predators such as the
mountain lion, a common predator of
Sierra Nevada bighorn sheep.
(4) Actions that would create
significant barriers to movement. Such
activities could include, but are not
limited to, road construction and resort
or campground facility development or
expansion. These activities could
interfere with movement within and
between habitats reducing the
availability of habitat for foraging,
breeding, reproduction, sheltering, and
rearing of offspring. These activities
could also reduce opportunities for
movement between existing
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populations. Dispersal and interaction
between populations could be affected,
restricting gene flow and jeopardizing
the integrity of the gene pool. Road
construction can result in the direct
mortality of individuals through
collisions with vehicles.
(5) Actions that would significantly
degrade habitat or cause a disturbance
to Sierra Nevada bighorn sheep. Such
activities could include, but are not
limited to, recreational activities, such
as hiking, camping, rock and ice
climbing, outfitter guides and pack
animal expeditions, snowmobiling, and
off-road vehicle use. These activities
could impact the quality and quantity of
forage across the landscape, or displace
animals from key foraging areas. These
activities could also impact the
accessibility to key habitats such as
escape terrain, breeding sites, or
lambing areas. If animals flee these areas
as a result of these activities, energy is
expended which can negatively impact
the animal’s body condition, resulting
in possible reduced reproductive
success.
We consider all of the units
designated as critical habitat to contain
features essential to the conservation of
the Sierra Nevada bighorn sheep,
including those units which were not
occupied at the time of listing. All units
are within the historical geographic
range of the subspecies, and those units
which were not occupied at the time of
listing have been determined to be
essential for the conservation of the
Sierra Nevada bighorn sheep. Detailed
descriptions of the units and their
occupancy status can be found in each
of the unit descriptions or within Table
3. Under section 7 of the Act, Federal
agencies already consult with us on
activities in areas currently occupied by
the Sierra Nevada bighorn sheep, or if
the subspecies may be affected by the
action, the consultation is to ensure that
their actions do not jeopardize the
continued existence of the Sierra
Nevada bighorn sheep.
Exclusions
Application of Section 4(b)(2) of the Act
Section 4(b)(2) of the Act states that
the Secretary must designate and revise
critical habitat on the basis of the best
available scientific data after taking into
consideration the economic impact,
impact on national security, and any
other relevant impact of specifying any
particular area as critical habitat. The
Secretary may exclude an area from
critical habitat if he determines that the
benefits of such exclusion outweigh the
benefits of specifying such area as part
of the critical habitat, unless he
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determines, based on the best scientific
data available, that the failure to
designate such area as critical habitat
will result in the extinction of the
species. In making that determination,
the statute on its face, as well as the
legislative history are clear that the
Secretary has broad discretion regarding
which factor(s) to use and how much
weight to give to any factor.
Under section 4(b)(2) of the Act, in
considering whether to exclude a
particular area from the designation, we
must identify the benefits of including
the area in the designation, identify the
benefits of excluding the area from the
designation, and determine whether the
benefits of exclusion outweigh the
benefits of inclusion. If we consider an
area for exclusion, then we must
determine whether excluding the area
would result in the extinction of the
species.
In the following sections, we address
a number of general issues that are
relevant to the exclusions we are
considering. In addition, we conducted
an economic analysis of the impacts of
the proposed critical habitat designation
and related factors, which was available
for public review and comment. Based
on public comment on that document,
the proposed designation itself, and the
information in the final economic
analysis, the Secretary may exclude
from critical habitat additional areas
beyond those identified in this
assessment under the provisions of
section 4(b)(2) of the Act. This is also
addressed in our implementing
regulations at 50 CFR 242.19.
Currently, we are aware of four
documents related to the conservation
and recovery of the Sierra Nevada
bighorn sheep. We reviewed these
documents, but we are not excluding
lands covered by them for reasons
indicated below. These documents
include the Sierra Nevada Bighorn
Sheep Recovery and Conservation Plan
(Sierra Nevada Bighorn Sheep
Interagency Advisory Group 1984), the
Bighorn Sheep Management Plan
(National Park Service 1986), the Inyo
National Forest Resource & Management
Plan (U.S. Forest Service 1988), and A
Conservation Strategy for Sierra Nevada
Bighorn Sheep (Sierra Nevada Bighorn
Sheep Interagency Advisory Group
1997). All of these documents were
prepared prior to the emergency listing
of the Sierra Nevada bighorn sheep in
1999.
The goal of the Sierra Nevada Bighorn
Sheep Recovery and Conservation Plan
(Sierra Bighorn Sheep Interagency
Advisory Group 1984, pp. 1–2) was to
improve the status of the Sierra Nevada
bighorn sheep by: (1) Maintaining the
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health and viability of existing
populations and promoting the
establishment of at least three
populations that exceeded 100 animals
and were geographically distant from
one another; (2) restoring bighorn sheep
to former ranges within the Sierra
Nevada where ecologically,
economically, and politically feasible
and where favorable to their success;
and (3) ensuring genetic integrity by
using only bighorn sheep from existing
Sierra Nevada populations to restock
historical ranges. Conservation
recommendations made in A
Conservation Strategy for Sierra Nevada
Bighorn Sheep (Sierra Nevada Bighorn
Sheep Interagency Advisory Group
1997, pp. 11–14) include restoration of
the Sierra Nevada bighorn sheep in a
distribution that assures long-term
viability and reestablishment
throughout its native range and
preservation of current populations,
predator control, fire (let burn policy),
addressing grazing by domestic sheep
and goats, ensuring genetic diversity,
reintroductions and augmentations, and
research and monitoring. The goal of the
Bighorn Sheep Management Plan
(National Park Service 1986, pp. 1–2)
was to restore and perpetuate bighorn
sheep and to protect the integrity of the
ecosystem. Management was directed
toward restoring and maintaining
populations of bighorn sheep for
ecological, scientific, educational,
aesthetic, and recreational values. The
Inyo National Forest’s Land & Resource
Management Plan (U.S. Forest Service
1988, pp. 101–102) provided guidance
to maintain existing sheep habitat,
expand the range of bighorn sheep by
transplanting animals into suitable
unoccupied habitats within the
historical range, maintain the health of
existing herds by not allowing an
increase in livestock use if disease
transmission was shown to be harmful
to bighorn sheep, and prohibit the
conversion of livestock type from cattle
to sheep on or adjacent to existing or
approved reintroduction sites for the
bighorn sheep.
The Inyo National Forest also
established two California Bighorn
Sheep Zoological Areas for the Mount
Baxter and Mount Williamson herds.
These areas totaled 4,505 ac (1,823 ha)
in addition to existing wilderness lands
(36,235 ac, 14,664 ha)) occupied by
bighorn sheep. In 1981, forest officials
issued Order No. 04–81–3, which
prohibited entrance into these areas
without a valid visitor use permit,
restricted entrance into closed portions
of the zoological areas during certain
time periods, restricted the presence of
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dogs, and restricted the discharge of
firearms unless taking a game animal
legally permitted by the State of
California (U.S. Forest Service 1981, p.
1). Exemptions were allowed for certain
individuals, duties, and activities. This
order was issued during a time when
recreational use was believed to be
detrimentally impacting the Mount
Baxter and Mount Williamson herds.
While these plans were prepared to
assist in the restoration and recovery
and habitat protection of the Sierra
Nevada bighorn sheep, they were
written prior to the final listing of this
subspecies in 2000, and they generally
offer only guidance and
recommendations related to
translocations, research, monitoring,
education, and habitat management
with little specificity of actions to be
implemented. The guidance provided in
these documents and the recreational
prohibitions in the California Bighorn
Sheep Zoological Areas did not provide
a basis for excluding lands covered by
them.
Economic Analysis
Section 4(b)(2) of the Act requires us
to designate critical habitat on the basis
of the best scientific information
available and to consider economic and
other relevant impacts of designating a
particular area as critical habitat.
Section 4(b)(2) of the Act allows the
Secretary to exclude areas from critical
habitat for economic reasons if the
Secretary determines that the benefits of
such exclusion outweigh the benefits of
designating the area as critical habitat.
However, this exclusion cannot occur if
it will result in the extinction of the
species concerned.
Following the publication of the
proposed critical habitat designation,
we conducted an economic analysis to
estimate the potential economic effect of
the designation. The draft analysis was
made available for public review on
February 5, 2008 (73 FR 6684). We
accepted comments on the draft analysis
until March 6, 2008. Following the close
of the comment period, a final analysis
of the potential economic effects of the
designation was developed taking into
consideration the public comments and
any relevant new information.
The primary purpose of the EA is to
estimate the potential economic impacts
associated with the designation of
critical habitat for the Sierra Nevada
bighorn sheep. This information is
intended to assist the Secretary in
making decisions about whether the
benefits of excluding particular areas
from the designation outweigh the
benefits of including those areas in the
designation. This EA considers the
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economic efficiency effects that may
result from the designation, including
habitat protections that may be coextensive with the listing of the species.
It also addresses distribution of impacts,
including an assessment of the potential
effects on small entities and the energy
industry. This information can be used
by the Secretary to assess whether the
effects of the designation might unduly
burden a particular group of the
economic sector.
The intent of the economic analysis is
to quantify the economic impacts of all
potential conservation efforts for the
Sierra Nevada bighorn sheep; some of
these costs will likely be incurred
regardless of whether we designate
critical habitat. The economic analysis
provides estimated costs of the
foreseeable potential economic impacts
of the critical habitat designation
(incremental impacts) and other
conservation-related actions (baseline
impacts) for this species over the next
20 years. It also considers past costs
associated with conservation of the
species from the time it was listed in
2000 (65 FR 20, January 3, 2000), until
the year the proposed critical habitat
rule was published (72 FR 40956, July
25, 2007).
The economic analysis considers the
potential economic effects of actions
relating to the conservation of the Sierra
Nevada bighorn sheep, including costs
associated with sections 4, 7, and 10 of
the Act, as well as those attributable to
the designation of critical habitat. It
further considers the economic effects of
protective measures taken as a result of
other Federal, State, and local laws that
aid habitat conservation for the Sierra
Nevada bighorn sheep in areas
containing features essential to the
conservation of the species. The
analysis considers both economic
efficiency and distributional effects. In
the case of habitat conservation,
efficiency effects generally reflect the
‘‘opportunity costs’’ associated with the
commitment of resources to comply
with habitat protection measures (such
as lost economic opportunities
associated with restrictions on land
use).
The economic analysis also addresses
how potential economic impacts are
likely to be distributed, including an
assessment of any local or regional
impacts of habitat conservation and the
potential effects of conservation
activities on government agencies,
private business, and individuals. The
analysis measures lost economic
efficiency associated with residential
and commercial development and
public projects and activities, such as
economic impacts on water
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management and transportation
projects, Federal lands, small entities,
and the energy industry. Decisionmakers can use this information to
assess whether the effects of the
designation might unduly burden a
particular group or economic sector.
Finally, the economic analysis looks
retrospectively at costs that have been
incurred since the date Sierra Nevada
bighorn sheep was listed as endangered
(65 FR 20, January 3, 2000) and
considers those costs that may occur in
the 20 years following the designation of
critical habitat. Forecasts of economic
conditions and other factors beyond this
point would be speculative.
Activities associated with the
conservation of the Sierra Nevada
bighorn sheep are likely to primarily
impact future domestic sheep grazing,
recreation management, and habitat
management. The EA forecasts baseline
economic impacts in the areas
designated. The present value of these
impacts, applying a 3 percent discount
rate, is $21.0 million ($1.41 million
annualized), or $15.5 million ($1.46
million annualized) using a 7 percent
discount rate. The EA forecasts the
present value of the incremental
economic impacts to be $120,000
($8,080 annualized), applying a 3
percent discount rate, or $94,900
($8,960 annualized) using a 7 percent
discount rate.
We evaluated the potential economic
impact of this designation as identified
in the economic analysis. Based on this
evaluation, we believe that there are no
disproportionate economic impacts that
warrant exclusion under section 4(b)(2)
of the Act at this time. The final
economic analysis is available at
https://www.regulations.gov and https://
www.fws.gov/nevada or upon request
from the Nevada Fish and Wildlife
Office (see ADDRESSES section).
After consideration of the impacts
under section 4(b)(2) of the Act, we have
not excluded any areas from the final
critical habitat designations based on
the identified economic impacts, any
impact on national security, and any
other relevant impacts.
Required Determinations
Regulatory Planning and Review
The Office of Management and Budget
(OMB) has determined that this rule is
not significant and has not reviewed
this rule under Executive Order 12866
(E.O. 12866). OMB bases its
determination upon the following four
criteria:
(a) Whether the rule will have an
annual effect of $100 million or more on
the economy or adversely affect an
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economic sector, productivity, jobs, the
environment, or other units of the
government.
(b) Whether the rule will create
inconsistencies with other Federal
agencies’ actions.
(c) Whether the rule will materially
affect entitlements, grants, user fees,
loan programs, or the rights and
obligations of their recipients.
(d) Whether the rule raises novel legal
or policy issues.
Regulatory Flexibility Act
Under the Regulatory Flexibility Act
(RFA; 5 U.S.C. 601 et seq.), as amended
by the Small Business Regulatory
Enforcement Fairness Act (SBREFA),
whenever an agency must publish a
notice of rulemaking for any proposed
or final rule, it must prepare and make
available for public comment a
regulatory flexibility analysis that
describes the effects of the rule on small
entities (i.e., small businesses, small
organizations, and small government
jurisdictions). However, no regulatory
flexibility analysis is required if the
head of the agency certifies the rule will
not have a significant economic impact
on a substantial number of small
entities. SBREFA amended RFA to
require Federal agencies to provide a
certification statement of the factual
basis for certifying that the rule will not
have a significant economic impact on
a substantial number of small entities.
In this final rule, we are certifying that
the critical habitat designation for Sierra
Nevada bighorn sheep will not have a
significant economic impact on a
substantial number of small entities.
The following discussion explains our
rationale.
According to the Small Business
Administration (SBA), small entities
include small organizations, such as
independent nonprofit organizations;
small governmental jurisdictions,
including school boards and city and
town governments that serve fewer than
50,000 residents; as well as small
businesses. Small businesses include
manufacturing and mining concerns
with fewer than 500 employees,
wholesale trade entities with fewer than
100 employees, retail and service
businesses with less than $5 million in
annual sales, general and heavy
construction businesses with less than
$27.5 million in annual business,
special trade contractors doing less than
$11.5 million in annual business, and
agricultural businesses with annual
sales less than $750,000. To determine
if potential economic impacts to these
small entities are significant, we
considered the types of activities that
might trigger regulatory impacts under
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this rule, as well as the types of project
modifications that may result. In
general, the term ‘‘significant economic
impact’’ is meant to apply to a typical
small business firm’s business
operations.
To determine if the rule could
significantly affect a substantial number
of small entities, we consider the
number of small entities affected within
particular types of economic activities
(e.g., housing development, grazing, oil
and gas production, timber harvesting).
We apply the ‘‘substantial number’’ test
individually to each industry to
determine if certification is appropriate.
However, the SBREFA does not
explicitly define ‘‘substantial number’’
or ‘‘significant economic impact.’’
Consequently, to assess whether a
‘‘substantial number’’ of small entities is
affected by this designation, this
analysis considers the relative number
of small entities likely to be impacted in
an area. In some circumstances,
especially with critical habitat
designations of limited extent, we may
aggregate across all industries and
consider whether the total number of
small entities affected is substantial. In
estimating the number of small entities
potentially affected, we also consider
whether their activities have any
Federal involvement.
Designation of critical habitat only
affects activities authorized, funded, or
carried out by Federal agencies. Some
kinds of activities are unlikely to have
any Federal involvement and so will not
be affected by critical habitat
designation. In areas where the species
is present, Federal agencies already are
required to consult with us under
section 7 of the Act on activities they
authorize, fund, or carry out that may
affect Sierra Nevada bighorn sheep (see
Section 7 Consultation section). Federal
agencies also must consult with us if
their activities may affect critical
habitat. Designation of critical habitat,
therefore, could result in an additional
economic impact on small entities due
to the requirement to reinitiate
consultation for ongoing Federal
activities (see Application of the
‘‘Adverse Modification’’ Standard
section).
In our economic analysis of the
critical habitat designation, we
evaluated the potential economic effects
on small business entities resulting from
conservation actions related to the
listing of the Sierra Nevada bighorn
sheep and the designation of critical
habitat. The analysis estimated
prospective economic impacts
associated with the proposed
rulemaking as described in Chapters 2
through 4 and Appendix A of the
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economic analysis and evaluates the
potential for economic impacts related
to three categories: Grazing, recreation
management, and habitat management.
The economic analysis identified one
domestic sheep grazing permittee
operating in the Humboldt-Toiyabe
National Forest, and two resorts and
unidentified outdoor pack companies
operating in the Humboldt-Toiyabe and
Inyo National Forests that qualify as
small businesses that could be impacted
due to their activities within areas
designated as critical habitat.
For the one grazing permittee, the
economic analysis estimates a cost of
$13,000 associated with conservation
activities for the Sierra Nevada bighorn
sheep over the next 20 years at a 3
percent discounted rate ($875
annualized). For the two resorts and
unidentified outdoor pack companies,
the analysis estimates a cost of $2,730
associated with conservation activities
for the Sierra Nevada bighorn sheep
over the next 20 years at a 3 percent
discounted rate ($183 annualized).
Incremental impacts are expected only
to occur in designated critical habitat
Units 1 and 2. This number of small
business entities is not considered a
substantial number.
The USFS is expected to incur
incremental costs as a result of this
designation, but it is not considered a
small entity by the SBA.
In summary, we have considered
whether the final rule would result in a
significant economic impact on a
substantial number of small entities.
Based on the above reasoning and
currently available information, we
certify that this rule will not have a
significant economic impact on a
substantial number of small business
entities. Therefore, a regulatory
flexibility analysis is not required.
Small Business Regulatory Enforcement
Fairness Act (5 U.S.C. 801 et seq.)
Under SBREFA, this rule is not a
major rule. Our detailed assessment of
the economic effects of this designation
is described in the economic analysis.
Based on the effects identified in the
economic analysis, we believe that this
rule will not have an annual effect on
the economy of $100 million or more,
will not cause a major increase in costs
or prices for consumers, and will not
have significant adverse effects on
competition, employment, investment,
productivity, innovation, or the ability
of U.S.-based enterprises to compete
with foreign-based enterprises. Refer to
the final economic analysis for a
discussion of the effects of this
determination (see ADDRESSES for
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information on obtaining a copy of the
final economic analysis).
Energy Supply, Distribution, or Use
On May 18, 2001, the President issued
an Executive Order (E.O. 13211;
‘‘Actions Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use’’) on regulations
that significantly affect energy supply,
distribution, and use. E.O. 13211
requires agencies to prepare Statements
of Energy Effects when undertaking
certain actions. OMB has provided
guidance for implementing this
Executive Order that outlines nine
outcomes that may constitute ‘‘a
significant adverse effect’’ when
compared without the regulatory action
under consideration. The economic
analysis finds that none of these criteria
are relevant to this analysis. Thus, based
on information in the economic
analysis, energy-related impacts
associated with Sierra Nevada bighorn
sheep conservation activities within the
final critical habitat designation are not
expected. As such, the designation of
critical habitat is not expected to
significantly affect energy supplies,
distribution, or use. Therefore, this
action is not a significant energy action,
and no Statement of Energy Effects is
required.
Unfunded Mandates Reform Act (2
U.S.C. 1501 et seq.)
In accordance with the Unfunded
Mandates Reform Act (2 U.S.C. 1501 et
seq.), we make the following findings:
(a) This rule will not produce a
Federal mandate. In general, a Federal
mandate is a provision in legislation,
statute, or regulation that would impose
an enforceable duty upon State, local, or
Tribal governments, or the private
sector, and includes both ‘‘Federal
intergovernmental mandates’’ and
‘‘Federal private sector mandates.’’
These terms are defined in 2 U.S.C.
658(5)–(7). ‘‘Federal intergovernmental
mandate’’ includes a regulation that
‘‘would impose an enforceable duty
upon State, local, or tribal governments’’
with two exceptions. It excludes ‘‘a
condition of Federal assistance.’’ It also
excludes ‘‘a duty arising from
participation in a voluntary Federal
program,’’ unless the regulation ‘‘relates
to a then-existing Federal program
under which $500,000,000 or more is
provided annually to State, local, and
tribal governments under entitlement
authority,’’ if the provision would
‘‘increase the stringency of conditions of
assistance’’ or ‘‘place caps upon, or
otherwise decrease, the Federal
Government’s responsibility to provide
funding,’’ and the State, local, or Tribal
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governments ‘‘lack authority’’ to adjust
accordingly. At the time of enactment,
these entitlement programs were:
Medicaid; Aid to Families with
Dependent Children work programs;
Child Nutrition; Food Stamps; Social
Services Block Grants; Vocational
Rehabilitation State Grants; Foster Care,
Adoption Assistance, and Independent
Living; Family Support Welfare
Services; and Child Support
Enforcement. ‘‘Federal private sector
mandate’’ includes a regulation that
‘‘would impose an enforceable duty
upon the private sector, except (i) a
condition of Federal assistance or (ii) a
duty arising from participation in a
voluntary Federal program.’’
The designation of critical habitat
does not impose a legally binding duty
on non-Federal Government entities or
private parties. Under section 7 of the
Act, the only regulatory effect is that
Federal agencies must ensure that their
actions do not result in the destruction
or adverse modification of critical
habitat. Non-Federal entities that
receive Federal funding, assistance, or
permits, or that otherwise require
approval or authorization from a Federal
agency for an action, may be indirectly
impacted by the designation of critical
habitat. However, the legally binding
duty to avoid destruction or adverse
modification of critical habitat rests
squarely on the Federal agency.
Furthermore, to the extent that nonFederal entities are indirectly impacted
because they receive Federal assistance
or participate in a voluntary Federal aid
program, the Unfunded Mandates
Reform Act would not apply, nor would
critical habitat shift the costs of the large
entitlement programs listed above onto
State governments.
(b) We do not believe that this rule
will significantly or uniquely affect
small governments because it will not
produce a Federal mandate of $100
million or greater in any year, that is, it
is not a ‘‘significant regulatory action’’
under the Unfunded Mandates Reform
Act. The designation of critical habitat
imposes no obligations on State or local
governments. By definition, Federal
agencies are not considered small
entities, although the activities they
fund or permit may be proposed or
carried out by small entities. As such, a
Small Government Agency Plan is not
required.
Executive Order 12630—Takings
In accordance with E.O. 12630
(‘‘Government Actions and Interference
with Constitutionally Protected Private
Property Rights’’), we have analyzed the
potential takings implications of
designating critical habitat for the Sierra
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Nevada bighorn sheep in a takings
implications assessment. Critical habitat
designation does not affect landowner
actions that do not require Federal
funding or permits, nor does it preclude
development of habitat conservation
programs or issuance of incidental take
permits to permit actions that do require
Federal funding or permits to go
forward. The takings implications
assessment concludes that this
designation of critical habitat for the
Sierra Nevada bighorn sheep does not
pose significant takings implications.
Federalism
In accordance with E.O. 13132
(Federalism), this rule does not have
significant Federalism effects. A
Federalism assessment is not required.
In keeping with Department of the
Interior and Department of Commerce
policy, we requested information from,
and coordinated development of, this
designated critical habitat designation
with appropriate State resource agencies
in California. The designation of critical
habitat in areas currently occupied by
the Sierra Nevada bighorn sheep
imposes no additional restrictions to
those currently in place and, therefore,
has little incremental impact on State
and local governments and their
activities. The designation may have
some benefit to these governments in
that the areas that contain the physical
and biological features essential to the
conservation of the subspecies are more
clearly defined, and the PCEs of the
habitat necessary to the conservation of
the subspecies are specifically
identified. This information does not
alter where and what federally
sponsored activities may occur.
However, it may assist local
governments in long-range planning
(rather than having them wait for caseby-case section 7 consultations to
occur).
approval by OMB under the Paperwork
Reduction Act of 1995 (44 U.S.C. 3501
et seq.). This rule will not impose
recordkeeping or reporting requirements
on State or local governments,
individuals, businesses, or
organizations. An agency may not
conduct or sponsor, and a person is not
required to respond to, a collection of
information unless it displays a
currently valid OMB control number.
National Environmental Policy Act
(NEPA)
It is our position that, outside the
Jurisdiction of the U.S. Court of Appeals
for the Tenth Circuit, we do not need to
prepare environmental analyses as
defined by the NEPA (42 U.S.C. 4321 et
seq.) in connection with designating
critical habitat under the Act. We
published a notice outlining our reasons
for this determination in the Federal
Register on October 25, 1983 (48 FR
49244). This position was upheld by the
U.S. Court of Appeals for the Ninth
Circuit (Douglas County v. Babbitt, 48
F.3d 1495 (9th Cir. 1995), cert. denied
516 U.S. 1042 (1996)).
Civil Justice Reform
In accordance with E.O. 12988 (Civil
Justice Reform), the regulation meets the
applicable standards set forth in
sections 3(a) and 3(b)(2) of the Order.
We are designating critical habitat in
accordance with the provisions of the
Act. This final rule uses standard
property descriptions and identifies the
physical and biological features
essential to the conservation of the
subspecies within the designated areas
to assist the public in understanding the
habitat needs of the Sierra Nevada
bighorn sheep.
Government-to-Government
Relationship With Tribes
In accordance with the President’s
memorandum of April 29, 1994,
‘‘Government-to-Government Relations
with Native American Tribal
Governments’’ (59 FR 22951), E.O.
13175, and the Department of the
Interior’s manual at 512 DM 2, we
readily acknowledge our responsibility
to communicate meaningfully with
recognized Federal Tribes on a
government-to-government basis. In
accordance with Secretarial Order 3206
of June 5, 1997, ‘‘American Indian
Tribal Rights, Federal—Tribal Trust
Responsibilities, and the Endangered
Species Act,’’ we readily acknowledge
our responsibilities to work directly
with Tribes in developing programs for
healthy ecosystems, to acknowledge that
Tribal lands are not subject to the same
controls as Federal public lands, to
remain sensitive to Indian culture, and
to make information available to tribes.
We have determined that there are no
Tribal lands occupied at the time of
listing that contain the features essential
for the conservation, and no unoccupied
Tribal lands that are essential for the
conservation of the Sierra Nevada
bighorn sheep. Therefore, critical
habitat for the Sierra Nevada bighorn
sheep has not been designated on Tribal
lands.
Paperwork Reduction Act of 1995
This rule does not contain any new
collections of information that require
References Cited
A complete list of all references cited
in this rulemaking is available on the
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Authority: 16 U.S.C. 1361–1407; 16 U.S.C.
1531–1544; 16 U.S.C. 4201–4245; Pub. L. 99–
625, 100 Stat. 3500; unless otherwise noted.
Internet at https://www.regulations.gov
and https://www.fws.gov/nevada/.
recordkeeping requirements,
Transportation.
Author(s)
Regulation Promulgation
The primary authors of this
rulemaking are staff members of the
Nevada Fish and Wildlife Office, Reno,
Nevada, and the Ventura Fish and
Wildlife Office, Ventura, California.
I
List of Subjects in 50 CFR Part 17
PART 17—[AMENDED]
§ 17.11 Endangered and threatened
wildlife.
Endangered and threatened species,
Exports, Imports, Reporting and
I
1. The authority citation for part 17
continues to read as follows:
*
Species
Vertebrate
population where
endangered
or threatened
Historic range
Common name
2. In § 17.11(h), revise the entry for
‘‘Sheep, Sierra Nevada bighorn’’ under
‘‘MAMMALS’’ in the List of Endangered
and Threatened Wildlife to read as
follows:
I
Accordingly, we amend part 17,
subchapter B of chapter I, title 50 of the
Code of Federal Regulations, as set forth
below:
Scientific name
*
*
(h) * * *
*
*
When listed
Critical
habitat
*
660E, 675
Status
Special
rules
17.95(a) ...
MAMMALS
*
Sheep, Sierra Nevada
bighorn.
*
Ovis canadensis
sierrae.
*
*
U.S.A. (CA)—Sierra
Nevada.
*
*
3. In § 17.95(a), add an entry for
‘‘Sierra Nevada bighorn sheep (Ovis
canadensis sierrae)’’ in the same
alphabetical order in which the
subspecies appears in the table in
§ 17.11(h) to read as follows:
I
§ 17.95
Critical habitat—fish and wildlife.
(a) Mammals.
*
*
*
*
*
Sierra Nevada Bighorn Sheep (Ovis
canadensis sierrae)
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(1) Critical habitat units are depicted
for Mono, Fresno, Inyo, Tulare, and
Tuolumne Counties, California, on the
maps below.
(2) The primary constituent elements
of critical habitat for the Sierra Nevada
bighorn sheep are the habitat
components that provide:
(i) Non-forested habitats or forest
openings within the Sierra Nevada from
4,000 ft (1,219 m) to 14,500 ft (4,420 m)
in elevation with steep (greater than or
VerDate Aug<31>2005
13:36 Aug 04, 2008
Jkt 214001
*
*
U.S.A. (CA)—Sierra
Nevada.
*
*
equal to 60 percent slope), rocky slopes
that provide for foraging, mating,
lambing, predator avoidance, and
bedding and that allow for seasonal
elevational movements between these
areas.
(ii) Presence of a variety of forage
plants as indicated by the presence of
grasses (e.g., Achnanthera spp.; Elymus
spp.) and browse (e.g., Ribes spp.;
Artemisia spp., Purshia spp.) in winter,
and grasses, browse, sedges (e.g., Carex
spp.) and forbs (e.g., Eriogonum spp.) in
summer.
(iii) Presence of granite outcroppings
containing minerals such as sodium,
calcium, iron, and phosphorus that
could be used as mineral licks in order
to meet nutritional needs.
(3) Critical habitat does not include
manmade structures, such as buildings,
aqueducts, airports, roads, and other
paved areas, and the land on which they
are located, existing on the effective
date of this rule and not containing one
PO 00000
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E
Sfmt 4700
*
*
NA
*
or more of the primary constituent
elements.
(4) Critical Habitat Map Units—
Boundaries of designated critical habitat
were derived from Sierra Nevada
Bighorn Sheep Herd Units developed by
the California Department of Fish and
Game for the final Sierra Nevada
Bighorn Sheep recovery plan. The
designated critical habitat unit
boundaries differ from Sierra Nevada
bighorn sheep Herd Unit polygons by
the removal of developed areas and
private parcels that are unlikely to
contain the primary constituent
elements. The data were projected to
Universal Transverse Mercator (UTM),
zone 11, on the North American Datum
of 1983.
(5) Note: Index map of Sierra Nevada
bighorn sheep critical habitat follows:
BILLING CODE 5310–55–P
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dwashington3 on PRODPC61 with RULES2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
(6) Unit 1 (Mount Warren); Mono and
Tuolumne Counties, California.
(i) From USGS 1:24,000 scale
quadrangles Dunderberg Peak, Lundy,
Tioga Pass, and Mount Dana. Land
bounded by the following UTM zone 11
NAD83 coordinates (E, N): 300786,
4215918; 301348, 4215650; 301467,
4215784; 302384, 4216077; 303459,
4215689; 303626, 4215452; 303452,
4215254; 303072, 4215278; 302764,
4215064; 302495, 4214977; 302218,
4214677; 302052, 4214558; 301783,
4214281; 300486, 4214005; 300351,
4213839; 299853, 4213704; 299442,
4213475; 299007, 4213079; 298991,
4212842; 299252, 4212723; 299640,
4212755; 300185, 4212913; 300359,
4213103; 300525, 4213166; 300565,
4213498; 300952, 4213562; 301111,
4213158; 301435, 4212858; 301593,
4213150; 301807, 4213253; 302566,
4213245; 303396, 4213317; 303902,
4213419; 304227, 4214044; 304567,
4214092; 304891, 4213752; 305310,
4213467; 305864, 4213158; 306239,
4212945; 306714, 4212984; 307362,
4212747; 307474, 4212940; 307514,
4213252; 307539, 4213822; 307697,
4214242; 307964, 4214386; 308395,
4214515; 308841, 4214450; 308846,
4214218; 308653, 4213802; 308499,
4213297; 308529, 4212618; 308692,
4211980; 308673, 4211876; 308514,
4211856; 308366, 4211891; 307853,
4211988; 307236, 4212146; 306682,
4212162; 306073, 4212186; 305788,
4211948; 305694, 4211640; 305788,
4211165; 305970, 4210944; 306192,
4210991; 306643, 4210857; 306801,
4210588; 306785, 4209932; 306813,
4209244; 306995, 4208658; 307596,
4208532; 307920, 4208532; 308173,
4208674; 308252, 4209244; 308315,
4209418; 308647, 4209275; 308774,
4208951; 308861, 4208635; 309082,
4208500; 309320, 4208184; 309415,
4207425; 309810, 4206847; 309023,
4206191; 308628, 4206151; 308177,
4206547; 308177, 4206927; 307679,
4207037; 307275, 4206863; 306856,
4206444; 306761, 4206033; 306991,
4205724; 307220, 4205701; 307560,
4205495; 307623, 4205179; 307797,
4204973; 307916, 4204649; 308074,
4204325; 308398, 4204182; 309134,
4204348; 309846, 4203850; 309960,
4203534; 310316, 4202846; 310490,
4202284; 310569, 4201841; 310585,
4201240; 310640, 4201098; 310799,
4200900; 310759, 4200655; 310672,
4200584; 310261, 4200536; 309984,
4200513; 309513, 4200252; 309102,
4200370; 308865, 4200418; 308651,
4200592; 308525, 4201043; 308303,
4201343; 308058, 4201644; 307837,
4202047; 307362, 4202403; 307180,
4202458; 307062, 4202268; 307165,
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
4202015; 306919, 4202023; 306477,
4202150; 306081, 4202300; 305599,
4202632; 305231, 4202751; 304456,
4203210; 304369, 4203344; 303989,
4203637; 303720, 4203913; 303420,
4204119; 303183, 4204870; 303325,
4205329; 303396, 4205661; 303345,
4206057; 303202, 4206278; 303052,
4206294; 302688, 4205582; 302894,
4205092; 302720, 4204799; 302736,
4204467; 303036, 4204198; 303036,
4203637; 303195, 4203399; 303487,
4203178; 303622, 4203036; 304120,
4202806; 304353, 4202577; 304529,
4202575; 304667, 4202584; 304837,
4202460; 304869, 4202391; 304869,
4202134; 304626, 4201784; 304263,
4201582; 304024, 4201380; 303875,
4201200; 303803, 4201210; 303746,
4201218; 303578, 4201335; 303363,
4201575; 303353, 4201611; 303344,
4201642; 303314, 4201600; 303309,
4201636; 303304, 4201627; 303289,
4201621; 303104, 4201636; 302748,
4201612; 302416, 4201770; 301988,
4202118; 301648, 4202442; 301387,
4202695; 301150, 4203099; 300897,
4203431; 300826, 4203787; 301024,
4204032; 301126, 4204412; 301142,
4205092; 300652, 4205970; 300253,
4206191; 299794, 4206294; 299311,
4206365; 298916, 4206349; 298584,
4205900; 298544, 4205764; 298853,
4205614; 299375, 4205622; 300142,
4204847; 300197, 4204617; 300166,
4204412; 300071, 4204174; 299565,
4204214; 298963, 4204174; 298315,
4204151; 298149, 4203953; 298188,
4203257; 298378, 4202893; 298350,
4202526; 298268, 4202121; 298476,
4201913; 298679, 4202026; 298698,
4202381; 298628, 4202634; 298691,
4202950; 299115, 4202552; 299185,
4202324; 298875, 4201482; 298647,
4201236; 298324, 4200742; 298369,
4200337; 298122, 4200388; 298116,
4200685; 298192, 4201109; 298160,
4201261; 298078, 4201337; 297970,
4201318; 297685, 4200983; 297319,
4200888; 297186, 4200793; 297091,
4200748; 296901, 4200951; 296654,
4200976; 296287, 4201008; 295857,
4200660; 295579, 4200200; 295506,
4200236; 295139, 4199793; 294924,
4199483; 294734, 4199641; 294582,
4199932; 294449, 4200109; 294095,
4200084; 293583, 4200369; 293323,
4200710; 293108, 4200609; 292950,
4200268; 292608, 4200369; 292754,
4200748; 292944, 4200964; 293228,
4201248; 293614, 4201014; 293874,
4200723; 294127, 4200571; 294563,
4200635; 295196, 4200805; 295310,
4200957; 295247, 4201122; 295367,
4201406; 295702, 4201318; 296031,
4201375; 296265, 4201622; 296474,
4201982; 296803, 4202349; 296942,
4202539; 296936, 4202849; 296635,
PO 00000
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45575
4202969; 296426, 4202994; 296078,
4202703; 295990, 4202507; 295541,
4202406; 294756, 4202697; 294674,
4202800; 294642, 4203007; 294813,
4203134; 295560, 4203178; 295661,
4203184; 295882, 4203418; 295927,
4203703; 295383, 4203855; 295326,
4203943; 295927, 4204057; 296135,
4204241; 296015, 4204405; 295522,
4204405; 295427, 4204608; 295569,
4205032; 295746, 4205354; 295980,
4205677; 296252, 4206012; 296347,
4206265; 296322, 4206778; 296328,
4207126; 296566, 4207328; 296800,
4207721; 296850, 4207948; 296743,
4208214; 295971, 4208777; 295813,
4208891; 295674, 4209163; 295212,
4209492; 294408, 4209555; 294161,
4209378; 293801, 4209239; 293776,
4209473; 294070, 4209967; 294620,
4210454; 295057, 4210327; 295215,
4210315; 295272, 4210625; 295234,
4210776; 295316, 4211010; 295689,
4211156; 295816, 4211023; 295879,
4210776; 295765, 4210618; 295898,
4210485; 296215, 4210416; 296297,
4210232; 296335, 4209954; 296436,
4209682; 296866, 4209384; 296923,
4209043; 297113, 4208904; 297160,
4209239; 296945, 4210163; 296926,
4210220; 296964, 4210511; 296838,
4210852; 296699, 4211542; 296578,
4211789; 296411, 4212206; 296316,
4212814; 296202, 4213219; 296316,
4213693; 296664, 4213959; 297094,
4213826; 297372, 4213535; 297676,
4213402; 297942, 4213301; 298157,
4213320; 298429, 4213434; 298625,
4213769; 298517, 4214085; 298464,
4214465; 298666, 4214705; 298919,
4214819; 299122, 4214832; 299267,
4214857; 299368, 4215136; 299027,
4215585; 299033, 4215781; 299210,
4215926; 299533, 4215711; 299988,
4215528; 300071, 4215756; 300090,
4215983; 299697, 4216559; 299546,
4216654; 299410, 4216907; 299359,
4217034; 299416, 4217413; 299454,
4217729; 299391, 4218002; 299410,
4218318; 299479, 4218577; 299529,
4218766; 299885, 4218821; 300296,
4218734; 300755, 4218505; 300865,
4218101; 300858, 4217690; 300731,
4217445; 300525, 4217247; 300446,
4216796; 300470, 4216409; returning to
300786, 4215918; excluding land
bounded by 304870, 4211718; 304755,
4211663; 304590, 4211666; 304426,
4211699; 304273, 4211615; 304237,
4211614; 304100, 4211575; 304119,
4211576; 304068, 4211562; 304036,
4211567; 303925, 4211593; 303824,
4211552; 303714, 4211495; 303668,
4211501; 303558, 4211486; 303473,
4211423; 303421, 4211366; 303381,
4211308; 303223, 4211322; 303176,
4211295; 303181, 4211202; 303103,
4211161; 303208, 4210962; 303418,
E:\FR\FM\05AUR2.SGM
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Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
4211073; 303481, 4211022; 303500,
4211020; 303617, 4211098; 303675,
4211109; 303894, 4211096; 303983,
4211127; 304053, 4211125; 304053,
4211124; 304106, 4211121; 304460,
4211207; 304518, 4211250; 304590,
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
4211261; 304644, 4211303; 304747,
4211336; 304863, 4211395; 304882,
4211457; 305018, 4211524; 305128,
4211543; 305289, 4211677; 305397,
4211739; 305477, 4211807; 305515,
4211863; 305405, 4211903; 305374,
PO 00000
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4211907; 305176, 4211813; 305029,
4211770; returning to 304870, 4211718.
(ii) Note: Map of Unit 1 Mount
Warren for Sierra Nevada bighorn sheep
follows:
BILLING CODE 5310–55–P
E:\FR\FM\05AUR2.SGM
05AUR2
45577
BILLING CODE 5310–55–C
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
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05AUR2
ER05AU08.001
dwashington3 on PRODPC61 with RULES2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
45578
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
(7) Unit 2 (Mount Gibbs); Mono and
Tuolumne Counties, California.
(i) From USGS 1:24,000 scale
quadrangles Mount Dana, Vogelsang
Peak, Kiop Peak, and June Lake. Land
bounded by the following UTM zone 11
NAD83 coordinates (E, N): 305185,
4201586; 305855, 4201263; 306124,
4201406; 306203, 4201516; 306615,
4201390; 307214, 4201220; 307539,
4200758; 307946, 4200481; 308191,
4199870; 308255, 4199529; 308437,
4199297; 308728, 4198949; 308679,
4198612; 308778, 4198157; 309188,
4197993; 309259, 4197840; 308990,
4197698; 308498, 4197676; 308268,
4197570; 308079, 4197576; 307891,
4197582; 307737, 4197512; 307657,
4197364; 307500, 4197181; 307271,
4197113; 307075, 4196893; 307221,
4196737; 307673, 4196685; 308081,
4196446; 308575, 4196543; 308912,
4196457; 309062, 4196415; 309890,
4196313; 309934, 4195897; 309443,
4195913; 309141, 4195923; 308877,
4195931; 308572, 4195866; 308570,
4195790; 308525, 4195566; 308481,
4195379; 308053, 4194978; 307970,
4194755; 308120, 4194712; 308418,
4194590; 308675, 4194356; 308668,
4194130; 308697, 4193865; 308613,
4193604; 308382, 4193461; 308112,
4193281; 307734, 4193293; 307728,
4193105; 307761, 4192953; 308063,
4192944; 308472, 4192742; 308775,
4192770; 308930, 4192878; 309271,
4192905; 309416, 4192712; 309403,
4192298; 309382, 4191659; 309372,
4191358; 309323, 4190983; 309238,
4190684; 309151, 4190348; 308920,
4190204; 308879, 4190093; 309026,
4189975; 309327, 4189928; 309478,
4189923; 309626, 4189843; 309582,
4189656; 309389, 4189511; 309271,
4189365; 309114, 4189181; 308699,
4189195; 308470, 4189127; 308167,
4189099; 308163, 4188986; 308347,
4188829; 308683, 4188705; 308907,
4188623; 309244, 4188537; 309241,
4188424; 309232, 4188161; 309187,
4187936; 309219, 4187747; 309325,
4187517; 309475, 4187475; 309740,
4187504; 309966, 4187459; 310116,
4187454; 310418, 4187445; 310796,
4187433; 310981, 4187314; 311089,
4187160; 311233, 4186929; 311450,
4186621; 311820, 4186383; 312166,
4186560; 312582, 4186585; 312850,
4186689; 313267, 4186713; 313537,
4186893; 313956, 4186993; 314142,
4186911; 314210, 4186683; 313896,
4186317; 313515, 4186216; 313165,
4185888; 312814, 4185560; 312729,
4185262; 312376, 4184859; 312069,
4184718; 312061, 4184454; 312163,
4184112; 312082, 4183926; 312340,
4183730; 312407, 4183464; 312433,
4183087; 312500, 4182821; 312680,
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
4182551; 312860, 4182282; 312892,
4182093; 312627, 4182063; 312476,
4182068; 312249, 4182075; 312208,
4182071; 311998, 4182077; 311586,
4182088; 311587, 4181967; 311448,
4181837; 311217, 4181694; 310862,
4181818; 310494, 4182132; 310199,
4182367; 310100, 4182822; 309769,
4183096; 309149, 4183794; 308929,
4183989; 308630, 4184112; 308254,
4184162; 307917, 4184248; 307768,
4184328; 307399, 4184603; 307064,
4184765; 306876, 4184771; 306831,
4184546; 306859, 4184244; 307079,
4184049; 307309, 4184154; 307832,
4183949; 307980, 4183869; 308206,
4183824; 308386, 4183555; 308415,
4183290; 308521, 4183061; 308890,
4182785; 309001, 4182707; 309101,
4182289; 309206, 4182022; 309387,
4181790; 309493, 4181561; 309480,
4181147; 309469, 4180808; 309422,
4180509; 309346, 4180511; 308934,
4180599; 308710, 4180682; 308336,
4180807; 307916, 4180670; 307577,
4180718; 307056, 4180961; 307062,
4181149; 307103, 4181261; 307594,
4181245; 307821, 4181238; 307972,
4181233; 308421, 4181105; 308651,
4181211; 308583, 4181439; 308513,
4181630; 308597, 4181891; 308640,
4182040; 308456, 4182197; 308228,
4182166; 308186, 4182017; 308104,
4181831; 307987, 4181722; 307724,
4181768; 307615, 4181885; 307621,
4182073; 307627, 4182261; 307712,
4182559; 307685, 4182899; 307543,
4183205; 307282, 4183289; 307129,
4183256; 307044, 4182957; 306921,
4182660; 306760, 4182326; 306600,
4182068; 306519, 4181882; 306400,
4181697; 306253, 4181853; 306186,
4182118; 306269, 4182342; 306507,
4182711; 306589, 4182897; 306638,
4183234; 306530, 4183426; 306339,
4183357; 306140, 4183024; 306019,
4182802; 305780, 4182395; 305402,
4182407; 304992, 4182571; 304691,
4182618; 304390, 4182666; 304162,
4182635; 303858, 4182570; 303478,
4182506; 303058, 4182369; 302790,
4182265; 302558, 4182084; 302321,
4181752; 302167, 4181682; 302174,
4181908; 302245, 4182357; 302609,
4183099; 303409, 4183300; 303569,
4183558; 303767, 4183853; 303915,
4183773; 304140, 4183691; 304291,
4183686; 304371, 4183834; 304419,
4184171; 304505, 4184470; 304744,
4184876; 305210, 4185276; 305624,
4185225; 305819, 4185407; 305910,
4185894; 305808, 4186236; 305819,
4186575; 305677, 4186881; 305456,
4187038; 305266, 4187007; 305033,
4186826; 304725, 4186647; 304426,
4186732; 304291, 4186912; 304361,
4187073; 304630, 4187215; 304639,
4187479; 304380, 4187675; 303774,
PO 00000
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Sfmt 4700
4187619; 303538, 4187326; 303336,
4186918; 302983, 4186515; 302551,
4186001; 302008, 4185567; 301544,
4185242; 301242, 4185252; 301103,
4185633; 301045, 4186162; 301023,
4186653; 300708, 4187454; 300429,
4188178; 300069, 4188717; 299821,
4189253; 299469, 4190055; 299301,
4190701; 299206, 4191269; 298879,
4191693; 298557, 4192269; 298227,
4192581; 297610, 4193354; 297507,
4193696; 297853, 4193873; 298117,
4193865; 298670, 4193433; 299225,
4193038; 299810, 4192455; 300248,
4191951; 300500, 4191566; 300693,
4191711; 300702, 4191974; 300710,
4192237; 300763, 4192688; 301153,
4193090; 301573, 4193227; 301797,
4193144; 301901, 4192840; 301743,
4192619; 301656, 4192283; 301725,
4192054; 301910, 4191935; 301638,
4191718; 301556, 4191495; 301664,
4191341; 301928, 4191332; 301999,
4191179; 301875, 4190844; 301831,
4190657; 301974, 4190389; 302007,
4190237; 302072, 4189934; 302332,
4189775; 302708, 4189725; 302857,
4189645; 302775, 4189459; 302842,
4189194; 303031, 4189188; 303109,
4189260; 303151, 4189410; 303419,
4189514; 303412, 4189288; 303441,
4189024; 303428, 4188610; 303908,
4188255; 304058, 4188213; 304396,
4188165; 304735, 4188116; 304855,
4188338; 304939, 4188599; 304950,
4188938; 304957, 4189164; 305187,
4189269; 305269, 4189455; 305127,
4189761; 305504, 4189711; 305763,
4189552; 305714, 4189215; 305825,
4189136; 305907, 4189322; 306137,
4189427; 306323, 4189346; 306553,
4189452; 306809, 4189180; 306998,
4189174; 307228, 4189279; 307030,
4189587; 307033, 4189700; 307043,
4190001; 306899, 4190231; 306523,
4190281; 306299, 4190364; 306043,
4190635; 305976, 4190901; 306020,
4191088; 306175, 4191196; 306371,
4191416; 306346, 4191831; 306166,
4192101; 306021, 4192293; 305873,
4192411; 305718, 4192266; 305637,
4192117; 305145, 4192096; 304781,
4192521; 304448, 4192720; 304155,
4193031; 303859, 4193229; 303716,
4193460; 303612, 4193764; 303468,
4193995; 303328, 4194338; 303076,
4194723; 302596, 4195078; 302527,
4195268; 302718, 4195337; 303205,
4195209; 303469, 4195200; 303808,
4195152; 304074, 4195219; 304642,
4195238; 304872, 4195344; 304913,
4195455; 304954, 4195567; 304921,
4195719; 304545, 4195768; 304283,
4195852; 304096, 4195896; 303835,
4196017; 303572, 4196063; 302817,
4196087; 302749, 4196316; 302916,
4196800; 303270, 4197241; 303129,
4197546; 302755, 4197671; 302575,
E:\FR\FM\05AUR2.SGM
05AUR2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
4197941; 302696, 4198201; 302856,
4198459; 302985, 4198945; 303114,
4199430; 303351, 4199762; 303767,
4199786; 304175, 4199547; 304351,
4199127; 304677, 4198702; 305313,
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
4198494; 305467, 4198602; 305372,
4199170; 305153, 4199403; 304741,
4199529; 304600, 4199835; 304504,
4200365; 304630, 4200775; 304836,
4201296; returning to 305185, 4201586.
PO 00000
Frm 00047
Fmt 4701
Sfmt 4700
45579
(ii) Note: Map of Unit 2 (Mount Gibbs)
for Sierra Nevada bighorn sheep
follows:
BILLING CODE 5310–55–P
E:\FR\FM\05AUR2.SGM
05AUR2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
BILLING CODE 5310–55–C
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
PO 00000
Frm 00048
Fmt 4701
Sfmt 4700
E:\FR\FM\05AUR2.SGM
05AUR2
ER05AU08.002
dwashington3 on PRODPC61 with RULES2
45580
dwashington3 on PRODPC61 with RULES2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
(8) Unit 3 (Convict Creek); Fresno and
Mono Counties, California.
(i) From USGS 1:24,000 scale
quadrangles Crystal Crag, Bloody
Mountain, Convict Lake, Graveyard
Peak, and Mount Abbot. Land bounded
by the following UTM zone 11 NAD83
coordinates (E, N): 327481, 4161516;
327397, 4161255; 327279, 4161108;
327082, 4160851; 327076, 4160663;
327184, 4160508; 327409, 4160464;
327720, 4160717; 327917, 4160975;
328080, 4161346; 328312, 4161527;
328424, 4161486; 328373, 4161073;
328322, 4160660; 328009, 4160294;
327814, 4160112; 327619, 4159930;
327573, 4159668; 327755, 4159436;
327980, 4159391; 328058, 4159464;
328100, 4159613; 328112, 4159989;
328455, 4160091; 328333, 4159794;
328366, 4159642; 328515, 4159600;
329004, 4159509; 329304, 4159462;
329223, 4159276; 329061, 4158942;
329089, 4158640; 329077, 4158264;
329260, 4158070; 329631, 4157870;
329891, 4157711; 330272, 4157812;
330655, 4157988; 330812, 4158171;
330677, 4158665; 330869, 4158772;
330951, 4158957; 330667, 4159531;
330492, 4159989; 330469, 4160441;
330231, 4160072; 329887, 4159970;
329706, 4160202; 329604, 4160582;
329624, 4161184; 329708, 4161445;
329829, 4161705; 329701, 4162424;
329860, 4162683; 330161, 4162636;
330229, 4162605; 330305, 4162536;
330367, 4162498; 330436, 4162454;
330524, 4162442; 330650, 4162448;
330788, 4162473; 330908, 4162473;
331083, 4162492; 331140, 4162504;
331203, 4162517; 331272, 4162523;
331366, 4162555; 331511, 4162561;
331699, 4162599; 331781, 4162643;
331938, 4162661; 332095, 4162680;
332208, 4162712; 332277, 4162768;
332465, 4162862; 332534, 4162913;
332635, 4162969; 332817, 4163076;
333112, 4163170; 333338, 4163252;
333477, 4163271; 333769, 4163236;
333886, 4163345; 333999, 4163342;
334489, 4163289; 334674, 4163170;
334896, 4163012; 335120, 4162930;
335271, 4162925; 335385, 4162959;
335499, 4162993; 335873, 4162868;
335986, 4162864; 336135, 4162784;
336130, 4162634; 336050, 4162486;
335971, 4162375; 335815, 4162230;
335736, 4162119; 335467, 4161977;
335312, 4161869; 335113, 4161536;
335031, 4161351; 334948, 4161090;
334944, 4160977; 334971, 4160637;
335037, 4160334; 335176, 4159953;
335396, 4159757; 335442, 4160020;
335634, 4160089; 335816, 4159895;
336039, 4159775; 336234, 4159957;
336206, 4160259; 336107, 4160714;
336230, 4161011; 336572, 4161076;
336860, 4160652; 337102, 4159929;
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
337085, 4159402; 336881, 4158919;
336718, 4158548; 336744, 4158170;
336769, 4157793; 336716, 4157305;
336743, 4156965; 336896, 4157036;
337058, 4157370; 337147, 4157781;
337196, 4158156; 337552, 4158634;
337948, 4159224; 338069, 4159446;
338416, 4159661; 338643, 4159692;
339127, 4159450; 339575, 4159285;
339958, 4159462; 340015, 4160062;
339770, 4160673; 339893, 4160970;
340382, 4160917; 340644, 4160833;
340942, 4160711; 341461, 4160393;
341779, 4159705; 341840, 4159251;
341780, 4158537; 341470, 4158284;
340960, 4157697; 340383, 4157377;
339777, 4157321; 339130, 4157191;
338931, 4156858; 339034, 4156553;
339306, 4156771; 339537, 4156914;
340337, 4157115; 340640, 4157143;
341134, 4157240; 341505, 4157040;
341686, 4156770; 341995, 4156987;
342165, 4157584; 342517, 4157949;
342774, 4157715; 342913, 4157334;
343193, 4156647; 343330, 4156191;
343594, 4155015; 343725, 4154371;
343966, 4153647; 343986, 4153082;
344111, 4152249; 343944, 4151765;
343522, 4151553; 343113, 4151754;
342857, 4152026; 342402, 4151965;
342317, 4151666; 342226, 4151180;
342065, 4150883; 341869, 4150664;
341671, 4150369; 341818, 4150251;
341851, 4150099; 341956, 4149833;
342177, 4149637; 342286, 4149521;
342403, 4149630; 342560, 4149813;
342900, 4149803; 343043, 4149572;
342844, 4149239; 342499, 4149100;
342680, 4148830; 342942, 4148747;
343179, 4149078; 343456, 4149484;
343790, 4149285; 343627, 4148913;
343392, 4148657; 343149, 4148138;
343258, 4148021; 343285, 4147681;
343274, 4147305; 343051, 4147425;
342828, 4147545; 342597, 4147402;
342331, 4147373; 342146, 4147492;
341968, 4147836; 341938, 4148063;
342128, 4148095; 342311, 4147938;
342503, 4148008; 342621, 4148154;
342698, 4148227; 342665, 4148379;
342076, 4148850; 341633, 4149165;
341530, 4149507; 341467, 4149886;
340838, 4150320; 340536, 4150330;
340193, 4150228; 339889, 4150162;
339587, 4150171; 339398, 4150177;
339018, 4150114; 338825, 4149970;
338896, 4149817; 339009, 4149813;
339161, 4149846; 339187, 4149469;
339290, 4149164; 339520, 4149270;
339943, 4149482; 339780, 4149111;
339617, 4148739; 339785, 4148094;
339553, 4147913; 339226, 4148338;
339052, 4148795; 338679, 4148958;
338273, 4149234; 338126, 4149389;
337938, 4149395; 337855, 4149172;
337743, 4149213; 337593, 4149256;
337372, 4149413; 337145, 4149421;
336956, 4149427; 336767, 4149395;
PO 00000
Frm 00049
Fmt 4701
Sfmt 4700
45581
336649, 4149248; 336606, 4149099;
336751, 4148906; 336861, 4148789;
337006, 4148597; 336889, 4148487;
336627, 4148571; 336405, 4148729;
336376, 4148993; 336231, 4149186;
335967, 4149194; 335890, 4149159;
335775, 4149088; 335555, 4149321;
335298, 4149555; 335219, 4149444;
335214, 4149294; 335317, 4148952;
335422, 4148685; 335343, 4148574;
335155, 4148618; 334974, 4148849;
334791, 4149044; 334636, 4148935;
334377, 4149094; 334726, 4149385;
334810, 4149646; 335042, 4149826;
335274, 4149970; 335582, 4150148;
335517, 4150489; 335252, 4150460;
334801, 4150550; 334430, 4150750;
334326, 4151054; 334556, 4151160;
334815, 4151001; 335077, 4150917;
335122, 4151142; 335386, 4151134;
335508, 4151393; 335481, 4151733;
335604, 4152030; 335946, 4152095;
335919, 4152435; 335770, 4152515;
335428, 4152450; 335229, 4152118;
334800, 4151717; 334460, 4151690;
334193, 4151623; 333778, 4151637;
333556, 4151794; 333602, 4152057;
333834, 4152200; 334068, 4152456;
333925, 4152686; 333513, 4152813;
333101, 4152939; 332646, 4152878;
332309, 4152964; 332579, 4153144;
332958, 4153169; 332736, 4153327;
332481, 4153636; 332603, 4153896;
332905, 4153886; 333240, 4153725;
333470, 4153831; 333326, 4154061;
332997, 4154411; 332816, 4154642;
332323, 4154583; 331984, 4154631;
331786, 4154336; 331739, 4154036;
331544, 4153854; 331056, 4153945;
330870, 4154064; 330929, 4153535;
330955, 4153158; 330490, 4152796;
330298, 4152689; 329759, 4152367;
329452, 4152226; 328877, 4151981;
328610, 4151876; 328051, 4152120;
327499, 4152590; 327096, 4152979;
326655, 4153370; 326660, 4153520;
326891, 4153664; 327222, 4153389;
327255, 4153238; 327701, 4152997;
328038, 4152911; 328485, 4152709;
328936, 4152619; 329510, 4152865;
329784, 4153157; 330092, 4153336;
330406, 4153702; 330418, 4154079;
330544, 4154489; 330398, 4154644;
330064, 4154843; 329848, 4155189;
329897, 4155526; 330114, 4155218;
330372, 4155021; 330745, 4154859;
330825, 4155007; 330829, 4155120;
330800, 4155422; 330658, 4155690;
330699, 4155802; 330882, 4155608;
331136, 4155298; 331392, 4155027;
331581, 4155021; 331776, 4155203;
331783, 4155428; 331529, 4155775;
331387, 4156044; 331135, 4156428;
331029, 4156658; 330886, 4156926;
330742, 4157156; 330441, 4157204;
330252, 4157172; 329987, 4157180;
329609, 4157155; 329273, 4157278;
329088, 4157397; 328941, 4157553;
E:\FR\FM\05AUR2.SGM
05AUR2
45582
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
328787, 4157445; 328668, 4157260;
328468, 4156927; 328161, 4156787;
328003, 4156566; 327921, 4156342;
327877, 4156155; 327758, 4155971;
327559, 4155676; 327286, 4155383;
327201, 4155085; 327007, 4154940;
326815, 4154833; 326772, 4154684;
326727, 4154460; 326612, 4154388;
326271, 4154361; 326126, 4154554;
325531, 4154874; 325086, 4155114;
324787, 4155237; 324378, 4155438;
324118, 4155560; 323895, 4155680;
323635, 4155838; 323259, 4155888;
322877, 4155750; 322732, 4155943;
322737, 4156093; 322896, 4156352;
323125, 4156420; 323018, 4156611;
322684, 4156810; 322343, 4156783;
321782, 4156952; 321290, 4156930;
320875, 4156943; 320497, 4156955;
320162, 4157117; 319826, 4157240;
319673, 4157170; 319511, 4156836;
319276, 4156580; 319088, 4156586;
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
318974, 4156589; 318478, 4156417;
318176, 4156426; 317723, 4156441;
317349, 4156566; 317047, 4156575;
316698, 4156285; 316351, 4156070;
316118, 4155889; 315930, 4155895;
315745, 4156014; 315795, 4156427;
316149, 4156868; 316383, 4157086;
316545, 4157420; 317188, 4157437;
317494, 4157578; 318140, 4157670;
318786, 4157801; 319280, 4157898;
319619, 4157849; 320036, 4157911;
320491, 4157935; 321164, 4157725;
322066, 4157583; 322813, 4157296;
323329, 4156903; 323662, 4156666;
324374, 4156493; 324515, 4156187;
324658, 4155919; 325033, 4155832;
325413, 4155895; 325671, 4155698;
325961, 4155313; 326257, 4155115;
326599, 4155179; 326800, 4155549;
327035, 4155806; 327234, 4156138;
327403, 4156698; 327602, 4157030;
327877, 4157361; 328071, 4157505;
PO 00000
Frm 00050
Fmt 4701
Sfmt 4700
328272, 4157875; 328618, 4158090;
328548, 4158243; 328136, 4158369;
328410, 4158662; 328343, 4158927;
328427, 4159188; 328470, 4159375;
328242, 4159307; 328161, 4159159;
327707, 4159136; 327489, 4159407;
327232, 4159641; 327165, 4159906;
327061, 4160211; 326614, 4160414;
326550, 4160755; 326336, 4161176;
326306, 4161403; 326647, 4161429;
326949, 4161420; 326992, 4161607;
327347, 4162047; 327465, 4162194;
327587, 4162492; 327642, 4163017;
327766, 4163352; 328145, 4163378;
328207, 4162961; 328235, 4162659;
328223, 4162283; 328027, 4162063;
327795, 4161882; 327560, 4161626;
returning to 327481, 4161516.
(ii) Note: Map of Unit 3 (Convict
Creek) for Sierra Nevada bighorn sheep
follows:
BILLING CODE 5310–55–P
E:\FR\FM\05AUR2.SGM
05AUR2
45583
BILLING CODE 5310–55–C
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
PO 00000
Frm 00051
Fmt 4701
Sfmt 4700
E:\FR\FM\05AUR2.SGM
05AUR2
ER05AU08.003
dwashington3 on PRODPC61 with RULES2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
45584
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
(9) Unit 4 (Wheeler Ridge); Fresno,
Inyo and Mono Counties, California.
(i) From USGS 1:24,000 scale
quadrangles Mount Abbot, Mount
Morgan, Mount Hilgard, Mount Tom,
Tungsten Hills, Mount Henry, Mount
Darwin and Mount Thompson. Land
bounded by the following UTM zone 11
NAD83 coordinates (E, N): 351676,
4150867; 352490, 4150441; 352738,
4150510; 353065, 4150282; 353442,
4150500; 353779, 4150847; 354294,
4150817; 354552, 4150341; 354641,
4149994; 354681, 4149558; 354453,
4149439; 354245, 4149221; 354463,
4148953; 354522, 4148735; 354413,
4148398; 354532, 4148140; 354493,
4147862; 354909, 4147912; 354711,
4147119; 355098, 4146296; 355132,
4146201; 355158, 4146034; 355162,
4145681; 355123, 4145288; 355123,
4144981; 355035, 4144787; 354974,
4144489; 354895, 4144120; 354745,
4143840; 354537, 4143588; 354359,
4143519; 354349, 4143132; 354329,
4142934; 354141, 4142686; 353967,
4141942; 353729, 4141853; 353600,
4141804; 353610, 4141566; 353729,
4141328; 353610, 4141219; 353600,
4141000; 354066, 4140584; 354463,
4140584; 354780, 4140286; 355068,
4140019; 355256, 4139642; 355425,
4139136; 355395, 4138799; 355489,
4138412; 355499, 4138254; 355618,
4138144; 355737, 4137748; 356035,
4137639; 356560, 4137272; 356818,
4136984; 356828, 4136617; 356996,
4136211; 357016, 4135715; 356649,
4135477; 356243, 4135299; 356084,
4135239; 356144, 4135011; 356491,
4135090; 356848, 4134892; 357046,
4134614; 357140, 4134515; 356932,
4134019; 356714, 4133771; 356476,
4133652; 356357, 4133405; 356486,
4133216; 356535, 4132839; 356307,
4132740; 355990, 4132611; 355782,
4132542; 355583, 4132294; 355197,
4132125; 355038, 4131907; 354671,
4131709; 354265, 4131739; 353898,
4131778; 353590, 4131719; 352817,
4131709; 352688, 4131421; 352787,
4131223; 353283, 4131263; 354235,
4131382; 354473, 4131253; 354721,
4131233; 355018, 4131144; 355157,
4131025; 355068, 4130757; 354721,
4130450; 354656, 4130281; 354746,
4130241; 354835, 4130132; 355103,
4130063; 355202, 4129944; 354934,
4129488; 354755, 4129111; 354865,
4128556; 355103, 4128189; 355222,
4127842; 355202, 4127385; 354993,
4127247; 354795, 4127544; 354458,
4127822; 354240, 4128020; 354081,
4128010; 353922, 4127792; 353893,
4127584; 354369, 4127524; 354398,
4127247; 354508, 4127038; 354438,
4126612; 354508, 4126443; 354364,
4126196; 354106, 4126086; 353888,
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
4125670; 353898, 4125491; 354215,
4125402; 354334, 4125204; 354721,
4124956; 355960, 4125313; 355940,
4125095; 355603, 4124926; 355197,
4124619; 354701, 4124411; 354126,
4123994; 353808, 4123806; 353828,
4123707; 354156, 4123508; 354661,
4123627; 354453, 4123449; 354354,
4123122; 353967, 4123042; 354512,
4122715; 355613, 4122546; 356089,
4122675; 356416, 4122497; 356501,
4122179; 356431, 4121832; 356035,
4121713; 355846, 4121644; 355638,
4121406; 355291, 4121436; 354835,
4121644; 354567, 4121674; 354160,
4121793; 353932, 4121862; 353843,
4121753; 353794, 4121406; 354527,
4120970; 355013, 4120742; 354954,
4120305; 354270, 4119691; 354022,
4119770; 353675, 4119730; 353357,
4119562; 353169, 4119413; 353159,
4119224; 352792, 4119304; 352653,
4119215; 352217, 4119224; 351553,
4119334; 351280, 4119026; 351250,
4118679; 351389, 4118570; 351617,
4118649; 351766, 4118471; 351914,
4118193; 352024, 4117945; 351984,
4117132; 351776, 4117013; 351468,
4116845; 350576, 4117102; 350080,
4117271; 349971, 4117152; 349406,
4117102; 349644, 4117549; 349911,
4117747; 350645, 4117618; 350982,
4117638; 351012, 4117945; 350725,
4118511; 350100, 4118600; 349545,
4118332; 349178, 4118342; 348712,
4117787; 348464, 4117142; 348196,
4116884; 348077, 4116914; 348057,
4117122; 347819, 4117142; 347750,
4117370; 347908, 4117737; 348156,
4117836; 348325, 4118154; 348176,
4118332; 347879, 4118352; 347175,
4118570; 346798, 4118848; 346937,
4119096; 347651, 4119294; 347482,
4119572; 346847, 4119532; 346728,
4119572; 346748, 4119750; 347165,
4120057; 347065, 4120295; 347065,
4120494; 346946, 4120583; 346788,
4120345; 346599, 4119998; 346461,
4119958; 346153, 4120256; 345801,
4120038; 345682, 4119661; 345414,
4119581; 345206, 4119373; 345018,
4119334; 344601, 4119026; 344403,
4118996; 344086, 4118610; 343848,
4118689; 343243, 4118877; 342846,
4118947; 342767, 4119096; 342836,
4119383; 343223, 4119691; 343620,
4119740; 344006, 4119899; 344343,
4120077; 344224, 4120256; 343887,
4120305; 343630, 4120414; 343798,
4120761; 343580, 4120890; 343064,
4120811; 342757, 4120910; 342678,
4120990; 342628, 4121366; 342886,
4121813; 342816, 4121912; 342549,
4121892; 342410, 4121991; 342122,
4122160; 341934, 4122209; 341825,
4121951; 342033, 4121753; 342043,
4121396; 341736, 4121198; 341755,
4120791; 341438, 4120424; 341150,
PO 00000
Frm 00052
Fmt 4701
Sfmt 4700
4120514; 341150, 4120752; 341061,
4120900; 340992, 4121366; 340541,
4121684; 340273, 4121654; 339757,
4121644; 339648, 4121505; 339351,
4121475; 339222, 4121555; 339222,
4121922; 339361, 4122298; 339787,
4122338; 340065, 4122249; 340263,
4122110; 340630, 4122070; 340987,
4121872; 341245, 4121743; 341384,
4121783; 341473, 4121942; 341324,
4122061; 341403, 4122417; 341284,
4122646; 341403, 4122854; 341691,
4122725; 341820, 4122774; 341859,
4122983; 341701, 4123241; 341542,
4123290; 341215, 4123161; 340947,
4123151; 340620, 4123211; 340313,
4123340; 340104, 4123538; 340164,
4123677; 340600, 4123657; 340937,
4123756; 341235, 4123816; 341354,
4124262; 341651, 4124192; 341790,
4123994; 341800, 4123707; 341969,
4123498; 342137, 4123389; 342355,
4123241; 342445, 4123022; 342564,
4122963; 342564, 4123290; 342425,
4123945; 342534, 4124252; 342831,
4124391; 342930, 4124500; 343208,
4124401; 342950, 4123915; 343020,
4123558; 342891, 4123022; 342901,
4122784; 343258, 4122616; 343387,
4122675; 343565, 4123191; 343555,
4123746; 343644, 4124083; 343773,
4124163; 343952, 4124034; 343962,
4123667; 344319, 4123746; 344269,
4123528; 343942, 4123300; 343922,
4122844; 343664, 4122298; 343506,
4122070; 343674, 4121832; 343922,
4121634; 344200, 4121614; 344497,
4121813; 344755, 4121882; 344775,
4122606; 344943, 4123241; 345241,
4123687; 345409, 4123161; 345350,
4122497; 345261, 4121664; 345340,
4121307; 345920, 4121237; 346416,
4121158; 346694, 4121128; 346912,
4121327; 346961, 4121604; 346832,
4121872; 346644, 4122120; 346446,
4122398; 346495, 4122546; 346743,
4122427; 347150, 4122239; 347368,
4121912; 347507, 4121991; 347665,
4122229; 347834, 4122189; 347675,
4121783; 347725, 4121585; 347388,
4121466; 347239, 4121099; 347417,
4120851; 347437, 4120623; 347576,
4120385; 347755, 4120206; 347953,
4120186; 348151, 4120305; 348102,
4120523; 348558, 4121456; 348667,
4121416; 348657, 4120434; 348697,
4120256; 348568, 4119978; 348300,
4119938; 348012, 4119938; 347923,
4119800; 348231, 4119472; 348488,
4119324; 348637, 4119145; 348786,
4119016; 349292, 4119423; 349242,
4119780; 349510, 4120038; 349530,
4120295; 349877, 4120295; 350244,
4120236; 350095, 4120028; 349827,
4119978; 349659, 4119810; 349659,
4119502; 349768, 4119234; 349817,
4118897; 350283, 4118907; 350710,
4119036; 350992, 4119552; 351141,
E:\FR\FM\05AUR2.SGM
05AUR2
dwashington3 on PRODPC61 with RULES2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
4119810; 350883, 4120434; 350814,
4120950; 350943, 4121426; 351091,
4121892; 350834, 4122328; 350596,
4122765; 350576, 4123003; 350655,
4123181; 350987, 4123112; 351592,
4123250; 351919, 4123746; 352088,
4124192; 352405, 4124678; 352286,
4125095; 351800, 4125372; 351463,
4125650; 351057, 4125888; 350700,
4126017; 350491, 4125868; 350194,
4126007; 350333, 4126255; 350660,
4126245; 350868, 4126414; 350819,
4126701; 350472, 4126850; 349986,
4126820; 349827, 4126662; 349629,
4126493; 349510, 4126652; 349371,
4127068; 349292, 4127227; 349113,
4127435; 348320, 4126840; 348161,
4126681; 347884, 4126681; 347794,
4126781; 347636, 4126751; 347536,
4126523; 347368, 4126295; 346912,
4126037; 346604, 4125769; 346545,
4125521; 346356, 4125333; 346029,
4125353; 345598, 4124986; 344963,
4124906; 344348, 4125115; 343962,
4125412; 343515, 4125809; 342891,
4125958; 342673, 4126156; 342722,
4126315; 343109, 4126562; 344110,
4126840; 344696, 4126949; 345538,
4127038; 346381, 4126999; 347046,
4127078; 347611, 4127247; 348057,
4127614; 348156, 4128090; 348275,
4128328; 348622, 4128447; 348969,
4128774; 349069, 4129200; 348945,
4129577; 348726, 4129736; 348350,
4129964; 348032, 4130003; 348350,
4130142; 348855, 4129914; 349153,
4129904; 349153, 4130261; 348984,
4130380; 348518, 4131035; 348231,
4131649; 348001, 4131812; 347610,
4131751; 346976, 4131497; 346488,
4131121; 345930, 4130538; 345600,
4130086; 344777, 4129685; 344366,
4129451; 343719, 4129106; 342627,
4129131; 341637, 4129314; 340922,
4129396; 340478, 4129563; 340320,
4129769; 340454, 4130269; 340201,
4130832; 340772, 4130769; 340978,
4130872; 341105, 4131166; 341113,
4131411; 341390, 4131760; 341494,
4132244; 341565, 4132387; 341763,
4132292; 341787, 4132165; 341985,
4132236; 342021, 4132578; 341902,
4132847; 341617, 4133117; 341371,
4133276; 340918, 4133339; 340696,
4133307; 340101, 4133347; 339586,
4133101; 339284, 4133061; 338737,
4133014; 338253, 4132800; 337650,
4132816; 337448, 4132887; 337432,
4133196; 337345, 4133442; 337392,
4133656; 337916, 4133775; 338027,
4134132; 338249, 4134339; 338360,
4134315; 338479, 4134132; 338328,
4133966; 338305, 4133736; 338400,
4133664; 338662, 4133736; 338939,
4133783; 339114, 4134005; 339106,
4134474; 339368, 4134688; 339439,
4134513; 339439, 4134243; 339606,
4134045; 340010, 4133910; 340177,
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
4133887; 340335, 4134132; 340288,
4134378; 340097, 4134719; 339883,
4134910; 339463, 4135053; 339375,
4135140; 339344, 4135529; 339399,
4135640; 339621, 4135759; 340177,
4135592; 340581, 4135061; 340883,
4134973; 340922, 4134831; 340851,
4134569; 340788, 4134442; 340859,
4134362; 341176, 4134513; 341462,
4134656; 341668, 4134664; 341775,
4135219; 341886, 4135624; 342053,
4135862; 342116, 4136068; 342410,
4136235; 343163, 4136211; 343290,
4136433; 343275, 4136576; 343052,
4136719; 342751, 4136687; 342529,
4136933; 342204, 4137234; 342283,
4137440; 342648, 4137440; 342973,
4137210; 343084, 4137298; 343060,
4137472; 342902, 4137631; 342616,
4137750; 342418, 4137948; 342398,
4138361; 342009, 4138670; 341652,
4138472; 341605, 4138242; 341375,
4138020; 341359, 4137837; 341145,
4137615; 340970, 4137298; 340891,
4137147; 340669, 4137012; 340312,
4136980; 340208, 4137052; 340034,
4137020; 339780, 4136695; 339709,
4136520; 339439, 4136385; 339320,
4136251; 339233, 4136028; 339130,
4135830; 338519, 4135830; 338419,
4135487; 338438, 4135279; 338210,
4134912; 337943, 4134872; 337397,
4134803; 337199, 4134803; 336852,
4134912; 336495, 4135408; 336247,
4135765; 336059, 4135903; 335632,
4135933; 335236, 4135775; 334898,
4135537; 334571, 4135338; 334125,
4135338; 334095, 4135884; 334482,
4136568; 334700, 4136845; 335216,
4137242; 335751, 4137718; 336019,
4137956; 336039, 4138174; 335771,
4138313; 335513, 4138571; 335513,
4138948; 335920, 4139245; 336168,
4139444; 336148, 4139672; 335930,
4139959; 335617, 4140653; 335548,
4141228; 335310, 4141357; 334953,
4141942; 334943, 4142200; 335379,
4142399; 335766, 4142389; 336113,
4142200; 336480, 4141417; 336599,
4141109; 336986, 4140752; 337105,
4140455; 337630, 4140197; 337948,
4139473; 338453, 4138601; 338543,
4138214; 338473, 4137817; 338275,
4137550; 338334, 4137391; 338632,
4137341; 338860, 4137490; 338900,
4137797; 339128, 4137847; 339266,
4137470; 339257, 4137321; 339623,
4137202; 339772, 4137510; 339723,
4138035; 340060, 4138333; 340357,
4138402; 340972, 4138690; 340947,
4139037; 340957, 4139265; 341265,
4139265; 341384, 4139106; 341731,
4139136; 341701, 4139354; 341463,
4139533; 341304, 4139701; 340917,
4139850; 340818, 4140138; 340412,
4140534; 339807, 4141040; 339252,
4141347; 338795, 4141615; 338627,
4141744; 338141, 4141734; 337943,
PO 00000
Frm 00053
Fmt 4701
Sfmt 4700
45585
4141595; 337665, 4141675; 337239,
4141942; 337040, 4142190; 336792,
4142488; 336505, 4142875; 336321,
4143360; 337382, 4143261; 337521,
4143668; 337680, 4143797; 337729,
4143559; 337710, 4143033; 337789,
4142835; 338086, 4142666; 338205,
4142765; 338265, 4142944; 338047,
4143142; 338186, 4143390; 338652,
4142894; 338622, 4142468; 339465,
4142200; 339485, 4142537; 339108,
4142706; 339009, 4142984; 339157,
4143370; 339465, 4143549; 339812,
4143767; 340109, 4143965; 340228,
4144302; 340496, 4144372; 340585,
4143777; 340109, 4142706; 340208,
4142289; 340288, 4142180; 340278,
4141714; 340456, 4141516; 340655,
4141893; 340556, 4142280; 340922,
4142736; 341041, 4143112; 341022,
4143906; 340942, 4144441; 340873,
4144937; 341190, 4145334; 341458,
4145235; 341557, 4145512; 341666,
4145532; 341924, 4145264; 341825,
4144620; 341914, 4144015; 341626,
4143479; 341825, 4143132; 341329,
4142557; 341428, 4141893; 341200,
4141675; 340962, 4141199; 340903,
4141060; 341041, 4141040; 341170,
4141060; 341141, 4140852; 341210,
4140643; 341398, 4140663; 341537,
4140514; 341696, 4140842; 341874,
4141179; 342038, 4141694; 342058,
4142349; 342127, 4143093; 342445,
4143291; 342306, 4143856; 342564,
4144511; 342752, 4144481; 343218,
4144025; 343287, 4143757; 343059,
4143499; 342772, 4142974; 342802,
4142835; 342970, 4142815; 343010,
4142448; 342980, 4142200; 342990,
4142042; 343238, 4141833; 343783,
4142101; 343922, 4142309; 344130,
4142458; 344606, 4142428; 344557,
4142151; 344408, 4141764; 344180,
4141347; 344041, 4140941; 344081,
4140554; 344497, 4140157; 344596,
4139721; 344626, 4139394; 344715,
4139245; 344973, 4139374; 344943,
4140058; 345171, 4140157; 345598,
4140386; 345727, 4140673; 345697,
4141080; 345568, 4141417; 345647,
4142002; 345717, 4142607; 345955,
4142785; 346133, 4143073; 346342,
4143698; 346550, 4144243; 346639,
4144808; 346847, 4145235; 347001,
4145631; 347298, 4145929; 347447,
4145879; 347586, 4145562; 347546,
4145135; 347556, 4144699; 347725,
4144174; 347715, 4143846; 347586,
4143539; 347527, 4143172; 347874,
4143598; 348211, 4143817; 348201,
4144084; 348449, 4144382; 348548,
4144419; 348838, 4144480; 348970,
4144480; 349110, 4144489; 349189,
4144489; 349295, 4144480; 349374,
4144498; 349461, 4144489; 349549,
4144489; 349602, 4144471; 349698,
4144436; 349795, 4144445; 349979,
E:\FR\FM\05AUR2.SGM
05AUR2
45586
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
4144471; 350190, 4144550; 350321,
4144594; 350453, 4144673; 350452,
4144878; 350432, 4145562; 350442,
4146236; 350551, 4146672; 350501,
4147158; 350670, 4147436; 350878,
4147664; 350591, 4148061; 350283,
4148229; 350353, 4148933; 350402,
4149459; 350348, 4150371; 350606,
4150788; 350992, 4151016; returning to
351676, 4150867; excluding land
bounded by 352666, 4139452; 352330,
4139197; 352261, 4139018; 352280,
4139004; 352300, 4138988; 352332,
4138964; 352634, 4139235; 352732,
4139417; 352718, 4139424; 352718,
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
4139425; 352694, 4139437; 352694,
4139437; 352690, 4139439; 352687,
4139441; 352687, 4139441; returning to
352666, 4139452; excluding land
bounded by 350254, 4136280; 350216,
4136187; 350216, 4136187; 350178,
4136094; 350363, 4136018; 350402,
4136111; 350402, 4136111; 350440,
4136204; 350478, 4136296; 350305,
4136368; 350300, 4136361; 350295,
4136351; 350293, 4136348; 350287,
4136341; 350283, 4136338; 350280,
4136335; 350276, 4136333; 350276,
4136333; returning to 350254, 4136280;
excluding land bounded by 349527,
PO 00000
Frm 00054
Fmt 4701
Sfmt 4700
4136002; 349500, 4136201; 349450,
4136194; 349408, 4136200; 349404,
4136201; 349391, 4136206; 349321,
4136238; 349317, 4136223; 349126,
4136278; 349099, 4136181; 349045,
4135990; 349139, 4135963; 349138,
4135962; 349235, 4135934; 349212,
4135851; 349308, 4135823; 349406,
4135799; 349478, 4135988; 349478,
4135995; returning to 349527, 4136002.
(ii) Note: Map of Unit 4 (Wheeler
Ridge) for Sierra Nevada bighorn sheep
follows:
BILLING CODE 5310–55–P
E:\FR\FM\05AUR2.SGM
05AUR2
45587
BILLING CODE 5310–55–C
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
PO 00000
Frm 00055
Fmt 4701
Sfmt 4700
E:\FR\FM\05AUR2.SGM
05AUR2
ER05AU08.004
dwashington3 on PRODPC61 with RULES2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
45588
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
(10) Unit 5 (Taboose Creek); Fresno
and Inyo Counties, California.
(i) From USGS 1:24,000 scale
quadrangles Coyote Flat, North Palisade,
Split Mountain, Fish Springs, Mount
Pinchot, and Aberdeen. Land bounded
by the following UTM zone 11 NAD83
coordinates (E, N): 376756, 4109414;
376837, 4109413; 376838, 4109467;
376865, 4109466; 377166, 4109426;
377588, 4109383; 377647, 4109351;
377738, 4109348; 377949, 4109341;
378189, 4109273; 378307, 4109179;
378423, 4109025; 378417, 4108844;
378288, 4108608; 378131, 4108402;
377943, 4108197; 377878, 4108048;
377872, 4107868; 377869, 4107777;
378016, 4107622; 378227, 4107615;
378408, 4107610; 378649, 4107602;
378949, 4107502; 378970, 4107230;
378903, 4107022; 378751, 4106996;
378625, 4106820; 378498, 4106643;
378218, 4106381; 378030, 4106176;
377814, 4106032; 377809, 4105881;
377958, 4105817; 378200, 4105809;
378319, 4105745; 378467, 4105650;
378524, 4105558; 378552, 4105466;
378547, 4105316; 378483, 4105198;
378299, 4105113; 378206, 4105056;
378232, 4104904; 378410, 4104808;
378404, 4104628; 378341, 4104539;
378248, 4104452; 378126, 4104426;
378006, 4104459; 377826, 4104495;
377612, 4104412; 377461, 4104416;
377400, 4104418; 377007, 4104401;
376822, 4104286; 376728, 4104169;
376786, 4104106; 377240, 4104122;
377424, 4104207; 377787, 4104225;
378148, 4104184; 378360, 4104177;
378631, 4104169; 378992, 4104097;
379233, 4104089; 379320, 4103966;
379283, 4103756; 378943, 4103526;
378788, 4103380; 378511, 4103239;
378355, 4103063; 378316, 4102793;
378220, 4102615; 378126, 4102528;
377794, 4102538; 377432, 4102550;
377312, 4102584; 377221, 4102587;
376947, 4102505; 376851, 4102327;
376876, 4102176; 376992, 4102021;
377135, 4101776; 377222, 4101653;
377248, 4101531; 377278, 4101500;
377365, 4101407; 377570, 4101190;
377685, 4101005; 377766, 4100702;
377727, 4100432; 377722, 4100251;
377713, 4099980; 377856, 4099735;
377972, 4099581; 378422, 4099476;
378659, 4099318; 378563, 4099140;
378468, 4099023; 378282, 4098848;
378125, 4098672; 377937, 4098467;
377751, 4098322; 377623, 4098085;
377528, 4097938; 377462, 4097789;
377306, 4097614; 377026, 4097381;
376873, 4097296; 376869, 4097175;
377043, 4096959; 377279, 4096771;
377430, 4096766; 377522, 4096793;
377673, 4096819; 377887, 4096872;
378039, 4096898; 378249, 4096861;
378578, 4096760; 378698, 4096726;
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
378967, 4096627; 379089, 4096684;
379571, 4096608; 379781, 4096571;
380053, 4096563; 380202, 4096498;
380257, 4096346; 380221, 4096166;
380069, 4096111; 379856, 4096087;
379613, 4096035; 379459, 4095949;
379305, 4095864; 379182, 4095777;
378998, 4095692; 378874, 4095606;
378844, 4095607; 378751, 4095550;
378627, 4095433; 378532, 4095316;
378350, 4095291; 378168, 4095267;
377956, 4095243; 377831, 4095127;
377766, 4094978; 377722, 4095010;
377686, 4094830; 377563, 4094744;
377407, 4094598; 377257, 4094633;
377106, 4094638; 376865, 4094675;
376779, 4094799; 376630, 4094894;
376207, 4094877; 375932, 4094795;
375628, 4094714; 375475, 4094659;
374990, 4094614; 374778, 4094621;
374629, 4094656; 374445, 4094571;
374327, 4094665; 374149, 4094791;
374001, 4094886; 373852, 4094951;
373761, 4094924; 373728, 4094835;
373783, 4094682; 373748, 4094533;
373656, 4094475; 373477, 4094541;
373359, 4094635; 373150, 4094732;
373059, 4094705; 372935, 4094619;
372930, 4094468; 373017, 4094345;
372984, 4094256; 372949, 4094106;
372732, 4093932; 372517, 4093818;
372366, 4093823; 372188, 4093919;
372167, 4094221; 372117, 4094554;
372151, 4094673; 372216, 4094822;
372313, 4095030; 372682, 4095229;
372838, 4095375; 373206, 4095544;
373388, 4095568; 373626, 4095440;
373747, 4095436; 373900, 4095522;
373933, 4095581; 373906, 4095703;
373849, 4095795; 373820, 4095856;
373676, 4096071; 373527, 4096136;
373351, 4096292; 373142, 4096389;
372962, 4096425; 372841, 4096429;
372626, 4096315; 372446, 4096351;
372387, 4096383; 372332, 4096566;
372306, 4096717; 372068, 4096815;
371887, 4096821; 371648, 4096919;
371440, 4097015; 371287, 4096960;
371191, 4096812; 371041, 4096847;
371079, 4097087; 371235, 4097233;
371298, 4097321; 371571, 4097343;
371661, 4097340; 371963, 4097330;
372056, 4097388; 372059, 4097478;
372062, 4097598; 372068, 4097779;
372131, 4097867; 372278, 4097742;
372485, 4097585; 372753, 4097456;
372962, 4097389; 373146, 4097474;
373153, 4097684; 373065, 4097777;
372952, 4098022; 372899, 4098265;
373024, 4098381; 373145, 4098377;
373387, 4098400; 373391, 4098520;
373396, 4098671; 373283, 4098915;
373167, 4099070; 373018, 4099135;
372559, 4098968; 372437, 4098942;
372349, 4099005; 372291, 4099097;
372174, 4099221; 372026, 4099316;
371875, 4099321; 371785, 4099324;
371695, 4099357; 371515, 4099393;
PO 00000
Frm 00056
Fmt 4701
Sfmt 4700
371363, 4099368; 371240, 4099311;
371118, 4099285; 370871, 4099112;
370782, 4099145; 370755, 4099266;
370452, 4099246; 370267, 4099131;
370291, 4098919; 370103, 4098714;
369949, 4098629; 369733, 4098485;
369636, 4098277; 369478, 4098071;
369421, 4098164; 369397, 4098375;
369247, 4098410; 368883, 4098361;
368578, 4098251; 368421, 4098075;
368236, 4097960; 368408, 4097683;
368555, 4097528; 368516, 4097258;
368782, 4097069; 368900, 4096975;
368983, 4096732; 369070, 4096608;
369216, 4096453; 369333, 4096329;
369664, 4096288; 369960, 4096098;
370169, 4096031; 370227, 4095939;
370311, 4095726; 370395, 4095512;
370478, 4095268; 370471, 4095058;
370317, 4094972; 370228, 4095005;
370143, 4095189; 370086, 4095311;
370033, 4095554; 369852, 4095559;
369759, 4095472; 369754, 4095321;
369931, 4095195; 370052, 4095192;
369896, 4095046; 369683, 4094992;
369532, 4094997; 369377, 4094851;
369310, 4094673; 369183, 4094466;
369211, 4094405; 369359, 4094310;
369449, 4094277; 369688, 4094179;
370050, 4094167; 370288, 4094039;
370281, 4093829; 370067, 4093745;
369857, 4093812; 369530, 4093973;
369319, 4093980; 369109, 4094046;
368894, 4093933; 368830, 4093814;
368917, 4093691; 369065, 4093596;
369099, 4093715; 369248, 4093650;
369486, 4093522; 369694, 4093425;
369843, 4093361; 369959, 4093206;
369715, 4093124; 369443, 4093132;
369292, 4093137; 369229, 4093049;
369285, 4092926; 369737, 4092882;
370010, 4092903; 370348, 4093074;
370470, 4093130; 370718, 4093303;
370874, 4093479; 370969, 4093596;
371087, 4093502; 371205, 4093408;
371198, 4093197; 371193, 4093047;
371183, 4092716; 370931, 4092392;
370682, 4092159; 370465, 4092015;
370342, 4091929; 370126, 4091785;
369852, 4091734; 369636, 4091590;
369421, 4091476; 369237, 4091391;
368843, 4091344; 368665, 4091470;
368548, 4091594; 368360, 4091841;
368334, 4091992; 368373, 4092262;
368409, 4092442; 368479, 4092741;
368637, 4092977; 368673, 4093156;
368709, 4093336; 368531, 4093432;
368410, 4093436; 368414, 4093556;
368453, 4093826; 368457, 4093977;
368495, 4094216; 368565, 4094515;
368542, 4094727; 368574, 4094786;
368698, 4094903; 368789, 4094900;
368883, 4095018; 368919, 4095197;
368924, 4095348; 368868, 4095500;
368715, 4095445; 368595, 4095448;
368472, 4095392; 368227, 4095279;
368044, 4095225; 368078, 4095344;
368205, 4095551; 368331, 4095698;
E:\FR\FM\05AUR2.SGM
05AUR2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
368364, 4095787; 368307, 4095909;
368194, 4096154; 368168, 4096305;
368052, 4096430; 367957, 4096312;
367742, 4096198; 367646, 4096021;
367429, 4095847; 367213, 4095703;
367067, 4095888; 367194, 4096065;
367350, 4096211; 367413, 4096299;
367418, 4096450; 367606, 4096685;
367759, 4096740; 367882, 4096796;
368006, 4096913; 368070, 4097001;
368013, 4097124; 367892, 4097127;
367710, 4097103; 367467, 4097050;
367410, 4097173; 367536, 4097319;
367660, 4097436; 367724, 4097524;
367728, 4097675; 367734, 4097855;
367741, 4098066; 367655, 4098219;
367475, 4098255; 367205, 4098324;
366941, 4098573; 366794, 4098698;
366678, 4098853; 366739, 4098881;
366947, 4098784; 367216, 4098685;
367456, 4098617; 367575, 4098553;
367756, 4098548; 367879, 4098604;
368093, 4098688; 368185, 4098745;
368340, 4098860; 368404, 4098979;
368408, 4099099; 368413, 4099250;
368295, 4099344; 368022, 4099322;
367900, 4099296; 367718, 4099272;
367507, 4099278; 367328, 4099344;
367241, 4099468; 367424, 4099522;
367668, 4099605; 367791, 4099661;
367824, 4099750; 367735, 4099813;
367676, 4099845; 367556, 4099879;
367347, 4099946; 367135, 4099923;
367103, 4099894; 366918, 4099779;
366800, 4099843; 366619, 4099879;
366379, 4099916; 366200, 4099982;
366106, 4099895; 365983, 4099809;
366017, 4099928; 366051, 4100077;
366055, 4100198; 365817, 4100296;
365759, 4100388; 365764, 4100538;
365707, 4100661; 365468, 4100728;
365289, 4100825; 365262, 4100916;
365238, 4101097; 365242, 4101248;
365305, 4101306; 365338, 4101395;
365461, 4101482; 365583, 4101508;
365707, 4101595; 365977, 4101556;
366008, 4101555; 366064, 4101433;
366149, 4101249; 366112, 4101040;
366107, 4100889; 366194, 4100766;
366281, 4100643; 366337, 4100520;
366394, 4100398; 366634, 4100330;
366906, 4100352; 367057, 4100347;
367270, 4100370; 367542, 4100392;
367636, 4100479; 367759, 4100566;
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
367793, 4100685; 367768, 4100837;
367771, 4100927; 367534, 4101085;
367235, 4101185; 367092, 4101430;
367124, 4101490; 367185, 4101518;
367366, 4101512; 367606, 4101444;
367787, 4101438; 367910, 4101525;
368004, 4101612; 367978, 4101764;
367950, 4101825; 367743, 4101952;
367539, 4102199; 367574, 4102349;
367786, 4102372; 367993, 4102215;
368261, 4102086; 368496, 4101868;
368612, 4101714; 368728, 4101559;
368932, 4101342; 369076, 4101127;
369126, 4100794; 369116, 4100463;
368958, 4100257; 368834, 4100140;
368738, 4099993; 368643, 4099845;
368729, 4099692; 368852, 4099748;
369094, 4099771; 369240, 4099615;
369508, 4099486; 369412, 4099309;
369169, 4099286; 368986, 4099232;
368953, 4099142; 369102, 4099077;
369344, 4099070; 369771, 4099207;
369894, 4099263; 369926, 4099323;
370111, 4099437; 370208, 4099645;
370427, 4099879; 370519, 4099906;
370610, 4099934; 370672, 4099992;
370707, 4100141; 370743, 4100321;
370868, 4100437; 371083, 4100551;
371115, 4100610; 371028, 4100734;
370728, 4100803; 370514, 4100720;
370122, 4100732; 370126, 4100883;
370163, 4101092; 370288, 4101209;
370533, 4101322; 370744, 4101285;
370922, 4101189; 371195, 4101240;
371378, 4101265; 371409, 4101294;
371412, 4101414; 371358, 4101597;
371421, 4101685; 371541, 4101651;
371686, 4101466; 371830, 4101251;
371977, 4101125; 372163, 4101270;
372198, 4101420; 372147, 4101692;
372058, 4101755; 371972, 4101909;
372009, 4102119; 372133, 4102235;
372138, 4102386; 372050, 4102449;
371932, 4102543; 371809, 4102486;
371747, 4102428; 371629, 4102522;
371477, 4102497; 371327, 4102532;
371331, 4102652; 371182, 4102717;
371001, 4102723; 370879, 4102696;
370699, 4102732; 370400, 4102832;
370157, 4102810; 370092, 4102661;
370179, 4102538; 370358, 4102472;
370384, 4102351; 370381, 4102230;
370284, 4102052; 370043, 4102060;
369801, 4102068; 369442, 4102169;
PO 00000
Frm 00057
Fmt 4701
Sfmt 4700
45589
369050, 4102212; 368692, 4102344;
368607, 4102527; 368855, 4102730;
369133, 4102902; 369262, 4103169;
369148, 4103384; 369067, 4103687;
369165, 4103925; 369441, 4104037;
369619, 4103941; 369732, 4103697;
369879, 4103571; 370210, 4103531;
370366, 4103677; 370400, 4103796;
370434, 4103915; 370500, 4104094;
370416, 4104308; 370421, 4104458;
370544, 4104545; 370549, 4104695;
370497, 4104968; 370506, 4105239;
370688, 4105263; 370743, 4105080;
370857, 4104866; 370970, 4104621;
370933, 4104412; 370928, 4104261;
370924, 4104111; 370982, 4104049;
371073, 4104046; 371227, 4104161;
371263, 4104341; 371360, 4104519;
371490, 4104816; 371501, 4105177;
371446, 4105329; 371364, 4105603;
371340, 4105815; 371315, 4105966;
371229, 4106119; 371082, 4106245;
371001, 4106548; 370978, 4106790;
370984, 4106971; 370989, 4107121;
371055, 4107300; 371210, 4107415;
371395, 4107530; 371668, 4107582;
371718, 4107249; 371740, 4106977;
371758, 4106615; 371873, 4106430;
372109, 4106242; 372322, 4106266;
372390, 4106505; 372276, 4106749;
372192, 4106963; 371960, 4107271;
371880, 4107605; 371891, 4107936;
371868, 4108178; 371847, 4108450;
371856, 4108751; 371860, 4108871;
371957, 4109079; 372145, 4109284;
372207, 4109342; 372301, 4109429;
372518, 4109603; 372702, 4109688;
373006, 4109738; 373158, 4109764;
373430, 4109785; 373856, 4109862;
374282, 4109969; 374583, 4109930;
375005, 4109886; 375212, 4109759;
375603, 4109686; 375630, 4109681;
375627, 4109522; 376032, 4109425;
376434, 4109419; 376474, 4109418;
376515, 4109417; 376595, 4109416;
376635, 4109416; 376676, 4109415;
376716, 4109414; returning to 376756,
4109414.
(ii) Note: Map of Unit 5 (Taboose
Creek) for Sierra Nevada bighorn sheep
follows:
BILLING CODE 5310–55–P
E:\FR\FM\05AUR2.SGM
05AUR2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
BILLING CODE 5310–55–C
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
PO 00000
Frm 00058
Fmt 4701
Sfmt 4700
E:\FR\FM\05AUR2.SGM
05AUR2
ER05AU08.005
dwashington3 on PRODPC61 with RULES2
45590
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
(11) Unit 6 (Sawmill Canyon); Fresno
and Inyo Counties, California.
(i) From USGS 1:24,000 scale
quadrangles Mount Pinchot, Aberdeen,
Mount Clarence King and Kearsarge
Peak. Land bounded by the following
UTM zone 11 NAD83 coordinates (E, N):
380512, 4083384; 380416, 4083207;
380321, 4083059; 380256, 4082940;
380133, 4082854; 379980, 4082799;
379859, 4082802; 379709, 4082837;
379527, 4082813; 379374, 4082757;
379265, 4082696; 379160, 4082674;
379038, 4082647; 378867, 4082568;
378795, 4082595; 378516, 4082363;
378327, 4082128; 378166, 4081831;
378065, 4081503; 377933, 4081146;
377834, 4080878; 377738, 4080700;
377610, 4080493; 377442, 4080457;
377339, 4080502; 377219, 4080536;
376984, 4080754; 376746, 4080882;
376628, 4080946; 376239, 4081079;
376030, 4081176; 375641, 4081278;
375519, 4081252; 375032, 4081147;
374788, 4081064; 374635, 4081009;
374295, 4080749; 373983, 4080457;
374028, 4080221; 373860, 4080371;
373684, 4080557; 373540, 4080772;
373455, 4080956; 373288, 4081413;
373050, 4081541; 372934, 4081695;
372606, 4081826; 372340, 4082015;
372244, 4082045; 372121, 4082062;
371940, 4082079; 371706, 4082035;
371156, 4081842; 370857, 4081941;
370503, 4082224; 370199, 4082263;
369698, 4082060; 368468, 4081749;
367602, 4081695; 367089, 4081384;
366778, 4081235; 366399, 4081303;
366264, 4081871; 366778, 4082344;
367143, 4082763; 367427, 4083358;
367548, 4083750; 367616, 4084237;
367778, 4084629; 367995, 4084724;
368279, 4084669; 368495, 4084764;
368738, 4084940; 368968, 4085237;
369198, 4085400; 369536, 4085481;
369769, 4085771; 369933, 4086158;
370188, 4086602; 370528, 4086832;
370742, 4086916; 370782, 4087216;
370816, 4087335; 370850, 4087454;
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
370978, 4087691; 371016, 4087931;
371050, 4088051; 371089, 4088321;
371394, 4088401; 371664, 4088363;
371848, 4088447; 371973, 4088564;
372034, 4088592; 372340, 4088703;
372640, 4088633; 372970, 4088562;
373118, 4088467; 373447, 4088367;
373629, 4088361; 373659, 4088360;
373750, 4088387; 373842, 4088414;
373968, 4088591; 373971, 4088682;
374007, 4088861; 374100, 4088949;
374253, 4089004; 374464, 4088967;
374645, 4088962; 374768, 4089048;
374801, 4089137; 374776, 4089289;
374686, 4089322; 374443, 4089269;
374323, 4089303; 374265, 4089365;
374147, 4089459; 374089, 4089551;
374033, 4089674; 374071, 4089913;
374164, 4090001; 374256, 4090058;
374379, 4090115; 374439, 4090113;
374535, 4090260; 374479, 4090413;
374486, 4090623; 374585, 4090891;
374648, 4090980; 374742, 4091067;
374806, 4091186; 374869, 4091274;
374873, 4091394; 374944, 4091724;
375104, 4092020; 375353, 4092253;
375506, 4092308; 375784, 4092480;
376026, 4092503; 376146, 4092469;
376298, 4092494; 376391, 4092582;
376454, 4092670; 376548, 4092757;
376700, 4092783; 376851, 4092778;
377125, 4092860; 377249, 4092946;
377375, 4093123; 377410, 4093272;
377564, 4093358; 377719, 4093474;
378147, 4093641; 378302, 4093756;
378486, 4093841; 378704, 4094045;
378951, 4094218; 379315, 4094267;
379468, 4094322; 379649, 4094316;
379894, 4094399; 380136, 4094421;
380289, 4094477; 380473, 4094561;
380690, 4094735; 380873, 4094790;
381053, 4094754; 381294, 4094716;
381411, 4094592; 381403, 4094351;
381394, 4094081; 381389, 4093900;
381322, 4093691; 381288, 4093572;
381041, 4093429; 380797, 4093346;
380552, 4093234; 380575, 4093022;
380630, 4092839; 380441, 4092604;
380495, 4092392; 380611, 4092238;
PO 00000
Frm 00059
Fmt 4701
Sfmt 4700
45591
380818, 4092111; 380998, 4092045;
381116, 4091981; 381142, 4091829;
381107, 4091680; 380983, 4091593;
380798, 4091479; 380494, 4091398;
380431, 4091340; 380366, 4091191;
380361, 4091041; 380386, 4090859;
380532, 4090704; 380796, 4090454;
381061, 4090235; 381269, 4090108;
381504, 4089920; 381771, 4089761;
381913, 4089455; 381966, 4089213;
381956, 4088912; 381975, 4088550;
382088, 4088305; 382178, 4088272;
382237, 4088240; 382297, 4088238;
382537, 4088170; 382775, 4088042;
383039, 4087793; 383123, 4087580;
383323, 4087242; 383434, 4086907;
383638, 4086690; 383908, 4086621;
384089, 4086615; 384330, 4086578;
384450, 4086544; 384718, 4086445;
384987, 4086346; 385137, 4086311;
385317, 4086245; 385466, 4086180;
385554, 4086117; 385552, 4086057;
385399, 4085971; 385278, 4085975;
385186, 4085948; 385065, 4085922;
384944, 4085926; 384792, 4085900;
384672, 4085934; 384490, 4085910;
384369, 4085914; 384277, 4085856;
384185, 4085829; 384094, 4085802;
383696, 4085634; 383574, 4085607;
383452, 4085581; 383330, 4085525;
383178, 4085499; 383086, 4085472;
382963, 4085386; 382749, 4085332;
382537, 4085309; 382385, 4085283;
382231, 4085198; 381960, 4085206;
381842, 4085300; 381721, 4085304;
381628, 4085217; 381595, 4085127;
381529, 4084949; 381466, 4084890;
381429, 4084681; 381331, 4084443;
381176, 4084297; 381080, 4084150;
381016, 4084031; 380956, 4084033;
380773, 4083979; 380619, 4083893;
380582, 4083683; 380513, 4083414;
returning to 380512, 4083384.
(ii) Note: Map of Unit 6 (Sawmill
Canyon) for Sierra Nevada bighorn
sheep follows:
BILLING CODE 5310–55–P
E:\FR\FM\05AUR2.SGM
05AUR2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
BILLING CODE 5310–55–C
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
PO 00000
Frm 00060
Fmt 4701
Sfmt 4700
E:\FR\FM\05AUR2.SGM
05AUR2
ER05AU08.006
dwashington3 on PRODPC61 with RULES2
45592
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
(12) Unit 7 (Mount Baxter); Fresno
and Inyo Counties, California.
(i) From USGS 1:24,000 scale
quadrangles Aberdeen, Mount Clarence
King and Kearsarge Peak. Land bounded
by the following UTM zone 11 NAD83
coordinates (E, N): 374028, 4080221;
373983, 4080457; 374295, 4080749;
374635, 4081009; 374788, 4081064;
375032, 4081147; 375519, 4081252;
375641, 4081278; 376030, 4081176;
376239, 4081079; 376628, 4080946;
376746, 4080882; 376984, 4080754;
377219, 4080536; 377339, 4080502;
377442, 4080457; 377610, 4080493;
377738, 4080700; 377834, 4080878;
377933, 4081146; 378065, 4081503;
378166, 4081831; 378327, 4082128;
378516, 4082363; 378795, 4082595;
378867, 4082568; 379038, 4082647;
379160, 4082674; 379265, 4082696;
379374, 4082757; 379527, 4082813;
379709, 4082837; 379859, 4082802;
379980, 4082799; 380133, 4082854;
380256, 4082940; 380321, 4083059;
380416, 4083207; 380512, 4083384;
380727, 4083498; 380880, 4083553;
381125, 4083666; 381307, 4083660;
381760, 4083676; 382157, 4083814;
382374, 4083988; 382561, 4084163;
382902, 4084423; 382969, 4084632;
383097, 4084869; 383261, 4085256;
383416, 4085401; 383537, 4085398;
383692, 4085513; 383967, 4085625;
384119, 4085650; 384182, 4085709;
384213, 4085738; 384244, 4085767;
384367, 4085853; 384670, 4085874;
384852, 4085898; 385092, 4085830;
385213, 4085827; 385396, 4085881;
385515, 4085817; 385631, 4085663;
385715, 4085479; 385770, 4085297;
385765, 4085147; 385729, 4084967;
385662, 4084758; 385564, 4084520;
385498, 4084342; 385402, 4084164;
385277, 4084047; 385184, 4083960;
385117, 4083751; 385113, 4083631;
385078, 4083481; 385073, 4083331;
385069, 4083210; 385124, 4083028;
385088, 4082848; 385084, 4082728;
385114, 4082697; 385234, 4082693;
385384, 4082658; 385383, 4082598;
385318, 4082480; 385255, 4082391;
385162, 4082304; 385128, 4082184;
385124, 4082064; 385023, 4081736;
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
384960, 4081647; 384898, 4081619;
384777, 4081593; 384649, 4081386;
384581, 4081147; 384392, 4080912;
384386, 4080702; 384320, 4080523;
384199, 4080527; 384108, 4080530;
383867, 4080537; 383745, 4080511;
383682, 4080423; 383584, 4080185;
383519, 4080036; 383422, 4079858;
383385, 4079619; 383318, 4079410;
383126, 4079084; 382787, 4078884;
382573, 4078801; 382268, 4078720;
382054, 4078636; 381899, 4078491;
381864, 4078341; 381857, 4078130;
382123, 4077941; 382299, 4077785;
382598, 4077685; 382685, 4077562;
382772, 4077439; 382798, 4077317;
382762, 4077138; 382693, 4076869;
382628, 4076720; 382592, 4076541;
382467, 4076394; 382431, 4076214;
382422, 4075944; 382420, 4075853;
382415, 4075703; 382411, 4075582;
382376, 4075433; 382219, 4075257;
382127, 4075200; 382006, 4075204;
381917, 4075237; 381828, 4075300;
381588, 4075367; 381498, 4075370;
381257, 4075408; 380982, 4075296;
380831, 4075301; 380799, 4075242;
380856, 4075149; 381004, 4075054;
381064, 4075022; 381215, 4075018;
381455, 4074980; 381605, 4074945;
381725, 4074911; 381844, 4074847;
382054, 4074810; 382239, 4074925;
382392, 4074981; 382544, 4075006;
382632, 4074913; 382593, 4074643;
382436, 4074467; 382281, 4074351;
382129, 4074296; 382216, 4074203;
382393, 4074047; 382659, 4073858;
382774, 4073673; 382858, 4073460;
382822, 4073280; 382787, 4073131;
382753, 4073011; 382778, 4072860;
382835, 4072737; 382895, 4072736;
383014, 4072672; 383010, 4072551;
382977, 4072462; 382885, 4072404;
382761, 4072318; 382640, 4072322;
382489, 4072327; 382488, 4072266;
382575, 4072173; 382694, 4072109;
382968, 4072161; 382965, 4072071;
382933, 4072011; 382902, 4071982;
382839, 4071924; 382810, 4071955;
382750, 4071957; 382686, 4071869;
382565, 4071842; 382502, 4071754;
382409, 4071696; 382314, 4071549;
382310, 4071428; 382273, 4071219;
382268, 4071068; 382264, 4070918;
PO 00000
Frm 00061
Fmt 4701
Sfmt 4700
45593
382141, 4070861; 381900, 4070869;
381691, 4070966; 381361, 4071037;
381238, 4070980; 380965, 4070929;
380812, 4070873; 380627, 4070759;
380476, 4070763; 380386, 4070796;
380329, 4070888; 380183, 4071044;
380004, 4071140; 379946, 4071202;
379823, 4071145; 379698, 4070999;
379600, 4070761; 379445, 4070645;
379050, 4070567; 378715, 4070487;
378534, 4070493; 378263, 4070532;
378142, 4070536; 377869, 4070514;
377753, 4070668; 377635, 4070762;
377516, 4070796; 377272, 4070744;
377151, 4070717; 376969, 4070723;
376700, 4070792; 376551, 4070857;
376068, 4070872; 375768, 4070942;
375405, 4070953; 375071, 4070903;
374892, 4070969; 374774, 4071063;
374477, 4071223; 374114, 4071205;
373869, 4071092; 373301, 4071291;
373065, 4071479; 372945, 4071628;
373168, 4071877; 373380, 4072302;
373305, 4073027; 373293, 4073252;
373093, 4073577; 372943, 4073790;
372693, 4073852; 372480, 4073752;
372330, 4073514; 372255, 4073289;
371993, 4073327; 371693, 4073689;
371543, 4074102; 371843, 4074765;
372030, 4075127; 372243, 4075427;
372205, 4075727; 371980, 4075927;
371824, 4076302; 371812, 4077578;
371661, 4078453; 371486, 4078640;
371024, 4078703; 370743, 4078628;
370443, 4078490; 370226, 4078314;
370197, 4078295; 370023, 4078503;
370037, 4078955; 369931, 4079410;
369948, 4079952; 370023, 4080401;
370216, 4080787; 370463, 4080930;
370861, 4081098; 371163, 4081088;
371407, 4081171; 371836, 4081368;
372051, 4081482; 372322, 4081443;
372676, 4081161; 372814, 4080765;
372865, 4080462; 373090, 4079913;
373259, 4079546; 373580, 4079174;
373739, 4079410; 373866, 4079617;
374025, 4079883; 374061, 4080063;
374035, 4080184; returning to 374028,
4080221.
(ii) Note: Map of Unit 7 (Mount
Baxter) for Sierra Nevada bighorn sheep
follows:
BILLING CODE 5310–55–P
E:\FR\FM\05AUR2.SGM
05AUR2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
BILLING CODE 5310–55–C
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
PO 00000
Frm 00062
Fmt 4701
Sfmt 4700
E:\FR\FM\05AUR2.SGM
05AUR2
ER05AU08.007
dwashington3 on PRODPC61 with RULES2
45594
dwashington3 on PRODPC61 with RULES2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
(13) Unit 8 (Mount Williamson); Inyo
and Tulare Counties, California.
(i) From USGS 1:24,000 scale
quadrangle Kearsarge Peak, Mount
Brewer, Mount Williamson, Manzanar,
Mount Whitney and Mount Langley.
Land bounded by the following UTM
zone 11 NAD83 coordinates (E, N):
384282, 4069770; 384492, 4069703;
384612, 4069699; 384763, 4069694;
384974, 4069658; 385152, 4069562;
385148, 4069441; 384994, 4069356;
384934, 4069358; 384840, 4069270;
384627, 4069217; 384623, 4069096;
384617, 4068886; 384580, 4068676;
384570, 4068345; 384463, 4067836;
384390, 4067447; 384376, 4066995;
384334, 4066635; 384385, 4066332;
384439, 4066120; 384495, 4065998;
384611, 4065813; 384637, 4065692;
384753, 4065538; 384810, 4065445;
384959, 4065380; 385077, 4065286;
384980, 4065079; 384910, 4064780;
384839, 4064450; 384862, 4064209;
384918, 4064056; 385100, 4064081;
385438, 4064281; 385590, 4064306;
385804, 4064360; 386017, 4064413;
386229, 4064437; 386532, 4064457;
386649, 4064333; 386769, 4064299;
386886, 4064205; 387004, 4064111;
387091, 4063988; 387176, 4063804;
387171, 4063654; 387194, 4063412;
387310, 4063258; 387397, 4063135;
387484, 4063042; 387660, 4062855;
387746, 4062702; 387828, 4062458;
387887, 4062396; 387883, 4062276;
387817, 4062097; 387843, 4061976;
387870, 4061855; 387898, 4061794;
387989, 4061791; 388140, 4061786;
388260, 4061782; 388319, 4061720;
388316, 4061630; 388344, 4061569;
388460, 4061414; 388579, 4061350;
388606, 4061229; 388631, 4061078;
388595, 4060898; 388555, 4060598;
388580, 4060417; 388546, 4060297;
388542, 4060177; 388630, 4060084;
388839, 4060017; 388928, 4059954;
388773, 4059838; 388618, 4059722;
388402, 4059579; 388397, 4059398;
388391, 4059217; 388447, 4059065;
388594, 4058940; 388774, 4058904;
388864, 4058871; 389100, 4058713;
389155, 4058531; 389363, 4058404;
389540, 4058278; 389596, 4058155;
389626, 4058124; 389745, 4058090;
389835, 4058057; 389834, 4058027;
389832, 4057967; 389829, 4057877;
389793, 4057697; 389668, 4057551;
389602, 4057372; 389476, 4057225;
389472, 4057075; 389497, 4056923;
389524, 4056832; 389490, 4056683;
389393, 4056505; 389239, 4056419;
389119, 4056423; 388970, 4056488;
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
388908, 4056460; 388935, 4056339;
388928, 4056128; 388917, 4055767;
388912, 4055616; 388873, 4055346;
388742, 4055019; 388615, 4054812;
388579, 4054633; 388511, 4054394;
388566, 4054241; 388716, 4054177;
388927, 4054170; 388956, 4054139;
389047, 4054136; 389195, 4054041;
389404, 4053974; 389523, 4053910;
389613, 4053877; 389637, 4053696;
389606, 4053667; 389515, 4053669;
389362, 4053584; 389208, 4053498;
388962, 4053355; 388780, 4053331;
388597, 4053277; 388261, 4053167;
388014, 4053024; 387829, 4052879;
387458, 4052620; 387303, 4052504;
387118, 4052389; 386845, 4052338;
386600, 4052255; 386356, 4052172;
386230, 4052026; 385918, 4051704;
385734, 4051619; 385550, 4051535;
385187, 4051516; 385006, 4051522;
384674, 4051532; 384346, 4051663;
384167, 4051759; 383870, 4051919;
383573, 4052079; 383456, 4052203;
383402, 4052416; 383346, 4052538;
383319, 4052629; 383116, 4052907;
382907, 4053004; 382548, 4053105;
382245, 4053085; 382121, 4052998;
381970, 4052973; 381696, 4052921;
381422, 4052870; 381087, 4052760;
380627, 4052563; 380323, 4052513;
380085, 4052610; 380029, 4052763;
379974, 4052945; 380013, 4053215;
380141, 4053422; 380360, 4053686;
380609, 4053919; 380948, 4054120;
381137, 4054355; 381414, 4054527;
381478, 4054645; 381571, 4054703;
381610, 4054972; 381611, 4055033;
381616, 4055183; 381592, 4055365;
381537, 4055547; 381513, 4055759;
381430, 4055972; 381345, 4056156;
381109, 4056344; 380873, 4056532;
380604, 4056631; 380274, 4056701;
380091, 4056647; 379968, 4056560;
379993, 4056409; 380049, 4056257;
380102, 4056044; 380036, 4055865;
379851, 4055751; 379547, 4055670;
379304, 4055647; 378973, 4055688;
378731, 4055665; 378518, 4055642;
378304, 4055558; 378158, 4055714;
378223, 4055862; 378114, 4056227;
377969, 4056443; 377946, 4056654;
378101, 4056770; 378405, 4056851;
378590, 4056965; 378715, 4057082;
378841, 4057259; 378934, 4057316;
379088, 4057402; 379180, 4057459;
379273, 4057546; 379521, 4057719;
379646, 4057866; 379741, 4058014;
379896, 4058129; 380108, 4058153;
380260, 4058178; 380561, 4058138;
380806, 4058251; 380993, 4058426;
380972, 4058698; 380976, 4058848;
380712, 4059098; 380536, 4059254;
PO 00000
Frm 00063
Fmt 4701
Sfmt 4700
45595
380206, 4059324; 379996, 4059391;
379902, 4059274; 379722, 4059310;
379631, 4059312; 379453, 4059408;
379369, 4059622; 379312, 4059744;
379080, 4060053; 378929, 4060027;
378803, 4059881; 378768, 4059731;
378794, 4059580; 378759, 4059430;
378755, 4059310; 378691, 4059191;
378537, 4059106; 378325, 4059082;
378175, 4059117; 378049, 4058971;
377834, 4058857; 377650, 4058772;
377526, 4058656; 377492, 4058536;
377306, 4058391; 377186, 4058425;
377161, 4058607; 377077, 4058790;
377052, 4058972; 376908, 4059187;
376820, 4059280; 376702, 4059374;
376581, 4059378; 376525, 4059501;
376711, 4059645; 376924, 4059699;
377053, 4059966; 377151, 4060204;
377277, 4060350; 377435, 4060587;
377600, 4061003; 377637, 4061243;
377703, 4061422; 377738, 4061571;
377771, 4061660; 377898, 4061837;
377992, 4061955; 378115, 4062011;
378327, 4062035; 378478, 4062030;
378900, 4061986; 379110, 4061950;
379325, 4062063; 379420, 4062181;
379485, 4062329; 379672, 4062534;
379860, 4062739; 380015, 4062855;
380292, 4063027; 380417, 4063144;
380483, 4063322; 380579, 4063500;
380562, 4063922; 380460, 4064498;
380261, 4064896; 380149, 4065201;
379947, 4065478; 379629, 4065940;
379428, 4066278; 379342, 4066431;
379258, 4066644; 379299, 4066975;
379427, 4067211; 379584, 4067387;
379680, 4067565; 379718, 4067805;
379784, 4067983; 379940, 4068159;
380098, 4068365; 380252, 4068451;
380591, 4068651; 380653, 4068709;
380777, 4068826; 380840, 4068884;
380901, 4068912; 380964, 4069001;
381026, 4069059; 381120, 4069146;
381180, 4069144; 381242, 4069173;
381362, 4069169; 381453, 4069166;
381543, 4069163; 381785, 4069156;
381935, 4069121; 382146, 4069114;
382297, 4069109; 382358, 4069107;
382478, 4069104; 382539, 4069102;
382572, 4069191; 382725, 4069246;
382815, 4069244; 382906, 4069241;
383119, 4069294; 383210, 4069322;
383243, 4069411; 383310, 4069590;
383403, 4069677; 383616, 4069731;
383828, 4069754; 383919, 4069751;
384010, 4069748; returning to 384282,
4069770.
(ii) Note: Map of Unit 8 (Mount
Williamson) for Sierra Nevada bighorn
sheep follows:
BILLING CODE 5310–55–P
E:\FR\FM\05AUR2.SGM
05AUR2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
BILLING CODE 5310–55–C
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
PO 00000
Frm 00064
Fmt 4701
Sfmt 4700
E:\FR\FM\05AUR2.SGM
05AUR2
ER05AU08.008
dwashington3 on PRODPC61 with RULES2
45596
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
(14) Unit 9 (Big Arroyo); Tulare
County, California.
(i) From USGS 1:24,000 scale
quadrangles Triple Divide Peak, Mount
Kaweah, and Chagoopa Falls. Land
bounded by the following UTM zone 11
NAD83 coordinates (E, N): 367856,
4049078; 368038, 4049073; 368311,
4049124; 368644, 4049144; 368824,
4049108; 369090, 4048919; 369207,
4048795; 369203, 4048644; 369201,
4048584; 369169, 4048525; 369072,
4048347; 368645, 4048210; 368224,
4048284; 367925, 4048383; 367593,
4048394; 367503, 4048397; 367260,
4048374; 366955, 4048293; 366591,
4048244; 366345, 4048102; 365916,
4047904; 365549, 4047765; 365361,
4047560; 364989, 4047270; 364864,
4047124; 364797, 4046915; 364973,
4046759; 365395, 4046715; 365735,
4046946; 366102, 4047085; 366467,
4047164; 366891, 4047211; 367465,
4047193; 367920, 4047269; 368407,
4047374; 368560, 4047429; 369013,
4047415; 368911, 4047057; 368632,
4046825; 368322, 4046593; 367802,
4046399; 367406, 4046291; 366767,
4046130; 366404, 4046141; 366068,
4046031; 365913, 4045886; 365868,
4045435; 366038, 4045068; 366392,
4044786; 366506, 4044572; 367012,
4044315; 366916, 4044167; 366999,
4043924; 367179, 4043858; 367575,
4043966; 367970, 4044044; 368277,
4044185; 368402, 4044331; 368714,
4044653; 369028, 4045005; 369348,
4045597; 369454, 4046076; 369830,
4046486; 370175, 4046897; 370518,
4047247; 370783, 4047028; 370644,
4046430; 370695, 4046127; 370690,
4045977; 370534, 4045831; 370317,
4045657; 370041, 4045515; 369914,
4045338; 369817, 4045130; 369781,
4044951; 369897, 4044797; 370077,
4044731; 370292, 4044844; 370507,
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
4044958; 370665, 4045194; 370946,
4045487; 371279, 4045506; 371607,
4045345; 372024, 4045152; 372379,
4044929; 372551, 4044623; 372817,
4044434; 373092, 4044546; 373223,
4044843; 373304, 4045503; 373323,
4046105; 373219, 4046650; 372992,
4047109; 372919, 4047684; 372692,
4048143; 372701, 4048414; 373011,
4048675; 373283, 4048667; 373432,
4048602; 373602, 4048265; 373805,
4047988; 373975, 4047621; 374080,
4047105; 374277, 4046647; 374322,
4046164; 374308, 4045712; 374200,
4045174; 374158, 4044783; 374181,
4044572; 374200, 4044210; 374217,
4043787; 374236, 4043425; 374288,
4043152; 374391, 4042607; 374467,
4042122; 374516, 4041759; 374537,
4041488; 374470, 4041279; 374347,
4041192; 374136, 4041229; 374014,
4041173; 373950, 4041054; 373904,
4040574; 373897, 4040333; 373915,
4039971; 373903, 4039579; 373888,
4039098; 373877, 4038737; 373895,
4038375; 373915, 4038043; 373877,
4037773; 373839, 4037533; 373619,
4037269; 373549, 4036970; 373479,
4036670; 373530, 4036368; 373518,
4035976; 373478, 4035676; 373263,
4035563; 373112, 4035567; 373019,
4035480; 373040, 4035208; 373120,
4034844; 373172, 4034601; 373171,
4034571; 373195, 4034360; 373188,
4034149; 373125, 4034061; 373093,
4034001; 372881, 4033978; 372671,
4034015; 372489, 4034020; 372278,
4034027; 372096, 4034002; 372005,
4034005; 371642, 4033987; 371403,
4034054; 371161, 4034062; 371012,
4034127; 370652, 4034198; 370474,
4034294; 370386, 4034387; 369997,
4034520; 369847, 4034555; 369670,
4034681; 369253, 4034875; 368900,
4035187; 368785, 4035372; 368611,
4035588; 368408, 4035866; 368444,
PO 00000
Frm 00065
Fmt 4701
Sfmt 4700
45597
4036045; 368544, 4036343; 368613,
4036612; 368531, 4036916; 368483,
4037309; 368432, 4037582; 368318,
4037827; 368114, 4038044; 367910,
4038291; 367764, 4038447; 367616,
4038542; 367411, 4038759; 367265,
4038914; 366971, 4039194; 366588,
4039508; 366295, 4039788; 366005,
4040159; 365710, 4040409; 365323,
4040602; 364940, 4040885; 364704,
4041073; 364407, 4041233; 364172,
4041451; 363937, 4041670; 363675,
4041979; 363294, 4042383; 363033,
4042722; 362830, 4043000; 362598,
4043309; 362513, 4043462; 362550,
4043702; 362773, 4044056; 362873,
4044354; 362976, 4044743; 362987,
4045104; 362907, 4045438; 362796,
4045743; 362624, 4046049; 362419,
4046267; 362243, 4046423; 362434,
4046718; 362771, 4046888; 363048,
4047030; 363355, 4047201; 363540,
4047316; 363809, 4047217; 363990,
4047211; 364085, 4047329; 364213,
4047566; 364430, 4047740; 364638,
4047643; 364880, 4047635; 364946,
4047814; 364918, 4047875; 364772,
4048061; 364751, 4048332; 364757,
4048543; 364885, 4048750; 365096,
4048743; 365274, 4048647; 365419,
4048432; 365540, 4048458; 365753,
4048482; 365964, 4048475; 366116,
4048500; 366302, 4048645; 366454,
4048671; 366638, 4048755; 366736,
4048993; 366926, 4049288; 367023,
4049466; 367148, 4049613; 367333,
4049727; 367635, 4049718; 367747,
4049443; 367652, 4049296; 367648,
4049175; 367736, 4049082; returning to
367856, 4049078.
(ii) Note: Map of Unit 9 (Big Arroyo)
for Sierra Nevada bighorn sheep
follows:
BILLING CODE 5310–55–P
E:\FR\FM\05AUR2.SGM
05AUR2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
BILLING CODE 5310–55–C
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
PO 00000
Frm 00066
Fmt 4701
Sfmt 4700
E:\FR\FM\05AUR2.SGM
05AUR2
ER05AU08.009
dwashington3 on PRODPC61 with RULES2
45598
dwashington3 on PRODPC61 with RULES2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
(15) Unit 10 (Mount Langley); Inyo
and Tulare Counties, California.
(i) From USGS 1:24,000 scale
quadrangles Mount Whitney, Mount
Langley, Lone Pine, Johnson Peak,
Cirque Peak, and Bartlett. Land bounded
by the following UTM zone 11 NAD83
coordinates (E, N): 391201, 4048676;
391835, 4048656; 392289, 4048672;
392648, 4048570; 393008, 4048499;
393517, 4048332; 393840, 4048051;
393861, 4047749; 393701, 4047453;
393997, 4047263; 394301, 4047313;
394691, 4047241; 394959, 4047112;
394980, 4046810; 394761, 4046576;
394545, 4046432; 394209, 4046322;
393872, 4046182; 393805, 4045973;
393952, 4045848; 394346, 4045866;
394557, 4045859; 394797, 4045822;
394914, 4045698; 395096, 4045722;
395312, 4045836; 395435, 4045922;
395609, 4045676; 395357, 4045352;
395142, 4045239; 394955, 4045064;
394737, 4044860; 394607, 4044562;
394630, 4044351; 394785, 4044466;
394972, 4044641; 395189, 4044815;
395465, 4044957; 395741, 4045069;
396017, 4045211; 396292, 4045323;
396624, 4045312; 396865, 4045275;
397011, 4045120; 396916, 4044972;
396912, 4044852; 396906, 4044671;
396989, 4044427; 397139, 4044392;
397225, 4044239; 397130, 4044092;
397004, 4043945; 396941, 4043856;
396910, 4043827; 396816, 4043710;
396872, 4043588; 397085, 4043611;
397269, 4043726; 397424, 4043841;
397610, 4043986; 397705, 4044134;
397826, 4044130; 397974, 4044035;
397988, 4043910; 398032, 4043812;
398101, 4043709; 398135, 4043591;
398258, 4043464; 398459, 4043386;
398630, 4043312; 398832, 4043175;
399028, 4043028; 399145, 4042939;
399209, 4042895; 399312, 4042807;
399366, 4042758; 399410, 4042704;
399454, 4042670; 399582, 4042567;
399694, 4042459; 399758, 4042385;
399846, 4042312; 399944, 4042199;
400033, 4042101; 400096, 4041978;
400219, 4041836; 400286, 4041643;
400252, 4041523; 400128, 4041437;
400005, 4041380; 399883, 4041324;
399698, 4041209; 399455, 4041157;
399327, 4040950; 399383, 4040797;
399592, 4040731; 399927, 4040810;
400292, 4040889; 400718, 4040966;
401019, 4040957; 401230, 4040920;
401313, 4040742; 401218, 4040743;
401216, 4040470; 401215, 4040469;
401123, 4040411; 400849, 4040330;
400699, 4040395; 400579, 4040398;
400425, 4040313; 400272, 4040257;
400151, 4040261; 399969, 4040237;
399818, 4040242; 399727, 4040214;
399573, 4040129; 399364, 4040196;
399184, 4040231; 399001, 4040177;
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
398875, 4040030; 398718, 4039824;
398769, 4039552; 398794, 4039370;
398816, 4039098; 398776, 4038798;
398854, 4038404; 398936, 4038130;
399265, 4038030; 399537, 4038021;
399838, 4037982; 400353, 4038026;
400864, 4037949; 401406, 4037902;
402036, 4037732; 402453, 4037568;
403052, 4037399; 403265, 4037370;
403437, 4037350; 403454, 4037349;
403451, 4037001; 403437, 4037001;
402801, 4037105; 402468, 4037086;
401954, 4037072; 401743, 4037078;
401474, 4037177; 401200, 4037095;
400986, 4037012; 400832, 4036926;
400587, 4036813; 400582, 4036663;
400580, 4036603; 400666, 4036449;
400841, 4036263; 401078, 4036105;
401286, 4036008; 401736, 4035904;
402332, 4035644; 402478, 4035459;
402592, 4035244; 402736, 4035029;
402939, 4034751; 403054, 4034567;
403316, 4034257; 403521, 4034040;
403693, 4033764; 403840, 4033638;
403988, 4033543; 404106, 4033449;
404311, 4033232; 404456, 4033047;
404629, 4032770; 404746, 4032646;
404742, 4032526; 404646, 4032378;
404481, 4032210; 404371, 4031974;
404270, 4031915; 404169, 4031814;
404034, 4031695; 403840, 4031602;
403679, 4031476; 403510, 4031223;
403325, 4031113; 403114, 4030986;
402911, 4030843; 402683, 4030682;
402455, 4030471; 402345, 4030421;
402016, 4030302; 401797, 4030311;
401611, 4030311; 401256, 4030370;
401079, 4030370; 400767, 4030328;
400404, 4030286; 400100, 4030159;
399880, 4030100; 399745, 4030286;
399661, 4030640; 399568, 4030868;
399652, 4031501; 399492, 4031881;
399323, 4032202; 399070, 4032464;
398876, 4032742; 398758, 4033029;
398606, 4033527; 398766, 4033823;
398859, 4034354; 398867, 4034473;
398867, 4034574; 398867, 4034692;
398859, 4034768; 398867, 4034878;
398859, 4034962; 398842, 4035047;
398817, 4035156; 398825, 4035292;
398817, 4035418; 398783, 4035553;
398775, 4035671; 398741, 4035787;
398591, 4035822; 398442, 4035887;
398294, 4035982; 398026, 4036080;
397844, 4036086; 397727, 4036104;
397729, 4036166; 397321, 4036177;
397117, 4036180; 397065, 4036291;
397073, 4036532; 397229, 4036678;
397565, 4036818; 397899, 4036868;
398144, 4036950; 398575, 4037208;
398760, 4037323; 398826, 4037501;
398587, 4037599; 398285, 4037609;
398074, 4037615; 397779, 4037835;
397573, 4038023; 397247, 4038214;
396925, 4038555; 396808, 4038679;
396694, 4038894; 396521, 4039140;
PO 00000
Frm 00067
Fmt 4701
Sfmt 4700
45599
396440, 4039474; 396020, 4039548;
395687, 4039528; 395353, 4039478;
395015, 4039308; 394354, 4039419;
393996, 4039551; 393553, 4039896;
393199, 4040148; 392841, 4040310;
392599, 4040288; 392388, 4040324;
392208, 4040360; 392026, 4040336;
391845, 4040341; 391695, 4040376;
391607, 4040469; 391464, 4040715;
391168, 4040905; 391019, 4040970;
390717, 4040979; 390615, 4040870;
390526, 4040776; 390443, 4040719;
390324, 4040646; 390241, 4040657;
390158, 4040641; 390080, 4040574;
390002, 4040480; 389955, 4040018;
390023, 4039509; 389862, 4039176;
389441, 4038958; 389108, 4038818;
389015, 4038797; 388682, 4038673;
388527, 4038553; 388246, 4038309;
388225, 4038111; 388142, 4038091;
388054, 4038169; 387992, 4038413;
387898, 4039083; 387695, 4039478;
387443, 4039666; 387108, 4039586;
386653, 4039541; 386445, 4039637;
386479, 4039787; 386788, 4039988;
387154, 4040097; 387492, 4040267;
387587, 4040415; 387626, 4040685;
387539, 4040808; 387242, 4040968;
387030, 4040945; 386663, 4040805;
386571, 4040778; 386423, 4040873;
386520, 4041081; 386706, 4041226;
386895, 4041461; 387083, 4041696;
387183, 4041994; 387197, 4042415;
387266, 4042684; 387125, 4043020;
387068, 4043112; 386891, 4043269;
386710, 4043274; 386617, 4043187;
386370, 4043014; 386328, 4042654;
386323, 4042503; 386227, 4042325;
386193, 4042206; 386187, 4042025;
386181, 4041815; 386147, 4041695;
385866, 4041403; 385677, 4041168;
385489, 4040963; 385424, 4040814;
385175, 4040581; 384687, 4040446;
384085, 4040495; 383395, 4040667;
382950, 4040922; 382597, 4041234;
382557, 4041868; 382965, 4042368;
383585, 4042860; 383899, 4043242;
383974, 4043692; 384083, 4044291;
384064, 4044653; 384347, 4045005;
384752, 4045384; 385209, 4045490;
385338, 4045757; 385674, 4045867;
386068, 4045915; 386432, 4045964;
386733, 4045925; 387003, 4045856;
387456, 4045842; 387935, 4045706;
388454, 4045870; 388701, 4046043;
388853, 4046069; 389062, 4046002;
389305, 4046024; 389585, 4046287;
389713, 4046524; 389873, 4046790;
390029, 4046966; 390102, 4047355;
390199, 4047563; 390149, 4047896;
390462, 4048217; 390866, 4048596;
returning to 391201, 4048676.
(ii) Note: Map of Unit 10 (Mount
Langley) for Sierra Nevada bighorn
sheep follows:
BILLING CODE 5310–55–P
E:\FR\FM\05AUR2.SGM
05AUR2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
BILLING CODE 5310–55–C
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
PO 00000
Frm 00068
Fmt 4701
Sfmt 4700
E:\FR\FM\05AUR2.SGM
05AUR2
ER05AU08.010
dwashington3 on PRODPC61 with RULES2
45600
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
(16) Unit 11 (Laurel Creek); Tulare
County, California.
(i) From USGS 1:24,000 scale
quadrangles Mineral King, Chagoopa
Falls, Quinn Peak, and Kern Lake. Land
bounded by the following UTM zone 11
NAD83 coordinates (E, N): 373174,
4031891; 373186, 4031558; 373154,
4031248; 373234, 4030979; 373246,
4030646; 373240, 4030446; 373299,
4030200; 373294, 4030045; 373311,
4029867; 373368, 4029577; 373315,
4029290; 373265, 4029114; 373238,
4028981; 373232, 4028782; 373228,
4028671; 373244, 4028471; 373261,
4028292; 373235, 4028160; 373118,
4027986; 373114, 4027853; 373201,
4027784; 373307, 4027625; 373303,
4027492; 373295, 4027248; 373288,
4027026; 373370, 4026802; 373343,
4026647; 373335, 4026403; 373361,
4025803; 373349, 4025426; 373426,
4025046; 373542, 4024488; 373421,
4024158; 373270, 4024319; 373084,
4024791; 372982, 4025082; 372972,
4025460; 373002, 4025726; 372967,
4026015; 372813, 4026087; 372622,
4026381; 372567, 4026738; 372492,
4027184; 372494, 4027251; 372544,
4027449; 372683, 4027600; 372797,
4027685; 372844, 4027773; 372868,
4027839; 372850, 4027950; 372627,
4027957; 372493, 4027939; 372334,
4027833; 372088, 4027819; 371867,
4027848; 371735, 4027896; 371467,
4027883; 371376, 4027819; 371153,
4027804; 370951, 4027743; 370794,
4027704; 370614, 4027665; 370368,
4027628; 370167, 4027590; 369942,
4027531; 369740, 4027471; 369540,
4027477; 369315, 4027417; 369225,
4027376; 369088, 4027291; 368842,
4027232; 368686, 4027237; 368416,
4027135; 368191, 4027075; 368057,
4027057; 367878, 4027018; 367675,
4026936; 367474, 4026920; 367297,
4026970; 367076, 4027021; 366900,
4027093; 366656, 4027101; 366475,
4027018; 366339, 4026933; 366202,
4026827; 366128, 4026607; 365901,
4026481; 365715, 4026220; 365708,
4025999; 365794, 4025885; 366031,
4025655; 366097, 4025609; 366225,
4025450; 366418, 4025199; 366479,
4025020; 366407, 4024844; 366270,
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
4024760; 366159, 4024741; 365979,
4024680; 365753, 4024599; 365468,
4024718; 365362, 4024899; 365163,
4024950; 365047, 4024798; 365032,
4024310; 364847, 4024094; 364692,
4024121; 364515, 4024171; 364294,
4024222; 364143, 4024360; 363697,
4024352; 363475, 4024359; 363204,
4024257; 362979, 4024175; 362728,
4023983; 362562, 4023655; 362372,
4023284; 362190, 4023156; 361949,
4023275; 361734, 4023526; 361439,
4024046; 361355, 4024226; 361276,
4024539; 361283, 4024739; 361287,
4024894; 361272, 4025116; 361278,
4025294; 361376, 4025579; 361426,
4025778; 361250, 4025827; 361010,
4025990; 360838, 4026196; 360688,
4026378; 360408, 4026675; 360260,
4026924; 360046, 4027197; 359897,
4027402; 359791, 4027583; 359529,
4027746; 359063, 4027783; 358774,
4027814; 358531, 4027866; 358309,
4027895; 358180, 4028033; 358116,
4028124; 358009, 4028282; 357927,
4028485; 357931, 4028618; 358005,
4028837; 358096, 4028901; 358170,
4029143; 358309, 4029316; 358871,
4029476; 359141, 4029579; 359257,
4029708; 359484, 4029857; 359667,
4030028; 359672, 4030184; 359521,
4030322; 359325, 4030483; 359243,
4030686; 359295, 4030928; 359325,
4031171; 359351, 4031282; 359270,
4031551; 359321, 4031749; 359261,
4031973; 359113, 4032221; 358851,
4032407; 358587, 4032504; 358259,
4032692; 358269, 4033003; 358344,
4033267; 358592, 4033348; 358837,
4033362; 358952, 4033470; 359201,
4033617; 359530, 4033452; 359660,
4033336; 359907, 4033395; 359976,
4033482; 360158, 4033587; 360425,
4033579; 360624, 4033550; 360800,
4033478; 361106, 4033313; 361280,
4033175; 361405, 4032904; 361468,
4032769; 361508, 4032613; 361594,
4032521; 361719, 4032251; 361664,
4031919; 361657, 4031698; 361918,
4031512; 362074, 4031507; 362141,
4031505; 362367, 4031609; 362415,
4031740; 362396, 4031852; 362578,
4031957; 362711, 4031931; 362842,
4031860; 362907, 4031814; 363107,
4031785; 363177, 4031894; 363224,
PO 00000
Frm 00069
Fmt 4701
Sfmt 4700
45601
4031959; 363248, 4032025; 363250,
4032092; 363320, 4032178; 363564,
4032148; 363742, 4032143; 363940,
4032092; 364228, 4032039; 364294,
4032015; 364472, 4032009; 364583,
4032005; 364830, 4032064; 364966,
4032127; 365212, 4032186; 365326,
4032249; 365371, 4032269; 365553,
4032397; 365712, 4032503; 365780,
4032523; 365916, 4032607; 366029,
4032671; 366122, 4032779; 366147,
4032889; 366152, 4033022; 366154,
4033088; 366317, 4033327; 366406,
4033325; 366516, 4033277; 366602,
4033185; 366665, 4033072; 366816,
4032912; 366948, 4032864; 367016,
4032884; 367175, 4032990; 367310,
4033030; 367512, 4033090; 367623,
4033087; 367799, 4033015; 367930,
4032944; 367993, 4032809; 367812,
4032726; 367632, 4032665; 367429,
4032582; 367248, 4032477; 367132,
4032325; 366969, 4032108; 366718,
4031916; 366739, 4031871; 366849,
4031823; 366916, 4031844; 367049,
4031839; 367250, 4031833; 367384,
4031851; 367499, 4031958; 367588,
4031978; 367634, 4032021; 367749,
4032128; 367815, 4032126; 367880,
4032057; 367852, 4031859; 367892,
4031724; 367957, 4031678; 368048,
4031741; 368183, 4031782; 368397,
4031508; 368486, 4031506; 368664,
4031500; 368891, 4031626; 368958,
4031646; 369050, 4031732; 369297,
4031791; 369564, 4031783; 369809,
4031797; 370121, 4031810; 370520,
4031753; 370984, 4031649; 371185,
4031643; 371741, 4031626; 372030,
4031617; 372432, 4031648; 372543,
4031667; 372702, 4031751; 372753,
4031949; 372714, 4032150; 372652,
4032285; 372548, 4032533; 372578,
4032776; 372564, 4033021; 372571,
4033264; 372624, 4033507; 372783,
4033635; 372942, 4033719; 373052,
4033671; 373028, 4033628; 373070,
4033537; 373088, 4033404; 373101,
4033115; 373095, 4032937; 373087,
4032671; 373125, 4032470; 373138,
4032159; returning to 373174, 4031891.
(ii) Note: Map of Unit 11 (Laurel
Creek) for Sierra Nevada bighorn sheep
follows:
BILLING CODE 5310–55–P
E:\FR\FM\05AUR2.SGM
05AUR2
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
BILLING CODE 5310–55–C
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
PO 00000
Frm 00070
Fmt 4701
Sfmt 4700
E:\FR\FM\05AUR2.SGM
05AUR2
ER05AU08.011
dwashington3 on PRODPC61 with RULES2
45602
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
dwashington3 on PRODPC61 with RULES2
(17) Unit 12 (Olancha Peak); Inyo and
Tulare Counties, California.
(i) From USGS 1:24,000 scale
quadrangles Cirque Peak, Bartlett,
Templeton Mountain, Olancha, and
Haiwee Pass. Land bounded by the
following UTM zone 11 NAD83
coordinates (E, N): 403133, 4029453;
403358, 4029282; 403619, 4029209;
403945, 4029133; 404369, 4029021;
404658, 4028816; 404816, 4028614;
405104, 4028376; 405331, 4028270;
405620, 4028065; 405682, 4027932;
405805, 4027666; 405734, 4027504;
405863, 4027434; 406060, 4027428;
406290, 4027421; 406385, 4027320;
406479, 4027153; 406544, 4027151;
406674, 4027081; 406738, 4027046;
406835, 4026978; 406993, 4026776;
407086, 4026610; 407116, 4026510;
407176, 4026345; 407206, 4026245;
407201, 4026082; 407131, 4025953;
407161, 4025854; 407158, 4025755;
407190, 4025722; 407251, 4025589;
407282, 4025522; 407279, 4025424;
407210, 4025328; 407206, 4025197;
407203, 4025099; 407234, 4025032;
407263, 4024933; 407291, 4024768;
407287, 4024637; 407250, 4024507;
407178, 4024313; 407042, 4024153;
406975, 4024123; 406909, 4024125;
406811, 4024128; 406841, 4024061;
406903, 4023928; 406933, 4023829;
406963, 4023763; 407057, 4023596;
407118, 4023463; 407282, 4023458;
407411, 4023355; 407439, 4023223;
407499, 4023025; 407524, 4022795;
407487, 4022632; 407350, 4022473;
407214, 4022313; 407044, 4022154;
407010, 4022123; 406941, 4021994;
406870, 4021832; 406765, 4021639;
406663, 4021511; 406627, 4021414;
406622, 4021283; 406686, 4021215;
406682, 4021085; 406739, 4020821;
406701, 4020658; 406634, 4020595;
406565, 4020498; 406562, 4020400;
406557, 4020237; 406553, 4020106;
406515, 4019943; 406508, 4019747;
406537, 4019615; 406434, 4019487;
406336, 4019490; 406301, 4019425;
406296, 4019262; 406194, 4019167;
406127, 4019103; 406121, 4018939;
406086, 4018842; 405983, 4018714;
405817, 4018654; 405649, 4018561;
405584, 4018563; 405583, 4018530;
405611, 4018398; 405572, 4018203;
405538, 4018139; 405435, 4018011;
405400, 4017946; 405332, 4017883;
405395, 4017783; 405428, 4017782;
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
405460, 4017748; 405620, 4017612;
405779, 4017443; 405875, 4017374;
405935, 4017209; 405999, 4017141;
405962, 4017011; 405959, 4016913;
405955, 4016782; 405919, 4016685;
405885, 4016653; 405816, 4016557;
405749, 4016494; 405747, 4016428;
405843, 4016360; 405942, 4016356;
406040, 4016353; 406104, 4016286;
406134, 4016219; 406131, 4016121;
406063, 4016025; 406026, 4015895;
405988, 4015732; 406018, 4015666;
406016, 4015600; 406108, 4015368;
406101, 4015172; 406062, 4014976;
406055, 4014747; 405918, 4014555;
405816, 4014460; 405812, 4014329;
405703, 4014005; 405598, 4013811;
405530, 4013715; 405491, 4013520;
405488, 4013422; 405480, 4013192;
405405, 4012900; 405336, 4012771;
405329, 4012542; 405353, 4012279;
405416, 4012179; 405313, 4012051;
405109, 4011828; 404843, 4011738;
404673, 4011547; 404541, 4011551;
404414, 4011686; 404316, 4011689;
404187, 4011758; 404086, 4011696;
403921, 4011668; 403724, 4011675;
403625, 4011678; 403527, 4011681;
403365, 4011751; 403199, 4011691;
403002, 4011697; 402935, 4011667;
402706, 4011707; 402610, 4011775;
402480, 4011845; 402250, 4011819;
402186, 4011887; 401989, 4011893;
401860, 4011962; 401729, 4011999;
401598, 4012003; 401366, 4011945;
401165, 4011820; 401032, 4011759;
400764, 4011604; 400498, 4011514;
400367, 4011518; 400040, 4011561;
399878, 4011631; 399816, 4011764;
399787, 4011896; 399790, 4011995;
399794, 4012093; 399732, 4012226;
399669, 4012326; 399540, 4012396;
399444, 4012464; 399349, 4012598;
399327, 4012927; 399402, 4013219;
399406, 4013350; 399445, 4013546;
399515, 4013674; 399520, 4013838;
399557, 4013968; 399563, 4014164;
399600, 4014294; 399608, 4014556;
399611, 4014654; 399615, 4014785;
399590, 4015016; 399595, 4015179;
399404, 4015382; 399177, 4015487;
399182, 4015618; 399286, 4015812;
399294, 4016073; 399398, 4016234;
399566, 4016360; 399635, 4016456;
399737, 4016551; 399901, 4016546;
399960, 4016347; 400087, 4016212;
400183, 4016111; 400341, 4015910;
400463, 4015611; 400557, 4015477;
400849, 4015337; 400916, 4015400;
PO 00000
Frm 00071
Fmt 4701
Sfmt 4700
45603
401120, 4015590; 401351, 4015648;
401360, 4015910; 401368, 4016172;
401440, 4016367; 401443, 4016465;
401381, 4016598; 401321, 4016764;
401226, 4016898; 401164, 4016998;
401067, 4017066; 400906, 4017170;
400742, 4017175; 400640, 4017047;
400342, 4016991; 400311, 4017057;
400313, 4017123; 400383, 4017252;
400419, 4017349; 400455, 4017446;
400490, 4017511; 400525, 4017575;
400592, 4017638; 400597, 4017769;
400471, 4017970; 400179, 4018077;
399917, 4018118; 399692, 4018256;
399663, 4018388; 399666, 4018487;
399735, 4018583; 399935, 4018675;
399939, 4018806; 399745, 4018910;
399617, 4019012; 399357, 4019119;
398800, 4019169; 398672, 4019272;
398480, 4019441; 398298, 4019906;
398237, 4020072; 398082, 4020371;
397992, 4020636; 397996, 4020767;
398000, 4020898; 398005, 4021062;
398011, 4021226; 398122, 4021648;
398191, 4021744; 398332, 4022035;
398442, 4022392; 398584, 4022748;
398657, 4022975; 398663, 4023171;
398935, 4023458; 399006, 4023619;
399074, 4023683; 399072, 4023617;
399110, 4023780; 399181, 4023941;
399119, 4024074; 399094, 4024337;
399000, 4024471; 398813, 4024805;
398716, 4024841; 398527, 4025109;
398467, 4025275; 398472, 4025438;
398510, 4025601; 398514, 4025732;
398553, 4025927; 398622, 4026023;
398722, 4026086; 398791, 4026182;
398928, 4026341; 399031, 4026502;
399002, 4026634; 398945, 4026898;
399113, 4027024; 399214, 4027086;
399283, 4027182; 399254, 4027314;
399194, 4027513; 399136, 4027744;
399140, 4027875; 399143, 4027973;
399180, 4028103; 399218, 4028266;
399226, 4028527; 399329, 4028655;
399466, 4028815; 399568, 4028943;
399902, 4029096; 399971, 4029225;
400106, 4029319; 400270, 4029314;
400401, 4029310; 400666, 4029367;
400864, 4029393; 400930, 4029391;
400995, 4029389; 401356, 4029378;
401586, 4029371; 401783, 4029365;
402145, 4029386; 402443, 4029442;
402676, 4029533; 403004, 4029523;
returning to 403133, 4029453.
(ii) Note: Map of Unit 12 (Olancha
Peak) for Sierra Nevada bighorn sheep
follows:
BILLING CODE 5310–55–P
E:\FR\FM\05AUR2.SGM
05AUR2
45604
*
*
*
Dated: July 16, 2008.
David M. Verhey,
Acting Assistant Secretary for Fish and
Wildlife and Parks.
[FR Doc. E8–16813 Filed 8–4–08; 8:45 am]
*
BILLING CODE 4310–55–C
VerDate Aug<31>2005
13:15 Aug 04, 2008
Jkt 214001
PO 00000
Frm 00072
Fmt 4701
Sfmt 4700
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dwashington3 on PRODPC61 with RULES2
*
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules and Regulations
Agencies
[Federal Register Volume 73, Number 151 (Tuesday, August 5, 2008)]
[Rules and Regulations]
[Pages 45534-45604]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-16813]
[[Page 45533]]
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Part II
Department of the Interior
-----------------------------------------------------------------------
Fish and Wildlife Service
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50 CFR Part 17
Endangered and Threatened Wildlife and Plants; Designation of Critical
Habitat for the Sierra Nevada Bighorn Sheep (Ovis canadensis sierrae)
and Taxonomic Revision; Final Rule
Federal Register / Vol. 73, No. 151 / Tuesday, August 5, 2008 / Rules
and Regulations
[[Page 45534]]
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[FWS-R8-ES-2008-0014; 92210-1117-0000-B4]
RIN 1018-AV05
Endangered and Threatened Wildlife and Plants; Designation of
Critical Habitat for the Sierra Nevada Bighorn Sheep (Ovis canadensis
sierrae) and Taxonomic Revision
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service (Service), are
designating critical habitat for the Sierra Nevada bighorn sheep (Ovis
canadensis sierrae) under the Endangered Species Act of 1973, as
amended (Act). In total, approximately 417,577 acres (ac) (168,992
hectares (ha)) fall within the boundaries of the critical habitat
designation. The critical habitat is located in Tuolumne, Mono, Fresno,
Inyo, and Tulare Counties, California. We also are finalizing the
revision of taxonomy of the listed entity from a distinct population
segment (DPS) of California bighorn sheep (Ovis canadensis
californiana) to subspecies, Ovis canadensis sierrae, based on recent
published information.
DATES: This rule becomes effective on September 4, 2008.
ADDRESSES: The final rule, economic analysis, and maps are available at
https://www.regulations.gov and at https://www.fws.gov/nevada. Supporting
documentation we used in the preparation of this final rule is
available for public inspection, by appointment, during normal business
hours, at the Nevada Fish and Wildlife Office, 1340 Financial
Boulevard, Suite 234, Reno, NV 89523; telephone 775-861-6300; facsimile
775-861-6301.
FOR FURTHER INFORMATION CONTACT: Robert D. Williams, U.S. Fish and
Wildlife Service, Nevada Fish and Wildlife Office (see ADDRESSES
section). If you use a telecommunications device for the deaf (TDD),
call the Federal Information Relay Service (FIRS) at 800-877-8339.
SUPPLEMENTARY INFORMATION:
Background
It is our intent to discuss only those topics directly relevant to
the designation of critical habitat in this rule. For more information
on the Sierra Nevada bighorn sheep, refer to the final listing rule
published in the Federal Register on January 3, 2000 (65 FR 20) and the
proposed critical habitat rule published in the Federal Register on
July 25, 2007 (72 FR 40955).
The bighorn sheep (Ovis canadensis) is a large mammal in the family
Bovidae described by Shaw in 1804 (Shackleton 1985, p. 1). Cowan (1940,
pp. 519-569) recognized several subspecies based on geography and skull
measurements. Recent genetic (Ramey 1993, pp. 62-86; 1995, p. 432-434;
Boyce et al. 1996, pp. 423-426, 429; Gutierrez-Espeleta et al. 1998,
pp. 7-9, 11) and morphological data (Wehausen and Ramey 1993, pp. 4-8;
2000, pp. 148-153), and review and reanalysis of Cowan's data (Ramey
1993, p. 83), do not support Cowan's original subspecies
differentiations.
Ramey (1993, pp. 71-72; 1995, p. 432) found, based on mitochondrial
DNA (mtDNA), bighorn sheep from the Sierra Nevada to be more allied
with sheep occupying the adjacent desert area than those to the north.
Ramey (1993, pp. 67-68; 1995, pp. 433, 435) also found Sierra Nevada
bighorn sheep to be a distinctive group in the desert region extending
east to Utah and New Mexico and south to northern Mexico. Ramey (1993
p. 54) used mtDNA as a genetic marker to help understand the
evolutionary history of North American mountain sheep. From the 116
individuals included in the surveys, 16 different mtDNA haplotypes were
identified in North America and four in Asia (Ramey 1993, p. 62). Two
major mtDNA lineages of mountain sheep were indicated in North America
(Ramey 1993, p. 63). Within the northern Alaska and western North
America clade, three mtDNA lineages were identified (Ramey 1993, p.
72). One lineage included bighorn sheep in the desert ranges of the
southwestern United States and Mexico and the Sierra Nevada (Ramey
1993, p. 72), where the Sierra Nevada population was found to be more
closely related to the desert-dwelling sheep than those from the
Cascade Ranges or Rocky Mountains (Ramey 1993, p. 72). Within the
desert-dwelling sheep populations, Sierra Nevada bighorn sheep differed
(Ramey 1993, p. 73). Ramey (1995 p. 429) used mtDNA as a genetic marker
to help understand the evolutionary history of North American mountain
sheep in the southwest United States. Ten mtDNA haplotypes were
identified in the southwest, with a common one being found in most
populations (Ramey 1995, pp. 431-432). The distribution of mtDNA
variants in the southwest did not support the recognition of O. c.
cremnobates, O. c. mexicana, and O. c. nelsoni as distinct and separate
subspecies, but the mtDNA analysis did show a unique fixed haplotype
for O. c. californiana from the Sierra Nevada (Ramey 1995, p. 433).
Based on this finding, bighorn sheep from the Sierra Nevada could be
distinguished from populations of other subspecies of bighorn sheep
(Ramey 1995, p. 433). Results indicated that significant differences in
mtDNA haplotype frequencies can be found among populations that are
adjacent to one another and separated by short distances (Ramey 1995,
p. 435). A few rare haplotypes were limited in distribution and found
in only single populations. One of these populations included the
Sierra Nevada (Ramey 1995, p. 433).
Wehausen and Ramey (2000, pp. 148-153) used univariate and
multivariate statistical methods to examine the geographic variation in
horn and skull characters of 694 bighorn sheep (Ovis canadensis) from
the Great Basin to British Columbia and Alberta. California bighorn
sheep (O. c. californiana) from Washington and British Columbia were
not distinguishable from Rocky Mountain bighorn sheep (O. c.
canadensis); however, they did differ from Sierra Nevada bighorn sheep
populations considered to be O. c. californiana. Extirpated populations
from northeastern California, Oregon, and southwestern Idaho shared a
horn-related character with Nelson bighorn sheep (O. c. nelsoni) from
the Great Basin; this shared character was different from Rocky
Mountain bighorn sheep. Individuals from the Sierra Nevada were
distinguishable from bighorn sheep from the Great Basin. These results
agree with geographic patterns identified with the mtDNA studies of
Ramey (1993, 1995) (Wehausen and Ramey 2000, p. 156). Wehausen and
Ramey (2000, pp. 153-157) synonymized the extinct Audubon subspecies,
O. c. auduboni, from east of the Rocky Mountains in eastern Montana and
Wyoming, North Dakota, South Dakota, and western Nebraska with O. c.
canadensis. They also assigned extinct and extant native populations of
O. c. californiana from Washington and British Columbia to O. c.
canadensis and the extinct native populations of O. c. californiana
from northeastern California, northern Nevada, southwestern Idaho, and
Oregon to O. c. nelsoni of the Great Basin desert form. Based on
genetic and morphometric data, Wehausen and Ramey (2000, p. 156)
concluded that bighorn sheep in the Sierra Nevada should be recognized
as a separate subspecies of O. canadensis, but they
[[Page 45535]]
did not recommend a change in nomenclature at that time.
In a recent investigation of the taxonomy of Sierra Nevada bighorn
sheep, Wehausen et al. (2005) reexamined the history of bighorn sheep
nomenclature. Grinnell (1912, p. 144) recognized bighorn sheep from the
Sierra Nevada of California as a distinct subspecies, Ovis cervina (=
canadensis) sierrae, designating a 5-year-old ram as the type specimen.
Cowan (1940, p. 556) did not recognize the subspecies O. c. sierrae as
valid, but included animals from the Sierra Nevada as O. c.
californiana. Wehausen and Ramey (2000, pp. 153-157) reassigned
specimens from north of the central Sierra Nevada to O. c. nelsoni and
O. c. canadensis. They kept the name O. c. californiana for bighorn
sheep in central and southern Sierra Nevada (Wehausen and Ramey 2000,
p. 156), raising the question of the correct subspecific name for
animals inhabiting this area. Based on this investigation of the
taxonomy of Sierra Nevada bighorn sheep and by the Principle of
Typification (International Commission on Zoological Nomenclature
1999), cited in Wehausen et al. (2005, p. 217), Wehausen et al. (2005
p. 217) concluded, based on Grinnell's original type specimen, that the
correct nomenclature for native sheep in the central and southern
Sierra Nevada of California is Ovis canadensis sierrae (Grinnell).
Therefore, with the publication of this final rule designating critical
habitat for the Sierra Nevada bighorn sheep, we formally revise its
taxonomy from DPS of California bighorn sheep (Ovis canadensis
californiana) to subspecies Ovis canadensis sierrae.
Sierra Nevada bighorn sheep inhabit portions of the Sierra Nevada
located along the eastern boundary of California in Tuolumne, Mono,
Fresno, Inyo, and Tulare Counties. Habitat occurs from the eastern base
of the range as low as 4,790 feet (ft) (1,460 meters (m)) to peaks
above 14,100 ft (4,300 m) (Wehausen 1980, pp. 3, 82).
Based on recent modeling efforts, discussed further in the Criteria
Used To Identify Critical Habitat section, Sierra Nevada bighorn sheep
habitat, as well as areas necessary to provide connectivity between
winter and summer ranges, occur as low as 4,000 ft (1,219 m) in the
southern portion of its range (Johnson et al. 2005). Sierra Nevada
bighorn sheep inhabit open areas where the land is rocky, sparsely
vegetated, and characterized by steep slopes and canyons (Wehausen
1980, p. 81; Sierra Nevada Bighorn Sheep Interagency Advisory Group
1997, p. 5). Wehausen (1980, pp. 18-25) provides a detailed description
of Sierra Nevada bighorn sheep habitat throughout its range. They
prefer open ground to better detect predators and allow enough time to
reach steep, rocky terrain (escape habitat) (Wehausen 1980, p. 81).
Forests and thick brush are usually avoided if possible (65 FR 21;
January 3, 2000). Most of the sheep live at higher elevations (10,000-
14,000 ft (3,050-4,270 m)) in subalpine and alpine areas during the
summer (65 FR 21; January 3, 2000). During winter, these sheep occupy
high-elevation, windswept ridges and tend to prefer south-facing slopes
where snow melts more readily (Jones 1950, pp. 44-45; McCullough and
Schneegas 1966, p. 71; Wehausen 1980, pp. 86-87) or migrate to lower
elevations (4,800 ft (1,460 m)) in sagebrush-steppe areas to avoid deep
snow and to find forage.
Sierra Nevada bighorn sheep are gregarious, with group size and
composition depending on gender and season. Spatial segregation by
gender occurs outside of the mating season. Bighorn sheep ewes
generally remain with the same band in which they were born (Cowan and
Geist 1971, pp. 80-81). Males older than 2 years of age remain apart
from females and younger males for most of the year (Jones 1950, p. 50;
Cowan and Geist 1971, p. 65; Wehausen 1980, p. 109). During the late
fall and winter, the groups come together and concentrate in suitable
winter habitat.
Breeding takes place in late fall, generally November and December
(Jones 1950, pp. 63-64; Cowan and Geist 1971, p. 64; Wishart 1978, p.
165). Lambing occurs between late April and early July (Wehausen 1996,
p. 475) on safe, precipitous, rocky slopes (Wehausen 1980, p. 95); most
lambs in the Sierra Nevada are born in May and June (Wehausen 1980, p.
94; 1996, p. 475). Ewes and lambs often occupy steep terrain that
provides a diversity of exposures and slopes for escape cover (65 FR
21; January 3, 2000). The lifespan for both Sierra Nevada bighorn sheep
males and females has been observed as 8 to 12 years (Wehausen 1980, p.
76; Stephenson 2008, p. 1).
Bighorn sheep are primarily diurnal (Jones 1950, pp. 54-57). They
are primarily grazers; however, they may browse woody vegetation at
times. Plants consumed include various grasses, browse, and forbs,
depending on season and location (Wehausen 1980, pp. 80-93). Naturally
occurring and mineral licks provide necessary minerals for bone and
muscle growth.
While distribution of bighorn sheep is naturally fragmented on the
landscape, the maintenance of migration corridors (space) is important
to allow genetic exchange between Sierra Nevada bighorn sheep herds.
The population ecology of bighorn sheep has been described as a
metapopulation with geographically distinct herds interacting in a
network (Schwartz et al. 1986, p. 184; Bleich et al. 1990, pp. 384-
388). The movements of rams between herds can counteract the effects of
inbreeding that can develop with small, isolated populations (Schwartz
et al. 1986, pp. 182-185).
Previous Federal Actions
On April 20, 1999, we published an emergency rule listing the
Sierra Nevada DPS of the California bighorn sheep as endangered (64 FR
19300), providing emergency protection to the DPS until such time that
we could complete the normal listing process. We also published a
proposed rule to list the DPS as endangered on the same date (64 FR
19333). On January 3, 2000, we published a final rule listing the
Sierra Nevada bighorn sheep as endangered (65 FR 20). The emergency
rule stated that the designation of critical habitat was not
determinable due to lack of information sufficient to perform the
required analysis of impacts of the designation. In the final listing
rule, we stated our revised determination that there is sufficient
information to perform the required impact analysis and that the
designation of critical habitat is prudent.
During the process of designating critical habitat for the Sierra
Nevada bighorn sheep, we noticed that the final listing rule published
in 2000 (65 FR 20) inadvertently listed this entity as a DPS rather
than as a subspecies. While the listing rule addressed the DPS
question, we failed to include the DPS language in the table found in
the regulatory section of the rule. However, as stated above, based on
the work of Wehausen and Ramey (2000, p. 156) and Wehausen et al.
(2005, p. 217), the Sierra Nevada bighorn sheep is recognized as a
subspecies, and the correct nomenclature is Ovis canadensis sierrae.
Therefore, we are formally providing a taxonomic revision herein to
amend the final listing rule to subspecies Ovis canadensis sierrae.
On July 30, 2003, we made available the Service's Draft Recovery
Plan for the Sierra Nevada Bighorn Sheep (Ovis canadensis californiana)
(68 FR 44808). On October 9, 2003, we reopened the comment period for
the draft Recovery Plan (68 FR 58355). On February 13, 2008, we
published a Notice of Availability for the final recovery plan (73 FR
8345).
[[Page 45536]]
On December 8, 2005, the Center for Biological Diversity filed a
complaint based on the Service's failure to designate critical habitat
for this subspecies within the time mandated under the Act (Center for
Biological Diversity v. U.S. Fish and Wildlife Service, et al. Case No.
2:05-CB-02492-DFL-KJM). On June 6, 2006, the Service entered into a
settlement agreement with the Center for Biological Diversity to submit
a proposed critical habitat designation for this subspecies for
publication in the Federal Register by July 17, 2007, and to submit a
final determination on the proposed critical habitat designation for
publication by July 17, 2008.
Our proposed critical habitat rule and taxonomic revision for the
Sierra Nevada bighorn sheep was published in the Federal Register on
July 25, 2007 (72 FR 40956). A notice of availability of the draft
economic analysis (DEA) of the proposed critical habitat designation
was published in the Federal Register on February 5, 2008 (73 FR 6684).
This final rule satisfies the June 6, 2006, settlement agreement with
respect to Sierra Nevada bighorn sheep.
For more information on previous Federal actions concerning Sierra
Nevada bighorn sheep, refer to the final listing rule published in the
Federal Register on January 3, 2000 (65 FR 20).
Summary of Comments and Recommendations
We requested written comments from the public on the proposed
designation of critical habitat for the Sierra Nevada bighorn sheep
published on July 25, 2007 (72 FR 40956). The 60-day comment period for
the proposed rule closed on September 24, 2007. A request for a comment
period extension was received from a private organization on August 20,
2007, and on October 9, 2007, the comment period was reopened until
November 23, 2007 (72 FR 57276). A 30-day comment period was opened on
the DEA and the proposed rule on February 5, 2008, and closed on March
6, 2008 (73 FR 6684). Comments and new information received in response
to the proposed rule and the DEA were incorporated in the final rule as
appropriate and summarized below.
During the comment periods for the proposed rule, we received a
total of 28,181 (28,153 in support, 12 opposed, and 16 neutral)
comments from Federal, State, and local governments, non-governmental
organizations and private individuals. We received two requests for
public hearings. The Inyo County Board of Supervisors made a request
for a public hearing on August 7, 2007, as did two private individuals
on August 29, 2007. A public hearing was held in Bishop, California, on
October 25, 2007 (72 FR 57276). We received 12 oral testimonies from 12
individuals. Of these commenters, three who provided oral comments also
submitted duplicative written comments. A request was made for a public
workshop by the Mono County Board of Supervisors on September 5, 2007.
We held two public meetings in Bridgeport and Bishop, California, on
October 24 and 25, 2007, respectively (72 FR 57276).
Peer Review
In accordance with our policy published July 1, 1994 (59 FR 34270),
we solicited expert opinions from three knowledgeable individuals with
scientific expertise that included familiarity with the species and
conservation biology principles. We received responses from two peer
reviewers. In general, the peer reviewers concurred with our methods
and conclusions and provided suggestions to improve the final critical
habitat rule.
We reviewed all comments received from the peer reviewers and the
public for substantive issues and new information regarding critical
habitat for the Sierra Nevada bighorn sheep, addressed them in the
following summary, and incorporated them into the final rule as
appropriate.
Peer Reviewer Comments
(1) Comment: Both peer reviewers raised concern that the proposed
designation did not adequately protect Sierra Nevada bighorn sheep from
the possible introduction of disease from domestic sheep and goats. One
suggested that the ``absence of risk of disease transmission'' should
be explicitly included as a primary constituent element (PCE) as
pneumonia caused by contact with domestic sheep or goats can be an
overriding factor affecting habitat suitability.
Our Response: Conservation of the Sierra Nevada bighorn sheep
depends on addressing both habitat and non-habitat related threats. In
terms of the consultation process under section 7(a)(2) of the Act, the
Service is required to analyze both the threats to the individuals
within a population and the threats to the PCEs of its designated
critical habitat. Under the Special Management Considerations or
Protection section, we have indicated that management of domestic
livestock grazing practices that result in overgrazing or forage
competition between these domestic species and Sierra Nevada bighorn
sheep can be a threat. The concern for overgrazing or competition is a
habitat-related threat associated with the PCEs (i.e., PCE 2). The
potential for contact and the possible transmission of disease to
bighorn sheep exists when domestic sheep or goats are present in
critical habitat. Management of the threat of disease transmission
between domestic sheep and goats and Sierra Nevada bighorn sheep is
needed to conserve this species; however, this threat is not strictly a
habitat-related threat. The potential effects of disease transmission
will be addressed through section 7 consultation with Federal agencies
under the jeopardy standard and through the section 9 prohibitions of
the Act to the extent applicable. There would be no benefit gained from
a critical habitat designation with respect to the effects of disease
on individual Sierra Nevada bighorn sheep because the regulatory
effects of critical habitat designations apply to adverse modification
or destruction of habitat, not to effects that result in the mortality
of individual Sierra Nevada bighorn sheep. Because the disease threat
faced by the species is not habitat-based, there would be no practical
benefit to including it as a PCE.
(2) Comment: One peer reviewer suggested that buffer zones be
established around designated critical habitat for management of
domestic sheep and goats because activities that could pose a risk of
disease transmission do not need to occur directly within critical
habitat to affect that habitat.
Our Response: The units designated as critical habitat for the
Sierra Nevada bighorn sheep contain the features essential for the
conservation of this subspecies. It is not our practice to establish
buffers around an area designated as critical habitat. As indicated
under the Special Management Considerations or Protection section,
domestic sheep and goat grazing may require management modifications to
protect Sierra Nevada bighorn sheep in critical habitat in certain
units. Any buffer distance recommended or suggested in a Federally
proposed action involving domestic sheep or goat grazing adjacent to a
designated critical habitat unit to reduce the potential threat of
disease transmission to Sierra Nevada bighorn sheep would be taken into
consideration during the jeopardy analysis of the consultation process
under section 7 of the Act.
(3) Comment: One peer reviewer raised concern for an elevated risk
of disease transmission with domestic sheep grazing on U.S. Forest
Service
[[Page 45537]]
(USFS) lands as Sierra Nevada bighorn sheep wander between units.
Our Response: We are aware of the potential risk of disease
transmission due to contact between domestic sheep (and goats) and
Sierra Nevada bighorn sheep. If a disease outbreak were to occur in a
Sierra Nevada bighorn sheep population, it could be passed to other
populations (units) because of, most likely, ram forays. This risk will
increase if Sierra Nevada bighorn sheep numbers increase as expected
due to continuing recovery actions. While we believe that this is an
issue of management concern, we do not believe that this critical
habitat designation necessarily affects the issue in any significant
way. Please also see our response to comment (1).
(4) Comment: Both peer reviewers raised concern that the proposed
critical habitat designation did not provide biologically based
corridors or linkage zones for movements among Sierra Nevada bighorn
sheep subpopulations. They were unclear how genetic exchange or
colonization would be allowed with unconnected units of critical
habitat.
Our Response: Connectivity, within a critical habitat unit, is a
PCE for the Sierra Nevada bighorn sheep (i.e., PCE 1). The current
critical habitat configuration provides for long-term connectivity
between groups within a particular unit. We recognize the importance of
migration between critical habitat units, as discussed under
Metapopulaton Structure in the Space for Individual and Population
Growth and for Normal Behavior section. However, due to the current
isolation of occupied herd units and extremely limited knowledge of
various migration paths that Sierra Nevada bighorn sheep, especially
rams, may have taken historically between units, we did not develop
criteria that would capture migration corridors between units.
(5) Comment: One peer reviewer was concerned about the fine-scale
mapping resulting in ``finger-like'' habitats for Units 1, 2, 3, 4, and
9. The concern was related to possible difficulties in managing such
areas. The reviewer suggested the boundaries be redrawn to reduce
sinuosity, possibly along watershed and or drainage boundaries.
Our Response: The critical habitat units have been developed to be
consistent with the herd units that the Sierra Nevada bighorn recovery
plan identifies as essential for recovery of the subspecies. Those herd
units were originally developed using expert opinion and information on
current and historical bighorn sheep locations in the Sierra Nevada.
Those units were later refined using a habitat selection model
developed by University of California Davis and the California
Department of Fish and Game (CDFG) (Johnson et al. 2005). Based on our
analysis of the biological needs of the subspecies, we believe that the
herd units developed for the recovery plan capture those areas that
contain the physical and biological features arranged in the
appropriate quantity and spatial arrangement for the conservation of
the subspecies.
It is important to remember that these critical habitat units are
not being established as Sierra Nevada bighorn sheep preserves or
management zones. These are regulatory designations of areas that
contain the features essential to the conservation of the subspecies.
Critical habitat would serve its regulatory role when analyzing a
particular Federal action in the consultation process under section
7(a)(2) of the Act to determine if that action would adversely modify
or destroy critical habitat by impacting the essential features within
that unit to such a degree that the unit no longer serves its function
for conservation.
It is possible that a Federal action immediately adjacent to these
units (e.g., between ``fingers'') could indirectly adversely modify
critical habitat within the units. In such a situation, the action
would be analyzed through the consultation process under section
7(a)(2) of the Act against the adverse modification standard. However,
because our analysis has not identified essential features in these
locations, unit boundary modification and designation of critical
habitat therein would not be appropriate.
(6) Comment: One peer reviewer commented that the indicated 9 to 11
year lifespan for bighorn sheep seemed short.
Our Response: We have modified the Background section of the final
rule to more accurately reflect the observed lifespan for male and
female bighorn sheep in the Sierra Nevada.
Comments From State Agencies
(7) Comment: California Department of Fish and Game (CDFG)
suggested a PCE that identifies a ``disease-free zone'' because of the
risk to Sierra Nevada bighorn sheep in proximity to domestic sheep.
Our Response: Please see our response to Comment 1.
(8) Comment: CDFG recommended establishment of a buffer that
excludes domestic sheep to ensure the integrity of the critical habitat
for Sierra Nevada bighorn sheep and provide additional protections.
Our Response: Please see our response to Comment 2.
(9) Comment: CDFG recommended more emphasis be placed on the use of
fire to maintain critical habitat because fire is an integral part of
the landscape.
Our Response: The Special Management Considerations or Protection
section identifies activities of Federal agencies or those with a
federal nexus that may impact Sierra Nevada bighorn sheep and their
habitat. The section is not meant to promote or discourage any
particular activity. We indicated that it may be necessary in some of
the critical habitat units to reduce forest cover to make habitat more
suitable for Sierra Nevada bighorn sheep. Prescribed fire can be used
as a tool to do this. Johnson et al. (2005, p. 34) indicate Sierra
Nevada bighorn sheep could gain additional habitat with a reduction in
forest cover. In addition, the final recovery plan (Appendix H, Genetic
Management of Sierra Nevada Bighorn Sheep) provides a specific
recommendation to use fire in addition to other methods to enhance
habitat within herd units (Service 2007, p. 174). This would improve
unit carrying capacity, as well as connectivity with adjacent herd
units, providing better opportunities for genetic exchange between
herds.
(10) Comment: California Department of Food & Agriculture (CDFA)
commented that there is ``still incomplete agreement in the scientific
community'' about disease transmission from domestic sheep to bighorn
sheep, in general, such as how often it occurs and its role in disease
epizootics in bighorn sheep. The CDFA agrees that a reasonable approach
is to keep the two species separated. How such separation occurs and
what measures are used to prevent possible contact are important to
both the survival of Sierra Nevada bighorn sheep and the domestic sheep
industry in Inyo and Mono Counties, California. The CDFA commented that
further scientific findings will improve understanding of the true
nature of respiratory disease in bighorn sheep, in general, and that
interested parties should cooperate on common interests. They also
noted that at the 111th Annual Meeting of the United States Animal
Health Association (USAHA) in October 2007, a joint resolution passed
recommending additional research and formation of a subcommittee. The
College of Agriculture, Biotechnology and Natural Resources at the
University of Nevada Reno (UNR) similarly mentions the USAHA
resolution.
Our Response: We are aware that disagreement continues regarding
the potential for disease transmission to
[[Page 45538]]
occur between domestic livestock, especially sheep and goats, and
bighorn sheep, in general, under range conditions. We have reviewed
Resolution No. 15 that reads, ``The United States Animal Health
Association (USAHA) urges the United States Secretary of Agriculture
and the United States Secretary of the Interior to seek resources
through the President's budget to fund research to better elucidate the
epidemiology and pathogenesis of bighorn/domestic sheep disease
interactions so informed and effective management decisions can be
made.'' We, along with others, continue to seek answers to questions
related to this disease transmission issue. We support continuing
research efforts to address uncertainties and to assist in the
decision-making process.
(11) Comment: The CDFA recommends consideration of the Western
Association of Fish and Wildlife Agencies' (WAFWA) document,
``Recommendations for Domestic Sheep and Goat Management in Wild Sheep
Habitat'', dated June 21, 2007, and the University of California--
Davis' ``Quantifying the Risk of Disease Transmission from Domestic
Sheep to Bighorn Sheep in the Sierra Nevada'' in future determinations
of effectively preventing the possibility of disease transmission
between domestic sheep and Sierra Nevada bighorn sheep, in addition to
working with livestock industry representatives.
Our Response: We are aware of these documents and consider
information contained within them during section 7 consultations, as
appropriate. Other documents also support the effective separation of
domestic sheep from bighorn sheep, in general, as a management tool to
reduce the risk of contact and possible disease transmission (Wyoming
State-wide Bighorn/Domestic Sheep Working Group 2004, pp. 7, 11; U.S.
Forest Service 2006, pp. 18-19). Also, an expert science panel (U.S.
Geological Survey and Bureau of Reclamation 2006) was convened in 2006
to discuss a risk analysis of disease transmission between domestic and
bighorn sheep on the Payette National Forest in Idaho. The panel
focused on science-based concerns raised by the risk analysis document,
specifically the disease/mortality category, and developed six
statements. References to concerns about domestic sheep also apply to
domestic goats. Three of these key statements follow: ``(1a) Scientific
observation and field studies demonstrate that ``contact'' between
domestic sheep and bighorn sheep is possible under range conditions.
This contact increases risk of subsequent bighorn sheep mortality and
reduced recruitment, primarily due to respiratory disease; (1b) The
complete range of mechanisms/causal agents that lead to epizootic
disease events cannot be conclusively proven at this point; and (1c)
Given the previous two statements, it is prudent to undertake
management to prevent contact between these species'' (U.S. Geological
Survey and Bureau of Reclamation 2006, p. 1). One panelist dissented
and preferred ``can increase risk'' in statement 1a because it did not
imply that any contact will result in disease transmission (U.S.
Geological Survey and Bureau of Reclamation 2006, p. 1).
(12) Comment: The California Department of Transportation
(CalTrans) states that roads are inconsistently addressed and that it
is inappropriate to include state highway right-of-ways (ROWs) and
facilities within critical habitat. It is recommended by CalTrans that
State Route (SR) 120 in Unit 1 and SR 158 in Unit 2 be excluded from
critical habitat.
Our Response: When determining critical habitat boundaries for
Sierra Nevada bighorn sheep, we made every effort to avoid including
developed areas such as lands covered by buildings, paved areas, and
other structures that lack PCEs for the Sierra Nevada bighorn sheep.
The scale of the maps prepared under the parameters for publication
within the Code of Federal Regulations may not reflect the exclusion of
such developed areas. Any such features and the land under them
inadvertently left inside critical habitat boundaries shown on the maps
of this final rule have been excluded by text in the final rule and are
not designated as critical habitat. Therefore, Federal actions limited
to these areas would not trigger section 7 consultation, unless they
may affect the species or PCEs in adjacent critical habitat.
We have determined, however, that the unpaved road right-of-ways of
SR 120 from Unit 1 and SR 158 from Unit 2 do contain the features
essential to the conservation of the Sierra Nevada bighorn sheep, and
therefore meet the definition of critical habitat. CalTrans did not
provide, nor are we aware of any additional information of the benefits
of excluding ROWs based on ongoing or planned management of these ROWs,
or how any on-going or planned management of the ROWs would benefit the
conservation of the Sierra Nevada bighorn sheep or the sheep itself.
The Secretary may exclude an area from critical habitat under
section 4(b)(2) of the Act after taking into consideration the economic
impact, the impact on national security, and any other relevant impact
if he determines that the benefits of such exclusion outweigh the
benefits of designating such area as critical habitat, unless he
determines that the exclusion would result in the extinction of the
species concerned.
Because we are not aware of any information describing the benefits
of excluding ROWs based on ongoing or planned management of these ROWs,
or how any existing or planned management provides the same or better
level of protection from adverse modification or destruction than that
provided through a consultation under section 7 of the Act, we have
determined that exclusion of these lands from the final designation of
critical habitat pursuant to section 4(b)(2) of the Act is not
appropriate at this time.
(13) Comment: CalTrans states that no bighorn sheep collisions with
vehicles are listed in their accident database. This is contrary to a
statement made in our proposed rule that a bighorn sheep collision with
a vehicle had occurred in the past.
Our Response: A CDFG employee was made aware of the collision we
referenced in the proposed rule (72 FR 40956) through a third party.
The employee contacted the motorist to obtain information about the
November 2003 collision. The Sierra Nevada bighorn sheep ram was
monitored after the collision by CDFG, and it subsequently died in
January 2004. No formal report was made by CDFG to CalTrans (Stephenson
2008, p. 1).
(14) Comment: CalTrans indicates references to SR 190 should be
corrected as SR 190 does not occur in or adjacent to critical habitat.
Our Response: We erroneously indicated SR 190 occurred in or
adjacent to Unit 10 in the Proposed Critical Habitat Designation and
the Special Management Considerations or Protection sections. The road
should have been indicated as Forest Route 16S02. This has been
corrected in both sections.
(15) Comment: CalTrans states that, although an alignment has not
been selected for the proposed Olancha/Cartago U.S. 395 project, an
alternative might occur on the west side of Los Angeles aqueduct.
Our Response: We appreciate this information. If the location for
this new road construction occurs within designated critical habitat or
may impact the Sierra Nevada bighorn sheep or its designated critical
habitat, consultation under section 7 of the Act will occur as
appropriate.
[[Page 45539]]
(16) Comment: The Nevada Department of Agriculture (NDOA) stated
that the disease transmission risk assessment model by Clifford et al.
(2007) is ``questionable'' as a tool for management and is a problem
when serving as the basis of a critical habitat designation. The
College of Agriculture, Biotechnology and Natural Resources at the
University of Nevada Reno (UNR) similarly recommends that the disease
risk assessment by Clifford et al. (2007) should not be used as the
basis for designating Sierra Nevada bighorn sheep critical habitat.
Our Response: We agree. Critical habitat as defined in section 3 of
the Act is; the specific areas within the geographical area occupied by
a species at the time it is listed in accordance with the Act, on which
are found those physical or biological features essential to the
conservation of the species and which may require special management
considerations or protection; and specific areas outside the
geographical area occupied by a species at the time it is listed, upon
a determination that such areas are essential for the conservation of
the species. Designation of critical habitat is not based on a single
management issue and, in this case, the concern for transmission of
diseases from the grazing of domestic sheep or goats in proximity to
Sierra Nevada bighorn sheep did not serve as the foundation for this
critical habitat designation. Domestic sheep grazing is a management
issue that is properly addressed through the consultation process under
section 7(a)(2) of the Act.
(17) Comment: The NDOA recommended that the critical habitat
designation be suspended until the scientific basis has been
established for disease transmission between domestic sheep and Sierra
Nevada bighorn sheep.
Our Response: We are designating critical habitat for Sierra Nevada
bighorn sheep in accordance with the deadlines established by a court-
approved settlement agreement. We agreed to submit to the Federal
Register a final determination of critical habitat for Sierra Nevada
bighorn sheep by July 17, 2008. We based our designation of critical
habitat on the best scientific and commercial data available as
required by Section 4 of the Act. Further, our Policy on Information
Standards Under the Endangered Species Act (published in the Federal
Register on July 1, 1994 (59 FR 34271)), the Information Quality Act
(section 515 of the Treasury and General Government Appropriations Act
for Fiscal Year 2001 (Pub. L. 106-554; H.R. 5658)), and our associated
Information Quality Guidelines provide criteria, establish procedures,
and provide guidance to ensure that our decisions are based on the best
scientific data available. We used published scientific literature and
the expertise of Recovery Team members (including scientists from a
variety of federal and state agencies, and other publics). We also
solicited peer review from individuals familiar with bighorn sheep, in
general, and related issues. We solicited new biological data, invited
public participation during multiple comment periods, conducted a
public hearing, and held informational meetings on the proposed rule.
We have considered peer review, agency, and public comments received
during the preparation of this final rule. Accordingly, we have used
the best scientific and commercial information available in this
designation. Designation of critical habitat is not based on a single
management issue and, in this case, the concern for transmission of
diseases from the grazing of domestic sheep or goats in proximity to
Sierra Nevada bighorn sheep did not serve as the foundation for this
critical habitat designation.
(18) Comment: The NDOA stated that uncertainties in general about
bighorn sheep epizootics exist per the USAHA meeting in October 2007.
Our Response: Please see our response to Comment 10.
(19) Comment: The NDOA stated that the occurrence of bighorn sheep
disease and die-offs can be associated with bighorn sheep reaching peak
numbers (Monello et al. 2001). Stagnant bighorn sheep population
numbers have occurred in association with predation by wolves and
mountain lions. These factors affect bighorn sheep populations
``permanently,'' not just ``temporarily'' like domestic sheep grazing.
Our Response: Bighorn sheep mortalities can be attributed to
various factors as discussed below in the ``Mortality Factors'' section
of this rule. These mortality factors may or may not affect bighorn
sheep populations ``permanently,'' depending on numerous variables.
Die-offs from diseases possibly transmitted from domestic sheep can
have long-lasting effects by influencing subsequent population
recruitment. Lambs born to surviving ewes can experience low survival
rates for 3 to 5 years after the initial outbreak (Foreyt 1990, p. 100;
Coggins and Matthews 1992; Ward et al. 1992; Foreyt 1995; Hunter 1995a,
as cited in Schommer and Woolever 2001, p. 3). We have added a short
discussion in the Physical and Biological Features section related to
these long-lasting impacts of pneumonia in bighorn sheep populations.
(20) Comment: The NDOA and UNR stated that climate and geographical
factors play a role in the recovery of a species and that the
``northern recovery unit'' is neither suitable nor essential habitat in
terms of winter range for the Sierra Nevada bighorn sheep due to its
higher elevation and greater snow depths than more southern units.
Our Response: As indicated in the Criteria Used to Identify
Critical Habitat section, we used the following criteria to select
areas occupied by the Sierra Nevada bighorn sheep at the time of
listing for inclusion in critical habitat:
(a) Those areas occupied by the Sierra Nevada bighorn sheep at the
time of listing (1999-2000) as indicated in the final listing rule (65
FR 20; January 3, 2000). In the final listing rule, we identified five
subpopulations of Sierra Nevada bighorn sheep that existed: (1) Lee
Vining Canyon (Mount Warren and Mount Gibbs Herd Units), (2) Wheeler
Crest (Wheeler Ridge Herd Unit), (3) Mount Baxter (Sawmill Canyon and
Mount Baxter Herd Units), (4) Mount Williamson (Mount Williamson Herd
Unit), and (5) Mount Langley (Mount Langley Herd Unit) in Mono and Inyo
counties, California (Wehausen 1999, pp. 1-7; 2000, pp. 1-6);
(b) Areas that are representative of the distribution of the Sierra
Nevada bighorn sheep throughout the geographical range occupied at the
time of listing with the goal of maintaining the subspecies' range of
habitat and genetic variability; and
(c) Areas that allow for the continued existence of viable
subpopulations under varying environmental conditions and that can
serve as locations for source populations. The locations of all five
subpopulations identified in the original listing rule continue to
remain occupied today.
We have determined that the areas occupied at the time of listing
continue to be occupied, contain features essential to the conservation
of the subspecies (possess one or more PCEs such that the area supports
one or more of the Sierra Nevada bighorn sheep's life processes) that
may require special management, and provide sufficient habitat to
protect these populations. Units 1 (Mount Warren) and 2 (Mount Gibbs)
of the northern recovery unit meet these criteria.
More specifically, essential habitat is available for Sierra Nevada
bighorn sheep in Units 1 (Mount Warren) and 2 (Mount Gibbs). This is
not only based on historical data indicating their presence as far
north as Sonora Pass (Grinnell and Storer 1924, as cited in Service
2007, p. 14), but also on the fact that these units also currently
support
[[Page 45540]]
Sierra Nevada bighorn sheep herds. Mount Warren has a population of
approximately 26 individuals, and Mount Gibbs has a population of
approximately 8 individuals (Wehausen and Stephenson 2006, p. 7). The
Mount Gibbs herd spends almost the entire year at elevations above
11,000 ft (3,353 m). In 2007, all ewes gave birth, and their lambs are
known to have survived through at least September. This herd continues
to survive and reproduce, expanding in numbers, although this alpine
environment is no doubt harsher than lower-elevation areas. It is
expected this herd will outgrow its carrying capacity of the alpine
winter ranges and begin using lower-elevation winter ranges in the
future (California Department of Fish and Game 2007, p. 2). Surveys
(ground and aerial observations) of the Mount Warren herd conducted
during the period from 2003 to 2007 indicate individuals are using this
unit during every month of the year (California Department of Fish and
Game files--monthly reports, Service files). In addition, a Resource
Selection Probability Functions model was developed for summer and
winter habitat and indicates an estimated 20.2 square kilometers (sq
km) (7.8 square miles (sq mi)) and 9.4 sq km (3.6 sq mi), respectively,
are available for Sierra Nevada bighorn sheep in the Mount Gibbs and
Mount Warren units (Johnson et al. 2005, p. 31). As discussed under the
Primary Constituent Elements for Sierra Nevada Bighorn Sheep section of
this rule, not all life history functions require all the PCEs,
therefore, not all areas designated as critical habitat contain all of
the PCEs. Units are designated based on sufficient PCEs being present
to support one or more of the subspecies' life history requirements.
This applies to both the occupied and unoccupied units designated.
(21) Comment: The NDOA and UNR noted that a memorandum to the
Director of the Service from the U.S. Department of the Interior's
Assistant Secretary for Fish and Wildlife and Parks, dated April 28,
2004, stated that critical habitat adds little additional conservation
benefit to a listed species and designations must not be based on
speculation or determinations that lack supporting data. Therefore, the
designation of critical habitat is of ``dubious value'' as identified
by your own agency.
Our Response: Section 4(A)(3) of the Act requires that the Service
identify those lands on which are found the physical or biological
features essential to the conservation of the species that may require
special management considerations or protection, and those areas
outside the geographical area occupied by the species at the time of
listing that are essential to the conservation of the species. In
identifying those lands, the Service must consider the recovery needs
of the species, such that, on the basis of the best scientific and
commercial data available at the time of designation, the habitat that
is identified, if managed, could provide for the survival and recovery
of the species.
The identification of those areas that are essential for the
conservation of the species and that can, if managed, provide for the
recovery of a species is beneficial. The process of proposing and
finalizing a critical habitat rule provides the Service with the
opportunity to determine the physical and biological features essential
to the conservation of the species within the geographical area
occupied by the species at the time of listing, as well as to determine
other areas essential for the conservation of the species. The
designation process includes peer review and public comment on the
identified physical and biological features and essential areas. This
process is valuable to land owners and managers in developing
conservation management plans for identified areas, as well as any
other occupied habitat or suitable habitat that may not have been
included in the Service's determination of essential habitat.
The consultation provisions under section 7(a) of the Act
constitute the regulatory benefits of critical habitat. As discussed
above, Federal agencies must consult with us on discretionary actions
that may affect critical habitat and must avoid the destruction or
adverse modification of critical habitat. Federal agencies must also
consult with us on discretionary actions that may affect a listed
species and refrain from undertaking actions that are likely to
jeopardize the continued existence of such species. The analysis of
effects to critical habitat is a separate and different analysis from
that of the effects to the species. Therefore, the difference in
outcomes of these two analyses represents the regulatory benefit of
critical habitat. For some species, and in some locations, the outcome
of these analyses will be similar, because effects on habitat will
often result in effects on the species. However, the regulatory
standard is different: The jeopardy analysis looks at the action's
impact on survival and recovery of the species, while the adverse
modification analysis looks at the action's effects on the designated
habitat's contribution to the species' conservation. This may, in many
instances, lead to different results and different regulatory
requirements. Thus, critical habitat designations may provide greater
regulatory benefits to the recovery of a species than would listing
alone.
Another benefit of including lands in critical habitat is that
designation of critical habitat serves to educate landowners, State and
local governments, and the public regarding the potential conservation
value of an area. In general, critical habitat designation always has
educational benefits; however, in some cases, they may be redundant
with other educational effects.
(22) Comment: The NDOA states that listing of Sierra Nevada bighorn
sheep as an endangered species, subspecies, or even distinct
metapopulation lacks scientific merit.
Our Response: Please refer to our final rule listing the Sierra
Nevada bighorn sheep published on January 3, 2000 (65 FR 20), which
outlines our rationale for listing.
(23) Comment: The UNR stated designating critical habitat for
Sierra Nevada bighorn sheep will lead to grazing allotment closures.
Our Response: The designation of critical habitat for Sierra Nevada
bighorn sheep does not automatically lead to closing allotments. For
those areas on Federal lands, consultation under section 7 of the Act
may be required to examine the effects of grazing on critical habitat.
Specific actions by the managing Federal agency could include the
elimination of, or restrictions on, livestock grazing in areas that
overlap with critical habitat. Please also see our responses to
Comments 24, 40, 41, and 42.
(24) Comment: UNR states that short-term, high intensity grazing by
domestic sheep helps maintain forage production and fuel load
accumulation. The regrowth of vegetation is more palatable and
nutritious for Sierra Nevada bighorn sheep during the growing season as
well as during winter. The removal of domestic sheep will lead to
poorer forage production and an accumulation of fuels.
Our Response: Regardless of any effects of grazing on fuel loads
and forage quantity and quality, domestic sheep in some locations may
pose a disease risk to Sierra Nevada bighorn sheep. The Service will
recommend the removal of domestic sheep from allotments where contact
with Sierra Nevada bighorn sheep cannot be prevented through section 7
of the Act. The Service has proposed actions in the recovery plan for
Sierra Nevada bighorn sheep to maintain and enhance the
[[Page 45541]]
integrity of habitat through the careful use of fire and other habitat
manipulations that do not involve domestic sheep grazing. These actions
would include maintenance and enhancement of habitat in areas where
domestic sheep may be removed to prevent contact with Sierra Nevada
bighorn sheep.
Comments From Other Federal Agencies
(25) Comment: Yosemite National Park raised a concern about any
reduction in the proposed critical habitat and protection of the Sierra
Nevada bighorn sheep in the ``northern recovery units'' which would
constitute the ``Yosemite herd.'' Sierra Nevada bighorn sheep in the
northern areas are the ones most likely to reoccupy habitat in
Yosemite, filling an ecological void and offering park visitors the
opportunity to observe these animals.
Our Response: We have not reduced the area of designated critical
habitat for the two units (Mount Warren and Mount Gibbs) that occur
within the northern recovery unit because they meet our criteria for
identifying critical habitat. These units contain the features
essential to the conservation of the Sierra Nevada bighorn sheep and
require special management. We also did not identify any areas within
these units where the benefits of exclusion outweighed the benefits of
inclusion. Please also see our response to Comment 20.
(26) Comment: Yosemite National Park supports the proposed critical
habitat designation and taxonomic revision but recommends expanding
critical habitat to cover all areas currently occupied by Sierra Nevada
bighorn sheep, accommodate further range expansion, and provide buffers
between domestic sheep and Sierra Nevada bighorn sheep to prevent
disease transmission.
Our Response: As indicated in our response to Comment 2, it is not
our practice to establish buffers around an area designated as critical
habitat. A buffer distance indicated in a Federally proposed action
involving domestic sheep or goat grazing near designated critical
habitat would be considered during the consultation process under
section 7 of the Act. As indicated in our response to Comment 36,
critical habitat should not include the entire area that can be
occupied by the species. We based our designation on the Recovery
Team's delineation of essential habitat and as indicated in our final
approved recovery plan (Service 2007, p. 41). For a more thorough
discussion of these topics, please see our responses to Comments 2 and
36.
(27) Comment: Sequoia and Kings Canyon National Parks indicated
their commitment to preserving and restoring natural ecosystems. They
view Sierra Nevada bighorn sheep as an essential component that has
been lost from much of its historical range within the Parks. By policy
and law there is a commitment to working with the Service and other
agencies to help restore the Sierra Nevada bighorn sheep to their
former range and abundance. Sequoia and Kings Canyon National Parks
fully support the proposed critical habitat designation.
Our Response: We appreciate the support and look forward to
continuing to work with the National Park Service and others to
conserve the Sierra Nevada bighorn sheep.
(28) Comment: The USFS suggested that designating critical habitat
does not provide any additional benefit to a species and that it
unnecessarily adds to USFS workload and may lead to re-initiation of
section 7 consultation for critical habitat where a consultation has
already been completed.
Our Response: Designating critical habitat identifies those areas
that contain the features that are essential to the conservation of a
particular species, thus signaling to Federal agencies to consider the
species' conservation in the design and implementation of their
management actions. The designation provides guidance on why these
areas need special management considerations or protection and
indicates activities that are likely to adversely modify or destroy
critical habitat. The designation of critical habitat assists the
recovery process by providing information on how actions might impact
the species' habitat. Including USFS lands as critical habitat is
significant because this will assist in maintaining the Service's role
in reviewing potential future impacts to areas that are important for
the conservation of Sierra Nevada bighorn sheep populations. Lands
administered by the USFS contain a substantial portion of habitat that
is essential for the conservation of Sierra Nevada bighorn sheep.
Designation of critical habitat may also provide protection for
unoccupied habitat that may not otherwise undergo the section 7
consultation process due to species' absence. Considering whether
proposed future projects will result in the destruction or adverse
modification of critical habitat in addition to the jeopardy analysis
will require some additional analysis during the section 7 consultation
process.
(29) Comment: The USFS indicated the 2001 Record of Decision for
the Ansel Adams, John Muir, and Dinky Lakes Wilderness Plans considered
various impacts on Sierra Nevada bighorn sheep and their habitats.
Our Response: We appreciate this information and have reviewed this
document. Only one item was found directly related to management of the
Sierra Nevada bighorn sheep. This addressed the closure of Sierra
Nevada bighorn sheep habitat to dogs. As indicated in the Special
Management Considerations or Protection section, dogs (with their
associated recreation activities) are a potential threat to Sierra
Nevada bighorn sheep critical habitat. At issue are the effects of
Wilderness Plans, associated Forest Land and Resource Management Plans,
and ongoing activities on USFS lands on federally listed species,
including the Sierra Nevada bighorn sheep. The goal of these plans is
to describe a strategic direction for the management of the wilderness
areas over a long period of time (15-20 years). The plans do not make
any decisions regarding USFS site-specific project proposals for
implementing the land management plans nor do they require managers to
implement any specific conservation activities.
(30) Comment: The USFS stated that management direction was
established to restrict dogs in Sierra Nevada bighorn sheep habitat
located in the Mt. Baxter and Mt. Williamson California Bighorn Sheep
Zoological Areas on the Inyo National Forest.
Our Response: Please see our response to Comment 29. These
statements also apply to FS Order No. 04-81-3 which established these
zoological areas in 1981.
(31) Comment: The USFS commented that the proposed critical habitat
designation does not establish migration corridors between the units
though migration is identified as important. While paths that rams may
take between units or groups may be unpredictable, the final
designation would be strengthened if it were to identify dispersal and
movement corridors that are integral to the habitat elements.
Our Response: Please see our response to Comment 4.
(32) Comment: The USFS requests clarification on why disease
transmission from domestic livestock grazing is included as a
stochastic event.
Our Response: This has been corrected. We have removed those
references specifically identifying the risk of disease transmission
from domestic livestock from (3) of the Criteria Used To Identify
Critical
[[Page 45542]]
Habitat section. The remaining reference addresses various diseases of
North American wild sheep.
(33) Comment: The USFS suggested that the proposal is not as clear
as it should be regarding the effects of disease transmission on Sierra
Nevada bighorn sheep populations. Incorporating disease-associated
risks into a PCE would strengthen the proposal.
Our Response: We have added some additional information in the
biological background of the Primary Constituent Elements section of
this rule. Please also see our response to Comment 1.
(34) Comment: The USFS stated that while it is important to
decrease the degree of habitat fragmentation in the Sierra Nevada, the
designation of critical habitat does not actually do that.
Our Response: Designation of critical habitat offers protection
from various impacts which may be proposed on the landscape. We believe
designating critical habitat in 12 units ranging from 22,037 ac (8,918
ha) to 80,966 ac (32,766 ha) does reduce potential habitat
fragmentation. Providing protections for currently unoccupied areas
that decrease the distances between occupied areas also assists in
reducing habitat fragmentation. The protection of these unoccupied
habitats will allow for future establishment of herds in these habitats
through translocation or natural colonization, which will help to
increase gene flow between populations. The ability to establish and
maintain regular gene flow between populations of Sierra Nevada bighorn
sheep is essential to their recovery. Reducing habitat fragmentation
through protection of these currently unoccupied habitats under a
critical habitat designation is essential to the subspecies'
conservation.
(35) Comment: The USFS recommended that the section discussing
wildfire be clarified to resolve apparent contradictions identifying
which management actions and stochastic events are considered
potentially beneficial or detrimental to critical habitat.
Our Response: Fires can have beneficial, as well as detrimental,
effects depending on the situation including location, severity, and
extent. As indicated in the Special Management Considerations or
Protection section, management actions such as the suppression of
wildfires over the past decades has allowed for encroachment of
forested habitat into Sierra Nevada bighorn sheep habitat. This has
been detrimental to the Sierra Nevada bighorn sheep by increasing
habitat for predator concealment. Management actions such as prescribed
fires are carried out in a planned, controlled manner in a specific
area and can be beneficial to Sierra Nevada bighorn sheep by reducing
selected forested habitat that can conceal predators. Stochastic events
such as wildfires can be beneficial or detrimental. For example, in
July 2007, lightning sparked fires in Sierra Nevada bighorn sheep
habitat in the Mount Baxter herd unit. The Seven Oaks Fire burned the
majority of the low elevation winter range [<8,000 ft (2438 m)]
(California Department of Fish and Game 2007, p. 5). The fire may
benefit Sierrra Nevada bighorn sheep by opening up forested areas. The
fire also scorched the above ground vegetation. With appropriate
moisture levels gained over the winter, sufficient forage may become
available. The CDFG personnel intend to evaluate the effects of this
fire on forage availability and quality and habitat selection by Sierra
Nevada bighorn sheep in this area (California Department of Fish and
Game 2007, p. 6).
(36) Comment: The USFS mentioned that the Mount Warren unit may not
extend northward enough to encompass currently occupied habitat as a
few Sierra Nevada bighorn sheep have occurred in the northern areas.
Our Response: According to 16 U.S.C. 1532(5)(C), ``critical habitat
should not include the entire geographic area that can be occupied by
the threatened or endangered species'' absent a finding of exceptional
circumstances by the Secretary of the Interior. We based our critical
habitat designation on the Recovery Team's delineation of essential
habitat and as indicated in our final approved recovery plan (Service
2007, p