Endangered and Threatened Wildlife and Plants; 90-Day Finding on a Petition To List a Distinct Population Segment of the American Black Bear in Nevada as Endangered or Threatened, 39670-39674 [2012-16335]
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Federal Register / Vol. 77, No. 129 / Thursday, July 5, 2012 / Proposed Rules
Services Field Office (see FOR FURTHER
INFORMATION CONTACT).
Author
The primary authors of this notice are
the staff members of the Caribbean
Ecological Services Field Office (see
ADDRESSES).
Authority: The authority for this action is
the Endangered Species Act of 1973, as
amended (16 U.S.C. 1531 et seq.).
Dated: June 20, 2012.
Daniel M. Ashe,
Director, U.S. Fish and Wildlife Service.
[FR Doc. 2012–16381 Filed 7–3–12; 8:45 am]
BILLING CODE 4310–55–P
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS–ES–R8–2012–0024;
4500030113]
Endangered and Threatened Wildlife
and Plants; 90-Day Finding on a
Petition To List a Distinct Population
Segment of the American Black Bear in
Nevada as Endangered or Threatened
Fish and Wildlife Service,
Interior.
ACTION: Notice of 90-day petition
finding.
AGENCY:
We, the U.S. Fish and
Wildlife Service, announce a 90-day
finding on a petition to list a distinct
population segment (DPS) of the
American black bear (Ursus
americanus) in Nevada as endangered
or threatened under the Endangered
Species Act of 1973, as amended (Act).
For the purposes of this finding, we
evaluated whether the petition presents
substantial information to indicate
whether the petitioned entity (the DPS
of the American black bear in Nevada)
may be a listable entity. Based on our
review, we conclude that the petition
does not provide substantial
information indicating that the DPS of
the American black bear in Nevada may
be a listable entity under the Act.
Because the petition does not present
substantial information indicating that
the American black bear in Nevada may
be a listable entity, we did not evaluate
whether the information contained in
the petition regarding threats was
substantial. Therefore, we are not
initiating a status review in response to
this petition. However, we ask the
public to submit to us any new
information that becomes available
concerning the status of, or threats to,
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the American black bear in Nevada or
its habitat at any time.
DATES: The finding announced in this
document was made on July 5, 2012.
ADDRESSES: This finding is available on
the Internet at https://
www.regulations.gov at Docket Number
[FWS–ES–R8–2012–0024]. Supporting
documentation we used in preparing
this finding is available for public
inspection, by appointment, during
normal business hours at the U.S. Fish
and Wildlife Service, Nevada Fish and
Wildlife Office, 1340 Financial
Boulevard, Suite 234, Reno, Nevada
89502–7147. Please submit any new
information, materials, comments, or
questions concerning this finding to the
above address.
FOR FURTHER INFORMATION CONTACT:
Edward D. Koch, State Supervisor of the
Nevada Fish and Wildlife Office (see
ADDRESSES), by telephone 775–861–
6300 or by facsimile to 775–861–6301.
If you use a telecommunications device
for the deaf (TDD), please call the
Federal Information Relay Service
(FIRS) at 800–877–8339.
SUPPLEMENTARY INFORMATION:
Background
Section 4(b)(3)(A) of the Act (16
U.S.C. 1531 et seq.) requires that we
make a finding on whether a petition to
list, delist, or reclassify a species
presents substantial scientific or
commercial information indicating that
the petitioned action may be warranted.
We are to base this finding on
information provided in the petition,
supporting information submitted with
the petition, and information otherwise
available in our files. To the maximum
extent practicable, we are to make this
finding within 90 days of our receipt of
the petition, and publish our notice of
the finding promptly in the Federal
Register.
Our standard for substantial scientific
or commercial information within the
Code of Federal Regulations (CFR) with
regard to a 90-day petition finding is
‘‘that amount of information that would
lead a reasonable person to believe that
the measure proposed in the petition
may be warranted’’ (50 CFR 424.14(b)).
If we find that substantial scientific or
commercial information was presented,
we are required to promptly conduct a
species status review, which we
subsequently summarize in our 12month finding.
Petition History
On September 6, 2011, we received a
petition dated September 1, 2011, from
Big Wildlife and NoBearHuntNV.org,
requesting that the American black bear
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in Nevada be designated as a DPS and
listed as endangered or threatened
under the Act. The petition clearly
identified itself as such and included
the requisite identification information
for the petitioners, as required by 50
CFR 424.14(a). In a November 4, 2011,
letter to the petitioner, we responded
that we reviewed the information
presented in the petition and
determined that issuing an emergency
regulation temporarily listing the
species under section 4(b)(7) of the Act
was not warranted. We also stated that
due to a requirement to complete a
significant number of listing and critical
habitat actions in Fiscal Year 2012,
pursuant to court orders, judicially
approved settlement agreements, and
other statutory deadlines, we would
conduct our review of the petition when
we secured funding for the action. At
that point, we anticipated making an
initial finding on the petition. This
finding addresses the petition.
Previous Federal Action(s)
No previous Federal actions have
been conducted specifically for
American black bears in Nevada.
Federal actions have been conducted for
black bears in other states, as discussed
below.
On February 15, 1983 (48 FR 6752),
the Service included the black bear in
Pennsylvania in a list of various
petitions; the Service determined that
the petition to list the black bear in
Pennsylvania did not provide
substantial information.
On June 21, 1990, the Service
published a proposed rule (55 FR
25341) to list the Louisiana black bear
(Ursus americanus luteolus) as
threatened in Louisiana, Mississippi,
and Texas. In addition, the Service
proposed a designation of threatened for
other black bear subspecies found
within the range of the Louisiana black
bear (Louisiana, Mississippi, Texas)
based on similarity of appearance. On
January 7, 1992, a final rule was
published in the Federal Register (57
FR 588) designating threatened status
for the Louisiana black bear and other
black bears within its range due to
similarity of appearance.
Species Information
American black bears are large
mammals with fur color that can be
black or cinnamon (Hall 1946, p. 171).
They are considered plantigrades (walk
on whole sole of foot) and both the front
and rear feet have five toes; claws are
longer on the front feet than on the hind
feet, and the tail is short (Hall 1946, p.
171). The profile is rather blunt; the
eyes are small, and the nose pad is
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broad with large nostrils (57 FR 588).
During summer, adult males generally
weigh between 300 and 350 pounds
(lbs) (135–158 kilograms (kg)) and adult
females about 150 lbs (68–90 kg)
(Lackey 2004, p. 8). Large males may
weigh in excess of 600 lbs (272 kg), but
weight varies greatly throughout the
species’ range (57 FR 588).
According to Hall (1981, p. 950), there
are 16 subspecies of black bear in North
America. Collectively, these subspecies
number approximately 800,000–900,000
bears in North America with about
400,000 in the United States
(Williamson 2002, p. 12; Renda 2010a,
no page number; Big Wildlife and
NoBearHuntNV.org 2011, p. 6).
The American black bear is adaptable
and inhabits forests, swamps, tundra,
and even the edges of suburbia (Bowers
et al. 2004, p. 142; Big Wildlife and
NoBearHuntNV.org 2011, p. 7).
American black bears are considered
omnivores, able to eat many types of
plant and animal material including
fruits, berries, nuts, roots, grass, seeds,
grubs, birds, fish, small mammals, and
carrion (Bowers et al. 2004, p. 143; Big
Wildlife and NoBearHuntNV.org 2011,
p. 8). They are considered intelligent,
with learning capabilities (Jonkel 1978,
p. 227; Big Wildlife and
NoBearHuntNV.org 2011, p. 7). In
addition, they are tolerant of humans
(Lackey 2004, p. 13). American black
bears have learned to associate humans
(including their homes and vehicles)
with food, leading some black bears to
move into urban areas (Lackey 2004, p.
13). This can lead to conflict or damage
between the two species (Beckmann and
Berger 2003, pp. 595–596; Beckmann
and Lackey 2004, p. 269; Lackey 2004,
p. 23; Breck et al. 2008, p. 429; Big
Wildlife and NoBearHuntNV.org 2011,
p. 7).
Bears, in general, are wide-ranging
animals with low reproductive rates and
low population densities (Jonkel 1978,
pp. 227, 231). The size of the habitat
needed by bears is generally related to
the abundance and availability of food
(Jonkel 1978, p. 238) and the age and
sex of the bear (Lackey 2004, p. 13).
Males will have larger home ranges than
females and may overlap with other
males and females (Lackey 2004, p. 13).
Bears can live within home ranges that
are small, provided there are many
available foods (Jonkel 1978, p. 238).
American black bear home ranges have
been recorded to be as small as 1 square
mile (mi2) (2.6 square kilometers) (km2)
(Jonkel 1978, p. 238). American black
bears are capable of moving
considerable distances in their search
for food or mates, and they are known
to return to their former habitat upon
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relocation (Beckmann and Lackey 2004,
pp. 270–271; Big Wildlife and
NoBearHuntNV.org 2011, p. 7).
Sexual maturity for American black
bear males occurs at about 4–6 years of
age; the age of sexual maturity for
females is about 4–5 years (Lackey 2004,
p. 11). American black bears mate in the
spring, with the embryo(s) implanting in
the fall; generally two or three cubs are
born in January or February (Bowers et
al. 2004, p. 142). The cubs do not
emerge from the den until spring and
stay with their mother until they are
about 18 months old, at which time they
disperse (Bowers et al. 2004, p. 142).
American black bears in western
Nevada belong to the subspecies Ursus
americanus californiensis, which is
found in the Sierra Nevada of California
and Nevada and the Cascade Range of
northern California and south central
Oregon (Hall 1981, pp. 949–950).
Known as the Sierra Nevada population,
it is estimated to consist of 10,000–
15,000 individuals (Renda 2010b, no
page number). We accept the
characterization of all American black
bears in Nevada as subspecies U. a.
californiensis based on Hall (1981, pp.
949–950) and Lackey (2004, p. 30).
Hall (1946, pp. 171, 175) indicates
that the historical distribution of
American black bears in Nevada
occurred near the vicinity of Lake Tahoe
(Douglas and Washoe Counties, Nevada)
on the border of Nevada and California.
However, Lackey (2004, pp. 2–3, 15)
states that the American black bear in
Nevada historically occurred in several
mountain ranges in the northeastern
(Jarbidge and Ruby), central (Toiyabe),
and western (Sierra Nevada) portions of
the State.
Currently, American black bears in
Nevada are known to occur in the
Carson (includes Lake Tahoe),
Sweetwater, Pine Nut, and Wassuk
Ranges of western Nevada (Beckmann
and Berger 2003, p. 597; Lackey 2004,
p. 19; Big Wildlife and
NoBearHuntNV.org 2011, p. 7).
Goodrich (1993 cited in Lackey 2004, p.
15) mentions these ranges and also
includes the Excelsior Range in Mineral
County. Confirmed recent American
black bear sightings have occurred in
the Delano, Independence, and Jarbidge
Mountains of Elko County; the Schell
Creek Range of White Pine County; and
the Vya Rim of northern Washoe County
(Nevada Department of Wildlife
(NDOW), unpublished data cited in
Lackey 2004, p. 15). These sightings
may indicate that the American black
bear in Nevada is expanding its range
eastward (Lackey 2004, p. 30).
There are currently an estimated 150–
300 adult American black bears living
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on the Nevada side of the Lake Tahoe
Basin and in the mountain ranges to the
south (Sonner 2011, no page number,
Big Wildlife and NoBearHuntNV.org
2011, p. 6). During the early 1990s in
Nevada, wild-land American black bears
(bears with almost 100 percent of their
point locations outside of urban areas,
in the Carson Range of the Sierra
Nevada, Sweetwater Range, Pine Nut
Range, and Wassuk Range) were at a
density of 20–40 bears/39 mi2 (20–40
bears/100 km2) (Beckmann and Berger
2003, pp. 597–598). During the late
1990s and early 2000s, urban-interface
American black bears (bears with 90
percent or more of their point locations
inside urban areas defined by town and
city delineation in Carson City, Incline
Village, Glenbrook, Stateline, Minden,
and Gardnerville, Nevada and South
Lake Tahoe, California), which did not
exist in the late 1980s (Goodrich 1990
cited in Beckmann and Berger 2003, p.
598), reached a density of 120 bears/39
mi2 (120 bears/100 km2) (Beckmann and
Berger 2003, pp. 597–598). Wild-land
American black bears were found at a
density of 3.2 bears/39 mi2 (3.2 bears/
100 km2) during the same period
(Beckmann and Berger 2003, p. 598).
The availability of food resources, such
as garbage, in urban areas is suggested
to have resulted in a redistribution of
American black bears across the
landscape in Nevada (Beckmann and
Berger 2003, p. 602), likely increasing
the number of American black bears in
urban-interface areas while decreasing
the number of American black bears in
wild-land areas.
Nevada Department of Wildlife
estimates that the American black bear
population in Nevada is growing at an
annual rate of 16 percent (Sonner 2011,
no page number). Beckmann and Berger
(2003, p. 602) were uncertain if the
American black bear population had
increased in their western Nevada study
area (Carson, Sweetwater, Pine Nut, and
Wassuk Ranges). While these authors
reported population numbers similar to
Goodrich (1990 cited in Beckmann and
Berger 2003, p. 602), they suggested that
the increase in numbers may be the
result of a shift of individuals from
wild-land areas to urban-interface areas
rather than an increase in population
size. During 1997–2002, Beckmann
(2002, p. 20) and Beckmann and Berger
(2003, p. 602) estimated Nevada’s
American black bear population at
about 300 in the Carson, Sweetwater,
Pine Nut, and Wassuk Ranges
collectively. This number is similar to
an estimate of 150–290 animals in the
same population based on an
extrapolation of Goodrich’s density
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estimate of 20–41 bears/39 mi2 (20–41
bears/100km2) (Goodrich 1990 cited in
Beckmann 2002, p. 20; Beckmann and
Berger 2003, p. 602) to the total area of
available habitat. The petitioners did
not provide, nor do we have in our files,
the information NDOW used to
determine that the American black bear
population in Nevada is increasing at an
annual rate of 16 percent. While the
petition presents information on the
total number of mortalities (104) that
occurred during the period from 1997 to
2004, we do not have data that indicate
the American black bear population in
Nevada is declining as stated in the
petition (Big Wildlife and
NoBearHuntNV.org 2011, p. 9). Based
on the petition and information
available in our files indicating past
population estimates, the current
American black bear population in
Nevada appears to be stable.
Review of Petition
The petition requests that the
American black bear in Nevada be listed
as a DPS under the Act. The petition
states that the American black bear in
Nevada is threatened by habitat loss due
primarily to residential development
and recreational encroachment (Big
Wildlife and NoBearHuntNV.org 2011,
p. 5). The petition also states that, due
to increasing interactions with humans,
anthropogenic killing of these bears is
identified as significant and increasing
(Big Wildlife and NoBearHuntNV.org
2011, p. 5). In addition, NDOW
authorized, for the first time, a fall hunt
in 2011; the petition asserts that hunting
will further endanger this population
(Big Wildlife and NoBearHuntNV.org
2011, p. 5).
The petition asserts that the American
black bear in Nevada should be listed
under the Act as a DPS because
Nevada’s black bears are markedly
separated (discrete) from other
populations of American black bears
due to physical and behavioral factors
(Big Wildlife and NoBearHuntNV.org
2011, p. 13). The petition cites Breck et
al. (2008) in support of genetic and
behavioral differences related to conflict
behavior between people and American
black bear populations in Yosemite
National Park, California, and Lake
Tahoe Basin, Nevada (Big Wildlife and
NoBearHuntNV.org 2011, p. 13).
The petition also asserts that the
American black bear population in
Nevada is significant due to the bear’s
continued existence in western Nevada
since the early 1990s in forested,
mountain range habitat that is isolated
by wide desert valleys; however, the
petition notes that American black bears
will occasionally use the desert valleys
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in Nevada for travel between mountain
ranges (Big Wildlife and
NoBearHuntNV.org 2011, p. 13). The
petition asserts that this bear habitat in
western Nevada is characteristic of the
unique Great Basin ecosystem (Big
Wildlife and NoBearHuntNV.org 2011,
p. 13). The petition asserts that loss of
the American black bear population in
Nevada would result in a significant gap
in the species’ range because this
population is genetically and
behaviorally distinct from other
American black bears as indicated
above, and, therefore, a unique
population would be lost (Big Wildlife
and NoBearHuntNV.org 2011, p. 14).
Evaluation of Listable Entity
Under the Service’s Policy Regarding
the Recognition of Distinct Vertebrate
Population Segments Under the
Endangered Species Act (61 FR 4722,
February 7, 1996), three elements are
considered in the decision concerning
the establishment and classification of a
possible DPS. These are applied
similarly for additions to or removal
from the Federal List of Endangered and
Threatened Wildlife. These elements
include:
(1) The discreteness of a population in
relation to the remainder of the taxon to
which it belongs;
(2) The significance of the population
segment to the taxon to which it
belongs; and
(3) The population segment’s
conservation status in relation to the
Act’s standards for listing, delisting
(removal from the list), or
reclassification (i.e., is the population
segment endangered or threatened).
In this analysis, we evaluate whether
the petition provides substantial
information that the American black
bear in Nevada may constitute a DPS.
Discreteness
Under the DPS policy, a population
segment of a vertebrate taxon may be
considered discrete if it satisfies either
one of the following conditions:
(1) It is markedly separated from other
populations of the same taxon as a
consequence of physical, physiological,
ecological, or behavioral factors.
Quantitative measures of genetic or
morphological discontinuity may
provide evidence of this separation.
(2) It is delimited by international
governmental boundaries within which
differences in control of exploitation,
management of habitat, conservation
status, or regulatory mechanisms exist
that are significant in light of section
4(a)(1)(D) of the Act.
The petition asserts that American
black bears in Nevada should be listed
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under the Act as a DPS because they are
markedly separate from other
populations of American black bears
due to physical and behavioral factors,
citing Breck et al. (2008) (Big Wildlife
and NoBearHuntNV.org 2011, p. 13).
Review of Breck et al. (2008) does not
support this assertion. Breck et al.
(2008, p. 428) investigated whether
food-conditioning behavior (discussed
more fully in the following paragraphs)
was inherited or learned through parentoffspring social learning. This study
involved the collection of genetic
samples (blood and hair) from two
American black bear populations: Lake
Tahoe Basin, Nevada, and Yosemite
National Park, California. Both
populations evaluated in this study
comprised individuals who were not
food-conditioned as well as those who
were food-conditioned (Breck et al.
2008, pp. 431–432). Breck et al. (2008)
used genetic data to determine
relatedness of individuals through
mother–offspring and sibling
relationships within each population.
These relationships were then used to
determine how food-conditioning
behavior was acquired. If behavior is
inherited or if parent-offspring learning
is a dominant means for obtaining
behavior, then behaviors that are of
significant advantage should lead to
subpopulations of related individuals
with similar behaviors (Breck et al.
2008, p. 428).
Breck et al. (2008) did not analyze
their genetic data to evaluate the degree
of genetic divergence between the Lake
Tahoe Basin, Nevada, and Yosemite
National Park, California populations. In
order to determine the degree of genetic
similarity among populations, genetic
material should be obtained from many
individuals from different geographic
areas to assess patterns and amounts of
gene flow among populations (Allendorf
and Luikart 2007, pp. 393–394). The
genetic information presented in Breck
et al. (2008, pp. 430–431) does not
support the petition’s assertion that the
American black bear population in
Nevada is markedly separate from other
American black bear populations. We
do not have additional information in
our files addressing the genetics of other
American black bears found in Nevada
or California. Therefore, substantial
information was not provided in the
petition, and information available in
our files does not suggest, that American
black bears in Nevada may be markedly
separate from other American black
bears found outside of Nevada based on
genetics.
As indicated above, Breck et al. (2008,
p. 428) investigated whether foodconditioning behavior was inherited or
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learned through parent-offspring social
learning. Learning can also occur
asocially (independently of others) and
socially (observing unrelated
individuals) (Breck et al. 2008, p. 428).
The authors concluded that three of
their four analyses were similar in that
they revealed little evidence that foodconditioning behavior was inherited or
learned from the parent-offspring
relationship (Breck et al. 2008, p. 431).
While their fourth analysis indicated
some statistical difference for the foodconditioned category compared with the
other category pairings (nonfoodconditioned compared to nonfoodconditioned; nonfood-conditioned
compared to food conditioned) for
American black bears at Yosemite
National Park, they also concluded that
it did not show strong evidence that
food-conditioning behavior was
inherited or learned from the parentoffspring relationship (Breck et al. 2008,
p. 432). They concluded that this fourth
analysis was statistically significant, but
not biologically meaningful, and the
result may be attributable to the large
sample size of the study (Breck et al.
2008, p. 432).
While food-conditioning behavior
could be learned from the parentoffspring relationship or through
inheritance, these are not the primary
means of learning (Breck et al. 2008, p.
433). Breck et al. (2008, p. 433) state
that, because American black bears are
adaptable, it is unlikely that a behavior
that can be applied under various
environmental conditions and over a
large geographic area would result in a
genetic lineage that is distinct. Breck et
al. (2008, pp. 430–431) do not support
the petition’s assertion that the
American black bear population in
Nevada may be markedly separate from
other populations of American black
bears outside of the State due to
behavioral differences. The petition
does not provide substantial
information, nor do we have
information in our files, to indicate that
American black bears in Nevada may be
markedly separate from other American
black bears outside of Nevada based on
behavioral factors.
There is further lack of support for the
claim that American black bear
populations between Nevada and
California are markedly separate
because the American black bear
population in Nevada is not physically
separated from American black bears in
California, nor is the habitat used by
American black bears in Nevada unique.
While Lake Tahoe (and its Basin) is
divided by the State boundary between
California and Nevada, it is not a
complete physical barrier to American
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black bear movement between the two
States; American black bears are found
throughout the Sierra Nevada (Zielinski
et al. 2005, pp. 1396, 1400) and can
move between the two States in the
Basin as well as to the north and south
of the Basin. There is no physical barrier
or terrain along the remaining State
boundary north or south of Lake Tahoe
(and its Basin) within the range of the
subspecies that prevents cross-border
movement. Beckmann (2002, pp. 39,
42–43) provides home range maps of
collared Nevada and California
American black bears that demonstrate
individuals’ use of habitat in both States
on both the north and south ends of
Lake Tahoe. Also, the American black
bear population in Nevada is not
isolated by individual mountain ranges
within the State. Beckmann (2002, pp.
42–43) demonstrated overlap of
American black bear home ranges in
central Nevada. This wide-ranging
species can travel long distances and is
capable of, and has been documented,
crossing desert valleys between
mountain ranges in Nevada (Beckmann
and Lackey 2004, p. 271).
The petition asserts that American
black bear habitat in western Nevada
(forested mountain ranges isolated by
valleys) is characteristic of the unique
Great Basin ecosystem (Big Wildlife and
NoBearHuntNV.org 2011, p. 13).
American black bears are adaptable and
are found in many habitat types across
North America (Bowers et al. 2004, p.
142; Big Wildlife and
NoBearHuntNV.org 2011, p. 7). The use
of forested mountain habitats by
American black bears in Nevada is not
unique (Zielinski et al. 2005, p. 1385).
Forested mountain ranges are not
unique to Nevada, nor do they terminate
discretely at the State border. The Great
Basin covers a large geographic area in
the western United States and includes
portions of the States of Oregon,
California, Nevada, Utah, and Idaho (70
FR 73190, December 9, 2005). This
geographic area extends well beyond the
boundaries of Nevada. The Great Basin
does not lie wholly within the State of
Nevada nor does it correspond to
Nevada State boundaries. The petition
does not provide substantial
information, nor is there information
available in our files, to suggest that the
American black bear in Nevada may be
markedly separate from other
populations of American black bears
outside of Nevada due to physical or
geographic reasons.
The petition does not present
information to suggest there may be a
markedly separate population of
American black bears in Nevada due to
physiological reasons. Additionally, we
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do not have information in our files to
indicate that the American black bear in
Nevada may be markedly separate from
other American black bears outside of
this area due to physiological reasons.
Substantial information is not
presented in the petition, nor is it
available in our files, to suggest there
may be a markedly separate population
of American black bears in Nevada due
to physical, physiological, ecological, or
behavioral differences as compared to
American black bears located in the
Sierra Nevada of California and
elsewhere. Therefore, we determine,
based on the information provided in
the petition and in our files that the
American black bear population in
Nevada may not be markedly separate
from other black bear populations found
outside of the State. Therefore, we
conclude that the black bear population
in Nevada does not meet the
discreteness criterion of the 1996 DPS
policy.
There are no international
governmental boundaries associated
with this subspecies that are significant.
The American black bear population
found in Nevada lies wholly within the
United States. Because this element is
not relevant in this case for a finding of
discreteness, it was not considered in
reaching this determination.
Significance
If a population segment is considered
discrete under one or more of the
conditions described in our DPS policy,
its biological and ecological significance
will be considered in light of
Congressional guidance that the
authority to list DPSs be used
‘‘sparingly’’ while encouraging the
conservation of genetic diversity. In
making this determination, we consider
available scientific evidence of the
discrete population segment’s
importance to the taxon to which it
belongs. Since precise circumstances are
likely to vary considerably from case to
case, the DPS policy does not describe
all the classes of information that might
be used in determining the biological
and ecological importance of a discrete
population. However, the DPS policy
does provide four possible reasons why
a discrete population may be significant.
As specified in the DPS policy (61 FR
4722), this consideration of the
population segment’s significance may
include, but is not limited to, the
following:
(1) Persistence of the discrete
population segment in an ecological
setting unusual or unique to the taxon;
(2) Evidence that loss of the discrete
population segment would result in a
significant gap in the range of a taxon;
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(3) Evidence that the discrete
population segment represents the only
surviving natural occurrence of a taxon
that may be more abundant elsewhere as
an introduced population outside its
historical range; or
(4) Evidence that the discrete
population segment differs markedly
from other populations of the species in
its genetic characteristics.
A population segment needs to satisfy
only one of these criteria to be
considered significant. Furthermore, the
list of criteria is not exhaustive; other
criteria may be used as appropriate.
Because we must find a population to
be both discrete and significant to
qualify as a DPS, and we did not find
the population to be discrete, we will
not address the potential significance of
the American black bear in Nevada to
the remainder of the taxon, nor will we
evaluate the population’s conservation
status.
Conclusion of Distinct Population
Segment Review
wreier-aviles on DSK5TPTVN1PROD with PROPOSALS
Based on the information provided in
the petition and in our files, we find
that the petition does not provide
substantial information to indicate that
the American black bear population in
Nevada meets the discreteness criterion
of the DPS policy. Since both
discreteness and significance are
required to satisfy the DPS policy, we
have determined that the American
black bear population in Nevada does
not qualify as a DPS under our policy
and, therefore, is not a listable entity
VerDate Mar<15>2010
14:29 Jul 03, 2012
Jkt 226001
under the Act. As a result, no further
analysis under the DPS policy is
necessary.
Finding
We reviewed the information
presented in the petition, and we
evaluated that information in relation to
information readily available in our
files. On the basis of our review, we find
that neither the petition, nor
information readily available in our
files, suggests that the American black
bear population in Nevada meets the
criteria for being discrete under our DPS
policy. Available information from the
petition and our files does not suggest
there may be a markedly separate
population of American black bears in
Nevada compared with other
populations due to physical,
physiological, ecological, or behavioral
differences. The American black bear in
Nevada is not found to be markedly
separate from other American black bear
populations because it is not physically
separate from other adjacent
populations due to various kinds of
barriers, it is not genetically different
and does not demonstrate physiological
or behavioral differences, nor does it
occur in ecological settings in Nevada
that are dissimilar from other areas
occupied by the American black bear.
Because the petition does not present
substantial information that the
American black bear in Nevada may be
a DPS, we did not evaluate whether the
information contained in the petition
regarding the conservation status was
PO 00000
Frm 00024
Fmt 4702
Sfmt 9990
substantial. We conclude that the
American black bear in Nevada does not
satisfy the elements of being a DPS
under our 1996 policy and, therefore, is
not a listable entity under section 3(16)
of the Act.
We encourage interested parties to
continue to gather data that will assist
with the conservation of the American
black bear in Nevada. If you wish to
provide information regarding the
American black bear in Nevada, you
may submit your information or
materials to the State Supervisor,
Nevada Fish and Wildlife Office (see
ADDRESSES), at any time.
References Cited
A complete list of references cited is
available on the Internet at https://
www.regulations.gov and upon request
from the Nevada Fish and Wildlife
Office (see FOR FURTHER INFORMATION
CONTACT).
Author
The primary authors of this notice are
the staff of the Nevada Fish and Wildlife
Office (see ADDRESSES).
Authority
The authority for this action is the
Endangered Species Act of 1973, as
amended (16 U.S.C. 1531 et seq.).
Dated: June 19, 2012.
Daniel M. Ashe,
Director, U.S. Fish and Wildlife Service.
[FR Doc. 2012–16335 Filed 7–3–12; 8:45 am]
BILLING CODE 4310–55–P
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Agencies
[Federal Register Volume 77, Number 129 (Thursday, July 5, 2012)]
[Proposed Rules]
[Pages 39670-39674]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2012-16335]
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DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS-ES-R8-2012-0024; 4500030113]
Endangered and Threatened Wildlife and Plants; 90-Day Finding on
a Petition To List a Distinct Population Segment of the American Black
Bear in Nevada as Endangered or Threatened
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Notice of 90-day petition finding.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service, announce a 90-day
finding on a petition to list a distinct population segment (DPS) of
the American black bear (Ursus americanus) in Nevada as endangered or
threatened under the Endangered Species Act of 1973, as amended (Act).
For the purposes of this finding, we evaluated whether the petition
presents substantial information to indicate whether the petitioned
entity (the DPS of the American black bear in Nevada) may be a listable
entity. Based on our review, we conclude that the petition does not
provide substantial information indicating that the DPS of the American
black bear in Nevada may be a listable entity under the Act. Because
the petition does not present substantial information indicating that
the American black bear in Nevada may be a listable entity, we did not
evaluate whether the information contained in the petition regarding
threats was substantial. Therefore, we are not initiating a status
review in response to this petition. However, we ask the public to
submit to us any new information that becomes available concerning the
status of, or threats to, the American black bear in Nevada or its
habitat at any time.
DATES: The finding announced in this document was made on July 5, 2012.
ADDRESSES: This finding is available on the Internet at https://www.regulations.gov at Docket Number [FWS-ES-R8-2012-0024]. Supporting
documentation we used in preparing this finding is available for public
inspection, by appointment, during normal business hours at the U.S.
Fish and Wildlife Service, Nevada Fish and Wildlife Office, 1340
Financial Boulevard, Suite 234, Reno, Nevada 89502-7147. Please submit
any new information, materials, comments, or questions concerning this
finding to the above address.
FOR FURTHER INFORMATION CONTACT: Edward D. Koch, State Supervisor of
the Nevada Fish and Wildlife Office (see ADDRESSES), by telephone 775-
861-6300 or by facsimile to 775-861-6301. If you use a
telecommunications device for the deaf (TDD), please call the Federal
Information Relay Service (FIRS) at 800-877-8339.
SUPPLEMENTARY INFORMATION:
Background
Section 4(b)(3)(A) of the Act (16 U.S.C. 1531 et seq.) requires
that we make a finding on whether a petition to list, delist, or
reclassify a species presents substantial scientific or commercial
information indicating that the petitioned action may be warranted. We
are to base this finding on information provided in the petition,
supporting information submitted with the petition, and information
otherwise available in our files. To the maximum extent practicable, we
are to make this finding within 90 days of our receipt of the petition,
and publish our notice of the finding promptly in the Federal Register.
Our standard for substantial scientific or commercial information
within the Code of Federal Regulations (CFR) with regard to a 90-day
petition finding is ``that amount of information that would lead a
reasonable person to believe that the measure proposed in the petition
may be warranted'' (50 CFR 424.14(b)). If we find that substantial
scientific or commercial information was presented, we are required to
promptly conduct a species status review, which we subsequently
summarize in our 12-month finding.
Petition History
On September 6, 2011, we received a petition dated September 1,
2011, from Big Wildlife and NoBearHuntNV.org, requesting that the
American black bear in Nevada be designated as a DPS and listed as
endangered or threatened under the Act. The petition clearly identified
itself as such and included the requisite identification information
for the petitioners, as required by 50 CFR 424.14(a). In a November 4,
2011, letter to the petitioner, we responded that we reviewed the
information presented in the petition and determined that issuing an
emergency regulation temporarily listing the species under section
4(b)(7) of the Act was not warranted. We also stated that due to a
requirement to complete a significant number of listing and critical
habitat actions in Fiscal Year 2012, pursuant to court orders,
judicially approved settlement agreements, and other statutory
deadlines, we would conduct our review of the petition when we secured
funding for the action. At that point, we anticipated making an initial
finding on the petition. This finding addresses the petition.
Previous Federal Action(s)
No previous Federal actions have been conducted specifically for
American black bears in Nevada. Federal actions have been conducted for
black bears in other states, as discussed below.
On February 15, 1983 (48 FR 6752), the Service included the black
bear in Pennsylvania in a list of various petitions; the Service
determined that the petition to list the black bear in Pennsylvania did
not provide substantial information.
On June 21, 1990, the Service published a proposed rule (55 FR
25341) to list the Louisiana black bear (Ursus americanus luteolus) as
threatened in Louisiana, Mississippi, and Texas. In addition, the
Service proposed a designation of threatened for other black bear
subspecies found within the range of the Louisiana black bear
(Louisiana, Mississippi, Texas) based on similarity of appearance. On
January 7, 1992, a final rule was published in the Federal Register (57
FR 588) designating threatened status for the Louisiana black bear and
other black bears within its range due to similarity of appearance.
Species Information
American black bears are large mammals with fur color that can be
black or cinnamon (Hall 1946, p. 171). They are considered plantigrades
(walk on whole sole of foot) and both the front and rear feet have five
toes; claws are longer on the front feet than on the hind feet, and the
tail is short (Hall 1946, p. 171). The profile is rather blunt; the
eyes are small, and the nose pad is
[[Page 39671]]
broad with large nostrils (57 FR 588). During summer, adult males
generally weigh between 300 and 350 pounds (lbs) (135-158 kilograms
(kg)) and adult females about 150 lbs (68-90 kg) (Lackey 2004, p. 8).
Large males may weigh in excess of 600 lbs (272 kg), but weight varies
greatly throughout the species' range (57 FR 588).
According to Hall (1981, p. 950), there are 16 subspecies of black
bear in North America. Collectively, these subspecies number
approximately 800,000-900,000 bears in North America with about 400,000
in the United States (Williamson 2002, p. 12; Renda 2010a, no page
number; Big Wildlife and NoBearHuntNV.org 2011, p. 6).
The American black bear is adaptable and inhabits forests, swamps,
tundra, and even the edges of suburbia (Bowers et al. 2004, p. 142; Big
Wildlife and NoBearHuntNV.org 2011, p. 7). American black bears are
considered omnivores, able to eat many types of plant and animal
material including fruits, berries, nuts, roots, grass, seeds, grubs,
birds, fish, small mammals, and carrion (Bowers et al. 2004, p. 143;
Big Wildlife and NoBearHuntNV.org 2011, p. 8). They are considered
intelligent, with learning capabilities (Jonkel 1978, p. 227; Big
Wildlife and NoBearHuntNV.org 2011, p. 7). In addition, they are
tolerant of humans (Lackey 2004, p. 13). American black bears have
learned to associate humans (including their homes and vehicles) with
food, leading some black bears to move into urban areas (Lackey 2004,
p. 13). This can lead to conflict or damage between the two species
(Beckmann and Berger 2003, pp. 595-596; Beckmann and Lackey 2004, p.
269; Lackey 2004, p. 23; Breck et al. 2008, p. 429; Big Wildlife and
NoBearHuntNV.org 2011, p. 7).
Bears, in general, are wide-ranging animals with low reproductive
rates and low population densities (Jonkel 1978, pp. 227, 231). The
size of the habitat needed by bears is generally related to the
abundance and availability of food (Jonkel 1978, p. 238) and the age
and sex of the bear (Lackey 2004, p. 13). Males will have larger home
ranges than females and may overlap with other males and females
(Lackey 2004, p. 13). Bears can live within home ranges that are small,
provided there are many available foods (Jonkel 1978, p. 238). American
black bear home ranges have been recorded to be as small as 1 square
mile (mi\2\) (2.6 square kilometers) (km\2\) (Jonkel 1978, p. 238).
American black bears are capable of moving considerable distances in
their search for food or mates, and they are known to return to their
former habitat upon relocation (Beckmann and Lackey 2004, pp. 270-271;
Big Wildlife and NoBearHuntNV.org 2011, p. 7).
Sexual maturity for American black bear males occurs at about 4-6
years of age; the age of sexual maturity for females is about 4-5 years
(Lackey 2004, p. 11). American black bears mate in the spring, with the
embryo(s) implanting in the fall; generally two or three cubs are born
in January or February (Bowers et al. 2004, p. 142). The cubs do not
emerge from the den until spring and stay with their mother until they
are about 18 months old, at which time they disperse (Bowers et al.
2004, p. 142).
American black bears in western Nevada belong to the subspecies
Ursus americanus californiensis, which is found in the Sierra Nevada of
California and Nevada and the Cascade Range of northern California and
south central Oregon (Hall 1981, pp. 949-950). Known as the Sierra
Nevada population, it is estimated to consist of 10,000-15,000
individuals (Renda 2010b, no page number). We accept the
characterization of all American black bears in Nevada as subspecies U.
a. californiensis based on Hall (1981, pp. 949-950) and Lackey (2004,
p. 30).
Hall (1946, pp. 171, 175) indicates that the historical
distribution of American black bears in Nevada occurred near the
vicinity of Lake Tahoe (Douglas and Washoe Counties, Nevada) on the
border of Nevada and California. However, Lackey (2004, pp. 2-3, 15)
states that the American black bear in Nevada historically occurred in
several mountain ranges in the northeastern (Jarbidge and Ruby),
central (Toiyabe), and western (Sierra Nevada) portions of the State.
Currently, American black bears in Nevada are known to occur in the
Carson (includes Lake Tahoe), Sweetwater, Pine Nut, and Wassuk Ranges
of western Nevada (Beckmann and Berger 2003, p. 597; Lackey 2004, p.
19; Big Wildlife and NoBearHuntNV.org 2011, p. 7). Goodrich (1993 cited
in Lackey 2004, p. 15) mentions these ranges and also includes the
Excelsior Range in Mineral County. Confirmed recent American black bear
sightings have occurred in the Delano, Independence, and Jarbidge
Mountains of Elko County; the Schell Creek Range of White Pine County;
and the Vya Rim of northern Washoe County (Nevada Department of
Wildlife (NDOW), unpublished data cited in Lackey 2004, p. 15). These
sightings may indicate that the American black bear in Nevada is
expanding its range eastward (Lackey 2004, p. 30).
There are currently an estimated 150-300 adult American black bears
living on the Nevada side of the Lake Tahoe Basin and in the mountain
ranges to the south (Sonner 2011, no page number, Big Wildlife and
NoBearHuntNV.org 2011, p. 6). During the early 1990s in Nevada, wild-
land American black bears (bears with almost 100 percent of their point
locations outside of urban areas, in the Carson Range of the Sierra
Nevada, Sweetwater Range, Pine Nut Range, and Wassuk Range) were at a
density of 20-40 bears/39 mi\2\ (20-40 bears/100 km\2\) (Beckmann and
Berger 2003, pp. 597-598). During the late 1990s and early 2000s,
urban-interface American black bears (bears with 90 percent or more of
their point locations inside urban areas defined by town and city
delineation in Carson City, Incline Village, Glenbrook, Stateline,
Minden, and Gardnerville, Nevada and South Lake Tahoe, California),
which did not exist in the late 1980s (Goodrich 1990 cited in Beckmann
and Berger 2003, p. 598), reached a density of 120 bears/39 mi\2\ (120
bears/100 km\2\) (Beckmann and Berger 2003, pp. 597-598). Wild-land
American black bears were found at a density of 3.2 bears/39 mi\2\ (3.2
bears/100 km\2\) during the same period (Beckmann and Berger 2003, p.
598). The availability of food resources, such as garbage, in urban
areas is suggested to have resulted in a redistribution of American
black bears across the landscape in Nevada (Beckmann and Berger 2003,
p. 602), likely increasing the number of American black bears in urban-
interface areas while decreasing the number of American black bears in
wild-land areas.
Nevada Department of Wildlife estimates that the American black
bear population in Nevada is growing at an annual rate of 16 percent
(Sonner 2011, no page number). Beckmann and Berger (2003, p. 602) were
uncertain if the American black bear population had increased in their
western Nevada study area (Carson, Sweetwater, Pine Nut, and Wassuk
Ranges). While these authors reported population numbers similar to
Goodrich (1990 cited in Beckmann and Berger 2003, p. 602), they
suggested that the increase in numbers may be the result of a shift of
individuals from wild-land areas to urban-interface areas rather than
an increase in population size. During 1997-2002, Beckmann (2002, p.
20) and Beckmann and Berger (2003, p. 602) estimated Nevada's American
black bear population at about 300 in the Carson, Sweetwater, Pine Nut,
and Wassuk Ranges collectively. This number is similar to an estimate
of 150-290 animals in the same population based on an extrapolation of
Goodrich's density
[[Page 39672]]
estimate of 20-41 bears/39 mi\2\ (20-41 bears/100km\2\) (Goodrich 1990
cited in Beckmann 2002, p. 20; Beckmann and Berger 2003, p. 602) to the
total area of available habitat. The petitioners did not provide, nor
do we have in our files, the information NDOW used to determine that
the American black bear population in Nevada is increasing at an annual
rate of 16 percent. While the petition presents information on the
total number of mortalities (104) that occurred during the period from
1997 to 2004, we do not have data that indicate the American black bear
population in Nevada is declining as stated in the petition (Big
Wildlife and NoBearHuntNV.org 2011, p. 9). Based on the petition and
information available in our files indicating past population
estimates, the current American black bear population in Nevada appears
to be stable.
Review of Petition
The petition requests that the American black bear in Nevada be
listed as a DPS under the Act. The petition states that the American
black bear in Nevada is threatened by habitat loss due primarily to
residential development and recreational encroachment (Big Wildlife and
NoBearHuntNV.org 2011, p. 5). The petition also states that, due to
increasing interactions with humans, anthropogenic killing of these
bears is identified as significant and increasing (Big Wildlife and
NoBearHuntNV.org 2011, p. 5). In addition, NDOW authorized, for the
first time, a fall hunt in 2011; the petition asserts that hunting will
further endanger this population (Big Wildlife and NoBearHuntNV.org
2011, p. 5).
The petition asserts that the American black bear in Nevada should
be listed under the Act as a DPS because Nevada's black bears are
markedly separated (discrete) from other populations of American black
bears due to physical and behavioral factors (Big Wildlife and
NoBearHuntNV.org 2011, p. 13). The petition cites Breck et al. (2008)
in support of genetic and behavioral differences related to conflict
behavior between people and American black bear populations in Yosemite
National Park, California, and Lake Tahoe Basin, Nevada (Big Wildlife
and NoBearHuntNV.org 2011, p. 13).
The petition also asserts that the American black bear population
in Nevada is significant due to the bear's continued existence in
western Nevada since the early 1990s in forested, mountain range
habitat that is isolated by wide desert valleys; however, the petition
notes that American black bears will occasionally use the desert
valleys in Nevada for travel between mountain ranges (Big Wildlife and
NoBearHuntNV.org 2011, p. 13). The petition asserts that this bear
habitat in western Nevada is characteristic of the unique Great Basin
ecosystem (Big Wildlife and NoBearHuntNV.org 2011, p. 13). The petition
asserts that loss of the American black bear population in Nevada would
result in a significant gap in the species' range because this
population is genetically and behaviorally distinct from other American
black bears as indicated above, and, therefore, a unique population
would be lost (Big Wildlife and NoBearHuntNV.org 2011, p. 14).
Evaluation of Listable Entity
Under the Service's Policy Regarding the Recognition of Distinct
Vertebrate Population Segments Under the Endangered Species Act (61 FR
4722, February 7, 1996), three elements are considered in the decision
concerning the establishment and classification of a possible DPS.
These are applied similarly for additions to or removal from the
Federal List of Endangered and Threatened Wildlife. These elements
include:
(1) The discreteness of a population in relation to the remainder
of the taxon to which it belongs;
(2) The significance of the population segment to the taxon to
which it belongs; and
(3) The population segment's conservation status in relation to the
Act's standards for listing, delisting (removal from the list), or
reclassification (i.e., is the population segment endangered or
threatened).
In this analysis, we evaluate whether the petition provides
substantial information that the American black bear in Nevada may
constitute a DPS.
Discreteness
Under the DPS policy, a population segment of a vertebrate taxon
may be considered discrete if it satisfies either one of the following
conditions:
(1) It is markedly separated from other populations of the same
taxon as a consequence of physical, physiological, ecological, or
behavioral factors. Quantitative measures of genetic or morphological
discontinuity may provide evidence of this separation.
(2) It is delimited by international governmental boundaries within
which differences in control of exploitation, management of habitat,
conservation status, or regulatory mechanisms exist that are
significant in light of section 4(a)(1)(D) of the Act.
The petition asserts that American black bears in Nevada should be
listed under the Act as a DPS because they are markedly separate from
other populations of American black bears due to physical and
behavioral factors, citing Breck et al. (2008) (Big Wildlife and
NoBearHuntNV.org 2011, p. 13). Review of Breck et al. (2008) does not
support this assertion. Breck et al. (2008, p. 428) investigated
whether food-conditioning behavior (discussed more fully in the
following paragraphs) was inherited or learned through parent-offspring
social learning. This study involved the collection of genetic samples
(blood and hair) from two American black bear populations: Lake Tahoe
Basin, Nevada, and Yosemite National Park, California. Both populations
evaluated in this study comprised individuals who were not food-
conditioned as well as those who were food-conditioned (Breck et al.
2008, pp. 431-432). Breck et al. (2008) used genetic data to determine
relatedness of individuals through mother-offspring and sibling
relationships within each population. These relationships were then
used to determine how food-conditioning behavior was acquired. If
behavior is inherited or if parent-offspring learning is a dominant
means for obtaining behavior, then behaviors that are of significant
advantage should lead to subpopulations of related individuals with
similar behaviors (Breck et al. 2008, p. 428).
Breck et al. (2008) did not analyze their genetic data to evaluate
the degree of genetic divergence between the Lake Tahoe Basin, Nevada,
and Yosemite National Park, California populations. In order to
determine the degree of genetic similarity among populations, genetic
material should be obtained from many individuals from different
geographic areas to assess patterns and amounts of gene flow among
populations (Allendorf and Luikart 2007, pp. 393-394). The genetic
information presented in Breck et al. (2008, pp. 430-431) does not
support the petition's assertion that the American black bear
population in Nevada is markedly separate from other American black
bear populations. We do not have additional information in our files
addressing the genetics of other American black bears found in Nevada
or California. Therefore, substantial information was not provided in
the petition, and information available in our files does not suggest,
that American black bears in Nevada may be markedly separate from other
American black bears found outside of Nevada based on genetics.
As indicated above, Breck et al. (2008, p. 428) investigated
whether food-conditioning behavior was inherited or
[[Page 39673]]
learned through parent-offspring social learning. Learning can also
occur asocially (independently of others) and socially (observing
unrelated individuals) (Breck et al. 2008, p. 428). The authors
concluded that three of their four analyses were similar in that they
revealed little evidence that food-conditioning behavior was inherited
or learned from the parent-offspring relationship (Breck et al. 2008,
p. 431). While their fourth analysis indicated some statistical
difference for the food-conditioned category compared with the other
category pairings (nonfood-conditioned compared to nonfood-conditioned;
nonfood-conditioned compared to food conditioned) for American black
bears at Yosemite National Park, they also concluded that it did not
show strong evidence that food-conditioning behavior was inherited or
learned from the parent-offspring relationship (Breck et al. 2008, p.
432). They concluded that this fourth analysis was statistically
significant, but not biologically meaningful, and the result may be
attributable to the large sample size of the study (Breck et al. 2008,
p. 432).
While food-conditioning behavior could be learned from the parent-
offspring relationship or through inheritance, these are not the
primary means of learning (Breck et al. 2008, p. 433). Breck et al.
(2008, p. 433) state that, because American black bears are adaptable,
it is unlikely that a behavior that can be applied under various
environmental conditions and over a large geographic area would result
in a genetic lineage that is distinct. Breck et al. (2008, pp. 430-431)
do not support the petition's assertion that the American black bear
population in Nevada may be markedly separate from other populations of
American black bears outside of the State due to behavioral
differences. The petition does not provide substantial information, nor
do we have information in our files, to indicate that American black
bears in Nevada may be markedly separate from other American black
bears outside of Nevada based on behavioral factors.
There is further lack of support for the claim that American black
bear populations between Nevada and California are markedly separate
because the American black bear population in Nevada is not physically
separated from American black bears in California, nor is the habitat
used by American black bears in Nevada unique. While Lake Tahoe (and
its Basin) is divided by the State boundary between California and
Nevada, it is not a complete physical barrier to American black bear
movement between the two States; American black bears are found
throughout the Sierra Nevada (Zielinski et al. 2005, pp. 1396, 1400)
and can move between the two States in the Basin as well as to the
north and south of the Basin. There is no physical barrier or terrain
along the remaining State boundary north or south of Lake Tahoe (and
its Basin) within the range of the subspecies that prevents cross-
border movement. Beckmann (2002, pp. 39, 42-43) provides home range
maps of collared Nevada and California American black bears that
demonstrate individuals' use of habitat in both States on both the
north and south ends of Lake Tahoe. Also, the American black bear
population in Nevada is not isolated by individual mountain ranges
within the State. Beckmann (2002, pp. 42-43) demonstrated overlap of
American black bear home ranges in central Nevada. This wide-ranging
species can travel long distances and is capable of, and has been
documented, crossing desert valleys between mountain ranges in Nevada
(Beckmann and Lackey 2004, p. 271).
The petition asserts that American black bear habitat in western
Nevada (forested mountain ranges isolated by valleys) is characteristic
of the unique Great Basin ecosystem (Big Wildlife and NoBearHuntNV.org
2011, p. 13). American black bears are adaptable and are found in many
habitat types across North America (Bowers et al. 2004, p. 142; Big
Wildlife and NoBearHuntNV.org 2011, p. 7). The use of forested mountain
habitats by American black bears in Nevada is not unique (Zielinski et
al. 2005, p. 1385). Forested mountain ranges are not unique to Nevada,
nor do they terminate discretely at the State border. The Great Basin
covers a large geographic area in the western United States and
includes portions of the States of Oregon, California, Nevada, Utah,
and Idaho (70 FR 73190, December 9, 2005). This geographic area extends
well beyond the boundaries of Nevada. The Great Basin does not lie
wholly within the State of Nevada nor does it correspond to Nevada
State boundaries. The petition does not provide substantial
information, nor is there information available in our files, to
suggest that the American black bear in Nevada may be markedly separate
from other populations of American black bears outside of Nevada due to
physical or geographic reasons.
The petition does not present information to suggest there may be a
markedly separate population of American black bears in Nevada due to
physiological reasons. Additionally, we do not have information in our
files to indicate that the American black bear in Nevada may be
markedly separate from other American black bears outside of this area
due to physiological reasons.
Substantial information is not presented in the petition, nor is it
available in our files, to suggest there may be a markedly separate
population of American black bears in Nevada due to physical,
physiological, ecological, or behavioral differences as compared to
American black bears located in the Sierra Nevada of California and
elsewhere. Therefore, we determine, based on the information provided
in the petition and in our files that the American black bear
population in Nevada may not be markedly separate from other black bear
populations found outside of the State. Therefore, we conclude that the
black bear population in Nevada does not meet the discreteness
criterion of the 1996 DPS policy.
There are no international governmental boundaries associated with
this subspecies that are significant. The American black bear
population found in Nevada lies wholly within the United States.
Because this element is not relevant in this case for a finding of
discreteness, it was not considered in reaching this determination.
Significance
If a population segment is considered discrete under one or more of
the conditions described in our DPS policy, its biological and
ecological significance will be considered in light of Congressional
guidance that the authority to list DPSs be used ``sparingly'' while
encouraging the conservation of genetic diversity. In making this
determination, we consider available scientific evidence of the
discrete population segment's importance to the taxon to which it
belongs. Since precise circumstances are likely to vary considerably
from case to case, the DPS policy does not describe all the classes of
information that might be used in determining the biological and
ecological importance of a discrete population. However, the DPS policy
does provide four possible reasons why a discrete population may be
significant. As specified in the DPS policy (61 FR 4722), this
consideration of the population segment's significance may include, but
is not limited to, the following:
(1) Persistence of the discrete population segment in an ecological
setting unusual or unique to the taxon;
(2) Evidence that loss of the discrete population segment would
result in a significant gap in the range of a taxon;
[[Page 39674]]
(3) Evidence that the discrete population segment represents the
only surviving natural occurrence of a taxon that may be more abundant
elsewhere as an introduced population outside its historical range; or
(4) Evidence that the discrete population segment differs markedly
from other populations of the species in its genetic characteristics.
A population segment needs to satisfy only one of these criteria to
be considered significant. Furthermore, the list of criteria is not
exhaustive; other criteria may be used as appropriate.
Because we must find a population to be both discrete and
significant to qualify as a DPS, and we did not find the population to
be discrete, we will not address the potential significance of the
American black bear in Nevada to the remainder of the taxon, nor will
we evaluate the population's conservation status.
Conclusion of Distinct Population Segment Review
Based on the information provided in the petition and in our files,
we find that the petition does not provide substantial information to
indicate that the American black bear population in Nevada meets the
discreteness criterion of the DPS policy. Since both discreteness and
significance are required to satisfy the DPS policy, we have determined
that the American black bear population in Nevada does not qualify as a
DPS under our policy and, therefore, is not a listable entity under the
Act. As a result, no further analysis under the DPS policy is
necessary.
Finding
We reviewed the information presented in the petition, and we
evaluated that information in relation to information readily available
in our files. On the basis of our review, we find that neither the
petition, nor information readily available in our files, suggests that
the American black bear population in Nevada meets the criteria for
being discrete under our DPS policy. Available information from the
petition and our files does not suggest there may be a markedly
separate population of American black bears in Nevada compared with
other populations due to physical, physiological, ecological, or
behavioral differences. The American black bear in Nevada is not found
to be markedly separate from other American black bear populations
because it is not physically separate from other adjacent populations
due to various kinds of barriers, it is not genetically different and
does not demonstrate physiological or behavioral differences, nor does
it occur in ecological settings in Nevada that are dissimilar from
other areas occupied by the American black bear. Because the petition
does not present substantial information that the American black bear
in Nevada may be a DPS, we did not evaluate whether the information
contained in the petition regarding the conservation status was
substantial. We conclude that the American black bear in Nevada does
not satisfy the elements of being a DPS under our 1996 policy and,
therefore, is not a listable entity under section 3(16) of the Act.
We encourage interested parties to continue to gather data that
will assist with the conservation of the American black bear in Nevada.
If you wish to provide information regarding the American black bear in
Nevada, you may submit your information or materials to the State
Supervisor, Nevada Fish and Wildlife Office (see ADDRESSES), at any
time.
References Cited
A complete list of references cited is available on the Internet at
https://www.regulations.gov and upon request from the Nevada Fish and
Wildlife Office (see FOR FURTHER INFORMATION CONTACT).
Author
The primary authors of this notice are the staff of the Nevada Fish
and Wildlife Office (see ADDRESSES).
Authority
The authority for this action is the Endangered Species Act of
1973, as amended (16 U.S.C. 1531 et seq.).
Dated: June 19, 2012.
Daniel M. Ashe,
Director, U.S. Fish and Wildlife Service.
[FR Doc. 2012-16335 Filed 7-3-12; 8:45 am]
BILLING CODE 4310-55-P