Endangered and Threatened Wildlife and Plants; Proposed Revision of Special Regulation for the Central Idaho and Yellowstone Area Nonessential Experimental Populations of Gray Wolves in the Northern Rocky Mountains, 36942-36949 [07-3268]
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36942
Federal Register / Vol. 72, No. 129 / Friday, July 6, 2007 / Proposed Rules
week to before the hearing date, to allow
sufficient time to process requests.
Information regarding the proposal is
available in alternative formats upon
request.
Authority
The authority for this action is the
Endangered Species Act of 1973, as
amended (16 U.S.C. 1531 et seq.).
Dated: June 28, 2007.
Kevin Adams,
Acting Director, U.S. Fish and Wildlife
Service.
[FR Doc. 07–3273 Filed 7–2–07; 8:45 am]
BILLING CODE 4310–55–P
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
RIN 1018–AV39
Endangered and Threatened Wildlife
and Plants; Proposed Revision of
Special Regulation for the Central
Idaho and Yellowstone Area
Nonessential Experimental
Populations of Gray Wolves in the
Northern Rocky Mountains
Fish and Wildlife Service,
Interior.
ACTION: Proposed rule.
rmajette on PROD1PC64 with PROPOSALS
AGENCY:
SUMMARY: We, the U.S. Fish and
Wildlife Service (Service), propose
revisions to the 2005 special rule for the
central Idaho and Yellowstone area
nonessential experimental population of
the gray wolf (Canis lupus) in the
northern Rocky Mountains (NRM).
Specifically, this rule proposes to
modify the definition of ‘‘unacceptable
impacts’’ to wild ungulate populations
so that States and Tribes with Serviceapproved post-delisting wolf
management plans can better address
the impacts of a biologically recovered
wolf population on ungulate
populations and herds while wolves
remain listed. We also propose to
modify the 2005 special rule to allow
private citizens in States or on Tribal
lands with approved post-delisting wolf
management plans to take wolves that
are in the act of attacking their stock
animals or dogs. All other provisions of
the 2005 special rule, including the
process to obtain Service approval and
the conditions for reporting all wolf
take, would remain unchanged. As
under the existing terms of the 2005
special rule, these proposed
modifications would not apply with
respect to States or Tribes without
approved post-delisting wolf
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management plans and would not
impact wolves outside the Yellowstone
or central Idaho nonessential
experimental population areas. A draft
environmental assessment will be
prepared on this proposed action.
DATES: Comments from all parties on
both the proposal and the draft
environmental assessment must be
received by August 6, 2007. We will
hold three public hearings on this
proposed rule in July. See
SUPPLEMENTARY INFORMATION for the
dates, times, and locations.
ADDRESSES: If you wish to comment,
you may submit comments and
materials concerning this proposal,
identified by ‘‘RIN 1018–AV39,’’ by any
of the following methods:
1. You may mail or hand deliver
written comments to the U.S. Fish and
Wildlife Service, Western Gray Wolf
Recovery Coordinator, 585 Shepard
Way, Helena, Montana 59601;
2. You may send comments by
electronic mail (e-mail) directly to the
Service at WolfRuleChange@fws.gov.
Include ‘‘RIN number 1018–Av39’’ in
the subject line of the message. See the
Public Comments Solicited section
below for file format for electronic
filing; or
3. You may submit your comments
through the Federal e-Rulemaking
Portal—https://www.regulations.gov.
Follow the instructions for submitting
comments.
Comments and materials received, as
well as supporting documentation used
in preparation of this proposed action,
will be available for inspection
following the close of the comment
period, by appointment, during normal
business hours, at our Helena office (see
ADDRESSES).
FOR FURTHER INFORMATION CONTACT:
Edward E. Bangs, Western Gray Wolf
Recovery Coordinator, U.S. Fish and
Wildlife Service, at our Helena office
(see ADDRESSES) or telephone (406) 449–
5225, extension 204.
SUPPLEMENTARY INFORMATION:
Public Comments Solicited
We intend that any final action
resulting from this proposal will be as
accurate and as effective as possible.
Therefore, data, comments, new
information, or suggestions from the
public, other concerned governmental
agencies, the scientific community,
industry, or any other interested party
concerning this proposed rule are
hereby solicited. We particularly seek
comments concerning (1) our proposed
modifications to the 2005 experimental
population rule to allow private citizens
to take wolves in the act of attacking
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their stock animals or dogs; and (2) our
establishing a reasonable process for
States and Tribes with approved postdelisting wolf management plans to
allow removal of wolves that are
scientifically demonstrated to be
impacting ungulate populations to the
degree that they are not meeting
respective State and Tribal management
goals. We specifically ask for comments
regarding whether the proposed
modifications would reasonably address
conflicts between wolves and domestic
animals or wild ungulate populations;
would provide sufficient safeguards to
prevent misuse of the modified rule;
would provide an appropriate and
transparent public process that ensures
decisions are science-based; and would
provide adequate guarantees that wolf
recovery will not be compromised.
If you wish to comment, you may
submit your comments and materials
concerning this proposed rule by any
one of several methods, as listed above
in the ADDRESSES section. If you submit
comments by e-mail, please submit
them in ASCII file format and avoid the
use of special characters and
encryption. Please note that the e-mail
address will be closed at the termination
of the public comment period.
Our practice is to make comments,
including names and home addresses of
respondents, available for public review
during regular business hours. Before
including your address, phone number,
e-mail address, or other personal
identifying information in your
comment, you should be aware that
your entire comment—including your
personal identifying information—may
be made publicly available at any time.
While you can ask us in your comment
to withhold your personal identifying
information from public review, we
cannot guarantee that we will be able to
do so. Comments and materials received
will be available for public inspection,
by appointment, during normal business
hours (see ADDRESSES section).
Peer Review
In accordance with our joint policy
published in the Federal Register on
July 1, 1994 (59 FR 34270), and the
Office of Management and Budget’s
(OMB) Final Information Quality
Bulletin for Peer Review, dated
December 16, 2004, we will seek
independent review of the science in
this rule. The purpose of such review is
to ensure that our final rule is based on
scientifically sound data, assumptions,
and analyses. We will send peer
reviewers copies of this proposed rule
immediately following publication in
the Federal Register. We will invite
these peer reviewers to comment,
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during the public comment period, on
the specific assumptions and
conclusions regarding the proposed
rule.
We will take into consideration all
comments, including peer review
comments, and any additional
information received during the
comment period on this proposed rule
during the preparation of a final
rulemaking. Accordingly, the final
decision may differ from this proposal.
Public Hearings
Three open houses will be held on:
July 17, 2007, Tuesday at Cody
Auditorium Facility, 1240 Beck
Avenue, Cody, Wyoming; open house
12:30 p.m. to 1:30 p.m. and public
hearing 1:30 p.m. to 3:30 p.m.;
July 18, 2007, Wednesday at Jorgenson’s
Inn & Suites, 1714 11th Avenue,
Helena, Montana; open house 6 p.m.
to 7 p.m. and public hearing 7 p.m.
to 9 p.m.; and
July 19, 2007, Thursday at Boise
Convention Center on the Grove, 850
Front Street, Boise, Idaho; open house
6 p.m. to 7 p.m. and public hearing
7 p.m. to 9 p.m.
Anyone wishing to make an oral
statement for the record is encouraged
to provide a written copy of their
statement and present it to us at the
hearing. In the event there is a large
attendance, the time allotted for oral
statements may be limited. Those that
wish to speak must sign up at the open
houses and hearing. Oral and written
statements receive equal consideration.
There are no limits on the length of
written comments submitted to us. If
you have any questions concerning the
public hearings, please contact Sharon
Rose (303) 236–4580. Persons needing
reasonable accommodations in order to
attend and participate in the public
hearing in Idaho should contact Joan
Jewett (503) 231–6211, and for hearings
in Montana or Wyoming, please contact
Sharon Rose at (303) 236–4580, as soon
as possible in order to allow sufficient
time to process requests. Please call no
later than 1 week before the hearing
date. Information regarding the proposal
is available in alternative formats upon
request.
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Previous Federal Actions
In 1974, four subspecies of gray wolf
were listed as endangered including the
northern Rocky Mountains gray wolf
(Canis lupus irremotus), the eastern
timber wolf (C. l. lycaon) in the northern
Great Lakes region, the Mexican wolf (C.
l. baileyi) in Mexico and the
southwestern United States, and the
Texas gray wolf (C. l. monstrabilis) of
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Texas and Mexico (39 FR 1171, January
4, 1974). In 1978, we published a rule
(43 FR 9607, March 9, 1978) relisting
the gray wolf as endangered at the
species level (C. lupus) throughout the
conterminous 48 States and Mexico,
except for Minnesota, where it was
reclassified as threatened. In 2007, we
published a rule (72 FR 6052) which
delisted the Western Great Lakes
population of wolves that included all
of Minnesota, Wisconsin, Michigan, and
parts of North and South Dakota, Iowa,
Illinois, Indiana, and Ohio. The
northern Rocky Mountain Wolf
Recovery Plan was approved in 1980
(Service 1980, p. i) and revised in 1987
(Service 1987, p. i).
On November 22, 1994, we designated
unoccupied portions of Idaho, Montana,
and Wyoming as two nonessential
experimental population areas for the
gray wolf under section 10(j) of the
Endangered Species Act of 1973, as
amended (Act) (59 FR 60252, November
22, 1994; 59 FR 60266, November 22,
1994). One area was the Yellowstone
National Park experimental population
area which included all of Wyoming,
and parts of southern Montana and
eastern Idaho (59 FR 60252, November
22, 1994). The other was the central
Idaho experimental population area that
included most of Idaho and parts of
southwestern Montana (59 FR 60266,
November 22, 1994). In 1995 and 1996,
we reintroduced wolves from
southwestern Canada into these areas
(Bangs and Fritts 1996, pp. 407–409;
Fritts et al. 1997, p. 7; Bangs et al. 1998,
pp. 785–786). This reintroduction and
accompanying management programs
greatly expanded the numbers and
distribution of wolves in the northern
Rocky Mountains. At the end of 2000,
the northern Rocky Mountain
population first met its numerical and
distributional recovery goal of a
minimum of 30 breeding pairs and over
300 wolves well-distributed among
Montana, Idaho, and Wyoming (68 FR
15804, April 1, 2003; Service et al. 2001,
Table 4). This minimum recovery goal
was again exceeded in 2001, 2002, 2003,
2004, 2005, and 2006 (Service et al.
2002–2006, Table 4).
On January 6, 2005, we published a
revised nonessential experimental
population special rule increasing
management flexibility for these
recovered populations (70 FR 1286,
January 6, 2005). For additional detailed
information on previous Federal actions
see the 1994 and 2005 special rules (59
FR 60252, November 22, 1994; 59 FR
60266, November 22, 1994; 70 FR 1286,
January 6, 2005), the 2003
reclassification rule (68 FR 15804, April
1, 2003), the Advanced Notice of
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Proposed Rulemaking to designate the
NRM gray wolf population as a Distinct
Population Segment (DPS) and remove
the Act’s protections for this population
(71 FR 6634, February 8, 2006) and the
2007 proposal to designate the NRM
gray wolf population as a DPS and
remove the Act’s protections for this
population (i.e., delist) (72 FR 6106,
February 8, 2007).
Background
Given the recovered status of the wolf
population and the practical limitations
on implementing the current
nonessential experimental rules, we
propose to slightly modify the 2005 rule
(70 FR 1286, January 6, 2005).
Additional background on nonessential
experimental rules implemented under
section 10(j) of the Act can be found in
the 1994 rules (59 FR 60252, November
22, 1994; 59 FR 60266, November 22,
1994) and the 2005 rule (70 FR 1286,
January 6, 2005).
Addressing Unacceptable Impacts on
Wild Ungulate Populations—States and
Tribes have the expertise to make
determinations of unacceptable impacts
to ungulate populations. Both the 1994
Environmental Impact Statement for
wolf reintroduction (Service 1994, pp. 6,
8) and the 1994 nonessential
experimental special rules addressed
the potential impact of wolf restoration
on State and Tribal objectives for wild
ungulate management. Specifically, the
1994 rules stated, ‘‘Potentially affected
States and Tribes may capture and
translocate wolves to other areas within
an experimental population area as
described in paragraph (i)(7), Provided,
the level of wolf predation is negatively
impacting localized ungulate
populations at an unacceptable level.
Such translocations cannot inhibit wolf
population recovery. The States and
Tribes will define such unacceptable
impacts, how they would be measured,
and identify other possible mitigation in
their State or Tribal wolf management
plans. These plans must be approved by
the Service before such movement of
wolves may be conducted’’ (59 FR
60264, November 22, 1994; 59 FR
60279, November 22, 1994). The
‘‘plans’’ referenced in the 1994 rules
related to the management of the listed
nonessential experimental wolves.
Two examples of conflicts that might
warrant relocation outlined in the
preamble of the 1994 rules were ‘‘(1)
when wolf predation is dramatically
affecting prey availability because of
unusual habitat or weather conditions;
and (2) when wolves cause prey to move
onto private property and mix with
livestock, increasing potential conflicts’’
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(59 FR 60257, November 22, 1994; 59
FR 60272, November 22, 1994).
No such State plans for managing
listed wolves were adopted; therefore,
no wolves were ever moved for ungulate
conflicts under the 1994 regulations.
Only Wyoming had requested that
wolves be moved by the Service. In that
situation, Wyoming reported that
wolves were occasionally chasing elk
with high rates of brucellosis infection
off winter elk feed grounds causing
them to temporarily mix more
frequently with nearby domestic cattle.
The Service suggested that the State
identify the sites in Wyoming where
they would prefer the wolves to be
moved, but no sites were ever identified
and no wolves were ever moved.
On January 6, 2005, we finalized a
new special rule that allowed greater
management flexibility for managing a
recovered wolf population in the
experimental population area of States
and Tribal reservations for States and
Tribes which had Service approved,
post-delisting wolf management plans
(70 FR 1286). It also allowed additional
opportunities for the public to take
wolves in order to protect their private
property.
The 2005 rule’s provision for ‘‘take in
response to wild ungulate impacts’’
states at 70 FR 1308 that:
‘‘If wolf predation is having an
unacceptable impact on wild ungulate
populations (deer, elk, moose, bighorn sheep,
mountain goats, antelope, or bison) as
determined by the respective State or Tribe,
a State or Tribe may lethally remove the
wolves in question.
(A) In order for this provision to apply, the
States or Tribes must prepare a science-based
document that:
(1) Describes what data indicate that
ungulate herd is below management
objectives, what data indicate the impact of
wolf predation on the ungulate population,
why wolf removal is a warranted solution to
help restore the ungulate herd to State or
Tribal management objectives, the level and
duration of wolf removal being proposed,
and how ungulate population response to
wolf removal will be measured;
(2) Identifies possible remedies or
conservation measures in addition to wolf
removal; and
(3) Provides an opportunity for peer review
and public comment on their proposal prior
to submitting it to the Service for written
concurrence.
(B) We must determine that such actions
are scientifically based and will not reduce
the wolf population below recovery levels
before we authorize lethal wolf removal.’’
The 2005 rule authorized lethal take
because we recognized that the wolf
population had exceeded its recovery
goals, that extra management flexibility
was required to address conflicts given
the recovered status of the population,
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that most of the suitable wolf habitat in
Montana, Idaho, and Wyoming was
occupied by resident wolf packs
(Oakleaf et al. 2006), and that absent
high-quality unoccupied suitable
habitat, wolf translocations were likely
to fail (70 FR 1294, January 6, 2005;
Bradley et al. 2005, p. 1506).
The 2005 rule’s definition of
‘‘Unacceptable impact’’ is a ‘‘State or
Tribally-determined decline in a wild
ungulate population or herd, primarily
caused by wolf predation, so that the
population or herd is not meeting
established State or Tribal management
goals. The State or Tribal determination
must be peer-reviewed and reviewed
and commented on by the public, prior
to a final determination by the Service
that an unacceptable impact has
occurred, and that wolf removal is not
likely to impede wolf recovery’’ (70 FR
1307, January 6, 2005).
In our definition of ‘‘Unacceptable
impact’’ in the 2005 rule, we set a
threshold that has not provided the
intended flexibility to allow States and
Tribes to resolve conflicts between
wolves and ungulate populations.
Current information does not indicate
that wolf predation alone is likely to be
the primary cause of a reduction of any
ungulate population in Montana, Idaho,
or Wyoming (Bangs et al. 2004, pp. 89–
100). There are no populations of wild
ungulates in Montana, Idaho, or
Wyoming where wolves are the sole
predator. Wolf predation is unlikely to
impact ungulate population trends
substantially unless other contributing
factors are in operation, such as habitat
quality and quantity (National Research
Council 1997, pp. 185–186; Mech and
Peterson 2003, p. 159), other predators
(bear predation on neonates) (Barber et
al. 2005, p. 42–43; Smith et al. 2006, p.
vii), high harvest by hunters (Vucetich
et al. 2005, p. 259; White and Garrott
2005, p. 942; Evans et al. 2006, p. 1372;
Hamlin 2006, p. 27–32), weather (Mech
and Peterson 2003, pp. 138–139), and
other factors (Pletscher et al. 1991, pp.
545–548; Garrott et al. 2005, p. 1245;
Smith et al. 2006, pp. 246–250).
However, in combination with any of
these factors, wolf predation can have a
substantial impact to some wild
ungulate herds (National Research
Council 1997, p. 183; Mech and
Peterson 2003, pp. 155–157; Evans et al.
2006, p. 1377) with the potential of
reducing them below State and Tribal
herd management objectives.
The unattainable nature of the
threshold set in the 2005 rule became
apparent soon after its completion. In
2005, the State of Idaho submitted a
proposal to the Service that indicated
wolf predation was impacting the
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survival of adult cow elk in the
Clearwater area of central Idaho and that
the elk population was below State
management objectives (Idaho Fish and
Game 2006). In the Clearwater proposal,
the State of Idaho and the peer
reviewers clearly concluded that wolf
predation was not ‘‘primarily’’ the cause
of the elk population’s decline, but was
one of the major factors maintaining the
elk herd’s status below State
management objectives. Declining
habitat quality due to forest maturation
was the primary factor affecting the
herd’s status, but black bear predation
on young elk calves, mountain lion
predation on adults, and the harsh
winter in 1996 to 97 also were major
factors. Data also clearly indicated that
wolf predation was one of the major
causes of mortality of adult female elk,
which contributed to the elk herd
remaining below State management
objectives. After discussions with the
Service, Idaho put their proposal on
hold because the proposal did not meet
the regulatory standard for an
‘‘Unacceptable impact’’ set by the 2005
special rule.
We are now proposing to redefine the
term ‘‘Unacceptable impact’’ to achieve
the originally intended management
flexibility. Specifically, we propose to
define ‘‘Unacceptable impact’’ as ‘‘State
or Tribally determined impact to a wild
ungulate population or herd, with
wolves as one of the major causes of the
population or herd not meeting
established State or Tribal population or
herd management goals. The State or
Tribal determination must be peerreviewed and reviewed and commented
on by the public prior to a final
determination by the Service that an
unacceptable impact has occurred and
that wolf removal is not likely to
impede wolf recovery.’’ This definition
expands the potential impacts for which
wolf removal might be warranted
beyond direct predation or those
causing immediate population declines.
It would, in certain circumstances,
allow wolf pack removal when wolves
are a major cause of the population or
herd not meeting established State or
Tribal population or herd management
goals. Management goals might include
cow/calf ratios, movements, use of key
feeding areas, survival rates, behavior,
nutrition, and other factors.
Under this proposal, as in the 2005
rule, science-based proposals from a
State or Tribe with an approved postdelisting wolf management plan would
have to undergo both public and peer
review. Based on that peer review and
public comment, the State or Tribe
would finalize the plan and then submit
it to the Service for a final
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determination. The Service expects the
following to be addressed in the State or
Tribal proposal: (1) What data indicate
that the ungulate herd is below
management objectives; (2) what data
indicate impact by wolf predation on
the ungulate population; (3) why wolf
removal is a warranted solution to help
restore the ungulate herd to State or
Tribal management objectives; (4) the
level and duration of wolf removal
being proposed; (5) how ungulate
population response to wolf removal
will be measured; and (6) possible
remedies or conservation measures in
addition to wolf removal. Before wolf
removals can be authorized, the Service
must determine if the State or Tribe
followed the rule’s procedures for
developing a proposal to remove wolves
in response to unacceptable impacts; if
the proposal meets the definition of
unacceptable impact; if the science
presented supports the recommended
action; and if the proposal is sciencebased.
The recovery goal for the NRM wolf
population requires that it be comprised
of at least 30 breeding pairs and 300
wolves that are equitably distributed in
potentially suitable habitat in Montana,
Idaho, and Wyoming. To ensure this
goal is achieved, each of the three States
(Wyoming, Montana, and Idaho)
committed to manage for an equitable
distribution of the overall population
and assume a management target of 15
breeding pairs in mid-winter within
each State. The 15 breeding pair
management target was not intended to
be the minimum goal for each State. It
was an objective so that each State’s
management would provide a
reasonable cushion to ensure each
State’s share of the wolf population did
not fall below the 10 breeding pairs
requirement and that the 30 breeding
pairs minimum would always be met or
exceeded.
While this change will likely result in
more wolf control than is currently
occurring, we propose to establish
controls to ensure that wolf control for
ungulate management purposes would
not undermine recovery goals.
Specifically, before any lethal control of
wolf populations can be authorized, we
must determine that such actions will
not reduce the wolf population in the
State below 20 breeding pairs and 200
wolves. This assures that the wolf
population is large enough to easily
rebound from such removal, that a large
safety margin is provided against
unseen mortality events that might
occur after such removal, and that a
substantial margin of safety is provided
to ensure that recovery objectives would
never be compromised. This limit is a
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necessary and advisable precaution
while wolves remain listed to ensure the
conservation of the species given the
additional take that might be authorized
pursuant to this proposed rule. Once
delisted, Montana, Idaho, and Wyoming
will manage for no less than 15 breeding
pairs.
By the end of 2006, the northern
Rocky Mountain wolf population was
estimated to contain 1,300 wolves in 86
breeding pairs (nearly three times the
minimum numeric recovery goal for
breeding pairs and more than four times
the minimum population goal), and for
the 7th consecutive year it exceeded
minimum recovery levels. Montana had
an estimated 316 wolves in 21 breeding
pairs, Idaho had 673 wolves in 40
breeding pairs, and Wyoming had 311
wolves in 25 breeding pairs. Wolf
biology allows for rapid recovery from
severe disruptions. After severe
declines, wolf populations can more
than double in just 2 years if mortality
is reduced; and increases of nearly 100
percent per year have been documented
in low-density suitable habitat (Fuller et
al. 2003, pp. 181–183; Service et al.
2007, Table 4). The literature suggests
that wolf populations can maintain
themselves despite a sustained humancaused mortality rate of 30 percent or
more per year (Keith 1983, p. 66; Fuller
et al. 2003, pp. 182–184).
Our data indicate that the humancaused mortality rate in the adult-sized
segment of the northern Rocky
Mountain wolf population was nearly
26 percent per year from 1994 to 2004
(Smith 2005), and that the wolf
population still continued to expand at
about 26 percent annually (Service et al.
2007, Table 4). This data indicates that
the current annual mortality rate of
about 26 percent in the adult portion of
the wolf population could be nearly
doubled and the wolf population could
still maintain itself at current levels.
Collectively, these factors mean that
wolf populations are quite resilient to
human-caused mortality if it is
regulated.
The wolf population now occupies
most of the suitable wolf habitat in the
northern Rocky Mountains (72 FR 6106–
6139, February 8, 2007; Oakleaf et al.
2006, p. 559). The population is
unlikely to significantly expand its
overall distribution beyond the outer
boundaries of the current population
because little unoccupied suitable
habitat is available. Given current
population density and these habitat
limitations, we believe the overall
numbers of wolf breeding pairs and
numbers of wolves cannot continue to
sustain a growth rate of 26 percent per
year. Thus, we do not believe any
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36945
increased take as a result of this rule, if
finalized, would have an impact on the
recovered status of the northern Rocky
Mountain wolf population in Montana,
Idaho, or Wyoming, as long as it
remains managed under a science-based
plan.
Addressing Take To Protect Stock
Animals and Dogs—The 1994
experimental population rules stated
that ‘‘any livestock producers on their
private land may take (including to kill
or injure) a wolf in the act of killing,
wounding, or biting livestock’’ (defined
as cattle, sheep, horses, and mules) (59
FR 60264, November 22, 1994; 59 FR
60279, November 22, 1994). Similar
provisions applied to producers on
public land if they obtained a permit
from the Service (59 FR 60264,
November 22, 1994; 59 FR 60279,
November 22, 1994).
The 2005 special rule expanded this
provision in States with approved postdelisting wolf management plans to
allow private citizens to also lethally
take wolves that were ‘‘in the act of
attacking’’ their livestock and dogs on
private land and any livestock or
herding and guarding dogs on active
public grazing allotments or special use
areas. ‘‘In the act of attacking’’ is
defined in 50 CFR 17.84(n)(3) as ‘‘the
actual biting, wounding, grasping, or
killing of livestock or dogs, or chasing,
molesting, or harassing by wolves that
would indicate to a reasonable person
that such biting, wounding, grasping, or
killing of livestock or dogs is likely to
occur at any moment.’’ Such incidents
had to be reported to the Service or our
designated agent(s) within 24 hours and
physical evidence of such an attack had
to be present.
This rule proposes to add a new
provision for lethal take of wolves in
States with approved post-delisting wolf
management plans when in defense of
‘‘stock animals’’ (defined as ‘‘a horse,
mule, donkey, or llama used to transport
people or their possessions’’) or dogs.
Specifically, the proposed modification
states that ‘‘any legally present private
citizen on private or public land may
immediately take a wolf that is in the
act of attacking the individuals’ legally
present stock animal or dog, provided
there is no evidence of intentional
baiting, feeding, or deliberate attractants
of wolves. The citizen must be able to
provide evidence of stock animals or
dogs recently (less than 24 hours)
wounded, harassed, molested, or killed
by wolves, and we or our designated
agents must be able to confirm that the
stock animals or dogs were wounded,
harassed, molested, or killed by wolves.
To preserve evidence that the take of a
wolf was conducted according to this
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rule, the carcass of the wolf and the area
surrounding should not be disturbed.
The take of any wolf without such
evidence of a direct and immediate
threat may be referred to the appropriate
authorities for prosecution.’’
Since 1995, only 43 wolves (about 8
percent of the 538 wolves legally
removed in agency-authorized control
actions) have been legally killed by
private citizens in defense of their
private property or by shoot-on-sight
permits as authorized by either the 1994
or 2005 experimental population special
rules. There has been no documentation
of wolf depredations on stock animals
that were accompanied by their owners
in the past 12 years, but a few instances
of stock animals being spooked by
wolves have been reported. While this
proposed revision will provide
additional opportunity for private
citizens to protect their private property,
we expect minor impacts on the wolf
population.
Ninety-one dogs have been confirmed
to be killed by wolves from 1987 to 2007
(Service et al. 2007, Table 5). No pet
dogs have been confirmed to be killed
by wolves while they were accompanied
by their owners, and no wolves have
been killed solely to protect dogs.
However, 35 hunting hounds have been
killed by wolves, primarily on public
land. In only a few of those instances,
the hounds’ owners were close enough
that they might have been able to better
protect their dogs by shooting at the
wolves involved. We expect that take of
wolves involved in conflicts with pet
dogs or hunting hounds would be rare.
This proposed modification would
allow for private citizens to protect their
dogs from wolf attack while not
meaningfully increasing the rate of wolf
removal.
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Required Determinations
Regulatory Planning and Review—In
accordance with the criteria in
Executive Order 12866, this rule is a
significant regulatory action and subject
to OMB review. An economic analysis
is not required because this rule will
result in only minor and positive
economic effects on a small percentage
of private citizens in Idaho and
Montana, and possibly Wyoming if it
develops an approved post-delisting
wolf management plan.
(a) This regulation does not have an
annual economic effect of $100 million
or adversely affect an economic sector,
productivity, jobs, the environment, or
other units of government. A brief
assessment to clarify the costs and
benefits associated with this rule
follows.
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Costs Incurred—Under the 2005
special rule, which this rule proposes to
modify, management of wolves by
States or Tribes with Service-approved
post-delisting wolf management plans is
voluntary. Therefore, associated costs
would be discretionary. While we do
not quantify these expected
expenditures, these costs may consist of
staff time and salary as well as
transportation and equipment necessary
to control wolves unacceptably
impacting ungulate populations or
herds.
We have funded State and Tribal wolf
monitoring, research, and management
efforts for gray wolves in Montana,
Idaho, and Wyoming, and intend to
continue to do so as long as wolves are
listed. For the past several years
Congress has targeted funding for wolf
management to Montana, Idaho, and
Wyoming, and the Nez Perce. In
addition, Federal grant programs are
available that fund wildlife management
programs by the States and Tribes.
Benefits Accrued—The objectives of
the proposed rule change are (1) to
allow States and Tribes with Serviceapproved post-delisting wolf
management plans to address the
unacceptable impacts of a biologically
recovered wolf population to ungulate
populations and herds, and (2) to allow
private citizens in States or on Tribal
lands with approved post-delisting wolf
management plans to take wolves that
are in the act of attacking their stock
animals or dogs. Allowing wolf removal
in response to unacceptable impacts
will help maintain ungulate populations
or herds at or above State or Tribal
objectives. Balancing the needs of
wolves and elk provides substantial and
sustainable economic benefits. Allowing
take of wolves in the act of attacking
stock animals or dogs would have a
beneficial economic impact by allowing
citizens to protect such private property.
This proposed amendment could
prevent the need for these citizens to
replace and retrain these animals. An
additional potential benefit may be a
lower level of illegal take of wolves due
to higher local public tolerance of
wolves resulting from reduced conflicts
between wolves and humans.
(b) This regulation does not create
inconsistencies with other agencies’
actions. It is exactly the same as the
nonessential experimental population
rules currently in effect regarding
agency responsibilities under section 7
of the Act. This rule reflects continuing
success in recovering the gray wolf
through long-standing cooperative and
complementary programs by a number
of Federal, State, and Tribal agencies.
Implementation of Service-approved
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State or Tribal post-delisting wolf
management plans supports these
existing partnerships.
(c) This rule will not alter the
budgetary effects or entitlements, grants,
user fees, or loan programs, or the rights
and obligations of their recipients
because we do not foresee any new
impacts or restrictions to existing
human uses of lands in Idaho or
Montana as a result of this rule, nor in
Wyoming or any Tribal reservations that
remain under the 1994 10(j) rules.
(d) This rule does not raise novel legal
or policy issues. Instead it proposes to
reduce the restrictions on take of
wolves. Similar take provisions are
already in place through the 1994 and
2005 special rules (59 FR 60252,
November 22, 1994; 59 FR 60266,
November 22, 1994; 70 FR 1286, January
6, 2005). No new novel legal or policy
issues are raised by the amendments
offered in this proposed rule.
Regulatory Flexibility Act (5 U.S.C. 601
et seq.)
Under the Regulatory Flexibility Act
(5 U.S.C. 601 et seq., as amended by the
Small Business Regulatory Enforcement
Fairness Act (SBREFA) of 1996),
whenever a Federal agency is required
to 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.
The SBREFA amended the Regulatory
Flexibility Act to require Federal
agencies to provide a statement of the
factual basis for certifying that a rule
will not have a significant economic
impact on a substantial number of small
entities. The SBREFA also amended the
Regulatory Flexibility Act to require a
certification statement. Based on the
information that is available to us at this
time, we certify that this regulation will
not have a significant economic impact
on a substantial number of small
entities. The following discussion
explains our rationale.
The majority of wolves in the West
are currently protected under the
nonessential experimental population
designations that cover Wyoming, most
of Idaho, and southern Montana that
treat wolves as a threatened species.
Special regulations exist for these
experimental populations that currently
allow government employees and
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designated agents, as well as livestock
producers and private citizens, to take
problem wolves. This proposed
regulation modification does not change
the nonessential experimental
designation, but does contain additional
special regulations that allow States and
Tribes with approved post-delisting
wolf management plans more flexibility
in managing nonessential experimental
wolves.
These changes are applicable only
where States or Tribes (on Tribal
reservations) that have an approved
post-delisting management plan for gray
wolves. Within the northern Rocky
Mountain gray wolf population’s range,
only the States of Idaho and Montana
have approved plans. Therefore, the
regulation is expected to result in a
small reduction of economic losses to
some private citizens in States with
approved post-delisting wolf
management plans (i.e., Idaho and
Montana) within the boundary of the
nonessential experimental populations
of the northern Rocky Mountain gray
wolf population (Central Idaho
nonessential experimental population
area and Yellowstone nonessential
experimental population area) (59 FR
60252, November 22, 1994; 59 FR
60266, November 22, 1994).
In anticipation of the possible
delisting the northern Rocky Mountain
gray wolf population, we have worked
closely with States to ensure that their
plans provide the protection and
flexibility necessary to manage wolves
at or above recovery levels after
delisting. Approved plans are those
plans that have passed peer review and
Service scrutiny aimed at ensuring that
the requirements under the Act are met
and that recovery levels are maintained.
It is appropriate for States that have met
this approval standard to manage
wolves prior to delisting for several
reasons. States with approved postdelisting wolf management plans
(Montana and Idaho) worked with their
elected officials and public to develop
biologically and socially accepted State
regulatory frameworks to conduct wolf
management. They have already
assumed an important role in the
management of this species and have
developed extensive field experience
and expertise, garnered considerable
public trust, and exceeded the goals for
recovery. A gradual transfer of
responsibilities while the wolves are
protected under the Act provides an
adjustment period for the State wildlife
agencies, Federal agencies, and Tribes to
work out any unforeseen issues that
may arise.
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Small Business Regulatory Enforcement
Fairness Act
other Federal, State, or local government
agencies to carry out specific activities.
This regulation is not a major rule
under 5 U.S.C. 801 et seq., the SBREFA.
(a) This regulation will not have an
annual effect on the economy of $100
million or more and is fully expected to
have no significant economic impacts.
The proposed regulation further reduces
the effect that wolves will have on a few
private citizens by increasing the
opportunity for them to protect their
stock animals and dogs. Since there are
so few small businesses impacted by
this regulation, the combined economic
effects are minimal.
(b) This regulation will not cause a
major increase in costs or prices for
consumers, individual industries,
Federal, State, or local government
agencies, or geographic regions and will
impose no additional regulatory
restraints in addition to those already in
operation.
(c) This regulation will not have
significant adverse effects on
competition, employment, investment,
productivity, innovation, or the ability
of United States-based enterprises to
compete with foreign-based enterprises.
Based on the analysis of identified
factors, we have determined that no
individual industries within the United
States will be significantly affected and
that no changes in the demography of
populations are anticipated. The intent
of this special rule is to facilitate and
continue existing commercial activities
while providing for the conservation of
species by better addressing the
concerns of affected landowners and the
impacts of a biologically recovered wolf
population.
Takings (Executive Order 12630)
In accordance with Executive Order
12630, this rule will not have significant
implications concerning taking of
private property by the Federal
Government. This rule will substantially
advance a legitimate government
interest (conservation and recovery of
listed species) and will not present a bar
to all reasonable and expected beneficial
use of private property. Because this
proposed rule change pertains only to
the relaxation of restrictions on lethal
removal of wolves, it would not result
in any takings of private property.
Unfunded Mandates Reform Act
The 2005 special rule, which this
proposed rule suggests amending,
defines a process for voluntary and
cooperative transfer of management
responsibilities for a listed species back
to the States. Therefore, in accordance
with the Unfunded Mandates Reform
Act (2 U.S.C. 1501, et seq.):
(a) This rule will not ‘‘significantly or
uniquely’’ affect small governments. A
Small Government Agency Plan is not
required. As stated above, this
regulation will result in only minor
positive economic effects for a very
small percentage of livestock producers.
(b) This rule 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.
This rule is not expected to have any
significant economic impacts nor will it
impose any unfunded mandates on
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Federalism (Executive Order 13132)
This proposed rule maintains the
existing relationship between the States
and the Federal Government. The State
wildlife agencies in Montana, Idaho,
and Wyoming requested that we
undertake this rulemaking in order to
assist the States in reducing conflicts
with local landowners and returning
wolf management to the States or
Tribes. We have cooperated with the
States in preparation of this rule.
Maintaining the recovery goals for these
wolves will contribute to their eventual
delisting and their return to State
management. Utilizing the 2005 special
rule, which this rule proposes to
modify, is voluntary. This rule will not
have substantial direct effects on the
States, on the relationship between the
States and the Federal Government, or
on the distribution of power and
responsibilities among the various
levels of government. No intrusion on
State policy or administration is
expected; roles or responsibilities of
Federal or State governments will not
change; and fiscal capacity will not be
substantially directly affected.
Therefore, this rule does not have
significant Federalism effects or
implications to warrant the preparation
of a Federalism Assessment pursuant to
the provisions of Executive Order
13132.
Civil Justice Reform (Executive Order
12988)
In accordance with Executive Order
12988, the Department of the Interior
has determined that this rule does not
unduly burden the judicial system and
meets the applicable standards provided
in sections 3(a) and 3(b)(2) of the order.
Paperwork Reduction Act
The OMB regulations at 5 CFR 1320,
which implement provisions of the
Paperwork Reduction Act (44 U.S.C.
3501 et seq.) require that Federal
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agencies obtain approval from OMB
before collecting information from the
public. 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
control number. This rule does not
contain any new collections of
information other than those permit
application forms already approved
under the Paperwork Reduction Act, 44
U.S.C. 3501 et seq., and assigned OMB
clearance number 1018–0095.
National Environmental Policy Act
In compliance with all provisions of
the National Environmental Policy Act
(NEPA), we are analyzing the impact of
this rule modification and will
determine if there are any new
significant impacts or effects caused by
this rule. A draft environmental
assessment will be prepared on this
proposed action and will be available
for public inspection and comments
when completed. All appropriate NEPA
documents will be finalized before this
rule is finalized.
Government-to-Government
Relationship With Tribes (Executive
Order 13175)
In accordance with the President’s
memorandum of April 29, 1994,
‘‘Government-to-Government Relations
with Native American Tribal
Governments’’ (59 FR 22951), Executive
Order 13175, and 512 DM 2, we have
been coordinating with affected Tribes
within the experimental population
areas of Montana, Idaho, and Wyoming
on this rule. We will fully consider all
of the comments on the proposed
special regulations that are submitted by
Tribes and Tribal members during the
public comment period and will attempt
to address those concerns, new data,
and new information where appropriate.
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Energy Supply, Distribution or Use
(Executive Order 13211)
On May 18, 2001, the President issued
Executive Order 13211 requiring
agencies to prepare Statements of
Energy Effects when undertaking certain
actions that significantly affect energy
supply, distribution, and use. This rule
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.
Clarity of the Rule
Executive Order 12866 requires
agencies to write regulations that are
easy to understand. We invite comments
on how to make this proposal easier to
understand, including answers to
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questions such as the following: Are the
requirements in the document clearly
stated? Does the rule contain technical
language or jargon that interferes with
the clarity? Does the format of the rule
(grouping and order of sections, use of
headings, paragraphing, etc.) aid or
reduce its clarity? And is the
description of the proposed rule in the
SUPPLEMENTARY INFORMATION section of
the preamble helpful in understanding
the proposed rule? What else could we
do to make the rule easier to
understand? We requested that any
comments about how we could make
this rule easier to understand be sent
to—Office of Regulatory Affairs,
Department of the Interior, Room 7229,
1849 C Street, NW., Washington, DC
20240. People also could e-mail
comments to Exsec@ios.doi.gov. We will
review all public comments and
incorporate them in the final rule to
make it easier to understand.
References Cited
A complete list of all references cited
in this rulemaking is available upon
request from our Helena office (see
ADDRESSES section).
List of Subjects in 50 CFR Part 17
Endangered and threatened species,
Exports, Imports, Reporting and
recordkeeping requirements, and
Transportation.
Proposed Regulation Promulgation
Accordingly, we propose to amend
part 17, subchapter B of chapter I, title
50 of the Code of Federal Regulations,
as set forth below:
PART 17—[AMENDED]
1. The authority citation for part 17
continues to read as follows:
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.
2. Amend § 17.84 by amending
paragraph (n) as follows:
a. In paragraph (n)(3), revise the term
‘‘unacceptable impact’’ and, in
alphabetical order, add the terms ‘‘stock
animal’’ and ‘‘ungulate population or
herd’’, to read as set forth below; and
b. In paragraph (n)(4), revise the first
sentence following the heading and
paragraph (n)(4)(v)(B), and add
paragraph (n)(4)(xiii), to read as set forth
below.
§ 17.84
Special rules—vertebrates.
*
*
*
(n) * * *
(3) * * *
*
*
*
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*
*
*
*
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Stock animal—A horse, mule,
donkey, or llama used to transport
people or their possessions.
Unacceptable impact—State or
Tribally determined impact to a wild
ungulate population or herd, with
wolves as one of the major causes of the
population or herd not meeting
established State or Tribal population or
herd management goals. The State or
Tribal determination must be peerreviewed and reviewed and commented
on by the public, prior to a final
determination by the Service that an
unacceptable impact has occurred, and
that wolf removal is not likely to
impede wolf recovery.
Ungulate population or herd—An
assemblage of wild ungulates living in
a given area.
*
*
*
*
*
(4) Allowable forms of take of gray
wolves. The following activities, only in
the specific circumstances described
under this paragraph (n)(4), are allowed:
Opportunistic harassment; intentional
harassment; take on private land; take
on public land; take in response to
impacts on wild ungulate populations;
take in defense of human life; take to
protect human safety; take by
designated agents to remove problem
wolves; incidental take; take under
permits; take per authorizations for
employees of designated agents; take for
research purposes; and take to protect
stock animals and dogs. * * *
*
*
*
*
*
(v) * * *
(B) We must determine that such
actions are science-based and will not
reduce the wolf population in the State
below 20 breeding pairs and 200 wolves
before we authorize lethal wolf removal.
*
*
*
*
*
(xiii) Take to protect stock animals
and dogs. Any legally present private
citizen on private or public land may
immediately take a wolf that is in the
act of attacking the individual’s legally
present stock animal or dog, provided
that there is no evidence of intentional
baiting, feeding, or deliberate attractants
of wolves. The citizen must be able to
provide evidence of stock animals or
dogs recently (less than 24 hours)
wounded, harassed, molested, or killed
by wolves, and we or our designated
agents must be able to confirm that the
stock animals or dogs were wounded,
harassed, molested, or killed by wolves.
To preserve evidence that the take of a
wolf was conducted according to this
rule, the citizen must not disturb the
carcass and the area surrounding it. The
take of any wolf without such evidence
of a direct and immediate threat may be
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referred to the appropriate authorities
for prosecution.
*
*
*
*
*
Dated: June 28, 2007.
Kevin Adams,
Acting Director, U.S. Fish and Wildlife
Service.
[FR Doc. 07–3268 Filed 7–2–07; 11:20 am]
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Agencies
[Federal Register Volume 72, Number 129 (Friday, July 6, 2007)]
[Proposed Rules]
[Pages 36942-36949]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 07-3268]
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
RIN 1018-AV39
Endangered and Threatened Wildlife and Plants; Proposed Revision
of Special Regulation for the Central Idaho and Yellowstone Area
Nonessential Experimental Populations of Gray Wolves in the Northern
Rocky Mountains
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service (Service), propose
revisions to the 2005 special rule for the central Idaho and
Yellowstone area nonessential experimental population of the gray wolf
(Canis lupus) in the northern Rocky Mountains (NRM). Specifically, this
rule proposes to modify the definition of ``unacceptable impacts'' to
wild ungulate populations so that States and Tribes with Service-
approved post-delisting wolf management plans can better address the
impacts of a biologically recovered wolf population on ungulate
populations and herds while wolves remain listed. We also propose to
modify the 2005 special rule to allow private citizens in States or on
Tribal lands with approved post-delisting wolf management plans to take
wolves that are in the act of attacking their stock animals or dogs.
All other provisions of the 2005 special rule, including the process to
obtain Service approval and the conditions for reporting all wolf take,
would remain unchanged. As under the existing terms of the 2005 special
rule, these proposed modifications would not apply with respect to
States or Tribes without approved post-delisting wolf management plans
and would not impact wolves outside the Yellowstone or central Idaho
nonessential experimental population areas. A draft environmental
assessment will be prepared on this proposed action.
DATES: Comments from all parties on both the proposal and the draft
environmental assessment must be received by August 6, 2007. We will
hold three public hearings on this proposed rule in July. See
SUPPLEMENTARY INFORMATION for the dates, times, and locations.
ADDRESSES: If you wish to comment, you may submit comments and
materials concerning this proposal, identified by ``RIN 1018-AV39,'' by
any of the following methods:
1. You may mail or hand deliver written comments to the U.S. Fish
and Wildlife Service, Western Gray Wolf Recovery Coordinator, 585
Shepard Way, Helena, Montana 59601;
2. You may send comments by electronic mail (e-mail) directly to
the Service at WolfRuleChange@fws.gov. Include ``RIN number 1018-Av39''
in the subject line of the message. See the Public Comments Solicited
section below for file format for electronic filing; or
3. You may submit your comments through the Federal e-Rulemaking
Portal--https://www.regulations.gov. Follow the instructions for
submitting comments.
Comments and materials received, as well as supporting
documentation used in preparation of this proposed action, will be
available for inspection following the close of the comment period, by
appointment, during normal business hours, at our Helena office (see
ADDRESSES).
FOR FURTHER INFORMATION CONTACT: Edward E. Bangs, Western Gray Wolf
Recovery Coordinator, U.S. Fish and Wildlife Service, at our Helena
office (see ADDRESSES) or telephone (406) 449-5225, extension 204.
SUPPLEMENTARY INFORMATION:
Public Comments Solicited
We intend that any final action resulting from this proposal will
be as accurate and as effective as possible. Therefore, data, comments,
new information, or suggestions from the public, other concerned
governmental agencies, the scientific community, industry, or any other
interested party concerning this proposed rule are hereby solicited. We
particularly seek comments concerning (1) our proposed modifications to
the 2005 experimental population rule to allow private citizens to take
wolves in the act of attacking their stock animals or dogs; and (2) our
establishing a reasonable process for States and Tribes with approved
post-delisting wolf management plans to allow removal of wolves that
are scientifically demonstrated to be impacting ungulate populations to
the degree that they are not meeting respective State and Tribal
management goals. We specifically ask for comments regarding whether
the proposed modifications would reasonably address conflicts between
wolves and domestic animals or wild ungulate populations; would provide
sufficient safeguards to prevent misuse of the modified rule; would
provide an appropriate and transparent public process that ensures
decisions are science-based; and would provide adequate guarantees that
wolf recovery will not be compromised.
If you wish to comment, you may submit your comments and materials
concerning this proposed rule by any one of several methods, as listed
above in the ADDRESSES section. If you submit comments by e-mail,
please submit them in ASCII file format and avoid the use of special
characters and encryption. Please note that the e-mail address will be
closed at the termination of the public comment period.
Our practice is to make comments, including names and home
addresses of respondents, available for public review during regular
business hours. Before including your address, phone number, e-mail
address, or other personal identifying information in your comment, you
should be aware that your entire comment--including your personal
identifying information--may be made publicly available at any time.
While you can ask us in your comment to withhold your personal
identifying information from public review, we cannot guarantee that we
will be able to do so. Comments and materials received will be
available for public inspection, by appointment, during normal business
hours (see ADDRESSES section).
Peer Review
In accordance with our joint policy published in the Federal
Register on July 1, 1994 (59 FR 34270), and the Office of Management
and Budget's (OMB) Final Information Quality Bulletin for Peer Review,
dated December 16, 2004, we will seek independent review of the science
in this rule. The purpose of such review is to ensure that our final
rule is based on scientifically sound data, assumptions, and analyses.
We will send peer reviewers copies of this proposed rule immediately
following publication in the Federal Register. We will invite these
peer reviewers to comment,
[[Page 36943]]
during the public comment period, on the specific assumptions and
conclusions regarding the proposed rule.
We will take into consideration all comments, including peer review
comments, and any additional information received during the comment
period on this proposed rule during the preparation of a final
rulemaking. Accordingly, the final decision may differ from this
proposal.
Public Hearings
Three open houses will be held on:
July 17, 2007, Tuesday at Cody Auditorium Facility, 1240 Beck Avenue,
Cody, Wyoming; open house 12:30 p.m. to 1:30 p.m. and public hearing
1:30 p.m. to 3:30 p.m.;
July 18, 2007, Wednesday at Jorgenson's Inn & Suites, 1714 11th Avenue,
Helena, Montana; open house 6 p.m. to 7 p.m. and public hearing 7 p.m.
to 9 p.m.; and
July 19, 2007, Thursday at Boise Convention Center on the Grove, 850
Front Street, Boise, Idaho; open house 6 p.m. to 7 p.m. and public
hearing 7 p.m. to 9 p.m.
Anyone wishing to make an oral statement for the record is
encouraged to provide a written copy of their statement and present it
to us at the hearing. In the event there is a large attendance, the
time allotted for oral statements may be limited. Those that wish to
speak must sign up at the open houses and hearing. Oral and written
statements receive equal consideration. There are no limits on the
length of written comments submitted to us. If you have any questions
concerning the public hearings, please contact Sharon Rose (303) 236-
4580. Persons needing reasonable accommodations in order to attend and
participate in the public hearing in Idaho should contact Joan Jewett
(503) 231-6211, and for hearings in Montana or Wyoming, please contact
Sharon Rose at (303) 236-4580, as soon as possible in order to allow
sufficient time to process requests. Please call no later than 1 week
before the hearing date. Information regarding the proposal is
available in alternative formats upon request.
Previous Federal Actions
In 1974, four subspecies of gray wolf were listed as endangered
including the northern Rocky Mountains gray wolf (Canis lupus
irremotus), the eastern timber wolf (C. l. lycaon) in the northern
Great Lakes region, the Mexican wolf (C. l. baileyi) in Mexico and the
southwestern United States, and the Texas gray wolf (C. l.
monstrabilis) of Texas and Mexico (39 FR 1171, January 4, 1974). In
1978, we published a rule (43 FR 9607, March 9, 1978) relisting the
gray wolf as endangered at the species level (C. lupus) throughout the
conterminous 48 States and Mexico, except for Minnesota, where it was
reclassified as threatened. In 2007, we published a rule (72 FR 6052)
which delisted the Western Great Lakes population of wolves that
included all of Minnesota, Wisconsin, Michigan, and parts of North and
South Dakota, Iowa, Illinois, Indiana, and Ohio. The northern Rocky
Mountain Wolf Recovery Plan was approved in 1980 (Service 1980, p. i)
and revised in 1987 (Service 1987, p. i).
On November 22, 1994, we designated unoccupied portions of Idaho,
Montana, and Wyoming as two nonessential experimental population areas
for the gray wolf under section 10(j) of the Endangered Species Act of
1973, as amended (Act) (59 FR 60252, November 22, 1994; 59 FR 60266,
November 22, 1994). One area was the Yellowstone National Park
experimental population area which included all of Wyoming, and parts
of southern Montana and eastern Idaho (59 FR 60252, November 22, 1994).
The other was the central Idaho experimental population area that
included most of Idaho and parts of southwestern Montana (59 FR 60266,
November 22, 1994). In 1995 and 1996, we reintroduced wolves from
southwestern Canada into these areas (Bangs and Fritts 1996, pp. 407-
409; Fritts et al. 1997, p. 7; Bangs et al. 1998, pp. 785-786). This
reintroduction and accompanying management programs greatly expanded
the numbers and distribution of wolves in the northern Rocky Mountains.
At the end of 2000, the northern Rocky Mountain population first met
its numerical and distributional recovery goal of a minimum of 30
breeding pairs and over 300 wolves well-distributed among Montana,
Idaho, and Wyoming (68 FR 15804, April 1, 2003; Service et al. 2001,
Table 4). This minimum recovery goal was again exceeded in 2001, 2002,
2003, 2004, 2005, and 2006 (Service et al. 2002-2006, Table 4).
On January 6, 2005, we published a revised nonessential
experimental population special rule increasing management flexibility
for these recovered populations (70 FR 1286, January 6, 2005). For
additional detailed information on previous Federal actions see the
1994 and 2005 special rules (59 FR 60252, November 22, 1994; 59 FR
60266, November 22, 1994; 70 FR 1286, January 6, 2005), the 2003
reclassification rule (68 FR 15804, April 1, 2003), the Advanced Notice
of Proposed Rulemaking to designate the NRM gray wolf population as a
Distinct Population Segment (DPS) and remove the Act's protections for
this population (71 FR 6634, February 8, 2006) and the 2007 proposal to
designate the NRM gray wolf population as a DPS and remove the Act's
protections for this population (i.e., delist) (72 FR 6106, February 8,
2007).
Background
Given the recovered status of the wolf population and the practical
limitations on implementing the current nonessential experimental
rules, we propose to slightly modify the 2005 rule (70 FR 1286, January
6, 2005). Additional background on nonessential experimental rules
implemented under section 10(j) of the Act can be found in the 1994
rules (59 FR 60252, November 22, 1994; 59 FR 60266, November 22, 1994)
and the 2005 rule (70 FR 1286, January 6, 2005).
Addressing Unacceptable Impacts on Wild Ungulate Populations--
States and Tribes have the expertise to make determinations of
unacceptable impacts to ungulate populations. Both the 1994
Environmental Impact Statement for wolf reintroduction (Service 1994,
pp. 6, 8) and the 1994 nonessential experimental special rules
addressed the potential impact of wolf restoration on State and Tribal
objectives for wild ungulate management. Specifically, the 1994 rules
stated, ``Potentially affected States and Tribes may capture and
translocate wolves to other areas within an experimental population
area as described in paragraph (i)(7), Provided, the level of wolf
predation is negatively impacting localized ungulate populations at an
unacceptable level. Such translocations cannot inhibit wolf population
recovery. The States and Tribes will define such unacceptable impacts,
how they would be measured, and identify other possible mitigation in
their State or Tribal wolf management plans. These plans must be
approved by the Service before such movement of wolves may be
conducted'' (59 FR 60264, November 22, 1994; 59 FR 60279, November 22,
1994). The ``plans'' referenced in the 1994 rules related to the
management of the listed nonessential experimental wolves.
Two examples of conflicts that might warrant relocation outlined in
the preamble of the 1994 rules were ``(1) when wolf predation is
dramatically affecting prey availability because of unusual habitat or
weather conditions; and (2) when wolves cause prey to move onto private
property and mix with livestock, increasing potential conflicts''
[[Page 36944]]
(59 FR 60257, November 22, 1994; 59 FR 60272, November 22, 1994).
No such State plans for managing listed wolves were adopted;
therefore, no wolves were ever moved for ungulate conflicts under the
1994 regulations. Only Wyoming had requested that wolves be moved by
the Service. In that situation, Wyoming reported that wolves were
occasionally chasing elk with high rates of brucellosis infection off
winter elk feed grounds causing them to temporarily mix more frequently
with nearby domestic cattle. The Service suggested that the State
identify the sites in Wyoming where they would prefer the wolves to be
moved, but no sites were ever identified and no wolves were ever moved.
On January 6, 2005, we finalized a new special rule that allowed
greater management flexibility for managing a recovered wolf population
in the experimental population area of States and Tribal reservations
for States and Tribes which had Service approved, post-delisting wolf
management plans (70 FR 1286). It also allowed additional opportunities
for the public to take wolves in order to protect their private
property.
The 2005 rule's provision for ``take in response to wild ungulate
impacts'' states at 70 FR 1308 that:
``If wolf predation is having an unacceptable impact on wild
ungulate populations (deer, elk, moose, bighorn sheep, mountain
goats, antelope, or bison) as determined by the respective State or
Tribe, a State or Tribe may lethally remove the wolves in question.
(A) In order for this provision to apply, the States or Tribes
must prepare a science-based document that:
(1) Describes what data indicate that ungulate herd is below
management objectives, what data indicate the impact of wolf
predation on the ungulate population, why wolf removal is a
warranted solution to help restore the ungulate herd to State or
Tribal management objectives, the level and duration of wolf removal
being proposed, and how ungulate population response to wolf removal
will be measured;
(2) Identifies possible remedies or conservation measures in
addition to wolf removal; and
(3) Provides an opportunity for peer review and public comment
on their proposal prior to submitting it to the Service for written
concurrence.
(B) We must determine that such actions are scientifically based
and will not reduce the wolf population below recovery levels before
we authorize lethal wolf removal.''
The 2005 rule authorized lethal take because we recognized that the
wolf population had exceeded its recovery goals, that extra management
flexibility was required to address conflicts given the recovered
status of the population, that most of the suitable wolf habitat in
Montana, Idaho, and Wyoming was occupied by resident wolf packs
(Oakleaf et al. 2006), and that absent high-quality unoccupied suitable
habitat, wolf translocations were likely to fail (70 FR 1294, January
6, 2005; Bradley et al. 2005, p. 1506).
The 2005 rule's definition of ``Unacceptable impact'' is a ``State
or Tribally-determined decline in a wild ungulate population or herd,
primarily caused by wolf predation, so that the population or herd is
not meeting established State or Tribal management goals. The State or
Tribal determination must be peer-reviewed and reviewed and commented
on by the public, prior to a final determination by the Service that an
unacceptable impact has occurred, and that wolf removal is not likely
to impede wolf recovery'' (70 FR 1307, January 6, 2005).
In our definition of ``Unacceptable impact'' in the 2005 rule, we
set a threshold that has not provided the intended flexibility to allow
States and Tribes to resolve conflicts between wolves and ungulate
populations. Current information does not indicate that wolf predation
alone is likely to be the primary cause of a reduction of any ungulate
population in Montana, Idaho, or Wyoming (Bangs et al. 2004, pp. 89-
100). There are no populations of wild ungulates in Montana, Idaho, or
Wyoming where wolves are the sole predator. Wolf predation is unlikely
to impact ungulate population trends substantially unless other
contributing factors are in operation, such as habitat quality and
quantity (National Research Council 1997, pp. 185-186; Mech and
Peterson 2003, p. 159), other predators (bear predation on neonates)
(Barber et al. 2005, p. 42-43; Smith et al. 2006, p. vii), high harvest
by hunters (Vucetich et al. 2005, p. 259; White and Garrott 2005, p.
942; Evans et al. 2006, p. 1372; Hamlin 2006, p. 27-32), weather (Mech
and Peterson 2003, pp. 138-139), and other factors (Pletscher et al.
1991, pp. 545-548; Garrott et al. 2005, p. 1245; Smith et al. 2006, pp.
246-250). However, in combination with any of these factors, wolf
predation can have a substantial impact to some wild ungulate herds
(National Research Council 1997, p. 183; Mech and Peterson 2003, pp.
155-157; Evans et al. 2006, p. 1377) with the potential of reducing
them below State and Tribal herd management objectives.
The unattainable nature of the threshold set in the 2005 rule
became apparent soon after its completion. In 2005, the State of Idaho
submitted a proposal to the Service that indicated wolf predation was
impacting the survival of adult cow elk in the Clearwater area of
central Idaho and that the elk population was below State management
objectives (Idaho Fish and Game 2006). In the Clearwater proposal, the
State of Idaho and the peer reviewers clearly concluded that wolf
predation was not ``primarily'' the cause of the elk population's
decline, but was one of the major factors maintaining the elk herd's
status below State management objectives. Declining habitat quality due
to forest maturation was the primary factor affecting the herd's
status, but black bear predation on young elk calves, mountain lion
predation on adults, and the harsh winter in 1996 to 97 also were major
factors. Data also clearly indicated that wolf predation was one of the
major causes of mortality of adult female elk, which contributed to the
elk herd remaining below State management objectives. After discussions
with the Service, Idaho put their proposal on hold because the proposal
did not meet the regulatory standard for an ``Unacceptable impact'' set
by the 2005 special rule.
We are now proposing to redefine the term ``Unacceptable impact''
to achieve the originally intended management flexibility.
Specifically, we propose to define ``Unacceptable impact'' as ``State
or Tribally determined impact to a wild ungulate population or herd,
with wolves as one of the major causes of the population or herd not
meeting established State or Tribal population or herd management
goals. The State or Tribal determination must be peer-reviewed and
reviewed and commented on by the public prior to a final determination
by the Service that an unacceptable impact has occurred and that wolf
removal is not likely to impede wolf recovery.'' This definition
expands the potential impacts for which wolf removal might be warranted
beyond direct predation or those causing immediate population declines.
It would, in certain circumstances, allow wolf pack removal when wolves
are a major cause of the population or herd not meeting established
State or Tribal population or herd management goals. Management goals
might include cow/calf ratios, movements, use of key feeding areas,
survival rates, behavior, nutrition, and other factors.
Under this proposal, as in the 2005 rule, science-based proposals
from a State or Tribe with an approved post-delisting wolf management
plan would have to undergo both public and peer review. Based on that
peer review and public comment, the State or Tribe would finalize the
plan and then submit it to the Service for a final
[[Page 36945]]
determination. The Service expects the following to be addressed in the
State or Tribal proposal: (1) What data indicate that the ungulate herd
is below management objectives; (2) what data indicate impact by wolf
predation on the ungulate population; (3) why wolf removal is a
warranted solution to help restore the ungulate herd to State or Tribal
management objectives; (4) the level and duration of wolf removal being
proposed; (5) how ungulate population response to wolf removal will be
measured; and (6) possible remedies or conservation measures in
addition to wolf removal. Before wolf removals can be authorized, the
Service must determine if the State or Tribe followed the rule's
procedures for developing a proposal to remove wolves in response to
unacceptable impacts; if the proposal meets the definition of
unacceptable impact; if the science presented supports the recommended
action; and if the proposal is science-based.
The recovery goal for the NRM wolf population requires that it be
comprised of at least 30 breeding pairs and 300 wolves that are
equitably distributed in potentially suitable habitat in Montana,
Idaho, and Wyoming. To ensure this goal is achieved, each of the three
States (Wyoming, Montana, and Idaho) committed to manage for an
equitable distribution of the overall population and assume a
management target of 15 breeding pairs in mid-winter within each State.
The 15 breeding pair management target was not intended to be the
minimum goal for each State. It was an objective so that each State's
management would provide a reasonable cushion to ensure each State's
share of the wolf population did not fall below the 10 breeding pairs
requirement and that the 30 breeding pairs minimum would always be met
or exceeded.
While this change will likely result in more wolf control than is
currently occurring, we propose to establish controls to ensure that
wolf control for ungulate management purposes would not undermine
recovery goals. Specifically, before any lethal control of wolf
populations can be authorized, we must determine that such actions will
not reduce the wolf population in the State below 20 breeding pairs and
200 wolves. This assures that the wolf population is large enough to
easily rebound from such removal, that a large safety margin is
provided against unseen mortality events that might occur after such
removal, and that a substantial margin of safety is provided to ensure
that recovery objectives would never be compromised. This limit is a
necessary and advisable precaution while wolves remain listed to ensure
the conservation of the species given the additional take that might be
authorized pursuant to this proposed rule. Once delisted, Montana,
Idaho, and Wyoming will manage for no less than 15 breeding pairs.
By the end of 2006, the northern Rocky Mountain wolf population was
estimated to contain 1,300 wolves in 86 breeding pairs (nearly three
times the minimum numeric recovery goal for breeding pairs and more
than four times the minimum population goal), and for the 7th
consecutive year it exceeded minimum recovery levels. Montana had an
estimated 316 wolves in 21 breeding pairs, Idaho had 673 wolves in 40
breeding pairs, and Wyoming had 311 wolves in 25 breeding pairs. Wolf
biology allows for rapid recovery from severe disruptions. After severe
declines, wolf populations can more than double in just 2 years if
mortality is reduced; and increases of nearly 100 percent per year have
been documented in low-density suitable habitat (Fuller et al. 2003,
pp. 181-183; Service et al. 2007, Table 4). The literature suggests
that wolf populations can maintain themselves despite a sustained
human-caused mortality rate of 30 percent or more per year (Keith 1983,
p. 66; Fuller et al. 2003, pp. 182-184).
Our data indicate that the human-caused mortality rate in the
adult-sized segment of the northern Rocky Mountain wolf population was
nearly 26 percent per year from 1994 to 2004 (Smith 2005), and that the
wolf population still continued to expand at about 26 percent annually
(Service et al. 2007, Table 4). This data indicates that the current
annual mortality rate of about 26 percent in the adult portion of the
wolf population could be nearly doubled and the wolf population could
still maintain itself at current levels. Collectively, these factors
mean that wolf populations are quite resilient to human-caused
mortality if it is regulated.
The wolf population now occupies most of the suitable wolf habitat
in the northern Rocky Mountains (72 FR 6106-6139, February 8, 2007;
Oakleaf et al. 2006, p. 559). The population is unlikely to
significantly expand its overall distribution beyond the outer
boundaries of the current population because little unoccupied suitable
habitat is available. Given current population density and these
habitat limitations, we believe the overall numbers of wolf breeding
pairs and numbers of wolves cannot continue to sustain a growth rate of
26 percent per year. Thus, we do not believe any increased take as a
result of this rule, if finalized, would have an impact on the
recovered status of the northern Rocky Mountain wolf population in
Montana, Idaho, or Wyoming, as long as it remains managed under a
science-based plan.
Addressing Take To Protect Stock Animals and Dogs--The 1994
experimental population rules stated that ``any livestock producers on
their private land may take (including to kill or injure) a wolf in the
act of killing, wounding, or biting livestock'' (defined as cattle,
sheep, horses, and mules) (59 FR 60264, November 22, 1994; 59 FR 60279,
November 22, 1994). Similar provisions applied to producers on public
land if they obtained a permit from the Service (59 FR 60264, November
22, 1994; 59 FR 60279, November 22, 1994).
The 2005 special rule expanded this provision in States with
approved post-delisting wolf management plans to allow private citizens
to also lethally take wolves that were ``in the act of attacking''
their livestock and dogs on private land and any livestock or herding
and guarding dogs on active public grazing allotments or special use
areas. ``In the act of attacking'' is defined in 50 CFR 17.84(n)(3) as
``the actual biting, wounding, grasping, or killing of livestock or
dogs, or chasing, molesting, or harassing by wolves that would indicate
to a reasonable person that such biting, wounding, grasping, or killing
of livestock or dogs is likely to occur at any moment.'' Such incidents
had to be reported to the Service or our designated agent(s) within 24
hours and physical evidence of such an attack had to be present.
This rule proposes to add a new provision for lethal take of wolves
in States with approved post-delisting wolf management plans when in
defense of ``stock animals'' (defined as ``a horse, mule, donkey, or
llama used to transport people or their possessions'') or dogs.
Specifically, the proposed modification states that ``any legally
present private citizen on private or public land may immediately take
a wolf that is in the act of attacking the individuals' legally present
stock animal or dog, provided there is no evidence of intentional
baiting, feeding, or deliberate attractants of wolves. The citizen must
be able to provide evidence of stock animals or dogs recently (less
than 24 hours) wounded, harassed, molested, or killed by wolves, and we
or our designated agents must be able to confirm that the stock animals
or dogs were wounded, harassed, molested, or killed by wolves. To
preserve evidence that the take of a wolf was conducted according to
this
[[Page 36946]]
rule, the carcass of the wolf and the area surrounding should not be
disturbed. The take of any wolf without such evidence of a direct and
immediate threat may be referred to the appropriate authorities for
prosecution.''
Since 1995, only 43 wolves (about 8 percent of the 538 wolves
legally removed in agency-authorized control actions) have been legally
killed by private citizens in defense of their private property or by
shoot-on-sight permits as authorized by either the 1994 or 2005
experimental population special rules. There has been no documentation
of wolf depredations on stock animals that were accompanied by their
owners in the past 12 years, but a few instances of stock animals being
spooked by wolves have been reported. While this proposed revision will
provide additional opportunity for private citizens to protect their
private property, we expect minor impacts on the wolf population.
Ninety-one dogs have been confirmed to be killed by wolves from
1987 to 2007 (Service et al. 2007, Table 5). No pet dogs have been
confirmed to be killed by wolves while they were accompanied by their
owners, and no wolves have been killed solely to protect dogs. However,
35 hunting hounds have been killed by wolves, primarily on public land.
In only a few of those instances, the hounds' owners were close enough
that they might have been able to better protect their dogs by shooting
at the wolves involved. We expect that take of wolves involved in
conflicts with pet dogs or hunting hounds would be rare. This proposed
modification would allow for private citizens to protect their dogs
from wolf attack while not meaningfully increasing the rate of wolf
removal.
Required Determinations
Regulatory Planning and Review--In accordance with the criteria in
Executive Order 12866, this rule is a significant regulatory action and
subject to OMB review. An economic analysis is not required because
this rule will result in only minor and positive economic effects on a
small percentage of private citizens in Idaho and Montana, and possibly
Wyoming if it develops an approved post-delisting wolf management plan.
(a) This regulation does not have an annual economic effect of $100
million or adversely affect an economic sector, productivity, jobs, the
environment, or other units of government. A brief assessment to
clarify the costs and benefits associated with this rule follows.
Costs Incurred--Under the 2005 special rule, which this rule
proposes to modify, management of wolves by States or Tribes with
Service-approved post-delisting wolf management plans is voluntary.
Therefore, associated costs would be discretionary. While we do not
quantify these expected expenditures, these costs may consist of staff
time and salary as well as transportation and equipment necessary to
control wolves unacceptably impacting ungulate populations or herds.
We have funded State and Tribal wolf monitoring, research, and
management efforts for gray wolves in Montana, Idaho, and Wyoming, and
intend to continue to do so as long as wolves are listed. For the past
several years Congress has targeted funding for wolf management to
Montana, Idaho, and Wyoming, and the Nez Perce. In addition, Federal
grant programs are available that fund wildlife management programs by
the States and Tribes.
Benefits Accrued--The objectives of the proposed rule change are
(1) to allow States and Tribes with Service-approved post-delisting
wolf management plans to address the unacceptable impacts of a
biologically recovered wolf population to ungulate populations and
herds, and (2) to allow private citizens in States or on Tribal lands
with approved post-delisting wolf management plans to take wolves that
are in the act of attacking their stock animals or dogs. Allowing wolf
removal in response to unacceptable impacts will help maintain ungulate
populations or herds at or above State or Tribal objectives. Balancing
the needs of wolves and elk provides substantial and sustainable
economic benefits. Allowing take of wolves in the act of attacking
stock animals or dogs would have a beneficial economic impact by
allowing citizens to protect such private property. This proposed
amendment could prevent the need for these citizens to replace and
retrain these animals. An additional potential benefit may be a lower
level of illegal take of wolves due to higher local public tolerance of
wolves resulting from reduced conflicts between wolves and humans.
(b) This regulation does not create inconsistencies with other
agencies' actions. It is exactly the same as the nonessential
experimental population rules currently in effect regarding agency
responsibilities under section 7 of the Act. This rule reflects
continuing success in recovering the gray wolf through long-standing
cooperative and complementary programs by a number of Federal, State,
and Tribal agencies. Implementation of Service-approved State or Tribal
post-delisting wolf management plans supports these existing
partnerships.
(c) This rule will not alter the budgetary effects or entitlements,
grants, user fees, or loan programs, or the rights and obligations of
their recipients because we do not foresee any new impacts or
restrictions to existing human uses of lands in Idaho or Montana as a
result of this rule, nor in Wyoming or any Tribal reservations that
remain under the 1994 10(j) rules.
(d) This rule does not raise novel legal or policy issues. Instead
it proposes to reduce the restrictions on take of wolves. Similar take
provisions are already in place through the 1994 and 2005 special rules
(59 FR 60252, November 22, 1994; 59 FR 60266, November 22, 1994; 70 FR
1286, January 6, 2005). No new novel legal or policy issues are raised
by the amendments offered in this proposed rule.
Regulatory Flexibility Act (5 U.S.C. 601 et seq.)
Under the Regulatory Flexibility Act (5 U.S.C. 601 et seq., as
amended by the Small Business Regulatory Enforcement Fairness Act
(SBREFA) of 1996), whenever a Federal agency is required to 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. The SBREFA amended
the Regulatory Flexibility Act to require Federal agencies to provide a
statement of the factual basis for certifying that a rule will not have
a significant economic impact on a substantial number of small
entities. The SBREFA also amended the Regulatory Flexibility Act to
require a certification statement. Based on the information that is
available to us at this time, we certify that this regulation will not
have a significant economic impact on a substantial number of small
entities. The following discussion explains our rationale.
The majority of wolves in the West are currently protected under
the nonessential experimental population designations that cover
Wyoming, most of Idaho, and southern Montana that treat wolves as a
threatened species. Special regulations exist for these experimental
populations that currently allow government employees and
[[Page 36947]]
designated agents, as well as livestock producers and private citizens,
to take problem wolves. This proposed regulation modification does not
change the nonessential experimental designation, but does contain
additional special regulations that allow States and Tribes with
approved post-delisting wolf management plans more flexibility in
managing nonessential experimental wolves.
These changes are applicable only where States or Tribes (on Tribal
reservations) that have an approved post-delisting management plan for
gray wolves. Within the northern Rocky Mountain gray wolf population's
range, only the States of Idaho and Montana have approved plans.
Therefore, the regulation is expected to result in a small reduction of
economic losses to some private citizens in States with approved post-
delisting wolf management plans (i.e., Idaho and Montana) within the
boundary of the nonessential experimental populations of the northern
Rocky Mountain gray wolf population (Central Idaho nonessential
experimental population area and Yellowstone nonessential experimental
population area) (59 FR 60252, November 22, 1994; 59 FR 60266, November
22, 1994).
In anticipation of the possible delisting the northern Rocky
Mountain gray wolf population, we have worked closely with States to
ensure that their plans provide the protection and flexibility
necessary to manage wolves at or above recovery levels after delisting.
Approved plans are those plans that have passed peer review and Service
scrutiny aimed at ensuring that the requirements under the Act are met
and that recovery levels are maintained. It is appropriate for States
that have met this approval standard to manage wolves prior to
delisting for several reasons. States with approved post-delisting wolf
management plans (Montana and Idaho) worked with their elected
officials and public to develop biologically and socially accepted
State regulatory frameworks to conduct wolf management. They have
already assumed an important role in the management of this species and
have developed extensive field experience and expertise, garnered
considerable public trust, and exceeded the goals for recovery. A
gradual transfer of responsibilities while the wolves are protected
under the Act provides an adjustment period for the State wildlife
agencies, Federal agencies, and Tribes to work out any unforeseen
issues that may arise.
Small Business Regulatory Enforcement Fairness Act
This regulation is not a major rule under 5 U.S.C. 801 et seq., the
SBREFA.
(a) This regulation will not have an annual effect on the economy
of $100 million or more and is fully expected to have no significant
economic impacts. The proposed regulation further reduces the effect
that wolves will have on a few private citizens by increasing the
opportunity for them to protect their stock animals and dogs. Since
there are so few small businesses impacted by this regulation, the
combined economic effects are minimal.
(b) This regulation will not cause a major increase in costs or
prices for consumers, individual industries, Federal, State, or local
government agencies, or geographic regions and will impose no
additional regulatory restraints in addition to those already in
operation.
(c) This regulation will not have significant adverse effects on
competition, employment, investment, productivity, innovation, or the
ability of United States-based enterprises to compete with foreign-
based enterprises. Based on the analysis of identified factors, we have
determined that no individual industries within the United States will
be significantly affected and that no changes in the demography of
populations are anticipated. The intent of this special rule is to
facilitate and continue existing commercial activities while providing
for the conservation of species by better addressing the concerns of
affected landowners and the impacts of a biologically recovered wolf
population.
Unfunded Mandates Reform Act
The 2005 special rule, which this proposed rule suggests amending,
defines a process for voluntary and cooperative transfer of management
responsibilities for a listed species back to the States. Therefore, in
accordance with the Unfunded Mandates Reform Act (2 U.S.C. 1501, et
seq.):
(a) This rule will not ``significantly or uniquely'' affect small
governments. A Small Government Agency Plan is not required. As stated
above, this regulation will result in only minor positive economic
effects for a very small percentage of livestock producers.
(b) This rule 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. This rule is not
expected to have any significant economic impacts nor will it impose
any unfunded mandates on other Federal, State, or local government
agencies to carry out specific activities.
Takings (Executive Order 12630)
In accordance with Executive Order 12630, this rule will not have
significant implications concerning taking of private property by the
Federal Government. This rule will substantially advance a legitimate
government interest (conservation and recovery of listed species) and
will not present a bar to all reasonable and expected beneficial use of
private property. Because this proposed rule change pertains only to
the relaxation of restrictions on lethal removal of wolves, it would
not result in any takings of private property.
Federalism (Executive Order 13132)
This proposed rule maintains the existing relationship between the
States and the Federal Government. The State wildlife agencies in
Montana, Idaho, and Wyoming requested that we undertake this rulemaking
in order to assist the States in reducing conflicts with local
landowners and returning wolf management to the States or Tribes. We
have cooperated with the States in preparation of this rule.
Maintaining the recovery goals for these wolves will contribute to
their eventual delisting and their return to State management.
Utilizing the 2005 special rule, which this rule proposes to modify, is
voluntary. This rule will not have substantial direct effects on the
States, on the relationship between the States and the Federal
Government, or on the distribution of power and responsibilities among
the various levels of government. No intrusion on State policy or
administration is expected; roles or responsibilities of Federal or
State governments will not change; and fiscal capacity will not be
substantially directly affected. Therefore, this rule does not have
significant Federalism effects or implications to warrant the
preparation of a Federalism Assessment pursuant to the provisions of
Executive Order 13132.
Civil Justice Reform (Executive Order 12988)
In accordance with Executive Order 12988, the Department of the
Interior has determined that this rule does not unduly burden the
judicial system and meets the applicable standards provided in sections
3(a) and 3(b)(2) of the order.
Paperwork Reduction Act
The OMB regulations at 5 CFR 1320, which implement provisions of
the Paperwork Reduction Act (44 U.S.C. 3501 et seq.) require that
Federal
[[Page 36948]]
agencies obtain approval from OMB before collecting information from
the public. 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 control number. This rule does not contain any new
collections of information other than those permit application forms
already approved under the Paperwork Reduction Act, 44 U.S.C. 3501 et
seq., and assigned OMB clearance number 1018-0095.
National Environmental Policy Act
In compliance with all provisions of the National Environmental
Policy Act (NEPA), we are analyzing the impact of this rule
modification and will determine if there are any new significant
impacts or effects caused by this rule. A draft environmental
assessment will be prepared on this proposed action and will be
available for public inspection and comments when completed. All
appropriate NEPA documents will be finalized before this rule is
finalized.
Government-to-Government Relationship With Tribes (Executive Order
13175)
In accordance with the President's memorandum of April 29, 1994,
``Government-to-Government Relations with Native American Tribal
Governments'' (59 FR 22951), Executive Order 13175, and 512 DM 2, we
have been coordinating with affected Tribes within the experimental
population areas of Montana, Idaho, and Wyoming on this rule. We will
fully consider all of the comments on the proposed special regulations
that are submitted by Tribes and Tribal members during the public
comment period and will attempt to address those concerns, new data,
and new information where appropriate.
Energy Supply, Distribution or Use (Executive Order 13211)
On May 18, 2001, the President issued Executive Order 13211
requiring agencies to prepare Statements of Energy Effects when
undertaking certain actions that significantly affect energy supply,
distribution, and use. This rule 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.
Clarity of the Rule
Executive Order 12866 requires agencies to write regulations that
are easy to understand. We invite comments on how to make this proposal
easier to understand, including answers to questions such as the
following: Are the requirements in the document clearly stated? Does
the rule contain technical language or jargon that interferes with the
clarity? Does the format of the rule (grouping and order of sections,
use of headings, paragraphing, etc.) aid or reduce its clarity? And is
the description of the proposed rule in the SUPPLEMENTARY INFORMATION
section of the preamble helpful in understanding the proposed rule?
What else could we do to make the rule easier to understand? We
requested that any comments about how we could make this rule easier to
understand be sent to--Office of Regulatory Affairs, Department of the
Interior, Room 7229, 1849 C Street, NW., Washington, DC 20240. People
also could e-mail comments to Exsec@ios.doi.gov. We will review all
public comments and incorporate them in the final rule to make it
easier to understand.
References Cited
A complete list of all references cited in this rulemaking is
available upon request from our Helena office (see ADDRESSES section).
List of Subjects in 50 CFR Part 17
Endangered and threatened species, Exports, Imports, Reporting and
recordkeeping requirements, and Transportation.
Proposed Regulation Promulgation
Accordingly, we propose to amend part 17, subchapter B of chapter
I, title 50 of the Code of Federal Regulations, as set forth below:
PART 17--[AMENDED]
1. The authority citation for part 17 continues to read as follows:
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.
2. Amend Sec. 17.84 by amending paragraph (n) as follows:
a. In paragraph (n)(3), revise the term ``unacceptable impact''
and, in alphabetical order, add the terms ``stock animal'' and
``ungulate population or herd'', to read as set forth below; and
b. In paragraph (n)(4), revise the first sentence following the
heading and paragraph (n)(4)(v)(B), and add paragraph (n)(4)(xiii), to
read as set forth below.
Sec. 17.84 Special rules--vertebrates.
* * * * *
(n) * * *
(3) * * *
* * * * *
Stock animal--A horse, mule, donkey, or llama used to transport
people or their possessions.
Unacceptable impact--State or Tribally determined impact to a wild
ungulate population or herd, with wolves as one of the major causes of
the population or herd not meeting established State or Tribal
population or herd management goals. The State or Tribal determination
must be peer-reviewed and reviewed and commented on by the public,
prior to a final determination by the Service that an unacceptable
impact has occurred, and that wolf removal is not likely to impede wolf
recovery.
Ungulate population or herd--An assemblage of wild ungulates living
in a given area.
* * * * *
(4) Allowable forms of take of gray wolves. The following
activities, only in the specific circumstances described under this
paragraph (n)(4), are allowed: Opportunistic harassment; intentional
harassment; take on private land; take on public land; take in response
to impacts on wild ungulate populations; take in defense of human life;
take to protect human safety; take by designated agents to remove
problem wolves; incidental take; take under permits; take per
authorizations for employees of designated agents; take for research
purposes; and take to protect stock animals and dogs. * * *
* * * * *
(v) * * *
(B) We must determine that such actions are science-based and will
not reduce the wolf population in the State below 20 breeding pairs and
200 wolves before we authorize lethal wolf removal.
* * * * *
(xiii) Take to protect stock animals and dogs. Any legally present
private citizen on private or public land may immediately take a wolf
that is in the act of attacking the individual's legally present stock
animal or dog, provided that there is no evidence of intentional
baiting, feeding, or deliberate attractants of wolves. The citizen must
be able to provide evidence of stock animals or dogs recently (less
than 24 hours) wounded, harassed, molested, or killed by wolves, and we
or our designated agents must be able to confirm that the stock animals
or dogs were wounded, harassed, molested, or killed by wolves. To
preserve evidence that the take of a wolf was conducted according to
this rule, the citizen must not disturb the carcass and the area
surrounding it. The take of any wolf without such evidence of a direct
and immediate threat may be
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referred to the appropriate authorities for prosecution.
* * * * *
Dated: June 28, 2007.
Kevin Adams,
Acting Director, U.S. Fish and Wildlife Service.
[FR Doc. 07-3268 Filed 7-2-07; 11:20 am]
BILLING CODE 4310-55-P