Endangered and Threatened Wildlife and Plants; 12-Month Finding and Candidate Removal for Potentilla basaltica, 46889-46897 [2013-18579]
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Federal Register / Vol. 78, No. 149 / Friday, August 2, 2013 / Proposed Rules
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Dated: July 23, 2013.
Rachel Jacobsen,
Principal Deputy Assistant Secretary for Fish
and Wildlife and Parks.
[FR Doc. 2013–18583 Filed 8–1–13; 8:45 am]
BILLING CODE 4310–55–C
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[FWS– R8–ES–2013–0079; 4500030113]
RIN 1018–AZ12
Endangered and Threatened Wildlife
and Plants; 12-Month Finding and
Candidate Removal for Potentilla
basaltica; Proposed Threatened
Species Status for Ivesia webberi
Fish and Wildlife Service,
Interior.
ACTION: 12-month petition finding;
proposed rule.
AGENCY:
We, the U.S. Fish and
Wildlife Service (Service), announce a
12-month finding on a petition to list
the plant Potentilla basaltica (Soldier
Meadow cinquefoil) as an endangered or
threatened species. After review of the
best available scientific information, we
find that listing Potentilla basaltica as
an endangered or threatened species
under the Endangered Species Act (Act)
is no longer warranted, and, therefore,
we are removing this species from the
candidate list. We propose to list the
plant Ivesia webberi (Webber’s ivesia) as
a threatened species under the Act. If
finalized, the effect of this regulation
would be to add Ivesia webberi to the
List of Endangered and Threatened
Plants and extend the Act’s protections
to this species. Elsewhere in today’s
Federal Register, we propose to
designate critical habitat under the Act
for Ivesia webberi.
DATES: We will accept comments
received or postmarked on or before
October 1, 2013. Comments submitted
electronically using the Federal
eRulemaking Portal (see ADDRESSES
section, below) must be received by
11:59 p.m. Eastern Time on the closing
date. We must receive requests for
public hearings, in writing, at the
address shown in FOR FURTHER
INFORMATION CONTACT by September 16,
2013.
Public meeting: We will hold a public
meeting on this proposed rule on
September 10, 2013, in Reno, NV, from
4:00 to 6:00 p.m. People needing
reasonable accommodations in order to
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SUMMARY:
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attend and participate in the public
hearing should contact Jeannie Stafford,
Nevada Fish and Wildlife Office, as
soon as possible (see FOR FURTHER
INFORMATION CONTACT).
ADDRESSES: You may submit comments
by one of the following methods:
(1) Electronically: Go to the Federal
eRulemaking Portal: https://
www.regulations.gov. In the Search box,
enter FWS–R8–ES–2013–0079, which is
the docket number for this rulemaking.
Then, in the Search panel on the left
side of the screen, under the Document
Type heading, click on the Proposed
Rules link to locate this document. You
may submit a comment by clicking on
‘‘Comment Now!’’
(2) By hard copy: Submit by U.S. mail
or hand-delivery to: Public Comments
Processing, Attn: FWS–R8–ES–2013–
0079; Division of Policy and Directives
Management; U.S. Fish and Wildlife
Service; 4401 N. Fairfax Drive, MS
2042–PDM; Arlington, VA 22203.
We request that you send comments
only by the methods described above.
We will post all comments on https://
www.regulations.gov. This generally
means that we will post any personal
information you provide us (see the
Public Comments section below for
more information).
FOR FURTHER INFORMATION CONTACT:
Edward D. Koch, State Supervisor, U.S.
Fish and Wildlife Service, Nevada Fish
and Wildlife Office, 1340 Financial
Boulevard, Suite 234, Reno, NV 89502,
by telephone 775–861–6300, or by
facsimile 775–861–6301. Persons who
use a telecommunications device for the
deaf (TDD) may call the Federal
Information Relay Service (FIRS) at
800–877–8339.
SUPPLEMENTARY INFORMATION:
Executive Summary
Why we need to publish a rule. Under
the Act, if we find a species to be
endangered or threatened throughout all
or a significant portion of its range, we
are required to promptly publish a
proposal in the Federal Register and
make a final determination on our
proposal within 1 year. We designate
critical habitat to the maximum extent
prudent and determinable, for any
species determined to be an endangered
or threatened species under the Act.
Listing a species as an endangered or
threatened species and designations and
revisions of critical habitat can only be
completed by issuing a rule.
What this rule does. We propose the
listing of Ivesia webberi (Webber’s
ivesia) as a threatened species. Ivesia
webberi is a candidate species for which
we have on file sufficient information
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46889
on biological vulnerability and threats
to support preparation of a listing
proposal, but for which development of
a listing regulation has been precluded
by other higher-priority listing
activities. This rule reassesses all
currently available information
regarding status of and threats to I.
webberi. Elsewhere in today’s Federal
Register, we propose to designate
critical habitat for I. webberi under the
Act.
The basis for our action. Under the
Act, we can determine that a species is
an endangered or threatened species
based on any of five factors: (A) The
present or threatened destruction,
modification, or curtailment of its
habitat or range; (B) Overutilization for
commercial, recreational, scientific, or
educational purposes; (C) Disease or
predation; (D) The inadequacy of
existing regulatory mechanisms; or (E)
Other natural or manmade factors
affecting its continued existence. We
find Ivesia webberi is subject to the
present or threatened destruction,
modification, or curtailment of its
habitat (Factor A) from the following:
Nonnative, invasive plants; modified
fire regime (increased wildfire); OHV
use and roads; development; livestock
grazing; and climate change.
We will seek peer review. We are
seeking all comments, including those
from independent specialists to ensure
that our designation is based on
scientifically sound data, assumptions,
and analyses. We will invite these peer
reviewers to comment on our listing
proposal for Ivesia webberi. A thorough
review of information that we relied on
in making this determination—
including information on taxonomy, life
history, ecology, population distribution
and abundance, and potential threats—
is presented in the Ivesia webberi
Species Report available at www.
regulations.gov (Docket Number FWS–
R8–ES–2013–0079). A summary of this
analysis is found within this proposed
rule. Because we will consider all
comments and information received
during the comment period, our final
determinations may differ from this
proposal.
Information Requested
Public Comments
We intend that any final action
resulting from this proposed rule for
Ivesia webberi will be based on the best
scientific and commercial data available
and be as accurate and as effective as
possible. Therefore, we request
comments or information from the
public, other concerned governmental
agencies, Native American tribes, the
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scientific community, industry, or any
other interested parties concerning this
proposed rule. We particularly seek
comments concerning:
(1) Ivesia webberi’s biology,
distribution, population size and trend,
including:
(a) Habitat requirements for
pollination, reproduction, and dispersal;
(b) Genetics and taxonomy;
(c) Historical and current range
including distribution patterns;
(d) Historical and current population
levels, and current and projected trends;
and
(e) Past and ongoing conservation
measures for the species, its habitat, or
both.
(2) The factors that are the basis for
making a listing determination for a
species under section 4(a) of the Act (16
U.S.C. 1531 et seq.), which are:
(a) The present or threatened
destruction, modification, or
curtailment of its habitat or range
(Factor A);
(b) Overutilization for commercial,
recreational, scientific, or educational
purposes (Factor B);
(c) Disease or predation (Factor C);
(d) The inadequacy of existing
regulatory mechanisms (Factor D); or
(e) Other natural or manmade factors
affecting its continued existence (Factor
E).
(3) Biological, commercial trade, or
other relevant data concerning any
threats (or lack thereof) to this species
and existing regulations that may be
addressing those threats.
(4) Additional information concerning
the historical and current status, range,
distribution, and population size of this
species, including the locations of any
additional populations of this species.
(5) Any information on the biological
or ecological requirements of the
species, and ongoing conservation
measures for the species and its habitat.
Please include sufficient information
with your submission (such as scientific
journal articles or other publications) to
allow us to verify any scientific or
commercial information you include.
Please note that submissions merely
stating support for or opposition to the
action under consideration without
providing supporting information,
although noted, will not be considered
in making a determination, as section
4(b)(1)(A) of the Act directs that
determinations as to whether any
species is a threatened or endangered
species must be made ‘‘solely on the
basis of the best scientific and
commercial data available.’’
You may submit your comments and
materials concerning this proposed rule
by one of the methods listed in the
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ADDRESSES section. We request that you
send comments only by the methods
described in the ADDRESSES section.
If you submit information via https://
www.regulations.gov, your entire
submission—including any personal
identifying information—will be posted
on the Web site. If your submission is
made via a hardcopy that includes
personal identifying information, you
may request at the top of your document
that we withhold this information from
public review. However, we cannot
guarantee that we will be able to do so.
We will post all hardcopy submissions
on https://www.regulations.gov. Please
include sufficient information with your
comments to allow us to verify any
scientific or commercial information
you include.
Comments and materials we receive,
as well as supporting documentation we
used in preparing this proposed rule,
will be available for public inspection
on https://www.regulations.gov, or by
appointment, during normal business
hours, at the U.S. Fish and Wildlife
Service, Nevada Fish and Wildlife
Office (see FOR FURTHER INFORMATION
CONTACT).
Public Hearing
Section 4(b)(5) of the Act provides for
one or more public hearings on this
proposal, if requested. Requests must be
received within 45 days after the date of
publication of this proposed rule in the
Federal Register. Such requests must be
sent to the address shown in the FOR
FURTHER INFORMATION CONTACT section.
We will schedule public hearings on
this proposal, if any are requested, and
announce the dates, times, and places of
those hearings, as well as how to obtain
reasonable accommodations, in the
Federal Register and local newspapers
at least 15 days before the hearing.
Peer Review
In accordance with our joint policy on
peer review published in the Federal
Register on July 1, 1994 (59 FR 34270),
we will seek the expert opinions of at
least three appropriate and independent
specialists regarding the Ivesia webberi
proposed rule. A thorough review of
information that we relied on in making
this determination—including
information on taxonomy, life history,
ecology, population distribution and
abundance, and potential threats—is
presented in the Ivesia webberi Species
Report available at https://
www.regulations.gov (Docket Number
FWS–R8–ES–2013–0079). A summary
of this analysis is found within this
proposed rule. The purpose of peer
review is to ensure that our listing
determination is based on scientifically
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sound data, assumptions, and analyses.
A peer review panel will conduct an
assessment of the proposed rule and the
specific assumptions and conclusions
regarding the proposed listing. This
assessment will be completed during
the public comment period.
12-Month Petition Finding and
Candidate Withdrawal for Potentilla
basaltica
This section summarizes the
information on species status and
potential threats that we evaluated in
order to determine that listing Potentilla
basaltica is not warranted and to
remove it from candidate status. A
thorough review of information that we
relied on in making this
determination—including information
on taxonomy, life history, ecology,
population distribution and abundance,
and potential threats—is presented in
the P. basaltica (Soldier Meadow
Cinquefoil) Species Report (Service
2013a, entire), which is available at
https://www.regulations.gov (in the
Search box, enter FWS–R8–ES–2013–
0079, which is the docket number for
this rulemaking).
The factors that are the basis for
making a listing determination for a
species under section 4(a) of the Act (16
U.S.C. 1531 et seq.), are:
(a) The present or threatened
destruction, modification, or
curtailment of its habitat or range
(Factor A);
(b) Overutilization for commercial,
recreational, scientific, or educational
purposes (Factor B);
(c) Disease or predation (Factor C);
(d) The inadequacy of existing
regulatory mechanisms (Factor D); or
(e) Other natural or manmade factors
affecting its continued existence (Factor
E).
We discuss the potential threats
related to each factor below.
We identified Potentilla basaltica as a
candidate in the June 13, 2002,
Candidate Notice of Review (CNOR, 67
FR 40657). At the time, our assessment
was that the species was being impacted
by the present or threatened destruction,
modification, or curtailment of its
habitat or range (Factor A) resulting
from the primary threats of heavy
recreational use, OHV activity, and
livestock grazing at Soldier Meadow. A
candidate species is one for which we
have on file sufficient information on
biological vulnerability and threats to
support a proposal to list as endangered
or threatened, but for which preparation
and publication of a proposal is
precluded by higher-priority listing
actions. Potentilla basaltica was
included in all subsequent annual
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CNORs (69 FR 24875, May 4, 2004; 70
FR 24869, May 11, 2005; 71 FR 53756,
September 12, 2006; 72 FR 69033,
December 6, 2007; 73 FR 75175,
December 10, 2008; 74 FR 57803,
November 9, 2009; 75 FR 69221,
November 10, 2010; and 76 FR 66370,
October 26, 2011; 77 FR 69993,
November 21, 2012). On May 11, 2004,
we received a petition to list a total of
225 plant and animal species from the
list of candidate species, including P.
basaltica. Because we previously found
that P. basaltica was warranted for
listing, no further action was taken on
the petition. When it was first identified
as a candidate in 2002, we assigned P.
basaltica a listing priority number (LPN)
of 5, reflecting a species with threats
that were considered high in magnitude
but nonimminent. In 2006 (71 FR
53756), we changed the LPN to 11,
reflecting a species with threats that
were considered moderate to low in
magnitude and nonimminent. The LPN
for P. basaltica remained at 11 in 2007
(72 FR 69034), 2008 (73 FR 75176), 2009
(74 FR 57804), 2010 (75 FR 69222), 2011
(76 FR 66370), and 2012 (77 FR 69993).
Potentilla basaltica is a low-growing,
perennial forb in the Rose family
(Rosaceae) that forms a basal rosette
with low-growing stems and small,
yellow flowers. This species has a
limited geographic range and is known
to occur on approximately 22.7 acres
(ac) (9.2 hectares (ha)) of habitat at
Soldier Meadow in Humboldt County,
Nevada, and Ash Valley in Lassen
County, California (Service 2013x, p. x).
Habitat conditions occupied by the
species differ between these two
locations. At Soldier Meadow, P.
basaltica occurs in or near alkali
meadows, seeps, and marsh habitats
bordering perennial thermal springs,
outflows, and meadow depressions,
while in Ash Valley, P. basaltica occurs
between the floodplain of Ash Creek
and the sagebrush steppe (Service
2013x, p. x). At these two locations, P.
basaltica is known from a total of three
populations (two in Soldier Meadow
and one in Ash Valley), each of which
is located primarily on public lands
managed by the Bureau of Land
Management (BLM; 95 percent). The
only available estimates of abundance
suggest a combined total of between
75,950 and 133,614 individual plants
across all three populations, with most
of these individuals occurring at the two
populations in Soldier Meadow in
Nevada (74,950 to 132,000 individuals)
(Service 2013a, p. 10).
Impacts to Potentilla basaltica and its
habitat identified at the time it was
determined to be a candidate species in
2002—recreational use, livestock
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grazing, roads and off-highway vehicle
(OHV) activity, geothermal exploration,
and nonnative, invasive plant species—
have been substantially reduced since
2002. The BLM implemented several
measures that have been effective in
reducing recreational use impacts to P.
basaltica in Soldier Meadow:
Establishing a designated, centralized
campground, which discourages
dispersed camping in wet meadow
habitats where P. basaltica occurs;
designating walkways away from P.
basaltica habitat; installing interpretive
signs informing recreationists about the
sensitive plant and animal species
found in the wetland and thermal spring
habitats of Soldier Meadow; and use of
a campground host in Soldier Meadow
who interacts with visitors informing
them of designated camping and bathing
areas and providing education about the
sensitive plant and animal species
present in the area (Service 2013a, p.
18).
Other impacts to Potentilla basaltica
also have been greatly reduced since
2002. In 2004, the areas where P.
basaltica occurred in Soldier Meadow
were fenced to exclude domestic
livestock, wild horses, and other large
ungulates; this initiative significantly
reduced livestock grazing impacts to the
species (Service 2013a, p. 20). In 2004,
the BLM also closed roads (authorized
and unauthorized) in Soldier Meadow
that led to spring, riparian, and wetland
areas and limited OHV use to
designated roads and trails (Service
2013a, p. 15). These closures and OHV
restrictions remain in place today and
have effectively reduced impacts to P.
basaltica from roads and OHVs. Within
Soldier Meadow, BLM personnel
coordinate efforts to detect and rapidly
respond to nonnative, invasive plant
species using chemical control and
other treatment methods (Service 2013a,
pp. 19–20). Geothermal exploration
occurred in the Soldier Meadow area
during the 1970s. Portions of Soldier
Meadow P. basaltica population areas
were protected from exploration and
development activities in 1982 when
the BLM designated the area as an Area
of Critical Environmental Concern
(ACEC). In 2003, the BLM expanded the
existing Soldier Meadow ACEC to
provide additional protection for the
desert dace (Eremichthys acros), which
was listed as threatened under the Act
in 1985, as well as to provide additional
protection for P. basaltica (USFWS
1997, p. 22). The Soldier Meadow ACEC
is also designated as a BLM Research
Natural Area.
The Ash Valley, California,
population, which occurs on a much
smaller area and contains many fewer
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plants than the Soldier Meadow
populations (Service 2013a, p. 10), is
located in part on BLM lands designated
as a Research Natural Area and ACEC
and in part on private lands (Service
2013a, pp. 10–11). These BLM lands
have been withdrawn from mining
activity and are excluded from timber
management and woodcutting activity
(Service 2013a, p. 18). In 2008, the BLM
issued a Record of Decision on the
Alturas Resource Area Management
Plan (RMP) and Final Environmental
Impact Statement (BLM 2008a, pp. A–1–
A–10). The RMP identified the need for
establishing a long-term monitoring plot
for Potentilla basaltica and limiting
OHV travel to designated routes within
the Ash Valley ACEC and Research
Natural Area (BLM 2007, p. 2–105).
And, if monitoring data suggested a
decline in numbers or reproductive
viability of P. basaltica, fencing would
be constructed to exclude livestock
grazing (BLM 2007, p. 2–106). The RMP
also proposed the acquisition of private
lands supporting unprotected
populations of special status plants,
including P. basaltica (BLM 2008a, p.
13).
In addition to evaluation of the threats
identified at the time Potentilla
basaltica was determined to be a
candidate species, we also evaluated
potential impacts of climate change on
the species. Although climate change is
likely to affect ecosystem function in
Soldier Meadow and Ash Valley where
P. basaltica occurs, we conclude that
because of uncertainty about specific
effects of climate change on P. basaltica,
the best available scientific and
commercial information does not
indicate at this time that effects of
climate change are likely to threaten the
continued existence of P. basaltica now
or in the foreseeable future (Service
2013a, pp. 22–23).
Potentilla basaltica is a BLM sensitive
species (Service 2013a, p. 2). The stated
objective for BLM sensitive species is to
initiate proactive conservation measures
that reduce or eliminate threats to
minimize the likelihood of and need for
listing (BLM 2008a, 6840.02).
Conservation, as it applies to BLM
sensitive species, is defined as ‘‘the use
of programs, plans, and management
practices to reduce or eliminate threats
affecting the status of the species, or
improve the condition of the species’
habitat on BLM-administered lands’’
(BLM 2008b, Glossary, p. 2).
Potentilla basaltica is not State listed
as endangered or threatened in either
Nevada or California. However, in
California, P. basaltica has a California
Native Plant Society (CNPS) rank of
1B.3 (not very threatened in California,
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with less than 20 percent of occurrences
threatened and low degree and
immediacy of threat or no current
threats known) (CNPS 2013). Plants, like
P. basaltica, with a CNPS 1.B rank must
be fully considered during preparation
of environmental documents relating to
the California Environmental Quality
Act (CEQA) (CNPS 2013).
Based on our analysis of the five
factors identified in section 4(a)(1) of
the Act, we conclude that the previously
recognized impacts to Potentilla
basaltica from present or threatened
destruction, modification, or
curtailment of its habitat or range
(Factor A) (recreational use; OHV use;
introduction of nonnative, invasive
plant species; and trampling by
livestock), do not rise to a level of
significance such that the species is in
danger of extinction now or in the
foreseeable future. We evaluated
additional potential impacts under the
the five listing factors stated above. In
that evaluation we found that potential
impacts such as livestock grazing
(Factors A and E), geothermal
exploration (Factors A and E), herbivory
(Factor B), disease (Factor C), and
climate change (Factor A) to either be of
no concern or insignificant concern at
this time. Additionally, conservation
measures and protection provided by
BLM for species associated with thermal
springs are benefiting P. basaltica, and
we anticipate these conservation
measures and protections to continue to
benefit P. basaltica into the foreseeable
future (in part due to other sensitive and
federally listed species occurring in
these areas). Thus, the existing
regulatory mechanisms are adequate to
protect the species from the potential
impacts (Factor D). See the ‘‘Factors
Affecting the Species’’ section of the
Species Report (Service 2013a, pp.
17–24) for a thorough discussion of all
potential and current threats.
The best available information to
assist us in assessing foreseeable future
for Potentilla basaltica is the time
period associated with management
planning activities. Because the majority
(95 percent) of P. basaltica occupied
areas are on Federal lands that receive
conservation protections resulting from
Federal laws and the regulations and
policies implementing those laws (i.e.,
Federal Land Policy Management Act,
National Environmental Policy Act), we
look to the historical timeframe for
completing management plans and
current planning efforts to assist us in
defining foreseeable future. Based on
this timeframe information, we estimate
the foreseeable future to be at least 30
years (i.e., 2043) for this analysis.
Therefore, we conclude that P. basaltica
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does not meet the definition of an
endangered or threatened species and
thus is no longer warranted for listing
under the Act. With the publication of
this notice, P. basaltica will be removed
from the list of candidate species.
Proposed Threatened Species Status for
Ivesia webberi
Previous Federal Actions
We identified Ivesia webberi as a
candidate in the June 13, 2002,
Candidate Notice of Review (CNOR, 67
FR 40657). Ivesia webberi was included
in all subsequent annual CNORs (69 FR
24875, May 4, 2004; 70 FR 24869, May
11, 2005; 71 FR 53756, September 12,
2006; 72 FR 69033, December 6, 2007;
73 FR 75175, December 10, 2008; 74 FR
57803, November 9, 2009; 75 FR 69221,
November 10, 2010; and 76 FR 66370,
October 26, 2011; 77 FR 69993,
November 21, 2012). On May 11, 2004,
we received a petition to list a total of
225 plant and animal species from the
list of candidate species, including I.
webberi. Because we previously found
the species was warranted for listing, no
further action was taken on the petition.
When it was first identified as a
candidate in 2002 (67 FR 40657), we
assigned I. webberi a listing priority
number (LPN) of 5, reflecting a species
with threats that were considered high
in magnitude but nonimminent; the
LPN remained at 5 in all subsequent
CNORs.
Background
In this and the following section, we
summarize from information on species
status and potential threats that we
evaluated in order to determine that
Ivesia webberi meets the Act’s definition
of a threatened species (section 3(20)). A
thorough review of information that we
relied on in making this
determination—including information
on taxonomy, life history, ecology,
population distribution and abundance,
and threats—is presented in the Ivesia
webberi (Webber’s ivesia) Species
Report (Service 2013b, entire; available
at https://www.regulations.gov (in the
Search box, enter FWS–R8–ES–2013–
0079, which is the docket number for
this rulemaking).
Ivesia webberi is a low, spreading
perennial forb in the Rose family
(Rosaceae) with grayish-green foliage,
dark-red, wiry stems, and headlike
clusters of small, yellow flowers. This
species occupies vernally moist, rocky,
clay soils with an argillic horizon that
shrink and swell upon drying and
wetting in open to sparsely vegetated
areas associated with an Artemisia
arbuscula (low sagebrush)–perennial
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bunchgrass–forb community. The
specialized soils are well developed, a
process estimated to take 1,000 years.
Limited seed dispersal and apparent
limited recruitment further restrict the
occupied range and distribution of I.
webberi.
Ivesia webberi is currently known to
occupy a total of approximately 165 ac
(66.8 ha) within five counties in
California and Nevada along the
transition zone between the eastern edge
of the northern Sierra Nevada and the
northwestern edge of the Great Basin
(Service 2013b, p. 2). The species is
known historically from a total of 17
populations, but 1 has been extirpated
and a portion of another (1 of 4
subpopulations) is possibly extirpated.
Of the remaining 16 populations, the
status of 4 is unknown, and we
currently are uncertain whether the
species still persists at these locations
(Service 2013b, p. 2). For the remaining
10 populations where the species’ status
is better understood, 6 occur on areas
that are less than 5 ac (2 ha) each.
Reliable estimation of population sizes
or trends in I. webberi is complicated
because past population estimates have
usually been obtained by different
observers employing a variety of
methodologies and varying levels of
survey effort (Service 2013b, p. 2).
Summary of Biological Status and
Threats
Due to the restricted range,
specialized habitat requirements, and
limited recruitment and dispersal of
Ivesia webberi, populations of this
species are vulnerable to ongoing and
future threats that affect both individual
plants and their habitat. The primary
threats to I. webberi are the additive and
synergistic effects due to nonnative,
invasive plant species and modified fire
regime (Service 2013b, pp. 31–32).
Nonnative, invasive plant species, such
as Bromus tectorum (cheatgrass), Poa
bulbosa (bulbous bluegrass), and
Taeniatherum caput-medusae
(medusahead), have become established
and are part of the associated plant
community at 12 of the 16 extant
populations of I. webberi. Nonnative,
invasive plant species negatively affect
I. webberi through competition,
displacement, and degradation of the
quality and composition of the
Artemisia arbuscula–perennial
bunchgrass–forb community in which I.
webberi occurs. In addition to these
effects, these nonnative, invasive plant
species, once established, contribute
fuels that increase the frequency and
likelihood of wildfire in I. webberi
habitat.
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Wildfire was historically infrequent in
the Great Basin because the native plant
communities made up of annuals and
perennial bunchgrasses did not provide
sufficient fine fuels to carry large-scale
wildfires. The bare spaces between
widely spaced shrubs and the low fuel
load of native annuals and perennial
bunchgrasses generally prevented fire
from spreading, so the fires that did
burn were restricted to isolated patches.
In Artemisia arbuscula communities,
such as those that Ivesia webberi
inhabits, the average fire return interval
is greater than 100 years, due to natural
lower productivity and fuel
accumulations (Service 2013b, p. 24).
However, beginning in the late 1800s,
the widespread invasion of nonnative
plant species, particularly annual
grasses, has created a bed of continuous
fine fuels across the sagebrush
landscape in many areas (Service 2013b,
p. 24). This increase in fine fuels created
by nonnative, invasive plants has
resulted in more frequent fires that burn
larger areas and often burn at higher
intensities. Post-fire conditions further
facilitate the invasion and establishment
of nonnative, invasive plant species,
thus creating a positive feedback loop
between increased wildfire and the
spread of these species (Service 2013b,
p. 24). Ten of the 16 extant I. webberi
populations have experienced wildfire
since 1984 (Service 2013b, p. 24).
Because I. webberi did not evolve with
frequent fire and does not possess
adaptations that would help it persist in
a frequent-fire fire regime, wildfires are
expected to have adverse populationlevel impacts on the species. In
addition, increased wildfire frequency
within the species’ range results in
increased wildfire suppression
activities, which also may adversely
affect I. webberi populations (Service
2013b, pp. 22, 24–25).
Other threats impacting Ivesia webberi
populations include OHV use and
roads, development, livestock grazing,
and climate change (Service 2013b, pp.
25–31). OHV impacts to I. webberi
populations have increased during the
past 20 years as population growth and
associated development have increased
(Bergstrom 2009, p. 22), especially in
the Reno urban area where 6 of the 16
populations occur. Ten of 16 extant I.
webberi populations are adjacent to or
intersected by dirt roads and have been
impacted to some degree by road
development and OHV use (Service
2013b, pp. 25–26). Roads cause habitat
loss and degradation and when vehicles
drive off existing roads and trails they
can crush plants, compact soils, and
provide a means for nonnative, invasive
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plant species to invade otherwise
remote, intact habitats. The U.S. Forest
Service concluded that a 2006 travel
management plan for Peavine Mountain
would benefit rare plant species,
including I. webberi; however,
designated roads open to all vehicles
continue to bisect I. webberi
populations, and unauthorized OHV use
remains high within I. webberi
populations on Forest Service lands in
the Reno urban area (Service 2013b, p.
26).
Development, which results in direct
mortality, habitat loss, degradation, and
fragmentation, has resulted in the
extirpation of one Ivesia webberi
population and the loss of a portion of
another population (Service 2013x, p.
x). Residential or commercial
development is ongoing or planned at
each of the four Nevada populations
located on private lands. In addition,
construction of a 120-kV overhead
transmission line may impact two I.
webberi populations located on Forest
Service lands (Service 2013b, p. 26).
Livestock grazing has the potential to
result in negative effects to I. webberi
due to trampling and substrate
disturbance, but this situation is
dependent on factors such as stocking
rate and season of use. Two I. webberi
populations occur in areas that are
currently grazed by cattle, and another
seven populations occur within vacant
grazing allotments that could be
reopened to grazing to alleviate grazing
pressures on nearby allotments (Service
2013b, p. 29).
Climate change is likely to affect
Ivesia webberi, although it is difficult to
project specific effects. In the Great
Basin, temperatures have risen 0.9 to
2.7 °F (0.5 to 1.5 °C) in the last 100 years
and are projected to warm another 3.8
to 10.3 °F (2.1 to 5.7 °C) over the rest of
the century (Service 2013b, p. 30).
Under current climate change
projections, we anticipate that future
climatic conditions will favor the
further spread of nonnative, invasive
plants and increase the frequency,
spatial extent, and severity of wildfires
(Service 2013b, p. 30). Alteration of
temperature and precipitation patterns
as a result of climate change also may
result in decreased survivorship of I.
webberi by causing physiological stress,
altering phenology, and reducing
reproduction or seedling establishment.
Because most of the habitat where the
species is known to occur is located on
Federal lands (69 percent of occupied
habitat occurs on Forest Service lands,
and 10 percent of occupied habitat
occurs on BLM lands), Ivesia webberi
receives some conservation protections
resulting from Federal laws and the
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regulations and policies implementing
those laws (e.g., the National Forest
Management Act, Federal Land Policy
Management Act, National
Environmental Policy Act). Ivesia
webberi receives special consideration
on Federal lands because it is classified
as a sensitive species by both the Forest
Service and BLM (Service 2013b, pp. 3–
4). The species also is classified as
threatened with extinction and fully
protected by the State of Nevada;
removing or destroying I. webberi and
other fully protected plants is
prohibited except under special permit
issued by the Nevada Division of
Forestry (NDF 2013). Ivesia webberi is
not listed as endangered or threatened
under the California Endangered
Species Act (CESA), but has a California
Native Plant Society (CNPS) rare plant
rank of 1B.1 (seriously threatened in
California with over 80 percent of
occurrences threatened and high degree
and immediacy of threat (CNPS 2013).
Ivesia webberi and other plants with a
CNPS 1B rank must be fully considered
during preparation of environmental
documents relating to the California
Environmental Quality Act (CEQA)
(CNPS 2013).
The Forest Service drafted a
rangewide conservation strategy for
Ivesia webberi to guide conservation
actions for the species on Forest Service
lands (Service 2013b, pp. 21–22). The
conservation strategy, which was signed
in 2010, will result in long-term benefits
to I. webberi populations located on
Forest Service lands (Bergstrom 2009,
pp. 1–46). However, we expect that the
landscape-level threats of nonnative,
invasive plants and increased wildfire
will continue to adversely affect I.
webberi populations across the species’
range (Service 2013b, p. 22).
Determination
We have carefully assessed the best
scientific and commercial information
available regarding the past, present,
and future threats to Ivesia webberi. We
considered the five factors identified in
section 4(a)(1) of the Act in determining
whether I. webberi meets the Act’s
definition of an endangered species
(section 3(6)) or threatened species
(section 3(20)). We find that I. webberi
is threatened by the present or
threatened destruction, modification, or
curtailment of its habitat or range
(Factor A). Present or threatened
destruction, modification, or
curtailment of its habitat or range
include habitat loss and degradation
due to nonnative, invasive plants,
modified fire regime (increased
wildfire), OHV use and roads,
development, livestock grazing, and
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climate change. Of these, we consider
the additive and synergistic effects of
nonnative, invasive plants and
increased wildfire to be the greatest
threats to I. webberi.
Nonnative, invasive plant species
such as Bromus tectorum and
Taeniatherum caput-medusae can
outcompete and displace I. webberi and
result in increased frequency, spatial
extent, and severity of wildfires because
of the increase in fine fuels they
produce. Twelve of the 16 extant
populations have already been invaded
by nonnative, invasive plant species and
10 of the 16 extant populations have
been impacted by wildfire since 1984.
Because there are currently no feasible
means for controlling the spread of
widespread nonnative, invasive plant
species such as B. tectorum and T.
caput-medusae, we expect that wildfires
will continue to impact I. webberi
populations. Increased temperatures
and altered precipitation patterns due to
climate change are projected to lead to
further increases in wildfire and
nonnative, invasive plants. OHV use
and roads, development, and livestock
grazing are having impacts on certain I.
webberi populations.
We did not identify threats to Ivesia
webberi due to overutilization for
commercial, recreational, scientific, or
educational purposes (Factor B); disease
or predation (Factor C); or other natural
or manmade factors affecting its
continued existence (Factor E).
Although regulatory mechanisms
(Factor D) are in place that provide
some protection to I. webberi and its
habitat, these mechanisms do not
completely alleviate all of the threats
currently acting on the species.
The Act defines an endangered
species as any species that is ‘‘in danger
of extinction throughout all or a
significant portion of its range’’ and a
threatened species as any species ‘‘that
is likely to become endangered
throughout all or a significant portion of
its range within the foreseeable future.’’
Available population information for
Ivesia webberi is not useful for
determining trends because population
estimates have been obtained by
different observers employing a variety
of means and levels of survey effort.
Nonnative, invasive plant species,
wildfire, and OHV activity are present
impacts throughout the range of I.
webberi and in some cases are found to
be increasing for many years with data
in particular related to increased
recreational OHV activity over the past
20 years (Service 2013b, pp. 25–26) and
increased wildfire and suppression
activities over the past 30 years (Service
2013b, pp. 22, 24–25). Additionally,
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consideration. The range of a species
can theoretically be divided into
portions an infinite number of ways.
However, analyzing portions of the
range that are not reasonably likely to be
both (1) significant and (2) endangered
or threatened would serve no purpose.
To identify only those portions that
warrant further consideration, we
determine whether substantial
information indicates that: (1) The
portions may be significant, and (2) the
species may be in danger of extinction
there or likely to become so within the
foreseeable future. In practice, a key part
of this analysis is whether the threats
are geographically concentrated in some
way. If the threats to the species are
essentially uniform throughout its
range, no portion is likely to warrant
further consideration. Moreover, if any
concentration of threats applies only to
portions of the species’ range that are
not significant, such portions will not
warrant further consideration.
If we identify portions that warrant
further consideration, we then
determine whether the species is
endangered or threatened in these
portions of its range. Depending on the
biology of the species, its range, and the
threats it faces, the Service may address
either the significance question or the
status question first. Thus, if the Service
considers significance first and
determines that a portion of the range is
not significant, the Service need not
determine whether the species is
endangered or threatened there.
Likewise, if the Service considers status
first and determines that the species is
not endangered or threatened in a
portion of its range, the Service need not
determine if that portion is significant.
However, if the Service determines that
both a portion of the range of a species
is significant and the species is
endangered or threatened there, the
Service will specify that portion of the
range as endangered or threatened
under section 4(c)(1) of the Act.
The primary threats to Ivesia webberi
occur throughout the species’ range and
are not restricted to or concentrated in
any particular portion of that range. The
Significant Portion of the Range
primary threats of nonnative, invasive
Having determined that Ivesia webberi plants and increased wildfire are
meets the Act’s definition of a
impacting I. webberi populations
threatened species, we must next
throughout the California and Nevada
consider whether there are any
portions of the species’ range. Climate
significant portions of its range where I. change also is acting on I. webberi
webberi is presently in danger of
throughout the species’ range. Thus, we
extinction and thus meets the definition conclude that threats impacting I.
of an endangered species. In
webberi are not concentrated in certain
determining whether a species is
areas and, thus, there are no significant
endangered or threatened in a
portions of its range where the species
should be classified as an endangered
significant portion of its range, we first
identify any portions of the range of the species. Accordingly, our proposal to
list I. webberi as a threatened species
species that warrant further
given current climate change
projections, we anticipate that future
climatic conditions will favor invasion
by nonnative, invasive plant species,
which will further contribute to
increases in frequency, spatial extent,
and severity of wildfires (Service 2013b,
pp. 29–31). Based on the timeframe
associated with the documented
increased level of some threats over the
past 30 years and the effects of climate
change projections on these threats, we
estimate the foreseeable future to be at
least 30 years (i.e., 2043).
We find that Ivesia webberi is not
presently in danger of extinction
throughout all of its range, but that it is
likely to become endangered throughout
all of its range in the foreseeable future.
We find that I. webberi is not presently
in danger of extinction because the
species is characterized by multiple
populations spread across northeastern
California and northwestern Nevada and
that, in total, these populations provide
sufficient redundancy (multiple
populations distributed across the
landscape), resiliency (capacity for a
species to recover from periodic
disturbance), and representation (range
of variation found in a species) such
that I. webberi is not at immediate risk
of extinction. However, because
multiple threats (nonnative, invasive
plants, increased wildfire, OHV use and
roads, development, livestock grazing,
and climate change) are impacting many
of the I. webberi populations and
because additive and synergistic effects
due to nonnative, invasive plants,
increased wildfire, and climate change
are likely to continue and increase in
the future, we find that I. webberi is
likely to become an endangered species
throughout all of its range in the
foreseeable future. Therefore, on the
basis of the best available scientific and
commercial information, we propose
listing I. webberi as a threatened species.
Under the Act and our implementing
regulations, a species may warrant
listing if it is endangered or threatened
throughout all or a significant portion of
its range.
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applies throughout the species’ entire
range.
Available Conservation Measures
Resulting From Listing
Conservation measures provided to
species listed as endangered or
threatened under the Act include
recognition, recovery actions,
requirements for Federal protection, and
prohibitions against certain practices.
Recognition through listing results in
public awareness and conservation by
Federal, State, Tribal, and local
agencies, private organizations, and
individuals. The Act provides direction
for cooperation with the States and
requires that recovery actions be carried
out for all listed species. The protection
required by Federal agencies and the
prohibitions against certain activities
are discussed, in part, below.
The primary purpose of the Act is the
conservation of endangered and
threatened species and the ecosystems
upon which they depend. The ultimate
goal of such conservation efforts is the
recovery of these listed species, so that
they no longer need the protective
measures of the Act. Subsection 4(f) of
the Act requires the Service to develop
and implement recovery plans for the
conservation of endangered and
threatened species. The recovery
planning process involves the
identification of actions that are
necessary to halt or reverse the species’
decline by addressing the threats to its
survival and recovery. The goal of this
process is to restore listed species to a
point where they are secure, selfsustaining, and functioning components
of their ecosystems.
Recovery planning includes the
development of a recovery outline
shortly after a species is listed and
preparation of a draft and final recovery
plan. The recovery outline guides the
immediate implementation of urgent
recovery actions and describes the
process to be used to develop a recovery
plan. Revisions of the plan may be done
to address continuing or new threats to
the species, as new substantive
information becomes available. The
recovery plan identifies site-specific
management actions that set a trigger for
review of the five factors that control
whether a species remains endangered
or may be downlisted or delisted, and
methods for monitoring recovery
progress. Recovery plans also establish
a framework for agencies to coordinate
their recovery efforts and provide
estimates of the cost of implementing
recovery tasks. Recovery teams
(composed of species experts, Federal
and State agencies, nongovernmental
organizations, and stakeholders) are
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often established to develop recovery
plans. When completed, the recovery
outline, draft recovery plan, and the
final recovery plan will be available on
our Web site (https://www.fws.gov/
endangered), or from our Nevada Fish
and Wildlife Office (see FOR FURTHER
INFORMATION CONTACT).
Implementation of recovery actions
generally requires the participation of a
broad range of partners, including other
Federal agencies, States, Tribal,
nongovernmental organizations,
businesses, and private landowners.
Examples of recovery actions include
habitat restoration (e.g., restoration of
native vegetation), research, captive
propagation and reintroduction, and
outreach and education. The recovery of
many listed species cannot be
accomplished solely on Federal lands
because their range may occur primarily
or solely on non-Federal lands. To
achieve recovery of these species
requires cooperative conservation efforts
on private, State, and Tribal lands.
If Ivesia webberi is listed, funding for
recovery actions will be available from
a variety of sources, including Federal
budgets, State programs, and cost share
grants for non-Federal landowners, the
academic community, and
nongovernmental organizations. In
addition, pursuant to section 6 of the
Act, the States of California and Nevada
would be eligible for Federal funds to
implement management actions that
promote the protection or recovery of I.
webberi. Information on our grant
programs that are available to aid
species recovery can be found at:
https://www.fws.gov/grants.
Although Ivesia webberi is only
proposed for listing under the Act at
this time, please let us know if you are
interested in participating in recovery
efforts for this species. Additionally, we
invite you to submit any new
information on this species whenever it
becomes available and any information
you may have for recovery planning
purposes (see FOR FURTHER INFORMATION
CONTACT).
Section 7(a) of the Act requires
Federal agencies to evaluate their
actions with respect to any species that
is proposed or listed as an endangered
or threatened species and with respect
to its critical habitat, if any is
designated. Regulations implementing
this interagency cooperation provision
of the Act are codified at 50 CFR Part
402. Section 7(a)(4) of the Act requires
Federal agencies to confer with the
Service on any action that is likely to
jeopardize the continued existence of a
species proposed for listing or result in
destruction or adverse modification of
proposed critical habitat. If a species is
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listed subsequently, section 7(a)(2) of
the Act requires Federal agencies to
ensure that activities they authorize,
fund, or carry out are not likely to
jeopardize the continued existence of
the species or destroy or adversely
modify its critical habitat. If a Federal
action may affect a listed species or its
critical habitat, the responsible Federal
agency must enter into consultation
with the Service.
Federal agency actions within Ivesia
webberi’s habitat that may require
conference or consultation or both as
described in the preceding paragraph
include land management actions that
could result in impacts to soil
characteristics or seedbank viability,
pollinators or their habitat, and
associated native vegetation community,
and any other landscape-altering
activities on Federal lands, such as:
Reauthorization of grazing permits by
the BLM and the U.S. Forest Service,
issuance of section 404 Clean Water Act
(33 U.S.C. 1251 et seq.) permits by the
U.S. Army Corps of Engineers,
construction and management of gas
pipeline and power line rights-of-way
by the Federal Energy Regulatory
Commission, and construction and
maintenance of roads or highways by
the Federal Highway Administration.
Our policy, as published in the
Federal Register on July 1, 1994 (59 FR
34272), is to identify to the maximum
extent practicable at the time a species
is listed, those activities that would or
would not constitute a violation of
section 9 of the Act. The intent of this
policy is to increase public awareness of
the effect of a proposed listing on
proposed and ongoing activities within
the range of species proposed for listing.
The Act and its implementing
regulations set forth a series of general
prohibitions and exceptions that apply
to endangered and threatened plants.
The prohibitions of section 9(a)(2) of the
Act, codified at 50 CFR 17.61, apply to
endangered plants. These prohibitions,
in part, make it illegal for any person
subject to the jurisdiction of the United
States to import or export, transport in
interstate or foreign commerce in the
course of a commercial activity, sell or
offer for sale in interstate or foreign
commerce, or remove and reduce the
species to possession from areas under
Federal jurisdiction. These take
prohibitions for endangered plant
species are extended to threatened plant
species under 50 CFR 17.71, except the
take prohibitions do not extend to seeds
of cultivated specimens, provided that a
statement that the seeds are of
‘‘cultivated origin’’ accompanies the
seeds or their container. Also, 50 CFR
17.71(b) authorizes Service and State
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conservation agency employees to
remove and reduce to possession from
Federal lands those threatened plant
species covered by cooperative
agreements under section 6(c) of the
Act.
We may issue permits to carry out
otherwise prohibited activities
involving endangered and threatened
wildlife species under certain
circumstances. Regulations governing
permits are codified at 50 CFR 17.62 for
endangered plants, and at 17.72 for
threatened plants. With regard to
endangered plants, a permit must be
issued for the following purposes: For
scientific purposes or to enhance the
propagation or survival of the species.
Under section 4(d) of the ESA, the
Secretary has discretion to issue such
regulations as he deems necessary and
advisable to provide for the
conservation of threatened species. Our
implementing regulations (50 CFR
17.71) for threatened plants generally
incorporate the prohibitions of section 9
of the Act for endangered plants, except
when a ‘‘special rule’’ promulgated
pursuant to section 4(d) of the Act has
been issued with respect to a particular
threatened species. In such a case, the
general prohibitions in 50 CFR 17.61
would not apply to that species, and
instead, the special rule would define
the specific take prohibitions and
exceptions that would apply for that
particular threatened species, which we
consider necessary and advisable to
conserve the species. The Secretary also
has the discretion to prohibit by
regulation with respect to a threatened
species any act prohibited by section
9(a)(2) of the ESA. Exercising this
discretion, which has been delegated to
the Service by the Secretary, the Service
has developed general prohibitions that
are appropriate for most threatened
species in 50 CFR 17.71 and exceptions
to those prohibitions in 50 CFR 17.62.
We are not proposing to promulgate a
special section 4(d) rule, and as a result,
all of the section 9 prohibitions,
including the ‘‘take’’ prohibitions, will
apply to the Ivesia webberi.
Questions regarding whether specific
activities would constitute a violation of
section 9 of the Act should be directed
to the U.S. Fish and Wildlife Service,
Nevada Fish and Wildlife Office (see
FOR FURTHER INFORMATION CONTACT).
In addition to the take prohibitions
that would be afforded to Ivesia webberi
throughout its range in California and
Nevada under section 9 of the Act, I.
webberi is listed as threatened by the
State of Nevada pursuant to Nevada
Revised Statute (N.R.S.) 527.260–.300
and was added to the State list of fully
protected species of native flora (Nevada
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Administrative Code 527.010) in 2004.
Removing or destroying plants on the
State’s fully protected list is prohibited
except under special permit issued by
the Nevada Division of Forestry (N.R.S.
527.270). Ivesia webberi is not listed by
the State of California under the
California Endangered Species Act
(CESA), so removal or destruction of
plants is not currently prohibited by
State law in California. Ivesia webberi
does have a California Native Plant
Society rare plant rank of 1B.1 and must
be fully considered during preparation
of environmental documents relating to
the California Environmental Quality
Act (CEQA) (see Summary of Biological
Status and Threats section).
Required Determinations
Clarity of the Rule
We are required by Executive Orders
12866 and 12988 and by the
Presidential Memorandum of June 1,
1998, to write all rules in plain
language. This means that each rule we
publish must:
(1) Be logically organized;
(2) Use the active voice to address
readers directly;
(3) Use clear language rather than
jargon;
(4) Be divided into short sections and
sentences; and
(5) Use lists and tables wherever
possible.
If you feel that we have not met these
requirements, send us comments by one
of the methods listed in the ADDRESSES
section. To better help us revise the
rule, your comments should be as
specific as possible. For example, you
should tell us the numbers of the
sections or paragraphs that are unclearly
written, which sections or sentences are
too long, the sections where you feel
lists or tables would be useful, etc.
Paperwork Reduction Act of 1995 (44
U.S.C. 3501 et seq.)
This rule does not contain any new
collections of information that require
approval by OMB under the Paperwork
Reduction Act of 1995 (44 U.S.C. 3501
et seq.). This rule will not impose
recordkeeping or reporting requirements
on State or local governments,
individuals, businesses, or
organizations. An agency may not
conduct or sponsor, and a person is not
required to respond to, a collection of
information unless it displays a
currently valid OMB control number.
National Environmental Policy Act (42
U.S.C. 4321 et seq.)
We have determined that
environmental assessments and
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environmental impact statements, as
defined under the authority of the
National Environmental Policy Act
(NEPA; 42 U.S.C. 4321 et seq.), need not
be prepared in connection with listing
a species as an endangered or
threatened species under the
Endangered Species Act. We published
a notice outlining our reasons for this
determination in the Federal Register
on October 25, 1983 (48 FR 49244).
Government-to-Government
Relationship With Tribes
In accordance with the President’s
memorandum of April 29, 1994
(Government-to-Government Relations
with Native American Tribal
Governments; 59 FR 22951), Executive
Order 13175 (Consultation and
Coordination With Indian Tribal
Governments), and the Department of
the Interior’s manual at 512 DM 2, we
readily acknowledge our responsibility
to communicate meaningfully with
recognized Federal Tribes on a
government-to-government basis. In
accordance with Secretarial Order 3206
of June 5, 1997 (American Indian Tribal
Rights, Federal-Tribal Trust
Responsibilities, and the Endangered
Species Act), we readily acknowledge
our responsibilities to work directly
with tribes in developing programs for
healthy ecosystems, to acknowledge that
tribal lands are not subject to the same
controls as Federal public lands, to
remain sensitive to Indian culture, and
to make information available to tribes.
References Cited
A complete list of references cited in
this rulemaking is available on the
Internet at https://www.regulations.gov
and upon request from the Nevada Fish
and Wildlife Office (see FOR FURTHER
INFORMATION CONTACT).
Authors
The primary authors of this proposed
rule are the staff members of the
Service’s Nevada Fish and Wildlife
Office and Region 8 Regional Office.
List of Subjects in 50 CFR Part 17
Endangered and threatened species,
Exports, Imports, Reporting and
recordkeeping requirements,
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:
■
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Federal Register / Vol. 78, No. 149 / Friday, August 2, 2013 / Proposed Rules
Authority: 16 U.S.C. 1361–1407; 1531–
1544; and 4201–4245; unless otherwise
noted.
§ 17.12
(Webber’s ivesia)’’ to the List of
Endangered and Threatened Plants in
alphabetical order under ‘‘Flowering
Plants’’ to read as follows:
2. Amend § 17.12 paragraph (h), by
adding an entry for ‘‘Ivesia webberi
■
*
Endangered and threatened plants.
*
*
(h) * * *
*
Species
Historic range
Scientific name
Family
Status
*
U.S.A. (CA, NV) .....
*
Rosaceae ...............
When listed
Common name
*
Critical
habitat
Special
rules
FLOWERING PLANTS
*
Ivesia webberi ..........
*
Webber’s ivesia ......
*
*
*
*
*
*
*
*
[FR Doc. 2013–18579 Filed 8–1–13; 8:45 am]
BILLING CODE 4310–55–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 130408348–3348–01]
RIN 0648–BD17
Fisheries of the Northeastern United
States; Atlantic Herring Fishery;
Framework Adjustment 2 and
Specifications
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Proposed rule, request for
comments.
AGENCY:
NMFS proposes regulations to
implement Framework Adjustment 2 to
the Atlantic herring Fishery
Management Plan and the 2013–2015
fishery specifications for the Atlantic
herring fishery. Framework 2 would
allow the New England Fishery
Management Council to split annual
catch limits seasonally for the four
Atlantic herring management areas, and
the carryover of unharvested catch, up
to 10 percent for each area’s annual
catch limit. The specifications would set
catch specifications for the herring
fishery for the 2013–2015 fishing years
and would establish seasonal splits for
management areas 1A and 1B as
recommended to NMFS by the New
England Fishery Management Council.
emcdonald on DSK67QTVN1PROD with PROPOSALS
SUMMARY:
17:00 Aug 01, 2013
Jkt 229001
Public comments must be
received by September 3, 2013.
ADDRESSES: Copies of supporting
documents used by the New England
Fishery Management Council (Council),
including the Environmental
Assessment (EA) and Regulatory Impact
Review (RIR)/Initial Regulatory
Flexibility Analysis (IRFA), are
available from: Thomas A. Nies,
Executive Director, New England
Fishery Management Council, 50 Water
Street, Mill 2, Newburyport, MA 01950,
telephone (978) 465–0492. The EA/RIR/
IRFA is also accessible via the Internet
at https://www.nero.nmfs.gov.
You may submit comments, identified
by NOAA–NMFS–2013–0120, by any
one of the following methods:
—Electronic Submission: Submit all
electronic public comments via the
Federal e-Rulemaking Portal. Go to
www.regulations.gov/#!docketDetail;
D=NOAA-NMFS-2013-0120, click the
‘‘Comment Now!’’ icon, complete the
required fields, and enter or attach your
comments;
—Mail: Submit written comments to
NMFS, Northeast Regional Office, 55
Great Republic Drive, Gloucester, MA
01930. Mark the outside of the envelope
‘‘Comments on Framework 2 and 2013–
2015 Herring Specifications;’’
—Fax: (978) 281–9135, Attn: Carrie
Nordeen.
Instructions: Comments sent by any
other method, to any other address or
individual, or received after the end of
the comment period, may not be
considered by NMFS. All comments
received are a part of the public record
and will generally be posted for public
viewing on www.regulations.gov
without change. All personal identifying
information (e.g., name, address, etc.),
confidential business information, or
otherwise sensitive information
submitted voluntarily by the sender will
be publicly accessible. NMFS will
accept anonymous comments (enter ‘‘N/
A’’ in the required fields if you wish to
PO 00000
Frm 00075
Fmt 4702
*
....................
*
DATES:
Dated: July 23, 2013.
Signed:
Stephen Guertin,
Director, U.S. Fish and Wildlife Service.
VerDate Mar<15>2010
*
*
T
Sfmt 4702
*
*
NA
NA
*
remain anonymous). Attachments to
electronic comments will be accepted in
Microsoft Word, Excel, or Adobe PDF
file formats only.
FOR FURTHER INFORMATION CONTACT:
Carrie Nordeen, Fishery Policy Analyst,
(978) 281–9272, fax (978) 281–9135.
SUPPLEMENTARY INFORMATION:
Background
Regulations implementing the
Atlantic Herring Fishery Management
Plan (FMP) for herring appear at 50 CFR
part 648, subpart K. The regulations at
§ 648.200 require the Council to
recommend herring specifications for
NMFS’ review and proposal in the
Federal Register, including the
overfishing limit (OFL), acceptable
biological catch (ABC), annual catch
limit (ACL), optimum yield (OY),
domestic annual harvest (DAH),
domestic annual processing (DAP), U.S.
at-sea processing (USAP), border
transfer (BT), the sub-ACL for each
management area, including seasonal
periods as allowed by § 648.201(d) and
modifications to sub-ACLs as allowed
by § 648.201(f), and the amount to be set
aside for the research set aside (RSA) (3
percent of the sub-ACL from any
management area) for up to 3 years.
The proposed 2013–2015 herring
specifications are based on the
provisions currently in the Herring
FMP, and provide the necessary
elements to comply with the ACL and
accountability measure (AM)
requirements of the Magnuson-Stevens
Fishery Conservation and Management
Act (MSA). This action also includes
measures proposed in Framework
Adjustment 2 (Framework 2) to the
FMP.
Framework 2 Measures
Framework 2 would allow seasonal
splits of sub-ACLs for all herring
management areas through the
specifications process. The Herring FMP
already authorizes seasonal splits of the
E:\FR\FM\02AUP1.SGM
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Agencies
[Federal Register Volume 78, Number 149 (Friday, August 2, 2013)]
[Proposed Rules]
[Pages 46889-46897]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2013-18579]
[[Page 46889]]
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[FWS- R8-ES-2013-0079; 4500030113]
RIN 1018-AZ12
Endangered and Threatened Wildlife and Plants; 12-Month Finding
and Candidate Removal for Potentilla basaltica; Proposed Threatened
Species Status for Ivesia webberi
AGENCY: Fish and Wildlife Service, Interior.
ACTION: 12-month petition finding; proposed rule.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service (Service), announce a
12-month finding on a petition to list the plant Potentilla basaltica
(Soldier Meadow cinquefoil) as an endangered or threatened species.
After review of the best available scientific information, we find that
listing Potentilla basaltica as an endangered or threatened species
under the Endangered Species Act (Act) is no longer warranted, and,
therefore, we are removing this species from the candidate list. We
propose to list the plant Ivesia webberi (Webber's ivesia) as a
threatened species under the Act. If finalized, the effect of this
regulation would be to add Ivesia webberi to the List of Endangered and
Threatened Plants and extend the Act's protections to this species.
Elsewhere in today's Federal Register, we propose to designate critical
habitat under the Act for Ivesia webberi.
DATES: We will accept comments received or postmarked on or before
October 1, 2013. Comments submitted electronically using the Federal
eRulemaking Portal (see ADDRESSES section, below) must be received by
11:59 p.m. Eastern Time on the closing date. We must receive requests
for public hearings, in writing, at the address shown in FOR FURTHER
INFORMATION CONTACT by September 16, 2013.
Public meeting: We will hold a public meeting on this proposed rule
on September 10, 2013, in Reno, NV, from 4:00 to 6:00 p.m. People
needing reasonable accommodations in order to attend and participate in
the public hearing should contact Jeannie Stafford, Nevada Fish and
Wildlife Office, as soon as possible (see FOR FURTHER INFORMATION
CONTACT).
ADDRESSES: You may submit comments by one of the following methods:
(1) Electronically: Go to the Federal eRulemaking Portal: https://www.regulations.gov. In the Search box, enter FWS-R8-ES-2013-0079,
which is the docket number for this rulemaking. Then, in the Search
panel on the left side of the screen, under the Document Type heading,
click on the Proposed Rules link to locate this document. You may
submit a comment by clicking on ``Comment Now!''
(2) By hard copy: Submit by U.S. mail or hand-delivery to: Public
Comments Processing, Attn: FWS-R8-ES-2013-0079; Division of Policy and
Directives Management; U.S. Fish and Wildlife Service; 4401 N. Fairfax
Drive, MS 2042-PDM; Arlington, VA 22203.
We request that you send comments only by the methods described
above. We will post all comments on https://www.regulations.gov. This
generally means that we will post any personal information you provide
us (see the Public Comments section below for more information).
FOR FURTHER INFORMATION CONTACT: Edward D. Koch, State Supervisor, U.S.
Fish and Wildlife Service, Nevada Fish and Wildlife Office, 1340
Financial Boulevard, Suite 234, Reno, NV 89502, by telephone 775-861-
6300, or by facsimile 775-861-6301. Persons who use a
telecommunications device for the deaf (TDD) may call the Federal
Information Relay Service (FIRS) at 800-877-8339.
SUPPLEMENTARY INFORMATION:
Executive Summary
Why we need to publish a rule. Under the Act, if we find a species
to be endangered or threatened throughout all or a significant portion
of its range, we are required to promptly publish a proposal in the
Federal Register and make a final determination on our proposal within
1 year. We designate critical habitat to the maximum extent prudent and
determinable, for any species determined to be an endangered or
threatened species under the Act. Listing a species as an endangered or
threatened species and designations and revisions of critical habitat
can only be completed by issuing a rule.
What this rule does. We propose the listing of Ivesia webberi
(Webber's ivesia) as a threatened species. Ivesia webberi is a
candidate species for which we have on file sufficient information on
biological vulnerability and threats to support preparation of a
listing proposal, but for which development of a listing regulation has
been precluded by other higher-priority listing activities. This rule
reassesses all currently available information regarding status of and
threats to I. webberi. Elsewhere in today's Federal Register, we
propose to designate critical habitat for I. webberi under the Act.
The basis for our action. Under the Act, we can determine that a
species is an endangered or threatened species based on any of five
factors: (A) The present or threatened destruction, modification, or
curtailment of its habitat or range; (B) Overutilization for
commercial, recreational, scientific, or educational purposes; (C)
Disease or predation; (D) The inadequacy of existing regulatory
mechanisms; or (E) Other natural or manmade factors affecting its
continued existence. We find Ivesia webberi is subject to the present
or threatened destruction, modification, or curtailment of its habitat
(Factor A) from the following: Nonnative, invasive plants; modified
fire regime (increased wildfire); OHV use and roads; development;
livestock grazing; and climate change.
We will seek peer review. We are seeking all comments, including
those from independent specialists to ensure that our designation is
based on scientifically sound data, assumptions, and analyses. We will
invite these peer reviewers to comment on our listing proposal for
Ivesia webberi. A thorough review of information that we relied on in
making this determination--including information on taxonomy, life
history, ecology, population distribution and abundance, and potential
threats--is presented in the Ivesia webberi Species Report available at
www. regulations.gov (Docket Number FWS-R8-ES-2013-0079). A summary of
this analysis is found within this proposed rule. Because we will
consider all comments and information received during the comment
period, our final determinations may differ from this proposal.
Information Requested
Public Comments
We intend that any final action resulting from this proposed rule
for Ivesia webberi will be based on the best scientific and commercial
data available and be as accurate and as effective as possible.
Therefore, we request comments or information from the public, other
concerned governmental agencies, Native American tribes, the
[[Page 46890]]
scientific community, industry, or any other interested parties
concerning this proposed rule. We particularly seek comments
concerning:
(1) Ivesia webberi's biology, distribution, population size and
trend, including:
(a) Habitat requirements for pollination, reproduction, and
dispersal;
(b) Genetics and taxonomy;
(c) Historical and current range including distribution patterns;
(d) Historical and current population levels, and current and
projected trends; and
(e) Past and ongoing conservation measures for the species, its
habitat, or both.
(2) The factors that are the basis for making a listing
determination for a species under section 4(a) of the Act (16 U.S.C.
1531 et seq.), which are:
(a) The present or threatened destruction, modification, or
curtailment of its habitat or range (Factor A);
(b) Overutilization for commercial, recreational, scientific, or
educational purposes (Factor B);
(c) Disease or predation (Factor C);
(d) The inadequacy of existing regulatory mechanisms (Factor D); or
(e) Other natural or manmade factors affecting its continued
existence (Factor E).
(3) Biological, commercial trade, or other relevant data concerning
any threats (or lack thereof) to this species and existing regulations
that may be addressing those threats.
(4) Additional information concerning the historical and current
status, range, distribution, and population size of this species,
including the locations of any additional populations of this species.
(5) Any information on the biological or ecological requirements of
the species, and ongoing conservation measures for the species and its
habitat.
Please include sufficient information with your submission (such as
scientific journal articles or other publications) to allow us to
verify any scientific or commercial information you include.
Please note that submissions merely stating support for or
opposition to the action under consideration without providing
supporting information, although noted, will not be considered in
making a determination, as section 4(b)(1)(A) of the Act directs that
determinations as to whether any species is a threatened or endangered
species must be made ``solely on the basis of the best scientific and
commercial data available.''
You may submit your comments and materials concerning this proposed
rule by one of the methods listed in the ADDRESSES section. We request
that you send comments only by the methods described in the ADDRESSES
section.
If you submit information via https://www.regulations.gov, your
entire submission--including any personal identifying information--will
be posted on the Web site. If your submission is made via a hardcopy
that includes personal identifying information, you may request at the
top of your document that we withhold this information from public
review. However, we cannot guarantee that we will be able to do so. We
will post all hardcopy submissions on https://www.regulations.gov.
Please include sufficient information with your comments to allow us to
verify any scientific or commercial information you include.
Comments and materials we receive, as well as supporting
documentation we used in preparing this proposed rule, will be
available for public inspection on https://www.regulations.gov, or by
appointment, during normal business hours, at the U.S. Fish and
Wildlife Service, Nevada Fish and Wildlife Office (see FOR FURTHER
INFORMATION CONTACT).
Public Hearing
Section 4(b)(5) of the Act provides for one or more public hearings
on this proposal, if requested. Requests must be received within 45
days after the date of publication of this proposed rule in the Federal
Register. Such requests must be sent to the address shown in the FOR
FURTHER INFORMATION CONTACT section. We will schedule public hearings
on this proposal, if any are requested, and announce the dates, times,
and places of those hearings, as well as how to obtain reasonable
accommodations, in the Federal Register and local newspapers at least
15 days before the hearing.
Peer Review
In accordance with our joint policy on peer review published in the
Federal Register on July 1, 1994 (59 FR 34270), we will seek the expert
opinions of at least three appropriate and independent specialists
regarding the Ivesia webberi proposed rule. A thorough review of
information that we relied on in making this determination--including
information on taxonomy, life history, ecology, population distribution
and abundance, and potential threats--is presented in the Ivesia
webberi Species Report available at https://www.regulations.gov (Docket
Number FWS-R8-ES-2013-0079). A summary of this analysis is found within
this proposed rule. The purpose of peer review is to ensure that our
listing determination is based on scientifically sound data,
assumptions, and analyses. A peer review panel will conduct an
assessment of the proposed rule and the specific assumptions and
conclusions regarding the proposed listing. This assessment will be
completed during the public comment period.
12-Month Petition Finding and Candidate Withdrawal for Potentilla
basaltica
This section summarizes the information on species status and
potential threats that we evaluated in order to determine that listing
Potentilla basaltica is not warranted and to remove it from candidate
status. A thorough review of information that we relied on in making
this determination--including information on taxonomy, life history,
ecology, population distribution and abundance, and potential threats--
is presented in the P. basaltica (Soldier Meadow Cinquefoil) Species
Report (Service 2013a, entire), which is available at https://www.regulations.gov (in the Search box, enter FWS-R8-ES-2013-0079,
which is the docket number for this rulemaking).
The factors that are the basis for making a listing determination
for a species under section 4(a) of the Act (16 U.S.C. 1531 et seq.),
are:
(a) The present or threatened destruction, modification, or
curtailment of its habitat or range (Factor A);
(b) Overutilization for commercial, recreational, scientific, or
educational purposes (Factor B);
(c) Disease or predation (Factor C);
(d) The inadequacy of existing regulatory mechanisms (Factor D); or
(e) Other natural or manmade factors affecting its continued
existence (Factor E).
We discuss the potential threats related to each factor below.
We identified Potentilla basaltica as a candidate in the June 13,
2002, Candidate Notice of Review (CNOR, 67 FR 40657). At the time, our
assessment was that the species was being impacted by the present or
threatened destruction, modification, or curtailment of its habitat or
range (Factor A) resulting from the primary threats of heavy
recreational use, OHV activity, and livestock grazing at Soldier
Meadow. A candidate species is one for which we have on file sufficient
information on biological vulnerability and threats to support a
proposal to list as endangered or threatened, but for which preparation
and publication of a proposal is precluded by higher-priority listing
actions. Potentilla basaltica was included in all subsequent annual
[[Page 46891]]
CNORs (69 FR 24875, May 4, 2004; 70 FR 24869, May 11, 2005; 71 FR
53756, September 12, 2006; 72 FR 69033, December 6, 2007; 73 FR 75175,
December 10, 2008; 74 FR 57803, November 9, 2009; 75 FR 69221, November
10, 2010; and 76 FR 66370, October 26, 2011; 77 FR 69993, November 21,
2012). On May 11, 2004, we received a petition to list a total of 225
plant and animal species from the list of candidate species, including
P. basaltica. Because we previously found that P. basaltica was
warranted for listing, no further action was taken on the petition.
When it was first identified as a candidate in 2002, we assigned P.
basaltica a listing priority number (LPN) of 5, reflecting a species
with threats that were considered high in magnitude but nonimminent. In
2006 (71 FR 53756), we changed the LPN to 11, reflecting a species with
threats that were considered moderate to low in magnitude and
nonimminent. The LPN for P. basaltica remained at 11 in 2007 (72 FR
69034), 2008 (73 FR 75176), 2009 (74 FR 57804), 2010 (75 FR 69222),
2011 (76 FR 66370), and 2012 (77 FR 69993).
Potentilla basaltica is a low-growing, perennial forb in the Rose
family (Rosaceae) that forms a basal rosette with low-growing stems and
small, yellow flowers. This species has a limited geographic range and
is known to occur on approximately 22.7 acres (ac) (9.2 hectares (ha))
of habitat at Soldier Meadow in Humboldt County, Nevada, and Ash Valley
in Lassen County, California (Service 2013x, p. x). Habitat conditions
occupied by the species differ between these two locations. At Soldier
Meadow, P. basaltica occurs in or near alkali meadows, seeps, and marsh
habitats bordering perennial thermal springs, outflows, and meadow
depressions, while in Ash Valley, P. basaltica occurs between the
floodplain of Ash Creek and the sagebrush steppe (Service 2013x, p. x).
At these two locations, P. basaltica is known from a total of three
populations (two in Soldier Meadow and one in Ash Valley), each of
which is located primarily on public lands managed by the Bureau of
Land Management (BLM; 95 percent). The only available estimates of
abundance suggest a combined total of between 75,950 and 133,614
individual plants across all three populations, with most of these
individuals occurring at the two populations in Soldier Meadow in
Nevada (74,950 to 132,000 individuals) (Service 2013a, p. 10).
Impacts to Potentilla basaltica and its habitat identified at the
time it was determined to be a candidate species in 2002--recreational
use, livestock grazing, roads and off-highway vehicle (OHV) activity,
geothermal exploration, and nonnative, invasive plant species--have
been substantially reduced since 2002. The BLM implemented several
measures that have been effective in reducing recreational use impacts
to P. basaltica in Soldier Meadow: Establishing a designated,
centralized campground, which discourages dispersed camping in wet
meadow habitats where P. basaltica occurs; designating walkways away
from P. basaltica habitat; installing interpretive signs informing
recreationists about the sensitive plant and animal species found in
the wetland and thermal spring habitats of Soldier Meadow; and use of a
campground host in Soldier Meadow who interacts with visitors informing
them of designated camping and bathing areas and providing education
about the sensitive plant and animal species present in the area
(Service 2013a, p. 18).
Other impacts to Potentilla basaltica also have been greatly
reduced since 2002. In 2004, the areas where P. basaltica occurred in
Soldier Meadow were fenced to exclude domestic livestock, wild horses,
and other large ungulates; this initiative significantly reduced
livestock grazing impacts to the species (Service 2013a, p. 20). In
2004, the BLM also closed roads (authorized and unauthorized) in
Soldier Meadow that led to spring, riparian, and wetland areas and
limited OHV use to designated roads and trails (Service 2013a, p. 15).
These closures and OHV restrictions remain in place today and have
effectively reduced impacts to P. basaltica from roads and OHVs. Within
Soldier Meadow, BLM personnel coordinate efforts to detect and rapidly
respond to nonnative, invasive plant species using chemical control and
other treatment methods (Service 2013a, pp. 19-20). Geothermal
exploration occurred in the Soldier Meadow area during the 1970s.
Portions of Soldier Meadow P. basaltica population areas were protected
from exploration and development activities in 1982 when the BLM
designated the area as an Area of Critical Environmental Concern
(ACEC). In 2003, the BLM expanded the existing Soldier Meadow ACEC to
provide additional protection for the desert dace (Eremichthys acros),
which was listed as threatened under the Act in 1985, as well as to
provide additional protection for P. basaltica (USFWS 1997, p. 22). The
Soldier Meadow ACEC is also designated as a BLM Research Natural Area.
The Ash Valley, California, population, which occurs on a much
smaller area and contains many fewer plants than the Soldier Meadow
populations (Service 2013a, p. 10), is located in part on BLM lands
designated as a Research Natural Area and ACEC and in part on private
lands (Service 2013a, pp. 10-11). These BLM lands have been withdrawn
from mining activity and are excluded from timber management and
woodcutting activity (Service 2013a, p. 18). In 2008, the BLM issued a
Record of Decision on the Alturas Resource Area Management Plan (RMP)
and Final Environmental Impact Statement (BLM 2008a, pp. A-1-A-10). The
RMP identified the need for establishing a long-term monitoring plot
for Potentilla basaltica and limiting OHV travel to designated routes
within the Ash Valley ACEC and Research Natural Area (BLM 2007, p. 2-
105). And, if monitoring data suggested a decline in numbers or
reproductive viability of P. basaltica, fencing would be constructed to
exclude livestock grazing (BLM 2007, p. 2-106). The RMP also proposed
the acquisition of private lands supporting unprotected populations of
special status plants, including P. basaltica (BLM 2008a, p. 13).
In addition to evaluation of the threats identified at the time
Potentilla basaltica was determined to be a candidate species, we also
evaluated potential impacts of climate change on the species. Although
climate change is likely to affect ecosystem function in Soldier Meadow
and Ash Valley where P. basaltica occurs, we conclude that because of
uncertainty about specific effects of climate change on P. basaltica,
the best available scientific and commercial information does not
indicate at this time that effects of climate change are likely to
threaten the continued existence of P. basaltica now or in the
foreseeable future (Service 2013a, pp. 22-23).
Potentilla basaltica is a BLM sensitive species (Service 2013a, p.
2). The stated objective for BLM sensitive species is to initiate
proactive conservation measures that reduce or eliminate threats to
minimize the likelihood of and need for listing (BLM 2008a, 6840.02).
Conservation, as it applies to BLM sensitive species, is defined as
``the use of programs, plans, and management practices to reduce or
eliminate threats affecting the status of the species, or improve the
condition of the species' habitat on BLM-administered lands'' (BLM
2008b, Glossary, p. 2).
Potentilla basaltica is not State listed as endangered or
threatened in either Nevada or California. However, in California, P.
basaltica has a California Native Plant Society (CNPS) rank of 1B.3
(not very threatened in California,
[[Page 46892]]
with less than 20 percent of occurrences threatened and low degree and
immediacy of threat or no current threats known) (CNPS 2013). Plants,
like P. basaltica, with a CNPS 1.B rank must be fully considered during
preparation of environmental documents relating to the California
Environmental Quality Act (CEQA) (CNPS 2013).
Based on our analysis of the five factors identified in section
4(a)(1) of the Act, we conclude that the previously recognized impacts
to Potentilla basaltica from present or threatened destruction,
modification, or curtailment of its habitat or range (Factor A)
(recreational use; OHV use; introduction of nonnative, invasive plant
species; and trampling by livestock), do not rise to a level of
significance such that the species is in danger of extinction now or in
the foreseeable future. We evaluated additional potential impacts under
the the five listing factors stated above. In that evaluation we found
that potential impacts such as livestock grazing (Factors A and E),
geothermal exploration (Factors A and E), herbivory (Factor B), disease
(Factor C), and climate change (Factor A) to either be of no concern or
insignificant concern at this time. Additionally, conservation measures
and protection provided by BLM for species associated with thermal
springs are benefiting P. basaltica, and we anticipate these
conservation measures and protections to continue to benefit P.
basaltica into the foreseeable future (in part due to other sensitive
and federally listed species occurring in these areas). Thus, the
existing regulatory mechanisms are adequate to protect the species from
the potential impacts (Factor D). See the ``Factors Affecting the
Species'' section of the Species Report (Service 2013a, pp. 17-24) for
a thorough discussion of all potential and current threats.
The best available information to assist us in assessing
foreseeable future for Potentilla basaltica is the time period
associated with management planning activities. Because the majority
(95 percent) of P. basaltica occupied areas are on Federal lands that
receive conservation protections resulting from Federal laws and the
regulations and policies implementing those laws (i.e., Federal Land
Policy Management Act, National Environmental Policy Act), we look to
the historical timeframe for completing management plans and current
planning efforts to assist us in defining foreseeable future. Based on
this timeframe information, we estimate the foreseeable future to be at
least 30 years (i.e., 2043) for this analysis. Therefore, we conclude
that P. basaltica does not meet the definition of an endangered or
threatened species and thus is no longer warranted for listing under
the Act. With the publication of this notice, P. basaltica will be
removed from the list of candidate species.
Proposed Threatened Species Status for Ivesia webberi
Previous Federal Actions
We identified Ivesia webberi as a candidate in the June 13, 2002,
Candidate Notice of Review (CNOR, 67 FR 40657). Ivesia webberi was
included in all subsequent annual CNORs (69 FR 24875, May 4, 2004; 70
FR 24869, May 11, 2005; 71 FR 53756, September 12, 2006; 72 FR 69033,
December 6, 2007; 73 FR 75175, December 10, 2008; 74 FR 57803, November
9, 2009; 75 FR 69221, November 10, 2010; and 76 FR 66370, October 26,
2011; 77 FR 69993, November 21, 2012). On May 11, 2004, we received a
petition to list a total of 225 plant and animal species from the list
of candidate species, including I. webberi. Because we previously found
the species was warranted for listing, no further action was taken on
the petition. When it was first identified as a candidate in 2002 (67
FR 40657), we assigned I. webberi a listing priority number (LPN) of 5,
reflecting a species with threats that were considered high in
magnitude but nonimminent; the LPN remained at 5 in all subsequent
CNORs.
Background
In this and the following section, we summarize from information on
species status and potential threats that we evaluated in order to
determine that Ivesia webberi meets the Act's definition of a
threatened species (section 3(20)). A thorough review of information
that we relied on in making this determination--including information
on taxonomy, life history, ecology, population distribution and
abundance, and threats--is presented in the Ivesia webberi (Webber's
ivesia) Species Report (Service 2013b, entire; available at https://www.regulations.gov (in the Search box, enter FWS-R8-ES-2013-0079,
which is the docket number for this rulemaking).
Ivesia webberi is a low, spreading perennial forb in the Rose
family (Rosaceae) with grayish-green foliage, dark-red, wiry stems, and
headlike clusters of small, yellow flowers. This species occupies
vernally moist, rocky, clay soils with an argillic horizon that shrink
and swell upon drying and wetting in open to sparsely vegetated areas
associated with an Artemisia arbuscula (low sagebrush)-perennial
bunchgrass-forb community. The specialized soils are well developed, a
process estimated to take 1,000 years. Limited seed dispersal and
apparent limited recruitment further restrict the occupied range and
distribution of I. webberi.
Ivesia webberi is currently known to occupy a total of
approximately 165 ac (66.8 ha) within five counties in California and
Nevada along the transition zone between the eastern edge of the
northern Sierra Nevada and the northwestern edge of the Great Basin
(Service 2013b, p. 2). The species is known historically from a total
of 17 populations, but 1 has been extirpated and a portion of another
(1 of 4 subpopulations) is possibly extirpated. Of the remaining 16
populations, the status of 4 is unknown, and we currently are uncertain
whether the species still persists at these locations (Service 2013b,
p. 2). For the remaining 10 populations where the species' status is
better understood, 6 occur on areas that are less than 5 ac (2 ha)
each. Reliable estimation of population sizes or trends in I. webberi
is complicated because past population estimates have usually been
obtained by different observers employing a variety of methodologies
and varying levels of survey effort (Service 2013b, p. 2).
Summary of Biological Status and Threats
Due to the restricted range, specialized habitat requirements, and
limited recruitment and dispersal of Ivesia webberi, populations of
this species are vulnerable to ongoing and future threats that affect
both individual plants and their habitat. The primary threats to I.
webberi are the additive and synergistic effects due to nonnative,
invasive plant species and modified fire regime (Service 2013b, pp. 31-
32). Nonnative, invasive plant species, such as Bromus tectorum
(cheatgrass), Poa bulbosa (bulbous bluegrass), and Taeniatherum caput-
medusae (medusahead), have become established and are part of the
associated plant community at 12 of the 16 extant populations of I.
webberi. Nonnative, invasive plant species negatively affect I. webberi
through competition, displacement, and degradation of the quality and
composition of the Artemisia arbuscula-perennial bunchgrass-forb
community in which I. webberi occurs. In addition to these effects,
these nonnative, invasive plant species, once established, contribute
fuels that increase the frequency and likelihood of wildfire in I.
webberi habitat.
[[Page 46893]]
Wildfire was historically infrequent in the Great Basin because the
native plant communities made up of annuals and perennial bunchgrasses
did not provide sufficient fine fuels to carry large-scale wildfires.
The bare spaces between widely spaced shrubs and the low fuel load of
native annuals and perennial bunchgrasses generally prevented fire from
spreading, so the fires that did burn were restricted to isolated
patches. In Artemisia arbuscula communities, such as those that Ivesia
webberi inhabits, the average fire return interval is greater than 100
years, due to natural lower productivity and fuel accumulations
(Service 2013b, p. 24). However, beginning in the late 1800s, the
widespread invasion of nonnative plant species, particularly annual
grasses, has created a bed of continuous fine fuels across the
sagebrush landscape in many areas (Service 2013b, p. 24). This increase
in fine fuels created by nonnative, invasive plants has resulted in
more frequent fires that burn larger areas and often burn at higher
intensities. Post-fire conditions further facilitate the invasion and
establishment of nonnative, invasive plant species, thus creating a
positive feedback loop between increased wildfire and the spread of
these species (Service 2013b, p. 24). Ten of the 16 extant I. webberi
populations have experienced wildfire since 1984 (Service 2013b, p.
24). Because I. webberi did not evolve with frequent fire and does not
possess adaptations that would help it persist in a frequent-fire fire
regime, wildfires are expected to have adverse population-level impacts
on the species. In addition, increased wildfire frequency within the
species' range results in increased wildfire suppression activities,
which also may adversely affect I. webberi populations (Service 2013b,
pp. 22, 24-25).
Other threats impacting Ivesia webberi populations include OHV use
and roads, development, livestock grazing, and climate change (Service
2013b, pp. 25-31). OHV impacts to I. webberi populations have increased
during the past 20 years as population growth and associated
development have increased (Bergstrom 2009, p. 22), especially in the
Reno urban area where 6 of the 16 populations occur. Ten of 16 extant
I. webberi populations are adjacent to or intersected by dirt roads and
have been impacted to some degree by road development and OHV use
(Service 2013b, pp. 25-26). Roads cause habitat loss and degradation
and when vehicles drive off existing roads and trails they can crush
plants, compact soils, and provide a means for nonnative, invasive
plant species to invade otherwise remote, intact habitats. The U.S.
Forest Service concluded that a 2006 travel management plan for Peavine
Mountain would benefit rare plant species, including I. webberi;
however, designated roads open to all vehicles continue to bisect I.
webberi populations, and unauthorized OHV use remains high within I.
webberi populations on Forest Service lands in the Reno urban area
(Service 2013b, p. 26).
Development, which results in direct mortality, habitat loss,
degradation, and fragmentation, has resulted in the extirpation of one
Ivesia webberi population and the loss of a portion of another
population (Service 2013x, p. x). Residential or commercial development
is ongoing or planned at each of the four Nevada populations located on
private lands. In addition, construction of a 120-kV overhead
transmission line may impact two I. webberi populations located on
Forest Service lands (Service 2013b, p. 26). Livestock grazing has the
potential to result in negative effects to I. webberi due to trampling
and substrate disturbance, but this situation is dependent on factors
such as stocking rate and season of use. Two I. webberi populations
occur in areas that are currently grazed by cattle, and another seven
populations occur within vacant grazing allotments that could be
reopened to grazing to alleviate grazing pressures on nearby allotments
(Service 2013b, p. 29).
Climate change is likely to affect Ivesia webberi, although it is
difficult to project specific effects. In the Great Basin, temperatures
have risen 0.9 to 2.7[emsp14][deg]F (0.5 to 1.5 [deg]C) in the last 100
years and are projected to warm another 3.8 to 10.3[emsp14][deg]F (2.1
to 5.7 [deg]C) over the rest of the century (Service 2013b, p. 30).
Under current climate change projections, we anticipate that future
climatic conditions will favor the further spread of nonnative,
invasive plants and increase the frequency, spatial extent, and
severity of wildfires (Service 2013b, p. 30). Alteration of temperature
and precipitation patterns as a result of climate change also may
result in decreased survivorship of I. webberi by causing physiological
stress, altering phenology, and reducing reproduction or seedling
establishment.
Because most of the habitat where the species is known to occur is
located on Federal lands (69 percent of occupied habitat occurs on
Forest Service lands, and 10 percent of occupied habitat occurs on BLM
lands), Ivesia webberi receives some conservation protections resulting
from Federal laws and the regulations and policies implementing those
laws (e.g., the National Forest Management Act, Federal Land Policy
Management Act, National Environmental Policy Act). Ivesia webberi
receives special consideration on Federal lands because it is
classified as a sensitive species by both the Forest Service and BLM
(Service 2013b, pp. 3-4). The species also is classified as threatened
with extinction and fully protected by the State of Nevada; removing or
destroying I. webberi and other fully protected plants is prohibited
except under special permit issued by the Nevada Division of Forestry
(NDF 2013). Ivesia webberi is not listed as endangered or threatened
under the California Endangered Species Act (CESA), but has a
California Native Plant Society (CNPS) rare plant rank of 1B.1
(seriously threatened in California with over 80 percent of occurrences
threatened and high degree and immediacy of threat (CNPS 2013). Ivesia
webberi and other plants with a CNPS 1B rank must be fully considered
during preparation of environmental documents relating to the
California Environmental Quality Act (CEQA) (CNPS 2013).
The Forest Service drafted a rangewide conservation strategy for
Ivesia webberi to guide conservation actions for the species on Forest
Service lands (Service 2013b, pp. 21-22). The conservation strategy,
which was signed in 2010, will result in long-term benefits to I.
webberi populations located on Forest Service lands (Bergstrom 2009,
pp. 1-46). However, we expect that the landscape-level threats of
nonnative, invasive plants and increased wildfire will continue to
adversely affect I. webberi populations across the species' range
(Service 2013b, p. 22).
Determination
We have carefully assessed the best scientific and commercial
information available regarding the past, present, and future threats
to Ivesia webberi. We considered the five factors identified in section
4(a)(1) of the Act in determining whether I. webberi meets the Act's
definition of an endangered species (section 3(6)) or threatened
species (section 3(20)). We find that I. webberi is threatened by the
present or threatened destruction, modification, or curtailment of its
habitat or range (Factor A). Present or threatened destruction,
modification, or curtailment of its habitat or range include habitat
loss and degradation due to nonnative, invasive plants, modified fire
regime (increased wildfire), OHV use and roads, development, livestock
grazing, and
[[Page 46894]]
climate change. Of these, we consider the additive and synergistic
effects of nonnative, invasive plants and increased wildfire to be the
greatest threats to I. webberi.
Nonnative, invasive plant species such as Bromus tectorum and
Taeniatherum caput-medusae can outcompete and displace I. webberi and
result in increased frequency, spatial extent, and severity of
wildfires because of the increase in fine fuels they produce. Twelve of
the 16 extant populations have already been invaded by nonnative,
invasive plant species and 10 of the 16 extant populations have been
impacted by wildfire since 1984. Because there are currently no
feasible means for controlling the spread of widespread nonnative,
invasive plant species such as B. tectorum and T. caput-medusae, we
expect that wildfires will continue to impact I. webberi populations.
Increased temperatures and altered precipitation patterns due to
climate change are projected to lead to further increases in wildfire
and nonnative, invasive plants. OHV use and roads, development, and
livestock grazing are having impacts on certain I. webberi populations.
We did not identify threats to Ivesia webberi due to
overutilization for commercial, recreational, scientific, or
educational purposes (Factor B); disease or predation (Factor C); or
other natural or manmade factors affecting its continued existence
(Factor E). Although regulatory mechanisms (Factor D) are in place that
provide some protection to I. webberi and its habitat, these mechanisms
do not completely alleviate all of the threats currently acting on the
species.
The Act defines an endangered species as any species that is ``in
danger of extinction throughout all or a significant portion of its
range'' and a threatened species as any species ``that is likely to
become endangered throughout all or a significant portion of its range
within the foreseeable future.'' Available population information for
Ivesia webberi is not useful for determining trends because population
estimates have been obtained by different observers employing a variety
of means and levels of survey effort. Nonnative, invasive plant
species, wildfire, and OHV activity are present impacts throughout the
range of I. webberi and in some cases are found to be increasing for
many years with data in particular related to increased recreational
OHV activity over the past 20 years (Service 2013b, pp. 25-26) and
increased wildfire and suppression activities over the past 30 years
(Service 2013b, pp. 22, 24-25). Additionally, given current climate
change projections, we anticipate that future climatic conditions will
favor invasion by nonnative, invasive plant species, which will further
contribute to increases in frequency, spatial extent, and severity of
wildfires (Service 2013b, pp. 29-31). Based on the timeframe associated
with the documented increased level of some threats over the past 30
years and the effects of climate change projections on these threats,
we estimate the foreseeable future to be at least 30 years (i.e.,
2043).
We find that Ivesia webberi is not presently in danger of
extinction throughout all of its range, but that it is likely to become
endangered throughout all of its range in the foreseeable future. We
find that I. webberi is not presently in danger of extinction because
the species is characterized by multiple populations spread across
northeastern California and northwestern Nevada and that, in total,
these populations provide sufficient redundancy (multiple populations
distributed across the landscape), resiliency (capacity for a species
to recover from periodic disturbance), and representation (range of
variation found in a species) such that I. webberi is not at immediate
risk of extinction. However, because multiple threats (nonnative,
invasive plants, increased wildfire, OHV use and roads, development,
livestock grazing, and climate change) are impacting many of the I.
webberi populations and because additive and synergistic effects due to
nonnative, invasive plants, increased wildfire, and climate change are
likely to continue and increase in the future, we find that I. webberi
is likely to become an endangered species throughout all of its range
in the foreseeable future. Therefore, on the basis of the best
available scientific and commercial information, we propose listing I.
webberi as a threatened species.
Under the Act and our implementing regulations, a species may
warrant listing if it is endangered or threatened throughout all or a
significant portion of its range.
Significant Portion of the Range
Having determined that Ivesia webberi meets the Act's definition of
a threatened species, we must next consider whether there are any
significant portions of its range where I. webberi is presently in
danger of extinction and thus meets the definition of an endangered
species. In determining whether a species is endangered or threatened
in a significant portion of its range, we first identify any portions
of the range of the species that warrant further consideration. The
range of a species can theoretically be divided into portions an
infinite number of ways. However, analyzing portions of the range that
are not reasonably likely to be both (1) significant and (2) endangered
or threatened would serve no purpose. To identify only those portions
that warrant further consideration, we determine whether substantial
information indicates that: (1) The portions may be significant, and
(2) the species may be in danger of extinction there or likely to
become so within the foreseeable future. In practice, a key part of
this analysis is whether the threats are geographically concentrated in
some way. If the threats to the species are essentially uniform
throughout its range, no portion is likely to warrant further
consideration. Moreover, if any concentration of threats applies only
to portions of the species' range that are not significant, such
portions will not warrant further consideration.
If we identify portions that warrant further consideration, we then
determine whether the species is endangered or threatened in these
portions of its range. Depending on the biology of the species, its
range, and the threats it faces, the Service may address either the
significance question or the status question first. Thus, if the
Service considers significance first and determines that a portion of
the range is not significant, the Service need not determine whether
the species is endangered or threatened there. Likewise, if the Service
considers status first and determines that the species is not
endangered or threatened in a portion of its range, the Service need
not determine if that portion is significant. However, if the Service
determines that both a portion of the range of a species is significant
and the species is endangered or threatened there, the Service will
specify that portion of the range as endangered or threatened under
section 4(c)(1) of the Act.
The primary threats to Ivesia webberi occur throughout the species'
range and are not restricted to or concentrated in any particular
portion of that range. The primary threats of nonnative, invasive
plants and increased wildfire are impacting I. webberi populations
throughout the California and Nevada portions of the species' range.
Climate change also is acting on I. webberi throughout the species'
range. Thus, we conclude that threats impacting I. webberi are not
concentrated in certain areas and, thus, there are no significant
portions of its range where the species should be classified as an
endangered species. Accordingly, our proposal to list I. webberi as a
threatened species
[[Page 46895]]
applies throughout the species' entire range.
Available Conservation Measures Resulting From Listing
Conservation measures provided to species listed as endangered or
threatened under the Act include recognition, recovery actions,
requirements for Federal protection, and prohibitions against certain
practices. Recognition through listing results in public awareness and
conservation by Federal, State, Tribal, and local agencies, private
organizations, and individuals. The Act provides direction for
cooperation with the States and requires that recovery actions be
carried out for all listed species. The protection required by Federal
agencies and the prohibitions against certain activities are discussed,
in part, below.
The primary purpose of the Act is the conservation of endangered
and threatened species and the ecosystems upon which they depend. The
ultimate goal of such conservation efforts is the recovery of these
listed species, so that they no longer need the protective measures of
the Act. Subsection 4(f) of the Act requires the Service to develop and
implement recovery plans for the conservation of endangered and
threatened species. The recovery planning process involves the
identification of actions that are necessary to halt or reverse the
species' decline by addressing the threats to its survival and
recovery. The goal of this process is to restore listed species to a
point where they are secure, self-sustaining, and functioning
components of their ecosystems.
Recovery planning includes the development of a recovery outline
shortly after a species is listed and preparation of a draft and final
recovery plan. The recovery outline guides the immediate implementation
of urgent recovery actions and describes the process to be used to
develop a recovery plan. Revisions of the plan may be done to address
continuing or new threats to the species, as new substantive
information becomes available. The recovery plan identifies site-
specific management actions that set a trigger for review of the five
factors that control whether a species remains endangered or may be
downlisted or delisted, and methods for monitoring recovery progress.
Recovery plans also establish a framework for agencies to coordinate
their recovery efforts and provide estimates of the cost of
implementing recovery tasks. Recovery teams (composed of species
experts, Federal and State agencies, nongovernmental organizations, and
stakeholders) are often established to develop recovery plans. When
completed, the recovery outline, draft recovery plan, and the final
recovery plan will be available on our Web site (https://www.fws.gov/endangered), or from our Nevada Fish and Wildlife Office (see FOR
FURTHER INFORMATION CONTACT).
Implementation of recovery actions generally requires the
participation of a broad range of partners, including other Federal
agencies, States, Tribal, nongovernmental organizations, businesses,
and private landowners. Examples of recovery actions include habitat
restoration (e.g., restoration of native vegetation), research, captive
propagation and reintroduction, and outreach and education. The
recovery of many listed species cannot be accomplished solely on
Federal lands because their range may occur primarily or solely on non-
Federal lands. To achieve recovery of these species requires
cooperative conservation efforts on private, State, and Tribal lands.
If Ivesia webberi is listed, funding for recovery actions will be
available from a variety of sources, including Federal budgets, State
programs, and cost share grants for non-Federal landowners, the
academic community, and nongovernmental organizations. In addition,
pursuant to section 6 of the Act, the States of California and Nevada
would be eligible for Federal funds to implement management actions
that promote the protection or recovery of I. webberi. Information on
our grant programs that are available to aid species recovery can be
found at: https://www.fws.gov/grants.
Although Ivesia webberi is only proposed for listing under the Act
at this time, please let us know if you are interested in participating
in recovery efforts for this species. Additionally, we invite you to
submit any new information on this species whenever it becomes
available and any information you may have for recovery planning
purposes (see FOR FURTHER INFORMATION CONTACT).
Section 7(a) of the Act requires Federal agencies to evaluate their
actions with respect to any species that is proposed or listed as an
endangered or threatened species and with respect to its critical
habitat, if any is designated. Regulations implementing this
interagency cooperation provision of the Act are codified at 50 CFR
Part 402. Section 7(a)(4) of the Act requires Federal agencies to
confer with the Service on any action that is likely to jeopardize the
continued existence of a species proposed for listing or result in
destruction or adverse modification of proposed critical habitat. If a
species is listed subsequently, section 7(a)(2) of the Act requires
Federal agencies to ensure that activities they authorize, fund, or
carry out are not likely to jeopardize the continued existence of the
species or destroy or adversely modify its critical habitat. If a
Federal action may affect a listed species or its critical habitat, the
responsible Federal agency must enter into consultation with the
Service.
Federal agency actions within Ivesia webberi's habitat that may
require conference or consultation or both as described in the
preceding paragraph include land management actions that could result
in impacts to soil characteristics or seedbank viability, pollinators
or their habitat, and associated native vegetation community, and any
other landscape-altering activities on Federal lands, such as:
Reauthorization of grazing permits by the BLM and the U.S. Forest
Service, issuance of section 404 Clean Water Act (33 U.S.C. 1251 et
seq.) permits by the U.S. Army Corps of Engineers, construction and
management of gas pipeline and power line rights-of-way by the Federal
Energy Regulatory Commission, and construction and maintenance of roads
or highways by the Federal Highway Administration.
Our policy, as published in the Federal Register on July 1, 1994
(59 FR 34272), is to identify to the maximum extent practicable at the
time a species is listed, those activities that would or would not
constitute a violation of section 9 of the Act. The intent of this
policy is to increase public awareness of the effect of a proposed
listing on proposed and ongoing activities within the range of species
proposed for listing. The Act and its implementing regulations set
forth a series of general prohibitions and exceptions that apply to
endangered and threatened plants. The prohibitions of section 9(a)(2)
of the Act, codified at 50 CFR 17.61, apply to endangered plants. These
prohibitions, in part, make it illegal for any person subject to the
jurisdiction of the United States to import or export, transport in
interstate or foreign commerce in the course of a commercial activity,
sell or offer for sale in interstate or foreign commerce, or remove and
reduce the species to possession from areas under Federal jurisdiction.
These take prohibitions for endangered plant species are extended to
threatened plant species under 50 CFR 17.71, except the take
prohibitions do not extend to seeds of cultivated specimens, provided
that a statement that the seeds are of ``cultivated origin''
accompanies the seeds or their container. Also, 50 CFR 17.71(b)
authorizes Service and State
[[Page 46896]]
conservation agency employees to remove and reduce to possession from
Federal lands those threatened plant species covered by cooperative
agreements under section 6(c) of the Act.
We may issue permits to carry out otherwise prohibited activities
involving endangered and threatened wildlife species under certain
circumstances. Regulations governing permits are codified at 50 CFR
17.62 for endangered plants, and at 17.72 for threatened plants. With
regard to endangered plants, a permit must be issued for the following
purposes: For scientific purposes or to enhance the propagation or
survival of the species.
Under section 4(d) of the ESA, the Secretary has discretion to
issue such regulations as he deems necessary and advisable to provide
for the conservation of threatened species. Our implementing
regulations (50 CFR 17.71) for threatened plants generally incorporate
the prohibitions of section 9 of the Act for endangered plants, except
when a ``special rule'' promulgated pursuant to section 4(d) of the Act
has been issued with respect to a particular threatened species. In
such a case, the general prohibitions in 50 CFR 17.61 would not apply
to that species, and instead, the special rule would define the
specific take prohibitions and exceptions that would apply for that
particular threatened species, which we consider necessary and
advisable to conserve the species. The Secretary also has the
discretion to prohibit by regulation with respect to a threatened
species any act prohibited by section 9(a)(2) of the ESA. Exercising
this discretion, which has been delegated to the Service by the
Secretary, the Service has developed general prohibitions that are
appropriate for most threatened species in 50 CFR 17.71 and exceptions
to those prohibitions in 50 CFR 17.62. We are not proposing to
promulgate a special section 4(d) rule, and as a result, all of the
section 9 prohibitions, including the ``take'' prohibitions, will apply
to the Ivesia webberi.
Questions regarding whether specific activities would constitute a
violation of section 9 of the Act should be directed to the U.S. Fish
and Wildlife Service, Nevada Fish and Wildlife Office (see FOR FURTHER
INFORMATION CONTACT).
In addition to the take prohibitions that would be afforded to
Ivesia webberi throughout its range in California and Nevada under
section 9 of the Act, I. webberi is listed as threatened by the State
of Nevada pursuant to Nevada Revised Statute (N.R.S.) 527.260-.300 and
was added to the State list of fully protected species of native flora
(Nevada Administrative Code 527.010) in 2004. Removing or destroying
plants on the State's fully protected list is prohibited except under
special permit issued by the Nevada Division of Forestry (N.R.S.
527.270). Ivesia webberi is not listed by the State of California under
the California Endangered Species Act (CESA), so removal or destruction
of plants is not currently prohibited by State law in California.
Ivesia webberi does have a California Native Plant Society rare plant
rank of 1B.1 and must be fully considered during preparation of
environmental documents relating to the California Environmental
Quality Act (CEQA) (see Summary of Biological Status and Threats
section).
Required Determinations
Clarity of the Rule
We are required by Executive Orders 12866 and 12988 and by the
Presidential Memorandum of June 1, 1998, to write all rules in plain
language. This means that each rule we publish must:
(1) Be logically organized;
(2) Use the active voice to address readers directly;
(3) Use clear language rather than jargon;
(4) Be divided into short sections and sentences; and
(5) Use lists and tables wherever possible.
If you feel that we have not met these requirements, send us
comments by one of the methods listed in the ADDRESSES section. To
better help us revise the rule, your comments should be as specific as
possible. For example, you should tell us the numbers of the sections
or paragraphs that are unclearly written, which sections or sentences
are too long, the sections where you feel lists or tables would be
useful, etc.
Paperwork Reduction Act of 1995 (44 U.S.C. 3501 et seq.)
This rule does not contain any new collections of information that
require approval by OMB under the Paperwork Reduction Act of 1995 (44
U.S.C. 3501 et seq.). This rule will not impose recordkeeping or
reporting requirements on State or local governments, individuals,
businesses, or organizations. An agency may not conduct or sponsor, and
a person is not required to respond to, a collection of information
unless it displays a currently valid OMB control number.
National Environmental Policy Act (42 U.S.C. 4321 et seq.)
We have determined that environmental assessments and environmental
impact statements, as defined under the authority of the National
Environmental Policy Act (NEPA; 42 U.S.C. 4321 et seq.), need not be
prepared in connection with listing a species as an endangered or
threatened species under the Endangered Species Act. We published a
notice outlining our reasons for this determination in the Federal
Register on October 25, 1983 (48 FR 49244).
Government-to-Government Relationship With Tribes
In accordance with the President's memorandum of April 29, 1994
(Government-to-Government Relations with Native American Tribal
Governments; 59 FR 22951), Executive Order 13175 (Consultation and
Coordination With Indian Tribal Governments), and the Department of the
Interior's manual at 512 DM 2, we readily acknowledge our
responsibility to communicate meaningfully with recognized Federal
Tribes on a government-to-government basis. In accordance with
Secretarial Order 3206 of June 5, 1997 (American Indian Tribal Rights,
Federal-Tribal Trust Responsibilities, and the Endangered Species Act),
we readily acknowledge our responsibilities to work directly with
tribes in developing programs for healthy ecosystems, to acknowledge
that tribal lands are not subject to the same controls as Federal
public lands, to remain sensitive to Indian culture, and to make
information available to tribes.
References Cited
A complete list of references cited in this rulemaking is available
on the Internet at https://www.regulations.gov and upon request from the
Nevada Fish and Wildlife Office (see FOR FURTHER INFORMATION CONTACT).
Authors
The primary authors of this proposed rule are the staff members of
the Service's Nevada Fish and Wildlife Office and Region 8 Regional
Office.
List of Subjects in 50 CFR Part 17
Endangered and threatened species, Exports, Imports, Reporting and
recordkeeping requirements, 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]
0
1. The authority citation for part 17 continues to read as follows:
[[Page 46897]]
Authority: 16 U.S.C. 1361-1407; 1531-1544; and 4201-4245; unless
otherwise noted.
0
2. Amend Sec. 17.12 paragraph (h), by adding an entry for ``Ivesia
webberi (Webber's ivesia)'' to the List of Endangered and Threatened
Plants in alphabetical order under ``Flowering Plants'' to read as
follows:
Sec. 17.12 Endangered and threatened plants.
* * * * *
(h) * * *
--------------------------------------------------------------------------------------------------------------------------------------------------------
Species
-------------------------------------------------------- Historic range Family Status When listed Critical Special
Scientific name Common name habitat rules
--------------------------------------------------------------------------------------------------------------------------------------------------------
Flowering Plants
* * * * * * *
Ivesia webberi................... Webber's ivesia..... U.S.A. (CA, NV).... Rosaceae........... T ........... NA NA
* * * * * * *
--------------------------------------------------------------------------------------------------------------------------------------------------------
* * * * *
Dated: July 23, 2013.
Signed:
Stephen Guertin,
Director, U.S. Fish and Wildlife Service.
[FR Doc. 2013-18579 Filed 8-1-13; 8:45 am]
BILLING CODE 4310-55-P