[Federal Register Volume 73, Number 238 (Wednesday, December 10, 2008)]
[Proposed Rules]
[Pages 75176-75244]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-28986]
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Part II
Department of the Interior
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Fish and Wildlife Service
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50 CFR Part 17
Endangered and Threatened Wildlife and Plants; Review of Native Species
That Are Candidates for Listing as Endangered or Threatened; Annual
Notice of Findings on Resubmitted Petitions; Annual Description of
Progress on Listing Actions; Proposed Rule
Federal Register / Vol. 73, No. 238 / Wednesday, December 10, 2008 /
Proposed Rules
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DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[FWS-R9-ES-2008-0115; MO-9221050083 - B2]
Endangered and Threatened Wildlife and Plants; Review of Native
Species That Are Candidates for Listing as Endangered or Threatened;
Annual Notice of Findings on Resubmitted Petitions; Annual Description
of Progress on Listing Actions
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Notice of review.
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SUMMARY: In this Candidate Notice of Review (CNOR), we, the U.S. Fish
and Wildlife Service (Service), present an updated list of plant and
animal species native to the United States that we regard as candidates
for or have proposed for addition to the Lists of Endangered and
Threatened Wildlife and Plants under the Endangered Species Act of
1973, as amended. Identification of candidate species can assist
environmental planning efforts by providing advance notice of potential
listings, allowing landowners and resource managers to alleviate
threats and thereby possibly remove the need to list species as
endangered or threatened. Even if we subsequently list a candidate
species, the early notice provided here could result in more options
for species management and recovery by prompting candidate conservation
measures to alleviate threats to the species.
The CNOR summarizes the status and threats that we evaluated in
order to determine that species qualify as candidates and to assign a
listing priority number (LPN) to each species, or to remove species
from candidate status. Additional material that we relied on is
available in the Species Assessment and Listing Priority Assignment
Forms (species assessment forms, previously called candidate forms) for
each candidate species.
Overall, this CNOR recognizes 1 new candidate, changes the LPN for
11 candidates, and removes 2 species from candidate status. Combined
with other decisions for individual species that were published
separately from this CNOR in the past year, the current number of
species that are candidates for listing is 251.
This document also includes our findings on resubmitted petitions
and describes our progress in revising the Lists of Endangered and
Threatened Wildlife and Plants during the period September 30, 2007,
through September 30, 2008.
We request additional status information that may be available for
the 251 candidate species identified in this CNOR.
DATES: We will accept information on this Candidate Notice of Review at
any time.
ADDRESSES: This notice is available on the Internet at http://
www.regulations.gov, and http://endangered.fws.gov/candidates/
index.html. Species assessment forms with information and references on
a particular candidate species' range, status, habitat needs, and
listing priority assignment are available for review at the appropriate
Regional Office listed below in SUPPLEMENTARY INFORMATION or at the
Branch of Candidate Conservation, Arlington, VA (see address below), or
on our Internet website (http://endangered.fws.gov/candidates/
index.html). Please submit any new information materials, comments, or
questions of a general nature on this notice to the Arlington, VA,
address listed below. Please submit any new information, materials,
comments, or questions pertaining to a particular species to the
address of the Endangered Species Coordinator in the appropriate
Regional Office listed in SUPPLEMENTARY INFORMATION.
FOR FURTHER INFORMATION CONTACT: The Endangered Species Coordinator(s)
in the appropriate Regional Office(s) or Chief, Branch of Candidate
Conservation, U.S. Fish and Wildlife Service, 4401 N. Fairfax Drive,
Room 420, Arlington, VA 22203 (telephone 703-358-2105; facsimile 703-
358-1735). Persons who use a telecommunications device for the deaf
(TDD) may call the Federal Information Relay Service (FIRS) at 800-877-
8339.
SUPPLEMENTARY INFORMATION:
Information Solicited
We request additional status information that may be available for
any of the candidate species identified in this CNOR. We will consider
this information in preparing listing documents and future revisions to
the notice of review, as it will help us in monitoring changes in the
status of candidate species and in management for conserving them. We
also request information on additional species to consider including as
candidates as we prepare future updates of this notice.
You may submit your information concerning this notice in general
or for any of the species included in this notice by one of the methods
listed in the ADDRESSES section.
Species-specific information and materials we receive will be
available for public inspection by appointment, during normal business
hours, at the appropriate Regional Office listed below in SUPPLEMENTARY
INFORMATION. General information we receive will be available at the
Branch of Candidate Conservation, Arlington, VA (see address above).
Candidate Notice of Review
Background
The Endangered Species Act of 1973, as amended (16 U.S.C. 1531 et
seq.) (Act), requires that we identify species of wildlife and plants
that are endangered or threatened, based on the best available
scientific and commercial information. As defined in section 3 of the
Act, an endangered species is any species which is in danger of
extinction throughout all or a significant portion of its range, and a
threatened species is any species which is likely to become an
endangered species within the foreseeable future throughout all or a
significant portion of its range. Through the Federal rulemaking
process, we add species that meet these definitions to the List of
Endangered and Threatened Wildlife at 50 CFR 17.11 or the List of
Endangered and Threatened Plants at 50 CFR 17.12. As part of this
program, we maintain a list of species that we regard as candidates for
listing. 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. A species may be indentified by us as a
candidate for listing based on an evaluation of its status that we
conducted on our own initiative, or as a result of making a finding on
a petition to list a species that listing is warranted but precluded by
other higher priority listing action (see the Petition Findings
section, below).
We maintain this list of candidates for a variety of reasons: to
notify the public that these species are facing threats to their
survival; to provide advance knowledge of potential listings that could
affect decisions of environmental planners and developers; to provide
information that may stimulate and guide conservation efforts that will
remove or reduce threats to these species and possibly make listing
unnecessary; to solicit input from interested parties to help us
identify those candidate species that may not require protection under
the Act or additional species that may require the
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Act's protections; and to solicit necessary information for setting
priorities for preparing listing proposals. We strongly encourage
collaborative conservation efforts for candidate species and offer
technical and financial assistance to facilitate such efforts. For
additional information regarding such assistance, please contact the
appropriate Regional Office listed in SUPPLEMENTARY INFORMATION or
visit our Internet website, http://endangered.fws.gov/candidates/
index.html.
Previous Notices of Review
We have been publishing candidate notices of review (CNOR) since
1975. The most recent CNOR (prior to this CNOR) was published on
December 6, 2007 (72 FR 69033). CNORs published since 1994 are
available on our Internet website, http://www.fws.gov/endangered/
candidates/index.html. For copies of CNORs published prior to 1994,
please contact the Branch of Candidate Conservation (see ADDRESSES
section above).
On September 21, 1983, we published guidance for assigning an LPN
for each candidate species (48 FR 43098). Using this guidance, we
assign each candidate an LPN of 1 to 12, depending on the magnitude of
threats, immediacy of threats, and taxonomic status; the lower the LPN,
the higher the listing priority (that is, a species with an LPN of 1
would have the highest listing priority). Such a priority ranking
guidance system is required under section 4(h)(3) of the Act (15 U.S.C.
1533(h)(3)). As explained below, in using this system we first
categorize based on the magnitude of the threat(s), then by the
immediacy of the threat(s), and finally by taxonomic status.
Under this priority ranking system, magnitude of threat can be
either ``high'' or ``moderate to low.'' This criterion helps ensure
that the species facing the greatest threats to their continued
existence receive the highest listing priority. It is important to
recognize that all candidate species face threats to their continued
existence, so the magnitude of threats is in relative terms. When
evaluating the magnitude of the threat(s) facing the species, we
consider information such as: the number of populations and/or extent
of range of the species affected by the threat(s); the biological
significance of the affected population(s), taking into consideration
the life history characteristics of the species and its current
abundance and distribution; whether the threats affect the species in
only a portion of its range, and if so the likelihood of persistence of
the species in the unaffected portions; and whether the effects are
likely to be permanent.
As used in our priority ranking system, immediacy of threat is
categorized as either ``imminent'' or ``nonimminent'' and is not a
measure of how quickly the species is likely to become extinct if the
threats are not addressed; rather, immediacy is based on when the
threats will begin. If a threat is currently occurring or likely to
occur in the very near future, we classify the threat as imminent.
Determining the immediacy of threats helps ensure that species facing
actual, identifiable threats are given priority for listing proposals
over those for which threats are only potential or species that are
intrinsically vulnerable to certain types of threats but are not known
to be presently facing such threats.
Our priority ranking system has three categories for taxonomic
status: species that are the sole members of a genus; full species (in
a genus that has more than one species); and subspecies, distinct
population segments of vertebrate species, and species for which
listing is appropriate in a significant portion of their range rather
than their entire range.
The result of the ranking system is that we assign each candidate a
listing priority number of 1 to 12. For example, if the threat(s) is of
high magnitude, with immediacy classified as imminent, the listable
entity is assigned an LPN of 1, 2, or 3 based on its taxonomic status
(e.g., a species that is the only member of a genus would be assigned
to the LPN 1 category, a full species to LPN 2, and a subspecies, DPS,
or a species for which listing is appropriate in a significant portion
of its range would be assigned to LPN 3). In summary, the LPN ranking
system provides a basis for making decisions about the relative
priority for preparing a proposed rule to list a given species. No
matter which LPN we assign to a species, each species included in this
notice as a candidate is one for which we have sufficient information
to prepare a proposed rule to list it because it is in danger of
extinction or likely to become endangered within the foreseeable future
throughout all or a significant portion of its range.
For more information on the process and standards used in assigning
LPNs, a copy of the guidance is available on our website at: http://
www.fws.gov/endangered/policy/index.html. For more information on the
LPN assigned to a particular species, the species assessment for each
candidate contains the LPN chart and a rationale for the determination
of the magnitude and imminence of threat(s) and assignment of the LPN;
that information is summarized in this CNOR.
This revised notice supersedes all previous animal, plant, and
combined candidate notices of review.
Summary of This CNOR
Since publication of the CNOR on December 6, 2007 (72 FR 69033), we
reviewed the available information on candidate species to ensure that
a proposed listing is justified for each species, and reevaluated the
relative LPN assigned to each species. We also evaluated the need to
emergency-list any of these species, particularly species with high
priorities (i.e., species with LPNs of 1, 2, or 3). This review and
reevaluation ensures that we focus conservation efforts on those
species at greatest risk first.
In addition to reviewing candidate species since publication of the
last CNOR, we have worked on numerous findings in response to petitions
to list species, and on proposed and final determinations for rules to
list species under the Act. Some of these findings and determinations
have been completed and published in the Federal Register, while work
on others is still under way. See the discussions of Preclusion and
Expeditious Progress, below, for details.
Based on our review of the best available scientific and commercial
information, with this CNOR we identify 1 new candidate species (see
New Candidates , below), change the LPN for 11 candidates (see Listing
Priority Changes in Candidates, below) and determine that listing
proposals are not warranted for 2 species and thus remove them from
candidate status (see Candidate Removals, below). Combined with the
other decisions published separately from this CNOR for individual
species that previously were candidates, a total of 251 species
(including 109 plant and 142 animal species) are now candidates
awaiting preparation of rules proposing their listing. These 251
species, along with the 50 species currently proposed for listing, are
included in Table 1.
Table 2 lists the changes from the previous CNOR, and includes
three species identified in the previous CNOR as either proposed for
listing or classified as candidates that are no longer in those
categories. This includes one species for which we published a final
rule to list, plus the two species that we have determined do not
warrant preparation of a rule to propose listing and therefore have
been removed from candidate status in this CNOR.
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New Candidates
Below we present a brief summary of one new plant candidate,
Sphaeralcea gierischii (Gierisch mallow), which we are recognizing in
this CNOR. Complete information, including references, can be found in
the species assessment form. You may obtain a copy of this form from
the Regional Office having the lead for the species (Region 2), or from
our Internet website (http://endangered.fws.gov/candidates/index.html).
For this species, we find that we have on file sufficient information
on biological vulnerability and threats to support a proposal to list
as endangered or threatened, but that preparation and publication of a
proposal is precluded by higher-priority listing actions (i.e., it met
our definition of a candidate species). We also note below that four
other species, Gunnison's prairie dog (specifically in the portion of
its range in montane portions of central and south central Colorado and
north central New Mexico), Rio Grande cutthroat trout, northern Mexican
garter snake, and Jollyville Plateau salamander, were identified as
candidates earlier this year as a result of separate petition findings
published in the Federal Register.
Mammals
Gunnison's prairie dog (Cynomys gunnisoni) - In a separate
warranted but precluded 12-month petition finding published on February
5, 2008 (73 FR 6660), we previously announced candidate status for the
Gunnison's prairie dog in the montane portion of its range, located in
central and south-central Colorado and north-central New Mexico. As
described in that notice, we determined that the montane portion of the
range, which comprises approximately 40 percent of the total range of
the species, is a significant portion of the range where listing the
species is warranted. In that notice we assigned the population an LPN
of 2. In this CNOR, we are making a technical correction to the LPN,
changing it to a 3. This correction makes the LPN for Gunnison's
prairie dog consistent with the clear intent of our 1983 LPN guidance
(48 FR 43098). Under our LPN guidance, among listable entities facing
threats of the same magnitude and imminence, a species that is the only
member of a genus has highest priority (e.g. LPN 1), a full species (in
a genus with more than one species) has the next highest priority (e.g.
LPN 2), and a subspecies or DPS are in the following priority category
(e.g. LPN 3). To be consistent with this approach, when we make a
finding that listing is warranted but precluded for a species in a
significant portion of its range (rather than throughout its entire
range), we assign it to the same LPN category as a subspecies or DPS
(e.g. LPN 3).
Reptiles
Northern Mexican gartersnake (Thamnophis eques megalops) - We
previously announced candidate status for this species in a separate
warranted but precluded 12-month petition finding published on November
25, 2008 (73 FR 71787).
Amphibians
Jollyville Plateau salamander (Eurycea tonkawae) - We previously
announced candidate status for this species in a separate warranted but
precluded 12-month petition finding published on December 13, 2007 (72
FR 71039).
Fish
Rio Grande cutthroat trout (Oncorhynchus clarki virginalis) - We
previously announced candidate status for this subspecies in a separate
warranted but precluded 12-month petition finding published on May 14,
2008 (73 FR 27899).
Flowering Plants
Sphaeralcea gierischii (Gierisch mallow) - The following
information is based on information contained in our files, including
site visits by species experts. There are nine known populations of
this species on a combined total of approximately 59.5 acres (ac)
(24.12 hectares (ha)) in Arizona and Utah. Seven populations are found
on approximately 55 ac (22.3 ha) managed by the Bureau of Land
Management in Arizona. One population occurs on approximately 2 ac
(0.81 ha) on land managed by the Arizona State Land Department. One
population occurs on approximately 2.5 ac (1.01 ha) in Utah. The
primary threat to the species in Arizona is ongoing gypsum mining and
associated activities. The primary threat to the species in Utah is
potential impacts from off-road vehicle use. The threats are high in
magnitude, since survival of the species is threatened throughout its
entire range in Arizona by gypsum mining, with the two largest
populations in active mining operations. Loss of those two populations
would significantly reduce the total number of individuals throughout
the range, threatening the long-term viability of this species. The
threats are imminent, since they are ongoing in Arizona. Therefore, we
assigned an LPN of 2 to this species.
Listing Priority Changes in Candidates
We reviewed the LPN for all candidate species and are changing the
numbers for the following species discussed below. Some of the changes
reflect actual changes in either the magnitude or imminence of the
threats. In one case, the LPN change reflects a change in the taxonomy
of the species. For some species, the LPN change reflects efforts to
ensure national consistency as well as closer adherence to the 1983
guidelines in assigning these numbers, rather than an actual change in
the nature of the threats.
Mammals
Gunnison's prairie dog (Cynomys gunnisoni) (montane population) -
See above summary under ``New Candidates''.
Birds
Red knot (Calidris canutus rufa) - The following summary is based
on information containted in our files and information provided by
petitioners. Four petitions to emergency list the red knot have been
received: one on August 9, 2004, two others on August 5, 2005, and the
latest on February 27, 2008. The rufa subspecies is one of six
recognized subspecies of red knot and one of three subspecies occurring
in North America (hereafter all mention of red knot in this CNOR refers
strictly to the rufa subspecies). This subspecies makes one of the
longest distance migrations known in the animal kingdom, as it travels
between breeding areas in the central Canadian Arctic and wintering
areas that are primarily in southern South America along the coast of
Chile and Argentina. They migrate along the Atlantic coast of the
United States, where they may be found from Maine to Florida.
The Delaware Bay area (in Delaware and New Jersey) is the largest
known spring migration stopover area, with far fewer migrants
congregating elsewhere along the Atlantic coast. The concentration in
the Delaware Bay area occurs from the middle of May to early June,
corresponding to the spawning season of horseshoe crabs. The knots feed
on horseshoe crab eggs, rebuilding energy reserves needed to complete
migrations to the Arctic and arrive on the breeding grounds in good
condition. In the past, horseshoe crab eggs at Delaware Bay were so
numerous that a knot could eat enough in two to three weeks to double
its weight.
Surveys at wintering areas and at Delaware Bay during spring
migration indicate a substantial decline in the red knot in recent
years. At the Delaware
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Bay area, peak counts between 1982 and 1998 were as high as 95,360
knots. Counts may vary considerably between years. Some of the
fluctuations can be attributed to predator-prey cycles in the breeding
grounds, and counts show that knots rebound from such reductions.
Research shows that since 1998, a high proportion of red knots leaving
the Delaware Bay failed to achieve threshold departure masses needed to
fly to breeding grounds and survive an initial few days of snow cover,
and this corresponded to reduced annual survival rates. Recently, peak
counts at the Delaware Bay area have been lower than in the past and do
not show a rebound. The peaks were 13,315 in 2004; 15,345 in 2005;
13,455 in 2006; and 12,375 in 2007. Counts in recent years at the
principal wintering areas in South America also are substantially lower
than in the past and do not show a rebound.
The primary factor threatening the red knot is destruction and
modification of its habitat, particularly the reduction in key food
resources resulting from reductions in horseshoe crabs, which are
harvested primarily for use as bait and secondarily to support a
biomedical industry. Commercial harvest increased substantially in the
1990s. Since 1999, a series of timing restrictions and substantially
lower harvest quotas have been adopted by the Atlantic States Marine
Fisheries Commission (ASMFC), as well as New Jersey and Delaware. In
May 2006, the ASMFC adopted restrictions effective from October 1,
2006, to September 30, 2008, including a prohibition on harvest and
landing of horseshoe crabs in New Jersey and Delaware from January 1
through June 7, harvest of males only from June 8 through December 31,
and harvest limited to no more than 100,000 horseshoe crabs per state
per year. The ASMFC also adopted other restrictions applicable to
Maryland and Virginia. New Jersey established regulations in 2006 which
superseded ASMFC restrictions; resulting in a moratorium on all
horseshoe crab harvest in New Jersey from May 15, 2006 through June 7,
2008. In March 2008, New Jersey passed legislation imposing an open-
ended moratorium on horseshoe crab harvest or landing within the State
until such time as the red knot has fully recovered. In February 2007,
Delaware imposed a 2-year moratorium, effective January 1, 2007, on
harvest of horseshoe crabs within Delaware lands or waters. In June
2007, following litigation by two businesses involved in the harvesting
and sale of horseshoe crabs, Delaware's moratorium was overturned.
Consequently Delaware developed regulations allowing for a male-only
horseshoe crab harvest, consistent with restrictions adopted by ASMFC.
The reductions in commercial harvest since 1999 are substantial:
726,660 horseshoe crab landings for bait were reported in 1999 in
Delaware and New Jersey, compared to 173,177 in 2004 and a preliminary
2007 report of 76,663 crabs landed for bait in Delaware and no
horseshoe crabs landed in New Jersey as a result of the State-imposed
harvest moratorium. However, we do not know whether horseshoe crab
populations will rebuild or how long a lag time there may be in
increased availability of eggs, as the species needs 8-10 years to
reach sexual maturity, and other key information for estimating
population response is lacking. A survey in Delaware Bay showed
horseshoe crab spawning activity was stable or slightly declining from
1999 to 2004. Updated spawning information following implementation of
additional harvest restrictions shows that female horseshoe crab
spawning activity in Delaware Bay has been stable for the overall
period of 1999 to 2007 and male horseshoe crab spawning increased
during that period. Thus, despite additional harvest regulations,
numbers of spawning females have not yet shown an increase.
The numbers of red knots at key wintering areas in South America
remained relatively steady from 2005 to 2007, giving optimism that the
declining trend may have ceased or slowed. In 2008, however, counts of
red knots within principal wintering areas showed an all-time low of
only 14,800 red knots. Counts of red knots within the principal
wintering areas in Chile and Argentina declined by nearly 75 percent
from 1985 to 2007 and declined by an additional 15 percent in the past
year (2007 to 2008). Thus, in recent years the number of knots in these
survey areas has been much lower than in the past and the trend in the
abundance is not improving despite a nearly tenfold reduction in
horseshoe crab landings since the late 1990s.
Other identified threat factors include habitat destruction due to
beach erosion and various shoreline protection and stabilization
projects that are affecting areas used by migrating knots for foraging,
the inadequacy of existing regulatory mechanisms, human disturbance,
and competition with other species for limited food resources. Also,
the concentration of red knots in the Delaware Bay areas and at a
relatively small number of wintering areas makes the species vulnerable
to potential large-scale events in those areas such as oil spills or
severe weather in those areas. Overall, we conclude that the threats,
in particular the modification of habitat through harvesting of
horseshoe crabs, severe enough that it puts the viability of the knot
at substantial risk and is therefore of a high magnitude. The threats
are currently occurring, and therefore imminent because of continuing
suppressed horseshoe-crab-egg forage conditions for red knot within the
Delaware Bay stopover. To help ensure consistency in the application of
our listing priority process, we changed the LPN from a 6 to a 3 for
this subspecies because threats are imminent.
Lesser prairie-chicken (Tympanuchus pallidicinctus) - The following
summary is based on information contained in our files and the petition
received on October 5, 1995. Additional information can be found in the
12-month finding published on June 7, 1998 (63 FR 31400). This species
occurs in Colorado, Kansas, New Mexico, Oklahoma, and Texas. Biologists
estimate that the occupied range has declined by 92 percent since the
1800s.
The most serious threat to the lesser prairie-chicken is the
present and threatened destruction, modification, and curtailment of
its habitat and range. This includes loss of habitat from conversion of
native rangelands to introduced forages and cultivation; conversion of
suitable restored habitat in the Conservation Reserve Program (CRP) to
cropland; cumulative habitat degradation caused by severe grazing; and
energy development, including wind, oil, and gas development. The
magnitude of threats to the species from wind energy development and
conversion of CRP lands to croplands has increased recently, both in
terms of ongoing activity and potential activity expected in the next
few years. Additional threats are woody plant invasion of open prairies
due to fire suppression, herbicide use (including resumption of
herbicide use in shinnery oak habitat), and habitat fragmentation
caused by structural and transportation developments. Many of these
threats may exacerbate the normal effects of periodic drought on
lesser- prairie-chicken populations. In many cases, the remaining
suitable habitat has become fragmented by the spatial arrangement of
these various activities. The increasing level of habitat fragmentation
means that (1) some of the remaining habitat patches may become smaller
than necessary to meet the requirements of individuals and populations;
(2) necessary habitat heterogeneity may be lost to areas of homogeneous
habitat structure; (3) areas between habitat patches may harbor higher
levels of
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predators or brood parasites; and (4) the probability of recolonization
of habitat that becomes unoccupied decreases as the distance between
suitable habitat patches expands. Based on our most recent assessment,
we find that ongoing threats to the lesser prairie-chicken have
increased in terms of the amount of habitat involved and that the
overall magnitude of threats to the lesser prairie-chicken throughout
its range is high because the threats put the viability of the lesser
prairie chicken at substantial risk. The threats are ongoing and thus,
imminent. Consequently, we changed the LPN from an 8 to a 2 for this
species.
Amphibians
Georgetown salamander (Eurycea naufragia) - The following summary
is based on information contained in our files. No new information was
provided in the petition received on May 11, 2004. The Georgetown
salamander is known from spring outlets along five tributaries to the
San Gabriel River and one cave in the City of Georgetown, Williamson
County, Texas. The Georgetown salamander has a very limited
distribution and depends on a constant supply of clean water from the
Northern Segment of the Edwards Aquifer for its survival.
Primary threats to this species are degradation of water quality
due to expanding urbanization. Increased impervious cover by
development increases the quantity and velocity of runoff that leads to
erosion and greater pollution transport. Pollutants and contaminants
that enter the Edwards Aquifer are discharged from spring outlets in
salamander habitat and have serious morphological and physiological
effects to the species. The Texas Commission on Environmental Quality
(TCEQ) adopted the Edwards Rules in 1995 and 1997, which require a
number of water-quality-protection measures for new development
occurring in the recharge and contributing zones of the Edwards
Aquifer. New developments are still obligated to comply with
regulations that were applicable at the time when project applications
for development were first filed. However, Chapter 245 of the Texas
Local Government Code permits ``grandfathering'' of state regulations.
Grandfathering allows developments to be exempted from any new local or
state requirements for water-quality controls and impervious-cover
limits if the developments were planned prior to the implementation of
such regulations. As a result of the grandfathering law, very few
developments have followed these ordinances. In addition, it is
significant that even if they were followed with every new development,
these ordinances do not span the entire watershed for the Edwards
Aquifer. The TCEQ has developed voluntary water quality protection
measures for development in the Edwards Aquifer region of Texas;
however, it is unknown if these measures will be implemented throughout
a large portion of the watershed or if they will be effective in
maintaining or improving water quality.
Development occurring outside the TCEQ's jurisdiction can have
negative consequences on water quality and thus affect the species.
Water-quality impacts threaten the continued existence of the
Georgetown salamander by altering physical aquatic habitats and the
food sources of the salamander. The threats are imminent because
urbanization is ongoing, and continues to expand over the Northern
Segment of the Edwards Aquifer. However, Williamson County and the
Williamson County Conservation Fund are currently actively working to
protect habitat and acquire land within the contributing watershed for
the Georgetown salamander. Also, they are planning to conduct
monitoring and data-collecting activities in an effort that is expected
to lead to the development of a conservation strategy for this species.
Although this species still meets our definition of a candidate, these
conservation actions reduce the magnitude of the threat to the
Georgetown salamander to a moderate level by reducing the amount of
development occurring in the portion of the watershed that affects the
species. Thus, we have changed the LPN from a 2 to an 8 for this
species.
Fishes
Headwater chub (Gila nigra) - The following summary is based on
information contained in our files and the 12-month finding on a
petition to list the species, which was published May 3, 2006 (71 FR
26007). The range of the headwater chub has been reduced by
approximately 60 percent. Seventeen streams (125 miles (200 kilometers)
of stream) are thought to be occupied out of 20 streams (312 miles (500
kilometers) of stream) formerly occupied in the Gila River Basin in
Arizona and New Mexico. Recent surveys have documented one new
population. All remaining populations are fragmented and isolated and
threatened by a combination of factors.
Headwater chub are threatened by introductions of nonnative fish
that prey on them and/or compete with them for food. These nonnative
fish are difficult to eliminate and, therefore, pose an ongoing threat.
Habitat destruction and modification has occurred and continues to
occur as a result of dewatering, impoundment, channelization, and
channel changes caused by alteration of riparian vegetation and
watershed degradation from mining, grazing, roads, water pollution,
urban and suburban development, groundwater pumping, and other human
actions. Existing regulatory mechanisms do not appear to be adequate
for addressing the impact of nonnative fish and also have not removed
or eliminated the threats that continue to be posed in relation to
habitat destruction or modification. The fragmented nature and rarity
of existing populations makes them vulnerable to other natural or
manmade factors, such as drought and wildfire.
The Arizona Game and Fish Department has created the Arizona
Statewide Conservation Agreement for Roundtail Chub (G. robusta),
Headwater Chub, Flannelmouth Sucker (Catostomus latipinnis), Little
Colorado River Sucker (Catostomus spp.), Bluehead Sucker (C.
discobolus), and Zuni Bluehead Sucker (C. discobolus yarrowi), which is
now final. The New Mexico Department of Game and Fish recently listed
the headwater chub as endangered and created a recovery plan for the
species, Colorado River Basin Chubs (Roundtail Chub, Gila Chub (G.
intermedia), and Headwater Chub) Recovery Plan, which was approved by
the New Mexico State Game Commission on November 16, 2006. Both the
Arizona Agreement and the New Mexico Recovery Plan recommend
preservation and enhancement of extant populations and restoration of
historical headwater-chub populations. The recovery and conservation
actions prescribed by Arizona and New Mexico plans, which we believe
will reduce and remove threats to this species, will require further
discussions and authorizations before they can be implemented, but
several of the actions are being planned. Although threats are ongoing,
new information indicates long-term persistence and stability of
existing populations. Surveys conducted in 2006-2007 found a new
population and determined that the Fossil Creek population is now
stable-secure. Currently 10 of the 17 extant populations are considered
stable based on abundance and evidence of recruitment. Based on our
assessment, threats (e.g., nonnative species, habitat loss from land
uses) remain imminent but are now of a moderate magnitude because the
threat of nonnative species and habitat destruction appear to be of
[[Page 75181]]
a lower magnitude than previously thought because all populations are
continuing to persist, and have persisted over approximately 15 years
of surveys on average, and some populations such as the upper Gila
River are now considered stable. Thus we changed the LPN from a 2 to an
8 for this species.
Clams
Texas hornshell (Popenaias popei) - The following summary is based
on information contained in our files and information provided by the
New Mexico Department of Game and Fish and Texas Parks and Wildlife
Department. No new information was provided in the petition received on
May 11, 2004. The Texas hornshell is a freshwater mussel found in the
Black River in New Mexico, and the Rio Grande and the Devils River in
Texas. Until March 2008, the only known extant populations were in New
Mexico's Black River and one locality in the Rio Grande near Laredo,
Texas. In March 2008, two new localities were confirmed in Texas - one
in the Devils River and one in the mainstem Rio Grande in the Rio
Grande Wild and Scenic River segment downstream of Big Bend National
Park.
The primary threats to this species are habitat alterations such as
stream bank channelization, impoundments, and diversions for
agriculture and flood control; contamination of water by oil and gas
activity; alterations in the natural riverine hydrology; and increased
sedimentation from prolonged overgrazing and loss of native vegetation.
Although riverine habitats throughout the species' known occupied range
are under constant threat from these ongoing or potential activities,
numerous conservation actions to benefit the species are underway in
New Mexico, including the completion of a state recovery plan for the
species and the drafting of a Candidate Conservation Agreement with
Assurances, and are beginning in Texas. We changed the LPN from a 2 to
an 8 based on our conclusion that these conservation actions have
reduced the magnitude of threats from high to moderate. This change in
the magnitude of threat is due to the discovery of previously unknown
locations where the species persists, as well as the implementation of
recovery planning and conservation actions that are underway in New
Mexico, and are beginning in Texas. The threats are still occurring,
and thus remain imminent.
Slabside pearlymussel (Lexingtonia dolabelloides) - The following
summary is based on information contained in our files. The slabside
pearlymussel is a freshwater mussel (Unionidae) endemic to the
Cumberland and Tennessee River systems (Cumberlandian Region) in
Alabama, Kentucky, Tennessee, and Virginia. It requires shoal habitats
in free-flowing rivers to survive and successfully recruit new
individuals into its populations.
Habitat destruction and alteration (e.g., impoundments,
sedimentation, and pollutants) are the chief factors contributing to
the decline of this species, which has been extirpated from numerous
regional streams and is no longer found in Kentucky. The slabside
pearlymussel was historically known from at least 32 streams, but is
currently restricted to no more than 10 isolated stream segments.
Current status information for most of the 10 populations deemed to be
extant is available from recent periodic sampling efforts (sometimes
annually) and other field studies. Comprehensive surveys have taken
place in the Middle and North Forks Holston River, Paint Rock River,
and Duck River in the past several years. Based on recent information,
the overall population of the slabside pearlymussel is declining
rangewide. Of the five streams in which the species remains in good
numbers (e.g., Clinch, North and Middle Forks Holston, Paint Rock, Duck
Rivers), the Middle and upper North Fork Holston Rivers have undergone
drastic recent declines, while the Clinch population has been in a
longer-term decline. Most of the remaining five populations (e.g.,
Powell River, Big Moccasin Creek, Hiwassee River, Elk River, Bear
Creek) have doubtful viability, and several if not all of them may be
on the verge of extirpation.
The threats remain high in magnitude, since all populations of this
species are severely affected in numerous ways (impoundments,
sedimentation, small population size, isolation of populations, gravel
mining, municipal pollutants, agricultural runoff, nutrient enrichment,
and coal processing pollution) which result in mortality and/or reduced
reproductive output. Since the threats are ongoing, they are imminent.
Therefore, to help ensure consistency in the application of our listing
priority process, we changed the LPN from a 5 to a 2 because the
threats are imminent and high in magnitude.
Snails
Fat-whorled pondsnail (Stagnicola bonnevillensis) - The fat-whorled
pondsnail, also known as the Bonneville pondsnail, occupies four spring
pools north of the Great Salt Lake in Box Elder County, Utah. The
number of individuals is unknown, and the total known occupied habitat
is less than 1 hectare (2.45 acres). The primary threat has been
chemical contamination of the groundwater. Significant actions are
under way to remediate this threat, including implementation of a
Corrective Action Plan to characterize and remediate groundwater
contamination and implementation of a site management plan. Also, a
groundwater model and risk assessment is being developed. The CAP is
being implemented, and conservation measures are currently being
monitored for effectiveness. Because these efforts have been under way
for a sufficient period to reduce the threat from contamination, the
magnitude of threats is reduced from moderate to low, and the threat is
now nonimminent. Therefore, we have changed the listing priority from
an 8 to an 11 for this species.
Elongate mud meadows springsnail (Pyrgulopsis notidicola) - The
following summary is based on information contained in our files.
Pyrgulopsis notidicola is endemic to Soldier Meadow, which is located
at the northern extreme of the western arm of the Black Rock Desert in
the transition zone between the Basin and Range Physiographic Province
and the Columbia Plateau Province, Humboldt County, Nevada. The type
locality, and the only known location of the species, occurs in a
stretch of thermal (between 45[deg] and 32[deg] Celsius, 113[deg] and
90[deg] Fahrenheit) aquatic habitat that is approximately 600 m (1,968
ft) long and 2 m (6.7 ft) wide. Pyrgulopsis notidicola occurs only in
shallow, flowing water on gravel substrate. The species does not occur
in deep water (i.e., impoundments) where water velocity is low, gravel
substrate is absent, and sediment levels are high.
The species and its habitat are threatened by recreational use in
the areas where it occurs, as well as by the ongoing impacts of past
water diversions and livestock grazing and current off-highway vehicle
travel. Conservation measures implemented recently by the Bureau of
Land Management include the installation of fencing to exclude
livestock, wild horses, burros and other large mammals; closing of
access roads to spring, riparian, and wetland areas and the limiting of
vehicles to designated routes; the establishment of a designated
campground away from the habitats of sensitive species; the
installation of educational signage; and increased staff presence,
including law enforcement and a volunteer site steward during the 6-
month period of peak visitor use. These conservation measures have
reduced the magnitude of threats to the
[[Page 75182]]
species to moderate; all remaining threats are nonimminent and involve
long-term changes to the habitat for the species resulting from past
impacts. Therefore, we have changed the LPN from 2 to 11.
Insects
Mardon skipper (Polites mardon) - The following summary is based on
information contained in our files and the petition we received on
December 24, 2002. The Mardon skipper is a northwestern butterfly with
a remarkably disjunct range. Currently this species is known from four
widely separated regions: south Puget Sound region, southern Washington
Cascades, Siskiyou Mountains of southern Oregon, and coastal
northwestern California/southern Oregon. The number of documented
locations for the species has increased from fewer than 10 in 1997 to
more than 100 rangewide in 2008. New site locations have been
documented in each year that targeted surveys have been conducted since
1999. In the past 8 years, significant local populations have been
located in the Washington Cascades and in Southern Oregon, with a few
local sites supporting populations of hundreds of Mardon skippers.
The Mardon skipper spends its entire life cycle in one location,
often on the same grassland patch. The dispersal ability of Mardon
skipper is restricted. Threats to the Mardon skipper include direct
impacts to individuals and local populations by off-road vehicle use,
livestock grazing, and pesticide drift. Habitat destruction or
modification through conifer encroachment, invasive nonnative plants,
roadside maintenance, and grassland/meadow management activities such
as prescribed burning and mowing are also threats. However, these
threats have been substantially reduced due to protections provided by
State and Federal special status species programs. The magnitude of the
threats is moderate because current regulatory mechanisms associated
with State and Federal special status species programs afford a
relatively high level of protection from additional habitat loss or
destruction across most of the species' range. Threats are imminent
because all sites within the species' range currently have one or more
identified threats that are resulting in direct impacts to individuals
within the populations, or a gradual loss or degradation of the
species' habitats. Mardon skippers face a variety of threats that may
occur at any time at any of the locations. Low numbers of individuals
have been found at most of the known locations. Only a few locations
are known to harbor greater than 100 individuals, and specific
locations could easily be lost by changes in vegetation composition or
from the threat of wildfire. The great distances between the known
locations for the species would not allow for dispersal of the species
between populations; thus, loss of any population could lead to
extirpation of the species at any of these locations. However, the
discovery of new populations and the wide geographic range for the
Mardon skipper provides a buffer against threats that could destroy all
existing habitat simultaneously or jeopardize the continued existence
of the species.
Since the threats are ongoing, they are imminent. Therefore, to
help ensure consistency in the application of our listing priority
process, we changed the LPN to reflect the fact that the threats are
imminent. At the same time, for the reasons described above, the
threats are now moderate in magnitude. Therefore, we changed the
listing priority number from a 5 to an 8 for the Mardon skipper.
Coral Pink Sand Dunes tiger beetle (Cicindela albissima) - The
following summary is based on information contained in our files and
the petition received April 25, 1994. The Coral Pink Sand Dunes tiger
beetle occurs only at the Coral Pink Sand Dunes, approximately 7 miles
west of Kanab, Kane County, in south-central Utah. It is restricted to
a small part of the dune field, situated at an elevation of about 1,820
m (6,000 ft).
The beetle's habitat is being adversely affected by ongoing,
recreational off-road vehicle use that is destroying and degrading the
beetle's habitat, especially the interdunal swales used by the larvae.
The continued survival of the beetle depends on the preservation of its
habitat. The two agencies that manage the dunes field, the Utah
Department of Parks and Recreation and the Bureau of Land Management,
have restricted recreational off-road vehicle use in some areas, which
reduces impacts. However, the protected areas may not be of sufficient
size to enable the population to increase in size, and off-road vehicle
use continues outside of the protected areas. Ongoing monitoring and
research has documented that conservation measures have failed to
lessen population declines. The beetle's population is also vulnerable
to over-collecting by professional and hobby tiger beetle collectors.
The taxon was previously recognized as a full species, resulting in a
change in the listing priority from a 9 to an 8, based on imminent
threats of a low to moderate magnitude. The magnitude of the threat
from off-road vehicle use is now high, since this threat results in
direct mortality to adult beetles, reduces available prey, and disturbs
and desiccates the microhabitat of the larvae, and in tandem with
drought, continues to cause steady declines in the tiger beetle
population. The threats continue to be ongoing and are, therefore,
imminent. Therefore, we changed the LPN from an 8 to a 2.
Flowering plants
Churchill Narrows buckwheat (Eriogonum diatomaceum) - The following
information is based on information contained in our files. Eriogonum
diatomaceum is restricted to chalky, diatomaceous outcrops between
1,311 and 1,390 meters (m) (4,300 and 4,560 feet (ft)) elevation in the
Churchill Narrows located in the Pine Nut Mountains, Lyon County,
Nevada.
Field surveys during 2005 have shown that the habitat of nearly all
the 15 known occurrences of E. diatomaceum is subject to exploration
and potential development of existing mining claims. Observations in
2003 confirmed that mining activities have had direct and indirect
impacts on E. diatomaceum in the recent past. Mineral development must
continue to be considered a threat of high magnitude because all known
populations of E. diatomaceum occur within existing mining claims on a
substrate with economic potential. However, because previous
applications to develop these industrial mineral deposits have been
withdrawn, we no longer consider mining to pose an imminent threat to
the species. Other threats to the species from trampling and soil
disturbance by livestock and other land uses are likely to have
localized impacts and to be cumulative over time; we do not consider
these activities to pose an imminent threat to the species.
Nevertheless, all known populations are small and current regulatory
mechanisms in place are inadequate in protecting the species throughout
its range. Eriogonum diatomaceum is considered threatened by the Nevada
Native Plant Society and was added to the Nevada State List of
critically endangered and threatened plants. Due to the nonimminent
threats of high magnitude, we have changed the LPN from a 2 to a 5 for
this species.
Candidate Removals
As summarized below, we have evaluated the threats to the following
two species and considered factors that, individually and in
combination, currently or potentially could pose a risk to these
species and their habitat. After a review of the best available
[[Page 75183]]
scientific and commercial data, we conclude that listing these two
species under the Endangered Species Act is not warranted because the
species are not likely to become endangered species within the
foreseeable future throughout all or a significant portion of their
range. Therefore, for each of these species we find that proposing a
rule to list it is not warranted, and we no longer consider it to be a
candidate species for listing. We will continue to monitor the status
of these species, and to accept additional information and comments
concerning this finding. We will reconsider our determination for each
species in the event that new information indicates that the threats to
the species are of a considerably greater magnitude or imminence than
identified through assessments of information contained in our files,
as summarized here.
Snails
Ogden mountainsnail (formerly considered to be Oreohelix
peripherica wasatchensis) - The Ogden mountainsnail was previously
thought to be a subspecies occurring at a single site near the mouth of
Ogden Canyon in Weber County, Utah. The subspecies was considered to be
vulnerable to extirpation from stochastic or human-caused events due to
its restricted range, its proximity to an expanding residential area,
and impacts from relatively heavy recreational use. Recent molecular
phylogenetic studies have clarified that what was previously classified
as Oreohelix peripherica wasatchensis is actually two distinct clades
(i.e., taxa descending from a common ancestor) rather than being a
separate subspecies: one clade is part of a different species, O.
strigosa, and the other is part of a different subspecies, O. p.
peripherica Because O. p. wasatchensis is no longer recognized as a
valid subspecies, it is not a listable entity under the Act. Therefore,
we find that listing O. p. wasatchensis is not warranted, and we have
removed it from candidate status.
Both O. strigosa and O. p. peripherica are widespread and abundant.
Our assessment shows that threats to the clades of these taxa at the
Ogden Canyon site are not affecting the overall status of O. strigosa
or O. p. peripherica such that either taxon is likely to become in
danger of extinction within the foreseeable future throughout all or a
significant portion of its range. Consequently, we find that listing is
not warranted for either O. strigosa or O. p. peripherica.
Flowering Plants
Indigofera trita subsp. scabra (formerly Indigofera mucronata var.
keyensis) (Florida indigo or Asian indigo) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. In 2007 we became
aware of new information regarding this plant's taxonomic status. We
now believe the most appropriate name for Florida indigo is I. trita
subsp. scabra. The current understanding is that this plant is
widespread, ranging widely from south Florida and the Caribbean to Asia
and Africa. We have only general information on this plant's status
outside of the United States. In Florida, this plant occurs in coastal
rock barrens, ecotone rock barren areas, and scraped areas mimicking
rock barren habitat. Based upon available data, there are 12
occurrences of Florida indigo on eight islands in the upper and middle
Florida Keys, in Monroe County; half of the original occurrences in the
Keys are now extirpated, as are historic occurrences on mainland
Florida in Collier and Miami-Dade Counties. Most occurrences in Florida
are small; total population size is probably close to 3,000
individuals. In the United States, Florida indigo is threatened by
habitat loss, even on public lands, as well as habitat loss and
degradation from exotic plants on all sites. Shading by hardwoods is a
problem at approximately half of the sites. Planned restoration
activities, illegal dumping, and trespass have also been identified as
threats. Florida indigo is vulnerable to natural disturbances, such as
hurricanes, tropical storms, and storm surges; however, these factors
may also work to maintain coastal rock barren habitat in the long-term.
Sea level rise is considered a long-term threat that will continue.
Although threats remain in Florida, the Florida indigo is now
considered to be a taxon that is widely distributed. We are not aware
of threats elsewhere in its considerable range; the species does not
warrant listing throughout its entire range. We have analyzed whether
the Florida population is a significant portion of the range. Based on
our evaluation of this population's low level of contribution toward
the resiliency, redundancy, and representation of the species as a
whole, we conclude that the Florida population of the Florida indigo is
not a significant portion of the range. Based on findings and analysis
in our updated assessment, we conclude that listing this species under
the Endangered Species Act is not warranted throughout all or a
significant portion of its range. The species no longer meets our
definition of a candidate, and we have removed it from candidate
status.
Petition Findings
The Act provides two mechanisms for considering species for
listing. One method allows the Secretary, on his own initiative, to
identify species for listing under the standards of section 4(a)(1). We
implement this through the candidate program, discussed above. The
second method for listing a species provides a mechanism for the public
to petition us to add a species to the Lists. Under section 4(b)(3)(A),
when we receive such a petition, we must determine within 90 days, to
the maximum extent practicable, whether the petition presents
substantial information that listing may be warranted (a ``90-day
finding''). If we make a positive 90-day finding, we must promptly
commence a status review of the species under section 4(b)(3)(A); we
must then make and publish one of three possible findings within 12
months of the receipt of the petition (a ``12-month finding''):
1. The petitioned action is not warranted;
2. The petitioned action is warranted (in which case we are
required to promptly publish a proposed regulation to implement the
petitioned action; once we publish a proposed rule for a species,
section 4(b)(5) and 4(b)(6) govern further procedures regardless of
whether we issued the proposal in response to a petition); or
3. The petitioned action is warranted but (a) the immediate
proposal of a regulation and final promulgation of regulation
implementing the petitioned action is precluded by pending proposals,
and (b) expeditious progress is being made to add qualified species to
the lists of endangered or threatened species. (We refer to this as a
``warranted-but-precluded finding.'')
Section 4(b)(3)(C) of the Act requires that when we make a
warranted-but-precluded finding on a petition, we are to treat such a
petition as one that is resubmitted on the date of such a finding.
Thus, we are required to publish new 12-month findings on these
``resubmitted'' petitions on an annual basis.
On December 5, 1996, we made a final decision to redefine
``candidate species'' to mean those species for which the Service has
on file sufficient information on biological vulnerability and
threat(s) to support issuance of a proposed rule to list, but for which
issuance of the proposed rule is
[[Page 75184]]
precluded (61 FR 64481; December 6, 1996). Therefore, the standard for
making a species a candidate through our own initiative is identical to
the standard for making a warranted-but-precluded 12-month petition
finding on a petition to list, and we add all petitioned species for
which we have made a warranted-but-precluded 12-month finding to the
candidate list.
This publication provides notice of substantial 90-day findings and
the warranted-but-precluded 12-month findings pursuant to section
4(b)(3) for candidate species listed on Table 1 that we identified on
our own initiative, and that subsequently have been the subject of a
petition to list. Even though all candidate species identified through
our own initiative already have received the equivalent of substantial
90-day and warranted-but-precluded 12-month findings, we reviewed the
status of the newly petitioned candidate species and through this CNOR
are publishing specific section 4(b)(3) findings (i.e., substantial 90-
day and warranted-but-precluded 12-month findings) in response to the
petitions to list these candidate species. We publish these findings as
part of the first CNOR following receipt of the petition.
Pursuant to section 4(b)(3)(C)(i) of the Act, once a petition is
filed regarding a candidate species, we must make a 12-month petition
finding in compliance with section 4(b)(3)(B) of the Act at least once
a year, until we publish a proposal to list the species or make a final
not-warranted finding. We make these annual findings for petitioned
candidate species through the CNOR.
Section 4(b)(3)(C)(iii) of the Act requires us to ``implement a
system to monitor effectively the status of all species'' for which we
have made a warranted-but-precluded 12-month finding, and to ``make
prompt use of the [emergency listing] authority [under section 4(b)(7)]
to prevent a significant risk to the well being of any such species.''
The CNOR plays a crucial role in the monitoring system that we have
implemented for all candidate species by providing notice that we are
actively seeking information regarding the status of those species. We
review all new information on candidate species as it becomes
available, prepare an annual species assessment form that reflects
monitoring results and other new information, and identify any species
for which emergency listing may be appropriate. If we determine that
emergency listing is appropriate for any candidate, whether it was
identified through our own initiative or through the petition process,
we will make prompt use of the emergency listing authority under
section 4(b)(7). We have been reviewing and will continue to review, at
least annually, the status of every candidate, whether or not we have
received a petition to list it. Thus, the CNOR and accompanying species
assessment forms also constitute the Service's annual finding on the
status of petitioned species pursuant to section 4(b)(3)(C)(i).
On June 20, 2001, the United States Court of Appeals for the Ninth
Circuit held that the 1999 CNOR (64 FR 57534; October 25, 1999) did not
demonstrate that we fulfilled the second component of the warranted-
but-precluded 12-month petition findings for the Gila chub and
Chiracahua leopard frog (Center for Biological Diversity v. Norton, 254
F.3d 833 (9\th\ Cir. 2001)). The court found that the one-line
designation in the table of candidates in the 1999 CNOR, with no
further explanation, did not satisfy section 4(b)(3)(B)(iii)'s
requirement that the Service publish a finding ``together with a
description and evaluation of the reasons and data on which the finding
is based.'' The court suggested that this one-line statement of
candidate status also precluded meaningful judicial review.
On June 21, 2004, the United States District Court for Oregon
agreed that we can use the CNOR as a vehicle for making petition
findings and that our reasoning for why listing is precluded does not
need to be based on an assessment at a regional level (as opposed to a
national level) (Center for Biological Diversity v. Norton Civ. No. 03-
1111-AA (D. Or.)). However, this court found that our discussion on why
listing the candidate species were precluded by other actions lacked
specificity; in the list of species that were the subject of listing
actions that precluded us from proposing to list candidate species, we
did not state the specific action at issue for each species in the list
and we did not indicate which actions were court-ordered.
On June 22, 2004, in a similar case, the United States District
Court for the Eastern District of California also concluded that our
determination of preclusion may appropriately be based on a national
analysis (Center for Biological Diversity v. Norton No. CV S-03-1758
GEB/DAD (E.D. Cal.)). This court also found that the Act's imperative
that listing decisions be based solely on science applies only to the
determination about whether listing is warranted, not the question of
when listing is precluded.
On March 24, 2005, the United States District Court for the
District of Columbia held that we may not consider critical habitat
activities in justifying our inability to list candidate species,
requiring that we justify both our preclusion findings and our
demonstration of expeditious progress by reference to listing
proceedings for unlisted species (California Native Plant Society v.
Norton, Civ. No. 03-1540 (JR) (D.D.C.)). The court further found that
we must adequately itemize priority listings, explain why certain
species are of high priority, and explain why actions on these high-
priority species preclude listing species of lower priority. The court
approved our reliance on national rather than regional priorities and
workload in establishing preclusion and approved our basic explanation
that listing candidate species may be precluded by statutorily mandated
deadlines, court-ordered actions, higher-priority listing activities,
and a limited budget.
In this CNOR we continue to incorporate information that addresses
the courts' concerns. We include a description of the reasons why the
listing of every petitioned candidate species is both warranted and
precluded at this time. We make our determinations of preclusion on a
nationwide basis to ensure that the species most in need of listing
will be addressed first and also because we allocate our listing budget
on a nationwide basis (see below). Regional priorities can also be
discerned from Table 1, which includes the lead region and the LPN for
each species. Our preclusion determinations are further based upon our
budget for listing activities for unlisted species, and we explain the
priority system and why the work we have accomplished does preclude
action on listing candidate species.
Pursuant to section 4(b)(3)(C)(ii) and the Administrative Procedure
Act (5 U.S.C. 551 et seq.), any party with standing may challenge the
merits of any not-warranted or warranted-but-precluded petition finding
incorporated in this CNOR. The analysis included herein, together with
the administrative record for the decision at issue (particularly the
supporting species assessment form), will provide an adequate basis for
a court to review the petition finding.
Nothing in this document or any of our policies should be construed
as in any way modifying the Act's requirement that we make a
resubmitted 12-month petition finding for each petitioned candidate
within 1 year of the date of publication of this CNOR. If we fail to
make any such finding on a timely basis, whether through publication of
a new CNOR or some
[[Page 75185]]
other form of notice, any party with standing may seek judicial review.
In this CNOR, we continue to address the concerns of the courts by
including specific information in our discussion on preclusion (see
below). In preparing this CNOR, we reviewed the current status of, and
threats to, the 174 candidates and 5 listed species for which we have
received a petition and for which we have found listing or
reclassification from threatened to endangered to be warranted but
precluded. We find that the immediate issuance of a proposed rule and
timely promulgation of a final rule for each of these species has been,
for the preceding months, and continues to be, precluded by higher-
priority listing actions. Additional information that is the basis for
this finding is found in the species assessments and our administrative
record for each species.
Through this CNOR we are making the first 90-day petition finding
and 12-month petition finding for Eriogonum corymbosum var. nilesii
(Las Vegas buckwheat) and the New Mexico meadow jumping mouse (Zapus
hudsonius luteus). We added these species to the candidate list in the
last CNOR (published December 6, 2007) and subsequently received
petitions for listing. We have not published separate substantial 90-
day and warranted-but-precluded 12-month petition findings, but are
making those findings in this CNOR.
Our review included updating the status of, and threats to,
petitioned candidate or listed species for which we published findings,
pursuant to section 4(b)(3)(B), in the previous CNOR. We have
incorporated new information we gathered since the prior finding and,
as a result of this review, we are making continued warranted-but-
precluded 12-month findings on the petitions for these species.
We have identified the candidate species for which we received
petitions by the code ``C*'' in the category column on the left side of
Table 1. The immediate publication of proposed rules to list these
species was precluded by our work on higher-priority listing actions,
listed below, during the period from October 1, 2007, through September
30, 2008. We will continue to monitor the status of all candidate
species, including petitioned species, as new information becomes
available to determine if a change in status is warranted, including
the need to emergency-list a species under section 4(b)(7) of the Act.
In addition to identifying petitioned candidate species in Table 1
below, we also present brief summaries of why these particular
candidates warrant listing. More complete information, including
references, is found in the species assessment forms. You may obtain a
copy of these forms from the Regional Office having the lead for the
species, or from the Fish and Wildlife Service's Internet website:
http://endangered.fws.gov/. As described above, under section 4 of the
Act we may identify and propose species for listing based on the
factors identified in section 4(a)(1), and section 4 also provides a
mechanism for the public to petition us to add a species to the lists
of species determined to be threatened species or endangered species
under the Act. Below we describe the actions that continue to preclude
the immediate proposal and final promulgation of a regulation
implementing each of the petitioned actions for which we have made a
warranted-but-precluded finding, and we describe the expeditious
progress we are making to add qualified species to the lists of
endangered or threatened species.
Preclusion and Expeditious Progress
Preclusion is a function of the listing priority of a species in
relation to the resources that are available and competing demands for
those resources. Thus, in any given fiscal year (FY), multiple factors
dictate whether it will be possible to undertake work on a proposed
listing regulation or whether promulgation of such a proposal is
warranted but precluded by higher-priority listing actions.
The resources available for listing actions are determined through
the annual Congressional appropriations process. The appropriation for
the Listing Program is available to support work involving the
following listing actions: proposed and final listing rules; 90-day and
12-month findings on petitions to add species to the Lists of
Endangered and Threatened Wildlife and Plants (Lists) or to change the
status of a species from threatened to endangered; annual
determinations on prior warranted-but- precluded petition findings as
required under section 4(b)(3)(C)(i) of the Act; critical habitat
petition findings, proposed and final rules designating critical
habitat; and litigation-related, administrative, and program management
functions (including preparing and allocating budgets, responding to
Congressional and public inquiries, and conducting public outreach
regarding listing and critical habitat). The work involved in preparing
various listing documents can be extensive, and may include, but is not
limited to: gathering and assessing the best scientific and commercial
data available and conducting analyses used as the basis for our
decisions; writing and publishing documents; and obtaining, reviewing,
and evaluating public comments and peer review comments on proposed
rules and incorporating relevant information into final rules. The
number of listing actions that we can undertake in a given year also is
influenced by the complexity of those listing actions; that is, more
complex actions generally are more costly. For example, during the past
several years, the cost (excluding publication costs) for preparing a
12-month finding, without a proposed rule, has ranged from
approximately $11,000 for one species with a restricted range that
requires a relatively uncomplicated analysis to $305,000 for another
species that is wide-ranging and requires a complex analysis.
We cannot spend more than is appropriated for the Listing Program
without violating the Anti-Deficiency Act (see 31 U.S.C.
1341(a)(1)(A)). In addition, in FY 1998 and for each fiscal year since
then, Congress has placed a statutory cap on funds which may be
expended for the Listing Program, equal to the amount expressly
appropriated for that purpose in that fiscal year. This cap was
designed to prevent funds appropriated for other functions under the
Act (for example, recovery funds for removing species from the Lists),
or for other Service programs, from beingused for Listing Program
actions (see House Report 105-163, 105\th\ Congress, 1st Session, July
1, 1997).
Recognizing that designation of critical habitat for species
already listed would consume most of the overall Listing Program
appropriation, Congress also put a critical habitat subcap in place in
FY 2002, and has retained it each subsequent year to ensure that some
funds are available for other work in the Listing Program: ``The
critical habitat designation subcap will ensure that some funding is
available to address other listing activities'' (House Report No. 107 -
103, 107\th\ Congress, 1st Session, June 19, 2001). In FY 2002 and each
year until FY 2006, the Service has had to use virtually the entire
critical habitat subcap to address court-mandated designations of
critical habitat, and consequently none of the critical habitat subcap
funds have been available for other listing activities. In FY 2007, we
were able to use some of the critical habitat subcap funds to fund
proposed listing determinations for high-priority candidate species;
however, in FY 2008 we were unable to do this because of all of the
critical habitat subcap funds were needed to
[[Page 75186]]
address our workload for designating critical habitat.
Thus, through the listing cap, the critical habitat subcap, and the
amount of funds needed to address court-mandated critical habitat
designations, Congress and the courts have in effect determined the
amount of money available for other listing activities. Therefore, the
funds in the listing cap, other than those needed to address court-
mandated critical habitat for already listed species, represent the
resources we must take into consideration when we make our
determinations of preclusion and expeditious progress.
Congress also recognized that the availability of resources was the
key element in deciding whether, when making a 12-month petition
finding, we would prepare and issue a listing proposal or instead make
a warranted-but-precluded finding for a given species. The Conference
Report accompanying Pub. L. 97-304, which established the current
statutory deadlines and the warranted-but-precluded finding, states (in
a discussion on 90-day petition findings that by its own terms also
covers 12-month findings) that the deadlines were ``not intended to
allow the Secretary to delay commencing the rulemaking process for any
reason other than that the existence of pending or imminent proposals
to list species subject to a greater degree of threat would make
allocation of resources to such a petition [that is, for a lower-
ranking species] unwise.'' Taking into account the information
presented above, in FY 2008, the outer parameter within which
``expeditious progress'' must be measured is that amount of progress
that could be achieved by spending $8,206,940, which was the amount
available in the Listing Program appropriation that was not within the
critical habitat subcap (because all of the funds within the subcap
were needed in order to complete court-mandated critical habitat
actions).
Our process is to make our determinations of preclusion on a
nationwide basis to ensure that the species most in need of listing
will be addressed first and also because we allocate our listing budget
on a nationwide basis. The $8,206,940 was used to fund work in the
following categories: compliance with court orders and court-approved
settlement agreements requiring that petition findings or listing
determinations be completed by a specific date; section 4 (of the Act)
listing actions with absolute statutory deadlines; essential
litigation-related, administrative, and listing program management
functions; and high-priority listing actions. The allocations for each
specific listing action are identified in the Service's FY 2008
Allocation Table (part of our administrative record).
Our decision that a proposed rule to list any of the petitioned
candidate species is warranted but precluded includes consideration of
its listing priority. In accordance with guidance we published on
September 21, 1983, we assign each candidate an LPN of 1 to 12,
depending on the magnitude of threats (high vs. moderate to low),
immediacy of threats (imminent or nonimminent), and taxonomic status of
the species (in order of priority: monotypic genus (a species that is
the sole member of a genus); species; or part of a species (subspecies,
distinct population segment, or significant portion of the range)). The
lower the listing priority number, the higher the listing priority
(that is, a species with an LPN of 1 would have the highest listing
priority). In addition to being precluded by lack of available funds,
work on proposed rules for candidates with lower priority (i.e., those
that have LPNs of 4-12) is also precluded by the need to issue proposed
rules for higher-priority candidate species facing high-magnitude,
imminent threats (i.e., LPNs of 1-3).
In FY 2007, we had more than 120 species with an LPN of 2.
Therefore, we further ranked the candidate species with an LPN of 2 by
using the following extinction-risk type criteria: International Union
for the Conservation of Nature and Natural Resources (IUCN) Red list
status/rank, Heritage rank (provided by NatureServe), Heritage threat
rank (provided by NatureServe), and species currently with fewer than
50 individuals, or 4 or fewer populations. Those species with the
highest IUCN rank (critically endangered), the highest Heritage rank
(G1), the highest Heritage threat rank (substantial, imminent threats),
and currently with fewer than 50 individuals, or fewer than 4
populations, comprised a list of approximately 40 candidate species.
These 40 candidate species have had the highest priority to receive
funding to work on a proposed listing determination. As we work on
proposed listing rules for these 40 candidates, we are applying the
ranking criteria to the next group of candidates with an LPN of 2 and 3
to determine the next set of highest priority candidate species.
To be more efficient in our listing process, as we work on proposed
rules for these species in the next several years, we are preparing
multi-species proposals when appropriate, and these may include species
with lower priority if they overlap geographically or have the same
threats as a species with an LPN of 2. In addition, available staff
resources are also a factor in determining which high-priority species
will receive funding. Finally, proposed rules for reclassification of
threatened species to endangered are lower priority, since as listed
species, they are already afforded the protection of the Act and
implementing regulations.
Thus, we continue to find that proposals to list the petitioned
candidate species included in Table 1 are all warranted but precluded,
except for the highest priority candidate species which are listed in
the tables below as having received funding in FY2008 for listing
activities.
As explained above, a determination that listing is warranted but
precluded must also demonstrate that expeditious progress is being made
to add and remove qualified species to and from the Lists of Endangered
and Threatened Wildlife and Plants. (Although we do not discuss it in
detail here, we are also making expeditious progress in removing
species from the list under the Recovery program, which is funded by a
separate line item in the budget of the Endangered Species Program. As
explained above in our description of the statutory cap on Listing
Program funds, the Recovery Program funds and actions supported by them
cannot be considered in determining expeditious progress made in the
Listing Program.) As with our ``precluded'' finding, expeditious
progress in adding qualified species to the Lists is a function of the
resources available and the competing demands for those funds. Given
that limitation, we find that we made expeditious progress in FY 2008
in the Listing Program. This progress included preparing and publishing
the following determinations:
[[Page 75187]]
FY 2008 Completed Listing Actions
----------------------------------------------------------------------------------------------------------------
Publication Date Title Actions FR Pages
----------------------------------------------------------------------------------------------------------------
10/09/2007 90-Day Finding on a Notice of 90-day 72 FR 57278-57283
Petition to List the Petition Finding,
Black-Footed Albatross Substantial
(Phoebastria nigripes)
as Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
;10/09/2007 90-Day Finding on a Notice of 90-day 72 FR 57273-57276
Petition To List the Petition Finding, Not
Giant Palouse substantial
Earthworm as
Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
;10/23/2007 90-Day Finding on a Notice of 90-day 72 FR 59983-9989
Petition To List the Petition Finding, Not
Mountain Whitefish substantial
(Prosopium
williamsoni) in the
Big Lost River, ID, as
Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
;10/23/2007 90-Day Finding on a Notice of 90-day 72 FR 59979-59983
Petition To List the Petition Finding, Not
Summer-Run Kokanee substantial
Population in Issaquah
Creek, WA, as
Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
11/08/2007 Response to Court on Response to Court 72 FR 63123-63140
Significant Portion of
the Range, and
Evaluation of Distinct
Population Segments,
for the Queen
Charlotte Goshawk
----------------------------------------------------------------------------------------------------------------
12/13/2007 12-Month Finding on a Notice of 12-month 72 FR 1039-71054
Petition To List the Petition Finding,
Jollyville Plateau Warranted but
salamander (Eurycea Precluded
tonkawae) as
Endangered With
Critical Habitat
----------------------------------------------------------------------------------------------------------------
1/08/2008 90-Day Finding on a Notice of 90-day 73 FR 1312-1313
Petition To List the Petition Finding,
Pygmy Rabbit Substantial
(Brachylagus
idahoensis) as
Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
1/10/2008 90-Day Finding on Notice of 90-day 73 FR 1855-1861
Petition To List the Petition Finding,
Amargosa River Substantial
Population of the
Mojave Fringe-Toed
Lizard (Uma scoparia)
as Threatened or
Endangered With
Critical Habitat
----------------------------------------------------------------------------------------------------------------
1/24/2008 12-Month Finding on a Notice of 12-month 73 FR 4379-4418
Petition To List the Petition Finding, Not
Siskiyou Mountains Warranted
Salamander (Plethodon
stormi) and Scott Bar
Salamander (Plethodon
asupak) as Threatened
or Endangered
----------------------------------------------------------------------------------------------------------------
2/05/2008 12-Month Finding on a Notice of 12-month 73 FR 6660-6684
Petition To List the Petition Finding,
Gunnison's Prairie Dog Warranted but
as Threatened or Precluded
Endangered
----------------------------------------------------------------------------------------------------------------
02/07/2008 12-Month Finding on a Notice of Review 73 FR 7236-7237
Petition To List the
Bonneville Cutthroat
Trout (Oncorhynchus
clarki utah) as
Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
02/19/2008 Listing Phyllostegia Proposed Listing, 73 FR 9078-9085
hispida (No Common Endangered
Name) as Endangered
Throughout Its Range
----------------------------------------------------------------------------------------------------------------
02/26/2008 Initiation of Status Notice of Status Review 73 FR 10218-10219
Review for the Greater
Sage-Grouse
(Centrocercus
urophasianus) as
Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
03/11/2008 12-Month Finding on a Notice 12-month 73 FR 12929-12941
Petition To List the petition finding, Not
North American warranted
Wolverine as
Endangered or
Threatened
----------------------------------------------------------------------------------------------------------------
03/20/2008 90-Day Finding on a Notice of 90-day 73 FR 14950-14955
Petition To List the Petition Finding,
U.S. Population of Substantial
Coaster Brook Trout
(Salvelinus
fontinalis) as
Endangered
----------------------------------------------------------------------------------------------------------------
04/29/2008 90-Day Finding on a Notice of 90-day 73 FR 23170-23172
Petition to List the Petition Finding,
Western Sage-Grouse Substantial
(Centrocercus
urophasianus phaios)
as Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
04/29/2008 90-Day Finding on Notice of 90-day 73 FR 23173-23175
Petitions To List the Petition Finding,
Mono Basin Area Substantial
Population of the
Greater Sage-Grouse
(Centrocercus
urophasianus) as
Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
05/06/2008 Petition To List the Notice of 90-day 73 FR 24611-24915
San Francisco Bay- Petition Finding,
Delta Population of Substantial
the Longfin Smelt
(Spirinchus
thaleichthys) as
Endangered
----------------------------------------------------------------------------------------------------------------
[[Page 75188]]
05/06/2008 90-Day Finding on a Notice of 90-day 73 FR 24915-24922
Petition to List Petition Finding,
Kokanee (Oncorhynchus Substantial
nerka) in Lake
Sammamish, Washington,
as Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
05/06/2008 12-Month Finding on a Notice of Status Review 73 FR 24910-24911
Petition to List the
White-tailed Prairie
Dog (Cynomys leucurus)
as Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
05/15/2008 90-Day Finding on a Notice of 90-day 73 FR 28080-28084
Petition To List the Petition Finding,
Ashy Storm-Petrel Substantial
(Oceanodroma
homochroa) as
Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
05/15/2008 Determination of Final Listing, 73 FR 28211-28303
Threatened Status for Threatened
the Polar Bear (Ursus
maritimus) Throughout
Its Range; Final Rule
----------------------------------------------------------------------------------------------------------------
05/15/2008 Special Rule for the Interim Final Special 73 FR 28305-28318
Polar Bear; Interim Rule
Final Rule
----------------------------------------------------------------------------------------------------------------
05/28/2008 Initiation of Status Notice of Status Review 73 FR 30596-30598
Review for the
Northern Mexican
Gartersnake
(Thamnophis eques
megalops)
----------------------------------------------------------------------------------------------------------------
06/18/2008 90-Day Finding on Notice of 90-day 73 FR 34686-34692
aPetition To List the Petition Finding, Not
Long-Tailed Duck substantial
(Clangula hyemalis) as
Endangered
----------------------------------------------------------------------------------------------------------------
07/10/2008 90-Day Finding on a Notice of 90-day 73 FR 39639-39643
Petition To Reclassify Petition Finding,
the Delta Smelt Substantial
(Hypomesus
transpacificus) From
Threatened to
Endangered
----------------------------------------------------------------------------------------------------------------
07/29/2008 90-Day Finding on a Notice of 90-day 73 FR 43905-43910
Petition To List the Petition Finding,
Tucson Shovel-Nosed Substantial
Snake (Chionactis
occipitalis klauberi)
as Threatened or
Endangered with
Critical Habitat
----------------------------------------------------------------------------------------------------------------
8/13/2008 Proposed Endangered Proposed Critical 73 FR 47257-47324
Status for Reticulated Habitat, Proposed
Flatwoods Salamander; Listing, Endangered
Proposed Designation
of Critical Habitat
for Frosted Flatwoods
Salamander and
Reticulated Flatwoods
Salamander
----------------------------------------------------------------------------------------------------------------
9/9/2008 12-month Finding on a Notice 12 month 73 FR 52235-52256
Petition to List the petition finding, Not-
Bonneville Cutthroat warranted
Trout as Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
Our expeditious progress also included work on listing actions,
which were funded in FY 2008, but were not completed in FY 2008
(information on the cost of individual actions are part of our
administrative record). These actions are listed below. We have
completed all work funded in FY 2008 on all actions under a deadline
set by a court. Actions in the middle section of the table are being
conducted to meet statutory timelines, that is, timelines required
under the Act. Actions in the bottom section of the table are high
priority listing actions. These actions include work primarily on
species with an LPN of 2, and selection of these species is partially
based on available staff resources, and when appropriate, include
species with a lower priority if they overlap geographically or have
the same threats as the species with the high priority. Including these
species together in the same proposed rule results in considerable
savings in time and funding as compared to preparing separate proposed
rules for each of them in the future.
Actions funded in FY 2008 but not completed in 2008
------------------------------------------------------------------------
Action
-----------------------------
Species Actions Subject to Court
Order/Settlement Agreement
------------------------------------------------------------------------
NONE NONE
------------------------------------------------------------------------
Actions with Statutory Deadlines
------------------------------------------------------------------------
Phyllostegia hispida Final listing
------------------------------------------------------------------------
Yellow-billed loon 12-month petition finding
------------------------------------------------------------------------
Black-footed albatross 12-month petition finding
------------------------------------------------------------------------
Mount Charleston blue butterfly 12-month petition finding
------------------------------------------------------------------------
Goose Creek milk-vetch 12-month petition finding
------------------------------------------------------------------------
Mojave fringe-toed lizard 12-month petition finding
------------------------------------------------------------------------
White-tailed prairie dog 12-month petition finding
------------------------------------------------------------------------
Pygmy rabbit (rangewide) 12-month petition finding
------------------------------------------------------------------------
Black-tailed prairie dog 90-day petition finding
------------------------------------------------------------------------
Lynx (include New Mexico in listing) 90-day petition finding
------------------------------------------------------------------------
Wyoming pocket gopher 90-day petition finding
------------------------------------------------------------------------
Dusky Tree Vole1 90-day petition finding
------------------------------------------------------------------------
Llanero coqui 90-day petition finding
------------------------------------------------------------------------
[[Page 75189]]
American pika 90-day petition finding
------------------------------------------------------------------------
Sacramento Valley Tiger Beetle1 90-day petition finding
------------------------------------------------------------------------
Sacramento Mts. checkerspot butterfly 90-day petition finding
------------------------------------------------------------------------
206 species 90-day petition finding
------------------------------------------------------------------------
475 Southwestern species 90-day petition finding
------------------------------------------------------------------------
High Priority Listing Actions ............................
------------------------------------------------------------------------
48 Kauai species1 (includes 31 candidate Proposed listing (completed
species: 24 with LPN = 2, 3 with LPN = 3, in October 2008)
1 with LPN = 5, 2 with LPN = 8)
------------------------------------------------------------------------
21 Oahu candidate species (16 plants, 5 Proposed listing
damselflies) (18 with LPN = 2, 3 with LPN
= 3, 1 with LPN = 9)
------------------------------------------------------------------------
3 southeast aquatic species (Georgia Proposed listing
pigtoe, interrupted rocksnail, rough
hornsnail)2 (all with LPN = 2)
------------------------------------------------------------------------
Casey's june beetle (LPN = 2) Proposed listing
------------------------------------------------------------------------
Sand dune lizard (LPN = 2) Proposed listing
------------------------------------------------------------------------
2 southwest springsnails (Pyrgulopsis Proposed listing
bernadina (LPN = 2), Pyrgulopsis
trivialis (LPN = 2))
------------------------------------------------------------------------
3 southwest springsnails (Pyrgulopsis Proposed listing
chupaderae (LPN = 2), Pyrgulopsis gilae
(LPN = 11), Pyrgulopsis thermalis (LPN =
11))
------------------------------------------------------------------------
2 mussels (rayed bean (LPN = 2), snuffbox Proposed listing
No LPN)
------------------------------------------------------------------------
2 mussels (sheepnose (LPN = 2), Proposed listing
spectaclecase (LPN = 4),)
------------------------------------------------------------------------
Ozark hellbender3 (LPN = 3) Proposed listing
------------------------------------------------------------------------
Altamaha spinymussel (LPN = 2) Proposed listing
------------------------------------------------------------------------
4 southeast fish (rush darter (LPN = 2), Proposed listing
chucky madtom (LPN = 2), Cumberland
darter (LPN = 5), laurel dace (LPN = 5))
------------------------------------------------------------------------
2 Colorado plants (Parachute beardtongue Proposed listing
(Penstemon debilis) (LPN = 2), Debeque
phacelia (Phacelia submutica) (LPN = 8))
------------------------------------------------------------------------
Pagosa skyrocket (Ipomopsis polyantha) Proposed listing
(LPN = 2)
------------------------------------------------------------------------
------------------------------------------------------------------------
1 These actions were completed in October 2008.
2 Funds for listing actions for 3 of these species were also provided in
FY 2007.
3 We funded a proposed rule for this subspecies with an LPN of 3 ahead
of other species with LPN of 2, because the threats to the species
were so imminent and of a high magnitude that we considered emergency
listing if we were unable to fund work on a proposed listing rule in
FY 2008.
We also funded work on resubmitted petitions findings for 174
candidate species (species petitioned prior to the last CNOR). We did
not update our resubmitted petition finding for the Columbia Basin
population of the greater sage-grouse in this notice, as we are
considering new information and will update our findings at a later
date (see 73 FR 23170, April 29, 2008). We also did not update our
resubmitted petition findings for the 66 candidate species for which we
are preparing proposed listing determinations; see summaries below
regarding publication of these determinations. We also funded revised
12-month petition findings for two candidate species that we are
removing from candidate status, which are being published as part of
this CNOR (see Summary of Candidate Removals). Because the majority of
these species were already candidate species prior to our receipt of a
petition to list them, we had already assessed their status using funds
from our Candidate Conservation Program. We also continue to monitor
the status of these species through our Candidate Conservation Program.
The cost of updating the species assessment forms and publishing the
joint publication of the CNOR and resubmitted petition findings is
shared between the Listing Program and the Candidate Conservation
Program.
During FY 2008, we also funded work on resubmitted petition
findings for uplisting five listed species, for which petitions were
previously received.
We have endeavored to make our listing actions as efficient and
timely as possible, given the requirements of the relevant law and
regulations, and constraints relating to workload and personnel. We are
continually considering ways to streamline processes or achieve
economies of scale, such as by batching related actions together. Given
our limited budget for implementing section 4 of the Act, these actions
described above collectively constitute expeditious progress.
Although we have not been able to resolve the listing status of
many of the candidates, several programs in the Service contribute to
the conservation of these species. In particular, we have a separate
budgeted program, the Candidate Conservation program, which focuses on
providing technical expertise for developing conservation strategies
and agreements to guide voluntary on-the-ground conservation work for
candidate and other at-risk species. The main goal of this program is
to address the threats facing candidate species. Through this program,
we work with our partners (other Federal agencies, State agencies,
Tribes, local governments, private landowners, and private conservation
organizations) to address the threats to candidate species and other
species at-risk. We are currently working with our partners to
implement voluntary conservation agreements for more than 140 species
covering 5 million acres of habitat.
We are actively working to conserve many candidate species. In some
instances, the sustained implementation of strategically designed
conservation efforts culminates in making listing
[[Page 75190]]
unnecessary for species that are proposed or candidates for listing.
Recent examples of species for which listing has been unnecessary due
to the contributions of conservation efforts include the Cow Head tui
chub, Beaver Cave beetle, Surprising Cave beetle, and Sand Mountain
blue butterfly.
Findings for Petitioned Candidate Species
For our revised 12-month petition findings for species we are
removing from candidate status, see summaries above under ``Summary of
Candidate Removals.''
Mammals
Pacific Sheath-tailed Bat, American Samoa DPS (Emballonura
semicaudata semicaudata) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. This small bat is a member of
the Emballonuridae, an Old World bat family that has an extensive
distribution, primarily in the tropics. The Pacific sheath-tailed bat
was once common and widespread in Polynesia and Micronesia and it is
the only insectivorous bat recorded from a large part of this area. The
species as a whole (E. semicaudata) occurred on several of the Caroline
Islands (Palau, Chuuk, and Pohnpei), Samoa (Independent and American),
the Mariana Islands (Guam and the CNMI), Tonga, Fiji, and Vanuatu.
While populations appear to be healthy in some locations, mainly in the
Caroline Islands, they have declined substantially in other areas,
including Independent and American Samoa, the Mariana Islands, Fiji,
and possibly Tonga. Scientists recognize four subspecies: E. s.
rotensis, endemic to the Mariana Islands (Guam and the Commonwealth of
the Northern Mariana Islands (CNMI)); E. s. sulcata, occurring in Chuuk
and Pohnpei; E. s. palauensis, found in Palau; and E. s. semicaudata,
occurring in American and Independent Samoa, Tonga, Fiji, and Vanuatu.
This candidate assessment form addresses the distinct population
segment (DPS) of E. s. semicaudata that occurs in American Samoa.
E. s. semicaudata historically occurred in American and Independent
Samoa, Tonga, Fiji, and Vanuatu. It is extant in Fiji and Tonga, but
may be extirpated from Vanuatu and Independent Samoa. There is some
concern that it is also extirpated from American Samoa, the location of
this DPS, where surveys are currently ongoing to ascertain its status.
The factors that led to the decline of this subspecies and the DPS are
poorly understood; however, current threats to this subspecies and the
DPS include habitat loss, predation by introduced species, and its
small population size and distribution, which make the taxon extremely
vulnerable to extinction due to typhoons and similar natural
catastrophes. Thus, the threats are high in magnitude. The Pacific
sheath-tailed bat may also by susceptible to disturbance to roosting
caves. The LPN for E. s. semicaudata is 3 because the magnitude of the
threats is high, the threats are ongoing, and therefore, imminent, and
the taxon is a distinct population segment of a subspecies.
Pacific Sheath-tailed Bat (Emballonura semicaudata rotensis), Guam
and the Commonwealth of the Northern Mariana Islands - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
This small bat is a member of the Emballonuridae, an Old World bat
family that has an extensive distribution, primarily in the tropics.
The Pacific sheath-tailed bat was once common and widespread in
Polynesia and Micronesia and it is the only insectivorous bat recorded
from a large part of this area. E. s. rotensis is historically known
from the Mariana Islands and formerly occurred on Guam and in the CNMI
on Rota, Aguiguan, Tinian (known from prehistoric records only),
Saipan, and possibly Anatahan and Maug. Currently, E. s. rotensis
appears to be extirpated from all but one island in the Mariana
archipelago. The single remaining population of this subspecies occurs
on Aguiguan, Commonwealth of the Northern Mariana Islands (CNMI).
Threats to this subspecies have not changed over the past year. The
primary threats to the subspecies are ongoing habitat loss and
degradation as a result of feral goat (Capra hircus) activity on the
island of Aguiguan and the taxon's small population size and limited
distribution. Predation by nonnative species and human disturbance are
also potential threats to the subspecies. The subspecies may be near
the point where stochastic events, such as typhoons, are increasingly
likely to affect its continued survival. The disappearance of the
remaining population on Aguiguan would result in the extinction of the
subspecies. Thus, the threats are high in magnitude. The LPN for E. s.
rotensis remains at 3 because the magnitude of the threats is high, the
threats are ongoing, and therefore, imminent, and the taxon is a
subspecies.
New England cottontail (Sylvilagus transitionalis) - The following
summary is based on information contained in our files and information
received in response to our notice published on June 30, 2004, when we
announced our 90-day petition finding and initiation of a status review
(69 FR 39395). We received the petition on August 30, 2000.
The New England cottontail (NEC) is a medium to large sized
cottontail rabbit that may reach 1,000 grams in weight, and is one of
two species within the genus Sylvilagus occurring in New England. New
England cottontails are considered habitat specialists, in so far as
they are dependent upon early-successional habitats typically described
as thickets. The species is the only endemic cottontail in New England.
Historically, the NEC occurred in seven states and ranged from
southeastern New York (east of the Hudson River) north through the
Champlain Valley, southern Vermont, the southern half of New Hampshire,
southern Maine and south throughout Massachusetts, Connecticut and
Rhode Island. The current range of the NEC has declined substantially
and occurrences have become increasingly separated. The species'
distribution is fragmented into five apparently isolated
metapopulations. The area occupied by the cottontail has contracted
from approximately 90,000 sq km to 12,180 sq km. Recent surveys
indicate that the long term decline in NEC continues. For example,
surveys for the species in early 2008 documented the presence of NEC in
7 of the 23 New Hampshire locations that were known to be occupied in
2002 and 2003. Similarly, surveys in Maine found the species present in
12 of 57 sites identified in an extensive survey that spanned the years
2000 to 2004. Unlike the New Hampshire study, several new sites were
documented in Maine during 2008. Some have suggested that the decline
in NEC occurrences in 2008 may be attributed to persistent snow cover
throughout northern New England during the winter of 2007-2008. Similar
surveys to assess trends in other states have not been conducted. It is
estimated that less than one third of the occupied sites occur on lands
in conservation status and fewer than 10 percent are being managed for
early-successional forest species.
The primary threat to the New England cottontail is loss of habitat
through succession and alteration. Isolation of occupied patches by
areas of unsuitable habitat and high predation rates are resulting in
local extirpation of New England cottontails from small patches. The
range of the New England cottontail has contracted by 75 percent
[[Page 75191]]
or more since 1960 and current land uses in the region indicate that
the rate of change, about two percent range loss per year, will
continue. Additional threats include competition for food and habitat
with introduced eastern cottontails and large numbers of native white-
tailed deer; inadequate regulatory mechanisms to protect habitat; and
mortality from predation. The magnitude of the threats continues to be
high, because they occur rangewide, and have an effect on the survival
of the species. They are imminent because they are ongoing. Thus, we
retained an LPN of 2 for this species.
Fisher, West Coast DPS (Martes pennanti) - The following summary is
based on information contained in our files and in the Service's
initial warranted-but-precluded finding published in the Federal
Register on April 8, 2004 (68 FR 18770). The fisher is a carnivore in
the family Mustelidae and is the largest member of the genus Martes.
Historically, the West Coast population of the fisher extended south
from British Columbia into western Washington and Oregon, and in the
North Coast Ranges, Klamath-Siskiyou Mountains, and Sierra Nevada in
California. The fisher is believed to be extirpated or reduced to
scattered individuals from the lower mainland of British Columbia
through Washington and in the central and northern Sierra Nevada range
in California. Native populations of fisher currently occur in the
North Coast Ranges of California, the Klamath- Siskiyou Mountains of
northern California and southern Oregon, and in isolated populations
occurring in the southern Sierra Nevada in California. Descendents of a
fisher reintroduction effort also occur in the southern Cascade Range
in Oregon. In January of 2008, the Washington Department of Fish and
Wildlife began to implement their fisher recovery goals for the state
through a reintroduction effort currently underway in the Olympic
National Park.
We lack precise empirical data on West Coast DPS fisher numbers.
However, there is a lack of detections over much of the fisher's
historic range, even with standardized survey and monitoring efforts in
California, Oregon, and Washington. There is also a high degree of
genetic relatedness within some populations, and populations of native
fisher in California are separated by four times the species' maximum
dispersal distance. The above listed factors all indicate that the
likely extant fisher populations are small and isolated from one
another.
Major threats that fragment or remove key elements of fisher
habitat include various forest vegetation management practices such as
timber harvest and fuels reduction treatments. Other potential major
threats in portions of the range include: uncharacteristically severe
wildfire, changes in forest composition and structure, urban and rural
development, recreation development, and highways. Major threats to
fisher that lead to direct mortality and injury to fisher include:
Collisions with vehicles; predation; and viral borne diseases such as
rabies, parvovirus, canine distemper, and Anaplasma phagocytophilum.
Existing regulatory mechanisms on Federal, State, and private lands
affect key elements of fisher habitat and do not currently provide
sufficient certainty that conservation efforts will be effective or
will be implemented. The magnitude of threats is high, as they occur
across the range of the DPS resulting in a negative impact on fisher
distribution and abundance. However, the threats are nonimminent as the
greatest long-term risks to the fisher in its west coast range are the
subsequent ramifications of the isolation of small populations and
their interactions with the listed threats. The three other areas
containing fisher populations appear to be stable or are not rapidly
declining based on recent survey and monitoring efforts. Therefore, we
assigned an LPN of 6 to this population.
New Mexico meadow jumping mouse (Zapus hudsonius luteus) - The
following summary is based on information contained in our files and
the petition we received October 15, 2008. The New Mexico meadow
jumping mouse (jumping mouse) is endemic to New Mexico, Arizona, and a
small area of southern Colorado. The jumping mouse nests in dry soils,
but uses moist, streamside, dense riparian/wetland vegetation. Recent
genetic studies confirm that the New Mexico meadow jumping mouse is a
distinct subspecies from other Zapus hudsonius subspecies, confirming
the currently accepted subspecies designation.
The threats that have been identified are excessive grazing
pressure, water use and management, highway reconstruction,
development, recreation, and beaver removal. Surveys conducted in 2005
and 2006 documented a drastic decline in the number of occupied
localities and suitable habitat across the range of the species in New
Mexico and Arizona. Of the original 98 known historical localities,
there are now only 9 known extant localities in New Mexico, 2 in
Arizona, and an additional 8 localities that have not been surveyed
since the early to mid 1990s. Moreover, the highly fragmented nature of
its distribution is also a major contributor to the vulnerability of
this species and increases the likelihood of very small, isolated
populations being extirpated. The insufficient number of secure
populations, and the destruction, modification, or curtailment of its
habitat, continue to pose the most immediate threats to this species.
Because the threats affect the survival of jumping mouse in all but two
of the extant localities, the threats are of a high magnitude. These
threats are currently occurring and, therefore, are imminent. Thus, we
continue to assign an LPN of 3 to this subspecies.
Mazama pocket gopher (Thomomys mazama ssp. couchi, douglasii,
glacialis, louiei, melanops, pugetensis, tacomensis, tumuli, yelmensis)
- The following summary is based on information contained in our files.
No new information was provided in the petition received December 11,
2002. One subspecies, T. m. melanops is found on alpine meadows in
Olympic National Park. Another subspecies, T. m. douglasii is found in
extreme southwest Washington. The other seven subspecies of this pocket
gopher are associated with glacial outwash prairies in western
Washington. Of these seven subspecies, five are likely still extant
(couchi, glacialis, pugetensis, tumuli, and yelmensis) and two (T. m.
louiei, and tacomensis) are likely extinct. Few glacial outwash
prairies remain in Washington today. Historically, such prairies were
patchily distributed, but the area they occupied totaled approximately
170,000 acres. Now, residential and commercial development, fire regime
alteration, and ingrowth of woody vegetation have further reduced their
numbers. In addition, development in or adjacent to these prairies has
likely increased predation on Mazama pocket gophers by dogs and cats.
The magnitude of threat is high because the survival of the
subspecies is significantly affected by the patchy and isolated
distributions of its populations in habitats highly desirable for
development and subject to a wide variety of human activities that
permanently alter the habitat. Only the Olympic pocket gopher is not
threatened with development. The threat of invasive plant species to
the quality of a highly specific habitat requirement is high and
constant. There are few known populations of each subspecies. A limited
dispersal capability, and the loss and degradation of additional
patches of appropriate habitat will further isolate populations and
increase their vulnerability to extinction. Loss of any of the
subspecies
[[Page 75192]]
will reduce the genetic diversity and the likelihood of continued
existence of the Thomomys mazama subspecies complex in Washington.
The threats are ongoing and, therefore, imminent. Gravel pits
threaten persistence of one of the remaining subspecies (Roy Prairie
(T. m. glacialis)), and the largest populations of two other subspecies
(Shelton (T. m. couchi) and Olympia (T. m. pugetensis)) are located on
airports with planned development. Yelm pocket gophers are also
threatened by proposed development on Fort Lewis, and Tenino pocket
gophers (T. m. tumuli) are threatened by ongoing development in
general. Only the Olympic pocket gopher (T. m. melanops) is relatively
safe from threats from development due to its more remote location
within the Olympic National Park, but this subspecies is still
currently affected by invasive plants. Thus, we assign an LPN of 3 to
these subspecies.
Palm Springs round-tailed ground squirrel (Spermophilus
tereticaudus chlorus) -The following summary is based on information
contained in our files. No new information was provided in the petition
we received on May 11, 2004. The Palm Springs round-tailed ground
squirrel is one of four recognized subspecies of round-tailed ground
squirrels. The range of this squirrel is limited to the Coachella
Valley region of Riverside County, California. Dunes and hummocks
associated with Prosopis glandulosa var. torreyana (honey mesquite) are
the primary habitat for the Palm Springs round-tailed ground squirrel
and to a lesser extent those dunes and hummocks associated with Larrea
tridentata (creosote), or other vegetation. Honey mesquite provides a
valuable food source for the squirrel and also provides cover and
shelter by trapping aeolian sand that form dunes occupied by the Palm
Springs round-tailed ground squirrel. Rapid growth of desert cities
such as Palm Springs and Palm Desert in the Coachella Valley has raised
concerns about the conservation of the narrowly distributed Palm
Springs round-tailed ground squirrel. Urban development and drops in
the groundwater table have eliminated 90 percent of the honey mesquite
in the Coachella Valley. Furthermore, urban development has fragmented
habitat occupied by this squirrel thereby isolating populations. The
high rate of urban development and associated lowering of the
groundwater table that was likely historically responsible for the high
losses of honey mesquite sand dune/hummocks habitat continues today. We
continue to assign the Palm Springs ground squirrel subspecies an LPN
of 3 because the threats are ongoing and are of a high magnitude as
they affect a large portion of its' range and significantly affect this
subspecies survival.
Southern Idaho ground squirrel (Spermophilus brunneus endemicus) -
The following summary is based on information contained in our files.
No new information was provided in the petition we received on May 11,
2004. The southern Idaho ground squirrel is endemic to four counties in
southwest Idaho; its total known range is approximately 425,630
hectares (1,051,752 acres). Threats to southern Idaho ground squirrels
include: habitat degradation and fragmentation; direct killing from
shooting, trapping, or poisoning; predation; competition with Columbian
ground squirrels; and inadequacy of existing regulatory mechanisms.
Habitat degradation and fragmentation appear to be the primary threats
to the species. Nonnative annuals now dominate much of this species'
range, have changed the species composition of vegetation used as
forage for the southern Idaho ground squirrel, and have altered the
fire regime by accelerating the frequency of wildfire. Habitat
deterioration, destruction, and fragmentation contribute to the current
patchy distribution of southern Idaho ground squirrels. Based on recent
genetic work, southern Idaho ground squirrels are subject to more
genetic drift and inbreeding than expected.
Two Candidate Conservation Agreements with Assurances (CCAAs) have
been completed for this species in recent years. Both CCAAs include
conservation measures that provide additional protection to southern
Idaho ground squirrels from recreational shooting and other direct
killing on enrolled lands, and also allow the State of Idaho, the
Service and BLM to investigate ways of restoring currently degraded
habitat. At this time, the acreage enrolled through these two CCAAs is
approximately 38,756 hectares (95,767 acres), or 9 percent of the known
range. While the ongoing conservation efforts have helped to reduce the
magnitude of threats to moderate, habitat degradation remains the
primary threat to the species throughout most of its range. This threat
is imminent due to the ongoing and increasing prevalence and dominance
of nonnative vegetation, and the current patchy distribution of the
species. Thus, we assign an LPN of 9 to this subspecies.
Washington ground squirrel (Spermophilus washingtoni) - The
following summary is based on information contained in our files and in
the petition we received on March 2, 2000. The Washington ground
squirrel is endemic to the Deschutes-Columbia Plateau sagebrush-steppe
and grassland communities in eastern Oregon and south-central
Washington. Although widely abundant historically, recent surveys
suggest that its current range has contracted toward the center of its
historic range. Approximately two-thirds of the Washington ground
squirrel's total historic range has been converted to agricultural and
residential uses. The most contiguous, least-disturbed expanse of
suitable habitat within the species' range occurs on a site owned by
Boeing, Inc. and on the Naval Weapons Systems Training Facility near
Boardman, Oregon. In Washington, the largest expanse of known suitable
habitat occurs on State and Federal lands.
Agricultural, residential, and wind power, among other forms of
development, continue to eliminate Washington ground squirrel habitat
in portions of its range. Throughout much of its range, Washington
ground squirrels are threatened by the establishment and spread of
invasive plant species, particularly cheatgrass, which alters available
cover, food quantity and quality, and increases fire intervals.
Additional threats include habitat fragmentation, recreational
shooting, genetic isolation and drift, and predation. Potential threats
include disease, drought, and possible competition with related species
in disturbed habitat at the periphery of their range. In Oregon, some
threats are being addressed as a result of the State listing of this
species, and by implementation of the Threemile Canyon Farms Multi-
Species Candidate Conservation Agreement with Assurances (CCAA). In
Washington, there are currently no formal agreements with private
landowners or with State or Federal agencies to protect the Washington
ground squirrel. Additionally, no State or Federal management plans
have been developed that specifically address the needs of the species
or its habitat. Since current and potential threats are widespread and,
in some cases, severe, we conclude the magnitude of threats remains
high. However, because the CCAA addressed the imminent loss of a large
portion of habitat to agriculture, and because there are no other
known, large-scale efforts to convert suitable habitat to agriculture,
the threats, overall, are not imminent. We, therefore, have kept the
LPN at 5 for this species.
[[Page 75193]]
Birds
Spotless crake, American Samoa DPS (Porzana tabuensis) - The
following summary is based on information contained in our files. No
new information was provided in the petition we received on May 11,
2004. P. tabuensis is a small, dark, cryptic rail found in wetlands and
rank scrub or forest in the Philippines, Australia, Fiji, Tonga,
Society Islands, Marquesas, Independent Samoa, and American Samoa (Ofu,
Tau). The genus Porzana is widespread in the Pacific, where it is
represented by numerous island-endemic and flightless species (many of
which are extinct as a result of anthropogenic disturbances) as well as
several more cosmopolitan species, including P. tabuensis. No
subspecies of P. tabuensis are recognized. The American Samoa
population is the only population of spotless crakes under U.S.
jurisdiction. The available information indicates that distinct
populations of the spotless crake, a species not noted for long-
distance dispersal, are definable. The population of spotless crakes in
American Samoa is discrete in relation to the remainder of the species
as a whole, which is distributed in widely separated locations.
Although the spotless crake (and other rails) have dispersed widely in
the Pacific, island rails have tended to reduce or lose their power of
flight over evolutionary time and so become isolated (and vulnerable to
terrestrial predators such as rats). The population of this species in
American Samoa is therefore distinct based on geographic and
distributional isolation from spotless crake populations on other
islands in the oceanic Pacific, the Philippines, and Australia. The
American Samoa population of the spotless crake links the Central and
Eastern Pacific portions of the species' range. The loss of this
population could cause an increase of roughly 500 miles (805
kilometers) in the disjunction between the central and eastern
Polynesian portions of the spotless crake's range, and could result in
the isolation of the Marquesas and Society Islands populations by
further limiting the potential for even rare genetic exchange. Based on
the discreteness and significance of the American Samoa population of
the spotless crake, we consider this population to be a distinct
vertebrate population segment.
Threats to this population have not changed over the past year. The
population in American Samoa is threatened by small population size,
limited distribution, predation by nonnative mammals, continued
development of wetland habitat, and natural catastrophes such as
hurricanes. The co-occurrence of a known predator of ground-nesting
birds, the Norway rat (Rattus norvegicus), along with the extremely
restricted observed distribution and low numbers, indicate that the
magnitude of the threats to the American Samoa DPS of the spotless
crake continues to be high, because the threats significantly affect
the species survival. The threats are ongoing, and therefore imminent.
Based on this assessment of existing information about the imminence
and high magnitude of these threats, we assigned the spotless crake an
LPN of 3.
Yellow-billed cuckoo, western U.S. DPS (Coccyzus americanus) - The
following summary is based on information contained in our files and
the petition we received on February 9, 1998. See also our 12-month
petition finding published on July 25, 2001 (66 FR 38611). We consider
the yellow-billed cuckoos that occur in the western United States as a
DPS. The area for this DPS is west of the crest of the Rocky Mountains.
The yellow-billed cuckoo (Coccyzus americanus) is a medium-sized bird
that breeds in large blocks of riparian habitats (particularly
woodlands with cottonwoods (Populus fremontii) and willows (Salix sp.).
Dense understory foliage appears to be an important factor in nest site
selection, while cottonwood trees are an important foraging habitat in
areas where the species has been studied in California.
The threats currently facing the yellow-billed cuckoo include
habitat destruction and modification and pesticide application.
Principal causes of riparian habitat losses are conversion to
agricultural and other uses, dams and river flow management, stream
channelization and stabilization, and livestock grazing. Available
breeding habitats for cuckoos have also been substantially reduced in
area and quality by groundwater pumping and the replacement of native
riparian habitats by invasive nonnative plants, particularly tamarisk.
Overuse by livestock has been a major factor in the degradation and
modification of riparian habitats in the western United States. The
effects include changes in plant community structure and species
composition and in relative abundance of species and plant density.
These changes are often linked to more widespread changes in watershed
hydrology. Livestock grazing in riparian habitats typically results in
reduction of plant species diversity and density, especially of
palatable broadleaf plants like willows and cottonwood saplings, and is
one of the most common causes of riparian degradation. In addition to
destruction and degradation of riparian habitats, pesticides may affect
cuckoo populations. In areas where riparian habitat borders
agricultural lands, e.g., in California's central valley, pesticide use
may indirectly affect cuckoos by reducing prey numbers, or by poisoning
nestlings if sprayed directly in areas where the birds are nesting. We
retained an LPN of 3 for this population of yellow-billed cuckoo; the
threats are ongoing and therefore imminent, and they are of a high
magnitude, because ongoing habitat degradation could affect the
survival of the DPS rangewide.
Friendly ground-dove, American Samoa DPS (Gallicolumba stairi
stairi) - The following summary is based on information contained in
our files. No new information was provided in the petition we received
on May 11, 2004. The genus Gallicolumba is distributed throughout the
Pacific and Southeast Asia. The genus is represented in the oceanic
Pacific by six species: Three are endemic to Micronesian islands or
archipelagos, two are endemic to island groups in French Polynesia, and
G. stairi is endemic to Samoa, Tonga, and Fiji. Some authors recognize
two subspecies of the friendly ground-dove, one, slightly smaller, in
the Samoan archipelago (G. s. stairi), and one in Tonga and Fiji (G. s.
vitiensis), but because morphological differences between the two are
minimal, we are not recognizing separate subspecies at this time.
In American Samoa, the friendly ground-dove has been found on the
islands of Ofu and Olosega (Manua Group). Threats to this subspecies
have not changed over the past year. Predation by nonnative species and
natural catastrophes such as hurricanes are the primary threats to the
subspecies. Of these, predation by nonnative species is thought to be
occurring now and likely has been occurring for several decades. This
predation may be an important impediment to increasing the population.
Predation by introduced species has played a significant role in
reducing, limiting, and extirpating populations of island birds,
especially ground-nesters, in the Pacific and other locations
worldwide. Nonnative predators known or thought to occur in the range
of the friendly ground-dove in American Samoa are feral cats (Felis
catus), Polynesian rats (Rattus exulans), black rats (R. rattus), and
Norway rats (R. norvegicus).
In January 2004 and February of 2005, hurricanes virtually
destroyed the habitat of G. stairi in an area on Olosega Island where
the species had been most
[[Page 75194]]
frequently recorded. Although this species has coexisted with severe
storms for millennia, this example illustrates the potential for
natural disturbance to exacerbate the effect of anthropogenic
disturbance on small populations. Consistent monitoring using a variety
of methods over the last 5 years yielded few observations of this taxon
in American Samoa. The total population size is poorly known, but is
unlikely to number more than a few hundred pairs. The past five years
or so of surveys have revealed no change in the relative abundance of
this taxon in American Samoa. The distribution of the friendly ground-
dove is limited to steep, forested slopes with an open understory and a
substrate of fine scree or exposed earth; this habitat is not common in
American Samoa. The threats are ongoing and, therefore imminent and the
magnitude is moderate because the relative abundance has remained the
same for several years. Thus, we assign this subspecies an LPN of 9.
Streaked horned lark (Eremophila alpestris strigata) - The
following summary is based on information contained in our files. No
new information was provided in the petition we received on December
11, 2002. The streaked horned lark occurs in Washington and Oregon, and
is thought to be extirpated in British Columbia, Canada. The streaked
horned lark nests on the ground in sparsely vegetated sites in short-
grass dominated habitats, such as native prairies, coastal dunes,
fallow agricultural fields, lightly- to moderately-grazed pastures,
seasonal mudflats, airports, and dredged-material formed islands in the
Columbia River. In Washington, surveys show that there are
approximately 330 remaining breeding birds. In Oregon, the breeding
population is estimated to be approximately 400 birds.
The streaked horned lark's breeding habitat continues to be
threatened by loss and degradation due to conversion of native
grasslands to other uses (such as agriculture, homes, recreational
areas, and industry), encroachment of woody vegetation, and invasion of
nonnative plant species (e.g., Scot's broom, sod-forming grasses, and
beachgrasses). Native prairies have been nearly eliminated throughout
the range of the species. Less than 1 to 3 percent of the native
grassland and savanna are estimated to remain. Those that remain have
been invaded by nonnative sod-forming grasses. Coastal nesting areas
have suffered the same fate. A recent purchase of prairie lands in
Washington has secured habitat that would have been developed, but its
status as suitable lark nesting habitat is unknown.
Wintering habitats are seemingly few, and susceptible to
unpredictable conversion to unsuitable over-wintering habitat. Where
larks inhabit human-created habitats similar in structure to native
prairies (such as airports, military reservations, agricultural fields,
and dredge-formed islands), or where they occur adjacent to human
habitation, they are subjected to a variety of unintentional human
disturbances such as mowing, recreational and military activities,
plowing, flooding, and dredge spoil dumping during the nesting season,
as well as intentional disturbances such as at the McChord AFB where
falcons and dogs are used to haze the birds in order to avoid aircraft
collisions. In some areas, landowners have taken steps to improve
streaked horned lark nesting habitat.
The magnitude of the threats is high due to small populations with
low genetic diversity, and patchy and isolated habitats in areas
desirable for development, many of which remain unsecured. The threat
of invasive plant species is high and constant, aside from a few
restoration sites. The numbers of individuals are low and the numbers
of populations are few. Over-wintering birds are concentrated in larger
flocks and subject to unpredictable wintering habitat loss (especially
in the Willamette Valley, Oregon), potentially affecting a large
portion of the population at one time. In Washington, known populations
occur on airports and military bases (6 of 13 sites), coastal beaches
(4 of 13 sites), and Columbia River islands (3 of 13 sites), where
management, training activities, recreation, and dredge spoil dumping
continue to negatively impact streaked horned lark breeding and
wintering. In Oregon, breeding and wintering sites occur on Columbia
River islands, in cultivated grass fields, grazed pastures, fallow
fields, roadside shoulders, Christmas tree farms, and wetland mudflats.
Such areas continue to be subject to negative impacts such as dredge
spoil dumping, development, plowing, mowing, pesticide and herbicide
applications, trampling, vehicle traffic, and recreation. Many of these
Oregon sites are ephemeral in nature, with the quality of habitat
changing from year to year from suitable to unsuitable. Thus the
numbers of sites also changes year to year.
The threats are imminent, due to the continued loss of suitable
lark habitat, risks to the wintering populations, plans for development
on and adjacent to several of its nesting areas, predation, use of
falcons and dogs to haze breeding birds at McChord AFB, planned and/or
continued expansions of the McChord AFB West Ramp and Olympia Airport,
and human disturbance, including annual Air Force military training and
fire-bombing on top of lark nesting habitat. We continue to assign an
LPN of 3 to this subspecies.
Red knot (Calidris canutus rufa) - See above in ``Summary of
Listing Priority Changes in Candidates.'' The above summary is based on
information contained in our files and information provided by
petitioners. Four petitions to emergency list the red knot have been
received: one on August 9, 2004, two others on August 5, 2005, and the
most recent on February 27, 2008.
Kittlitz's murrelet (Brachyramphus brevirostris) - The following
summary is based on information contained in our files and the petition
we received on May 9, 2001. Kittlitz's murrelet is a small diving
seabird whose entire North American population, and most of the world's
population, inhabits Alaskan coastal waters discontinuously from Point
Lay south to northern portions of Southeast Alaska. Kittlitz's
murrelets are associated with tidewater glaciers. The current
population estimate for Kittlitz's murrelets in Alaska is approximately
16,700 birds, a decline of 74 to 84 percent during the past 10 to 20
years. New survey information supports and strengthens the negative
population trend estimates that have been previously reported.
Threats to Kittlitz's murrelets include large-scale processes such
as global climate change and marine climate regime shift. These large-
scale processes may influence Kittlitz's murrelet survival and
reproduction. Glacial retreat, a global phenomenon that affects many of
the glaciers with which Kittlitz's murrelets are associated, is
associated with changing forage fish availability and may result in
increased predation. Other ongoing threats include oil spills, bycatch
in commercial gillnet fisheries, and disturbance by tour boats.
Kittlitz's murrelets are believed to have been seriously affected by
the Exxon Valdez oil spill in Prince William Sound in 1989.
Catastrophic events such as oil spills could have a significant
negative effect on the population of this already diminished species.
Susceptibility to mortality as bycatch in commercial fishing could be a
significant factor in their population decline; Kittlitz's murrelets
are caught in gill nets in numbers disproportionate to their density.
Tour boat visitation to glacial fjords is a growing industry, and this
activity may increasingly disrupt Kittlitz's murrelet feeding behavior;
tour
[[Page 75195]]
boats may provide artificial perch sites for avian predators.
Based on the observed population trajectory and the severity of
present threats (rapid glacial retreat, acute and chronic oil spills,
commercial gillnet fishing, and human disturbance from tour boats), the
threats to this species are high in magnitude and imminent. Therefore,
we assigned an LPN of 2 to this species.
Xantus's murrelet (Synthliboramphus hypoleucus) - The following
summary is based on information contained in our files and the petition
we received on April 16, 2002. The Xantus's murrelet is a small seabird
in the Alcid family that occurs along the west coast of North America
in the United States and Mexico. The species has a limited breeding
distribution, only nesting on the Channel Islands in southern
California and on islands off the west coast of Baja California,
Mexico. Although data on population trends are scarce, the population
is suspected to have declined greatly over the last century, mainly due
to introduced predators such as rats (Rattus sp.) and feral cats (Felis
catus) to nesting islands, with extirpations on three islands in
Mexico. A dramatic decline (up to 70 percent) from 1977 to 1991 was
detected at the largest nesting colony in southern California, possibly
due to high levels of predation on eggs by the endemic deer mouse
(Peromyscus maniculatus elusus). Identified threats include introduced
predators at nesting colonies, oil spills and oil pollution, reduced
prey availability, human disturbance, and impacts related to artificial
light pollution.
Although substantial declines in the Xantus's murrelet population
likely occurred over the last century, some of the largest threats are
being addressed, and, to some degree, ameliorated. Declines and
extirpations at several nesting colonies were thought to have been
caused by nonnative predators, which have been removed from many of the
islands where they once occurred. Most notably, since 1994, Island
Conservation and Ecology Group has systematically removed rats, cats,
and dogs from every murrelet nesting colony in Mexico, with the
exception of cats and dogs on Guadalupe Island. In 2002, rats were
eradicated from Anacapa Island in southern California, which has
resulted in improvements in reproductive success at that island. In
southern California, there are also plans to remove rats from San
Miguel Island, and to restore nesting habitat on Santa Barbara Island
through the Montrose Settlements Restoration Project, which may benefit
the Xantus's murrelet population at those islands.
Artificial lighting from squid fishing and other vessels, or lights
on islands, remains a potential threat to the species. Bright lights
make Xantus's murrelets more susceptible to predation, and they can
also become disoriented and exhausted from continual attraction to
bright lights. Chicks can become disoriented and separated from their
parents at sea, which could result in death of the dependent chicks.
High-wattage lights on commercial market squid (Loligo opalescens)
fishing vessels used at night to attract squid to the surface of the
water in the Channel Islands was the suspected cause of unusually high
predation on Xantus's murrelets by western gulls and barn owls at Santa
Barbara Island in 1999. To address this threat, in 2000, the California
Fish and Game Commission required light shields and a limit of 30,000
watts per boat; it is unknown if this is sufficient to reduce impacts.
Squid fishing has not occurred at a particularly noticeable level near
any of the colonies in the Channel Islands since 1999; however, this
remains a potential future threat.
A proposal to build a liquid natural gas (LNG) facility 600 meters
(1,969 feet) off the Coronados Islands in Baja California, Mexico, was
considered a potential major threat to the species. This island
contains one of the largest nesting populations of Xantus's murrelets
in the world. Potential impacts of this facility to the nesting colony
included bright lights at night from the facility and visiting tanker
vessels, noise from the facility or from helicopters visiting the
facility, and the threat of oil spills associated with visiting tanker
vessels. However, Chevron announced in March 2007 that they have
abandoned plans to develop this facility and withdrew their permits.
There are three proposed LNG facilities in the Channel Islands;
however, these are early in the complex and long-term planning
processes, and it is possible that none of these facilities will be
built. In addition, none of them are directly adjacent to nesting
colonies, where their impacts would be expected to be more significant.
The LNG facility off the Coronados Islands was considered to be an
imminent threat of high magnitude, which resulted in a previous LPN of
2. The remaining threats to the species are of high magnitude since
they have the potential to result in mortality for a large portion of
the species' range. However, the threats are nonimminent since they are
not currently occurring at most of the murrelet nesting sites.
Therefore, we retained an LPN of 5 for this species.
Lesser prairie-chicken (Tympanuchus pallidicinctus) - See above in
``Summary of Listing Priority Changes in Candidates.'' The above
summary is based on information contained in our files and the petition
received on October 5, 1995. Additional information can be found in the
12-month finding published on June 7, 1998 (63 FR 31400).
Greater sage-grouse, Columbia Basin DPS (Centrocercus urophasianus)
- For the reasons discussed below, we have not updated our finding with
regard to the Columbia Basin DPS of the western subspecies of the
greater sage-grouse (C. u. phaios) in this notice. The following
summary is based on information in our files and a petition, dated May
14, 1999, requesting the listing of the Washington population of
western sage grouse. On May 7, 2001, we concluded that listing the
Columbia Basin DPS of western sage grouse was warranted but precluded
by higher priority listing actions (66 FR 22984); this DPS was
historically found in northern Oregon and central Washington. The
Service subsequently received two petitions requesting the listing of
the entire ranges of what the petitions called the western and eastern
subspecies of greater sage-grouse, dated January 24 and July 3, 2002,
respectively. The petition involving the western sage-grouse requested
listing the subspecies in northern California through Oregon and
Washington (including the Columbia Basin DPS, for which we had already
concluded listing was warranted but precluded), as well as any western
sage-grouse still occurring in parts of Idaho.
In evaluating the two petitions, we communicated with recognized
sage-grouse experts, and discovered there was disagreement as to the
taxonomic validity of these subspecies of the greater sage-grouse. Due
to this disagreement in the scientific community, the we evaluated the
available information and concluded that the eastern and western
subspecies designations for greater sage-grouse are inappropriate given
current taxonomic standards, which also meant they were not listable
entities under the Act. We also concluded that the eastern and western
populations did not constitute DPSs of the greater sage-grouse.
Therefore, we published findings that the petitions did not present
substantial information indicating that what the petitions had
identified as the western or eastern subspecies may be warranted for
listing under the Act (68 FR 6500 and 69 FR 933, respectively). The
Institute for Wildlife Protection filed a
[[Page 75196]]
court complaint, dated June 6, 2003, challenging the merits of our 90-
day finding on the petition to list the western subspecies. On August
10, 2004, a U.S. District Court judge ruled in favor of the Service and
dismissed the plaintiff's case. An appeal, dated November 24, 2004, was
filed by the Institute for Wildlife Protection. On March 3, 2006, the
9th Circuit Court of Appeals remanded the 90-day finding to the Service
on the grounds that we did not provide an adequate basis for concluding
that the petition failed to present substantial information indicating
the western sage-grouse may be a valid subspecies. The Court did,
however, uphold our conclusion that the petitioned entity (western
sage-grouse) does not constitute a DPS of the greater sage-grouse. On
April 29, 2008, we published a substantial 90-day petition finding
which concluded that the petition presented substantial information
indicating that listing the western subspecies of the greater sage-
grouse may be warranted, announced that we were initiating a status
review, and requested relevant information from the public (73 FR
23170). We will publish an updated finding addressing the Columbia
Basin DPS in the Federal Register after completing our status review
and 12-month petition finding regarding the petition to list the
western subspecies of the greater sage-grouse.
Band-rumped storm-petrel, Hawaii DPS (Oceanodroma castro) - The
following summary is based on information contained in our files and
the petition we received on May 8, 1989. No new information was
provided in the second petition received on May 11, 2004. The band-
rumped storm-petrel is a small seabird that is found in several areas
of the subtropical Pacific and Atlantic Oceans. In the Pacific, there
are three widely separated breeding populations - one in Japan, one in
Hawaii, and one in the Galapagos. Populations in Japan and the
Galapagos are comparatively large and number in the thousands, while
the Hawaiian birds represent a small, remnant population of possibly
only a few hundred pairs. Band-rumped storm-petrels are most commonly
found in close proximity to breeding islands. The three populations in
the Pacific are separated by long distances across the ocean where
birds are not found. Extensive at-sea surveys of the Pacific have
revealed a broad gap in distribution of the band-rumped storm-petrel to
the east and west of the Hawaiian Islands, indicating the distribution
of birds in the central Pacific around Hawaii is disjunct from other
nesting areas. The available information indicates that distinct
populations of band-rumped storm-petrels are definable and that the
Hawaiian population is distinct based on geographic and distributional
isolation from other band-rumped storm-petrel populations in Japan, the
Galapagos, and the Atlantic Ocean. A population also can be considered
discrete if it is delimited by international boundaries across which
exist differences in management control of the species. The Hawaiian
population of the band-rumped storm-petrel is the only populationwithin
U.S. borders or under U.S. jurisdiction. Loss of the Hawaiian
population would cause a significant gap in the distribution of the
band-rumped storm-petrel in the Pacific, and could result in the
complete isolation of the Galapagos and Japan populations without even
occasional genetic exchanges. Therefore, the population is both
discrete and significant, and is therefore a DPS.
The band-rumped storm-petrel probably was common on all of the main
Hawaiian Islands when Polynesians arrived about 1,500 years ago, based
on storm-petrel bones found in middens on the island of Hawaii and in
excavation sites on Oahu and Molokai. Nesting colonies of this species
in the Hawaiian Islands currently are restricted to remote cliffs on
Kauai and Lehua Island and high-elevation lava fields on Hawaii.
Vocalizations of the species were heard in Haleakala Crater on Maui as
recently as 2006; however, no nesting sites have been located on the
island to date. The significant reduction in numbers and range of the
band-rumped storm-petrel is due primarily to predation by nonnative
predators introduced by humans, including the domestic cat (Felis
catus), small Indian mongoose (Herpestes auropunctatus), common barn
owl (Tyto alba), black rat (R. rattus), Polynesian rat (Rattus
exulans), and Norway rat (R. norvegicus), which occur throughout the
main Hawaiian Islands, with the exception of the mongoose, which is not
established on Kauai. Attraction of fledglings to artificial lights,
which disrupts their night-time navigation, resulting in collisions
with building and other objects, and collisions with artificial
structures such as communication towers and utility lines are also
threats. Erosion of nest sites caused by the actions of nonnative
ungulates is a potential threat in some locations. Efforts are underway
in some areas to reduce light pollution and mitigate the threat of
collisions, but there are no large-scale efforts to control nonnative
predators in the Hawaiian Islands. The threats are imminent because
they are ongoing, and they are of a high magnitude because they can
significantly affect the survival of this DPS. Therefore, we assign
this distinct population segment an LPN of 3.
Elfin-woods warbler (Dendroica angelae) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. The elfin woods
warbler, is a small entirely black and white warbler, and was at first
thought to occur only in the high elevation dwarf or elfin forests of
Puerto Rico, but it has since been found at lower elevations including
shade coffee plantations and secondary forests. The elfin woods warbler
has been documented from four locations in Puerto Rico: Luquillo
Mountains, Sierra de Cayey, and the Commonwealth forests of Maricao and
Toro Negro. However, it has not been recorded again in Toro Negro or
Cayey, since Hurricane Hugo in 1989. In 2003 and 2004, surveys for the
elfin-woods warbler in the Carite Commonwealth Forest, Toro Negro
Forest, Guilarte Forest, Bosque del Pueblo, Maricao Forest and the
Caribbean National Forest, only detected the species in the latter two
areas. In the Maricao Commonwealth Forest, 778 elfin woods warblers
were recorded, and in the Caribbean National Forest, 196 elfin-woods
warblers were recorded.
Habitat destruction from expansion of public facilities within the
forests, potential construction of additional telecommunication towers
and their maintenance, disruption of breeding activities from
pedestrians and high human use areas, switching from shade to sun
coffee plantations, timber management practices, potential predators,
and catastrophic natural events such as hurricanes and forest fires,
threaten this species. Although these threats are not imminent because
most of the range of the elfins wood warbler is within protected lands,
the magnitude of threat to this species is high, because the restricted
distribution and low population numbers cause the threats to have a
significant impact on the species' survival. Therefore, we assign a
listing priority number of 5 to this species.
Reptiles
Sand dune lizard (Sceloporus arenicolus) - We have not updated our
assessment for this species, as we are currently developing a proposed
listing rule.
[[Page 75197]]
Eastern massasauga rattlesnake (Sistrurus catenatus catenatus) -
The following summary is based on information contained in our files.
No new information was provided in the petition received on May 11,
2004. The eastern massasauga is one of three recognized subspecies of
massasauga, a rattlesnake. It occupies shallow wetlands and adjacent
upland habitat in portions of Illinois, Indiana, Iowa, Michigan,
Minnesota, Missouri, New York, Ohio, Pennsylvania, Wisconsin, and
Ontario.
Although the current range of the eastern massasauga resembles the
subspecies' historical range, the geographic distribution has been
restricted by the loss of the subspecies from much of the area within
the boundaries of that range. Approximately 40 percent of the counties
that were historically occupied by the eastern massasauga no longer
support the subspecies. This subspecies is currently considered
imperiled in every State and province which it occupies. Each State and
Canadian province across the range of the eastern massasauga has lost
more than 30 percent, and for the majority more than 50 percent, of
their historical populations. Furthermore, fewer than 35 percent of the
remaining populations are considered secure. Approximately 59 percent
of the remaining eastern massasauga populations occur wholly or in part
on public land, and Statewide and/or site-specific Candidate
Conservation Agreements with Assurances (CCAAs) are currently being
developed for many of these areas in Iowa, Illinois, Michigan, and
Wisconsin. In 2004, a Candidate Conservation Agreement (CCA) with the
Lake County Forest Preserve District in Illinois was completed. In
2005, a CCA with the Forest Preserve District of Cook County in
Illinois was completed. In 2006, a CCAA with the Ohio Department of
Natural Resources Division of Natural Areas and Preserves was completed
for Rome State Nature Preserve in Ashtabula County. Populations
expected to be under CCAs and CCAAs have a high likelihood of
persisting and remaining viable. Other populations are likely to suffer
additional losses in abundance and genetic diversity and some will
likely be extirpated unless threats are removed in the near future. The
primary threats to the eastern massasauga are habitat modification,
habitat succession, incompatible land management practices, illegal
collection for the pet trade, and human persecution. Because of the
ongoing effort to protect the subspecies through CCAAs, the threats are
moderate overall. Although the CCAAs have decreased the immediacy of
some threats in some areas, the majority of the threats are ongoing or
are in areas not covered by a CCAA. As a result, overall these threats
remain an imminent threat to many remaining populations, particularly
those inhabiting private lands. We have kept the LPN at 9 for this
subspecies.
Black pine snake (Pituophis melanoleucus lodingi) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
There are historical records for the black pine snake from one parish
in Louisiana, 14 counties in Mississippi, and 3 counties in Alabama
west of the Mobile River Delta. Black pine snake surveys and trapping
indicate that this species has been extirpated from Louisiana and from
four counties in Mississippi. Moreover, the distribution of remaining
populations has become highly restricted due to the destruction and
fragmentation of the remaining longleaf pine habitat within the range
of the subspecies. Most of the known Mississippi populations are
concentrated on the DeSoto National Forest. Populations occurring on
properties managed by State and other governmental agencies as gopher
tortoise mitigation banks or wildlife sanctuaries represent the best
opportunities for long-term survival of the subspecies in Alabama.
Other factors affecting the black pine snake include vehicular
mortality and low reproductive rates, which magnify the threats from
destruction and fragmentation of longleaf pine habitat and increase the
likelihood of local extinctions. Due to the imminent threats of high
magnitude caused by the past destruction of most of the longleaf pine
habitat of the black pine snake, and the continuing persistent
degradation of what remains, we assigned an LPN of 3 to this
subspecies.
Louisiana pine snake (Pituophis ruthveni) -The following summary is
based on information contained in our files and the petition we
received on July 19, 2000. The Louisiana pine snake historically
occurred in the fire-maintained longleaf pine ecosystem within west-
central Louisiana and extreme east-central Texas. Most of the
historical longleaf pine habitat of the Louisiana pine snake has been
destroyed or degraded due to logging, fire suppression, roadways,
short-rotation silviculture, and grazing. In the absence of recurrent
fire, suitable habitat conditions for the Louisiana pine snake and its
primary prey, the Baird's pocket gopher (Geomys breviceps), are lost
due to vegetative succession. The loss and fragmentation of the
longleaf pine ecosystem has resulted in extant Louisiana pine snake
populations that are isolated and small. Trapping and occurrence data
indicate the Louisiana pine snake is currently restricted to seven
disjunct populations; five of the populations occur on Federal lands
and two occur mainly on private industrial timberlands. Current
potentially occupied habitat in Louisiana and Texas is estimated to be
approximately 163,000 acres, with 53 percent occurring on public lands
and 47 percent in private ownership.
All remnant Louisiana pine snake populations have been affected by
habitat loss and all require active habitat management. A Candidate
Conservation Agreement (CCA) was completed in 2003 to maintain and
enhance potentially occupied habitat on public lands, and to protect
known Louisiana pine snake populations. On Federal lands, signatories
of the Louisiana pine snake CCA currently conduct habitat management
(i.e., prescribed burning and thinning) that is beneficial to the
Louisiana pine snake. This proactive habitat management has likely
slowed or reversed the rate of Louisiana pine snake habitat degradation
on many portions of Federal lands. The largest extant Louisiana pine
snake population exists on private industrial timberlands. Although two
conservation areas are managed to benefit Louisiana pine snakes on this
property, the majority of the intervening occupied habitat is
threatened by land management activities (habitat conversion to short-
rotation pine plantations) that decrease habitat quality.
Three of the remnant Louisiana pine snake populations may be
vulnerable to decreased demographic viability or other factors
associated with low population sizes and demographic isolation.
Although these remnant Louisiana pine snake populations are
intrinsically vulnerable and thus threatened by these factors, it is
not known if they are presently actually facing these threats. Because
all extant populations are currently isolated and fragmented by habitat
loss in the matrix between populations, there is little potential for
dispersal among remnant populations or for the natural re-colonization
of vacant habitat patches. Thus, the loss of any remnant population is
likely to be permanent. Other factors affecting the Louisiana pine
snake throughout its range include low fecundity, which magnifies other
threats and increases the likelihood of local extinctions, and
vehicular
[[Page 75198]]
mortality, which may significantly affect Louisiana pine snake
populations.
While the extent of Louisiana pine snake habitat loss has been
great in the past and much of the remaining habitat has been degraded,
habitat loss does not represent an imminent threat, primarily because
the rate of habitat loss appears to be declining on public lands.
However, all populations require active habitat management, and the
lack of adequate habitat remains a threat for several populations. The
potential threats to a large percentage of extant Louisiana pine snake
populations, coupled with the likely permanence of these effects and
the species' low fecundity and low population sizes (based on capture
rates and occurrence data), lead us to conclude that the threats have
significant effect on the survival of the species and therefore remain
high in magnitude. Thus, based on nonimminent, high-magnitude threats,
we assign a listing priority number of 5 to this species.
Sonoyta mud turtle (Kinosternon sonoriense longifemorale) - The
following summary is based on information contained in our files. No
new information was provided in the petition we received on May 11,
2004. The Sonoyta mud turtle occurs in a spring and pond at
Quitobaquito Springs on Organ Pipe Cactus National Monument in Arizona,
and in the Rio Sonoyta and Quitovac Spring of Sonora, Mexico. Loss and
degradation of stream habitat from water diversion and groundwater
pumping, along with its very limited distribution, is the primary
threat to the Sonoyta mud turtle. Sonoyta mud turtles are highly
aquatic and depend on permanent water for survival. The area of
southwest Arizona and northern Sonora where the Sonoyta mud turtle
occurs is one of the driest regions of the southwest. Due to continuing
drought, irrigated agriculture, and development in the region, surface
water in the Rio Sonoyta can be expected to dwindle further and
therefore have a significant impact on the survival of this subspecies
which may also be vulnerable to aerial spraying of pesticides on nearby
agricultural fields. We retained an LPN of 3 for this subspecies
because threats are of a high magnitude and continue to date, and
therefore, are imminent.
Amphibians
Columbia spotted frog, Great Basin DPS (Rana luteiventris) - The
following summary is based on information contained in our files and
the petition we received on May 1, 1989. Currently, Columbia spotted
frogs appear to be widely distributed throughout southwestern Idaho,
eastern Oregon, northeastern and central Nevada but local populations
within this general area appear to be small and isolated from each
other. Recent work by researchers in Idaho and Nevada has documented
the loss of historically known sites, reduced numbers of individuals
within local populations, and declines in the reproduction of those
individuals. Small, highly fragmented populations, characteristic of
the majority of existing populations of Columbia spotted frogs in the
Great Basin, are highly susceptible to extinction processes. The
populations within the Columbia Basin are discrete and significant, and
thus are a DPS.
Water development, improper grazing, mining activities and
nonnative species have and continue to contribute to the degradation
and fragmentation of Columbia spotted frog habitat. Emerging fungal
diseases such as chytridiomycosis and the spread of parasites are
contributing factors to Columbia spotted frog population declines
throughout portions of its range. A 10-year Conservation Agreement/
Strategy was signed in September 2003 for both the Northeast and the
Toiyabe subpopulations in Nevada. The goals of the Conservation
Agreements are to reduce threats to Columbia spotted frogs and their
habitat to the extent necessary to prevent populations from becoming
extirpated throughout all or a portion of their historic range and to
maintain, enhance, and restore a sufficient number of populations of
Columbia spotted frogs and their habitat to ensure their continued
existence throughout their historic range. Additionally, a Candidate
Conservation Agreement with Assurances was completed in 2006 for the
Owyhee subpopulation at Sam Noble Springs, Idaho. While some threats
(habitat modification and fragmentation, nonnative species, inadequate
regulatory mechanisms, and climate change) to the species and its
habitat occur rangewide but at various intensities, other threats
(disease and mining) only impact local populations; overall, the
magnitude of the threats is moderate. Based on ongoing, and therefore,
imminent threats of moderate magnitude, we assigned a listing priority
number of 9 to this Distinct Population Segment of the Columbia spotted
frog.
Mountain yellow-legged frog, Sierra Nevada DPS (Rana muscosa) - The
following summary is based on information contained in our files and
the petition received on February 8, 2000. Also see our 12-month
petition finding published on January 16, 2003 (68 FR 2283) and our
amended 12-month petition finding published on June 25, 2007 (72 FR
34657). The mountain yellow-legged frog inhabits the high elevation
lakes, ponds, and streams in the Sierra Nevada Mountains of California,
from near 4,500 feet (ft) (1,370 meters (m)) to 12,000 ft (3,650 m).
The distribution of the mountain yellow-legged frog is from Butte and
Plumas Counties in the north to Tulare and Inyo Counties in the south.
The population in the Sierra Nevada is discrete and significant and is
therefore a DPS. A separate population in southern California is
already listed as endangered (67 FR 44382).
Predation by introduced trout is the best-documented cause of the
decline of the Sierra Nevada mountain yellow-legged frog, because it
has been repeatedly observed that nonnative fishes and mountain yellow-
legged frogs rarely co-exist. Mountain yellow-legged frogs and trout
(native and nonnative) do co-occur at some sites, but these co-
occurrences probably are mountain yellow-legged frog populations with
negative population growth rates in the absence of immigration. To help
reverse the decline of the mountain yellow-legged frog, the Sequoia and
Kings Canyon National Parks have been removing introduced trout since
2001. Over 18,000 introduced trout have been removed from 11 lakes
since the project started in 2001. The lakes are completely- to mostly
fish-free and substantial mountain yellow-legged frog population
increases have resulted. The California Department of Fish and Game
(CDFG) has also removed or is in the process of removing nonnative
trout from a total of between 10 and 20 water bodies in the Inyo,
Humboldt-Toiyabe, Sierra, and El Dorado National Forests. In the El
Dorado National Forest golden trout were removed from Leland Lakes, and
attempts have been made to remove trout from two sites near Gertrude
Lake and a tributary of Cole Creek; no data showing increase in
mountain yellow-legged frogs at these sites was available.
In California, chytridiomycosis, more commonly known as chytrid
fungus, has been detected in many amphibian species, including the
mountain yellow-legged frog within the Sierra Nevada. Recent research
has shown that this pathogenic fungus is widely distributed throughout
the Sierra Nevada, and that infected mountain yellow-legged frogs die
soon after metamorphosis. Several infected and uninfected populations
were monitored in Sequoia and Kings Canyon National Parks over multiple
years, documenting dramatic declines and extirpations in infected but
not in uninfected populations. In the summer
[[Page 75199]]
of 2005, 39 of 43 populations assayed in Yosemite National Park were
positive for chytrid fungus.
The current distribution of the Sierra Nevada mountain yellow-
legged frog is restricted primarily to publicly managed lands at high
elevations, including streams, lakes, ponds, and meadow wetlands
located on national forests, including wilderness and non-wilderness on
the forests, and national parks. In several areas where detailed
studies of the effects of chytrid fungus on the mountain yellow-legged
frog are ongoing, substantial declines have been observed over the past
several years. For example, in 2007 surveys in Yosemite National Park,
mountain yellow-legged frogs were not detectable at 37 percent of 285
sites where they had been observed in 2000-2002; in 2005 in Sequoia and
Kings Canyon National Parks, mountain yellow-legged frogs were not
detected at 54 percent of sites where they had been recorded 3-8 years
earlier. A compounding effect of disease-caused extinctions of mountain
yellow-legged frogs is that recolonization may never occur, because
streams connecting extirpated sites to extant populations now contain
introduced fishes, which act as barriers to frog movement within
metapopulations. The most recent assessment of the species status in
the Sierra Nevada indicates that mountain-yellow legged frogs occur at
less than 8 percent of the sites from which they were historically
observed. A group of prominent scientists further suggest a 10 percent
decline per year in the number of remaining Rana mucosa populations.
Based on threats that are imminent (because they are ongoing) and high-
magnitude (because they affect the survival of the DPS rangewide), we
continue to assign the population of mountain yellow-legged frog in the
Sierra Nevada an LPN of 3.
Oregon spotted frog (Rana pretiosa) - The following summary is
based on information contained in our files and the petition we
received on May 4, 1989. Historically, the Oregon spotted frog ranged
from British Columbia to the Pit River drainage in northeastern
California. Based on surveys of historical sites, the Oregon spotted
frog is now absent from at least 76 percent of its former range. The
majority of the remaining Oregon spotted frog populations are small and
isolated.
The threats to the species' habitat include development, livestock
grazing, introduction of nonnative plant species, vegetation
succession, changes in hydrology due to construction of dams and
alterations to seasonal flooding, lack of management of exotic
vegetation predators, and poor water quality. Additional threats to the
species are predation by nonnative fish and introduced bullfrogs;
competition with bullfrogs for habitat; and diseases, such as oomycete
water mold Saprolegnia and chytrid fungus infections. The magnitude of
threat is high for this species because this wide range of threats to
both individuals and their habitats could seriously reduce or eliminate
any of these isolated populations and further reduce the species' range
and potential survival. Habitat restoration and management actions have
not prevented a decline in the reproductive rates in some populations.
The threats are imminent because each population is faced with multiple
ongoing and potential threats as identified above. Therefore, we retain
an LPN of 2 for the Oregon spotted frog.
Relict leopard frog (Rana onca) - The following summary is based on
information contained in our files and the petition we received on May
9, 2002. Relict leopard frogs are currently known to occur only in two
general areas in Nevada: near the Overton Arm area of Lake Mead, and
Black Canyon below Lake Mead. These two areas comprise a small fraction
of the historical distribution of the species, which included springs,
streams, and wetlands within the Virgin River drainage downstream from
the vicinity of Hurricane, Utah; along the Muddy River, Nevada; and
along the Colorado River from its confluence with the Virgin River
downstream to Black Canyon below Lake Mead, Nevada and Arizona.
Suggested factors contributing to the decline of the species include
alteration of aquatic habitat due to agriculture and water development,
including regulation of the Colorado River, and the introduction of
exotic aquatic species which potentially prey on the relict leopard
frog and may compete for food and cover sites. In 2005, the National
Park Service, in cooperation with the Service and various other
Federal, State, and local partners, developed a conservation agreement
and strategy which is intended to improve the status of the species
through prescribed management actions and protection. Conservation
actions identified for implementation in the agreement and strategy
include captive rearing tadpoles for translocation and refugium
populations, habitat and natural history studies, habitat enhancement,
population and habitat monitoring, and translocation. Conservation
efforts are proceeding under the agreement, but, additional time is
needed to determine whether the agreement will be effective in
eliminating or reducing the threats to the point that the relict
leopard frog can be removed from candidate status. However, because of
these conservation efforts the magnitude of existing threats has been
reduced to low to moderate. Most populations of the relict leopard frog
face one or more threats which may be long-term in timing and duration.
However, no populations are currently threatened by disease or any
proposed human activity that would reduce the numbers and distribution
of any given population. Since the threats are not currently occurring,
they are nonimminent. We assigned an LPN of 11 to this species.
Ozark hellbender (Cryptobranchus alleganiensis bishopi) - We have
not updated our assessment for this species, as we are currently
developing a proposed listing rule.
Austin blind salamander (Eurycea waterlooensis) - Austin blind
salamander (Eurycea waterlooensis) - The following summary is based on
information contained in our files. No new information was provided in
the petition received on May 11, 2004. The Austin blind salamander is
known to occur in and around three of the four spring sites that
comprise the Barton Springs complex in the City of Austin, Travis
County, Texas. Primary threats to this species are degradation of water
quality due to expanding urbanization. The Austin blind salamander
depends on a constant supply of clean water in the Edwards Aquifer
discharging from Barton Springs for its survival. Urbanization
dramatically alters the normal hydrologic regime and water quality of
an area. Increased impervious cover caused by development increases the
quantity and velocity of runoff that leads to erosion and greater
pollution transport. Pollutants and contaminants that enter the Edwards
Aquifer are discharged in salamander habitat at Barton Springs and have
serious morphological and physiological effects to the salamander.
The Texas Commission on Environmental Quality adopted the Edwards
Rules in 1995 and 1997, which require a number of water quality
protection measures for new development occurring in the recharge and
contributing zones of the Edwards Aquifer. However, Chapter 245 of the
Texas Local Government Code permits ``grandfathering'' of state
regulations. Grandfathering allows developments to be exempted from any
new local or state requirements for water quality controls and
impervious cover limits if the developments were planned prior to the
implementation of such regulations. As
[[Page 75200]]
a result of the grandfathering law, very few developments have followed
these ordinances. New developments are still obligated to comply with
regulations that were applicable at the time when project applications
for development were first filed. In addition, it is significant that
even if they were followed with every new development, these ordinances
do not span the entire watershed for Barton Springs. Consequently,
development occurring outside these jurisdictions can have negative
consequences on water quality and thus have an impact on the species.
Water quality impacts threaten the continued existence of the
Austin blind salamander by altering physical aquatic habitats and the
food sources of the salamander. We consider the threats to be imminent
because urbanization is ongoing and continues to expand over the Barton
Springs Segment of the Edwards Aquifer and water quality continues to
degrade. While the City of Austin and many other partners are actively
working on conservation of the Barton Springs salamander, and the
Austin blind salamander could benefit from all of the ongoing
conservation actions that are being conducted for the Barton Springs
salamander, these efforts have not yet been successful in improving
water quality. In addition, the existence of the species continues to
be threatened by hazardous chemical spills within the Barton Springs
Segment of the Edwards Aquifer, which could result in direct mortality.
Because the Austin blind salamander is known from only three clustered
spring sites and must rely on clear, clean spring discharges from the
Edwards Aquifer for its survival, degraded water quality poses a threat
to the entire population, and is therefore a high-magnitude threat.
Thus, we retain an LPN of 2 for this species.
Georgetown salamander (Eurycea naufragia) - See above in ``Summary
of Listing Priority Changes in Candidates.'' The above summary is based
on information contained in our files. No new information was provided
in the petition we received on May 11, 2004.
Salado salamander (Eurycea chisholmensis) - The following summary
is based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. The Salado
salamander is historically known from two spring sites, Big Boiling
Springs and Robertson Springs, near Salado, Bell County, Texas. We have
received only one anecdotal report of a salamander sighting in Big
Boiling Springs in 2008; prior to that, the salamander had not been
sighted there since 1991. Robertson Springs are on private land and
access to the site has not been granted. The last survey at Robertson
Springs was in the early 1990s.
Primary threats to this species are habitat modification and
degradation of water quality due to expanding urbanization. The Salado
salamander depends on a constant supply of clean water from the
Northern Segment of the Edwards Aquifer for its survival. Pollutants
and contaminants that enter the Edwards Aquifer discharge in salamander
habitat and have morphological and physiological effects on the
salamander. We do not know how likely spills are to occur within the
contributing watersheds of the springs that support this species.
However, several groundwater contamination incidents have occurred
within Salado salamander habitat in recent years. The salamander is
reasonably expected to be vulnerable to catastrophic hazardous
materials spills, groundwater contamination from the Northern Segment
of the Edwards Aquifer, and impacts to its surface habitat. In
addition, because Big Boiling Springs is located near Interstate 35 and
in the center of the city, increasing traffic and urbanization is
likely to increase rather than decrease the threats of contamination
from spills, higher levels of impervious cover, and subsequent impacts
to groundwater. These threats significantly affect the survival of this
species, and groundwater contamination and impact to surface habitat
are ongoing. Moreover, we do not have information that the magnitude or
imminence of the threats to the species has changed since our previous
assessment when we concluded there are ongoing, and therefore, imminent
threats of a high magnitude. Therefore we continue to assign an LPN of
2 to this species.
Yosemite toad (Bufo canorus) - The following summary is based on
information contained in our files and the petition we received on
April 3, 2000. See also our 12-month petition finding published on
December 10, 2002 (67 FR 75834). Yosemite toads are most likely to be
found in areas with thick meadow vegetation or patches of low willows
near or in water, and use rodent burrows for overwintering and
temporary refuge during the summer. Breeding habitat includes the edges
of wet meadows, slow flowing streams, shallow ponds and shallow areas
of lakes. The historic range of Yosemite toads in the Sierra Nevada
occurs from the Blue Lakes region north of Ebbetts Pass (Alpine County)
to south of Kaiser Pass in the Evolution Lake/Darwin Canyon area
(Fresno County). The historic elevational range of Yosemite toads is
1,460 to 3,630 m (4,790 to 11,910 ft).
The threats currently facing the Yosemite toad include cattle
grazing, timber harvesting, recreation, disease, and climate change.
Inappropriate grazing has shown to cause loss in vegetative cover and
destruction of peat layers in meadows, which lowers the groundwater
table and summer flows. This may increase the stranding and mortality
of tadpoles, or make these areas completely unsuitable for Yosemite
toads (Martin 2002). Grazing can also degrade or destroy moist upland
areas the Yosemite toad use as non-breeding habitat and it can collapse
rodent burrows the Yosemite toads use as cover and hibernation sites.
Timber harvesting and associated road development could severely alter
the terrestrial environment and result in the reduction and occasional
extirpation of amphibian populations in the Sierra Nevada. These
habitat gaps may act as dispersal barriers and contribute to the
fragmentation of Yosemite toad habitat and populations. Trails (foot,
horse, bicycle, or off-highway motor vehicle) compact soil in riparian
habitat, which increases erosion, displaces vegetation, and can lower
the water table. Trampling or the collapsing of rodent burrows by
recreationists, pets, and vehicles could lead to direct mortality of
all life stages of the Yosemite toad and disrupt their behavior.
Various diseases have been confirmed in Yosemite toads. Mass die-offs
of amphibians have been attributed to: chytrid fungal infections of
metamorphs and adults; Saprolegnia fungal infections of eggs;
iridovirus infection of larvae, metamorphs, or adults; and bacterial
infections. However, recent surveys in Yosemite National Park have
found that the park populations are not currently infected with chytrid
fungus. Yosemite toads probably are exposed to a variety of pesticides
and other chemicals throughout their range. Environmental contaminants
could negatively affect the species by causing direct mortality;
suppressing the immune system; disrupting breeding behavior,
fertilization, growth or development of young; and disrupting the
ability to avoid predation. There is no indication that any of these
threats in ongoing or planned and the threats are therefore
nonimminent. In addition, since there are a number of substantial
populations and these threats tend to have localized effects, the
threats are moderate to low in magnitude. We therefore retained an LPN
of 11 for the Yosemite toad.
[[Page 75201]]
Black Warrior waterdog (Necturus alabamensis) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
The Black Warrior waterdog is a salamander that inhabits streams above
the Fall Line within the Black Warrior River Basin in Alabama. There is
very little specific locality information available on the historical
distribution of the Black Warrior waterdog since little attention was
given to this species between its description in 1937 and the 1980s. At
that time, there were a total of only 11 known historical records from
4 Alabama counties. Two of these sites have now been inundated by
impoundments. Extensive survey work was conducted in the 1990s to look
for additional populations. Currently, the species is known from 14
sites in 5 counties.
Water-quality degradation is the biggest threat to the continued
existence of the Black Warrior waterdog. Most streams that have been
surveyed for the waterdog showed evidence of pollution and many
appeared biologically depauperate. Sources of point and nonpoint
pollution in the Black Warrior River Basin have been numerous and
widespread. Pollution is generated from inadequately treated effluent
from industrial plants, sanitary landfills, sewage treatment plants,
poultry operations, and cattle feedlots. Surface mining represents
another threat to the biological integrity of waterdog habitat. Runoff
from old, abandoned coal mines generates pollution through
acidification, increased mineralization, and sediment loading. The
North River, Locust Fork, and Mulberry Fork, all streams that this
species inhabits, are on the Environmental Protection Agency's list of
impaired waters. An additional threat to the Black Warrior waterdog is
the creation of large impoundments that have flooded thousands of
square hectares (acres) of its habitat. These impoundments are likely
marginal or unsuitable habitat for the salamander. While the water-
quality threat is pervasive and problematic, the overall magnitude of
the threat is moderate, as there has not been a steep rate of decline
in the population of this species. Water quality degradation in the
Black Warrior basin is ongoing; therefore, the threats are imminent. We
assigned an LPN of 8 to this species.
Fishes
Headwater chub (Gila nigra) - See above in ``Summary of Listing
Priority Changes in Candidates.'' The above summary is based on
information contained in our files and the 12-month finding published
in the Federal Register on May 3, 2006 (71 FR 26007).
Arkansas darter (Etheostoma cragini) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. The Arkansas
darter is a small fish in the perch family native to portions of the
Arkansas River basin. The species' range includes sites in extreme
northwestern Arkansas, southwestern Missouri, and northeastern
Oklahoma, within the Neosho River watershed. It also occurs in a number
of watersheds and isolated streams in eastern Colorado, south-central
and southwestern Kansas, and the Cimarron watershed in northwest
Oklahoma. The species is most often found in small spring-fed streams
with sand substrate and aquatic vegetation. It appears stable at most
sites where spring flows persist. It has declined in areas where spring
flows have decreased or been eliminated. We estimate that currently
there are approximately 135 locality occurrences of the Arkansas darter
distributed across the 5 States; it was found at 29 of 67 sites sampled
in 2005-2006. Threats to the species include stream dewatering
resulting from groundwater pumping in the western portion of the
species' range, and potential development pressures in portions of its
eastern range. Spills and runoff from confined animal feeding
operations also potentially affect the species range-wide. The
magnitude of threats facing this species is moderate to low, given the
number of different locations where the species occurs and the fact
that no single threat or combination of threats is working to affect
more than a portion of the wide-spread population occurrences. Overall,
the threats are not imminent since groundwater pumping is declining and
development, spills, runoff are not currently affecting the species
rangewide. Thus, we are retaining an LPN of 11 for the Arkansas darter.
Cumberland darter (Etheostoma susanae) - We have not updated our
assessment for this species, as we are currently developing a proposed
listing rule.
Pearl darter (Percina aurora) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Little is known about the
specific habitat requirements or natural history of the Pearl darter.
Pearl darters have been collected from a variety of river/stream
attributes, mainly over gravel bottom substrate. This species is
historically known only from localized sites within the Pascagoula and
Pearl River drainages in two states ( Louisiana and Mississippi).
Currently, the Pearl darter is considered extirpated from the Pearl
River drainage and rare in the Pascagoula River drainage. Since 1983,
the range of the Pearl darter has decreased by 55 percent.
Pearl darters are vulnerable to the cumulative impacts of a variety
of non-point pollution sources, such as sedimentation and chemicals,
and to more localized and concentrated pollution events. The potential
of reduction of the flow rate for the Leaf and Pascagoula rivers may be
significant if the Department of Energy's Strategic Petroleum Reserve
project occurs by 2014. However, the only current threat to the species
is believed to be the steady yet gradual change in river and tributary
geomorphology and hydrology over time. The magnitude of this threat to
Pearl darter is high because even a gradual change in hydrology can
have a significant impact on the survival of the species' limited and
disjunct populations. The immediacy of the threat is nonimminent, since
no known confirmed projects are planned that would have a direct impact
on the species, and the decline of water quality is slow and gradual.
In addition, efforts are underway to improve habitat by reducing these
threats and to increase and augment the numbers of Pearl darters by
husbandry. Therefore, we assign this species an LPN of 5.
Rush darter (Etheostoma phytophilum) - We have not updated our
assessment for this species, as we are currently developing a proposed
listing rule.
Yellowcheek darter (Etheostoma moorei) - The following summary is
based on information from our files. No new information was provided in
the petition we received on May 11, 2004. The yellowcheek darter is
endemic to four headwater tributaries of the Little Red River in
Arkansas. It is vulnerable to alterations in physical habitat
characteristics such as the impoundment of Greers Ferry Reservoir,
channel maintenance in the Archey Fork, increased sedimentation from
eroding stream banks and poor riparian management, and illegal gravel
mining. Factors affecting the remaining populations include loss of
suitable breeding habitat, habitat and water quality degradation,
population isolation due to stretches of unsuitable habitat between
populations, and severe population declines exacerbated by stochastic
drought conditions. A 2004-2005 threats assessment by Service personnel
documented occurrences of the aforementioned activities
[[Page 75202]]
(impoundment, channel maintenance, poor riparian management, illegal
gravel mining) and found 52 sites on the Middle Fork, 28 sites on the
South Fork, 8 sites on Archey Fork, and 1 site in the Turkey/Beech/
Devils Fork system where those activities are potentially contributing
to the decline of the species. Since the threats assessment was
completed, natural gas exploration and development in the Fayetteville
Shale formation in north central Arkansas has also become a sizeable
threat in all watersheds. The Middle Fork was listed as an impaired
waterbody by the Arkansas Department of Environmental Quality in 2004
due to excessive bacteria and low dissolved oxygen.
Recent studies have documented significant declines in the numbers
(60,000 in 1981; 10,300 in 2000) of this fish in the remaining
populations and further range restriction within the tributaries (130.4
to 65.0 stream km). As a result, yellowcheek darter numbers declined
over a 20-year period by 83 percent in both the Middle Fork and South
Fork, and 60 percent in the Archey Fork, based on a 2000 status survey.
No yellowcheek darters have been found in the Turkey Fork between 1999
and 2005; the species has apparently been extirpated in that reach. The
threats are high in magnitude since they significantly affect the
ability of this species to survive and they are not currently targeted
by conservation actions. They are also imminent, because they are
ongoing. Therefore, we assigned this species a listing priority number
of 2.
Chucky madtom (Noturus crypticus) - We have not updated our
assessment for this species, as we are currently developing a proposed
listing rule.
Grotto sculpin (Cottus sp., sp. nov.) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. The Grotto
sculpin, a small fish, is restricted to two karst areas (limestone
regions characterized by sink holes, abrupt ridges, caves, and
underground streams): the Central Perryville Karst and Mystery-Rimstone
Karst in Perry County, southeast Missouri. Data supports the genetic
distinctness of the grotto sculpin as a species, although it has not
yet been formally described. Grotto sculpins have been documented in
only 5 caves. The current overall range of the grotto sculpin has been
estimated to encompass approximately 260 square kilometers (100 square
miles).
The small population size and endemism of the grotto sculpin make
it vulnerable to extinction due to genetic drift, inbreeding
depression, and random or chance changes to the environment. The
species' karst habitat is located down-gradient of the city of
Perryville, Missouri, which poses a potential threat if contaminants
from this urban area enter cave streams occupied by grotto sculpins.
Various agricultural chemicals, such as ammonia, nitrite/nitrate,
chloride, and potassium have been detected at levels high enough to be
detrimental to aquatic life within the Perryville Karst area. More than
half of the sinkholes in Perry County contain anthropogenic refuse,
ranging from household cleansers and sewage to used pesticide and
herbicide containers. As a result, potential water contamination from
various sources of point and non-point pollution poses a significant
threat to the grotto sculpin. Of the 5 cave systems documented to have
grotto sculpins, populations in one cave system were likely eliminated,
presumably as the result of point-source pollution. When the cave was
searched in the spring of 2000, a mass mortality of grotto sculpin was
noted, and subsequent visits to the cave have failed to document a
single live grotto sculpin. Thus, the species appears to have suffered
a 20 percent decrease in the number of populations from the single
event. Predatory fish such as common carp, fat-head minnow, yellow
bullhead, green sunfish, bluegill, and channel catfish occur in all of
the caves occupied by grotto sculpin. These predators may escape
surface farm ponds that unexpectedly drain through sinkholes into the
underground cave systems and enter grotto sculpin habitat. Although we
do not have direct observations of these fish preying on grotto
sculpins, it is highly likely that predation is occurring. No
regulatory mechanisms are in place that would provide protection to the
grotto sculpin. Ongoing threats from chemical contamination of the
habitat of the grotto sculpin and competition from nonnative fish,
combined with its low population numbers, increase the likelihood of
extinction. Due to the high magnitude of ongoing, and thus imminent,
threats we assigned this species an LPN of 2.
Sharpnose shiner (Notropis oxyrhynchus) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. The sharpnose
shiner is a small, slender minnow, endemic to the Brazos River Basin in
Texas. Historically, the sharpnose shiner existed throughout the Brazos
River and several of its major tributaries within the watershed. It has
also been found in the Wichita River (within the Red River Basin) where
it may have once naturally occurred but has since been extirpated.
Current information indicates that the population within the Upper
Brazos River drainage (upstream of Possum Kingdom Reservoir) is
apparently stable, while the population within the Middle and Lower
Brazos River Basins may only exist in remnant populations in areas of
suitable habitat, which may no longer be viable, representing a
reduction of approximately 68 percent of its historical range.
The most significant threat to the existence of the sharpnose
shiner is potential reservoir development within its current range.
Additional threats include irrigation and water diversion,
sedimentation, desalination, industrial and municipal discharges,
agricultural activities, in-stream sand and gravel mining, and the
spread of invasive saltcedar. The current limited distribution of the
sharpnose shiner within the Upper Brazos River Basin makes it
vulnerable to catastrophic events such as the introduction of
competitive species or prolonged drought. State law does not provide
protection for the sharpnose shiner. The magnitude of threat is
considered high, since the major threat of reservoir development within
the current range of the species may render its remaining habitat
unsuitable throughout its limited distribution. The immediacy of threat
is nonimminent because the most significant threat - major reservoir
projects - are not likely to occur in the near future, and there is
potential for implementing other water supply options that could
preclude reservoir development. For these reasons, we assigned an LPN
of 5 to this species.
Smalleye shiner (Notropis buccula) - The following summary is based
on information contained in our files. No new information was provided
in the petition we received on May 11, 2004. The smalleye shiner is a
small, pallid minnow endemic to the Brazos River Basin in Texas. The
population of smalleye shiners within the Upper Brazos River drainage
(upstream of Possum Kingdom Reservoir) is apparently stable. However,
the shiner may be extirpated downstream from the reservoir,
representing a reduction of approximately 54 percent of its historical
range.
The most significant threat to the existence of the smalleye shiner
is potential reservoir development within its current range. Additional
threats include irrigation and water diversion, sedimentation,
desalination, industrial
[[Page 75203]]
and municipal discharges, agricultural activities, in-stream sand and
gravel mining, and the spread of invasive saltcedar. The current
limited distribution of the smalleye shiner within the Upper Brazos
River Basin makes it vulnerable to catastrophic events such as the
introduction of competitive species or prolonged drought. State law
does not provide protection for the smalleye shiner. The magnitude of
threat is considered high since the major threat of reservoir
development within the current range may render its remaining habitat
unsuitable throughout its limited distribution. The immediacy of threat
is nonimminent because the most significant threat - major reservoir
projects - are not likely to occur in the near future, and there is
potential for implementing other water supply options that could
preclude reservoir development. For these reasons, we assigned an LPN
of 5 to this species.
Zuni bluehead sucker (Catostomus discobolus yarrowi) - The
following summary is based on information contained in our files. No
new information was provided in the petition we received on May 11,
2004. The range of the Zuni bluehead sucker has been reduced by over
90%. The Zuni bluehead sucker currently occupies 9 river miles (15
kilometers) in 3 areas of New Mexico, and potentially occurs in 27
miles (43 kilometers) in the Kinlichee drainage of Arizona. However,
the number of occupied miles in Arizona is unknown, and the genetic
composition of these fish is still under investigation. Zuni bluehead
sucker range reduction and fragmentation is caused by discontinuous
surface water flow, introduced species, and habitat degradation from
fine sediment deposition. Zuni bluehead sucker persist in very small
creeks that are subject to very low flows and drying during periods of
drought. Because of climate change (warmer air temperatures) stream
flow is predicted to decrease in the Southwest, even if precipitation
were to increase moderately. Warmer winter and spring temperatures
cause an increased fraction of precipitation to fall as rain, resulting
in a reduced snow pack, an earlier snow melt, and a longer dry season
leading to decreased stream flow in the summer and a longer fire
season. These changes would have a negative effect on Zuni bluehead
sucker. Another major impact to populations of Zuni bluehead sucker was
the application of fish toxicants through at least two dozen treatments
in the Nutria and Pescado rivers between 1960 and 1975. Large numbers
of Zuni bluehead suckers were killed during these treatments.
For several years, the New Mexico Department of Game and Fish has
been the lead agency to develop a conservation plan for Zuni bluehead
sucker. The Zuni Bluehead Sucker Recovery Plan was approved by the New
Mexico State Game Commission during a State Game Commission meeting on
December 15, 2004. The recovery plan recommends preservation and
enhancement of extant populations and restoration of historical Zuni
bluehead sucker populations. We believe the recovery actions prescribed
by the State Recovery Plan will reduce and remove threats to this
subspecies; however those actions will require further discussions and
authorizations before they can be implemented. The ongoing threats
including loss of habitat (loss of both historical and current habitat
from beaver activity), degradation of remaining habitat (from nonnative
species and land development), drought, fire, and climate change are
high magnitude because they significantly affect the survival of the
subspecies. We therefore maintained the current LPN of 3 for this
subspecies.
Clams
Texas hornshell (Popenaias popei) - See above in ``Summary of
Listing Priority Changes in Candidates.'' The above summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004.
Fluted kidneyshell (Ptychobranchus subtentum) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
The fluted kidneyshell is a freshwater mussel (Unionidae) endemic to
the Cumberland and Tennessee River systems (Cumberlandian Region) in
Alabama, Kentucky, Tennessee, and Virginia. It requires shoal habitats
in free-flowing rivers to survive and successfully recruit new
individuals into its populations.
This species has been extirpated from numerous regional streams and
is no longer found in the State of Alabama. Habitat destruction and
alteration (e.g., impoundments, sedimentation, and pollutants) are the
chief factors that contributed to its decline. The fluted kidneyshell
was historically known from at least 37 streams but is currently
restricted to no more than 12 isolated populations. Current status
information for most of the 12 populations deemed to be extant is
available from recent periodic sampling efforts (sometimes annually)
and other field studies, particularly in the upper Tennessee River
system. Some populations in the Cumberland River system have had recent
surveys as well (e.g., Wolf, Little Rivers; Little South Fork; Horse
Lick, Buck Creeks). Populations in Buck Creek, Little South Fork, Horse
Lick Creek, Powell River, and North Fork Holston River have clearly
declined over the past two decades. Based on recent information, the
overall population of the fluted kidneyshell is declining rangewide. At
this time, the species remains in large numbers and is viable in just
the Clinch River/Copper Creek, although smaller, viable populations
remain (e.g., Wolf, Little, North Fork Holston Rivers; Rock Creek).
Most other populations are of questionable or limited viability, with
some on the verge of extirpation (e.g., Powell River; Little South
Fork; Horse Lick, Buck, Indian Creeks). Newly reintroduced populations
in the Nolichucky and Duck Rivers will hopefully begin to reverse the
downward population trend of this species. The threats are high in
magnitude, since the majority of populations of this species are
severely affected by numerous threats (impoundments, sedimentation,
small population size, isolation of populations, gravel mining,
municipal pollutants, agricultural runoff, nutrient enrichment, and
coal processing pollution) which result in mortality and/or reduced
reproductive output. Since the threats are ongoing, they are imminent.
We assigned an LPN of 2 to this mussel species.
Neosho mucket (Lampsilis rafinesqueana) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. The Neosho mucket
is a freshwater mussel native to Arkansas, Kansas, Missouri, and
Oklahoma. The species has been extirpated from approximately 62 percent
(835 river miles) of its range, most in Kansas and Oklahoma. The Neosho
mucket survives in four river drainages; however, only two of these,
the Spring and Illinois Rivers, currently support relatively large
populations.
Large portions of the historic range have been inundated by the
construction of at least 11 dams. Channel instability downstream of
these dams has further reduced suitable habitat and mussel
distribution. Range restriction and population declines have occurred
due to habitat degradation attributed to impoundments, mining,
sedimentation, and agricultural pollutants. Rapid development and
urbanization in the Illinois River
[[Page 75204]]
watershed will likely continue to increase sedimentation and
eutrophication, but populations are currently stable in this river. The
threats to the remaining extant populations include random catastrophic
events (e.g., flood scour, drought, toxic spills), land use changes
within the limited range, and genetic isolation and the deleterious
effects of inbreeding. These threats have caused the species to be
intrinsically vulnerable to extirpation. Although State regulations
limit harvest of this species, there is little protection for habitat.
The threats are high in magnitude as they occur and affect survival
throughout the range of this species. While some of the threats are
ongoing and thus, imminent (sedimentation, mining), others are
nonimminent (habitat reduction and degradation from reservoir
construction, contaminants, genetic isolation), but on the balance are
nonimminent. Thus, we assigned a listing priority number of 5 to this
species.
Alabama pearlshell (Margaritifera marrianae) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
The Alabama pearlshell (Margaritifera marrianae) inhabits shallow
riffles and pool margins of small creeks and streams of southwest
Alabama. Only three populations of Alabama pearlshell have been
confirmed to survive during the past 15 years. One of the three
populations has declined significantly over the past few years,
apparently due to increased sedimentation at this location and possibly
other forms of non-point source (NPS) pollution. Most recent data
suggest that the other two populations may also be declining. Severe
droughts in 2007 may have also adversely affected surviving
populations. We assigned the Alabama pearlshell an LPN of 2 because the
NPS pollution is ongoing, and therefore imminent, and the vulnerability
of small stream habitat to continuing NPS pollution, combined with the
fewer numbers of live mussels in the three known populations, means
that the NPS pollution poses a high-magnitude threat to this species.
Slabside pearlymussel (Lexingtonia dolabelloides) - See above in
``Summary of Listing Priority Changes in Candidates.'' The above
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Georgia pigtoe (Pleurobema hanleyanum) - We have not updated our
assessment for this species, as we are currently developing a proposed
listing rule.
Altamaha spinymussel (Elliptio spinosa) - We have not updated our
assessment for this species, as we are currently developing a proposed
listing rule.
Snails.
Fat-whorled (Bonneville) pondsnail (Stagnicola bonnevillensis) -
See above in ``Summary of Listing Priority Changes in Candidates.'' The
above summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Interrupted rocksnail (Leptoxis foremani) (=downei) - We have not
updated our assessment for this species, as we are currently developing
a proposed listing rule for this species.
Sisi snail (Ostodes strigatus) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. The sisi snail is a ground-
dwelling species in the Potaridae family, and is endemic to American
Samoa. The species is now known from a single population on the island
of Tutuila, American Samoa.
This species is currently threatened by habitat loss and
modification and by predation from nonnative predatory snails. The
decline of the sisi in American Samoa has resulted, in part, from loss
of habitat to forestry and agriculture and loss of forest structure to
hurricanes and alien weeds that establish after these storms. All live
sisi snails have been found in the leaf litter beneath remaining intact
forest canopy. No snails were found in areas bordering agricultural
plots or in forest areas that were severely damaged by three hurricanes
(1987, 1990, and 1991). Under natural historic conditions, loss of
forest canopy to storms did not pose a great threat to the long-term
survival of these snails; enough intact forest with healthy populations
of snails would support dispersal back into newly regrown canopy
forest. However, the presence of alien weeds such as mile-a-minute vine
(Mikania micrantha) may reduce the likelihood that native forest will
re-establish in areas damaged by the hurricanes. This loss of habitat
to storms is greatly exacerbated by expanding agriculture. Agricultural
plots on Tutuila have spread from low elevation up to middle and some
high elevations, greatly reducing the forest area and thus reducing the
resilience of native forests and its populations of native snails.
These reductions also increase the likelihood that future storms will
lead to the extinction of populations or species that rely on the
remaining canopy forest. In an effort to eradicate the giant African
snail (Achatina fulica), the alien rosy carnivore snail (Euglandia
rosea) was introduced in 1980. The rosy carnivore snail has spread
throughout the main island of Tutuila. Numerous studies show that the
rosy carnivore snail feeds on endemic island snails including the sisi,
and is a major agent in their declines and extirpations. At present,
the major threat to long-term survival of the native snail fauna in
American Samoa is predation by nonnative predatory snails. These
threats are ongoing and are therefore imminent. Since the threats occur
throughout the entire range of the species and have a significant
effect on the survival of the snails, they are of a high magnitude.
Therefore we assigned this species an LPN of 2.
Diamond Y Spring snail (Pseudotryonia adamantina) and Gonzales
springsnail (Tryonia circumstriata) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Diamond Y Spring snail and
Gonzales springsnail are small aquatic snails endemic to Diamond Y
Spring in Pecos County, Texas. The spring and its outflow channel are
owned and managed by The Nature Conservancy.
These snails are primarily threatened with habitat loss due to
springflow declines from drought and from pumping of groundwater.
Additional threats include water contamination from accidental releases
of petroleum products, as their habitat is in an active oil and gas
field. Also, a nonnative aquatic snail (Melanoides sp.) was recently
introduced into the native snails' habitat, and may compete with
endemic snails for space and resources. The magnitude of threats is
high because limited distribution of these narrow endemics makes any
impact from increasing threats (e.g., loss of springflow, contaminants,
and nonnative species) likely to result in the extinction of the
species. These species occur in one location in an arid region
currently plagued by drought and ongoing aquifer withdrawals, making
the eventual loss of spring flow an imminent threat of total habitat
loss. Thus, we maintain the LPN of 2 for both species.
Fragile tree snail (Samoana fragilis) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004.
[[Page 75205]]
A tree-dwelling species, the fragile tree snail is a member of the
Partulidae family of snails, and is endemic to the islands of Guam and
Rota (Mariana Islands). Requiring cool and shaded native forest
habitat, the species is now known from 4 populations on Guam and a
single population on Rota.
This species is currently threatened by habitat loss and
modification and by predation from nonnative predatory snails and
flatworms. Large numbers of Philippine deer (Cervus mariannus) (Guam
and Rota), pigs (Sus scrofra) (Guam), water buffalo (Bubalus bubalis)
(Guam), and cattle (Bos taurus) (Rota) directly alter the understory
plant community and overall forest microclimate, making it unsuitable
for snails. Predation by the alien rosy carnivore snail (Euglandina
rosea) and the Manokwar flatworm (Platydemus manokwari) is a serious
threat to the survival of the fragile tree snail. Field observations
have established that the rosy carnivore snail and the Manokwar
flatworm will readily feed on native Pacific island tree snails,
including the Partulidae, such as those of the Mariana Islands. The
rosy carnivore snail has caused the extirpation of many populations and
species of native snails throughout the Pacific islands. The Manokwar
flatworm has also contributed to the decline of native tree snails, in
part due to its ability to ascend into trees and bushes that support
native snails. Areas with populations of the flatworm usually lack
partulid tree snails or have declining numbers of snails. Because all
of the threats occur rangewide and have a significant effect on the
survival of this snail species, they are high in magnitude. The threats
are also ongoing and thus are imminent. Therefore, we assigned this
species an LPN of 2.
Guam tree snail (Partula radiolata) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. A tree-dwelling
species, the Guam tree snail is a member of the Partulidae family of
snails and is endemic to the island of Guam. Requiring cool and shaded
native forest habitat, the species is now known from 22 populations on
Guam.
This species is primarily threatened by predation from nonnative
predatory snails and flatworms. In addition, the species is also
threatened by habitat loss and degradation. Predation by the alien rosy
carnivore snail (Euglandina rosea) and the alien Manokwar flatworm
(Platydemus manokwari) is a serious threat to the survival of the Guam
tree snail (see summary for the fragile tree snail, above). On Guam,
open agricultural fields and other areas prone to erosion were seeded
with tangantangan (Leucaena leucocephala) by the U.S. Military.
Tangantangan grows as a single species stand with no substantial
understory. The microclimatic condition is dry with little accumulation
of leaf litter humus and is particularly unsuitable as Guam tree snail
habitat. In addition, native forest cannot reestablish and grow where
this alien weed has become established. Because all of the threats
occur rangewide and have a significant effect on the survival of this
snail species, they are high in magnitude. The threats are also ongoing
and thus are imminent. Therefore, we assigned this species an LPN of 2.
Humped tree snail (Partula gibba) - The following summary is based
on information contained in our files. No new information was provided
in the petition we received on May 11, 2004. A tree-dwelling species,
the humped tree snail is a member of the Partulidae family of snails,
and was originally known from the island of Guam and the Commonwealth
of the Northern Mariana Islands (islands of Rota, Aguiguan, Tinian,
Saipan, Anatahan, Sarigan, Alamagan, and Pagan). Most recent surveys
revealed a total of 14 populations on the islands of Guam, Rota,
Aguiguan, Sarigan, Saipan, Alamagan, and Pagan. Although still the most
widely distributed tree snail endemic in the Mariana Islands, remaining
population sizes are often small.
This species is currently threatened by habitat loss and
modification and by predation from nonnative predatory snails and flat
worms. Throughout the Mariana Islands, feral ungulates (pigs (Sus
scrofa), Philippine deer (Cervus mariannus), cattle (Bos taurus), water
buffalo (Bubalus bubalis), and goats (Capra hircus)) have caused severe
damage to native forest vegetation by browsing directly on plants,
causing erosion, and retarding forest growth and regeneration. This in
turn reduces the quantity and quality of forested habitat for the
humped tree snail. Currently, populations of feral ungulates are found
on the islands of Guam (deer, pigs, and water buffalo), Rota (deer and
cattle), Aguiguan (goats), Saipan (deer, pigs, and cattle), Alamagan
(goats, pigs, and cattle), and Pagan (cattle, goats, and pigs). Goats
were eradicated from Sarigan in 1998 and the humped tree snail has
increased in abundance on that island, likely in response to the
removal of all the goats. However, the population of humped tree snails
on Anatahan is likely extirpated due to the massive volcanic explosions
of the island beginning in 2003 and still continuing, and the resulting
loss of up to 95 percent of the vegetation on the island. Predation by
the alien rosy carnivore snail (Euglandina rosea) and the alien
Manokwar flatworm (Platydemus manokwari) is a serious threat to the
survival of the humped tree snail (see summary for the fragile tree
snail, above). The magnitude of threats is high because these alien
predators cause significant population declines to the humped tree
snail rangewide. These threats are ongoing and thus are imminent.
Therefore, we assigned this species an LPN of 2.
Lanai tree snail (Partulina semicarinata) - The following summary
is based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. A tree-dwelling
species, P. semicarinata is a member of the Achatinellidae family of
snails. Endemic to the island of Lanai, the species is currently known
from 3 populations totaling 29 individuals. This species is highly
threatened throughout its limited range by habitat loss and
modification and by predation from rats. No efforts are being
undertaken to remove rats in areas where P. semicarinata occur. The
threat from this predator is expected to continue or increase unless
the rats are actively controlled or eradicated. Habitat loss also
continues as nonnative ungulates trample and browse native vegetation
required by P. semicarinata. Although the snails are in an area to be
fenced, the habitat will continue to be degraded until the fence is
completed and the ungulates have been removed. The small number of
individuals and the small number of populations make this species very
susceptible to the negative effects of stochastic events such as
hurricanes and storms. A population in captivity is protected from the
effects of unexpected droughts, although the effects of severe storms
may still affect this population as evidenced by the loss of snails
when a severe flood interrupted the power supply to the Hawaii
Endangered Snail Captive Propagation Lab and temperatures increased
within the environmental chambers containing the snails. In addition,
these captive snails are likely subjected to the same risks of reduced
reproductive vigor and loss of genetic variability as the snail in the
wild population. The magnitude of threats is high because they cause
significant population declines to P.semicarinata rangewide. The
threats are also ongoing and thus are imminent.
[[Page 75206]]
Therefore, we assigned this species an LPN of 2.
Lanai tree snail (Partulina variabilis) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. A tree-dwelling
species, P. variabilis is a member of the Achatinellidae family of
snails. Endemic to the island of Lanai, the species is currently known
from 12 populations totaling 90 individuals. This species is highly
threatened throughout its limited range by habitat loss and
modification and by predation from rats. The same description of
threats for P. semicarinata, above, applies to this species, including
threats to a population in captivity. The magnitude of threats is high
because they result in direct mortality or significant population
declines to P. variabilis rangewide. The threats are ongoing and thus
are imminent. Therefore, we assigned this species an LPN of 2.
Langford's tree snail (Partula langfordi) - The following summary
is based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. A tree-dwelling
species, Langford's tree snail is a member of the Partulidae family of
snails, and is known from one population on the island of Aguiguan.
This species is currently threatened by habitat loss and modification
and by predation from nonnative predatory snails. In the 1930s, the
island of Aguiguan was mostly cleared of native forest to support sugar
cane and pineapple production. The abandoned fields and airstrip are
now overgrown with alien weeds. The remaining native forest understory
has greatly suffered from large and uncontrolled populations of alien
goats and the invasion of weeds. Goats (Capra hircus) have caused
severe damage to native forest vegetation by browsing directly on
plants, causing erosion, and retarding forest growth and regeneration.
This in turn reduces the quantity and quality of forested habitat for
Langford's tree snail. Predation by the alien rosy carnivore snail
(Euglandina rosea) and by the Manokwar flatworm (Platydemus manokwari)
(see summary for the fragile tree snail, above) is also a serious
threat to the survival of Langford's tree snail. All of the threats are
occurring rangewide and no efforts to control or eradicate the
nonnative predatory snail species or to reduce habitat loss are being
undertaken. The magnitude of threats is high because they result in
direct mortality or significant population declines to Langford's tree
snail rangewide. A survey of Aguiguan in November 2006 failed to find
any live Langford's tree snails. These threats are also ongoing and
thus are imminent. Therefore, we assigned this species an LPN of 2.
Newcomb's tree snail (Newcombia cumingi) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. The species is
endemic to the island of Maui, where it is currently known from a
single remaining population. The greatest threats to Newcomb's tree
snail are the loss of the only known remaining population due to
predation from rats and the rosy carnivore snail (Euglandina rosea).
There are no efforts in place to reduce the threat from the rosy
carnivore snail. Discussions are underway with the private landowner to
construct a rat-proof fence in the area occupied by this snail. Our
attempts to raise this species in a captive propagation facility have
been unsuccessful. The magnitude of threats is high because they occur
within the last known population of the species and result in direct
mortality or significant population declines. These threats are also
ongoing and thus are imminent. Therefore, we assigned this species an
LPN of 2.
Phantom Cave snail (Cochliopa texana) and Phantom springsnail
(Tryonia cheatumi) - The following summary is based on information
contained in our files. No new information was provided in the petition
we received on May 11, 2004. Phantom Cave snail and Phantom springsnail
are small aquatic snails that occur in three spring outflows in the
Toyah Basin in Reeves and Jeff Davis Counties, Texas. The primary
threat to both species is the loss of surface flows due to declining
groundwater levels from drought and pumping for agricultural
production. Although much of the land immediately surrounding their
habitat is owned and managed by The Nature Conservancy, Bureau of
Reclamation, and Texas Parks and Wildlife Department, the water which
is needed to maintain their habitat, has declined due to a reduction in
spring flows, possibly as a result of private groundwater pumping in
areas beyond that controlled by these landowners. As an example,
Phantom Lake Spring, one of the sites of occurrence, has already ceased
flowing, and aquatic habitat in the spring is supported only by a
pumping system. The magnitude of the threats is high because spring
flow loss would result in complete habitat destruction and permanent
elimination of all populations of the species. The immediacy of the
threats is imminent, as evidenced by the drastic decline in spring flow
at Phantom Lake Spring that is currently happening and may extirpate
these populations in the near future. Declining spring flows in San
Solomon Spring are also becoming evident, and will affect that spring
site as well within the foreseeable future. Thus, we maintained the LPN
of 2 for both species.
Tutuila tree snail (Eua zebrina) - The following summary is based
on information contained in our files. No new information was provided
in the petition we received on May 11, 2004. A tree-dwelling species,
the Tutuila tree snail is a member of the Partulidae family of snails,
and is endemic to American Samoa. The species is known from 32
populations on the islands of Tutuila, Nuusetoga, and Ofu.
This species is currently threatened by habitat loss and
modification and by predation from nonnative predatory snails and rats.
All live Tutuila tree snails were found on understory vegetation
beneath remaining intact forest canopy. No snails were found in areas
bordering agricultural plots or in forest areas that were severely
damaged by three hurricanes (1987, 1990, and 1991). (See summary for
the sisi snail, above, regarding impacts of alien weeds and of the rosy
carnivore snail.). Rats (Rattus spp) have also been shown to devastate
snail populations, and rat-chewed snail shells have been found at sites
where the Tutuila snail occurs. At present, the major threat to the
long-term survival of the native snail fauna in American Samoa is
predation by nonnative predatory snails and rats. The magnitude of
threats is high because they result in direct mortality or significant
population declines to the Tutuila tree snail rangewide. The threats
are also ongoing and thus are imminent. Therefore, we assigned this
species an LPN of 2.
Chupadera springsnail (Pyrgulopsis chupaderae) - We have not
updated our assessment for this species, as we are currently developing
a proposed listing rule.
Elongate mud meadows springsnail (Pyrgulopsis notidicola) - See
above in ``Summary of Listing Priority Changes in Candidates.'' The
above summary is based on information contained in our files. No new
information was provided in the petition received on May 11, 2004.
Gila springsnail (Pyrgulopsis gilae) - The following summary is
based on information contained in our files and the petition we
received on November 20, 1985. Also see our 12-month petition finding
published in the
[[Page 75207]]
Federal Register on October 4, 1988 (53 FR 38969). The Gila springsnail
is an aquatic species known from 13 populations in New Mexico. Surveys
conducted in 2008 may have located two additional populations, but the
identification of the species at those sites awaits confirmation.
Preliminary assessment of springsnail collections made in 2008
indicates there are morphological differences between some Gila
springsnail populations, which suggests there may be some level of
genetic divergence or speciation.
The long-term persistence of the Gila springsnail is contingent
upon protection of the riparian corridor immediately adjacent to the
springhead and springrun. Sites on both private and Federal lands are
subject to levels of recreational use and livestock grazing that
negatively affect this species, thus placing the long-term survival of
the Gila springsnail at risk. Natural events such as drought, forest
fire, sedimentation, and flooding; wetland habitat degradation by
recreational bathing in thermal springs; and poor watershed management
practices represent the primary threats to the Gila springsnail. Fire
suppression activities and fire retardant chemicals have potentially
deleterious effects on this species, as well. Because several of the
springs occur on U.S. Forest Service land, management options for the
protection of the snail should be possible. However, randomly occurring
events, especially fire and drought, could have a major impact on the
species. Moderate use by recreationalists and livestock is ongoing. If
these uses remain at current or lower levels, they will not pose an
imminent threat to the species. Of greater concern is drought, which
could affect spring discharge and increases the potential for fire.
Although the effect global warming will have on streams and forests of
the Southwest is unpredictable, mean annual temperatures in New Mexico
have increased by 0.6 degrees per decade since 1970. Higher
temperatures lead to higher evaporation rates which may reduce the
amount of runoff and groundwater recharge. Increased temperatures may
also increase the extent of area influenced by drought and fire. Large
fires have occurred in the Gila National Forest and subsequent floods
and ash flows have severely affected aquatic life in streams. Although
some of the threats facing the species are ongoing and therefore
imminent (such as livestock and recreational uses), the biggest threats
are nonimminent (such as fire, drought, and increased temperatures).
Therefore, the threats overall are nonimminent. The threats are
moderate to low magnitude because the threats are occurring at low
levels and populations appear to be stable. Therefore, we retained a
listing priority number of 11 for this species.
Gonzales springsnail (Tryonia circumstriata) - See summary above
under Diamond Y Spring snail (Pseudotryonia adamantina).
Huachuca springsnail (Pyrgulopsis thompsoni) - The following is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. The Huachuca
springsnail inhabits approximately 16 springs and cienegas at
elevations of 4,500 to 7,200 feet in southeastern Arizona (14 sites)
and adjacent portions of Sonora, Mexico (2 sites). The springsnail is
typically found in the shallower areas of springs or cienegas, often in
rocky seeps at the spring source. Ongoing threats include habitat
modification and destruction through catastrophic wildfire, drought,
streamflow alteration, and, potentially, grazing, recreation, military
activities, and timber harvest. Overall, the threats are moderate in
magnitude because threats are not occurring throughout the range of the
species uniformly and not all populations would likely be impacted
simultaneously by any of the known threats. In addition, multiple
landowners (Forest Service, Fort Huachuca, The Nature Conservancy) are
including consideration for the springsnail or other co-occurring
listed species in their activities. The threats are ongoing and, thus,
imminent. Therefore, we have assigned an LPN of 8 to this species.
New Mexico springsnail (Pyrgulopsis thermalis) - We have not
updated our assessment for this species, as we are currently developing
a proposed listing rule.
Page springsnail (Pyrgulopsis morrisoni) - The following summary is
based on information contained in our files. No new information was
provided in the petition received on May 11, 2004. The Page springsnail
is known to exist only within a complex of springs located within an
approximately 0.93-mi (1.5-km) stretch along the west side of Oak Creek
around the community of Page Springs, and within springs located along
Spring Creek, tributary to Oak Creek, Yavapai County, Arizona. The
primary threat to the Page springsnail is modification for domestic,
agricultural, ranching, fish hatchery, and recreational activities.
Many of the springs where the species occurs have been subjected to
some level of such modification. Arizona Game and Fish Department
management plans for the Bubbling Ponds and Page Springs fish
hatcheries include commitments to replace lost habitat and to monitor
remaining populations of invertebrates such as the Page springsnail. A
draft Candidate Conservation Agreement with Assurances was published
and available for public review and comment on January 28, 2008. Based
on recent survey data, it appears that the Page springsnail is abundant
within natural habitats and persists in modified habitats, albeit at
reduced densities. The magnitude of threats is considered high because
limited distribution of this narrow endemic makes any detrimental
effects from threats likely to result in extirpation or extinction. The
immediacy of the threat of ground water withdrawal is uncertain due to
conflicting information regarding imminence. However, overall, the
threats are imminent because modification of the species' habitat is
currently occurring. Therefore, we retain an LPN of 2 for the Page
springsnail.
Phantom springsnail (Tyronia cheatumi) - See summary above under
Phantom Cave snail (Cochliopa texana).
Three Forks springsnail (Pyrgulopsis trivialis) - We have not
updated our assessment for this species, as we are currently developing
a proposed listing rule.
Insects
Wekiu bug (Nysius wekiuicola) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. The wekiu bug belongs to the
true bug family, Lygaeidae, and is endemic to the island of Hawaii.
This species only occurs on the summit of Mauna Kea and feeds upon
other insect species which are blown to the summit of this large
volcano. The wekiu bug is primarily threatened by the loss of its
habitat from astronomy development. In 2004 and early 2005, surveys
found multiple new locations of the wekiu bug on cinder cones on the
Mauna Kea summit. Several of these cinder cones within the Mauna Kea
Science Reserve, as well as two cinder cones located in the State Ice
Age Natural Area Reserve, are not currently undergoing development nor
are they the site of any planned development. Thus, the threats,
although ongoing, do not occur across the entire range of the wekiu
bug. Because there are occupied locations that are not subject to the
primary threat of astronomy development, the overall magnitude of the
threat is moderate. The immediacy of the threats is imminent because
there are significant parts of the
[[Page 75208]]
wekiu bug's range where ongoing development is occurring. Therefore, we
assigned this species an LPN of 8.
Mariana eight spot butterfly (Hypolimnas octucula mariannensis) -
The following summary is based on information contained in our files.
No new information was provided in the petition we received on May 11,
2004. The Mariana eight spot butterfly is a nymphalid butterfly species
that feeds upon two host plants, Procris pedunculata and Elatostema
calcareum. Endemic to the islands of Guam and Saipan, the species is
now known from ten populations on Guam. This species is currently
threatened by predation and parasitism. The Mariana eight spot
butterfly has extremely high mortality of eggs and larvae due to
predation by alien ants and wasps. Because the threat of parasitism and
predation by nonnative insects occurs range-wide and can cause
significant population declines to this species, they are high in
magnitude. The threats are imminent because they are ongoing.
Therefore, we assigned an LPN of 3 for this subspecies.
Mariana wandering butterfly (Vagrans egestina) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
The Mariana wandering butterfly is a nymphalid butterfly species which
feeds upon a single host plant species, Maytenus thompsonii. Originally
known from and endemic to the islands of Guam and Rota, the species is
now known from one population on Rota. This species is currently
threatened by alien predation and parasitism. The Mariana wandering
butterfly is likely predated on by alien ants and parasitized by native
and nonnative parasitoids. Because the threat of parasitism and
predation by nonnative insects occurs range-wide and can cause
significant population declines to this species, they are high in
magnitude. These threats are imminent because they are ongoing.
Therefore, we assigned an LPN of 2 for this species.
Miami blue butterfly (Cyclargus thomasi bethunebakeri) - The
following summary is based on information contained in our files and in
the petition we received on June 15, 2000. The Miami blue is endemic to
south Florida. Historically, it occurred throughout the Florida Keys,
north to Hillsborough and Volusia Counties. None were reported to be
found between 1996 and 1999. It is presently located at two sites in
the Keys. In 1999, a metapopulation was discovered at Bahia Honda State
Park on Bahia Honda Key and in 2006 a second metapopulation was
discovered on the outer islands of Key West National Wildlife Refuge.
The former appears restricted to several hundred individuals at most,
while the latter likely includes at least 1,500 individuals. Capacity
to expand at either site or successfully emigrate from either site
appears to be very low due to the sedentary nature of the butterfly and
isolation of habitats. Captive propagation and reintroduction efforts
are continuing, but success has yet to be shown. The Miami blue is
predominantly a coastal species, occurring in disturbed and early
successional habitats such as the edges of tropical hardwood hammock,
coastal berm forest, and along trails and other open sunny areas, and
historically in pine rocklands. These habitats provide larval host
plants and adult nectar sources that are required to occur in close
proximity. The primary threats to the subspecies are the limited
population size and range, hurricanes, and mosquito control activities.
In addition, illegal collection may also pose a threat. The threats are
high in magnitude because they occur rangewide and in combination
affect the population levels. Except for hurricanes, the threats are
nonimminent because the current range is within a State park and
National Wildlife Refuge, where the above threats are substantially
controlled. Therefore, we assigned the Miami blue a LPN of 6.
Sequatchie caddisfly (Glyphopsyche sequatchie) - The following
summary is based on information in our files. No new information was
provided in the petition wereceived on May 11, 2004. The Sequatchie
caddisfly is known from two spring runs that emerge from caves in
Marion County, Tennessee - Owen Spring Branch (the type locality) and
Martin Spring run in the Battle Creek system. In 1998, biologists
estimated population sizes at 500 to 5000 individuals for Owen Spring
Branch and 2 to 10 times higher at Martin Spring, due to the greater
amount of apparently suitable habitat. In spite of greater amounts of
suitable habitat at the Martin Spring run, Sequatchie caddisflies are
more difficult to find at this site, and in 2001 (the most recent
survey) the Sequatchie caddisfly was ``abundant'' at the Owen Spring
Branch location, while only two individuals were observed at the Martin
Spring. Threats to the Sequatchie caddisfly include siltation, point
and nonpoint discharges from municipal and industrial activities and
introduction of toxicants during episodic events. These threats,
coupled with the extremely limited distribution of the species, its
apparent small population size, the limited amount of occupied habitat,
ease of accessibility, and the annual life cycle of the species, are
all factors that leave the Sequatchie caddisfly vulnerable to
extirpation. Therefore, the magnitude of the threat is high. These
threats are gradual and/or not necessarily imminent. Based on high-
magnitude, nonimminent threats, we assigned this species a listing
priority number of 5.
Clifton cave beetle (Pseudanophthalmus caecus) - The following
summary is based upon information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Clifton cave beetle is a small, eyeless, reddish-brown predatory insect
that feeds upon small cave invertebrates. It is cave dependent, and is
not found outside the cave environment. Clifton cave beetle is only
known from two privately owned Kentucky caves. Soon after the species
was first collected in 1963 in one cave, the cave entrance was enclosed
due to road construction. We do not know whether the species still
occurs at the original location or if it has been extirpated from the
site by the closure of the cave entrance. Other caves in the vicinity
of this cave were surveyed for the species during a 1995-1996. Only one
additional site was found to support the Clifton Cave beetle. The
limestone caves in which the Clifton cave beetle is found provide a
unique and fragile environment that supports a variety of species that
have evolved to survive and reproduce under the demanding conditions
found in cave ecosystems. The limited distribution of the species makes
it vulnerable to isolated events that would only have a minimal effect
on the more wide-ranging insects. Events such as toxic chemical spills,
discharges of large amounts of polluted water or indirect impacts from
off-site construction activities, closure of entrances, alteration of
entrances, or the creation of new entrances could have serious adverse
impacts on this species. Therefore, the magnitude of threat is high for
this species. The immediacy of threat is nonimminent because there are
no known projects planned that would affect the species in the near
future. We therefore have assigned a listing priority number of 5 to
this species.
Icebox cave beetle (Pseudanophthalmus frigidus) - The following
summary is based upon information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Icebox cave beetle is a small, eyeless, reddish-brown predatory insect
that feeds upon small cave invertebrates. It
[[Page 75209]]
is not found outside the cave environment, and is only known from one
privately owned Kentucky cave. The limestone cave in which this species
is found provides a unique and fragile environment that supports a
variety of species that have evolved to survive and reproduce under the
demanding conditions found in cave ecosystems. The species has not been
observed since it was originally collected, but species experts believe
that it may still exist in the cave in low numbers. The limited
distribution of the species makes it vulnerable to isolated events that
would only have a minimal effect on the more wide-ranging insects.
Events such as toxic chemical spills or discharges of large amounts of
polluted water, or indirect impacts from off-site construction
activities, closure of entrances, alteration of entrances, or the
creation of new entrances, could have serious adverse impacts on this
species. Therefore, the magnitude of threat is high for this species
because it is limited in distribution and the threats would result in
mortality or reduced reproductive capacity. The immediacy of threat is
nonimminent because there are no known projects planned that would
affect the species in the near future. We therefore have assigned an
LPN of 5 to this species.
Inquirer cave beetle (Pseudanophthalmus inquisitor) - The following
summary is based upon information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
The inquirer cave beetle is a fairly small, eyeless, reddish-brown
predatory insect that feeds upon small cave invertebrates. It is not
found outside the cave environment, and is only known from one
privately owned Tennessee cave. The limestone cave in which this
species is found provides a unique and fragile environment that
supports a variety of species that have evolved to survive and
reproduce under the demanding conditions found in cave ecosystems. The
species was last observed in 2006. The limited distribution of the
species makes it vulnerable to isolated events that would only have a
minimal effect on the more wide-ranging insects. The area around the
only known site for the species is in a rapidly expanding urban area.
The entrance to the cave is protected by the landowner through a
cooperative management agreement with the Service, The Nature
Conservancy and Tennessee Wildlife Resources Agency; however, a
sinkhole that drains into the cave system is located away from the
protected entrance and is near a highway. Events such as toxic chemical
spills, discharges of large amounts of polluted water or indirect
impacts from off-site construction activities could adversely affect
the species and the cave habitat. The magnitude of threat is high for
this species because it is limited in distribution and the threats
would have negative impacts on its continued existence. The threats are
nonimminent because there are no known projects planned that would
affect the species in the near future and it receives some protection
under a cooperative management agreement. We therefore have assigned a
listing priority number of 5 to this species.
Louisville cave beetle (Pseudanophthalmus troglodytes) - The
following summary is based upon information contained in our files. No
new information was provided in the petition we received on May 11,
2004. The Louisville cave beetle is a small, eyeless, reddish-brown
predatory insect that feeds upon cave invertebrates. It is not found
outside the cave environment, and is only known from two privately
owned Kentucky caves. The limestone caves in which this species is
found provide a unique and fragile environment that supports a variety
of species that have evolved to survive and reproduce under the
demanding conditions found in cave ecosystems. The limited distribution
of the species makes it vulnerable to isolated events that would only
have a minimal effect on the more wide-ranging insects. Events such as
toxic chemical spills, discharges of large amounts of polluted water or
indirect impacts from off-site construction activities, closure of
entrances, alteration of entrances, or the creation of new entrances
could have serious adverse impacts on this species. The magnitude of
threat is high for this species, because it is limited in distribution
and the threats would have negative impacts on the species. The
immediacy of threat is nonimminent because there are no known projects
planned that would affect the species in the near future. We therefore
have assigned an LPN of 5 to this species.
Tatum Cave beetle (Pseudanophthalmus parvus) - The following
summary is based upon information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Tatum Cave beetle is a small, eyeless, reddish-brown predatory insect
that feeds upon cave invertebrates. It is not found outside the cave
environment, and is only known from one privately owned Kentucky cave.
The limestone cave in which this species is found provides a unique and
fragile environment that supports a variety of species that have
evolved to survive and reproduce under the demanding conditions found
in cave ecosystems. The species has not been observed since 1965, but
species experts believe that it still exists in low numbers. The
limited distribution of the species makes it vulnerable to isolated
events that would only have a minimal effect on the more wide-ranging
insects. Events such as toxic chemical spills or discharges of large
amounts of polluted water, or indirect impacts from off-site
construction activities, closure of entrances, alteration of entrances,
or the creation of new entrances could have serious adverse impacts on
this species. The magnitude of threat is high for this species, because
its limited numbers mean that any threats could affect its continued
existence. The immediacy of threat is nonimminent because there are no
known projects planned that would affect the species in the near
future. We therefore have assigned an LPN of 5 to this species.
Taylor's (Whulge, Edith's) checkerspot butterfly (Euphydryas editha
taylori) - The following summary is based on information contained in
our files and in the petition received on December 11, 2002.
Historically, the Taylor's checkerspot butterfly was known from 70
locations: 23 in British Columbia, 34 in Washington, and 13 in Oregon.
Based on surveys during the 2008 flight period, 11 populations are now
known, with a total of about 2,500 to 3,000 individuals observed
rangewide. Currently, eight populations are known from Washington, two
in the Willamette Valley of Oregon and one on Denman Island, British
Columbia, Canada.
Threats include degradation and destruction of native grasslands
due to agriculture; residential and commercial development;
encroachment by nonnative plants; succession from grasslands to native
shrubs and trees; and fire. The grassland ecosystem on which this
subspecies depends requires annual management to maintain suitable
grassland habitat for the species. The application of Bacillus
thuringiensis var. kurstake (Btk) for Asian gypsy moth control was
routinely applied in Pierce County, Washington for many years. This
pesticide is documented to have deleterious effects on non-target
lepidopteron species, including all moths and butterflies. Because of
the timing and close proximity of the Btk application to native
prairies where Taylors' checkerspot adults, or their larvae, were
historically known to occur, it is likely that the spraying contributed
to the
[[Page 75210]]
extirpation of the subspecies at three locations in Pierce County,
Washington.
Threats also include the loss of prairies to development or the
conversion of native grasslands to agriculture; the threat of vehicle
and foot traffic that crushes larvae and larval host plants on roads
where host plants have become established, thus acting as a mortality
sink at north Olympic Peninsula sites. Other important threats include
changes to the structure and composition of prairie habitat brought on
by the invasion of shrubs and trees (Scot's broom and Douglas-fir) or
nonnative pasture grasses that quickly invade onto prairies when
processes like fire, or its surrogate mowing, are not implemented.
These changes to prairie habitat threaten Taylor's checkerspot by
degrading prairie habitat and making it unsuitable for the butterfly.
The threats that lead to habitat degradation and loss are ubiquitous,
occurring rangewide, and affect the survival of the subspecies.
Therefore, they are high in magnitude. The threats are imminent because
they are ongoing and occur simultaneously at all of the known locations
for the subspecies. Based on the high magnitude and the imminent nature
of threats, we assigned the Taylor's checkerspot butterfly a listing
priority number of 3.
Blackline Hawaiian damselfly (Megalagrion nigrohamatum
nigrolineatum) - We have not updated our assessment for this species,
as we are currently developing a proposed listing rule.
Crimson Hawaiian damselfly (Megalagrion leptodemas) - We have not
updated our assessment for this species, as we are currently developing
a proposed listing rule.
Flying earwig Hawaiian damselfly (Megalagrion nesiotes) - We have
not updated our assessment for this species, as we are currently
developing a proposed listing rule.
Oceanic Hawaiian damselfly (Megalagrion oceanicum) - We have not
updated our assessment for this species, as we are currently developing
a proposed listing rule.
Orangeblack Hawaiian damselfly (Megalagrion xanthomelas) - The
following summary is based on information contained in our files. No
new information was provided in the petition we received on May 11,
2004. The orangeblack Hawaiian damselfly is a stream-dwelling species
endemic to the Hawaiian Islands of Kauai, Oahu, Molokai, Maui, Lanai,
and Hawaii. The species no longer is found on Kauai, and is now
restricted to 16 populations on the islands of Oahu, Maui, Molokai,
Lanai, and Hawaii. This species is threatened by predation from alien
aquatic species such as fish and predacious insects and habitat loss
through dewatering of streams and invasion by nonnative plants.
Nonnative fish and insects prey on the naiads of the damselfly, and
loss of water reduces the amount of suitable naiad habitat available.
Invasive plants (e.g., California grass (Brachiaria mutica)) also
contribute to loss of habitat by forming dense, monotypic stands that
completely eliminate any open water. Nonnative fish and plants are
found in all the streams the orangeblack damselfly occur in, except the
Oahu location, where there are no nonnative fish. We assigned this
species an LPN of 8 because, although the threats are ongoing and
therefore imminent, they affect the survival of the species in varying
degrees throughout the range of the species and are of moderate
magnitude.
Pacific Hawaiian damselfly (Megalagrion pacificum) - We have not
updated our assessment for this species, as we are currently developing
a proposed listing rule.
Picture-wing fly (Drosophila digressa) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004, but new
information was provided by one Drosophila expert in 2006. This
picture-wing fly, a member of the family Drosophilidae, feeds only upon
species of Charpentiera, and is endemic to the Hawaiian Island of
Hawaii. Never abundant in number of individuals observed, D. digressa
was originally known from 5 population sites and may now be limited to
as few as 1 or 2 sites. Due to the small population size of the species
and its small known habitat area, Drosophila researchers believe this
species and its habitat are particularly vulnerable to a myriad of
threats. Feral ungulates (pigs, goats, and cattle) degrade and destroy
D. digressa host plants and habitat by directly trampling plants,
facilitating erosion, and spreading nonnative plant seeds. Nonnative
plants degrade host plant habitat and compete for light, space, and
nutrients. Direct predation of D. digressa by nonnative social insects,
particularly yellow jacket wasps, is also a serious threat.
Additionally, this species faces competition at the larval stage from
nonnative tipulid flies, which feed within the same portion of the
decomposing host plant area normally occupied by the D. digressa larvae
during their development with a resulting reduction in available host
plant material. The threats to the native forest habitat of D.
digressa, and to individuals of this species, occur throughout its
range and are expected to continue or increase unless efforts at
control or eradication are undertaken. In additions, because of the
limited distribution and small population of the species, any of the
threats would significantly impair survival of the species. The threats
are also imminent, because they are ongoing. No known conservation
measures have been taken to date to specifically address these threats,
and we have therefore assigned this species an LPN of 2.
Stephan's riffle beetle (Heterelmis stephani) - The following
summary is based on information contained in our files. No new
information was provided in the petition received on May 11, 2004. The
Stephan's riffle beetle is an endemic riffle beetle found in limited
spring environments within the Santa Rita Mountains, Pima County,
Arizona. The beetle is known from Sylvester Springs in Madera Canyon,
within the Coronado National Forest. These springs are typical
isolated, mid-elevation, permanently saturated, spring-fed aquatic
climax communities commonly referred to as cienegas. Threats are
largely from habitat modification (from recreational activities in the
springs and changes in water chemistry due to catastrophic natural
disasters such as fires or floods). The threats to be of moderate to
low magnitude based on our current knowledge of the permanence of
threats and the likelihood that the species will persist in areas that
are unaffected by the threats. Because the threats from recreational
activities are currently occurring, they are imminent. Therefore, we
assigned a LPN of 8 to the Stephan's riffle beetle.
Casey's junebeetle (Dinacoma caseyi) - We have not updated our
assessment for this species, as we are currently developing a proposed
listing rule.
Dakota skipper (Hesperia dacotae) - The following summary is based
on information contained in our files, including information from the
petition received on May 12, 2003. The Dakota skipper is a small- to
mid-sized butterfly that inhabits high-quality tallgrass and mixed
grass prairie in Minnesota, North Dakota, South Dakota, and the
provinces of Manitoba and Saskatchewan in Canada. The species is
presumed to be extirpated from Iowa and Illinois and from many sites
within occupied States.
The species is threatened by conversion of its native prairie
habitat for agricultural purposes, overgrazing, invasive species,
gravel mining, inbreeding, population isolation, and, in some cases,
prescribed fire. Prairie succeeds to shrubland or forest without
[[Page 75211]]
periodic fire, grazing, or mowing; thus, the species is also threatened
at sites where such management practices are not applied. We, other
agencies, and private organizations (e.g., The Nature Conservancy)
protect and manage some Dakota skipper sites. Although proper
management is always necessary to ensure its persistence, even at
protected sites, it is secure at some sites owned by these entities.
The species is also secure at some sites where private landowners
manage native prairie in ways that conserve Dakota skipper. Despite
these protections, recent surveys in at least parts of the species'
range have led us to view threats to Dakota skipper as being more
imminent than we previously believed. In January 2007, for example,
Minnesota Department of Natural Resources proposed (although, it did
not finalize) revising the status of Dakota skipper in the state from
threatened to endangered because it ``appears to be rapidly
disappearing from remnant habitat.'' In addition, approximately half of
the inhabited sites are privately owned with little or no protection.
Ongoing threats on these sites include invasive species, overgrazing,
and herbicide applications. A few private sites are protected from
conversion by easements, but these do not prevent adverse effects from
overgrazing. Overall, the threats are moderate in magnitude because
they are not occurring rangewide. They are, however, ongoing and
therefore imminent, particularly on private lands. We assigned an LPN
of 8 to this species.
Mardon skipper (Polites mardon) - See above in ``Summary of Listing
Priority Changes in Candidates.'' The above summary is based on
information contained in our files and the petition we received on
December 24, 2002.
Coral Pink Sand Dunes tiger beetle (Cicindela limbata albissima) -
See above in ``Summary of Listing Priority Changes in Candidates.'' The
above summary is based on information contained in our files, including
information from the petition we received on April 21, 1994.
Highlands tiger beetle (Cicindela highlandensis) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
The Highlands tiger beetle is narrowly distributed and restricted to
areas of bare sand within upland oak scrub and pine vegetation on
ancient sand dunes of the Lake Wales Ridge in Polk and Highlands
Counties, Florida. Adult tiger beetles have been found at 40 sites from
near Haines City south to Josephine Creek. In 2004-2005 surveys, a
total of 1,574 adults were found at 40 sites, compared with 643 adults
at 31 sites in 1996, 928 adults at 31 sites in 1995, and 742 adults at
21 sites in 1993. Of the 40 sites in the 2004-2005 surveys with one or
more adults, results ranged from 3 sites with large populations of over
100 adults, to 13 sites with fewer than 10 adults. Results from a
limited removal study at four sites suggest that the actual population
size at the various survey sites is likely to be as much as two times
as high as indicated by the visual index counts.
Lack of fire to create open sand, pesticide use, small population
sizes, and over-collecting pose serious threats to this species.
Because this species is narrowly distributed with specific habitat
requirements and small populations, any of the threats could have a
significant impact on the survival of the species. Therefore, the
magnitude of threats is high. Although the majority of its historic
range has been lost, degraded, and fragmented, numerous sites are
protected and land managers are implementing prescribed fire, which are
expected to restore habitat and help reduce threats and have already
helped stabilize and somewhat improve the populations. Overall, the
threats are nonimminent. Therefore, we assigned the Highlands tiger
beetle an LPN of 5.
Arachnids
Warton cave meshweaver (Cicurina wartoni) - The following summary
is based on information contained in our files. No new information was
provided in the petition received on May 11, 2004. Warton Cave
meshweaver is an eyeless, cave-dwelling, unpigmented, 0.25 inch long
invertebrate known only from female specimens. This meshweaver is known
to occur in only one cave, Pickle Pit, in Travis County, Texas. Primary
threats to the species and its habitat are predation and competition
from fire ants, surface and subsurface effects from runoff from an
adjacent subdivision, unauthorized entry into the area surrounding the
cave, modification of vegetation near the cave from human use, and
trash dumping which may include toxic materials near the feature. The
magnitude of threats is high because the single location for this
species makes it highly vulnerable to extinction from the identified
threats. The threats are imminent because fire ants are known to occur
in the vicinity of the cave, and impacts to the cave from runoff and
human activities are an imminent threat. Thus, we assign an LPN of 2 to
this species.
Crustaceans
Anchialine pool shrimp (Metabetaeus lohena) - The following summary
is based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. Metabetaeus
lohena is an anchialine pool-inhabiting species of shrimp belonging to
the family Alpheidae. This species is endemic to the Hawaiian Islands
and is currently known from populations on the islands of Oahu, Maui,
and Hawaii. The primary threats to this species are predation by fish
(which do not naturally occur in the pools inhabited by this species)
and habitat loss from degradation. The pools where this species occurs
on the islands of Maui and Hawaii are located within State Natural Area
Reserves (NAR). Hawaii's State statutes prohibit the collection of the
species and the disturbance of the pools in State NARs. However,
enforcement of collection and disturbance prohibitions is difficult,
and the negative effects from the introduction of fish are extensive
and happen quickly. In addition, the pools where this species occurs on
the island of Oahu do not receive protection from collection of the
species or disturbance of the pools. Therefore, threats to this species
have a significant adverse effect on the survival of the species, and
are of a high magnitude. However, the primary threats of predation from
fish and loss of habitat due to degradation are nonimminent overall,
because on the islands of Maui and Hawaii no fish were observed in any
of the pools where this species occurs and there has been no documented
dumping in these pools. Only one site on Oahu had a dumping instance,
and in that case the dumping was cleaned up immediately and the species
subsequently observed. No additional dumping events are known to have
occurred. Therefore, we assigned this species an LPN of 5.
Anchialine pool shrimp (Palaemonella burnsi) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Palaemonella burnsi is an anchialine pool-inhabiting species of shrimp
belonging to the family Palaemonidae. This species is endemic to the
Hawaiian Islands and is currently known from three populations on the
island of Maui and one population on the island of Hawaii. The primary
threats to this species are predation by fish (which do not naturally
occur in the pools inhabited by this species) and habitat loss due to
degradation. The pools
[[Page 75212]]
where this species occurs on Maui are located within a State Natural
Area Reserve (NAR). Hawaii's State statutes prohibit the collection of
the species and the disturbance of the pools in State NARs. On the
island of Hawaii, the species occurs within a National Park, and
collection and disturbance are also prohibited. However, enforcement of
these prohibitions is difficult, and the negative effects from the
introduction of fish are extensive and happen quickly. Therefore,
threats to this species have a significant adverse effect on the
survival of the species, and are of a high magnitude. However, the
threats are nonimminent, because surveys in 2004 and 2007 did not find
fish in the pools where these shrimp occur on Maui or the island of
Hawaii. Also, there was no evidence of recent habitat degradation at
those pools. We assigned this species an LPN of 5.
Anchialine pool shrimp (Procaris hawaiana) - The following summary
is based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. Procaris hawaiana
is an anchialine pool-inhabiting species of shrimp belonging to the
family Procarididae. This species is endemic to the Hawaiian Islands,
and is currently known from two populations on the island of Maui and
one population on the island of Hawaii. The primary threats to this
species are predation from fish (which do not naturally occur in the
pools inhabited by this species) and habitat loss due to degradation.
The pools where this species occurs on Maui are located within a State
Natural Area Reserve (NAR). Hawaii's State statutes prohibit the
collection of the species and the disturbance of the pools in State
NARs. However, enforcement of these prohibitions is difficult and the
negative effects from the introduction of fish are extensive and happen
quickly. In addition, there are no conservation efforts underway to
alleviate the potential for any of these threats in the one pool on the
island of Hawaii. Therefore, threats to this species have a significant
adverse effect on the survival of the species, and thus remain at a
high magnitude. However, the threats to the species are nonimminent
because, during 2004 and 2007 surveys, no fish were observed in the
pools where these shrimp occur on Maui, and no fish were observed in
the one pool on the island of Hawaii during a site visit in 2005. In
addition, there were no signs of dumping or fill in any of the pools
where the species occurs. Therefore, we assigned this species an LPN of
5.
Anchialine pool shrimp (Vetericaris chaceorum) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Vetericaris chaceorum is an anchialine pool-inhabiting species of
shrimp belonging to the family Procarididae; it is the only species in
its genus. This species is endemic to the Hawaiian Islands, and is only
known from one population in a single pool on the island of Hawaii. The
primary threats to this species are predation from nonnative fish and
habitat degradation and contamination from illegal trash dumping. This
species would be highly vulnerable to predation by any intentionally or
accidentally introduced fish, or contamination from illegal dumping
into its single known location. This pool lies within lands
administered by the State of Hawaii Department of Hawaiian Home Lands.
The threats to V. chaceorum from habitat degradation and destruction,
as well as from predation by nonnative fish are of high magnitude,
because this species occurs in only one pool; thus the threats could
significantly impair the survival of the species. All individuals of
this species may be adversely impacted by a single dumping of trash or
release of nonnative fish in its only known pool. However, the threats
are nonimminent, as fish have not been introduced into the pool (nor is
there any reason to believe that introduction is imminent) and a site
visit in early 2005 showed there were no signs of dumping or fill.
Therefore we assigned this species an LPN of 4 because the threats are
of high magnitude but nonimminent, and the species is in a monotypic
genus.
Troglobitic groundwater shrimp (Typhlatya monae) - The following
summary is based on information contained in our files including
information from the petition we received on May 11, 2004. The
troglobitic groundwater shrimp is a subterranean small shrimp known
from Puerto Rico, Barbuda, and Dominican Republic. It is classified as
a troglobite, or obligatory cave organism, of which its most
extraordinary feature is the reduction or loss of vision and
pigmentation. Members of the species feed on organic waste material and
debris, such as bat guano. Little is known concerning the status of the
species in either Barbuda or Dominican Republic. Although in Puerto
Rico this species was previously found at Mona Island, currently it is
known from only three caves within the Gu[aacute]nica Commonwealth
Forest in the municipalities of Gu[aacute]nica, Yauco, and Guayanilla.
However, the species may still be found in the reef deposit aquifers in
Mona Island that have not yet been surveyed. In 1995, close to 2,000
individuals were estimated; over 95% of these were observed in only one
cave. Although no systematic censuses have been conducted since 1995,
the Service recently documented the presence of the species in all
three caves and obtained information from Puerto Rico Commonwealth
Forest personnel regarding another cave in which the species may occur.
Changes in groundwater quality, collection of rare animals,
predation, limited distribution of the species, limited availability of
appropriate habitat (i.e., underground aquifers within cave
formations), potential reduction of food sources (e.g., mortality or
reduction in bat populations), and low population numbers, potentially
threaten populations of the troglobitic groundwater shrimp. However,
because the known range of the species is within protected lands, and
based on available information of known management activities within
the Gu[aacute]nica Commonwealth Forest or Mona Island, the magnitude of
the remaining threats, possible extraction of ground-water in Mona and
vulnerability to catastrophic events, is moderate to low. The threats
are not currently occurring, and therefore are nonimminent. We continue
to assign a LPN of 11 to this species.
Flowering plants
Abronia alpina (Ramshaw Meadows sand-verbena) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Abronia alpina is a small perennial herb, 2.5 to 15.2 centimeters (1 to
6 inches) across, forming compact mats with lavender-pink, trumpet-
shaped, and generally fragment flowers. Abronia alpina is known from
one main population center in Ramshaw Meadow on the Kern Plateau of the
Sierra Nevada, California and from one subpopulation found in adjacent
Templeton Meadow. The total estimated area occupied is approximately 6
hectares (15 acres). The population fluctuates from year to year
without any clear trends. Population estimates from 1985-1994 range
from a low of 69,652 plants in 1986 to 132,215 plants in 1987. Surveys
conducted since 1994 indicate that no significant changes have occurred
in population size or location, although the 2003 survey showed
population numbers to be at the low end of the range. The population
was last monitored in 2007.
[[Page 75213]]
The factors threatening Abronia alpina include natural and human
alteration of habitat, hydrologic changes to the water table, and
recreational use within meadow habitats. Lodgepole pine encroachment
has altered the meadow and trees are becoming established within A.
alpina habitat. Lodgepole pine encroachment may alter soil
characteristics by increasing organic matter levels, decreasing
porosity, and moderating diurnal temperature fluctuations thus reducing
the competitive ability of A. alpina to persist in an environment more
hospitable to other plant species. The Ramshaw Meadow ecosystem is
subject to potential alteration by lowering of the water table due to
downcutting of the South Fork of the Kern River (SFKR). The SFKR flows
through Ramshaw Meadow, at times coming within 15 m (50 ft) of A.
alpina habitat, particularly in the vicinity of five subpopulations.
The habitat occupied by A. alpina directly borders the meadow system
supported by the SFKR. Drying out of the meadow system could
potentially affect A. alpina pollinators and/or seed dispersal agents.
Established hiker, packstock, and cattle trails pass through A. alpina
subpopulations. Two main hiker trails pass through Ramshaw Meadow, but
were rerouted out of A. alpina subpopulations where feasible, in 1988
and 1997. Remnants of cattle trails that pass through subpopulations in
several places receive occasional incidental use by horses and
sometimes hikers. Cattle use, however, currently, is not a threat due
to the 2001 implementation of a ten year moratorium on the Templeton
allotment which prohibits cattle from all A. alpina locations. The
Service is funding studies to determine appropriate conservation
measures and working with the U.S. Forest Service on developing a
conservation strategy for the species. The threats are of a low
magnitude and nonimminent because of the conservation actions already
implemented. Therefore, we assigned a LPN of 11 to this species.
Arabis georgiana (Georgia rockcress) - The following summary is
based on information in our files. No new information was provided in
the petition we received on May 11, 2004. The Georgia rockcress grows
in a variety of dry situations, including shallow soil accumulations on
rocky bluffs, ecotones of gently sloping rock outcrops, and in sandy
loam along eroding river banks. It is occasionally found in adjacent
mesic woods, but it will not persist in heavily shaded conditions.
Currently, approximately 20 populations are known from the Gulf Coastal
Plain, Piedmont, and Ridge and Valley physiographic provinces of
Alabama and Georgia. Populations of this species typically have a
limited number of individuals over a small area. Habitat degradation,
more than outright habitat destruction, is the most serious threat to
the continued existence of this species. Disturbance, associated with
timber harvesting, road building, and grazing has created favorable
conditions for the invasion of exotic weeds, especially Japanese
honeysuckle (Lonicera japonica), in this species' habitat. A large
number of the populations are currently or potentially threatened by
the presence of exotics. The heritage programs in Alabama and Georgia
have initiated plans for exotic control at several populations. The
magnitude of threats to this species is considered to be moderate to
low due to the number of populations (20) across multiple counties in
two states and due to the fact that several sites are protected.
However, since a number of the populations are currently being affected
by nonnative plants, the threat is imminent. Thus, we assigned an LPN
of 8 to this species.
Argythamnia blodgettii (Blodgett's silverbush) - The following
summary is based on information in our files. No new information was
provided in the petition we received on May 11, 2004. Blodgett's
silverbush occurs in Florida and is found in open, sunny areas in pine
rockland, edges of rockland hammock, edges of coastal berm, and
sometimes disturbed areas at the edges of natural areas. Plants can be
found growing from crevices on limestone, or on sand. The pine rockland
habitat where the species occurs in Miami-Dade County and the Florida
Keys requires periodic fires to maintain habitat with a minimum amount
of hardwoods. There are approximately 27 extant occurrences, 12 in
Monroe County and 15 in Miami-Dade County; many occurrences are on
conservation lands. However, 4-5 sites are recently thought to be
extirpated. The estimated population size of Blodgett's silverbush in
the Florida Keys, excluding Big Pine Key, is roughly 11,000; the
estimated population in Miami-Dade County is 375 to 13,650 plants.
Blodgett's silverbush is threatened by habitat loss, which is
exacerbated by habitat degradation due to fire suppression, the
difficulty of applying prescribed fire to pine rocklands, and threats
from exotic plants. Remaining habitats are fragmented. Threats such as
road maintenance and enhancement, infrastructure, and illegal dumping
threaten some populations. Blodgett's silverbush is vulnerable to
natural disturbances, such as hurricanes, tropical storms, and storm
surges. Climatic change, particularly sea level rise, is a long-term
threat that is expected to continue to affect pine rocklands and
ultimately reduce the extent of available habitat, especially in the
Keys. Overall, the magnitude of threats is moderate because not all of
the populations are affected by the threats and the species has a
relatively large population size. In addition, land managers are aware
of the threats from exotic plants and lack of fire, and are, to some
extent, working to reduce this threat where possible. While some of the
threats are occurring in some areas, the threat from development is
nonimminent since most of the populations are on public land and sea-
level rise is not currently affecting this species. Overall, the
threats are nonimminent. Thus, we assigned an LPN of 11 to this
species.
Artemisia campestris var. wormskioldii (Northern wormwood) - The
following summary is based on information contained in our files. No
new information was provided in the petition we received on May 11,
2004. Historically known from eight sites, northern wormwood is
currently known from two populations in Klickitat and Grant Counties,
Washington. This plant is restricted to exposed basalt, cobbly-sandy
terraces, and sand habitat along the shore and on islands in the
Columbia River. The two sites are separated by 200 miles (322
kilometers) of the Columbia River and three large hydroelectric dams.
The Klickitat County population is declining; the status is unclear for
the Grant County population; however, both are vulnerable to
environmental variability. Surveys have not detected any additional
plants.
Threats to northern wormwood include direct loss of habitat through
regulation of water levels in the Columbia River and placement of
riprap along the river bank; trampling of plants as a result of
recreational use; competition with nonnative invasive species; burial
by wind and water-borne sediments; small population sizes;
susceptibility to genetic drift and inbreeding; and the potential for
hybridization with two other species of Artemisia. Ongoing conservation
actions have reduced trampling, but have not eliminated or reduced the
other threats at the Grant County site. The magnitude of threat is high
for this subspecies because the only two remaining populations are
widely separated and distributed such that one or both populations
could be eliminated by a
[[Page 75214]]
single disturbance. The threats are imminent because recreational use
is ongoing, invasive nonnative species occur at both sites, erosion of
the substrate is ongoing at the Klickitat County site, and high water
flows are random, naturally occurring events that may occur
unpredictably in any year. Therefore, we have retained an LPN of 3 for
this subspecies.
Astragalus tortipes (Sleeping Ute milkvetch) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Sleeping Ute milkvetch is a perennial plant that grows only on the
Smokey Hills layer of the Mancos Shale Formation on the Ute Mountain
Ute Indian Reservation in Montezuma County, Colorado. In 2000, 3,744
plants were recorded at 24 locations covering 500 acres within an
overall range of 64,000 acres. Available information from 2000
indicates that the species remains stable. Previous and ongoing threats
from borrow pit excavation, off-highway vehicles, irrigation canal
construction, and a prairie dog colony have had minor impacts that
reduced the range and number of plants by small amounts. Off-highway
vehicle use of the habitat is reportedly increasing. Oil and gas
development is active in the general area, but the Service has received
no information from the Tribe to indicate whether there is development
within the habitat for the plants. The Tribe reported this year that
the status of the species remains unchanged, and that a management plan
for the species is currently in draft form. The threats are moderate in
magnitude, since they have had minor impacts and, based on information
we have, the population appears to be stable. While ORV use is
currently occurring at a rate that causes minor impacts and may be
increasing, oil and gas production is not known to currently occur in
the areas where this species exists. Overall, we conclude threats are
nonimminent. Therefore, we assigned an LPN of 11 to this species.
Bidens amplectens (Kookooalu) - We have not updated our assessment
for this species, as we are currently developing a proposed listing
rule.
Bidens campylotheca ssp. pentamera (Kookooalu) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
This subspecies is an erect, perennial herb found in Cheirodendron-
Metrosideros (olapa-ohia) montane wet forest on Maui, Hawaii. This
subspecies is known from four populations with a total of approximately
180 individuals. Bidens campylotheca ssp. pentamera is threatened by
feral pigs that degrade and destroy habitat, and by nonnative plants
that compete for habitat. Feral pigs have been fenced out of one
population at Kipahulu. These ongoing conservation efforts (fencing and
nonnative plant removal) benefit only one of the four known populations
as the remaining populations on east and west Maui are still affected
by these threats. Habitat destruction and nonnative plants continue to
be high-magnitude threats, because they threaten the continued
existence of this subspecies. In addition, threats to B. campylotheca
ssp. pentamera are imminent because they are ongoing in three
populations. Therefore, we retained an LPN of 3 for this subspecies.
Bidens campylotheca ssp. waihoiensis (Kookooalu) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Bidens campylotheca ssp. waihoiensis is an erect, perennial herb found
in wet Acacia-Metrosideros (koa-ohia) forest on Maui, Hawaii. Bidens
campylotheca ssp. waihoiensis is known from two populations, totaling
300 to 350 individuals. It is threatened by feral pigs and cattle,
which eat this plant and degrade and destroy habitat, and by nonnative
plants that outcompete and displace it. Conservation measures such as
strategic fences and control of nonnative plants benefit the plants in
Kipahulu Valley; however, the individuals in Waihoi Valley are still
affected by these threats. Since foraging and habitat destruction
result in direct mortality, they pose a high-magnitude threat to the
small populations. They are also a imminent threat because they are
ongoing in the Wahoi Valley. Therefore, we retained an LPN of 3 for
this subspecies.
Bidens conjuncta (Kookooalu) - The following summary is based on
information in our files. No new information was provided in the
petition we received on May 11, 2004. Bidens conjuncta is an erect,
perennial herb found in Metrosideros-Dicranopteris-Cheirodendron (ohia-
uluhe-olapa) lowland to montane wet forest and shrubland on Maui,
Hawaii. Eight populations are known, totaling fewer than 3,000
individuals, scattered throughout upper elevation drainages of west
Maui. Although the overall range of the species has not changed, the
number of individuals has declined over the last decade or so. This
species is threatened by pigs that degrade and destroy habitat, and eat
vegetative parts and fruit of B. conjuncta, and by nonnative plants
that outcompete and displace it. Feral pigs have been fenced out of the
lower elevation populations in the west Maui mountains and in the
summit areas and nonnative plants have been greatly reduced in the
fenced areas. Because these conservation efforts have alleviated the
threats in several portions of the range, the magnitude of the threats
are moderate. However, these threats are imminent because they are
still ongoing in portions of this species range. Therefore, we retained
an LPN of 8 for this species.
Bidens micrantha ssp. ctenophylla (Kookooalu) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
This subspecies is an erect, perennial herb found in open mixed
shrubland to dry Metrosideros (ohia) forest on the island of Hawaii,
Hawaii. This subspecies is endemic to the island of Hawaii, where it is
restricted to an area of less than 10 square miles (26 square
kilometers). Bidens micrantha ssp. ctenophylla is known from four wild
and four outplanted populations totaling approximately 130 to 140
individuals, the majority of which occur in only two (wild)
populations. This subspecies is threatened by fire and nonnative
plants, and two populations are threatened by residential and
commercial development. The threats to B. micrantha ssp. ctenophylla
from fire and nonnative plants are of a high magnitude and imminent
because they are occurring range-wide, they threaten the continued
existence of the species, and no efforts for their control have been
undertaken. In addition, two populations are also threatened by
development. Therefore, we retained an LPN of 3 for this subspecies.
Brickellia mosieri (Florida brickell-bush) - The following summary
is based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. This species is
restricted to pine rocklands of Miami-Dade County, Florida. This
habitat requires periodic prescribed fires to maintain the low
understory and prevent encroachment by native tropical hardwoods and
exotic plants, such as Brazilian pepper. Only one large population is
known to exist, plus 18 other occurrences each containing less than 100
individuals. Ten of these occurrences are on conservation lands. This
species is threatened by habitat loss, which is exacerbated by habitat
degradation due to fire suppression, the difficulty of applying
prescribed fire to pine rocklands, and threats from exotic plants.
Remaining habitats are
[[Page 75215]]
fragmented. The species is vulnerable to natural disturbances, such as
hurricanes, tropical storms, and storm surges. Due to its restricted
range and the small sizes of most isolated occurrences, this species is
vulnerable to environmental (catastrophic hurricanes), demographic
(potential episodes of poor reproduction), and genetic (potential
inbreeding depression) threats. Ongoing conservation efforts includes a
project aimed at facilitating restoration and management of privately
owned pine rockland habitats in Miami-Dade County, and a project funded
in 2008 to restore suitable habitat and reintroduce and establish new
populations of the plants in pine rocklands. The Service is also
pursuing additional habitat restoration projects, which could help
further improve the status of the species. Because of these efforts,
the overall magnitude of threats is moderate. The threats are ongoing
and thus imminent. We assigned this species an LPN of 8.
Calamagrostis expansa (Maui reedgrass) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. This species is a
robust, short-rhizomatous perennial found in wet forest, open bogs, and
bog margins on the islands of Maui and Hawaii, Hawaii. Historically
rare, C. expansa was restricted to wet forest and bogs on Maui. Its
historical status is unknown on Hawaii. Currently, this species is
known from 11 populations totaling approximately 230 individuals on
Maui, and was recently discovered in eight populations totaling
approximately 350 individuals on the island of Hawaii. Calamagrostis
expansa is threatened by pigs that degrade and destroy habitat and by
nonnative plants that outcompete and displace it. Feral pigs have been
fenced out of most of the west Maui populations, and nonnative plants
have been reduced in the fenced areas. However, the threats are not
controlled and are ongoing in the remaining unfenced populations on
Maui and at all of the populations on the island of Hawaii. Therefore,
overall the threats from feral pigs and nonnative plants are of a high
magnitude and imminent for C. expansa, and we retained an LPN of 2 for
this species.
Calamagrostis hillebrandii (Hillebrand's reedgrass) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Calamagrostis hillebrandii is a slender, short-rhizomatous perennial
found in Metrosideros-Machaerina (ohia-uki) montane wet bog or
Metrosideros-Rhynchospora-Oreobolus (ohia-kuolohia-oreobolus) mixed bog
on Maui, Hawaii. This species is known from two populations of fewer
than 2,000 individuals, restricted to the bogs of west Maui. There is
an unconfirmed report of C. hillebrandii from central Molokai. This
species is currently threatened by pigs that degrade and destroy
habitat and nonnative plants that outcompete and displace it. A portion
of one population is protected by an ungulate exclosure fence while the
other population may indirectly benefit from conservation actions for
ungulate control and control of nonnative plants conducted in a nearby
preserve. The threats are imminent because they are ongoing in one of
the two known populations. Because they threaten the continued
existence of the species, the threats are high in magnitude. Therefore,
we retained an LPN of 2 for this species.
Calliandra locoensis (no common name) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. Calliandra
locoensis is a spiny, leguminous shrub currently known from five
localities within the Sus[uacute]a Commonwealth Forest in the
municipalities of Yauco and Sabana Grande, in southwestern Puerto Rico.
Surveys in 2007 estimated 1,600 adult plants with numerous seedlings.
Twenty-five native species of Calliandra have been reported for the
Antilles, three of which are native to Puerto Rico, including C.
locoensis. This species is endemic to Puerto Rico, and was discovered
in 1991 during a study of the flora of the Sus[uacute]a Commonwealth
Forest. It is found on shallow, serpentine soils with low nutrients,
high drainage, and low fertility. Much of the vegetation in the forest
was cut for wood, cultivation, livestock grazing, and charcoal
production, prior to its designation as a public forest. Calliandra
locoensis exhibits a low degree of self-compatibility in pollination
tests. Seeds have short viability period, do not appear to have a
biotic dispersal agent (dispersed by dehiscence (natural bursting
open)), and require mesic conditions for germination, which may be
factors in the species' limited distribution.
The restricted distribution, forest management practices
(accidental trampling, brush clearing, trail maintenance), forest fires
(natural or manmade), and catastrophic natural events (hurricanes,
floods, mudslides), threaten this species. The magnitude of threat to
Calliandra locoensis is high due to its restricted distribution, which
makes it vulnerable to catastrophic events, and apparent low dispersal
capability; and the threats are nonimminent given that the populations
are found within protected lands and there are no known projects or
management activities planned that would destroy the known populations.
Therefore, we assigned an LPN of 5 to this species.
Calochortus persistens (Siskiyou mariposa lily) - The following
summary is based on information contained in our files and the petition
we received on September 10, 2001. The Siskiyou mariposa lily is a
narrow endemic that is restricted to three disjunct ridge tops in the
Klamath-Siskiyou Range on the California-Oregon border. The southern-
most occurrence of this species is comprised of nine separate sites on
approximately 10 hectares (ha) (24.7 acres (ac)) of Klamath National
Forest and privately owned lands that stretch for 6 kilometers (km)
(3.7 miles (mi)) along the Gunsight-Humbug Ridge, Siskiyou County,
California. In 2007, a new occurrence was confirmed in the locality of
Cottonwood Peak and Little Cottonwood Peak, Siskiyou County. The
northern-most occurrence consists of not more than five Siskiyou
mariposa lily plants that were discovered in 1998, on Bald Mountain,
west of Ashland, Jackson County, Oregon.
Major threats include competition and shading by native and
nonnative species fostered by suppression of wild fire; increased fuel
loading and subsequent risk of wild fire; fragmentation by roads, fire
breaks, tree plantations, and radio-tower facilities; maintenance and
construction around radio towers and telephone relay stations located
on Gunsight Peak and Mahogany Point; and soil disturbance, direct
damage, and exotic weed and grass species introduction as a result of
heavy recreational use and construction of fire breaks. Dyer's woad
(Isatis tinctoria), an invasive, nonnative plant that may prevent
germination of Siskiyou mariposa lily seedlings, is now found
throughout the southern-most California occurrence, affecting 75
percent of the known lily habitat on Gunsight-Humbug Ridge. Forest
Service staff and the Klamath-Siskiyou Wildlands Center cite
competition with dyer's woad as a significant and chronic threat to the
survival of Siskiyou mariposa lily.
The combination of restricted range, extremely low numbers (five
plants) in one of three disjunct populations, poor competitive ability,
short seed dispersal distance, slow growth rates, low seed production,
apparently poor survival
[[Page 75216]]
rates in some years, herbivory, and competition from exotic plants
threaten the continued existence of this species. These threats are of
high magnitude because of their potential to negatively affect the
overall survival of the species. Because the threats from herbivory and
competition from exotic plants are not anticipated in the immediate
future, and the threats from low seed production and survival are
longer-term threats, overall the threats are nonimminent. Therefore, we
assigned a listing priority number of 5 to this species.
Calyptranthes estremerae (no common name) - The following summary
is based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. Calyptranthes
estremerae is a small tree from the subtropical moist forest of
northwestern Puerto Rico, in the municipalities of Camuy, Utuado, and
Arecibo. Calyptranthes estremerae was only known from several
individuals found near the recreation area adjacent to the Camuy Caves,
but specimens were later found within the R[iacute]o Abajo Commonwealth
Forest (up to 50 individuals) at a site affected by the construction of
Highway PR 10 in 1995. At the present time, a minimum of 100 specimens
of C. estremerae are estimated for the Rio Abajo Commonwealth Forest
and an undetermined number in the Camuy area. The magnitude of threat
to C. estremerae is high, due to restricted distribution and small
number of individuals, and the potential destruction of specimens and
habitat from catastrophic natural events and the expansion of
recreational facilities. However, these threats are not imminent
because the largest known population of C. estremerae is found within
protected lands, there are no known recreational facility projects
planned that would destroy the sites, and the species can be
transplanted successfully. Therefore, we assigned an LPN of 5 to
Calyptranthes estremerae.
Canavalia pubescens (Awikiwiki) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Awikiwiki is a perennial
climber found in lowland dryland forest on Maui and Lanai, and is
possibly on the island of Niihau, Hawaii. This species is known from
five populations totaling a little over 200 individuals. This species
is threatened by development (Maui), goats (Maui) and axis deer (Maui
and Lanai) that degrade and destroy habitat, and by nonnative plants
that outcompete and displace native plants (both islands). An ungulate
exclosure fence protects six individuals of C. pubescens, and weed
control is ongoing at this location on Maui. This species is
represented in two ex-situ collections. Threats to this species from
feral goats, axis deer, and nonnative plants are ongoing, or imminent,
and of high magnitude because they significantly affect the species
throughout its range. Therefore, we retained an LPN of 2 for this
species.
Castilleja christii (Christ's paintbrush) - The following summary
is based on information contained in our files and the petition we
received on January 2, 2001. Castilleja christii is found in one
population covering approximately 85 ha (220 ac) on the summit of Mount
Harrison in Cassia County, Idaho. This endemic species is considered a
hemiparasite (dependent on the health of their surrounding native plant
community), and it grows in association with subalpine meadow and
sagebrush habitats. The population may be large (greater than 10,000
individual plants); however, the species is considered to be subject to
large variations in annual abundance and an accurate current population
estimate is not available. Monitoring indicates that reproductive stems
per plant and plant density declined between 1995 and 2007. The primary
threat to the species is the nonnative invasive plant smooth brome
(Bromus inermis). Despite cooperative Forest Service and Service
efforts to control smooth brome in 2005, 2006, and 2007, it still
persists and has increased in some C. christii habitats. Other threats
to C. christii from recreational use appear to be mostly seasonal and
affect only a small portion of the population, although they too are
imminent. The magnitude of the threats to this species is moderate at
this time because, although the smooth brome control efforts have not
been effective, the Service and Forest Service are continuing their
efforts in order to protect this potentially large population of
plants. The threat from smooth brome is imminent because the threat
still persists at a level that affects the native plant communities
that provide habitat for C. christii. Thus, we assign an LPN of 8 to
this species.
Chamaecrista lineata var. keyensis (Big Pine partridge pea) -The
following summary is based on information contained in our files. No
new information was provided in the petition we received on May 11,
2004. This pea is endemic to the lower Florida Keys, and restricted to
pine rocklands and hardwood hammock edges, and roadsides and firebreaks
within these ecosystems. Historically, it was known from Big Pine, No
Name, Ramrod, and Cudjoe Keys (Monroe County, Florida). In 2005, a
small population was detected on lower Sugarloaf Key, but this
population was apparently extirpated later in 2005, due to the effects
of Hurricane Wilma. It presently occurs on Big Pine Key, plus a very
small population found on Cudjoe Key in 2005. It is fairly well
distributed in Big Pine Key pine rocklands, which encompass
approximately 580 hectares (1,433 acres), approximately 360 hectares
(890 acres) of which are within the Service's National Key Deer Refuge
(NKDR). Over 80% of the population probably exists on NKDR, with the
remainder distributed among State, County, and private properties.
Hurricane Wilma (October 2005) resulted in a storm surge that
covered most of Big Pine Key with sea water. In plots sampled after
Wilma, frequency of occurrence was less than a third and density was
less than half that found in plots sampled before Wilma.
Pine rockland communities are maintained by relatively frequent
fires. In the absence of fire, shrubs and trees encroach on pine
rockland and the subspecies is eventually shaded out. NKDR has a
prescribed fire program, although with many constraints on
implementation. Habitat loss due to development was historically the
greatest threat to the pea. Much of the remaining habitat is now
protected on public lands. Absence of fire now appears to be the
greatest of the deterministic threats. Given the recent increase in
hurricane activity, storm surges are the greatest of the stochastic
threats. The small range and patchy distribution of the subspecies
increases risk from stochastic events. Additional threats include sea
level rise, restricted range, invasive exotic plants, roadside dumping,
loss of pollinators, seed predators, and development. The above
description of threats also apply to Chamaesyce deltoidea ssp.
serpyllum, below.
We maintain the previous assessment that hurricane storm surges,
lack of fire, and limited distribution results in a moderate magnitude
of threat because a large part of the range is on conservation lands
wherein threats are being controlled although fire management is at
much slower rate than is required. The immediacy of hurricane threats
is difficult to characterize. Sea level rise remains uncontrolled, but
is nonimminent regarding most of the habitat area or population on an
annual basis. Overall, the threats from limited distribution and
inadequate fire management are imminent since they
[[Page 75217]]
are ongoing. Therefore, we retained an LPN of 9 for Big Pine partridge
pea.
Chamaesyce deltoidea pinetorum (Pineland sandmat) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
The pineland sandmat in only known from Miami-Dade County, Florida. The
largest occurrence, estimated at more than 10,000 plants, is located on
Long Pine Key within Everglades National Park. All other occurrences
are smaller and are in isolated pine rockland fragments in heavily
urbanized Miami-Dade County. Occurrences on private lands and on one
county-owned parcel are at risk from development and habitat
degradation and fragmentation. All occurrences of the species are
threatened by habitat loss and degradation due to fire suppression, the
difficulty of applying prescribed fire, and exotic plants. These
threats are severe within small and unmanaged fragments in urban areas.
However, the threats of fire suppression and exotics are reduced on
lands managed by the National Park Service. Another threat is hydrology
changes. Hydrology has been altered within Long Pine Key due to
artificial drainage, which lowered ground water, and construction of
roads, which either impounded or diverted water. Regional water
management intended to restore the Everglades could negatively affect
the pinelands of Long Pine Key. At this time, we do not know whether
the proposed restoration and associated hydrological modifications will
have a positive or negative effect on pineland sandmat. This narrow
endemic may be vulnerable to catastrophic events and natural
disturbances, such as hurricanes. Conditions related to climate change,
particularly sea level rise, may be a factor over the long-term.
Overall, the magnitude of threats to this species is moderate, since by
applying regular prescribed fire, the National Park Service has kept
Long Pine Key's pineland vegetation intact and relatively free of
exotic plants, and the extent to which proposed restoration will
negatively affect this subspecies are unclear. Overall, the threats are
nonimminent since fire management is regularly conducted, and sea level
rise and hurricanes are longer-term threats. Therefore, we assigned a
LPN of 12 to this subspecies.
Chamaesyce deltoidea ssp. serpyllum (Wedge spurge) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
The most recent surveys were conducted in 2005. Additional surveys were
initiated in 2008. Wedge spurge is a small prostrate herb. It was
historically, and remains, restricted to pine rocklands on Big Pine Key
in Monroe County, Florida. Pine rocklands encompass approximately 580
hectares (1,433 acres) on Big Pine Key, approximately 360 hectares (890
acres) of which are within the Service's National Key Deer Refuge
(NKDR). Most of the species' range falls within the NKDR, with the
remainder on State, County, and private properties. It is not widely
dispersed within the limited range. Occurrences are sparser in the
southern portion of Big Pine Key, which contains smaller areas of NKDR
lands than does the northern portion. Wedge spurge inhabits sites with
low woody cover (e.g., low palm and hardwood densities) and usually,
exposed rock or gravel. See description of threats above under
Chamaecrista lineata var. keyensis
We maintain the previous assessment that low fire return intervals
plus hurricane-related storm surges, in combination with a limited,
fragmented distribution and threats from sea level rise, results in a
moderate magnitude of threat, in part, because a large part of the
range is on conservation lands wherein threats can be substantially
controlled. The immediacy of hurricane threats is difficult to
categorize. Sea level rise remains uncontrolled, but over much of the
range is nonimminent compared to other prominent threats. Threats
resulting from limited fire occurrences are imminent. Since major
threats are ongoing, overall, the threats are imminent. Therefore, we
retained an LPN of 9 for this subspecies.
Chorizanthe parryi var. fernandina (San Fernando Valley
spineflower) - The following summary is based on information contained
in our files and the petition we received on December 14, 1999.
Chorizanthe parryi var. fernandina is a low growing herbaceous annual
plant in the buckwheat family. The plant currently is known from two
disjunct localities in southern California: the first is in the
southeastern portion of Ventura County on a site within the Upper Las
Virgenes Canyon Open Space Preserve, formerly known as Ahmanson Ranch,
and the second is in an area of southwestern Los Angeles County known
as Newhall Ranch. Investigations of historical locations and seemingly
suitable habitat within the range of the species have not revealed any
other occurrences.
The threats currently facing San Fernando Valley spineflower
include threatened destruction, modification, or curtailment of its
habitat or range, and other natural or manmade factors. One of the two
populations (Upper Las Virgenes Canyon Open Space Preserve) is in
permanent, public ownership and is being managed by an agency that is
working to conserve the plant; however, the use of adjacent habitat for
filming movies has recently been brought to our attention; the
potential impacts to C. parryi var. fernandina have not yet been
evaluated. We will be working with the landowners to manage the site
for the benefit of C. parryi var. fernandina. The other population
(Newhall Ranch) is under the threat of development; however, a
Candidate Conservation Agreement (CCA) is being developed with the
landowner, and it is possible that the remaining plants can also be
conserved. Until such an agreement is finalized, the threat of
development and the potential damage to the Newhall Ranch population
still exists, as shown by the destruction of some plants during
installation of an agave farm. Furthermore, cattle grazing on Newhall
Ranch may be a current threat. Cattle grazing may harm C. parryi var.
fernandina by trampling and soil compaction. Grazing activity could
also alter the nutrient content of the soils through fecal inputs,
which in turn may favor the growth of other plant species that would
otherwise not grow so readily on the mineral-based soils. Over time,
changes in species composition may render the sites less favorable for
the persistence of C. parryi var. fernandina. Invasive nonnative
plants, including grasses, could potentially displace it from available
habitat; compete for light, water, and nutrients; and reduce survival
and establishment.
Chorizanthe parryi var. fernandina is particularly vulnerable to
extinction due to its concentration in two isolated areas. The
existence of only two areas of occurrence, and a relatively small
range, makes it highly susceptible to extinction or extirpation from a
large part of its range due to possible development and/or other
habitat modification, or random events such as fire, drought, erosion,
or other occurrences. We retained an LPN of 6 for C. parryi var.
fernandina due to a high magnitude of nonimminent threats.
Chromolaena frustrata (Cape Sable thoroughwort) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
This species is found most commonly in open sun to partial shade at the
edges of rockland tropical hammock and in coastal rock barrens. There
are nine extant occurrences located at five islands in the Florida Keys
and two
[[Page 75218]]
locations within Everglades National Park (ENP). The plant has been
extirpated from half of the islands where it occurred. Prior to
Hurricane Wilma in 2005, the population was estimated at roughly 5,000
individuals, with all but 500 occurring on one privately owned island.
More recently, an estimate of 1,500 plants was given for areas within
ENP.
This species is threatened by habitat loss and modification, even
on public lands, and habitat loss and degradation due to threats from
exotic plants at almost all sites. The species is vulnerable to natural
disturbances, such as hurricanes, tropical storms, and storm surges.
While these factors may also work to maintain coastal rock barren
habitat in the long-term, Hurricane Wilma appeared to have had severe
impacts, at least in the short-term. Occurrences probably declined due
to inundation of its coastal barren and rockland hammock habitats in
the short-term; long-term effects on this species are unknown. Sea
level rise is considered a major threat that will continue. Potential
effects from other changes in fresh water deliveries and the
construction of the Buttonwood Canal are unknown. Problems associated
with small population size and isolation are likely major factors, as
occurrences may not be large enough to be viable; this narrowly endemic
plant has uncertain viability at most locations, especially following
Hurricane Wilma. Thus, these factors constitute a high magnitude of
threat. The threats of small population size, isolation, and uncertain
viability are imminent because they are ongoing. As a result, we
assigned an LPN of 2 to this species.
Consolea corallicola (Florida semaphore cactus) - The following
summary is based on information in our files. No new information was
provided in the petition we received on May 11, 2004. The Florida
semaphore cactus is endemic to the Florida Keys, and was discovered on
Big Pine Key in 1919, but that population was extirpated as a result of
road building and poaching. This cactus grows close to salt water on
bare rock with a minimum of humus soil cover in or along the edges of
hammocks near sea level. The species is known to occur naturally only
in two areas, Swan Key within Biscayne National Park and Little Torch
Key. Outplantings have been attempted in several locations in the upper
and lower Keys; however, success has been low. Few plants remain in the
population at The Nature Conservancy's Torchwood Hammock Preserve on
Little Torch Key. During monitoring work conducted in 2005, a total of
655 plants were documented at the Swan Key population. The cactus does
not propagate sexually, and asexual reproduction is the main life
history strategy of this species. Recent genetic studies have shown no
variation within populations and very limited variation between
populations. Findings support the conclusion that the Swan Key (upper
Keys), Little Torch Key, and Big Pine Key (outplanting; lower Keys)
populations are clonally derived and genetically distinct from each
other. Studies examining the reproductive biology of the species
indicate that all extant wild and cultivated plants are male.
The causes for the population decline of this species include
destruction or modification of habitat, predation from nonnative
Cactoblastis cactorum moths and disease, poaching and vandalism, sea
level rise, and hurricanes. Because of low population numbers, lack of
variation between and within populations, and reproductive problems,
the threats are of high magnitude. The numerous threats are ongoing and
therefore, are imminent. Thus, we assigned this species an LPN of 2.
Cordia rupicola (no common name) - The following summary is based
on information contained in our files. No new information was provided
in the petition we received on May 11, 2004. Cordia rupicola, a small
shrub, has been described from southwestern Puerto Rico
(Pe[ntilde]uelas and Gu[aacute]nica), Vieques Island, and Anegada
Island (British Virgin Islands). All four sites lay within the
subtropical dry forest life zone overlying a limestone substrate.
Cordia rupicola has a restricted distribution in the subtropical dry
forest of southwestern Puerto Rico and Vieques Island. Currently,
approximately 226 individuals are known from 3 locations:
Pe[ntilde]uelas and Guanica Commonwealth Forests and Vieques National
Wildlife Refuge. Additionally, the species is reported as common on
Anegada Island.
However, the species is threatened by residential and commercial
development on Anegada Island and is also vulnerable to natural (e.g.,
hurricanes) or manmade (e.g., human-induced fires) threats throughout
most of its range. All of these threats have a significant effect on
the survival of the species. For these reasons, the magnitude of the
current threats is high. Additionally, all sites are located in xeric
environment vulnerable to human-induced fires. Only a few individuals
are located in protected lands managed for conservation by the Puerto
Rico Department of Natural and Environmental Resources or the Service.
The population of C. rupicola on Anegada Island is currently in good
standing. The threats this species faces are ones that will arise in
the future if conservation measures are not implemented and long-term
impacts are not averted. For these reasons, threats to the species as a
whole are nonimminent. Therefore, we assigned an LPN of 5 to this
species.
Cyanea asplenifolia (Haha) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Cyanea asplenifolia is a
shrub found in Acacia-Metrosideros (koa-ohia) forest on Maui, Hawaii.
Currently, this species is known from eight populations totaling fewer
than 145 individuals. Cyanea asplenifolia is threatened by pigs, goats,
and cattle that degrade and destroy habitat and by nonnative plants,
such as Australian tree fern, that outcompete and displace it. This
species is likely threatened by predation by axis deer and by feral
ungulates, rats, and slugs that may directly prey upon and defoliate
individuals. Pig and goat exclusion fences protect individuals of two
of the known populations of this species, and nonnative plants have
been reduced in one fenced area; however, continued monitoring of these
fences will be necessary, as feral ungulates from surrounding areas can
easily access unmaintained fenced areas. This species is represented in
three ex-situ collections. The threats continue to be of a high
magnitude because they significantly affect the species resulting in
direct mortality or reduced reproductive capacity. The threats are
imminent because they are ongoing in at least two of the eight known
populations. Therefore, we retained an LPN of 2 for this species.
Cyanea calycina (Haha) - We have not updated our assessment for
this species, as we are currently developing a proposed listing rule.
Cyanea kunthiana (Haha) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Cyanea kunthiana is a shrub
found in closed Metrosideros-Dicranopteris (ohia-uluhe) montane wet
forest on Maui, Hawaii. The historic range of C. kunthiana was wet
forest on the island of Maui. Currently, C. kunthiana is declining
throughout its range, and is known from 38 populations totaling between
475 and 675 individuals. This species is threatened by pigs that
directly prey upon the plants and degrade and destroy habitat, and by
nonnative plants that outcompete and
[[Page 75219]]
displace it. Potential threats to this species include rats and slugs
that may directly prey upon and defoliate individuals. Predation and
habitat destruction significantly affect the continued existence of the
species. While large-scale fencing, ungulate removal, and invasive
species control measures are underway in areas in which five of the
current populations exist, these efforts have not served to completely
remove these threats, and there are no efforts to control the ongoing
and imminent threats to the remaining 33 populations. Therefore, the
threats continue to be of a high magnitude to C. kunthiana, and are
imminent for more than eighty percent of the populations. Therefore, we
retained an LPN of 2 for this species.
Cyanea lanceolata (Haha) - We have not updated our assessment for
this species, as we are currently developing a proposed listing rule.
Cyanea obtusa (Haha) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Cyanea obtusa is a shrub
found in Metrosideros polymorpha (ohia) mixed mesic forest on Maui,
Hawaii. This species is known from two populations with a combined
total of fewer than 24 individuals. Cyanea obtusa is threatened by
feral goats, pigs, and cattle that degrade and destroy habitat, and by
nonnative plants that outcompete and displace it. Potential threats
include fire, and rats and slugs that may directly prey upon and
defoliate individuals of C. obtusa. Feral pigs have been fenced out of
one population of this species, with nonnative plant control in the
fenced area. Although one population of C. obtusa has been fenced and
is undergoing weed control, there are no efforts to control the ongoing
and imminent threats to the other population. The threats continue to
be of a high magnitude for C. obtusa because they significantly affect
the species resulting in direct mortality or reduced reproductive
capacity, and the threats are ongoing. Therefore, we retained an LPN of
2 for this species.
Cyanea tritomantha (Aku) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Cyanea tritomantha is a palm-
like tree found in Metrosideros-Cibotium (ohia-hapuu) montane wet
forest on the island of Hawaii. This species is known from 16
populations with a total of approximately 300 to 400 individuals.
Cyanea tritomantha is threatened by pigs and cattle that degrade and
destroy habitat, and nonnative plants that outcompete and displace it.
Potential threats to this species include predation by rats and slugs
that may directly prey upon and defoliate individuals, and human
trampling of individuals located near trails. Feral pigs and cattle
have been fenced out of three populations of C. tritomantha, and
nonnative plants have been reduced in the fenced areas. Although three
populations of C. tritomantha have been fenced and weeds are being
controlled in these fenced areas, there are no efforts to control the
ongoing and imminent threats to the other 13 populations. The threats
continue to be of a high magnitude to C. tritomantha because they
significantly affect the species resulting in direct mortality or
reduced reproductive capacity. They are ongoing and therefore imminent
for more than seventy-five percent of the population where no control
measures have been implemented. Because the threats continue to be of a
high magnitude and are imminent for the unmanaged populations, we
retained an LPN of 2 for this species.
Cyrtandra filipes (Haiwale) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Haiwale is a shrub found in
lowland to montane wet forest on Maui and Molokai, Hawaii. Historically
rare, C. filipes was found in southeastern Molokai and west Maui.
Currently, this species is known from 10 populations, 3 on Molokai and
7 on west Maui, totaling approximately 2,000 individuals. There is some
question as to the true identity of the Maui populations, which do not
fit the description of the species precisely. If, upon further
taxonomic study, the Maui populations are determined not to be this
species, then it is even rarer, with only the Molokai populations of a
few individuals remaining. Cyrtandra filipes is threatened by pigs,
goats, and deer that degrade and destroy habitat, by nonnative plants
that outcompete and displace it, and potentially by rats that directly
prey on it. Feral pigs have been fenced out of one of the populations
of C. filipes on Maui, and strategic fencing for axis deer is under
construction on west Maui, but deer are able to jump over most pig
exclusion fences so they are still considered a threat. Nonnative
plants are being reduced in the population that is fenced but all
populations are potentially threatened by rats. The threats from pigs
and nonnative plants are of a high magnitude because of their severity
and the fact that they occur in eight of the 10 known populations. In
addition, these threats are imminent because they are ongoing.
Therefore, we retained an LPN of 2 for this species.
Cyrtandra kaulantha (Haiwale) - We have not updated our assessment
for this species, as we are currently developing a proposed listing
rule.
Cyrtandra oxybapha (Haiwale) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Cyrtandra oxybapha is a shrub
found in Metrosideros polymorpha-Cheirodendron trigynum (ohia-olapa)
montane wet forest to mesic Acacia-Metrosideros (koa-ohia) forest on
Maui, Hawaii. Currently, this species is known from two populations
totaling 73 to 123 individuals on west Maui. This species is threatened
by pigs, goats, and cattle that degrade and destroy habitat, and by
nonnative plants that outcompete and displace it. Fire is a likely
threat at the Kahikinui population. The individuals within the fence at
Kahikinui benefit from management actions; however, the remaining
individuals there and on west Maui are threatened by pigs, goats,
cattle, and likely threatened by fire. The threats are of a high
magnitude because of their severity and are imminent since they are
ongoing. Therefore, we retained an LPN of 2 for C. oxybapha.
Cyrtandra sessilis (Haiwale) - We have not updated our assessment
for this species, as we are currently developing a proposed listing
rule.
Dalea carthagenensis floridana (Florida prairie-clover) - The
following summary is based on information contained in our files. No
new information was provided in the petition we received on May 11,
2004. Dalea carthagenensis var. floridana occurs in Big Cypress
National Preserve (BCNP) in Monroe and Collier Counties, Florida. It is
also known from small populations in Miami-Dade County. There are a
total of nine extant occurrences, most of which are on conservation
land. Existing occurrences are extremely small and may not be viable,
especially those in Miami-Dade County. Remaining habitats are
fragmented. This plant is threatened by habitat loss and degradation
due to fire suppression, the difficulty of applying prescribed fire to
pine rocklands, and threats from exotic plants. Damage to plants by
off-road vehicles is a serious threat within the BCNP; the threat from
illegal mountain-biking at the R. Hardy Matheson Preserve has been
reduced. One location within BCNP is threatened by changes in mowing
practices; this
[[Page 75220]]
threat is considered to be low. This species is being parasitized by
the introduced insect lobate lac scale at some localities (e.g., R.
Hardy Matheson Preserve), but we do not know the extent of this threat.
This plant is vulnerable to natural disturbances, such as hurricanes,
tropical storms, and storm surges. Due to its restricted range and the
small sizes of most isolated occurrences, this species is vulnerable to
environmental (catastrophic hurricanes), demographic (potential
episodes of poor reproduction), and genetic (potential inbreeding
depression) threats. The magnitude of threats is high, and threats are
imminent because of the limited number of occurrences and the small
number of individual plants at each occurrence. In addition, even
though many sites are on conservation lands, these plants still face
significant ongoing threats. Therefore, we have assigned an LPN of 3 to
this subspecies.
Dichanthelium hirstii (Hirsts' panic grass) - The following summary
is based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. D. hirstii is a
perennial grass that produces erect leafy flowering stems from May to
October. D. hirstii occurs in coastal plain intermittent ponds, usually
in wet savanna or pine barren habitats and is found at only two sites
in New Jersey, one site in Delaware, and one site in North Carolina.
While all four extant D. hirstii populations are located on public land
or privately owned conservation lands, natural threats to the species
from encroaching vegetation and fluctuations in climatic conditions
remain of concern and may be exacerbated by anthropomorphic factors
occurring adjacent to the species' wetland habitat. Given the low
numbers of plants found at each site, even minor changes in the
species' habitat could result in local extirpation. Loss of any known
sites could result in a serious protraction of the species' range.
However, the most immediate and severe of the threats to this species
(i.e., ditching of the Laboundsky Pond site, and encroachment of
aggressive vegetative competitors) have been curtailed or are being
actively managed by The Nature Conservancy at one New Jersey site and
by the Delaware Division of Fish and Wildlife and Delaware Natural
Heritage Program at the Assawoman Pond, Delaware site. Based on
nonimminent threats of a high magnitude, we retain an LPN of 5 for this
species.
Digitaria pauciflora (Florida pineland crabgrass) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Florida pineland crabgrass occurs in the pineland/prairie ecotones and
prairies in Miami-Dade and Monroe Counties, Florida. Pine rocklands in
Miami-Dade County have largely been destroyed by residential,
commercial, and urban development and agriculture. Most remaining
habitat has been negatively altered, and this species has been
extirpated from much of its historical range, including extirpation
from all areas outside of National Parks. Two large occurrences remain
within Everglades National Park and Big Cypress National Preserve.
While privately owned pine rocklands and prairies are at risk to
development, the plants on Federal lands are protected from this
threat.
This species is threatened by habitat loss and degradation due to
fire suppression, the difficulty of applying prescribed fire to pine
rocklands, and exotic plants. Since the only remaining populations are
on lands managed by the National Park Service, the threats of fire
suppression and exotics are somewhat reduced. The presence of the
exotic Old World climbing fern is of particular concern due to its
ability to spread rapidly. In Big Cypress National Preserve, plants
have been threatened by off-road vehicle use. Another threat is
hydrology changes. Hydrology has been altered within Long Pine Key due
to artificial drainage, which lowered ground water, and construction of
roads, which either impounded or diverted water. Regional water
management intended to restore the Everglades has the potential to
affect the pinelands of Long Pine Key, where a large population occurs.
At this time, it is not known whether Everglades restoration will have
a positive or negative effect. This narrow endemic may be vulnerable to
catastrophic events and natural disturbances, such as hurricanes. Sea
level rise will likely be a factor over the long-term. Overall, the
magnitude of threats is high because occurrence of the species within
the National Park has not eliminated such threats as exotic plants and
off-road vehicle use, which may negatively affect this species
throughout its range. However, the majority of threats are nonimminent
as they are long-term in nature (water management, hurricanes, and sea-
level rise). Therefore, we assigned an LPN of 5 for this species.
Echinomastus erectocentrus var. acunensis (Acuna cactus) - The
following summary is based on information contained in our files and
the petition we received on October 30, 2002. The Acuna cactus is known
from six sites in Arizona and Mexico. It occurs on well-drained gravel
ridges and knolls on granite soils in Sonoran Desert scrub association
at 1300-2000 feet elevation.
Habitat destruction has been a threat in the past and is a
potential future threat to this species. New roads and illegal
activities have not yet directly affected the cactus populations at
Organ Pipe Cactus National Monument, Arizona, but areas in close
proximity to these known populations have been altered. Cactus
populations located in the Florence area (Arizona) have not been
monitored, and these populations may be in danger of habitat loss due
to recent urban growth in the area. Urban development near Ajo,
Arizona, as well as that near Sonoyta, Mexico, is a significant threat
to the Acuna cactus. Populations of the Acuna cactus within the Organ
Pipe Cactus National Monument have shown a 50 percent mortality rate in
recent years. The reason(s) for the mortality are not known, but
continuing drought conditions which are prevalent throughout the range
of the Acuna cactus are thought to play a role. The Arizona Plant Law
and the Convention on International Trade in Endangered Species of Wild
Fauna and Flora provide some protection for the Acuna cactus. However,
illegal collection is a primary threat to this cactus variety, and has
been documented on the Organ Pipe Cactus National Monument in the past.
The threats continue to be of a high magnitude as they have a
significant negative impact to the long-term viability of this cactus
as demonstrated by the continued dramatic decline of the variety. The
threats are imminent because habitat loss from drought and urban
development are ongoing. Therefore, we assigned an LPN of 3 to the
Acuna cactus.
Erigeron lemmonii (Lemmon fleabane) - The following summary is
based on information contained in our files and the petition we
received in July 1975. The species is known from one site in a canyon
in the Fort Huachuca Military Reservation of southeastern Arizona. As
of 2006, approximately 950 plants were known from this site, where the
occupied habitat encompasses about 1 square kilometer.
The threats to this species are from catastrophic wildfire in the
canyon and ongoing drought conditions. We do not know if this species
has any adaptations to fire. Due to its location on cliffs, we suspect
that fires may have occurred at regular intervals and burned at low
intensities, and thus may have had little to no effect on this species.
It is due only to lack of fire and the accumulated
[[Page 75221]]
fuel load that the fire intensity and associated heat may be high
enough to damage or kill plants on adjacent cliffs, especially near the
ground. On the other hand, plants that are much higher on the cliff
face would probably not be affected. The magnitude of threats is
moderate because we believe that not all of the population would be
adversely affected by a wildfire or drought. The threats are imminent
because the likelihood of a fire is high. The LPN for Lemmon fleabane
remains an 8 due to moderate, imminent threats.
Eriogonum codium (Umtanum Desert buckwheat) - The following summary
is based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. This species is a
long-lived, slow-growing, woody perennial plant that forms low dense
mats. The species occupies a single location on the Hanford National
Monument in Washington State. It is found only on an exposed basalt
ridge; we do not know if this association is related to the chemical or
physical characteristics of the bedrock or other factors. Individual
plants may exceed 100 years of age, based on counts of annual growth
rings. A count in 1997 reported 5,228 individuals; by 2005 the figure
had dropped to 4,418, declining 15% over eight years. A population
viability analysis in 2006 based on 9 years of demographic data
estimated that that there is little or no risk of a population decline
greater than 90 percent within 100 years, but there is a 72 percent
chance of a decline of 50 percent.
The major threats to the species are wildfire, fire-fighting
activities, trampling, and invasive weeds. However, the relationship
between the decline in population numbers and the known threats is not
understood at this time. With the possible exception of wildfire, the
observed decline in population numbers and recruitment since 1997 is
not directly attributable to the currently known threats. Because the
population is small, limited to a single site, and sensitive to fire
and disturbance, the species remains vulnerable to the identified
threats. The magnitude of threats is high because, given the limited
range of the species and the degree of uncertainty about its habitat
and the cause of its declines, any of the threats could adversely
affect its continued existence. The threats are both ongoing and
imminent in nature. Because the species continues to be vulnerable to
these threats, we assigned an LPN of 2 to this species.
Eriogonum kelloggii (Red Mountain buckwheat) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Red Mountain buckwheat is a perennial herb endemic to serpentine
habitat of lower montane forests found between 1,900 and 4,100 feet.
Its distribution is limited to the Red Mountain and Little Red Mountain
areas of Mendocino County, California, where it occupies a total of 50
acres and 900 square feet, respectively. Occupied habitat at Red
Mountain is scattered over 4 square miles. Total population size is
estimated at between 20,000 and 30,000 plants, which occur in 44
polygons. Intensive monitoring of permanent plots on three study sites
in Red Mountain suggests considerable annual variation in plant density
and reproduction, but no discernable population trend was evident in
two of three study sites. One study site showed a 65 percent decline in
plant density over 11 years.
The primary threat to this species is the potential for surface
mining for chromium and nickel. Virtually the entire distribution of
Red Mountain buckwheat is either owned by mining interests, or is
covered by existing mining claims, none of which are currently active.
Surface mining would destroy habitat suitability for this species. The
species is also believed threatened by tree and shrub encroachment into
its habitat, in absence of fire. The threat of surface mining is high
in magnitude because it would prevent the continued existence of the
species in the larger of two locations. That threat is nonimminent
because none of the mining claims are active. Because of the high-
magnitude, nonimminent threat to the small, scattered populations, we
assigned a listing priority number of 5 to this species.
Eriogonum corymbosum var. nilesii (Las Vegas buckwheat) - The
following summary is based on information contained in our files and
the petition we received on April 23, 2008. The Las Vegas buckwheat is
a woody perennial shrub restricted to gypsum soil outcroppings in Clark
and Lincoln Counties, Nevada.
Destruction and modification of habitat from development is a
significant threat with over 95 percent of the historic range and
potential habitat of the subspecies affected. In 2005, the Las Vegas
buckwheat was known from nine locations on approximately 1,149 acres,
but occupied habitat has declined since then to 892 acres due to
development. In addition, OHV activity and other public land uses
(casual public use, mining, and dumping) directly and indirectly
threaten over half of the remaining habitat. To date, regulatory
mechanisms to protect the Las Vegas buckwheat are inadequate. Its
designation by the Bureau of Land Management (BLM) as a special status
species has not provided adequate protection on lands managed by the
BLM in large part due to limitations on resources and law enforcement
personnel. The Las Vegas buckwheat is not protected by the State of
Nevada or any other regulatory mechanisms on other federal lands.
Conservation measures are being developed that could reduce the amount
of occupied habitat at risk, but we believe it would be premature to
consider these measures sufficiently complete as to remove these
threats. The magnitude of threats is high, since the more significant
threats (development and surface mining) would result in direct
mortality of the plants in over half of its habitat. While both
development and mining are very likely to occur in the future, they are
not expected to happen in the immediate future, and thus, the threats
are nonimminent. Accordingly, we assigned the Las Vegas buckwheat an
LPN of 6.
Festuca hawaiiensis (no common name) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. This species is a
cespitose (growing in dense, low tufts) annual found in dry forest on
the island of Hawaii. Festuca hawaiiensis is known from four
populations totaling approximately 1,000 individuals in and around the
Pohakuloa Training Area (PTA). Historically, this species was also
found on Hualalai and Puu Huluhulu on Hawaii and possibly Ulupalakua on
Maui, but it no longer occurs at these sites. Festuca hawaiiensis is
threatened by pigs, goats, mouflon, and sheep that degrade and destroy
habitat; fire; military training activities; and nonnative plants that
outcompete and displace it. Feral pigs, goats, mouflon, and sheep have
been fenced out of a portion of the populations of F. hawaiiensis, and
nonnative plants have been reduced in the fenced areas but the majority
of this population is still impacted by threats from fire and will
require long-term monitoring and management. The threats are imminent
because they are not controlled and are ongoing in the remaining,
unfenced populations. Firebreaks have been established at two other
populations but again fire is an imminent threat to the other two
populations that have no firebreaks. The threats are of a high
magnitude because
[[Page 75222]]
they could adversely affect F. hawaiiensis resulting in direct
mortality or reduced reproductive capacity. Therefore, we retained an
LPN of 2 for this species.
Festuca ligulata (Guadalupe fescue) - The following summary is
based on information contained in our files and the petition we
received in 1975. Guadalupe fescue is a member of the Poaceae (grass
family). This species is currently only known from higher elevations in
the Chisos Mountains in the Big Bend Area of Texas (one population) and
adjacent Coahuila, Mexico (two populations). The population in Big Bend
National Park is bisected by a trail and subject to occasional
trampling by horses and hikers and may be impacted by the lack of
proper fire management. A new Candidate Conservation Agreement between
the Service and the National Park Service provides for additional
conservation efforts, population monitoring, fire management, and trail
operation by the National Park Service; these actions partially address
threats to the species. Overall, the magnitude of the threats of
trampling and lack of proper fire management is moderate to low and
nonimminent because of the actions under this agreement. Thus, we
assign a LPN of 11 to this species.
Gardenia remyi (Nanu) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Nanu is a tree found in mesic
to wet forest on islands of Kauai, Molokai, Maui, and Hawaii, Hawaii.
Gardenia remyi is known from 20 populations totaling between 77 and 104
individuals. This species is threatened by pigs, goats, and deer that
degrade and destroy habitat and possibly prey upon the species, and by
nonnative plants that outcompete and displace it. It is also threatened
by landslides on the island of Hawaii. This species is represented in
an ex-situ collection. Feral pigs have been fenced out of the west Maui
populations of G. remyi, and nonnative plants have been reduced in
those areas. However, these threats are not controlled and are ongoing
in the remaining, unfenced populations, and are, therefore, imminent.
In addition, the threat from goats and deer is ongoing and imminent
throughout the range of the species, because no goat or deer control
measures have been undertaken for any of the populations of G. remyi.
All of the threats are of a high magnitude because habitat destruction,
predation, and landslides are significant enough that they could
adversely affect the species resulting in direct mortality or reduced
reproductive capacity. Therefore, we retained an LPN of 2 for this
species.
Geranium hanaense (Nohoanu) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Geranium hanaense is
threatened by pigs that degrade and destroy habitat, and by nonnative
plants that outcompete and displace it. However, feral pigs have been
fenced out of and removed from both bogs in which this species
currently occurs, and a control program has reduced nonnative plants in
all fenced areas. Given that the threats to the only known populations
of this species are currently being managed and the populations are
routinely monitored, the overall magnitude of these threats is
moderate. The threats are imminent because the fences must be routinely
monitored and nonnative plants must continually be controlled.
Therefore, we retained an LPN of 8 for this species.
Geranium hillebrandii (Nohoanu) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Geranium hillebrandii is a
decumbent subshrub found in bogs on Maui, Hawaii. It is currently known
from three populations totaling approximately 10,000 individuals.
Geranium hillebrandii is threatened by pigs that degrade and destroy
habitat, and by nonnative plants that outcompete and displace it.
Conservation measures taken to control feral pigs and nonnative plants
reduce the impact of these threats to G. hillebrandii; however,
continued monitoring will be necessary to keep the areas threat-free.
The threats from feral pigs and nonnative plants are, therefore, of a
moderate magnitude to this species; however, these threats are imminent
because they are ongoing in half of the populations and require
continued monitoring in the other half. Therefore, we retained an LPN
of 8 for this species.
Gonocalyx concolor (no common name) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. Gonocalyx
concolor is a small evergreen epiphytic shrub. Currently, G. concolor
is known only from the dwarf or elfin forest type in the Carite
Commonwealth Forest (Cerro La Santa), located in the Sierra de Cayey in
the municipalities of Guayama, Cayey, Caguas, San Lorenzo, and Patillas
in southeastern Puerto Rico. The population previously reported in the
Caribbean National Forest in Puerto Rico is apparently no longer
extant. The entire population located at one site consists of
approximately 172 individuals. Habitat destruction from construction of
roads and telecommunication towers, certain forest management practices
such as the development and maintenance of trails, and potential for
catastrophic natural events threaten this species. Its restricted
distribution renders this species highly vulnerable to natural (e.g.,
hurricanes, landslides) or manmade (e.g., telecommunication towers,
forest management practices) threats to its habitat and population,
thus making the threat magnitude high. This species is classified as
critical by Puerto Rico Department of Natural and Environmental
Resources (PRDNER); however, this designation does not provide any
regulatory protection. The PRDNER developed a management plan for the
Carite Commonwealth Forest in 1976, which includes the protection and
conservation of species classified under PRDNER regulations as
critical, threatened, or endangered, but it does not include specific
measures for the protection of this species. Generally, PRDNER
scrutinizes any actions that may affect species classified as critical,
and recommends or implements measures to minimize or avoid impacts to
these species if deemed appropriate. The immediacy of the threats from
building roads and towers and developing and maintaining trails is thus
nonimminent. Therefore, we have assigned a listing priority number of 5
for Gonocalyx concolor.
Hazardia orcuttii (Orcutt's hazardia) - The following summary is
based on information contained in our files and the petition we
received on March 8, 2001. Hazardia orcuttii is an evergreen shrubby
species in the Asteraceae (sunflower family). The only known extant
native occurrence of this species in the U.S. is in the Manchester
Conservation Area in northwestern San Diego County, California. This
site is managed by Center for Natural Lands Management. Hazardia
orcuttii also occurs at a few coastal sites in Mexico, where it has no
conservation protections in Mexico. There are approximately 668 native
adult plants and 50 seedlings remaining in the U.S., and the population
in Mexico is estimated at approximately 1300 plants.
The occurrences in Mexico are threatened by the rapid rate of
coastal development from Tijuana to Ensenada. Apparent threats to the
U.S. population include ongoing pedestrian trampling, impacts from on
and off-leash dogs, and creation of bicycle trails near Hazardia
orcuttii plants. Competition from
[[Page 75223]]
invasive nonnative plants may pose a threat to the reproductive
potential of this species. Another significant threat is the species'
apparently low reproductive output; in a recent study, 95 percent of
the flowers examined were damaged by insects or fungal agents or
aborted prematurely, and insects or fungal agents damaged 50 percent of
the seeds produced. Overall, the threats are of a high magnitude since
they have the potential to significantly reduce the reproductive
potential of this species. The threats are nonimminent overall because
although trampling and other recreational impacts are ongoing, the most
significant threats (competition and low reproductive output) are
nonimminent and long-term in nature. Thus, we assigned this species a
LPN of 5.
Hedyotis fluviatilis (Kamapuaa) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Kamapuaa is a scandent shrub
found in mixed shrubland to wet lowland forest on Oahu and Kauai,
Hawaii. This species is known from 12 populations totaling 1,000 to
1,400 individuals. Hedyotis fluviatilis is threatened by pigs and goats
that degrade and destroy habitat, and by nonnative plants that
outcompete and displace it. All of the threats occur range-wide, and no
efforts for their control or eradication are being undertaken.
Displacement and habitat destruction have a negative impact on the
continued existence of the species. We retained an LPN of 2 because the
severity of the threats is high and the threats are ongoing so are
imminent.
Helianthus verticillatus (Whorled sunflower) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
The whorled sunflower is found in moist, prairie-like openings in
woodlands and along adjacent creeks. Despite extensive surveys
throughout its range, only five populations are known: two populations
in Cherokee County, Alabama; one population in Floyd County, Georgia;
and one each in Madison and McNairy Counties, Tennessee. This species
appears to have restricted ecological requirements and is dependent
upon the maintenance of prairie-like openings for its survival. Much of
its habitat has been degraded or destroyed for agricultural,
silvicultural, and residential purposes. Populations near roadsides or
powerlines are threatened by herbicide usage in association with right-
of-way maintenance. The majority of the Georgia population is protected
due to their location within a conservation easement area; however,
only 15 to 20 plants are estimated to occur at this site. We assigned
an LPN of 5 to this species, as the magnitude of threats is high, since
there are only five populations and only one of these is under any
protection from threats that could eliminate the continued existence of
the other populations; the threats are nonimminent, since the whorled
sunflower appears to withstand some disturbance and there are no known
immediate threats to the sites.
Hibiscus dasycalyx (Neches River rose-mallow) - The following
summary is based on information contained in our files. No new
information was provided in the petition received on May 11, 2004. This
mallow species, found in Cherokee, Houston, and Trinity Counties,
Texas, appears to be restricted to portions of wetlands that are
exposed to open sun and normally hold standing water early in the
growing season, with water levels dropping during late summer and fall.
Habitat has been affected by drainage or filling of floodplain
depressions and oxbows, stream channelization, road construction,
timber harvesting, agricultural activities (primarily mowing and
grazing), and herbicide use. Threats that continue to affect the
species include wetland alteration, herbicide use, grazing, mowing
during the species' growing and flowering period, and genetic swamping
by other Hibiscus species.
A 1995 status survey of 10 counties resulted in confirmation of the
species at only three sites, but in three separate counties and three
different watersheds, suggesting a relatively wide historical range.
These three populations were all within highway rights-of-way and
vulnerable to herbicides and adjacent agricultural activities. As of
2005, only 20 plants remained at one of these sites. Additional surveys
for H. dasycalyx resulted in identifying new populations. About 300
plants were found on land owned by Temple-Inland Corporation in east
Trinity County. A Candidate Conservation Agreement was developed for
this site, but smaller plant numbers have been seen in recent years,
possibly due to changes in the wetland's hydrology. Another site
discovered on land previously owned by Champion International
Corporation (near White Rock Creek in west Trinity County) once
supported 300-400 plants; this site was modified in 2007, and was
reassessed in 2008, but data is still being analyzed. In west Houston
County, a population of 300 to 400 plants discovered on private land
has been purchased by the Natural Area Preservation Association in
order to protect this land in perpetuity. In east Houston County, a
population discovered in Compartment 55 in Davy Crockett National
Forest numbered over 1,000 in 2006. In 2000, nearly 800 plants were
introduced into Compartments 16 and 20 of Davy Crockett National Forest
as part of a reintroduction effort. One population retained high
numbers (350 in 2006), but sustained high water in 2007, and may have
been adversely affected. The second site was affected by a change in
hydrology, and had declined to 50 plants in 2006. In 2004, 200 plants
were placed in a wetland in Compartment 11 of Davy Crockett National
Forest, but only 10 plants were seen in 2006. High water from heavy
spring and summer rains prevented further assessment of these rose-
mallow sites in 2007.
The threats continue to be of a high magnitude because they can
severely affect the survival and reproductive capacity of the species.
Overall, the threats are nonimminent since they are not currently
affecting or likely to affect the majority of the populations of this
species in the immediate future. Thus, we have retained an LPN of 5 for
the Neches River rose-mallow.
Ivesia webberi (Webber ivesia) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Ivesia webberi is a low,
spreading, perennial herb that occurs very infrequently in Lassen,
Plumas, and Sierra counties in California, and in Douglas and Washoe
counties, Nevada. The species is restricted to sites with sparse
vegetation and shallow, rocky soils composed of volcanic ash or derived
from andesitic rock. Occupied sites generally occur on mid-elevation
flats, benches, or terraces on mountain slopes above large valleys
along the transition zone between the eastern edge of the northern
Sierra Nevada and the northwestern edge of the Great Basin Desert.
Currently, the global population is estimated at approximately 4.8
million individuals at 15 known sites. The Nevada sites support nearly
98 percent of the total number of individuals (4.7 million) on about 30
acres of occupied habitat. The California sites are larger in area,
totaling about 156 acres, but support fewer individuals (approximately
115,000).
The primary threats to Webber ivesia include urban development,
authorized and unauthorized roads, off-road vehicle activities and
other dispersed recreation, livestock grazing and trampling, fire and
fire suppression activities including fuels reduction and prescribed
fires, and displacement by
[[Page 75224]]
noxious weeds. Despite the high numbers of individuals, observations in
2002 and 2004 confirmed that direct and indirect impacts to the species
and its habitat, specifically from urban development and off-highway
vehicle activity, remain high and are likely to increase. Therefore,
the magnitude of these threats is high. The U.S. Forest Service has
committed to develop a conservation strategy and monitoring program to
protect this species on National Forest lands, and the State of Nevada
has listed the species as critically endangered, which provides a
mechanism to track future impacts on private lands. In addition, both
the Forest Service and State of Nevada have agreed to coordinate
closely with the Fish and Wildlife Service on all activities that may
affect this species. In light of these conservation commitments, we
have determined that the threats to Webber ivesia are nonimminent and
the LPN remains a 5.
Joinvillea ascendens ssp. ascendens (Ohe) - The following summary
is based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. Ohe is an erect
herb found in wet to mesic Metrosideros polymorpha-Acacia koa (ohia-
koa) forest on the islands of Kauai, Oahu, Molokai, Maui, and Hawaii,
Hawaii. Ohe is known from 38 populations totaling approximately 180
individuals throughout its range. Plants are typically found as only
one or two individuals, with miles between populations. This subspecies
is threatened by destruction or modification of habitat due to pigs,
goats, and deer, and by nonnative plants that outcompete and displace
native plants. Predation by pigs, goats, deer, and rats is a likely
threat to this species. Seedlings have rarely been observed in the
wild. Seeds germinate in cultivation, but most die soon thereafter. It
is uncertain if this rarity of reproduction is typical of this
subspecies, or if it is related to habitat disturbance. Feral pigs have
been fenced out of a few of the populations of this subspecies, and
nonnative plants have been reduced in a few populations that are
fenced. However, these threats are not controlled and are ongoing in
the many remaining, unfenced populations. The threats are of high
magnitude because habitat degradation, nonnative plants and predation
could affect the ability of the subspecies to survive. The threats are
ongoing, and thus are imminent. Therefore, we retained an LPN of 3 for
this subspecies.
Korthalsella degeneri (Hulumoa) - We have not updated our
assessment for this species, as we are currently developing a proposed
listing rule.
Leavenworthia crassa (Gladecress) - The following information is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. This species of
gladecress is a component of glade flora, occurring in association with
limestone outcroppings. Leavenworthia crassa is endemic to a 13-mile
radius area in Lawrence and Morgan Counties, Alabama, where only six
populations of this species are documented. Glade habitats today have
been reduced to remnants fragmented by agriculture and development.
Populations of this species are now located in glade-like areas
exhibiting various degrees of disturbance including pastureland,
roadside rights-of-way, and cultivated or plowed fields. The most
vigorous populations of this species are located in areas which receive
full, or near full, sunlight with limited herbaceous competition. The
magnitude of threat is high because with the limited number of
populations, the threats from herbicide use, and degradation of habitat
by dumping, ATV use, and competition from other plants including
nonnative species, could result in direct mortality or reduced
reproductive capacity of the species. This species appears to be able
to adjust to periodic disturbances and the potential impacts to
populations from competition, exotics, and herbicide use are
nonimminent. In addition, at this time, we know of no projects planned
in the area that would lead to the destruction of habitat where this
species is currently located. Thus, we assigned an LPN of 5 to this
species.
Leavenworthia texana (Texas golden gladecress) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
The gladecress occurs only on the Weches outcrops of east Texas in San
Augustine and Sabine counties. The Weches geologic formation consists
of a layer of calcareous sediment, lying above a layer of glauconite
clay deposited up to 50 million years ago. Erosion of this complex has
produced topography of steep, flat-topped hills and escarpments, as
well as the unique ecology of Weches glades: islands of thin, loamy,
seepy, alkaline soils that support open-sun, herbaceous, and highly
diverse and specialized plant communities.
The gladecress was historically recorded at eight sites, all in a
narrow region along north San Augustine and Sabine counties. All sites
are on private land. The species has been extirpated from three sites
due to glauconite mining. Two sites are currently closed to visitors.
The Sabine County site supported 1,000 plants within 9 square meters
(97 square feet) in 2007. The Tiger Creek site in San Augustine County
(less than 0.1 hectare (.2 acre) in size) was found to have about 200
gladecress in 2007. The Kardell site (less than 9 square meters (97
square feet)) has supported 400-500 plants in past years, but none in
2005. An introduced population in Nacogdoches County numbered about
1,000 within an area of about 18 square meters (194 square feet) in
2007.
Historic gladecress habitat has been affected by highway
construction, residential development, conversion to pasture and
cropland, widespread use of herbicide, overgrazing, and glauconite
mining. The primary threat to existing gladecress populations is the
invasion of nonnative and weedy shrubs and vines (primarily Macartney
rose (Rosa bracteata) and Japanese honeysuckle (Lonicera japonica)).
All known sites are undergoing severe degradation by the incursion of
nonnative shrubs and vines, which restrict both growth and reproduction
of the gladecress. Brush clearing carried out in 1995 resulted in the
reappearance of gladecress after a 10-year absence at one site.
However, nonnative shrubs have again invaded this area. More effective
control measures for nonnative species, such as burning and selective
herbicide use, need to be tested and monitored. The small number of
known sites also makes the gladecress vulnerable to extreme natural
disturbance events. A severe drought in 1999 and 2000 had a pronounced
adverse effect on gladecress reproduction. Since the threat from
nonnative plants severely affects all known sites, the magnitude of
threats is high. The threats are imminent, since they are ongoing.
Therefore, we retain an LPN of 2 for the Texas golden gladecress.
Lesquerella globosa (Desvaux) Watson (Short's bladderpod) - The
following summary is based on information contained in our files. No
new information was provided in the petition we received on May 11,
2004. Short's bladderpod is a perennial member of the mustard family
that occurs in Indiana (1 location), Kentucky (6 locations), and
Tennessee (18 locations). It grows on steep, rocky, wooded slopes,
talus areas, along cliff tops and bases, and on cliff ledges. It is
usually associated with south to west facing calcareous outcrops
adjacent to rivers or streams. Road construction and road maintenance
have played a significant role in the decline of L.
[[Page 75225]]
globosa. Specific activities that have affected the species in the past
and may continue to threaten it include bank stabilization, herbicide
use, mowing during the growing season, grading of road shoulders, and
road widening or repaving. Sediment deposition during road maintenance
or from other activities also potentially threatens the species.
Because the natural processes that maintained habitat suitability and
competition from invasive nonnative vegetation have been interrupted at
many locations, active habitat management is necessary at those sites.
The threats are high in magnitude because they have the potential to
significantly affect the survival and reproductive capacity of the
species, in particular since many of the populations are small. Based
upon the number of populations and the anticipation that most of these
threats will not be realized in the next several years, the threats are
nonimminent. Therefore, we assigned an LPN of 5 to this species.
Linum arenicola (Sand flax) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Sand flax is found in pine
rockland and marl prairie habitats which requires periodic wildfires in
order to maintain an open, shrub free subcanopy and reduce litter
levels. Based upon available data, there are 11 extant occurrences of
sand flax; 11 others are extirpated or destroyed. Only small and
isolated occurrences remain in a restricted range of southern Florida
and the Florida Keys.
Habitat loss and degradation due to development is a major threat;
most of the remaining occurrences are on private land or non-
conservation public land. However, much of the pine rocklands on Big
Pine Key are protected from development. Nearly all remaining
populations are threatened by fire suppression, difficulty in applying
prescribed fire, road maintenance activities, exotic species, or
illegal dumping. However, some efforts are underway to use prescribed
fire and control exotics on conservation lands where this species
occurs. Sand flax is vulnerable to natural disturbances, such as
hurricanes, tropical storms, and storm surges. Hurricane Wilma
inundated most of its habitat on Big Pine Key in 2005, and plants were
not found 8-9 weeks post-storm; the density of sand flax declined to
zero in all management units at The Nature Conservancy's preserve in
2006. We also consider sea level rise to be a substantial threat that
will reduce the extent of upland habitats. Due to the small and
fragmented nature of the current population, stochastic events,
disease, or genetic bottlenecks may strongly affect this species.
Reduced pollinator activity and suppression of pollinator populations
from pesticides used in mosquito control and decreased seed production
due to increased seed predation in a fragmented wildland urban
interface may also affect sand flax; however, not enough information is
known on this species' reproductive biology or life history to assess
these potential threats. Overall, the magnitude of threats is high
because they are all present habitat modifications that limit the
continued existence of the species, and most threats are ongoing and
thus are imminent. Therefore, we assigned an LPN of 2 to this species.
Linum carteri var. carteri (Carter's small-flowered flax) - The
following summary is based on information contained in our files. No
new information was provided in the petition we received on May 11,
2004. This plant occupies open sites in pinelands of Miami-Dade County,
Florida. Currently, there are 10 known occurrences. Occurrences with
fewer than 100 individuals are located on three county-owned preserves.
A site with more than 100 plants is owned by the U.S. government, but
the site is not managed for conservation. The 10 existing occurrences
are small and vulnerable to habitat loss, which is exacerbated by
habitat degradation due to fire suppression, the difficulty of applying
prescribed fire to pine rocklands, and threats from exotic plants.
Remaining habitats are fragmented. Non-compatible management practices
are also a threat at most protected sites; several sites are mowed
during the flowering and fruiting season. The species is vulnerable to
natural disturbances, such as hurricanes, tropical storms, and storm
surges. This species exists in such small numbers at so few sites, that
it may be difficult to develop and maintain viable occurrences on the
available conservation lands. Although no population viability analysis
has been conducted for this plant, indications are that existing
occurrences are at best marginal and it is possible that none are truly
viable. As a result, the magnitude of threats is high. The threats are
ongoing, and thus are imminent. Therefore, we assigned an LPN of 3 to
this plant variety.
Melicope christophersenii (Alani) - We have not updated our
assessment for this species, as we are currently developing a proposed
listing rule.
Melicope hiiakae (Alani) - We have not updated our assessment for
this species, as we are currently developing a proposed listing rule
for this species.
Melicope makahae (Alani) - We have not updated our assessment for
this species, as we are currently developing a proposed listing rule.
Myrsine fosbergii (Kolea) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Myrsine fosbergii is a
branched shrub or small tree found in cloud swept ridges and wet forest
on Kauai and Oahu, Hawaii. This species is currently known from 11
populations totaling approximately 58 individuals on Kauai and from 8
populations totaling between 73 and 83 individuals in the Koolau
Mountains of Oahu. Myrsine fosbergii is threatened by feral pigs and
goats that degrade and destroy habitat and may prey upon the plant, and
nonnative plants that compete for light and nutrients. Although there
are plans to fence and remove ungulates from the Helemano area of Oahu,
which may benefit this species, no conservation measures have been
taken to date to alleviate these threats for this species. Feral pigs
and goats are found throughout the known range of M. fosbergii, as are
nonnative plants. The threats from feral pigs, goats, and nonnative
plants are of a high magnitude because they pose a severe threat
throughout the limited range of this species, and they are ongoing and
therefore imminent. We retained an LPN of 2 for this species.
Myrsine vaccinioides (Kolea) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Myrsine vaccinioides is a
small branched shrub found in shrubby bogs on Maui, Hawaii. This
species is found scattered throughout the bogs of west Maui, totaling
approximately 500 individuals. Myrsine vaccinioides is threatened by
feral pigs that degrade and destroy habitat, and nonnative plants that
compete for light and nutrients. Pig exclusion fences protect some
individuals of this species, and nonnative plants have been reduced
around some individuals that are fenced. However, these ongoing
conservation efforts benefit only a small number of the known
individuals. Further, nonnative plants will probably never be
completely eradicated because new propagules are constantly being
dispersed into the fenced areas from surrounding, unmanaged lands. The
threats are of a high magnitude because they pose a severe threat
throughout the limited range of the species and are
[[Page 75226]]
ongoing, and thus imminent. Therefore, we retained an LPN of 2 for this
species.
Narthecium americanum (Bog asphodel) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. Bog asphodel is a
perennial herb that is found in savannah areas, usually with water
moving through the substrate, as well as in sandy bogs along streams
and rivers. The historic range of bog asphodel included New York, New
Jersey, Delaware, North Carolina, and South Carolina, but it is now
only found within the Pine Barrens region of New Jersey.
As an obligate wetland species, N. americanum is threatened by
changes in hydrology, loss of habitat due to filling or draining of
wetlands, flooding as a result of reservoir construction, and
conversion of natural wetlands to commercial cranberry bogs. In the
Pine Barrens region, the Pinelands Commission is responsible for
issuing the State-assumed Clean Water Act Section 404 permits. The
Pinelands Commission grants wetland exemptions to cranberry production
and other agricultural uses. However, illegal wetland filling is
occurring. For example, a cranberry expansion was illegally completed
without a State permit a few years ago. In addition, activities not
needing State or federal permits are occurring in uplands that are
indirectly affecting the wetlands. In wetlands supporting bog asphodel,
natural succession of vegetation from emergent (herbaceous) to forested
wetlands may also be contributing to the species' decline. Suppression
of natural wildfires that would retard succession or create open
wetland savannahs may be a factor in the decline of the species. Other
factors adversely affecting N. americanum include trampling, erosion,
and siltation caused by recreationists on foot or using off-road
vehicles. Approximately 75 percent of known extant populations occur on
State-owned lands. These populations are threatened by recreational use
and erosion, which are moderate threat because they are localized and
occasional. We are working with the New Jersey Department of
Environmental Protection to abate these threats. Approximately 20
percent of the known extant sites are on privately owned lands, many of
which are threatened by habitat degradation from on-site or adjacent
residential or commercial development. These threats could eliminate
the bog asphodel from those sites, but because they only represent 20
percent of the occurrences, the threats are moderate overall. The
remaining 5 percent of known extant sites occur on federal lands. The
threats are imminent because conversion to cranberry bogs, natural
succession, wildfire suppression, recreational impacts, and erosion are
all ongoing. Overall, based on these imminent, moderate threats, we
retain a listing priority number of 8 for this species.
Nothocestrum latifolium (Aiea) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Aiea is a small tree found in
dry to mesic forest and diverse mesic forests on Kauai, Oahu, Maui,
Molokai, and Lanai, Hawaii. Nothocestrum latifolium is known from 20
populations totaling fewer than 1,100 individuals. This species is
threatened by feral pigs, goats, and axis deer that degrade and destroy
habitat and may prey upon it; by nonnative plants that compete for
light and nutrients; and by the loss of pollinators that negatively
affect the reproductive viability of the species. Ungulates have been
fenced out of some areas where N. latifolium currently occurs, and
nonnative plants have been reduced in some populations that are fenced.
However, these ongoing conservation efforts for this species benefit
only a few of the known populations. The threats are not controlled and
are ongoing in the remaining unfenced populations. In addition, little
regeneration is observed in this species. The threats are of a high
magnitude, since they are severe enough to affect the continued
existence of the species. The threats are imminent, since they are
ongoing. Therefore, we retained an LPN of 2 for this species.
Ochrosia haleakalae (Holei) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Holei is a tree found often
on lava in dry to mesic forest on the islands of Hawaii and Maui,
Hawaii. This species is currently known from 11 populations totaling
fewer than 130 individuals. Ochrosia haleakalae is threatened by fire;
by feral pigs, goats, and cattle that degrade and destroy habitat and
may directly prey upon it; and by nonnative plants that compete for
light and nutrients. Feral pigs, goats, and cattle have been fenced out
of one wild and one outplanted population on private lands on the
island of Maui and one outplanted population in Hawaii Volcanoes
National Park on the island of Hawaii. Nonnative plants have been
reduced in the fenced areas. No known conservation measures have been
taken to date for the remaining populations on the islands of Maui and
Hawaii. The threat from fire is of a high magnitude and imminent
because no control measures have been undertaken to address this threat
that could adversely affect O. haleakalae as a whole. The threats from
feral pigs, goats, and cattle are ongoing to the unfenced populations
of O. haleakalae. The threat from nonnative plants is ongoing and
imminent, and of a high magnitude to the wild populations on both
islands, since this threat has the potential to adversely affect the
continued existence of this species. Therefore, we retained an LPN of 2
for this species.
Pediocactus peeblesianus var. fickeiseniae (Fickeisen plains
cactus) - The following summary is based on information contained in
our files. No new information was provided in the petition we received
on May 11, 2004. The Fickeisen plains cactus is a small cactus known
from the Gray Mountain vicinity to the Arizona strip in Coconino,
Navajo, and Mohave Counties, Arizona. The cactus grows on exposed
layers of Kaibab limestone on canyon margins and well-drained hills in
Navajoan desert or grassland. In 1999, the Arizona Game and Fish
Department noted 23 occurrences of the species, including historical
ones. The species is located on Bureau of Land Management (BLM), Forest
Service, tribal, and possibly State lands. Recent reports from the BLM
and Navajo Nation describe populations of the species as being in
decline. The main human-induced threats to this cactus are off-road
vehicles and trampling associated with livestock grazing. Monitoring
data has detected mortality associated with livestock grazing. Illegal
collection of this species has been noted in the past, but we do not
know if it is a continuing threat. The populations that have been
monitored have been affected, in part, by the continuing drought. There
has been very low recruitment, and rabbits and rodents have consumed
adult plants, since there is reduced forage available to these animals
during drought conditions. Given that there are only a few known
populations, that the range of this taxon is limited, and that the
majority of the known populations on BLM lands and the Navajo Nation
are experiencing declines in populations as a result of the combined
threats, we conclude that the threats are of a high magnitude. Since
all of the locations of this variety on BLM lands are within grazing
allotments and the monitoring data provide evidence that trampling of
plants does occur, these threats are ongoing. Therefore, we assigned
this plant variety an LPN of 3.
[[Page 75227]]
Penstemon debilis (Parachute beardtongue) - We have not updated our
assessment for this species, as we are currently developing a proposed
listing rule.
Penstemon scariosus var. albifluvis (White River beardtongue) - The
following summary is based on information contained in our files and
the petition we received on October 27, 1983. The White River
beardtongue is restricted to calcareous soils derived from oil shale
barrens of the Green River Formation in the Uinta Basin of northeastern
Utah and adjacent Colorado. There are 14 occurrences known in Utah and
1 in Colorado. Most of the occupied habitat of the White River
beardtongue is within developed and expanding oil and gas fields. The
location of the species' habitat exposes it to destruction from road,
pipeline, and well-site construction in connection with oil and gas
development. Recreational off-road vehicle use, heavy grazing by
livestock, and wildlife and livestock trampling are additional
potential threats. The threats are of high magnitude because they
involve habitat destruction that could limit the continued existence of
this plant variety. The threats are nonimmient because increased
threats associated with oil and gas and oil shale development will
probably not be increasing substantially within the next year. Oil
shale development remains uncertain within the species' habitat, and is
not expected to be a significant factor in the near term. Therefore,
based on current information, we retained an LPN of 6.
Peperomia subpetiolata (Ala ala wai nui) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. Ala ala wai nui
is a short-lived perennial herb found in montane mesic forest on Maui,
Hawaii. This species is known from one occurrence consisting of two
subpopulations on windward east Maui, totaling 23 individuals. Further
study of the occurrence indicates that the plants may actually
represent clones of only six genetically distinct individuals. There is
some question as to the taxonomy of these populations, as putative
hybrids have been found in the same areas. Peperomia subpetiolata is
threatened by feral pigs that may eat this plant and degrade and
destroy habitat, and by nonnative plants that compete for light and
nutrients. Individuals that occur within the Waikamoi Preserve may
benefit from fencing and management actions; however, all of the
threats occur range-wide. Te threats are of a high magnitude because
they pose a significant threat to the species resulting in direct
mortality or reduced reproductive capacity, and are ongoing and
therefore imminent. Therefore, we retained an LPN of 2 for this
species.
Phacelia submutica (DeBeque phacelia) - We have not updated our
assessment for this species, as we are currently developing a proposed
listing rule.
Phyllostegia bracteata (no common name) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. Phyllostegia
bracteata is a scandent perennial herb found in Metrosideros-
Cheirodendron-Dicranopteris (ohia-olapa-uluhe) montane wet forest on
the island of Maui, Hawaii. Currently this species is known from five
populations totaling no more than 12 to 17 individuals on east and west
Maui. Phyllostegia bracteata is threatened by feral pigs that may
directly prey upon it and degrade and destroy habitat, nonnative plants
that compete for light and nutrients, and reduced reproductive vigor
and randomly occurring natural events. The threats to P. bracteata from
pigs and nonnative plants are of a high magnitude and imminent because
in light of their severity and the limited population size of the
species, they pose a risk to the species range-wide, are ongoing, and
are not subject to any control efforts. Therefore, we retained an LPN
of 2 for this species.
Phyllostegia floribunda (no common name) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. This species is
an erect subshrub found in mesic to wet forest on the island of Hawaii,
Hawaii. This species is known from 10 locations totaling fewer than 270
naturally occurring and outplanted individuals on State, private, and
Federal lands. Phyllostegia floribunda is threatened by feral pigs that
degrade and destroy habitat, and nonnative plants that compete for
light and nutrients. The National Park Service, The Nature Conservancy,
and the State have outplanted more than 170 individuals at Olaa Forest
Reserve, Kona Hema, and Waiakea Forest Reserve (greater than 50, 20
individuals, and 100 individuals, respectively). Fences protect
approximately seven populations on private, State, and National Park
lands. Nonnative plants have been reduced in these fenced areas.
However, no conservation efforts have been implemented for the unfenced
populations. Overall, the threats are moderate because the conservation
efforts, for over half of the populations, reduces the severity of the
threats. The threats are ongoing in the unfenced portions and must be
constantly managed in the fenced portions. Therefore, the threats are
imminent. We retained an LPN of 8 because the threats are of moderate
magnitude and are imminent for the majority of the populations.
Physaria tuplashensis (White Bluffs bladder-pod) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
White Bluffs bladder-pod is a low-growing, herbaceous, short-lived,
perennial plant in the Brassicaceae (mustard) family. Historically and
currently, White Bluffs bladder-pod has only been known from a single
population that occurs along the White Bluffs of the Columbia River in
Franklin County, Washington. The entire range of the species is a
narrow band, approximately 33 feet (10 meters) wide by 10.6 miles (17
kilometers) long, at the upper edge of the bluffs. The species occurs
only on cemented, highly alkaline, calcium carbonate paleosol (a
``caliche'' soil) and is believed to be a ``calciphile.''
Approximately 35 percent of the known range of the species has been
moderately to severely affected by landslides, an apparently permanent
destruction of the habitat. The entire population of the species is
down-slope of irrigated agricultural land, the source of the water
seepage causing the mass failures and landslides. Other significant
threats include the presence of invasive plants, and some potential use
of the habitat by recreational off road vehicles. While P. tuplashensis
is inherently vulnerable because it is a narrow endemic, the threats
are nonimminent since they are unlikely to occur in the immediate
future, except the threat from invasive plants. Invasive plants are
present in the vicinity, but have not yet been described as a
significant problem. Currently, we know of no plans to expand or
significantly modify the existing agriculture activities in areas
adjacent to the population. In addition, deliberate modification of the
species' immediate habitat is unlikely due to its location and 85
percent Federal ownership. However, because the threats could
negatively affect the only known population of this species, the
threats are high in magnitude. Therefore, we assigned an LPN of 5 to
this species. We are currently reviewing information from recent site
visits and the effects of a fire during the summer
[[Page 75228]]
of 2007 to determine whether to change the LPN next year.
Platanthera integrilabia (Correll) Leur (White fringeless orchid) -
The following summary is based on information contained in our files.
No new information was provided in the petition we received on May 11,
2004. Platanthera integrilabia is a perennial herb that grows in
partially, but not fully, shaded, wet, boggy areas at the head of
streams and on seepage slopes in Alabama, Georgia, Kentucky and
Tennessee. Historically, there were at least 90 populations of P.
integrilabia. Currently there are only 53 extant sites supporting the
species.
Several populations have been extirpated due to road, residential,
and commercial construction, and to projects that altered soil and site
hydrology such that suitability for the species was reduced. Several of
the known populations are in or adjacent to powerline rights-of-way.
Mechanical clearing of these areas may benefit the species by
maintaining adequate light levels; however, the use of herbicides in
these areas could pose a significant threat to the species. All-terrain
vehicles have damaged several sites and pose a threat at most sites.
Most of the known sites for the species occur in areas that are managed
specifically for timber production. Timber management is not
necessarily incompatible with the protection and management of the
species, but care must be taken during timber management to ensure that
the hydrology of the bogs that support the species is not altered.
Natural succession can result in decreased light levels. Because of the
species dependence upon moderate to high light levels, some type of
active management to prevent complete canopy closure is required at
most locations. Collecting for commercial and other purposes is a
potential threat. Herbivory (primarily deer) threatens the species at
several sites. Due to the alteration of habitat and changes in natural
conditions, protection and recovery of this species is dependent upon
active management rather than just preservation of habitat. Invasive,
nonnative plants such as Japanese honeysuckle and kudzu threaten
several sites. Overall, the magnitude of threats to this species is
high because they result in direct mortality or significantly decrease
the reproductive capacity of this species. Because we anticipate that
most of these threats will not be realized in the near future, the
threats are nonimminent. Therefore, we assigned an LPN of 5 to this
species.
Platydesma cornuta var. cornuta (no common name) - We have not
updated our assessment for this species, as we are currently developing
a proposed listing rule.
Platydesma cornuta var. decurrens (no common name) - We have not
updated our assessment for this species, as we are currently developing
a proposed listing rule.
Platydesma remyi (no common name) - The following summary is based
on information contained in our files. No new information was provided
in the petition we received on May 11, 2004. Platydesma remyi is a
shrub or shrubby tree found in wet forests on old volcanic slopes on
the island of Hawaii, Hawaii. This species is known from two
populations totaling fewer than 50 individuals. Platydesma remyi is
threatened by feral pigs and cattle that degrade and destroy habitat,
nonnative plants that compete for light and nutrients, reduced
reproductive vigor, and stochastic extinction due to naturally
occurring events. Only one individual is included in a rare plant
exclosure in the Laupahoehoe Natural Area Reserve. The threats are
ongoing and therefore imminent, and of a high magnitude because of
their severity; the threats cause direct mortality or significantly
reduce the reproductive capacity of the species throughout its limited
range. Therefore, we retained an LPN of 2 for this species.
Pleomele forbesii (Hala pepe) - We have not updated our assessment
for this species, as we are currently developing a proposed listing
rule.
Potentilla basaltica (Soldier Meadow cinquefoil or basalt
cinquefoil) - The following summary is based on information contained
in our files; the petition we received on May 11, 2004, provided no
additional information on the species. Soldier Meadow cinquefoil is a
low growing, rhizomatous, herbaceous perennial that is associated with
alkali meadows, seeps, and occasionally marsh habitats bordering
perennial thermal springs, outflows, and meadow depressions. In Nevada,
the species is known only from Soldier Meadow in Humboldt County. At
Soldier Meadow, there are 10 discrete known occurrences within an area
of about 70 acres that support about 130,000 individuals. In
northeastern California, a single population occurs in Lassen County.
The California population occupies less than one acre on private lands
and supports fewer than 1,000 plants. The species and its habitat are
threatened by recreational use in the areas where it occurs, and
ongoing impacts of past water diversions livestock grazing, and off-
highway vehicle travel. Because of several conservation measures
implemented by the Bureau of Land Management, the magnitude of threat
to the species is moderate since the measures have reduced the effect
of the threats on the species. All remaining threats are nonimminent
and involve long-term changes to the habitat for the species resulting
from past impacts. Therefore, we assigned an LPN of 11 to this species.
Pseudognaphalium (Gnaphalium) sandwicensium var. molokaiense
(Enaena) - The following summary is based on information contained in
our files. No new information was provided in the petition we received
on May 11, 2004. Pseudognaphalium sandwicensium var. molokaiense is a
perennial herb found in strand vegetation in dry consolidated dunes on
Molokai and Maui, Hawaii. This variety is known from a total of five
populations totaling approximately 2,000 individuals in the Moomomi
area on the island of Molokai, and from two populations of a few
individuals at Waiehu dunes and at Puu Kahulianapa on west Maui.
Pseudognaphalium sandwicensium var. molokaiense is threatened by axis
deer and cattle that degrade and destroy habitat and possibly prey upon
it, and by nonnative plants that compete for light and nutrients.
Potential threats also include collection for lei and off-road vehicles
that directly damage plants and degrade habitat. While ungulate
exclusion fences protect one population on Molokai and nonnative plant
control has been implemented in this population, no conservation
efforts have been initiated to date for the other populations on
Molokai or for the individuals on Maui. The ongoing threats from axis
deer, cattle, nonnative plants, collection, and off-road vehicles are
of a high magnitude because no control measures have been undertaken
for the Maui population and the threats are significant to this plant.
Therefore, we retained an LPN of 3 for this plant variety.
Psychotria hexandra ssp. oahuensis var. oahuensis (Kopiko) - We
have not updated our assessment for this species, as we are currently
developing a proposed listing rule.
Pteralyxia macrocarpa (Kaulu) - We have not updated our assessment
for this species, as we are currently developing a proposed listing
rule.
Ranunculus hawaiensis (Makou) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Ranunculus hawaiensis is an
erect or ascending perennial herb found in mesic to wet forest
dominated by
[[Page 75229]]
Metrosideros polymorpha and Acacia koa with scree substrate on Maui and
the island of Hawaii, Hawaii. Populations formerly within Haleakala
National Park have been extirpated. This species is currently known
from fewer than 12 individuals in 4 populations: three wild populations
occur on Hawaii totaling 8 individuals; 1 wild population at Waikamoi
(on Maui) was last observed in 1995, and the second Maui population
(Kukui planeze) was not relocated on a survey conducted in 2006.
Ranunculus hawaiensis is threatened by direct predation by slugs, feral
pigs, goats, cattle, mouflon, and sheep; by pigs, goats, cattle,
mouflon and sheep that degrade and destroy habitat; and by nonnative
plants that compete for light and nutrients. Three populations have
been outplanted into protected exclosures; however, feral ungulates and
nonnative plants are not controlled in the remaining, unfenced
populations. In addition, the threat from slugs is of a high magnitude
because slugs occur throughout the limited range of this species and no
effective measures have been undertaken to control them or prevent them
from causing significant adverse impacts to this species. Therefore,
the threats from pigs, goats, cattle, mouflon, sheep, slugs, and
nonnative plants are of a high magnitude, and ongoing (imminent) for R.
hawaiensis. We retained an LPN of 2 for this species.
Ranunculus mauiensis (Makou) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Ranunculus mauiensis is an
erect to weakly ascending perennial herb found in open sites in mesic
to wet forest and along streams on the islands of Maui, Kauai, and
Molokai, Hawaii. This species is currently known from 1 individual on
Molokai, 60 individuals on Maui, and approximately 46 individuals on
Kauai. Ranunculus mauiensis is threatened by feral pigs, goats, deer,
and slugs that consume it; by habitat degradation and destruction by
feral pigs, goats and deer; and by nonnative plants that compete for
light and nutrients. Feral pigs have been fenced out of the Maui
populations of R. mauiensis, and nonnative plants have been reduced in
the fenced areas. One individual occurs in the Kamakou Preserve on
Molokai, managed by The Nature Conservancy. However, ongoing
conservation efforts benefit only the Maui and Molokai individuals, and
absent conservation efforts for the Kauai individuals, the threats
continue to be of a high magnitude on Kauai. Therefore, since half of
the individuals are found on Kauai threats to the species overall are
also of a high magnitude because these threats present a significant
risk to the continued existence of R. mauiensis. In addition, the
threats are imminent because they are ongoing in the Kauai and the
majority of the Maui populations. Therefore, we retained an LPN of 2
for this species.
Rorippa subumbellata (Tahoe yellow cress) - The following summary
is based on information contained in our files and the petition we
received on December 27, 2000. Tahoe yellow cress is a small perennial
herb known only from the shores of Lake Tahoe in California and Nevada.
Data collected over the last 25 years generally indicate that species
occurrence fluctuates yearly as a function of both lake level and the
amount of exposed habitat. Records kept since 1900 show a preponderance
of years with high lake levels that isolate and reduce Tahoe yellow
cress occurrences at higher beach elevations. From the standpoint of
the species, less favorable peak years have occurred almost twice as
often as more favorable low-level years. Annual surveys are conducted
to determine population numbers, site occupancy, and general
disturbance regime. During the 2003 and 2004 annual survey period, the
lake level was approximately 6,224 ft (1,898 m); 2004 was the fourth
consecutive year of low water. Tahoe yellow cress was present at 45 of
the 72 sites surveyed (65 percent occupied), up from 15 sites (19
percent occupied) in 2000 when the lake level was high at 6,228 ft.
Approximately 25,200 stems were counted or estimated in 2003, whereas
during the 2000 annual survey, the estimated number of stems was 4,590.
Lake levels began to rise again in 2005 and less habitat was available;
intermediate lake levels were expected in 2008.
Many Tahoe yellow cress sites are intensively used for commercial
and public purposes and are subject to various activities such as
erosion control, marina developments, pier construction, and
recreation. The U.S. Forest Service, California Tahoe Conservancy, and
California Department of Parks and Recreation have management programs
for Tahoe yellow cress that include monitoring, fenced enclosures, and
transplanting efforts when funds and staff are available. Public
agencies (including the Service), private landowners, and environmental
groups collaborated to develop a conservation strategy coupled with a
Memorandum of Understanding/Conservation Agreement. The conservation
strategy, completed in 2003, contains goals and objectives for recovery
and survival, a research and monitoring agenda, and will serve as the
foundation for an adaptive management program. Because of the continued
commitments to conservation demonstrated by regulatory and land
management agencies participating in the conservation strategy, we have
determined the threats to Tahoe yellow cress from various land uses are
moderate in magnitude. In high lake level years such as 2005, however,
recreational use is concentrated within Tahoe yellow cress habitat, and
this threat in particular is ongoing and imminent. Therefore, we are
maintaining an LPN of 8 for this species.
Schiedea pubescens (Maolioli) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Schiedea pubescens is a
reclining or weakly climbing vine found in diverse mesic to wet forest
on Maui, Molokai, and Hawaii. Currently, this species is known from six
populations totaling between 29 and 71 individuals on Maui, from four
populations totaling 25 individuals on Molokai, and from one population
of 4 to 6 individuals on the island of Hawaii. Schiedea pubescens is
threatened by feral goats that consume it and degrade and destroy
habitat, and by nonnative plants that compete for light and nutrients.
Feral ungulates have been fenced out of the population of S. pubescens
on Hawaii. Feral goats have been fenced out of a few of the west Maui
populations of S. pubescens. Nonnative plants have been reduced in the
populations that are fenced on Maui. However, the threats are not
controlled and are ongoing in the remaining unfenced populations on
Maui and the three populations on Molokai. In light of the extremely
low number of individuals of this species, the threats from goats and
nonnative plants are of a high magnitude because they pose a
significant threat to the species, and imminent because they are
ongoing with respect to most of the populations. Therefore, we retained
an LPN of 2 for this species.
Schiedea salicaria (no common name) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. Schiedea
salicaria is an erect subshrub or shrub found on ridges and steep
slopes in dry shrubland on Maui, Hawaii. Currently, this species is
declining throughout its range, and is known from four populations
totaling approximately 260 individuals. This
[[Page 75230]]
species is threatened by cattle that may directly prey upon it and
degrade and destroy habitat, fire, and nonnative plants that compete
for light and nutrients. This species is represented in an ex-situ
collection. All of the threats occur range-wide, and no efforts for
their control or eradication are being undertaken. We retained an LPN
of 2. The threats are imminent because they are ongoing, and they are
of a high magnitude because, in light of their severity and the small
size of the population, they have the potential to adversely affect the
species.
Sedum eastwoodiae (Red Mountain stonecrop) - The following summary
is based on information contained in our files and information provided
by the California Department of Fish and Game. The petition we received
on May 11, 2004 provided no new information on the species. Red
Mountain stonecrop is a perennial succulent which occupies relatively
barren, rocky openings and cliffs in lower montane coniferous forests,
between 1,900 and 4,000 feet elevation. Its distribution is limited to
Red Mountain, Mendocino County, California, where it occupies 30 acres
scattered over 4 square miles. Total population size is estimated at
between 5,300 and 23,000 plants, contained within 27 habitat polygons.
Intensive monitoring suggests considerable annual variation in plant
seedling success and inflorescence production; stonecrop density has
varied from year-to-year. The primary threat to the species is the
potential for surface mining for chromium and nickel. The entire
distribution of Red Mountain stonecrop is either owned by mining
interests, or is covered by mining claims; none of the claims are
currently active and therefore the primary threat from mining is
nonimminent. Surface mining would destroy habitat suitability for this
species. The species is also believed threatened by tree and shrub
encroachment into its habitat, in absence of fire. Given the high
magnitude and nonimminent threats to the small, scattered populations
of this plant species, we assigned an LPN of 5 to Red Mountain
stonecrop.
Sicyos macrophyllus (Anunu) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Sicyos macrophyllus is a
perennial vine found in wet Metrosideros polymorpha (ohia) forest and
subalpine Sophora chrysophylla-Myoporum sandwicense (mamane-naio)
forest on the island of Hawaii, Hawaii. This species is known from 11
populations totaling fewer than 50 individuals in the Kohala and Mauna
Kea areas and in Hawaii Volcanoes National Park (Puna area) on the
island of Hawaii. It appears that a naturally occurring population at
Kipuka Ki in Hawaii Volcanoes National Park is reproducing by seeds,
but seeds have not been successfully germinated under nursery
conditions. This species is threatened by feral pigs and sheep that
degrade and destroy habitat, and nonnative plants that compete for
light and nutrients. Feral pigs have been fenced out of some of the
areas where S. macrophyllus currently occurs, but the fences do not
exclude sheep. Nonnative plants have been reduced in the populations
that are fenced. However, the threats are not controlled and are
ongoing in the remaining, unfenced populations, and are, therefore,
imminent. Similarly the threat from sheep is ongoing and imminent in
all populations, because the current fences do not exclude sheep. In
addition, all of the threats are of a high magnitude because habitat
degradation and competition from nonnative plants present a risk to the
species, resulting in direct mortality or significantly reducing the
reproductive capacity. Therefore, we retained an LPN of 2 for this
species.
Solanum nelsonii (popolo) - The following summary is based on
information contained in our files. No new information was provided in
the petition we received on May 11, 2004. Solanum nelsonii is a
sprawling or trailing shrub found in coral rubble or sand in coastal
sites. This species is known from populations in Molokai (approximately
300 plants) and the northwestern Hawaiian Islands: Midway
(approximately 260 plants), Laysan (approximately 490 plants), Pearl
and Hermes (unknown number of individuals), Nihoa (8,000 to 15,000
adult plants); and from five individuals last observed on the Island of
Hawaii in 1995. On Molokai, S. nelsonii is moderately threatened by
ungulates which degrade and destroy habitat, and that may eat it, and
on Molokai and the northwestern Hawaiian Islands by nonnative plants
that outcompete and displace it. Ungulate exclusion fences, routine
fence monitoring and maintenance, and weed control protect the
population of S. nelsonii on Molokai. Limited weed control is conducted
in the northwestern Hawaiian Islands. In addition, S. nelsonii is
likely threatened by being eaten by a nonnative grasshopper,
Schistocerca nitens, in the northwestern Hawaiian Islands. Currently no
control measures are in place for this grasshopper. These threats are
of moderate magnitude because of the relatively large number of plants,
and are imminent for the majority of the populations because they are
ongoing and are not being controlled. We therefore retained an LPN of 8
for this species.
Stenogyne cranwelliae (no common name) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. Stenogyne
cranwelliae is a creeping vine found in wet forest dominated by
Metrosideros polymorpha on the island of Hawaii, Hawaii. Stenogyne
cranwelliae is known from 11 populations totaling fewer than 100
individuals. This species is threatened by feral pigs that degrade and
destroy habitat, and nonnative plants that compete for light and
nutrients. In addition, this species is potentially threatened by rats
that may directly prey upon it, and by randomly occurring natural
events such as hurricanes and landslides. All of the threats occur
range-wide, and no efforts for control or eradication are being
undertaken for the pigs, nonnative plants, or rats. These threats are
sufficient to adversely affect the species particularly in light of its
small population size. We retained an LPN of 2 because the threats are
of a high magnitude and are ongoing, so are imminent.
Symphyotrichum georgianum (Georgia aster) - The following summary
is based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. Georgia aster is
a relict species of post oak savanna/prairie communities that existed
across much of the southeast prior to widespread fire suppression and
extirpation of large native grazing animals. Most remaining populations
survive adjacent to roads, utility rights-of-way, and other openings
where current land management mimics natural disturbance regimes.
Georgia aster currently occurs in the states of Alabama, Georgia, North
Carolina and South Carolina. The species is presumed extant in three
counties in Alabama, ten counties in Georgia, nine counties in North
Carolina, and eleven counties in South Carolina. The species appears to
have been eliminated from Florida. Most populations are small (10-100
stems), and, since the species' main mode of reproduction is
vegetative, each isolated population may represent only a few
genotypes.
Many populations are threatened by one or more of the following
factors: woody succession due to fire suppression, development, highway
[[Page 75231]]
expansion/improvement, and herbicide application. These threats are
currently occurring (and are therefore imminent). These threats are
expected to continue to operate throughout the range of the species;
however, data on the frequency, timing, and consequences of these
threats are lacking. Based upon data on other rare plant species, some
of which are federally listed, occurring in similar habitats and
possessing similar life histories, it is not currently expected that
these threats are likely to be irreversible (e.g., to result in the
extirpation of populations). Therefore, the ongoing threats are of
moderate to low magnitude, and we assigned an LPN of 8 to this species.
Zanthoxylum oahuense (Ae) - We have not updated our assessment for
this species, as we are currently developing a proposed listing rule.
Ferns and Allies
Christella boydiae (no common name) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. This species is a
small- to medium-sized fern found in mesic to wet forest along
streambanks on Oahu and Maui, Hawaii. Historically, this species was
also found on the island of Hawaii, but it has been extirpated there.
Currently, this species is known from five populations totaling 316
individuals. This species is threatened by feral pigs which degrade
and/or destroy habitat and that may eat this plant, nonnative plants
that compete for light and nutrients, and stream diversion. Feral pigs
have been fenced out of the largest population on Maui, and nonnative
plants have been reduced in the fenced area. No conservation efforts
are under way to alleviate threats to the other two populations on
Maui, or for the two populations on Oahu. The magnitude of the threats
acting upon the currently extant populations is moderate because the
largest population is protected from pigs, and nonnative plants have
been reduced in this area. The threats are ongoing and therefore
imminent. Therefore, we retained an LPN of 8 for this species.
Doryopteris takeuchii (no common name) - We have not updated our
assessment for this species, as we are currently developing a proposed
listing rule for this species.
Huperzia stemmermanniae (Waewaeiole) - The following summary is
based on information contained in our files. No new information was
provided in the petition we received on May 11, 2004. This species is a
pendant clubmoss found in mesic to wet Metrosideros polymorpha-Acacia
koa (ohia-koa) forests on the islands of Maui and Hawaii, Hawaii. Only
four populations are known, totaling 19 to 29 individuals on Hawaii and
Maui. Huperzia stemmermanniae is threatened by feral pigs, goats,
cattle, and deer that degrade and/or destroy habitat, and by nonnative
plants that compete for light, space, and nutrients. It is also
threatened by randomly occurring natural events due to its small
population size. One individual at Waikamoi Preserve may benefit from
fencing for deer and pigs. The threats from pigs, goats, cattle, deer,
and nonnative plants are of a high magnitude because they are
sufficiently severe to adversely affect the species throughout its
limited range, resulting in direct mortality or significantly reducing
reproductive capacity. The threats are imminent because they are
ongoing. Therefore, we retained an LPN of 2 for this species.
Microlepia strigosa var. mauiensis (Palapalai) - The following
summary is based on information contained in our files. No new
information was provided in the petition we received on May 11, 2004.
Palapalai is a fern found in mesic to wet forests. It is currently
found on the islands of Maui, Hawaii, and Oahu, from at least 10
populations totaling at least 46 individuals. There is a possibility
that the range of this plant variety could be larger and include the
other main Hawaiian Islands. Microlepia strigosa var. mauiensis is
threatened by feral pigs that degrade and destroy habitat, and
nonnative plants that compete for light and nutrients. Pigs have been
fenced out of areas on east and west Maui, and on Hawaii, where M.
strigosa var. mauiensis currently occurs, and nonnative plants have
been reduced in the fenced areas. However, the threats are not
controlled and are ongoing in the remaining unfenced populations on
Maui, Hawaii, and Oahu. Therefore, the threats from feral pigs and
nonnative plants are imminent. The threats are of a high magnitude
because they are sufficiently severe to adversely affect the species
throughout its range, resulting in direct mortality or significantly
reducing reproductive capacity. We therefore retained an LPN of 3 for
M. strigosa var. mauiensis.
Petitions To Reclassify Species Already Listed
We previously made warranted-but-precluded findings on five
petitions seeking to reclassify threatened species to endangered
status. The taxa involved are three populations of the grizzly bear
(Ursus arctos horribilis), the spikedace (Meda fulgida), and the loach
minnow (Tiaroga cobitis). Because these species are already listed
under the Act, they are not candidates for listing and are not included
in Table 1. However, this notice and associated species assessment
forms also constitute the resubmitted petition findings for these
species. For the three grizzly bear populations, we have not updated
our assessments through this notice as explained below. Pending the
completion of an ongoing review of the status of the grizzly bear in
the lower 48 States outside of the Greater Yellowstone Areas (see
below), we continue to find that reclassification to endangered for
each of the three populations (described below) is warranted but
precluded by work indentified above (see ``Petition Findings for
Candidate Species ''). For the spikedace and loach minnow, our updated
assessments are provided below. We find that reclassification to
endangered status for both the spikedace and loach minnow is currently
warranted but precluded by work identified above (see ``Petition
Findings for Candidate Species ''). One of the primary reasons that the
work identified above is higher priority is that the grizzly bear
populations, spikedace, and loach minnow are currently listed as
threatened, and therefore already receive certain protections under the
Act. The Service promulgated regulations extending take prohibitions
for endangered species under section 9 to threatened species (50 CFR
17.31). Prohibited actions under section 9 include, but are not limited
to, take (i.e., to harass, harm, pursue, hunt, shoot, wound, kill,
trap, capture, or collect, or attempt to engage in such activity).
Other protections include those under section 7(a)(2) of the Act
whereby Federal agencies must insure that any action they authorize,
fund, or carry out is not likely to jeopardize the continued existence
of any endangered or threatened species.
Grizzly bear (Ursus arctos horribilis) North Cascades ecosystem,
Cabinet-Yaak, and Selkirk populations (Region 6) - We have not updated
our finding with regard to these grizzly bear populations in this
notice. Between 1991 and 1999, we issued warranted but precluded
findings to reclassify grizzly bears as endangered in the North
Cascades (56 FR 33892-33894, July 24, 1991; 63 FR 30453-30454, June 4,
1998), the Cabinet-Yaak (58 FR 8250-8251, February 12, 1993; 64 FR
26725-26733, May 17, 1999), and the Selkirk Ecosystems (64 FR 26725-
26733, May 17, 1999). We also made resubmitted
[[Page 75232]]
petition findings that uplisting these three populations to endangered
was warranted but precluded through previous CNORs (most recently on
September 12, 2006; 71 FR 53755). However, none of the findings
included a formal analysis under our 1996 Policy Regarding the
Recognition of Distinct Vertebrate Population Segments (DPS) under the
Endangered Species Act (61 FR 4722-4725, February 7, 1996). Under this
policy a formal analysis of discreteness and significance is necessary
to determine if the entity is a ``listable entity.'' While our 1999
revised 12-month finding performed a preliminary DPS analysis, it
appears to have incorrectly analyzed significance to the listed entity
(i.e. grizzly bears in the lower 48 States) instead of significance to
the taxon (Ursus arctos horribilis) as required by our DPS policy (64
FR 26725-26733, May 17, 1999; 61 FR 4722-4725, February 7, 1996;
National Association of Home Builders v. Norton, 340 F. 3d 835, 852
(9\th\ Cir. 2003)). Additionally, emerging biological information now
suggests increasing levels of connectivity among some of these
populations, casting doubt on their discreteness.
Also relevant is the March 16, 2007, Department of the Interior
Office of the Solicitor memorandum (available at: http://www.doi.gov/
solicitor/opinions/M37013.pdf) regarding the meaning of ``significant
portion of [a species'] range.'' This memorandum states that ``whenever
the Secretary concludes because of the statutory five-factor analysis
that a species is `in danger of extinction throughout...a significant
portion of its range,' it is to be listed and the protections of the
ESA applied to the species in that portion of its range.'' The
memorandum goes on to say, ``the Secretary has broad discretion in
defining what portion of a range is `significant.''' To date, the
Service has not determined whether the North Cascade, the Cabinet-Yaak,
or the Selkirk Ecosystems each constitutes a significant portion of the
grizzly bear's range or whether they only represent significant
portions of the species' range when combined with other units.
On April 18, 2007, the Service initiated a 5-year review to
evaluate the current status of grizzly bears in the lower 48-States
outside of the Greater Yellowstone Area (72 FR 19549-19551). This
status review will fully evaluate the status of each population and the
appropriate application of the DPS policy and the Solicitor memorandum
regarding recognition and listing of significant portions of range. We
expect this 5-year review to be completed in FY 2009. We will use
information from that review to update our findings for the petitions
to reclassify the three grizzly bear populations.
Spikedace (Meda fulgida) (Region 2) (see 59 FR 35303, July 11,
1994, and the species assessment form (see ADDRESSES) for additional
information on why reclassification to endangered is warranted-but-
precluded) - The spikedace, a small fish species in a monotypic genus,
is found in moderate-to-large perennial waters, where it inhabits
shallow riffles with sand, gravel, and rubble substrates, and moderate-
to-swift currents and swift pools over sand or gravel substrates. This
species is now relatively common only in Aravaipa Creek and portions of
the upper Gila River in New Mexico. Smaller, less stable populations
occur in some areas of the upper Gila, as well as in the Verde River.
The threats to this species are primarily from nonnative aquatic
species and water withdrawals, including groundwater pumping. Other
threats include grazing, road construction, and recreation. Spikedace
occur in only 5 to 10 percent of their historical range, and threats
occur over the majority of their range to varying degrees. Threats are
exacerbated by ongoing drought. In addition, different threats can
interact with each other to cause further decline. For example, drought
and water withdrawals may decrease the amount of habitat available to
all species within a given stream, forcing natives and nonnatives into
closer proximity to one another. Effects from nonnative species
introductions are permanent, unless streams are actively renovated and/
or barriers installed to preclude further recolonization by nonnatives.
Grazing pressures have eased somewhat as Federal agencies remove cattle
from streams directly, but upland conditions continue to degrade
watersheds in general. Groundwater withdrawals or exchanges that affect
streamflow are not reversible. For these reasons, the magnitude of the
threat to this species is high. In addition, most of the threats to
this species are ongoing, in particular grazing, water withdrawals,
nonnative stocking programs, recreational use, and drought. Because
threats have gone on for many years in the past, are associated with
irreversible commitments (i.e., water exchanges), or are not easily
reversed (i.e., nonnative stocking and impacts from grazing), the
threats to the species are imminent. Therefore, we assigned this
species an LPN of 1 for uplisting to endangered.
Loach minnow (Tiaroga cobitis) (Region 2) (see 59 FR 35303, July
11, 1994, and the species assessment form (see ADDRESSES) for
additional information on why reclassification to endangered is
warranted-but-precluded) - This small fish, the only species within the
genus, is found in small-to-large perennial streams and uses shallow,
turbulent riffles with primarily cobble substrate and swift currents.
This species is now common only in Aravaipa Creek and the Blue River in
Arizona, and limited portions of the San Francisco, upper Gila, and
Tularosa rivers in New Mexico. Smaller, less stable populations occur
in some areas of the upper Gila, such as the Middle Fork and in small
areas of several tributary streams to Aravaipa Creek and the Blue and
Tularosa rivers, such as Pace, Frieborn, Negrito, Turkey, and Deer
creeks. Small populations are also present in Eagle Creek and the Black
River.
The threats to this species are primarily from nonnative aquatic
species and water withdrawals, including groundwater pumping. Other
threats include grazing, road construction, and recreation. Loach
minnow occur in only 10 to 15 percent of their historic range, and
threats occur over the majority of their range, to varying degrees.
Threats are exacerbated by ongoing drought. In addition, different
threats can interact with each other to cause further decline. For
example, drought and water withdrawals may decrease the amount of
habitat available to all species within a given stream, bringing
natives and nonnatives into closer contact. Effects from nonnative
species introductions are permanent, unless streams are actively
renovated and/or barriers installed to preclude further recolonization
by nonnatives. Grazing pressures have eased somewhat as Federal
agencies remove cattle from streams directly, but upland conditions
continue to degrade watersheds in general. Groundwater withdrawals or
exchanges that affect streamflow are not reversible. For these reasons,
the magnitude of the threats to this species is high. In addition, most
of the threats to this species are ongoing, in particular grazing,
water withdrawals, nonnative stocking programs, recreational use, and
drought. Because threats have gone on for many years in the past, are
associated with irreversible commitments (i.e., water exchanges), or
are not easily reversed (i.e., nonnative stocking and impactsfrom
grazing), the threats to this species are imminent. Therefore, we
assigned this species an LPN of 1 for uplisting to endangered.
[[Page 75233]]
Current Notice of Review
We gather data on plants and animals native to the U.S. that appear
to merit consideration for addition to the Lists of Endangered and
Threatened Wildlife and Plants. This notice identifies those species
that we currently regard as candidates for addition to the Lists. These
candidates include species and subspecies of fish, wildlife, or plants
and DPSs of vertebrate animals. This compilation relies on information
from status surveys conducted for candidate assessment and on
information from State Natural Heritage Programs, other State and
Federal agencies, knowledgeable scientists, public and private natural
resource interests, and comments received in response to previous
notices of review.
Tables 1 and 2 list animals arranged alphabetically by common names
under the major group headings, and list plants alphabetically by names
of genera, species, and relevant subspecies and varieties. Animals are
grouped by class or order. Plants are subdivided into two groups: (1)
flowering plants and (2) ferns and their allies. Useful synonyms and
subgeneric scientific names appear in parentheses with the synonyms
preceded by an ``equals'' sign. Several species that have not yet been
formally described in the scientific literature are included; such
species are identified by a generic or specific name (in italics),
followed by ``sp.'' or ``ssp.'' We incorporate standardized common
names in these notices as they become available. We sorted plants by
scientific name due to the inconsistencies in common names, the
inclusion of vernacular and composite subspecific names, and the fact
that many plants still lack a standardized common name.
Table 1 lists all candidate species plus species currently proposed
for listing under the Act. We emphasize that in this notice we are not
proposing to list any of the candidate species; rather, we will develop
and publish proposed listing rules for these species in the future. We
encourage State agencies, other Federal agencies, and other parties to
give consideration to these species in environmental planning.
In Table 1, the ``category'' column on the left side of the table
identifies the status of each species according to the following codes:
PE - Species proposed for listing as endangered. Proposed species
are those species for which we have published a proposed rule to list
as endangered or threatened in the Federal Register. This category does
not include species for which we have withdrawn or finalized the
proposed rule.
PT - Species proposed for listing as threatened.
PSAT - Species proposed for listing as threatened due to similarity
of appearance.
C - Candidates: Species for which we have on file sufficient
information on biological vulnerability and threats to support
proposals to list them as endangered or threatened. Issuance of
proposed rules for these species is precluded at present by other
higher-priority listing actions. This category includes species for
which we made a 12-month warranted-but-precluded finding on a petition
to list. We made new findings on all petitions for which we previously
made ``warranted-but-precluded'' findings. We identify the species for
which we made a continued warranted-but-precluded finding on a
resubmitted petition by the code ``C*'' in the category column (see
``Findings on Resubmitted Petitions'' section for additional
information).
The ``Priority'' column indicates the LPN for each candidate
species which we use to determine the most appropriate use of our
available resources. The lowest numbers have the highest priority. We
assign LPNs based on the immediacy and magnitude of threats as well as
on taxonomic status. We published a complete description of our listing
priority system in the Federal Register (48 FR 43098, September 21,
1983).
The third column, ``Lead Region,'' identifies the Regional Office
to which you should direct information, comments, or questions (see
addresses at the end of the SUPPLEMENTARY INFORMATION section).
Following the scientific name (fourth column) and the family
designation (fifth column) is the common name (sixth column). The
seventh column provides the known historic range for the species or
vertebrate population (for vertebrate populations, this is the historic
range for the entire species or subspecies and not just the historic
range for the distinct population segment), indicated by postal code
abbreviations for States and U.S. territories. Many species no longer
occur in all of the areas listed.
Species in Table 2 of this notice are those we included either as
proposed species or as candidates in the previous CNOR (published
December 6, 2007) that are no longer proposed species or candidates for
listing. Since December 6, 2007, we removed one species from proposed
status and removed three species from candidate status for the reasons
indicated by the codes. The first column indicates the present status
of each species, using the following codes (not all of these codes may
have been used in this CNOR):
E - Species we listed as endangered.
T - Species we listed as threatened.
Rc - Species we removed from the candidate list because currently
available information does not support a proposed listing.
Rp - Species we removed from the candidate list because we have
withdrawn the proposed listing.
The second column indicates why we no longer regard the species as
a candidate or proposed species using the following codes (not all of
these codes may have been used in this CNOR):
A - Species that are more abundant or widespread than previously
believed and species that are not subject to the degree of threats
sufficient to warrant continuing candidate status, or issuing a
proposed or final listing.
F - Species whose range no longer includes a U.S. territory.
I - Species for which we have insufficient information on
biological vulnerability and threats to support issuance of a proposed
rule to list.
L - Species we added to the Lists of Endangered and Threatened
Wildlife and Plants.
M - Species we mistakenly included as candidates or proposed
species in the last notice of review.
N - Species that are not listable entities based on the Act's
definition of ``species'' and current taxonomic understanding.
U - Species that are not subject to the degree of threats
sufficient to warrant issuance of a proposed listing or continuance of
candidate status due, in part or totally, to conservation efforts that
remove or reduce the threats to the species.
X - Species we believe to be extinct.
The columns describing lead region, scientific name, family, common
name, and historical range include information as previously described
for Table 1.
Request for Information
We request you submit any further information on the species named
in this notice as soon as possible or whenever it becomes available. We
are particularly interested in any information:
(1) indicating that we should add a species to the list of
candidate species;
(2) indicating that we should remove a species from candidate
status;
(3) recommending areas that we should designate as critical habitat
for a species, or indicating that designation of critical habitat would
not be prudent for a species;
(4) documenting threats to any of the included species;
[[Page 75234]]
(5) describing the immediacy or magnitude of threats facing
candidate species;
(6) pointing out taxonomic or nomenclature changes for any of the
species;
(7) suggesting appropriate common names; and
(8) noting any mistakes, such as errors in the indicated historical
ranges.
Submit information, materials, or comments regarding a particular
species to the Regional Director of the Region identified as having the
lead responsibility for that species. The regional addresses follow:
Region 1. Hawaii, Idaho, Oregon, Washington, American Samoa, Guam,
and Commonwealth of the Northern Mariana Islands. Regional Director
(TE), U.S. Fish and Wildlife Service, Eastside Federal Complex, 911
N.E. 11th Avenue, Portland, OR 97232-4181 (503/231-6158).
Region 2. Arizona, New Mexico, Oklahoma, and Texas. Regional
Director (TE), U.S. Fish and Wildlife Service, 500 Gold Avenue SW.,
Room 4012, Albuquerque, NM 87102 (505/248-6920).
Region 3. Illinois, Indiana, Iowa, Michigan, Minnesota, Missouri,
Ohio, and Wisconsin. Regional Director (TE), U.S. Fish and Wildlife
Service, Bishop Henry Whipple Federal Building, One Federal Drive, Fort
Snelling, MN 55111-4056 (612/713-5334).
Region 4. Alabama, Arkansas, Florida, Georgia, Kentucky, Louisiana,
Mississippi, North Carolina, South Carolina, Tennessee, Puerto Rico,
and the U.S. Virgin Islands. Regional Director (TE), U.S. Fish and
Wildlife Service, 1875 Century Boulevard, Suite 200, Atlanta, GA 30345
(404/679-4156).
Region 5. Connecticut, Delaware, District of Columbia, Maine,
Maryland, Massachusetts, New Hampshire, New Jersey, New York,
Pennsylvania, Rhode Island, Vermont, Virginia, and West Virginia.
Regional Director (TE), U.S. Fish and Wildlife Service, 300 Westgate
Center Drive, Hadley, MA 01035-9589 (413/253-8615).
Region 6. Colorado, Kansas, Montana, Nebraska, North Dakota, South
Dakota, Utah, and Wyoming. Regional Director (TE), U.S. Fish and
Wildlife Service, P.O. Box 25486, Denver Federal Center, Denver, CO
80225-0486 (303/236-7400).
Region 7. Alaska. Regional Director (TE), U.S. Fish and Wildlife
Service, 1011 East Tudor Road, Anchorage, AK 99503-6199 (907/786-3505).
Region 8. California and Nevada. Regional Director (TE), U.S. Fish
and Wildlife Service, 2800 Cottage Way, Suite W2606, Sacramento, CA
95825 (916/414-6464)
We will provide information received in response to the previous
CNOR to the Region having lead responsibility for each candidate
species mentioned in the submission. We will likewise consider all
information provided in response to this CNOR in deciding whether to
propose species for listing and when to undertake necessary listing
actions (including whether emergency listing pursuant to section
4(b)(7) of the Act is appropriate). Information and comments we receive
will become part of the administrative record for the species, which we
maintain at the appropriate Regional Office.
Before including your address, phone number, e-mail address, or
other personal identifying information in your submission, be advised
that your entire submission - including your personal identifying
information - may be made publicly available at any time. While you can
ask us in your submission to withhold from public review your personal
indentifying information, we cannot guarantee that we will be able to
do so.
Authority
This notice is published under the authority of the Endangered
Species Act (16 U.S.C. 1531 et seq.).
Dated: November 26, 2008
Rowan W. Gould
Deputy Director, Fish and Wildlife Service
Table 1. - Candidate Notice of Review (Animals and Plants)
Note: See end of SUPPLEMENTARY INFORMATION for an explanation of symbols used in this table.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Status
----------------------------------------------------- Lead region Scientific name Family Common name Historic range
Category Priority
--------------------------------------------------------------------------------------------------------------------------------------------------------
MAMMALS
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Emballonura Emballonuridae Bat, Pacific U.S.A. (GU, CNMI)
semicaudata sheath-tailed
rotensis (Mariana Islands
subspecies)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Emballonura Emballonuridae Bat, Pacific U.S.A. (AS), Fiji,
semicaudata sheath-tailed Independent
semicaudata (American Samoa Samoa, Tonga,
DPS) Vanuatu
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R5 Sylvilagus Leporidae Cottontail, New U.S.A. (CT, MA,
transitionalis England ME, NH, NY, RI,
VT)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 6 R8 Martes pennanti Mustelidae Fisher (west coast U.S.A. (CA, CT,
DPS) IA, ID, IL, IN,
KY, MA, MD,ME,
MI, MN, MT, ND,
NH, NJ, NY, OH,
OR, PA, RI, TN,
UT, VA, VT, WA,
WI, WV, WY),
Canada
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R2 Zapus hudsonius Zapodidae Mouse, New Mexico U.S.A. (AZ, CO,
luteus meadow jumping NM)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Thomomys mazama Geomyidae Pocket gopher, U.S.A. (WA)
couchi Shelton
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 3 R1 Thomomys mazama Geomyidae Pocket gopher, U.S.A. (WA)
douglasii Brush Prairie
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Thomomys mazama Geomyidae Pocket gopher, Roy U.S.A. (WA)
glacialis Prairie
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Thomomys mazama Geomyidae Pocket gopher, U.S.A. (WA)
louiei Cathlamet
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 75235]]
C* 3 R1 Thomomys mazama Geomyidae Pocket gopher, U.S.A. (WA)
melanops Olympic
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Thomomys mazama Geomyidae Pocket gopher, U.S.A. (WA)
pugetensis Olympia
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Thomomys mazama Geomyidae Pocket gopher, U.S.A. (WA)
tacomensis Tacoma
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Thomomys mazama Geomyidae Pocket gopher, U.S.A. (WA)
tumuli Tenino
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Thomomys mazama Geomyidae Pocket gopher, U.S.A. (WA)
yelmensis Yelm
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R6 Cynomys gunnisoni Sciuridae Prairie dog, U.S.A. (CO, NM)
Gunnison's
(central and
south-central
Colorado, north-
central New
Mexico SPR)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R8 Spermophilus Sciuridae Squirrel, Palm U.S.A. (CA)
tereticaudus Springs (=
chlorus Coachella Valley)
round-tailed
ground
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 9 R1 Spermophilus Sciuridae Squirrel, Southern U.S.A. (ID)
brunneus Idaho ground
endemicus
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R1 Spermophilus Sciuridae Squirrel, U.S.A. (WA, OR)
washingtoni Washington ground
--------------------------------------------------------------------------------------------------------------------------------------------------------
BIRDS
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Loxops Fringillidae Akekee U.S.A. (HI)
caeruleirostris (honeycreeper)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Oreomystis bairdi Fringillidae Akikiki (Kauai U.S.A. (HI)
creeper)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Porzana tabuensis Rallidae Crake, spotless U.S.A. (AS),
(American Samoa Australia, Fiji,
DPS) Independent
Samoa, Marquesas,
Philippines,
Society Islands,
Tonga
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R8 Coccyzus Cuculidae Cuckoo, yellow- U.S.A. (Lower 48
americanus billed (Western States), Canada,
U.S. DPS) Mexico, Central
and South America
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 9 R1 Gallicolumba Columbidae Ground-dove, U.S.A. (AS),
stairi friendly Independent Samoa
(American Samoa
DPS)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Eremophila Alaudidae Horned lark, U.S.A. (OR, WA),
alpestris streaked Canada (BC)
strigata
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R5 Calidris canutus Scolopacidae Knot, red U.S.A. (Atlantic
rufa coast), Canada,
South America
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R7 Brachyramphus Alcidae Murrelet, U.S.A. (AK),
brevirostris Kittlitz's Russia.
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R8 Synthliboramphus Alcidae Murrelet, Xantus's U.S.A. (CA),
hypoleucus Mexico
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R2 Tympanuchus Phasianidae Prairie-chicken, U.S.A. (CO, KA,
pallidicinctus lesser NM, OK, TX)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 6 R1 Centrocercus Phasianidae Sage-grouse, U.S.A. (AZ, CA,
urophasianus greater (Columbia CO, ID, MT, ND,
Basin DPS) NE, NV, OR, SD,
UT, WA, WY),
Canada (AB, BC,
SK)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Oceanodroma castro Hydrobatidae Storm-petrel, band- U.S.A. (HI),
rumped (Hawaii Atlantic Ocean,
DPS) Ecuador
(Galapagos
Islands), Japan
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Dendroica angelae Emberizidae Warbler, elfin- U.S.A. (PR)
woods
--------------------------------------------------------------------------------------------------------------------------------------------------------
REPTILES
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R2 Thamnophis eques Colubridae Gartersnake, U.S.A. (AZ, NM,
megalops northern Mexican NV), Mexico
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 75236]]
C* 2 R2 Sceloporus Iguanidae Lizard, sand dune U.S.A. (TX, NM)
arenicolus
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 9 R3 Sistrurus Viperidae Massasauga U.S.A. (IA, IL,
catenatus (=rattlesnake), IN, MI, MO, MN,
catenatus eastern NY, OH, PA, WI),
Canada
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R4 Pituophis Colubridae Snake, black pine U.S.A. (AL, LA,
melanoleucus MS)
lodingi
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Pituophis ruthveni Colubridae Snake, Louisiana U.S.A. (LA, TX)
pine
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R2 Kinosternon Kinosternidae Turtle, Sonoyta U.S.A. (AZ),
sonoriense mud Mexico
longifemorale
--------------------------------------------------------------------------------------------------------------------------------------------------------
AMPHIBIANS
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 9 R8 Rana luteiventris Ranidae Frog, Columbia U.S.A. (AK, ID,
spotted (Great MT, NV, OR, UT,
Basin DPS) WA, WY), Canada
(BC)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R8 Rana muscosa Ranidae Frog, mountain U.S.A (CA, NV)
yellow-legged
(Sierra Nevada
DPS)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Rana pretiosa Ranidae Frog, Oregon U.S.A. (CA, OR,
spotted WA), Canada (BC)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R8 Rana onca Ranidae Frog, relict U.S.A. (AZ, NV,
leopard UT)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R3 Cryptobranchus Crytobranchidae Hellbender, Ozark U.S.A. (AR, MO)
alleganiensis
bishopi
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R2 Eurycea Plethodontidae Salamander, Austin U.S.A. (TX)
waterlooensis blind
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R2 Eurycea naufragia Plethodontidae Salamander, U.S.A. (TX)
Georgetown
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R2 Eurycea tonkawae Plethodontidae Salamander, U.S.A. (TX)
Jollyville
Plateau
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R2 Eurycea Plethodontidae Salamander, Salado U.S.A. (TX)
chisholmensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R8 Bufo canorus Bufonidae Toad, Yosemite U.S.A. (CA)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 3 R2 Hyla wrightorum Hylidae Treefrog, Arizona U.S.A. (AZ),
(Huachuca/Canelo Mexico (Sonora)
DPS)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R4 Necturus Proteidae Waterdog, black U.S.A. (AL)
alabamensis warrior (=Sipsey
Fork)
--------------------------------------------------------------------------------------------------------------------------------------------------------
FISHES
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R2 Gila nigra Cyprinidae Chub, headwater U.S.A. (AZ, NM)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R4 Phoxinus saylori Cyprinidae Dace, laurel U.S.A. (TN)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R6 Etheostoma cragini Percidae Darter, Arkansas U.S.A. (AR, CO,
KS, MO, OK)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Etheostoma susanae Percidae Darter, Cumberland U.S.A. (KY, TN)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Percina aurora Percidae Darter, Pearl U.S.A. (LA, MS)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R4 Etheostoma Percidae Darter, rush U.S.A. (AL)
phytophilum
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R4 Etheostoma moorei Percidae Darter, U.S.A (AR)
yellowcheek
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R4 Noturus crypticus Ictaluridae Madtom, chucky U.S.A. (TN)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R4 Moxostoma sp. Catostomidae Redhorse, U.S.A. (GA, NC,
sicklefin TN)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R3 Cottus sp. Cottidae Sculpin, grotto U.S.A. (MO)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R2 Notropis Cyprinidae Shiner, sharpnose U.S.A. (TX)
oxyrhynchus
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R2 Notropis buccula Cyprinidae Shiner, smalleye U.S.A. (TX)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R2 Catostomus Catostomidae Sucker, Zuni U.S.A. (AZ, NM)
discobolus bluehead
yarrowi
--------------------------------------------------------------------------------------------------------------------------------------------------------
PSAT N/A R1 Salvelinus malma Salmonidae Trout, Dolly U.S.A. (AK, WA),
Varden Canada, East Asia
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 75237]]
C* 9 R2 Oncorhynchus Salmonidae Trout, Rio Grande U.S.A. (CO, NM)
clarki virginalis cutthroat
--------------------------------------------------------------------------------------------------------------------------------------------------------
CLAMS
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R4 Villosa Unionidae Bean, Choctaw U.S.A. (AL, FL)
choctawensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 2 R3 Villosa fabalis Unionidae Bean, rayed U.S.A. (IL, IN,
KY, MI, NY, OH,
TN, PA, VA, WV),
Canada (ON)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 2 R4 Fusconaia rotulata Unionidae Ebonyshell, round U.S.A. (AL, FL)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R2 Popenaias popei Unionidae Hornshell, Texas U.S.A. (NM, TX),
Mexico
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R4 Ptychobranchus Unionidae Kidneyshell, U.S.A. (AL, KY,
subtentum fluted TN, VA)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 2 R4 Ptychobranchus Unionidae Kidneyshell, U.S.A. (AL, FL)
jonesi southern
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Lampsilis Unionidae Mucket, Neosho U.S.A. (AR, KS,
rafinesqueana MO, OK)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 2 R3 Plethobasus Unionidae Mussel, sheepnose U.S.A. (AL, IA,
cyphyus IL, IN, KY, MN,
MO, MS, OH, PA,
TN, VA, WI, WV)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R4 Margaritifera Margaritiferidae Pearlshell, U.S.A. (AL)
marrianae Alabama
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R4 Lexingtonia Unionidae Pearlymussel, U.S.A. (AL, KY,
dolabelloides slabside TN, VA)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R4 Pleurobema Unionidae Pigtoe, fuzzy U.S.A. (AL, FL)
strodeanum
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R4 Pleurobema Unionidae Pigtoe, Georgia U.S.A. (AL, GA,
hanleyianum TN)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R4 Fusconaia escambia Unionidae Pigtoe, narrow U.S.A. (AL, FL)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 11 R4 Fusconaia Unionidae Pigtoe, tapered U.S.A. (AL, FL)
(=Quincuncina)
burkei
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R4 Hamiota Unionidae Sandshell, U.S.A. (AL, FL)
(=Lampsilis) southern
australis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 4 R3 Cumberlandia Margaritiferidae Spectaclecase U.S.A. (AL, AR,
monodonta IA, IN, IL, KS,
KY, MO, MN, NE,
OH, TN, VA, WI,
WV)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R4 Elliptio spinosa Unionidae Spinymussel, U.S.A. (GA)
Altamaha
--------------------------------------------------------------------------------------------------------------------------------------------------------
SNAILS
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 2 R4 Pleurocera Pleuroceridae Hornsnail, rough U.S.A. (AL)
foremani
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 8 R4 Elimia melanoides Pleuroceridae Mudalia, black U.S.A. (AL)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R6 Stagnicola Lymnaeidae Pondsnail, fat- U.S.A. (UT)
bonnevillensis whorled
(=Bonneville)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R4 Leptoxis foremani Pleuroceridae Rocksnail, U.S.A. (GA, AL)
(=downei) Interrupted (=
Georgia)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Ostodes strigatus Potaridae Sisi snail U.S.A. (AS)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R2 Pseudotryonia Hydrobiidae Snail, Diamond Y U.S.A. (TX)
adamantina Spring
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Samoana fragilis Partulidae Snail, fragile U.S.A. (GU, MP)
tree
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Partula radiolata Partulidae Snail, Guam tree U.S.A. (GU)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Partula gibba Partulidae Snail, Humped tree U.S.A. (GU, MP)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Partulina Achatinellidae Snail, Lanai tree U.S.A. (HI)
semicarinata
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Partulina Achatinellidae Snail, Lanai tree U.S.A. (HI)
variabilis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Partula langfordi Partulidae Snail, Langford's U.S.A. (MP)
tree
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R2 Cochliopa texana Hydrobiidae Snail, Phantom U.S.A. (TX)
cave
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 75238]]
C* 2 R1 Newcombia cumingi Achatinellidae Snail, Newcomb's U.S.A. (Hl)
tree
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Eua zebrina Partulidae Snail, Tutuila U.S.A. (AS)
tree
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R2 Pyrgulopsis Hydrobiidae Springsnail, U.S.A. (NM)
chupaderae Chupadera
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R8 Pyrgulopsis Hydrobiidae Springsnail, U.S.A. (NV)
notidicola elongate mud
meadows
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R2 Pyrgulopsis gilae Hydrobiidae Springsnail, Gila U.S.A. (NM)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R2 Tryonia Hydrobiidae Springsnail, U.S.A. (TX)
circumstriata(=st Gonzales
ocktonensis)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R2 Pyrgulopsis Hydrobiidae Springsnail, U.S.A. (AZ),
thompsoni Huachuca Mexico
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R2 Pyrgulopsis Hydrobiidae Springsnail, New U.S.A. (NM)
thermalis Mexico
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R2 Pyrgulopsis Hydrobiidae Springsnail, Page U.S.A. (AZ)
morrisoni
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R2 Tryonia cheatumi Hydrobiidae Springsnail U.S.A. (TX)
(=Tryonia),
Phantom
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 2 R2 Pyrgulopsis Hydrobiidae Springsnail, San U.S.A. (AZ),
bernardina Bernardino Mexico (Sonora)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R2 Pyrgulopsis Hydrobiidae Springsnail, Three U.S.A. (AZ)
trivialis Forks
--------------------------------------------------------------------------------------------------------------------------------------------------------
INSECTS
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R1 Nysius wekiuicola Lygaeidae Bug, Wekiu U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 3 R4 Strymon acis Lycaenidae Butterfly, U.S.A. (FL)
bartrami Bartram's
hairstreak
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 3 R4 Anaea troglodyta Nymphalidae Butterfly, Florida U.S.A. (FL)
floridalis leafwing
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Hypolimnas Nymphalidae Butterfly, Mariana U.S.A. (GU, MP)
octucula eight-spot
mariannensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Vagrans egistina Nymphalidae Butterfly, Mariana U.S.A. (GU, MP)
wandering
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 6 R4 Cyclargus thomasi Lycaenidae Butterfly, Miami U.S.A. (FL),
bethunebakeri blue Bahamas
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Glyphopsyche Limnephilidae Caddisfly, U.S.A. (TN)
sequatchie Sequatchie
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R4 Pseudanophthalmus Carabidae Cave beetle, Baker U.S.A. (TN)
insularis Station (=
insular)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Pseudanophthalmus Carabidae Cave beetle, U.S.A. (KY)
caecus Clifton
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 11 R4 Pseudanophthalmus Carabidae Cave beetle, U.S.A. (TN)
colemanensis Coleman
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R4 Pseudanophthalmus Carabidae Cave beetle, U.S.A. (TN)
fowlerae Fowler's
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Pseudanophthalmus Carabidae Cave beetle, U.S.A. (KY)
frigidus icebox
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R4 Pseudanophthalmus Carabidae Cave beetle, U.S.A. (TN)
tiresias Indian Grave
Point (=
Soothsayer)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Pseudanophthalmus Carabidae Cave beetle, U.S.A. (TN)
inquisitor inquirer
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Pseudanophthalmus Carabidae Cave beetle, U.S.A. (KY)
troglodytes Louisville
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R4 Pseudanophthalmus Carabidae Cave beetle, U.S.A. (TN).
paulus Noblett's
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Pseudanophthalmus Carabidae Cave beetle, Tatum U.S.A. (KY)
parvus
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Euphydryas editha Nymphalidae Checkerspot U.S. A. (OR, WA),
taylori butterfly, Canada (BC)
Taylor's (=
Whulge)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 9 R1 Megalagrion Coenagrionidae Damselfly, U.S.A. (HI)
nigrohamatum blackline
nigrolineatum Hawaiian
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Megalagrion Coenagrionidae Damselfly, crimson U.S.A. (HI)
leptodemas Hawaiian
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Megalagrion Coenagrionidae Damselfly, flying U.S.A. (HI)
nesiotes earwig Hawaiian
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 75239]]
C* 2 R1 Megalagrion Coenagrionidae Damselfly, oceanic U.S.A. (HI)
oceanicum Hawaiian
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R1 Megalagrion Coenagrionidae Damselfly, U.S.A. (HI)
xanthomelas orangeblack
Hawaiian
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Megalagrion Coenagrionidae Damselfly, Pacific U.S.A. (HI)
pacificum Hawaiian
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R8 Dinacoma caseyi Scarabidae June beetle, U.S.A. (CA)
Casey's
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R8 Ambrysus funebris Naucoridae Naucorid bug U.S.A. (CA)
(=Furnace Creek),
Nevares Spring
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Drosophila attigua Drosophilidae fly, Hawaiian U.S.A. (HI)
picture-wing
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Drosophila Drosophilidae fly, Hawaiian U.S.A. (HI)
digressa Picture-wing
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R2 Heterelmis Elmidae Riffle beetle, U.S.A. (AZ)
stephani Stephan's
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R3 Hesperia dacotae Hesperiidae Skipper, Dakota U.S.A. (MN, IA,
SD, ND, IL),
Canada
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R1 Polites mardon Hesperiidae Skipper, Mardon U.S.A. (CA, OR,
WA)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R6 Cicindela Cicindelidae Tiger beetle, U.S.A. (UT)
albissima Coral Pink Sand
Dunes
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Cicindela Cicindelidae Tiger beetle, U.S.A. (FL)
highlandensis highlands
--------------------------------------------------------------------------------------------------------------------------------------------------------
ARACHNIDS
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R2 Cicurina wartoni Dictynidae Meshweaver, Warton U.S.A. (TX)
cave
--------------------------------------------------------------------------------------------------------------------------------------------------------
CRUSTACEANS
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 2 R2 Gammarus Gammaridae Amphipod, U.S.A. (TX)
hyalleloides diminutive
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R1 Metabetaeus lohena Alpheidae Shrimp, anchialine U.S.A. (HI)
pool
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R1 Palaemonella Palaemonidae Shrimp, anchialine U.S.A. (HI)
burnsi pool
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R1 Procaris hawaiana Procarididae Shrimp, anchialine U.S.A. (HI)
pool
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 4 R1 Vetericaris Procaridae Shrimp, anchialine U.S.A. (HI)
chaceorum pool
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R4 Typhlatya monae Atyidae Shrimp, U.S.A. (PR),
troglobitic Barbuda,
groundwater Dominican
Republic
--------------------------------------------------------------------------------------------------------------------------------------------------------
FLOWERING PLANTS
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R8 Abronia alpina Nyctaginaceae Sand-verbena, U.S.A. (CA)
Ramshaw Meadows
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R4 Arabis georgiana Brassicaceae Rockcress, Georgia U.S.A. (AL, GA)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R4 Argythamnia Euphorbiaceae Silverbush, U.S.A. (FL)
blodgettii Blodgett's
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Artemisia Asteraceae Wormwood, northern U.S.A. (OR, WA)
campestris var.
wormskioldii
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Astelia waialealae Liliaceae Pa`iniu U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R6 Astragalus Fabaceae Milk-vetch, U.S.A. (CO)
tortipes Sleeping Ute
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Bidens amplectens Asteraceae Ko`oko`olau U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Bidens Asteraceae Ko`oko`olau U.S.A. (HI)
campylotheca
pentamera
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Bidens Asteraceae Ko`oko`olau U.S.A. (HI)
campylotheca
waihoiensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R1 Bidens conjuncta Asteraceae Ko`oko`olau U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Bidens micrantha Asteraceae Ko`oko`olau U.S.A. (HI)
ctenophylla
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R4 Brickellia mosieri Asteraceae Brickell-bush, U.S.A. (FL)
Florida
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Calamagrostis Poaceae Reedgrass, Maui U.S.A. (HI)
expansa
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Calamagrostis Poaceae Reedgrass, U.S.A. (HI)
hillebrandii Hillebrand's
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Calliandra Mimosaceae No common name U.S.A. (PR)
locoensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 75240]]
C* 5 R8 Calochortus Liliaceae Mariposa lily, U.S.A. (CA, OR)
persistens Siskiyou
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Calyptranthes Myrtaceae No common name U.S.A. (PR)
estremerae
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Canavalia Fabaceae `Awikiwiki U.S.A. (HI)
napaliensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Canavalia Fabaceae `Awikiwiki U.S.A. (HI)
pubescens
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R1 Castilleja Scrophulariaceae Paintbrush, U.S.A. (ID)
christii Christ's
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 9 R4 Chamaecrista Fabaceae Pea, Big Pine U.S.A. (FL)
lineata var. partridge
keyensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 12 R4 Chamaesyce Euphorbiaceae Sandmat, pineland U.S.A. (FL)
deltoidea
pinetorum
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 9 R4 Chamaesyce Euphorbiaceae Spurge, wedge U.S.A. (FL)
deltoidea
serpyllum
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Chamaesyce Euphorbiaceae `Akoko U.S.A. (HI)
eleanoriae
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 3 R1 Chamaesyce remyi Euphorbiaceae `Akoko U.S.A. (HI)
var. kauaiensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 3 R1 Chamaesyce remyi Euphorbiaceae `Akoko U.S.A. (HI)
var. remyi
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Charpentiera Amaranthaceae Papala U.S.A. (HI)
densiflora
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 6 R8 Chorizanthe parryi Polygonaceae Spineflower, San U.S.A. (CA)
var. fernandina Fernando Valley
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R4 Chromolaena Asteraceae Thoroughwort, Cape U.S.A. (FL)
frustrata Sable
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R4 Consolea Cactaceae Cactus, Florida U.S.A. (FL)
corallicola semaphore
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Cordia rupicola Boraginaceae No common name U.S.A. (PR),
Anegada
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Cyanea Campanulaceae Haha U.S.A. (HI)
asplenifolia
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Cyanea calycina Campanulaceae Haha U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Cyanea dolichopoda Campanulaceae Haha U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Cyanea eleeleensis Campanulaceae Haha U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Cyanea Campanulaceae Haha U.S.A. (HI)
kolekoleensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Cyanea kuhihewa Campanulaceae Haha U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Cyanea kunthiana Campanulaceae Haha U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Cyanea lanceolata Campanulaceae Haha U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Cyanea obtusa Campanulaceae Haha U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Cyanea tritomantha Campanulaceae `aku `aku U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Cyrtandra filipes Gesneriaceae Ha`iwale U.S.A. (HI).
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Cyrtandra Gesneriaceae Ha`iwale U.S.A. (HI)
kaulantha
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Cyrtandra Gesneriaceae Ha`iwale U.S.A. (HI)
oenobarba
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Cyrtandra oxybapha Gesneriaceae Ha`iwale U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Cyrtandra paliku Gesneriaceae Ha`iwale U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Cyrtandra sessilis Gesneriaceae Ha`iwale U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R4 Dalea Fabaceae Prairie-clover, U.S.A. (FL)
carthagenensis Florida
var. floridana
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R5 Dichanthelium Poaceae Panic grass, U.S.A. (DE, GA,
hirstii Hirsts' NC, NJ)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Digitaria Poaceae Crabgrass, Florida U.S.A. (FL)
pauciflora pineland
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 3 R1 Dubautia imbricata Asteraceae Na`ena`e U.S.A. (HI)
imbricata
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 75241]]
PE - R1 Dubautia Asteraceae Na`ena`e U.S.A. (HI)
kalalauensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Dubautia kenwoodii Asteraceae Na`ena`e U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 3 R1 Dubautia Asteraceae Na`ena`e U.S.A. (HI)
plantaginea
magnifolia
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Dubautia Asteraceae Na`ena`e U.S.A. (HI)
waialealae
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R2 Echinomastus Cactaceae Cactus, Acuna U.S.A. (AZ),
erectocentrus Mexico
var. acunensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R2 Erigeron lemmonii Asteraceae Fleabane, Lemmon U.S.A. (AZ)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Eriogonum codium Polygonaceae Buckwheat, Umtanum U.S.A. (WA)
Desert
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 6 R8 Eriogonum Polygonaceae Buckwheat, Las U.S.A. (NV)
corymbosum var. Vegas
nilesii
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R8 Eriogonum Polygonaceae Buckwheat, U.S.A (NV)
diatomaceum Churchill Narrows
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R8 Eriogonum Polygonaceae Buckwheat, Red U.S.A. (CA)
kelloggii Mountain
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Festuca Poaceae No common name U.S.A. (HI)
hawaiiensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R2 Festuca ligulata Poaceae Fescue, Guadalupe U.S.A. (TX),
Mexico
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Gardenia remyi Rubiaceae Nanu U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R1 Geranium hanaense Geraniaceae Nohoanu U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R1 Geranium Geraniaceae Nohoanu U.S.A. (HI)
hillebrandii
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 5 R1 Geranium kauaiense Geraniaceae Nohoanu U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Gonocalyx concolor Ericaceae No common name U.S.A. (PR)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 2 R4 Harrisia Cactaceae Pricklyapple, U.S.A. (FL)
aboriginum aboriginal
(shellmound
applecactus)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R8 Hazardia orcuttii Asteraceae Orcutt's hazardia U.S.A. (CA),
Mexico
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Hedyotis Rubiaceae Kampua`a U.S.A. (HI)
fluviatilis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Helianthus Asteraceae Sunflower, whorled U.S.A. (AL, GA,
verticillatus TN)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R2 Hibiscus dasycalyx Malvaceae Rose-mallow, U.S.A. (TX)
Neches River
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 2 R6 Ipomopsis Polemoniaceae Skyrocket, Pagosa U.S.A. (CO)
polyantha
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R8 Ivesia webberi Rosaceae Ivesia, Webber U.S.A. (CA, NV)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Joinvillea Joinvilleaceae `Ohe U.S.A. (HI)
ascendens
ascendens
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Keysseria erici Asteraceae No common name U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 8 R1 Keysseria helenae Asteraceae No common name U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Korthalsella Viscaceae Hulumoa U.S.A. (HI)
degeneri
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Labordia helleri Loganiaceae Kamakahala U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Labordia pumila Loganiaceae Kamakahala U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Leavenworthia Brassicaceae Gladecress, U.S.A. (AL)
crassa unnamed
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R2 Leavenworthia Brassicaceae Gladecress, Texas U.S.A. (TX)
texana golden
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Lesquerella Brassicaceae Bladderpod, U.S.A. (IN, KY,
globosa Short's TN)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R4 Linum arenicola Linaceae Flax, sand U.S.A. (FL)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R4 Linum carteri var. Linaceae Flax, Carter's U.S.A. (FL)
carteri small-flowered
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 8 R1 Lysimachia Myrsinaceae Lehua makanoe U.S.A. (HI)
daphnoides
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Lysimachia iniki Myrsinaceae No common name U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Lysimachia pendens Myrsinaceae No common name U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 75242]]
PE - R1 Lysimachia Myrsinaceae No common name U.S.A. (HI)
scopulensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Lysimachia venosa Myrsinaceae No common name U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Melicope Rutaceae Alani U.S.A. (HI)
christophersenii
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Melicope degeneri Rutaceae Alani U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Melicope hiiakae Rutaceae Alani U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Melicope makahae Rutaceae Alani U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Melicope Rutaceae Alani U.S.A. (HI)
paniculata
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Melicope puberula Rutaceae Alani U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Myrsine fosbergii Myrsinaceae Kolea U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Myrsine knudsenii Myrsinaceae Kolea U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Myrsine mezii Myrsinaceae Kolea U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Myrsine Myrsinaceae Kolea U.S.A. (HI)
vaccinioides
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R5 Narthecium Liliaceae Asphodel, bog U.S.A. (DE, NC,
americanum NJ, NY, SC)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Nothocestrum Solanaceae `Aiea U.S.A. (HI)
latifolium
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Ochrosia Apocynaceae Holei U.S.A. (HI)
haleakalae
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R2 Pediocactus Cactaceae Cactus, Fickeisen U.S.A. (AZ)
peeblesianus var. plains
fickeiseniae
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R6 Penstemon debilis Scrophulariaceae Beardtongue, U.S.A. (CO)
Parachute
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 6 R6 Penstemon Scrophulariaceae Beardtongue, White U.S.A. (CO, UT)
scariosus var. River
albifluvis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Peperomia Piperaceae `Ala `ala wai nui U.S.A. (HI)
subpetiolata
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 5 R8 Phacelia stellaris Hydrophyllaceae Phacelia, Brand's U.S.A. (CA),
Mexico
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R6 Phacelia submutica Hydrophyllaceae Phacelia, DeBeque U.S.A. (CO)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Phyllostegia Lamiaceae No common name U.S.A. (HI)
bracteata
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R1 Phyllostegia Lamiaceae No common name U.S.A. (HI)
floribunda
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Phyllostegia Lamiaceae No common name U.S.A. (HI)
hispida
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Phyllostegia Lamiaceae No common name U.S.A. (HI)
renovans
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R1 Physaria Brassicaceae Bladderpod, White U.S.A. (WA)
tuplashensis Bluffs
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Pittosporum Pittosporaceae Ho`awa U.S.A. (HI)
napaliense
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R4 Platanthera Orchidaceae Orchid, white U.S.A. (AL, GA,
integrilabia fringeless KY, MS, NC, SC,
TN, VA)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Platydesma cornuta Rutaceae No common name U.S.A. (HI)
var. cornuta
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Platydesma cornuta Rutaceae No common name U.S.A. (HI)
var. decurrens
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Platydesma remyi Rutaceae No common name U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Platydesma Rutaceae Pilo kea lau li`i U.S.A. (HI)
rostrata
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 2 R1 Pleomele fernaldii Agavaceae Hala pepe U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Pleomele forbesii Agavaceae Hala pepe U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 11 R8 Potentilla Rosaceae Cinquefoil, U.S.A. (NV)
basaltica Soldier Meadow
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Pritchardia hardyi Asteraceae Lo`ulu U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 75243]]
C* 3 R1 Pseudognaphalium Asteraceae `Ena`ena U.S.A. (HI)
(=Gnaphalium)
sandwicensium
var. molokaiense
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Psychotria Rubiaceae Kopiko U.S.A. (HI)
grandiflora
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Psychotria Rubiaceae Kopiko U.S.A. (HI)
hexandra ssp.
oahuensis var.
oahuensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Psychotria hobdyi Rubiaceae Kopiko U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Pteralyxia Apocynaceae Kaulu U.S.A. (HI)
macrocarpa
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Ranunculus Ranunculaceae Makou U.S.A. (HI)
hawaiensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Ranunculus Ranunculaceae Makou U.S.A. (HI)
mauiensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R8 Rorippa Brassicaceae Cress, Tahoe U.S.A. (CA, NV)
subumbellata yellow
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Schiedea attenuata Caryophyllaceae No common name U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Schiedea pubescens Caryophyllaceae Ma`oli`oli U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Schiedea salicaria Caryophyllaceae No common name U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 5 R8 Sedum eastwoodiae Crassulaceae Stonecrop, Red U.S.A. (CA)
Mountain
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Sicyos Cucurbitaceae `Anunu U.S.A. (HI)
macrophyllus
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 12 R4 Sideroxylon Sapotaceae Bully, Everglades U.S.A. (FL)
reclinatum ssp.
austrofloridense
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R1 Solanum nelsonii Solanaceae Popolo U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 8 R4 Solidago plumosa Asteraceae Goldenrod, Yadkin U.S.A. (NC)
River
--------------------------------------------------------------------------------------------------------------------------------------------------------
C 2 R2 Sphaeralcea Malvaceae Mallow, Gierisch U.S.A. (AZ, UT)
gierischii
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Stenogyne Lamiaceae No common name U.S.A. (HI)
cranwelliae
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE 2 R1 Stenogyne kealiae Lamiaceae No common name U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R4 Symphyotrichum Asteraceae Aster, Georgia U.S.A. (AL, FL,
georgianum GA, NC, SC)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Tetraplasandra Araliaceae No common name U.S.A. (HI)
bisattenuata
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Tetraplasandra Araliaceae No common name U.S.A. (HI)
flynnii
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Zanthoxylum Rutaceae A`e U.S.A. (HI)
oahuense
--------------------------------------------------------------------------------------------------------------------------------------------------------
FERNS AND ALLIES
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 8 R1 Christella boydiae Thelypteridaceae No common name U.S.A. (HI)
(=Cyclosorus
boydiae var.
boydiae +
Cyclosorus
boydiae
kipahuluensis)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Diellia mannii Aspleniaceae No common name U.S.A. (HI)
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Doryopteris Pteridaceae No common name U.S.A. (HI)
angelica
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Doryopteris Pteridaceae No common name U.S.A. (HI)
takeuchii
--------------------------------------------------------------------------------------------------------------------------------------------------------
PE - R1 Dryopteris Dryopteridaceae Palapalai aumakua U.S.A. (HI)
crinalis var.
podosorus
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 2 R1 Huperzia (= Lycopodiaceae Wawae`iole U.S.A. (HI)
Phlegmariurus)
stemmermanniae
--------------------------------------------------------------------------------------------------------------------------------------------------------
C* 3 R1 Microlepia Dennstaedtiaceae Palapalai U.S.A. (HI)
strigosa var.
mauiensis
(=Microlepia
mauiensis)
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 75244]]
Table 2. Animals and Plants Formerly Candidates or Formerly Proposed for Listing
Note: See end of SUPPLEMENTARY INFORMATION for an explanation of symbols used in this table.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Status
----------------------------------------------------- Lead region Scientific name Family Common name Historical range
Code Expl.
--------------------------------------------------------------------------------------------------------------------------------------------------------
MAMMALS
--------------------------------------------------------------------------------------------------------------------------------------------------------
T L R7 Ursus maritimus Ursidae Bear, polar U.S.A. (AK),
Canada, Russia,
Denmark
(Greenland),
Norway
--------------------------------------------------------------------------------------------------------------------------------------------------------
SNAILS
--------------------------------------------------------------------------------------------------------------------------------------------------------
Rc A R6 Oreohelix Oreohelicidae Mountainsnail, U.S.A. (UT)
peripherica Ogden
wasatchensis
--------------------------------------------------------------------------------------------------------------------------------------------------------
FLOWERING PLANTS
--------------------------------------------------------------------------------------------------------------------------------------------------------
Rc A R4 Indigofera trita Fabaceae Indigo, Florida U.S.A. (FL);
subsp. scabra Belize, Brazil,
(formerly Columbia, Costa
Indigofera Rica, Cuba,
mucronata var. Ecuador, El
keyensis) Salvador,
Ethiopia,
Guatemala,
Honduras, India,
Jamaica, Laos,
Madagascar,
Mexico, Pakistan,
Panama, Peru,
Sierra Leone,
Somalia, Sri
Lanka, Tanzania,
Zaire, and the
islands of
Hispaniola and
New Guinea
--------------------------------------------------------------------------------------------------------------------------------------------------------
[FR Doc. E8-28986 Filed 12-9-08; 8:45 am]
BILLING CODE 4310-55-S