[Federal Register Volume 69, Number 86 (Tuesday, May 4, 2004)]
[Proposed Rules]
[Pages 24876-24904]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 04-9893]
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Part III
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 Species That
Are Candidates or Proposed for Listing as Endangered or Threatened;
Annual Notice of Findings on Resubmitted Petitions; Annual Description
of Progress on Listing Actions; Notice of Review; Proposed Rule
Federal Register / Vol. 69, No. 86 / Tuesday, May 4, 2004 / Proposed
Rules
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DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
Endangered and Threatened Wildlife and Plants; Review of Species
That Are Candidates or Proposed 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 2003 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 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 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.
We request additional status information that may be available for
the identified candidate species and information on additional species
that we should include as candidates in future updates of this list. We
will consider this information in preparing listing documents and
future revisions to the notice of review. This information will help us
in monitoring changes in the status of candidate species and also in
conserving candidate species.
As part of the CNOR, we announce the availability of Candidate and
Listing Priority Assignment Forms (candidate forms) for each candidate
species. The CNOR and the candidate forms constitute our findings as to
the status and threats that we evaluated in order to assign a listing
priority number to each species. This includes our findings on
resubmitted petitions and describes our progress in revising the Lists
of Endangered and Threatened Wildlife and Plants during the period June
13, 2002 through April 19, 2004.
DATES: We will accept comments on the Candidate Notice of Review at any
time.
ADDRESSES: Submit your comments regarding a particular species to the
Regional Director of the Region identified in SUPPLEMENTARY INFORMATION
as having the lead responsibility for that species. You may submit
comments of a more general nature to the Chief, Division of
Conservation and Classification, U. S. Fish and Wildlife Service, 4401
N. Fairfax Drive, Room 420, Arlington, VA 22203 (703/358-2171). Written
comments and materials received in response to this notice will be
available for public inspection by appointment at the Division of
Conservation and Classification (for comments of a general nature only)
or at the appropriate Regional Office listed in SUPPLEMENTARY
INFORMATION.
Copies of the candidate forms that contain information and
references regarding the range, status, and habitat needs of and
listing priority assignment for a particular species are available for
review at the appropriate Regional Office listed below in SUPPLEMENTARY
INFORMATION or at the Division of Conservation and Classification,
Arlington, Virginia (see ADDRESSES above), or on our Internet Web site
(http://endangered.fws.gov/).
FOR FURTHER INFORMATION CONTACT: The Endangered Species Coordinator(s)
in the appropriate Regional Office(s) or Chris Nolin, Chief, Division
of Conservation and Classification (703-358-2171).
SUPPLEMENTARY INFORMATION:
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. Through the Federal rulemaking
process, we add these species 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. We maintain this list
for a variety of reasons, including: 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 conservation efforts that will remove or reduce threats to
these species; to solicit input from interested parties to identify
those candidate species that may not require protection under the Act
or additional species that may require the Act's protections; and to
solicit information needed to prioritize the order in which we will
propose species for listing.
Table 1 of this CNOR includes 279 species that we regard as
candidates for addition to the Lists of Endangered and Threatened
Wildlife and Plants (Lists), as well as 24 species for which we have
published proposed rules to list as threatened or endangered species.
Most of the proposed species were previously identified in the 2002
CNOR (67 FR 40657, June 13, 2002). We encourage consideration of these
species in conservation planning, as well as other environmental
planning, such as in environmental impact analysis done under the
National Environmental Policy Act of 1969 (implemented at 40 CFR parts
1500-1508) and in local and statewide land use planning. Table 2 of
this notice contains 19 species we identified as candidates or as
proposed species in the June 13, 2002, CNOR that we now no longer
consider candidates. This includes fourteen species we have listed as
threatened or endangered since June 13, 2002, one species that we are
removing from candidacy through this notice, and four species for which
we withdrew the proposed listing rule. The Regions identified as having
lead responsibility for the particular species will maintain updated
records of information on candidate species.
Publication of this notice has been delayed due to efforts to
resolve outstanding issues. As a result, many of the candidate forms
reflect that our formal analysis was conducted in late winter/early
spring of 2003, as shown by the approval date of the Regional Director
on each form. However, we were able to update a small subset of the
candidate forms recently to reflect additional information we have
obtained on those species. We intend to publish an updated combined
CNOR for animals and plants that will update all of the candidate
forms, including our findings on resubmitted petitions and a
description of our progress on listing actions, within the next few
months in the Federal Register.
Previous Notices of Review
The Act directed the Secretary of the Smithsonian Institution to
prepare a report on endangered and threatened
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plant species, which was published as House Document No. 94-51. We
published a notice in the Federal Register on July 1, 1975 (40 FR
27823), in which we announced that we would review more than 3,000
native plant species named in the Smithsonian's report and other
species added by the 1975 notice for possible addition to the List of
Endangered and Threatened Plants. A new comprehensive notice of review
for native plants, which took into account the earlier Smithsonian
report and other accumulated information, superseded the 1975 notice on
December 15, 1980 (45 FR 82479). On November 28, 1983 (48 FR 53640), a
supplemental plant notice of review announced changes in the status of
various species. We published complete updates of the plant notice on
September 27, 1985 (50 FR 39526), February 21, 1990 (55 FR 6184),
September 30, 1993 (58 FR 51144), and, as part of combined animal and
plant notices, on February 28, 1996 (61 FR 7596), September 19, 1997
(62 FR 49398), October 25, 1999 (64 FR 57534), October 30, 2001 (66 FR
54808), and June 13, 2002 (67 FR 40657). Additionally, on January 8,
2001 (66 FR 1295), we published our resubmitted petition finding for
one plant species that had an outstanding ``warranted-but-precluded
finding'' on a petition to list.
We published earlier comprehensive reviews for vertebrate animals
in the Federal Register on December 30, 1982 (47 FR 58454), and on
September 18, 1985 (50 FR 37958). We published an initial comprehensive
review for invertebrate animals on May 22, 1984 (49 FR 21664). We
published a combined animal notice of review on January 6, 1989 (54 FR
554), and with minor corrections on August 10, 1989 (54 FR 32833). We
again published comprehensive animal notices on November 21, 1991 (56
FR 58804), November 15, 1994 (59 FR 58982), and, as part of combined
animal and plant notices, on February 28, 1996 (61 FR 7596), September
19, 1997 (62 FR 49398), October 25, 1999 (64 FR 57534), October 30,
2001 (66 FR 54808), and June 13, 2002 (67 FR 40657). On January 8, 2001
(66 FR 1295), we published our resubmitted petition findings for 25
animal species that had outstanding ``warranted-but-precluded''
petition findings as well as notice of one candidate removal.
This revised notice supersedes all previous animal, plant, and
combined notices of review.
Summary
Since publication of the 2002 CNOR, we reviewed the available
information on candidate species to ensure that a proposed listing is
justified for each species and to reevaluate the relative listing
priority assignment of each species. We also evaluated whether we
should emergency-list any of these species, particularly species with
high priorities (i.e., species with listing priority numbers of 1, 2,
or 3). We undertook this effort to ensure that we focus conservation
efforts on those species at greatest risk. As of April 19, 2004, 20
animals are proposed for endangered status; 3 animals are proposed for
threatened status (not including proposed reclassifications of
endangered species); 1 animal is proposed for threatened due to
similarity of appearance; and 142 plant and 137 animal candidates are
awaiting preparation of proposed rules (see Table 1). Table 2 includes
19 species that we previously classified as either proposed for listing
or candidates that we no longer classify in those categories.
Summary of New Candidates
Below we present brief summaries of 24 new candidates. Complete
information, including references, can be found in the candidate forms.
You may obtain a copy of these forms from the Regional office that has
the lead for the species, or from our Internet Web site (http://
endangered.fws.gov).
Mammals
Fisher, West Coast DPS (Martes pennanti)--See our initial
``warranted-but-precluded'' finding signed on April 2, 2004, and
published in the Federal Register on April 8, 2004 (68 FR 18770).
Birds
Kittlitz's murrelet (Brachyramphus brevirostris)--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 murrelet is a relatively rare
seabird. Most recent population estimates indicate that it has the
smallest population of any seabird considered a regular breeder in
Alaska (9,000 to 25,000 birds). This species appears to have undergone
significant population declines in three of its core population
centers--Prince William Sound, Malaspina Forelands, and Glacier Bay. As
populations become smaller, they become increasingly vulnerable to
events that may result in extirpation. Causes for the declines are not
well known, but likely include: habitat loss or degradation, increased
adult and juvenile mortality, and low recruitment and we believe that
glacial retreat and oceanic regime shifts are the factors that are most
likely causing population-level declines in this species. Existing
regulatory mechanisms appear inadequate to stop or reverse population
declines or to reduce the threats to this species. Due to the non-
imminent threats of high magnitude, we assign this species a listing
priority number of 5.
Xantus's murrelet (Synthliboramphus hypoleucus)--Xantus's murrelet
is a small seabird of the Alcid family that occurs along the western
coast of North America in the United States and Mexico. Xantus's
murrelet populations in the United States and Mexico appear to have
declined due to a wide variety of threats, with substantial declines
evident at the largest known breeding population and extirpations on
three of the Mexican islands. Data from the largest breeding population
in the United States indicated a dramatic decline (up to 70 percent);
data from other islands are scarce.
Although the decline in Xantus's murrelet populations appears to
have been substantial, the largest threats are being addressed, and, to
some degree, ameliorated in the United States. Although predation is a
large contributor to the current low population numbers of the Xantus's
murrelet, it does not pose as imminent a threat as it once did. Cats
and rats have been removed from many of the islands where they once
occurred. Anacapa Island implemented a rat eradication program in 2001
that seems to have been successful in removing that non-native predator
of the Xantus's murrelet. Rats were eradicated in 1994 from San Roque
Island. The Service has been working with the State of California,
National Park Service, and National Marine Fisheries Service to address
the threats of light pollution and human disturbance. To address this
threat, the California Department of Fish and Game implemented
regulations to require shielding and limit wattage of lights used by
boats conducting nighttime fishing activities. Although these
regulations do not remove the negative effects of this activity, they
likely have resulted in a reduction of the impacts. Oil pollution may
pose a potential threat to the survival of the Xantus's murrelet
population, but is not likely responsible for the species' current low
numbers. Due to the nonimminent threats of high magnitude, we assign
this species a listing priority number of 5.
Clams
Rayed bean (Villosa fabalis)--Once a common mussel species, the
rayed bean
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has disappeared from a large portion of its range, including the entire
Tennessee River system and south of the Ohio River. The threats to the
rayed bean appear significant and present throughout the species'
range. Threats associated with habitat loss and degradation appear to
include ongoing impoundments, channelization, chemical contaminants,
mining, and sedimentation. Population losses due to impoundments appear
to have contributed more to the decline and imperilment of the rayed
bean than any other single factor. In addition, the invasive exotic
zebra mussel has become established throughout the majority of the
rayed bean's range and has the long-term potential of spreading
throughout additional portions of the range. Remaining rayed bean
populations are small and geographically isolated, making them
susceptible to a single catastrophic event and making natural
repopulation and genetic interchange impossible. The zebra mussel has
already eliminated the rayed bean from Lakes Erie and Tippecanoe and
the Detroit River and is posing an immediate threat to the rayed bean
populations in the Lake St. Clair drainages, Allegheny and Tippecanoe
Rivers, French Creek, and Lake Maxinkuckee. The resulting range
restrictions and disjunct nature of the remaining populations may make
the rayed bean subject to reductions in genetic diversity and limited
natural reproduction. Because the threats appear to be imminent and of
high magnitude, we assign this species a listing priority number of 2.
Sheepnose mussel (Plethobasus cyphyus)--Historically, the sheepnose
was fairly widespread in many Mississippi River system streams,
although rarely very common. The sheepnose has apparently been
eliminated from two-thirds of the total number of streams from which it
was historically known (26 streams currently compared to 77 streams
historically). Recruitment reduction or failure is a potential problem
for many small sheepnose populations rangewide; this potential problem
is exacerbated by the species' reduced range and increasingly isolated
populations. The threats to the sheepnose appear include exotic species
(especially zebra mussels), impoundments, fluctuating flow releases
from dams, sedimentation, small population size, isolation of
populations, gravel mining, channel dredging, municipal pollutants,
agricultural runoff, nutrient enrichment, and coal processing
pollution. These threats may be catastrophic, such as spills, or
chronic, such as zebra mussel infestation and habitat quality
degradation. Most extant populations have few individuals. Such
populations may have extreme difficulty in successfully reproducing.
Threats that affect the ability to reproduce over time could result in
essentially sterile, aging, disjunct populations. Although there are
ongoing attempts to alleviate some of these threats, there appear to be
no populations without significant threats, and many threats are
without obvious or readily available solutions. Due to high-magnitude
threats that appear to be imminent, we assign this species a listing
priority number of 2.
Spectaclecase (Cumberlandia monodonta)--The currently accepted
taxonomy places the spectaclecase in the monotypic genus, Cumberlandia.
The spectaclecase occurred historically in at least 45 streams in the
Mississippi, Ohio, and Missouri Rivers. Extant populations of the
spectaclecase are known from 20 streams. Of the 20 extant populations,
7 of those populations are represented by a single specimen each. Only
three or four populations could be characterized as large. Threats to
the continued existence of the spectaclecase appear to include exotic
species, especially zebra mussels; delivery and deposition of fine
sediments; small population sizes; isolation of populations; livestock
grazing; wastewater effluents; mine runoff; unstable and coldwater
flows downstream of dams; gravel mining; and channel dredging. Although
there are ongoing attempts to alleviate some of these threats at some
locations, there appear to be no populations without significant
threats and many threats are without obvious or readily available
solutions. In addition, the fish host of the spectaclecase is unknown;
thus, propagation to reestablish the species in restored habitats and
to maintain nonreproducing populations and focused conservation of its
fish host are not yet possible. Therefore, we consider the threats to
spectaclecase to be of high magnitude. However, 10 populations are
reproducing or supported via immigration from large populations, and
three or four of these populations may be described as large. We assign
this species a listing priority number of 4.
Round ebonyshell (Fusconaia rotulata)--The round ebonyshell is
endemic to the Escambia River drainage and is only known from the main
channel of the Conecuh/Escambia River (the river name changes across
the Alabama/Florida State boundary). Only 3 of 9 historic locations
appear to contain living individuals; thus, the number of sites known
to support this species has declined by 67%. On average, only 2 live
individuals were found at each of the remaining 3 sites. Threats
associated with habitat loss and degradation appear to occur throughout
the range of the seven Gulf-Coast mussel species discussed here and
below. The river habitats of mussel species are vulnerable to habitat
modification, sedimentation, and water quality degradation. Highway and
reservoir construction, poorly managed logging practices, agricultural
runoff, housing developments, pipeline crossings, and livestock grazing
may result in physical disturbance of stream substrates or the riparian
zone, and/or changes in water quality, temperature, or flow.
Sedimentation can cause direct mortality of mussels by deposition and
suffocation. Although the negative effects of point source discharges
on aquatic communities in Alabama and Florida have been reduced over
time due to compliance with State and Federal water quality
regulations, there has been less success in dealing with non-point
source pollution impacts, particularly sediments, on small stream
drainages. The round ebonyshell is restricted to a few populations with
few individuals. Due to the high magnitude and immediacy of the
threats, we assign the round ebonyshell a listing priority number of 2.
Southern kidneyshell (Ptychobranchus jonesi)--The southern
kidneyshell is endemic to the Escambia and Yellow river drainages in
Alabama, and the Choctawhatchee river drainage in Alabama and Florida.
Currently, of 20 sites for which we have recent data, southern
kidneyshells were only found at 1or 2 sites, representing at least a
78% decline in the number of sites supporting this species. The threats
associated with habitat loss and degradation are described in the above
paragraph for the round ebonyshell; all seven new Gulf Coast candidate
mussel species appear to share the same threats. The southern
kidneyshell is restricted to a few populations with very few
individuals. Due to the high magnitude and immediacy of the threats, we
assign the southern kidneyshell a listing priority number of 2.
Narrow pigtoe (Fusconaia escambia)--The narrow pigtoe is endemic to
the Escambia River drainage in Alabama and Florida and the Yellow River
drainage in Florida. Twenty-one locations currently support narrow
pigtoes, although in very low numbers, with an average of 3 live
individuals found per site. The threats associated with habitat loss
and degradation are described in the above paragraph for the round
ebonyshell; all seven new Gulf
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Coast candidate mussel species appear to share the same threats.
However, the narrow pigtoe is spread among a number of populations,
with each population containing few individuals. Since we consider
threats to be of a high magnitude and but nonimminent, we assigned the
narrow pigtoe a listing priority number of 5.
Southern sandshell (Lampsilis australis)--The southern sandshell is
endemic to the Escambia River drainage in Alabama, and the Yellow and
Choctawhatchee River drainages in Alabama and Florida. Recent mussel
surveys found that live populations of the southern sandshell have
declined from a total of 51 historic sites to its current distribution
of 30 active sites and 5 sites with unknown population status. It
appears to have been extirpated from approximately 31-41% of its
historic range. Recent mussel surveys found an average of 2-3 live
animals per site. Gravid females have been detected within the 2 larger
populations found in the Choctawhatchee River basin. Low levels of
recruitment are likely occurring within these two populations, although
juvenile southern sandshells were not detected. The threats associated
with habitat loss and degradation are described in the above paragraph
for the round ebonyshell; all seven new Gulf Coast candidate mussel
species appear to share the same threats. The southern sandshell is
spread among a number of populations, with each population containing
few individuals. Because we consider threats to be of high magnitude
and nonimminent, we assign the southern sandshell a listing priority
number of 5.
Fuzzy pigtoe (Pleurobema strodeanum)--The fuzzy pigtoe is endemic
to the Escambia and Choctawhatchee Rivers in Alabama and Florida, and
the Yellow River in Alabama. Recent mussel status surveys found that
the populations of the fuzzy pigtoe (represented by live animals and
shell material) have declined from a total of 86 historic sites to its
remaining distribution of 58 sites, representing an approximate 22%
decline in its historic range. Four populations were as large as 10-20
individuals; most supported only 1 or 2 individuals. The threats
associated with habitat loss and degradation are described in the above
paragraph for the round ebonyshell; all seven new Gulf Coast candidate
mussel species appear to share the same threats. The fuzzy pigtoe is
spread among a number of populations with each population containing
few individuals. We consider threats to be of high magnitude and
nonimminent. We assign the fuzzy pigtoe a listing priority number of 5.
Choctaw bean (Villosa choctawensis)--The Choctaw bean is endemic to
the Escambia, Yellow, and Choctawhatchee River drainages in Alabama and
Florida. Recent mussel status surveys found that populations (live and
shell material only) of the Choctaw bean have declined from a total of
45 historic sites to its remaining distribution of 34 sites. It appears
to have been extirpated from approximately 11% of its historic range.
An average of two individuals were found live per site. The threats
associated with habitat loss and degradation are described in the above
paragraph for the round ebonyshell; all seven new Gulf Coast candidate
mussel species appear to share the same threats. The Choctaw bean is
spread among a number of populations, with each population containing
few individuals. Threats appear to be of high magnitude and
nonimminent, and we assign the Choctaw bean a listing priority number
of 5.
Tapered Pigtoe (Quincuncina burkei)--The tapered pigtoe is endemic
to the Choctawhatchee River drainage in Alabama and Florida. During
recent status surveys, the tapered pigtoe was found live and as shell
material at 33 of 54 historical sites with an average of 7 individuals
per site. Only four populations contained as many as 10-20 individuals.
The tapered pigtoe has been extirpated from approximately 28% of its
historic range. The threats associated with habitat loss and
degradation are described in the above paragraph for the round
ebonyshell; all seven new Gulf Coast candidate mussel species appear to
share the same threats. The threats to the tapered pigtoe appear to be
moderate-to-low magnitude and nonimminent, and we assign the tapered
pigtoe a listing priority number of 11.
Insects
Coleman cave beetle (Pseudanophthalmus colemanensis)--The Coleman
Cave beetle is only known from Coleman Cave, Montgomery County,
Tennessee. Most members of the insect genus Pseudanophthalmus are cave
dependent (troglobites) and are not found outside the cave environment.
Due to the Coleman's cave beetle's limited distribution, it is
vulnerable to isolated events. Events such as toxic chemical spills,
discharges of large amounts of polluted water, closure of entrances,
alteration of entrances, or the creation of new entrances could have
serious adverse impacts on the Coleman Cave beetles and could result
its extinction. The Coleman Cave beetle currently receives some
protection under a formal Cooperative Management Agreement;
consequently the threats it faces are more moderate. Due the moderate
magnitude of the nonimminent threats, we assign the Coleman Cave beetle
a listing priority number of 11.
Fowler's cave beetle (Pseudanophthalmus fowlerae)--Fowler's cave
beetle was described from 11 specimens collected from 1959 through 1965
from Sheals Cave, Clay County, Tennessee. The species is not known from
any other caves. Fowler's cave beetle has not been observed or
collected since 1965, but species experts presume that it still exists
in low numbers. The limited distribution of Fowler's cave beetle makes
it vulnerable to isolated events that would only have a minimal effect
on the more wide-ranging members of the genus. Events such as toxic
chemical spills, discharges of large amounts of polluted water, closure
of entrances, alteration of entrances, or the creation of new entrances
could have serious adverse impacts on cave beetles and could result in
their extinction. Due to the high magnitude of the nonimminent threats,
we assign the Fowler's cave beetle a listing priority number of 5.
Insular cave beetle (Pseudanophthalmus insularis)--The insular cave
beetle is known from only one cave. In 1988, this cave was searched in
1998 for additional specimens of this species but none were found.
Although the species has not been observed since 1957, species experts
presume that it still exists in low numbers. The limited distribution
of the insular cave beetle makes it vulnerable to isolated events that
would only have a minimal effect on the more wide-ranging members of
the genus. Events such as toxic chemical spills, discharges of large
amounts of polluted water, closure of entrances, alteration of
entrances, or the creation of new entrances could have serious adverse
impacts on the insular cave beetle and could result in their
extinction. Due the high magnitude of the nonimminent threats, we
assign the insular cave beetle a listing priority number of 5.
Soothsayer cave beetle (Pseudanophthalmus tiresias)--The soothsayer
cave beetle is known to occur in two caves. The original description of
this taxon was based upon six specimens collected from Indian Grave
Point Cave, DeKalb County, Tennessee, in 1956. These specimens were
collected near the cave's entrance sink in an area that had high
humidity, stable temperatures, and
[[Page 24880]]
a few fragments of rotten wood that had fallen into the sink. Four
specimens were later collected from nearby Fox Cave. Three searches
were conducted between 1997 and 1999, but no additional specimens of
this species have been found. Despite the recent failures to find the
species, species experts believe that the soothsayer cave beetle is
still present in Indian Grave Point and Fox caves, in at least very low
numbers. The limited distribution of soothsayer cave beetle makes it
vulnerable to isolated events that would only have a minimal effect on
the more wide-ranging members of the genus. Events such as toxic
chemical spills, discharges of large amounts of polluted water, closure
of entrances, alteration of entrances, or the creation of new entrances
could have serious adverse impacts on cave beetles and could result in
their extinction. Due the high magnitude of the nonimminent threats, we
assign the soothsayer cave beetle a listing priority number of 5.
Noblett's cave beetle (Pseudanophthalmus paulus)--Noblett's Cave
beetle was described from two specimens collected in 1967 from
Noblett's Cave, Monroe County, Tennessee. Despite several searches
conducted in this cave and in other caves in the vicinity, no
additional specimens have been found. However, species experts believe
that it probably still exists in low numbers. Noblett's Cave is a small
(about 500 feet long) muddy cave with a stream flowing through it. The
limited distribution of Noblett's Cave beetle makes it vulnerable to
isolated events that would only have a minimal effect on the more wide-
ranging members of the genus. Events such as toxic chemical spills,
discharges of large amounts of polluted water, closure of entrances,
alteration of entrances, or the creation of new entrances could have
serious adverse impacts on cave beetles and could result in their
extinction. Due to the high magnitude of the nonimminent threats, we
assign the Noblett's Cave beetle a listing priority number of 5.
Nevares Spring naucorid bug (Ambrysus funebris)--The Nevares Spring
naucorid bug is an aquatic insect that has a distribution that is
limited to the Travertine-Nevares Springs Complex within Death Valley
National Park, in Inyo County, California, where surveys indicate that
it is extremely rare component of the aquatic invertebrate community.
The Travertine and Nevares Springs areas have eight water collection
facilities that provide water for commercial and domestic uses.
Information pertaining to the historical distribution of the Nevares
Spring naucorid bug prior to the development of the local water
collection systems is not available. It is likely that the species
occupied a large area of habitat where suitable micro-habitat features
were present. The widespread loss of aquatic habitat within the
Travertine-Nevares Springs Complex since the water collection systems
were installed suggests the species has experienced major reductions in
abundance and distribution as stream environments were eliminated or
reduced in extent. The effects of water diversion activities are also
most pronounced during the summer months when aquatic habitats and the
species that occupy those habitats are most restricted, and therefore
vulnerable to perturbation. Nevares Spring naucorid bugs are also
likely to experience direct predation by mosquitofish and compete with
these fish for limited food resources. Due the high magnitude and
nonimminent threats, we assign the Nevares Spring naucorid bug a
listing priority number of 5.
Flowering Plants
Hala pepe (Pleomele fernaldii)--We accidentally removed this
species from the June 13, 2002, list of candidates and are now
restoring it to the list of candidates.
Brand's phacelia (Phacelia stellaris)--Brand's phacelia was
historically found in Los Angeles, Riverside, and San Diego Counties,
and in coastal northern Baja California, Mexico. Only 3 of the 15 sites
in the United States ever known to support populations of this species
still remain. Two of the three known extant populations in the United
States are from coastal San Diego County. The other is in western
Riverside County. Two populations may remain in Mexico, although one
has not been verified since 1975. The apparent threats to this species
include trampling or habitat degradation by foot or vehicular traffic
and the invasive spread of non-native iceplant (Carpobrotus edulis).
Therefore, with imminent threats of high magnitude, we assign this
species a listing priority number of 2.
Churchill Narrows buckwheat (Eriogonum diatomaceum)--Churchill
Narrows buckwheat 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. The habitat of all but 3 of the 15 occurrences of
Churchill Narrows buckwheat is subject to imminent exploration and
potential development of existing mining claims. Observations in 2003
confirmed that mining activities have had direct and indirect impacts
on Churchill Narrows buckwheat in the recent past and these impacts are
likely to increase. A Notice of Operation for the exploration and
development of a mining claim within the largest occurrence of the
species has been filed with the BLM. Threats on the species from
mining, trampling and soil disturbance by livestock habitat occur
rangewide, populations are small and somewhat fragmented, and
inadequate regulatory mechanisms are in place to protect this species
throughout its range. Due to the imminent threats of high magnitude, we
assign this species a listing priority number of 2.
Orcutt's hazardia (Hazardia orcuttii)--Orcutt's hazardia is a
shrubby species in the Asteraceae (sunflower family). Although once
described as fairly common in open habitats along coastal plains from
Colonet to Tijuana in Baja California, Mexico, only one occurrence in
Mexico has been confirmed since 1975. The only known extant occurrence
in the United States of this species is in Encinitas, California,
primarily within the Manchester Conservation Area (MCA) managed by
Center for Natural Lands Management. Apparent threats on the species
include ongoing, direct impacts from unauthorized access to MCA.
Impacts include pedestrian trespass, creation of bicycle trails, and
unauthorized fire suppression training (without the permission of the
land owners). Introduced invasive exotic plants may also pose a
significant threat. With imminent threats of high magnitude, we assign
this species a priority number of 2.
Everglades bully (Sideroxylon reclinatum ssp. austrofloridense)--
The Everglades bully is a shrub restricted to the tropical pinelands of
Miami-Dade County, Florida. Outside of Everglades National Park, only
about 1 percent of the Miami Pine Rock Ridge pinelands remain, and much
of what is left is in small remaining blocks isolated from other
natural areas. Everglades bully is known to occur on conservation lands
only at Long Pine Key (8,029 ha or 19,839 acres) in Everglades National
Park, Larry and Penny Thompson Park (93 hectares or 229 acres), and the
privately owned Pine Ridge Sanctuary (5.7 ha or 14 acres). Fire
suppression and exotic plant invasions are the greatest threats to
Everglades bully and other pineland understory plants. Historically,
pine rocklands had an open low understory where natural fires remained
patchy, with relatively low temperatures, thus sparing many native
grasses and shrubs. Dense exotic plant
[[Page 24881]]
growth can create much higher temperature fires and longer burning
periods. Pine rockland plants cannot tolerate these extreme conditions.
Among the exotic pest plants present in the Everglades National Park is
Old World climbing fern, Lygodium microphyllum, which is capable of
smothering vegetation and is spreading rapidly in Florida. It is
spreading into southernmost Florida, and is already a very serious
problem in Loxahatchee National Wildlife Refuge. Based on the moderate
magnitude of the imminent threats, we assign a listing priority number
of 9.
Summary of Listing Priority Changes in Candidates
Mammals
Southern Idaho ground squirrel (Spermophilus brunneus endemicus)--A
dramatic population decline of the southern Idaho ground squirrel has
occurred during the past 30 years. Scientists attribute the decline to
invasive non-native plants associated with a change in the fire
frequency, and the lack of reclamation or restoration of habitat by
various land management agencies and private landowners. Even though
habitat degradation is pervasive in many areas of this species' range,
suitable habitat areas that can support southern Idaho ground squirrels
still persist. Conservation and habitat rehabilitation actions have
begun in some areas, and in 2001 and 2002, over 100 squirrels were
captured from the Weiser Golf Course (the largest known colony site)
and translocated to suitable habitat on lands covered by a Candidate
Conservation Agreement with Assurances. These actions, in combination
with other conservation and research actions described in the candidate
form, lead us to conclude that the magnitude of threats, while still
high, is trending toward a moderate-to-low range. While there is still
concern for genetic constriction and isolation due to generally low
numbers of individuals at existing sites, natural dispersal is
occurring at some sites, and translocation efforts are being
implemented each year. Based on the recent conservation efforts
described above, it seems apparent there is now some commitment by
various agencies and parties to initiate and implement conservation
actions on behalf of the southern Idaho ground squirrel. These actions,
in combination with other conservation and research actions described
above, lead us to change the imminence of threats to non-imminent.
Thus, the listing priority number is changed from a 3 to a 6.
Birds
Gunnison sage-grouse (Centrocercus minimus)--The range of the
Gunnison sage-grouse has been reduced to less than 25 percent of its
historical range. Size of the range and quality of its habitat have
been reduced by direct habitat loss, fragmentation, and degradation
from building development, road and utility corridors, fences, energy
development, conversion of native habitat to hay or other crop fields,
alteration or destruction of wetland and riparian areas, inappropriate
livestock management, competition for winter range by big game, and
creation of large reservoirs. Other factors affecting the Gunnison
sage-grouse include fire suppression, overgrazing by elk (Cervus
elaphus) and deer (Odocoileus hemionus), drought, disturbance or death
by off-highway vehicles, harassment from people and pets, noise that
impairs acoustical quality of leks (courtship areas), genetic
depression, pesticides, pollution, and competition for habitat from
other species. For greater detail, see 65 FR 82310 (December 28, 2000).
Numerous conservation actions have occurred and funding and plans
for additional conservation actions are in place. However, threats to
the sage-grouse currently have not been eliminated or reduced enough
through conservation actions to remove the potential need for listing.
With population numbers already low, the threat of drought-related
declines, coupled with other threats, are of concern. Not only have
sage-grouse numbers declined in 2003 and may decline in 2004 due to the
2002 drought, it is unknown how long drought conditions may last. Based
on information available to date, including continued and significant
population declines in 2003, threats to the sage-grouse have increased
in the last year due to drought-related effects to the habitat and
effects to chick survival and recruitment, and relaxation of
restrictions on land use in Gunnison County, which harbors the only
large population of the bird. Given these ongoing high magnitude
threats, we are elevating the listing priority from a 5 to a 2.
However, we do not believe that emergency listing is warranted at this
time based on the size of the population remaining in the Gunnison
Basin and continued pre-listing conservation actions.
Fish
Fluvial arctic grayling, upper Missouri River DPS (Thymallus
arcticus)--The fluvial arctic grayling distinct vertebrate population
segment (DPS) once ranged throughout the upper Missouri River drainage,
but now the only remnant population is restricted to the upper Big Hole
River, an area estimated to be less than 5 percent of the species'
historical range. In fall of 2002, the remnant grayling population in
the Big Hole River apparently had declined to such a low level that not
enough fish were captured to estimate population density. The spring
2002 spawning surveys captured the lowest number of grayling in the
past 14 years of sampling, and the spawning population was skewed to
older fish, indicating limited recruitment for the past 2 years. In
2003, abundant numbers of grayling were found in the lower reaches of
tributaries with the coolest water temperatures.
Efforts to reestablish grayling populations within the historic
range in the upper Missouri River basin began in 1997. At this time,
there is no evidence that these efforts have been successful in
reestablishing self-sustaining populations at any of four
reintroduction sites. Drought conditions since 1999 have increased
water temperatures, reduced flows, and exacerbated the effects of
ongoing threats such as flow reductions from irrigation and stock water
withdrawals, locally degraded habitat conditions, and potential
competition or predation from non-native fish. Cooperative, community-
based efforts have focused primarily on working with water users to
leave water in the Big Hole River to increase flows and reduce water
temperatures during periods of drought. The Big Hole Watershed
Committee, the Montana Fish, Wildlife and Parks Department, and the
Service's Partners for Fish and Wildlife program are committed to
ongoing, on-the-ground conservation efforts for grayling. Despite these
efforts, there continue to be periods when flows are well below those
considered ``survival'' flows for grayling and water temperatures
exceed the thermal tolerance of grayling. Based on the 2002 grayling
population surveys, we are elevating the listing priority number for
this population from a 9 to 3 because the threats continue to be
imminent and the magnitude is now high. However, these threats do not
rise to the level that emergency listing is necessary, since, among
other things, biologists found increased population numbers in the
lower, cooler reaches of tributaries to the mainstem Big Hole River, in
2002 and 2003, hopefully mitigating for the low numbers of grayling
found in the mainstem Big Hole River.
[[Page 24882]]
Snails
Page springsnail (Pyrgulopsis morrisoni)--The Page springsnail is
known to exist only within a complex of springs located within an
approximately 1.5-kilometer (0.93-mile) stretch along the west side of
Oak Creek around the community of Page Springs, Yavapai County,
Arizona. Many of the springs where the Page springsnail occurs have
been subjected to some level of modification to meet domestic,
agricultural, ranching, fish hatchery, and recreational needs. Arizona
Game and Fish Department (AGFD) management plans for the Bubbling Ponds
and Page Springs fish hatcheries included commitments to replace lost
habitat and to monitor remaining populations of invertebrates such as
the Page springsnail. Based on recent survey data, it appears that the
Page springsnail is abundant within its habitats and is more widely
distributed than previously known. Monitoring by AGFD and Service
biologists no longer entails snail removal, which appears to have had a
temporary impact on population numbers. In addition, the threat of
ground water withdrawal is not considered imminent because recent
studies indicate that the groundwater system of the Verde Valley has
not yet been affected by development and base flow in the Verde River
Valley has remained virtually unchanged since 1915. Because these
threats are nonimminent, we changed the listing priority number from 2
to 5 for this species.
Insects
The Surprising Cave beetle (Pseudanophthalmus inexpectatus)--This
species was described from specimens collected in the historic section
of Mammoth Cave and White Cave, Mammoth Cave National Park (MCNP),
Edmonston County, Kentucky. Subsequent to these original discoveries,
the species was also found in MCNP's Great Onyx Cave. In 2002, MCNP
discovered a previously unknown population of this species in a fourth
MCNP cave. The insect genus Pseudanophthalmus is in the predatory-
ground-beetle family Carabidae. Most members of this genus are cave
dependent (troglobites) and are not found outside the cave environment.
Their limited distributions make these species vulnerable to isolated
events that would only have a minimal effect on the more wide-ranging
members of the genus. Events such as toxic chemical spills, discharges
of large amounts of polluted water, closure of entrances, alteration of
entrances, or the creation of new entrances could have serious adverse
impacts on these cave beetles and could result in their extinction. In
September 2001, MCNP and the Service entered into a Candidate
Conservation Agreement for the surprising cave beetle. The Agreement
will ensure that all habitat components required to protect and improve
the conservation status of this species, especially an adequate food
source, are provided through the MCNP's management of the caves that
support the species. Under this agreement MCNP has developed and
implemented a monitoring program for the species and its habitat. Thus,
the magnitude of the threat to the surprising cave beetle is reduced
because of its location on Federal land and the formal commitment
through a Candidate Conservation Agreement between MCNP and the Service
to protect the species. Therefore, we changed the listing priority
number for the surprising cave beetle from a 5 to an 11.
Flowering Plants
San Fernando Valley spineflower (Chorizanthe parryi var.
fernandina)--San Fernando Valley spineflower is currently known from
only two populations. The plants are under threat by habitat loss due
to residential development, competition from non-native plants (e.g.,
several non-native grasses), stochastic events, such as erosion and
fire, and the potential loss of the native pollinator community due to
competition with and predation by the non-native Argentine ants
(Linepithema humilis). The site in Los Angeles County, the Newhall
Ranch, is proposed for residential development that has the potential
to cause the loss of most, if not all, of the remaining plants at that
site. Development at this site is expected to begin in 2004. While the
landowner has approached us with the idea to enter into a Candidate
Conservation Agreement, no documents have been submitted nor any
agreement processed, so we cannot assume that the immediate threats
from the Newhall Ranch development are gone. However, the site in
Ventura County, the former Ahmanson Ranch, is now under the auspices of
the Santa Monica Mountains Conservancy; a joint powers authority
operated by the State to conserve lands within the Conservancy's sphere
of influence. We believe the direct threats to the species from the
former Ahmanson Ranch development plan have been eliminated, and we are
working with the new landowners to manage the site for the benefit of
Chorizanthe parryi var. fernandina. Since the threats to Chorizanthe
parryi var. fernandina from habitat destruction or modification are
less than they were 2 years ago, we are lowering the listing priority
number from a 3 to a 6 reflecting threats that are high but
nonimmenent.
Whorled sunflower (Helianthus verticillatus)--This species is found
in moist, prairie-like openings in woodlands and along adjacent creeks
in northwest Georgia, Alabama, and Tennessee. This species appears to
be a narrow habitat specialist occurring in natural wet meadows or
prairies and calcareous barrens. The greatest threat to this species
appears to be from industrial forestry practices. The largest
population is permanently protected through a conservation easement
with The Nature Conservancy. The magnitude of threat is now considered
moderate due to this recent development. The threats are viewed as not
imminent, in that the species is able to withstand some disturbance and
we know of no projects/activities at this time that imminently threaten
the other populations. Thus, we changed the listing priority number
from a 5 to an 11.
Graham beardtongue (Penstemon grahamii)-Penstemon grahamii 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. The species population is estimated at about 7,000
individuals with 36 known occurrences. Most of the occupied habitat of
P. grahamii is within developed and expanding oil and gas fields with
several wells and access roads within the species' occupied habitat.
The location of P. grahamii habitat exposes it to possibility of
habitat destruction from off-road vehicle (ORV) use and road, pipeline,
and well-site construction in connection with oil and gas development.
With such a small population and limited occupied habitat, any
destruction, modification, or curtailment of the habitat could
negatively impact the species. Collection of plants and seeds is a
significant threat due to the desire of rock-garden enthusiasts to
obtain this very attractive plant. The species is heavily grazed by
wildlife (rodents, rabbits, and possibly deer) and by livestock
(primarily sheep). Livestock trampling is affecting some populations.
Historical overgrazing is thought to have caused the extirpation of
some P. grahamii populations. The potential threats associated with oil
and gas development within the habitat of P. grahamii are considered to
be imminent in light of the increased seismic survey and petroleum
leasing. Therefore, we have elevated the LPN for this species
[[Page 24883]]
from 5 to 2 because the threats continue to be of high magnitude, and
are now considered imminent.
Ferns and Allies
Palapali (Microlepia strigosa var. mauiensis)--This fern was
formally known as the full species Microlepia mauiensis. In a recent
review of the taxonomy of Hawaiian ferns, it was changed to a variety
of M. strigosa. This fern, now classified as a variety, continues to be
a candidate; however, this taxonomic change changes the priority number
from a 2 to a 3.
Christella boydiae--This Hawaiian fern species (no common name) was
originally described in 1897 in the genus Christella. It was then
placed in the genus Thelypteris. More recently, in 1999, it was placed
in the genus Cyclosorus and split into two varieties (var.
kipahuluensis and var. boydiae). Both of these varieties were
recognized in the June 13, 2002, CNOR as candidates, each with the
priority number of 6. In a 2002 review of Hawaiian ferns, the species
was returned to the genus Christella. The most recent taxonomic
description removes recognition of the two former varieties within the
species of Christella boyidae; however, the entire species remains a
candidate. Therefore, the priority number moves from 6 to 5.
Other Taxonomic Changes in Candidates
Sheath-tailed bat (Emballonura semicaudata semicaudata and E.
semicaudata rotensis)--This species was included in the 2002 CNOR as a
Distinct Vertebrate Population Segment within the U.S. Territories,
which encompasses a subspecies and a Distinct Population Segment of a
second subspecies: E. semicaudata rotensis, endemic to the Mariana
Islands; and the American Samoa DPS of E. semicaudata semicaudata,
endemic to Western and American Samoa, Tonga, Fiji, and Vanuatu. In
1997, Koopman described four subspecies to E. semicaudata, which are
now widely accepted. The sheath-tailed bats that continue to warrant
candidacy are within E. semicaudata rotensis and the American Samoa DPS
of Emballonura semicaudata semicaudata. Thus, with this 2003 CNOR and
accompanying candidate form, we are renaming the continuing candidate
entity as the following two entities: the subspecies historically found
in the Marianas Islands (E. s. rotensis) and the American Samoan DPS of
E. s. semicaudata that was historically found in Samoa, Fiji, Tonga,
and Vanuatu. In addition, due to a clerical error, we previously
identified this species being subject to an active petition and
therefore requiring a ``resubmitted warranted-but-precluded'' 12-month
petition finding. In this notice we do not treat the sheath-tailed bat
among the petitioned candidates.
Populations of E. s. rotensis on the Mariana Islands of Guam and
Rota have been extirpated and the Mariana population on Aguijan has
been reduced to approximately 10 individuals. A similar drastic decline
has occurred in American Samoa where populations of E. s. semicaudata
were estimated at over 10,000 in 1976. In 1993, only four bats were
recorded. E. s. semicaudata occurs only on Tutuila Island and is
probably extirpated from Western Samoa. The nearest population is in
Tonga.
Tutuila is within the U.S. territory of American Samoa, thus this
DPS is delimited by international government boundaries. The sheath-
tailed bat resides in caves and is very susceptible to disturbance.
Roost sites have been rendered unsuitable for bats by human intrusion
into caves and the use of some caves as garbage dumps. Typhoons have
also damaged some caves by blocking entrances or by flooding coastal
caves. No single threat appears to be the cause of the reduced range of
the sheath-tailed bat in the Marianas and in American Samoa. The loss
of roosting caves, the loss of foraging habitat due to deforestation,
disturbance by feral ungulates, introduced predators, and possibly
pesticide use are appear to be the primary factors. In addition, small
populations and limited numbers of populations place these two
candidate sheath-tailed bats at great risk of extinction from
inbreeding, random events, and storms. Based on immediate threats of a
high magnitude, we retained the listing priority number of the sheath-
tailed bat for the two candidate entities: E. s. rotensis and the
American Samoa DPS of E. s. semicaudata, each a listing priority number
of 3.
Candidate Removals
Ferns and Allies
Hohiu kilau (Dryopteris glabra var. pusilla (formerly Dryopteris
tenebrosa))--This recently discovered small terrestrial fern was
previously treated as one of six separate species that are now all
recognized as varieties of one species, Dryopteris glabra, which occurs
widely through Hawaii. It is believed that the variety pusilla is more
widespread than currently recorded, and additional surveys are needed.
Therefore, we are removing it from candidate status.
Petition for a Candidate Species
The Act provides two mechanisms for considering species for
listing. First, the Act requires us to identify and propose for listing
those species that require listing under the standards of section
4(a)(1). We implement this through the candidate program, discussed
above. Second, the Act 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, under section 4(b)(3)(B) we must make
one of three possible findings within 12 months of the receipt of the
petition (a ``12-month finding'').
The first possible 12-month finding is that listing is not
warranted, in which case we need take no further action on the
petition. Second, we may find that listing is warranted, in which case
we must promptly publish a proposed rule to list the species. Once we
publish a proposed rule for a species, section 4(b)(5) and 4(b)(6)
govern further procedures, regardless of whether or not we issued the
proposal in response to a petition. Third, we may find that listing is
warranted but precluded. Such a finding means that immediate
publication of a proposed rule to list the species is precluded by
higher priority listing proposals, and that we are making expeditious
progress to add and remove species from the Lists, as appropriate.
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 precluded (61 FR 64481, December 6,
1996). Therefore, the standard for making a species a candidate 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 subject to a ``warranted-but-precluded'' 12-month finding to
the candidate list.
This publication also provides notice of both the positive 90-day
finding and the warranted but precluded 12-month findings pursuant to
section 4(b)(3) for candidate species listed on Table 1 that have been
the subject of a petition to list. Even though all candidate species
have warranted but precluded status (and thus the equivalent of
positive 90-
[[Page 24884]]
day and warranted but precluded 12-month findings), we will continue to
publish specific section 4(b)(3) findings on subsequent petitions to
list candidate species in the first CNOR following receipt of the
petition.
In addition, pursuant to section 4(b)(3)(C)(i) of the Act, once a
petition is filed regarding a candidate species, the Service must make
a 12-month petition finding in compliance with section 4(b)(3)(B) of
the Act at least once a year, until the Service proposes the species
for listing or makes a final ``not-warranted'' finding. Section
4(b)(3)(C)(iii) of the Act requires the Service to ``implement a system
to monitor effectively the status of all species'' subject to 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 Service's monitoring of all candidate
species by seeking information regarding the status of those species.
The Service reviews all new information on candidate species as it
becomes available, and identifies any species for which emergency
listing may be appropriate. If the Service determines that emergency
listing is appropriate for any candidate, the Service will make prompt
use of its authority under section 4(b)(7). We have been reviewing and
will continue to review at least annually the status of all candidates
whether or not we receive a petition. Thus, the CNOR and accompanying
candidate 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
fulfill the second component of ``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 (9th Cir. 2001)). In
particular, while the Court found designation as a candidate arguably
constitutes a 90-day finding that there is substantial information that
listing may be warranted and the first prong of a 12-month finding that
protection is warranted, the Court also 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 pursuant to section 4 of
the Act. The Court suggested that this one-line statement of candidate
status also precluded meaningful judicial review and may have
diminished the obligation to monitor the species on an annual basis.
We have drafted subsequent CNORs (including this one) to address
the Court's concerns. We have included below a description of why the
listing of every petitioned candidate species is both warranted and
precluded at this time. Pursuant to section 4(b)(3)(C)(ii) and the
Administrative Procedure Act (5 U.S.C. section 206), any party with
standing may challenge the merits of any ``not warranted'' or
``warranted but precluded'' petition findings incorporated in this
CNOR. The analysis included herein, together with the administrative
record for the decision at issue (particularly the supporting candidate
form), will provide an adequate basis for a court to review the
petition finding. Finally, 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 new 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 other form of notice, any
party with standing may seek judicial review.
We reviewed the current status of and threats to the 42 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. This includes 43 candidate or
listed species for which we previously have published findings. For 42
of these 43 species, we have incorporated any new information we have
gathered since the prior finding (for black-tailed prairie dog, see
below) and, as a result of this review, we made continued ``warranted-
but-precluded'' 12-month findings on the petitions for these species.
There also are 3 new candidate species for which we have received
petitions, and for which we are announcing initial ``warranted-but-
precluded'' findings in this CNOR. Additionally, for one new candidate
species for which we have received a petition, we recently published a
separate initial ``warranted-but-precluded'' finding.
We have identified the 41 species that are candidates and for which
we received petitions by the code ``C*'' in the category column on the
left side of Table 1. As discussed above, this finding means that the
immediate publication of proposed rules to list these species was
precluded by our work on the higher priority listing actions, listed
below, during the period from June 13, 2002 through April 19, 2004. We
will continue to monitor the status of all candidate species, including
petitioned species, as new information becomes available. This review
will 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,
we also present brief summaries of why these particular candidates
warrant listing. More complete information, including references, is
found in the candidate forms. You may obtain a copy of these forms from
the Regional office that has the lead for the species, or from the Fish
and Wildlife Service's Internet Web site: http://endangered.fws.gov/.
We find that the immediate issuance of a proposed rule and timely
promulgation of a final rule for each of these actions has been, for
the preceding months, and continues to be, precluded by higher priority
listing actions. As described in section 4(b)(3)(B)(iii) of the Act, in
order for us to make a ``warranted but precluded'' finding on a
petitioned action, we must be making expeditious progress to add
qualified species to the Lists and to remove from the Lists species for
which the protections of the Act are no longer necessary. This notice
describes our progress in revising the lists since our June 13, 2002,
publication of the last CNOR. We intend to publish these descriptions
annually.
On February 20, 2003, the President signed into law the Fiscal Year
(FY) 2003 Omnibus Appropriations Bill (Omnibus Bill), which
appropriates funding to many Federal agencies and programs, including
the Service's program for completing listing and critical habitat rules
pursuant to Section 4 of the ESA (Listing Program), for the period from
October 1, 2002, through September 30, 2003. Through the Omnibus Bill,
Congress specified that the Service could not spend more than
$9,077,000 on Listing Program actions in FY 2003. Of that total,
Congress also specified that the Service could not spend more than $6
million on designating critical habitat for already-listed species,
leaving $3,077,000 for other listing activities. The Service has worked
to ensure that Congress understands the level of funding necessary to
comply with all of the Service's statutory requirements. In a January
7, 2003, Effects Statement to Conference Managers, the Department of
the Interior informed Congress about these listing program requirements
and requested an increase in the FY 2003 listing budget to $11.8
million.
[[Page 24885]]
Congress, nevertheless, retained the $9 million limit for spending.
For Fiscal Year (FY) 2004, the President requested an increase of
$3,209,000 above the FY 2003 request to bring the Listing Program
budget to $12,286,000. The request included $8,900,000 for designation
of critical habitat for already-listed species, and $3,386,000 to
conduct other Listing Program work. Subsequent to the President's FY
2004 budget request, a number of factors increased the amount of
funding needed to complete judicially-mandated critical habitat work in
FY 2004. Most significantly, the work that the Service was compelled to
defer from FY 2003 had to be funded under the FY 2004 budget, at an
estimated cost of $2,000,000. The Service also received several
additional court orders requiring the Service to perform critical
habitat work in FY 2004. In an October 2003 Effect Statement to the
Conference managers, the Department of the Interior informed Congress
that, because of these additional obligations, the Service needed an
additional $2.5 million for the Listing Program in FY 2004.
Congress did not approve a Listing Program appropriation for FY
2004 until November 7, 2003, more than a month after the start of the
fiscal year. On November 10, 2003, the President signed the 2004
Interior and Related Agencies Appropriations Bill, which funded nearly
fully the amount of the President's request (Pub. L. 108-108 (Nov. 10,
2003)). However, the bill did not address the Service's request for an
additional $2.5 million to fully fund the Listing Program in FY 2004.
Thus, we anticipate that most or all of listing actions for the
candidate species included in this CNOR will continue to be precluded
by higher priority listing actions. The Service allocates the listing
appropriation by task, rather than by region as we have done in the
past. Thus, listing prioritization is accomplished at the national
scale. However, the $3,386,000 is fully allocated to fund any emergency
listings, and essential litigation-related, administrative, and program
management functions and to comply with court orders and court-approved
settlement agreements requiring petition findings or listing
determinations. We are funding actions on the following species this
fiscal year: California tiger salamander--central DPS, Boreal toad,
Miami blue butterfly, Sacramento Mountians checkerspot butterfly, four
subspecies of the skipper Pseudocipaeodes eunus, Rota bridled white-
eye, eastern sage grouse, greater sage grouse, Salt Creek tiger beetle,
Bromus arizonicus, Nasselia cernua, Nesogenes rotensis, Osmoxylon
mariannense, Tabernaemontana rotensis, Lepidium papilliferum,
Cymopterus deserticola, Midvalley fairy shrimp, pacific fisher, Florida
black bear, New England cottontail, Mariana fruit bat, white-tailed
prairie dog, wolverine, Santa Catalina Island fox, Santa Rosa Island,
San Miguel Island fox, Santa Cruz Island fox, northern sea otter--
southwest Alaska DPS, and Colorado river cutthroat trout. We do still
allocate a small amount of funding ($100,000) that is not earmarked for
particular listing actions to each of the Regions. This funding is
referred to ``capability funding.'' With respect to Regions with
relatively few court-mandated deadlines, this funding ensures that
those Regions will maintain the expertise to take listing actions in
the future. When any of this capability funding is available, we may
use it for other high-priority listing actions. We generally prioritize
these other listings by each Region in order of the highest listing
priority number; we fund petition findings for outstanding petitions
regarding species that are not already on the candidate list, and
generally, we fund older petitions before newer ones.
Our progress in listing and delisting qualified species since June
13, 2002, is represented by the publication in the Federal Register of
final listing actions for 14 species; proposed listing actions for the
Gila chub, Southwest Alaska DPS of the northern sea otter, slickspot
peppergrass, and the California tiger salamander; withdrawal of a
proposed listing for the westslope cutthroat trout, flat-tailed horned
lizard, slickspot peppergrass and Tabernaemontana rotensis; final
reclassification for the gray wolf; proposed reclassification of
endangered to threatened for the Missouri bladderpod; proposed
delisting actions for the Truckee barberry; and final delisting actions
for Robbins' cinquefoil. In addition, we proposed critical habitat for
13 listed species, and finalized critical habitat for 323 listed
species. ``Expeditious progress'' is a function of the resources that
are available and the way in which those resources are used. As
discussed above, the bulk of the funds that would be otherwise
available for adding qualified species to the list in FY 2003 and FY
2004 have been spent or will be spent on complying with court orders
and court-approved settlement agreements to designate critical habitat
and make petition findings. Nonetheless, the Service has endeavored to
make its designations and other listing actions as efficient and timely
as possible, given the requirements of the relevant law, regulations,
and policy and constraints relating to workload and personnel. The
Service is continually considering ways to streamline processes or
achieving economies of scale, such as by batching related actions
together. Given our limited budget for implementing section 4 of the
Act, these achievements constitute expeditious progress.
Given the recent decision in Center for Biological Diversity v.
Badgley, 284 F. 3d 1046 (9th Cir. 2002), which held that the Act
requires that 90-day petition findings be made no later than 12 months
after receipt of the petition, regardless of whether it is practicable
to do so, we may need to make petition findings on most or all of the
outstanding petitions for those species that we have not previously
determined to warrant candidate status. If over the next year we can
devote any resources to issuing proposed rules for the highest-priority
candidates without jeopardizing our ability to comply with court
orders, court-approved settlement agreements, or unqualified statutory
deadlines, we will do so.
Work on proposed rules for candidates with lower priority (i.e.,
those that have listing priority numbers of 4-12) is also precluded by
the need to issue proposed rules for higher-priority species facing
high-magnitude, imminent threats (i.e., listing priority numbers of 1,
2, or 3). Table 1 shows the listing priority number for each candidate
species. Finally, 12-month ``warranted but precluded'' petition
findings for reclassification of threatened species to endangered are
lower priority, since the listing of the species already affords the
protection of the Act and implementing regulations.
Summary of Petitioned Candidates
Mammals
Black-tailed prairie dog (Cynomys ludovicianus)--We have not
updated our finding with regard to the black-tailed prairie dog in this
notice. In the 2002 CNOR, we found that a listing proposal for this
species was still warranted but precluded by higher priorities, and we
assigned the species a listing priority number of 8. We have since
received significant new information about this species from the
National Wildlife Federation, Forest Guardians, and the States of
Arizona, Colorado, Kansas, Montana, Nebraska, New Mexico, North Dakota,
Oklahoma, South Dakota, Texas, and Wyoming. We are considering this
information and, upon completion, we intend to publish
[[Page 24886]]
a finding for this species in the Federal Register.
Fisher, west coast DPS (Martes pennanti)--See our initial
``warranted-but-precluded'' finding signed on April 2, 2004, and
published in the Federal Register on April 8, 2004 (68 FR 18770).
Southern Idaho ground squirrel (Spermophilus brunneus endemicus)--
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 January 29, 2001.
Washington ground squirrel (Spermophilus washingtoni)--The
following summary is based on information contained in our files and
the petition received on March 2, 2000. The Washington ground squirrel
is endemic to the Columbia Plateau, south of the Columbia River and
east of the John Day River. The historical range of the species,
distributed over much of the shrub-steppe habitat of southeastern
Washington and northeastern Oregon, has been modified and reduced to
three disjunct areas. The greatest threat to the species is loss of
habitat. Habitat is destroyed through commercial, residential, and
agricultural development, and the conversion of suitable habitat to
agricultural uses is an ongoing practice. Disturbance through
activities such as tilling and irrigation of the appropriate soil types
renders the habitat unsuitable and can result in loss of occupied
colonies. The soil types used by the squirrels are distributed
sporadically within the species' range and have been seriously
fragmented by human development in the Columbia Basin, particularly
conversion to agricultural use. Where agriculture occurs, little
evidence of ground squirrel use has been documented, and reports
indicate that ongoing agricultural conversion permanently eliminates
Washington ground squirrel habitat.
Given the lack of substantial dispersal movements, isolation and
fragmentation of colonies and habitat can severely affect Washington
ground squirrels by limiting genetic exchange and reproduction,
exposing small colonies to destruction from unpredictable catastrophic
events such as fire or drought, and limiting habitat available for
escape if occupied habitat becomes unsuitable. Badgers (Taxidea taxus)
appear to be an important predator of Washington ground squirrels. Some
colonies appeared to have been eliminated by badgers on the Boeing
Tract, and badger-digging activity is common within Washington ground
squirrel colonies. In Washington, recent declines have been precipitous
and for unknown reasons. The causes of starvation, lack of
reproduction, and colony losses are unknown. Subjective observations of
habitat conditions did not appear to be substantially different from
previous years, but biologists observed that colonies with higher
survival, reproduction, and average body mass may have benefited from
presence of non-native bulbous bluegrass (Poa bulbosa), whereas non-
native cheatgrass (Bromus tectorum) predominates at colony sites with
poor reproduction, body mass, or survival.
The Service is working with the State of Oregon to pursue
cooperative agreements primarily with the Navy to conserve the species
on the Boardman Bombing Range. Three Mile Canyon Farms has recently
purchased the Boeing tract from the State of Oregon and, in
coordination with the Service, is in the process of developing a
Candidate Conservation Agreement with Assurances for this property.
Based on our current evaluation of threats, we assigned a listing
priority number of 2 to this species.
Birds
Band-rumped storm-petrel, Hawaii DPS (Oceanodroma castro)--The
following summary is based on information contained in our files and
the petition received on May 8, 1989. The band-rumped storm-petrel is a
small, widespread seabird found in the subtropics of the 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.
Estimates of the total Statewide population could exceed 100 pairs if
viable breeding populations exist on Maui and Hawaii. Although small
populations do occur on Maui and Hawaii, we have been unable to
determine if they are viable; certainly they are not large and they
represent a fraction of prehistoric distribution. Predation by
introduced species is believed to have played a significant role in
reducing storm-petrel numbers and in exterminating colonies in the
Pacific and other locations worldwide. Additionally, artificial lights
have had a significant negative effect on fledgling young and, to a
lesser degree, adults. Artificial lighting of roadways, resorts,
ballparks, residences, and other development in lower elevation areas
attracts and confuses night-flying storm-petrel fledglings, resulting
in ``fallout'' and collisions with buildings and other objects.
Currently, the species is not known to be taken or used for commercial,
recreational, scientific, or educational purposes. During 1992 surveys
on Mauna Loa, Hawaii, several caches of Hawaiian dark-rumped petrel
carcasses associated with feral cat predation were recorded in areas
where band-rumped storm-petrel vocalizations were recorded. Based on
imminent threats of a high magnitude, we assigned this Hawaii DPS of
the band-rumped storm-petrel a listing priority number of 3.
Gunnison sage-grouse (Centrocercus minimus)--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
January 25, 2000.
Lesser prairie-chicken (Tympanuchus pallidicinctus)--The following
summary is based on information contained in our files and the petition
received on October 5, 1995. Biologists estimate that the occupied
range has declined by at least 78 percent since 1963 and by 92 percent
since the 1800s. The most serious threats to the lesser prairie-chicken
are loss of habitat from conversion of native rangelands to introduced
forages and cultivation, and cumulative habitat degradation caused by
severe grazing, fire suppression, herbicides, and structural
developments. Many of these threats may exacerbate the normal effects
of periodic drought on lesser prairie-chicken populations. We view
current and continued habitat fragmentation to be a serious ongoing
threat that facilitates the extinction process through several
mechanisms: Remaining habitat patches may become smaller than necessary
to meet the yearlong requirements of individuals and populations;
necessary habitat heterogeneity may be lost to large areas of
monoculture vegetation and/or homogenous habitat structure; areas
between habitat patches may harbor high levels of predators or brood
parasites; and the probability of recolonization decreases as the
distance between suitable habitat patches expands. At present, all
States within occupied range are committing significant resources via
personnel, outreach, and habitat improvement incentives to landowners
to optimize habitat in currently occupied range and adjacent lands to
recover the species. We recognize that measurable increases in
populations often come years after certain habitat improvements occur.
However, we will continue to monitor potential effects of emerging
habitat fragmentation threats, in the form of
[[Page 24887]]
commercial wind-power facilities and extensive oil and gas exploration
and development.
We have determined that the overall magnitude of threats to the
lesser prairie-chicken throughout its range is moderate. The magnitude
of threats to lesser prairie-chickens is primarily based on the quality
and scale of existing habitat. The majority of threats to remaining
lesser prairie-chicken populations are ongoing, and thus they are
considered imminent. We will continue to monitor the effectiveness of
the current conservation efforts to stabilize and increase existing
populations throughout significant portions of the species range. Based
on all currently available information, we assigned the lesser prairie-
chicken a listing priority number of 8.
Yellow-billed cuckoo, western continental U.S. DPS (Coccyzus
americanus)--The following summary is based on information contained in
our files and the petition received on February 9, 1998. Also see our
12-month petition finding published on July 25, 2001 (66 FR 38611).
While the cuckoo is still relatively common east of the crest of the
Rocky Mountains, biologists estimate that more than 90 percent of the
bird's riparian (streamside) habitat in the West has been lost or
degraded. These modifications, and the resulting decline in the
distribution and abundance of yellow-billed cuckoos throughout the
western states, are believed to be due to conversion to agriculture;
grazing; competition from non-native plants, such as tamarisk; river
management, including altered flow and sediment regime; and flood
control practices, such as channelization and bank protection. Based on
ongoing but nonimminent threats of a high magnitude, we assigned a
listing priority number of 6 to this DPS of yellow-billed cuckoo.
Kittlitz's murrelet (Brachyramphus brevirostris)--See above in
``Summary of New Candidates.'' The above summary is based on
information in our files and the petition received on May 9, 2001.
Greater sage-grouse, Columbia Basin DPS (Centrocercus
urophasianus)--The following summary is based on information in our
files and the petition received on June 21, 1999. Currently, the AOU
recognizes two subspecies of greater sage-grouse. Compared to the
eastern subspecies (C. u. urophasianus), the western subspecies (C. u.
phaios) has reduced white markings and darker grayish-brown feathering,
resulting in a more dusky overall appearance. Based on recent
communications with recognized experts, some disagreement as to the
validity of these current subspecies designations exists. With regard
to current taxonomic standards and information generated over the last
few decades, these subspecies designations may be inappropriate. When
informed taxonomic opinion is not unanimous, the Service evaluates the
available information. The Service has conducted a detailed analysis of
available information and has determined that the subspecies
designations for greater sage-grouse are inappropriate given current
taxonomic standards (68 FR 6500, February 7, 2003). However, the
Service still considers the Columbia Basin population to be a Distinct
Population Segment. The abundance of greater sage-grouse within the
Columbia Basin DPS declined by approximately 30 percent between 2000
and 2001. Of even greater concern is the estimated reduction in size of
the larger subpopulation in Douglas and Grant Counties, Washington,
which accounted for the majority of the decline (dropping from 684 in
2000 to 395 in 2001, or approximately 42 percent). The current, overall
population estimate of roughly 700 individuals is the lowest ever
recorded for the Columbia Basin DPS, although it is just slightly lower
than the previous lowest estimate recorded in 1994. Since 1970, the
estimated population lows for the Columbia Basin DPS have occurred
``regularly'' over a 3- to 4-year period at mid-decade (e.g., 1975-78,
1985-87, and 1993-96). Should this cyclical pattern in population
abundance hold, we may expect further significant declines in the
Columbia Basin DPS over the next several years.
Military training constitutes the primary threat to the southern
subpopulation, while habitat conversion is the primary threat impacting
the northern subpopulation. However, we conclude that threats related
to military training are not imminent, based on the implementation of
the Army's conservation measures and considerably less-than-planned
training activities occurring in Yakima and Kittitas Counties. Large
areas of privately owned lands in Douglas County are currently
withdrawn from crop production and planted to native and non-native
cover under the Federal Conservation Reserve Program (CRP), established
in 1985. Lands under the CRP are very important to the northern
subpopulation of the Columbia Basin DPS. Much of the CRP acreage that
could have expired was re-enrolled and total CRP acreage increased in
1998 in Douglas County. As such, we conclude that the high-magnitude,
nonimminent threats to the Columbia Basin DPS of the greater sage
grouse, leading to the assignment of a listing priority number of 6.
Xantus's murrelet (Synthilboramphus hypoleucus)--See above in
``Summary of New Candidates.'' The above summary is based on
information in our files and the petition received on April 16, 2002.
Reptiles
Louisiana pine snake (Pituophis ruthveni)--The following summary is
based on information contained in our files and the petition received
on July 19, 2000. The Louisiana pine snake historically occurred in
portions of west-central Louisiana and extreme east-central Texas.
Louisiana pine snakes have not been documented in over a decade in some
of the best remaining habitat within their historical range. Surveys
and results of Louisiana pine snake trapping and radio-telemetry
suggest that extensive population declines and local extirpations have
occurred during the last 50 to 80 years. Most of the longleaf pine
habitat of the Louisiana pine snake has been destroyed and the quality
of remaining Louisiana pine snake habitat has been degraded due to
logging, fire suppression, short-rotation silviculture, and conversion
of habitat to other uses such as grazing. Louisiana pine snake habitat
loss is continuing, albeit at a slower rate than in the past. Also, a
comprehensive partnership that is attempting to address the species,
its status, and threats to the species and habitat has had some recent
successes. Other factors affecting Louisiana pine snakes include low
fecundity (reproductive output), which magnifies other threats and
increases the likelihood of local extinctions, and vehicular mortality,
which may cause significant impacts to the Louisiana pine snake's
population numbers and community structure. Due to nonimminent threats
of a high magnitude, we assigned a listing priority number of 5 to this
species.
Cagle's map turtle (Graptemys caglei)--The following summary is
based on information contained in our files and the petition received
on April 26, 1991. Cagle's map turtle occurs in scattered sites in
seven counties in Texas on the Guadalupe, San Marcos, and Blanco
Rivers. Loss and degradation of riverine habitat from large and/or
small impoundments (dams or reservoirs) is the primary threat to
Cagle's map turtle. One detrimental effect of impoundment is the loss
of riffle and riffle/pool transition areas
[[Page 24888]]
used by males for foraging. Depending on its size, a dam itself may be
a partial or complete barrier to Cagle's map turtle movements and could
fragment a population. Construction of smaller impoundments and human
activities on the river has likely eliminated or reduced foraging and
basking habitats. Cagle's map turtle is also vulnerable to
overcollecting and target shooting. Due to nonimminent threats of a
high magnitude, we assigned a listing priority number of 5 to this
species.
Sand dune lizard (Sceloporus arenicolus)--The following summary is
based on information in our files and the petition received on June 6,
2002. The sand dune lizard is endemic to a small area in southeastern
New Mexico (Chaves, Eddy, Lea, and Roosevelt Counties) and adjacent
west Texas (Andrews, Crane, Ward, and Winkler Counties). Within this
area, the known occupied and potentially occupied habitat is only 1,697
kilometers \2\ (655 miles \2\) in New Mexico, and an unknown amount in
west Texas. The sand dune lizard has the second-most restricted range
of any native lizard in the United States. The lizard's distribution is
localized and fragmented (i.e., known populations are separated by vast
areas of unoccupied habitat), and the species is restricted to sand
dune blowouts associated with active sand dunes with shinnery oak
(Quercus harvardii) and scattered sandsage (Artemisia filifolia). Sand
dune lizards are not found at sites lacking shinnery oak dune habitat.
Extensive surveys within New Mexico, conducted in conjunction with a 5-
year study, documented sand dune lizards at only half of the sites
surveyed. It is clear that shinnery oak removal (e.g., by treating with
herbicides), for livestock range improvements, results in dramatic
reductions and extirpation of sand dune lizards. Scientists repeatedly
confirmed the extirpation of sand dunes lizards from areas with
herbicide treatment to remove shinnery oak. Biologists estimate that
about 25 percent of the total sand dune lizard habitat in New Mexico
has been eliminated in the last 10 years. The population of sand dune
lizards has been affected by the spraying of the herbicide Tebuthiuron
to control shinnery oak, and also by oil and gas field development. An
estimated 50-percent decline in sand dune lizard populations can be
expected in areas with at least 30 oil and/or gas wells per section.
The distribution of sand dune lizards is localized and fragmented and
this species is a habitat specialist; therefore, impacts to its habitat
will most likely greatly decrease populations. If current herbicide
application continues and oil and gas development progresses as
expected, the magnitude of threat to sand dune lizards remains high.
Continued pressure to develop oil and gas resources in areas with sand
dune lizards poses an imminent threat to the species. Therefore, this
species is assigned a priority number of 2.
Amphibians
Columbia spotted frog, Great Basin DPS (Rana luteiventris)--The
following summary is based on information contained in our files and
the petition received on May 1, 1989. Currently, Columbia spotted frogs
appear to be widely distributed throughout southwestern Idaho and
eastern Oregon, but local populations within this general area appear
to be 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. Habitat degradation and
fragmentation is probably a combined result of past and current
influences of heavy livestock grazing, spring alterations, agricultural
development, urbanization, and mining activities. Fragmentation of
habitat may be one of the most significant barriers to Columbia spotted
frog recovery and population persistence. Loss of vegetation and/or
lowering of the water table as a result of the above-mentioned
activities can significantly threaten frogs moving from one area to
another. Likewise, fragmentation and loss of habitat can prevent frogs
from colonizing suitable sites elsewhere. Based on imminent threats of
high magnitude, we assigned a listing priority number of 3 to this DPS
of the Columbia spotted frog.
Oregon spotted frog (Rana pretiosa)--The following summary is based
on information contained in our files and the petition 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 threats to the species'
habitat include development, livestock grazing, introduction of non-
native plant species, changes in hydrology due to construction of dams
and alterations to seasonal flooding, and poor water quality.
Additional threats to the species are predation by non-native fish and
introduced bullfrogs. The high magnitude of threat is due to small
populations with patchy and isolated distributions; and the wide range
of threats to both individuals and their habitats. Habitat restoration
and management actions have not prevented a decline in the reproductive
rates in some populations. Each population is faced with multiple
actual and potential threats that could seriously reduce or eliminate
any of these isolated populations and further reduce the range of the
species. Based on these threats, we assigned the Oregon spotted frog a
listing priority number of 2.
Boreal toad, Southern Rocky Mountains DPS (Bufo boreas boreas)--The
following summary is based on information contained in our files and
the petition received on September 30, 1993. See also our 12-month
petition finding published on March 23, 1995 (60 FR 15281). Boreal
toads of the Southern Rocky Mountain DPS were once common throughout
much of the high elevations in Colorado, in the Snowy and Sierra Madre
Ranges of southeast Wyoming, and at three breeding localities at the
southern periphery of their range in the San Juan Mountains of New
Mexico. In the late 1980s, boreal toads were found to be absent from 83
percent of breeding localities in Colorado and 94 percent of breeding
localities in Wyoming previously known to contain toads. In 1999, the
number of known breeding localities increased from 33 to 50, with 1 in
Wyoming, none in New Mexico, and the remaining sites in Colorado. This
increase in known breeding localities, however, was likely due to
increased survey efforts rather than expansion of the population.
Land use in boreal toad habitat includes recreation, timber
harvesting, livestock grazing, and watershed alteration activities.
Though declines in toad numbers have not been directly linked to
habitat alteration, activities that destroy, modify, or curtail habitat
likely contribute to the continued decline in toad numbers. The current
and future use of water rights in the Southern Rocky Mountains may
affect boreal toads. Increased demands on limited water resources can
result in water level drops in reservoirs that toads are using.
Transferring rights from one user group to another (e.g., agricultural
to municipal) also could reduce toad habitat, particularly if
dewatering of reservoir sites resulted from these transfers. Additional
threats to the boreal toad include a chytrid fungus, which likely
caused the boreal toad to decline in the 1970s and continues to cause
declines. Despite numerous conservation actions funded and implemented
to date, additional populations or breeding localities of the
[[Page 24889]]
toad being found in the last several years, and protection of the toad
afforded by State and Federal laws, we continue to give the toad a
listing priority of 3. The chytrid fungus infection is an ongoing
threat of high magnitude and is likely to extirpate additional infected
boreal toad populations.
Yosemite toad (Bufo canorus)--The following summary is based on
information contained in our files and the petition received on April
3, 2000. See also our 12-month petition finding published on December
10, 2002 (67 FR 75834). The historical range of Yosemite toads in the
Sierra Nevada occurs from the Blue Lakes region north of Ebbetts Pass
to 5 kilometers (km) (3.1 miles (mi)) south of Kaiser Pass in the
Evolution Lake/Darwin Canyon area. Alteration and loss of habitat due
to grazing, timber management, water diversion, recreation, and
vegetative/fire management are threats. The decline of some populations
of Yosemite toad has been attributed to the effects of poorly managed
livestock grazing. The levels of timber harvest and road construction
have declined substantially since implementation of the California
Spotted Owl Sierran Province Interim Guidelines in 1993, and some
existing roads have been, or are scheduled for, decommissioning.
Therefore, the risks posed by new roads and timber harvests have
declined, but those already existing still pose risks to the species
and its habitat through erosion, roadkill, and contaminant
introduction. Reservoirs represent both a loss of habitat and a barrier
to dispersal and gene flow. In addition, the evidence of an adverse
physiologic effect of pesticides on Sierra Nevada amphibians in the
field indicates that contaminants may be a risk to the Yosemite toad
and may have contributed to the species' decline. These factors have
probably contributed to the decline of Yosemite toads and continue to
pose a risk to the species. We determined the magnitude of threats to
be moderate, rather than high, because almost all of the species' range
occurs on Federal land, which facilitates management of the species by
Federal agencies. We determined the threats to the Yosemite toad to be
nonimminent. Therefore, we assign the Yosemite toad a listing priority
number of 11.
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). The
mountain yellow-legged frog is restricted to two disjunct areas in
California and a portion of Nevada. One area is in the Sierra Nevada
and the other area is in southern California (Los Angeles, San
Bernardino, Riverside, and San Diego counties). The southern California
population is isolated from the Sierra Nevada population by the
Tehachapi mountain range, with a distance of about 225 kilometers (km)
(140 miles (mi)) between the two populations. The 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 in national forests and national
parks. Rangewide, it is estimated that the number of mountain yellow-
legged frog populations have undergone a 50- to 80- percent reduction.
Direct predation by non-native fishes has resulted in rangewide
population declines and local extirpations.
Furthermore, the result of these extirpations is that the remaining
populations are fragmented and isolated, making them vulnerable to
further declines and local extirpations caused by other factors such as
disease. For example, in reviewing documented mountain yellow-legged
frog declines over the last 5 years in Sequoia and Kings National
Parks, we found the frog suffered a 39-percent extinction rate of the
frog where fish have not been stocked since the late 1970s. In
comparison, over the last 7 years, in the Sierra National Forest's John
Muir Wilderness Area there has been a 61-percent extinction rate where
fish stocking has continued. The rate of extinction observed by Knapp
over a 5- to 7-year time frame suggests the species' extinction within
a few decades (assuming that the rate of extinction and recolonization
observed over this time period accurately reflects the long-term
rates). It is likely that disease, specifically chytrid fungus, has
caused these recently observed declines. Although the life history and
modes of transmission of chytrid fungus are not well understood, it
appears that this pathogen is widespread throughout the range of the
mountain yellow-legged frog within the Sierra Nevada, it is persistent
in ecosystems, and it is resilient to environmental conditions such as
drought and freezing. Therefore, we conclude that all remaining
mountain yellow-legged frog populations within the Sierra Nevada are at
risk to declines and extirpation as a result of infection by this
pathogen. The overall magnitude and immediacy of threats to the Sierra
Nevada distinct population segment of the mountain yellow-legged frog
is high. Therefore, we assigned this species a listing priority of 3.
Relict leopard frog (Rana onca)--The following summary is based on
information contained in our files and the petition 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. The Service estimates that the current
distribution is less than 20 percent of the historical distribution. As
habitat generalists, relict leopard frogs historically likely occupied
a variety of habitats including springs, streams, and wetlands
characterized by clean, clear water, in both deep and shallow water,
and cover/forage such as submerged, emergent, and perimeter vegetation.
The causes for the population declines of this species are not entirely
clear, but suggested factors include alteration of aquatic habitat due
to agriculture and water development, and the introduction of exotic
predators and competitors. The magnitude of threats to the relict
leopard frog are high based on its limited numbers and distribution,
the presence of non-native predators, potential alteration of remaining
habitat including groundwater pumping, and diversion of surface water.
We do not consider threats to be imminent at this time. Although the
numbers are low and distribution is limited, efforts are underway to
improve habitat and increase numbers through captive rearing and
translocation. There are no proposed projects that may result in
further habitat degradation. Therefore, we assigned the relict leopard
frog a listing priority number of 5.
Fishes
Fluvial arctic grayling, upper Missouri River DPS (Thymallus
arcticus)--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 2, 1992. See also our
12-month petition finding published on July 25, 1994 (59 FR 37738).
Snails
Chupadera springsnail (Pyrgulopsis chupaderae)--The following
summary is based on information contained in our files and the petition
received on November 20, 1985. See also our 12-month petition finding
published on October 4, 1988 (53 FR 38969). This aquatic species is
endemic to Willow Spring on the Willow Spring Ranch
[[Page 24890]]
(formerly Cienega Ranch) at the south end of the Chupadera Mountains in
Socorro County, New Mexico. The Chupadera springsnail has been
documented from two hillside groundwater discharges that flow through
grazed areas among rhyolitic gravels containing sand, mud, and
hydrophytic plants. Regional and local groundwater depletion, springrun
dewatering, and riparian habitat degradation represent the principal
threats. The survival and recovery of the Chupadera springsnail is
contingent upon protection of the riparian corridor immediately
adjacent to Willow Spring and the availability of perennial, oxygenated
flowing water within the species' thermal range. Several factors--the
extremely localized distribution of the snail, its occurrence only on
private property, the lack of regulatory protection of its habitat, and
the inability of land managers to participate in its management--
indicate that the magnitude of threat to this species is high. Either
human-caused disturbance (grazing of cattle, water withdrawal) or
natural disturbance (drought or fire) could eliminate this species.
Therefore, there is an immediate threat to this species and we assigned
this species a listing priority number of 2.
Gila springsnail (Pyrgulopsis gilae)--The following summary is
based on information contained in our files and the petition received
on November 20, 1985. Also see our 12-month petition finding published
on October 4, 1988 (53 FR 38969). The Gila springsnail is an aquatic
species known from 13 populations in New Mexico. The long-term
persistence of the Gila springsnail is contingent upon protection of
the riparian corridor immediately adjacent to springhead and springrun
habitats, thereby ensuring the maintenance of perennial, oxygenated
flowing water within the species' required thermal range. Sites on both
private and Federal lands are subject to uncontrolled recreational use
and livestock grazing, 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 and retardant chemicals have potentially deleterious
effects on this species. Because several of the springs occur on Forest
Service land, management options for the protection of the snail should
be possible. However, stochastic events, especially fire and drought,
could have a major impact on the species. Moderate use by
recreationalists and livestock is ongoing. If use by these groups
remains at current or lower levels, it will not pose an imminent threat
to the species. Of greater concern is the current drought that could
impact spring discharge and increases the potential for fire.
Catastrophic fires have occurred in the Gila National Forest, and
subsequent floods and ash flows have decimated aquatic life in streams.
If the drought continues or worsens, the imminence of threat (decreased
discharge, fire) will increase. Based on these nonimminent threats of a
low magnitude, we assigned a listing priority number of 11 to this
species.
New Mexico springsnail (Pyrgulopsis thermalis)--The following
summary is based on information contained in our files and the petition
received on November 20, 1985. Also see our 12-month petition finding
published on October 4, 1988 (53 FR 38969). The New Mexico springsnail
is an aquatic species known from only two separate populations
associated with a series of spring-brook systems along the Gila River
in the Gila National Forest in Grant County, New Mexico. The long-term
persistence of the New Mexico springsnail is contingent upon protection
of the riparian corridor immediately adjacent to springhead and
springrun habitats, thereby ensuring the maintenance of perennial,
oxygenated flowing water within the species-required thermal range.
While the New Mexico springsnail populations may be stable, the sites
inhabited by the species are subject to uncontrolled recreational use
and livestock grazing. Wetland habitat degradation via recreational use
and overgrazing in or near the thermal springs and/or poor watershed
management practices represent the primary threats to the New Mexico
springsnail. Moderate use by recreationalists and livestock is ongoing.
If use by these groups remains at the current or lower levels, it will
not pose an imminent threat to the species. Of greater concern is the
current drought, which could impact spring discharge and increases the
potential for fire. Catastrophic fires have occurred in the Gila
National Forest and subsequent floods and ash flows have decimated
aquatic life in streams. If the drought continues or worsens, the
imminence of threat (decreased discharge, fire) will increase. Based on
these nonimminent threats of a low magnitude, we assigned this species
a listing priority number of 11.
Page springsnail (Pyrgulopsis morrisoni)--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 April
12, 2002.
Insects
Coral Pink Sand Dunes tiger beetle (Cicindela limbata albissima)--
The following summary is based on information contained in our files,
including information from the petition received on April 21, 1994. The
Coral Pink Sand Dunes tiger beetle is known to occur only at Coral Pink
Sand Dunes, about 7 miles west of Kanab, Kane County, in south-central
Utah. It is restricted mostly to a small part of the approximately 13-
kilometer (8-mile) long 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 (ORV) use. The ORV activity is
destroying and degrading the beetle's habitat, especially the
interdunal swales used by the larval population. Having the greatest
abundance of suitable prey species, the interdunal swales are the most
biologically productive areas in this ecosystem. The continued survival
of the beetle depends on the preservation of its habitat at its only
breeding site and probably requires the establishment or
reestablishment of additional reproductive subpopulations in other
suitable habitat sites. The beetle's population is also vulnerable to
overcollecting by professional and hobby tiger beetle collectors,
although quantification of this threat is difficult without continuous
monitoring of the beetle's population. The recreational ORV use threat
is currently managed by active measures taken by both the Utah
Department of Parks and Recreation and the BLM, which reduces the
threat from high to moderate. The subspecies population is still at low
levels and has only recently improved. Based on imminent threats of a
low to moderate magnitude, we assigned this subspecies a listing
priority number of 9.
Wekiu bug (Nysius wekiuicola)--The following summary is based on
information contained in our files, including information from the
petition received on May 22, 2003. The wekiu bug, first discovered in
1979 on the summit cinder cone of Mauna Kea on the island of Hawaii, is
a flightless insect in the seed bug family. This species is only found
on Mauna Kea and is believed to inhabit sites no lower than
approximately 3,658 meters in elevation. Threats to this species
include past and potential habitat destruction from building and
updating of facilities for astronomical study. Resultant impacts have
included road
[[Page 24891]]
construction, parking areas, tourist facilities, temporary storage
areas, substrate removal, and oil spills, and constant traffic to the
summit with the concomitant human dispersal of trash and debris; more
than two thirds of the wekiu's potential range is unprotected from
astronomical development. In addition, introductions of alien
arthropods and parasites may also negatively affect this species. For
example, the wekiu bug now competes with at least one introduced
species of Linyphiidae (small sheetweb) spiders which have become
established on the summit.
The summit area where wekiu bug habitat occurs lies within a State
conservation district and any construction in the area requires a
permit from the State Department of Land and Natural Resources (DLNR).
Prior to development of the Mauna Kea Science Reserve, a development
plan for the summit area was written that addressed the sensitivity of
the wekiu bug and its habitat. Despite the fact that important wekiu
bug habitat was identified as sensitive in the 1983 plan and was to be
avoided in the development of the facilities, a lack of communication
and insufficient monitoring of construction activities at the summit
during construction of the Subaru telescope facility resulted in the
loss of most wekiu bug habitat in Puu Hau Oki. Currently, the Institute
for Astronomy is developing a new Mauna Kea Science Reserve master plan
and is funding a series of surveys to determine how the impact of
future development might impact the flora and fauna (particularly the
wekiu bug) of the summit area. Under the current management plan, the
number of telescopes is limited to 13. However, old facilities could be
torn down and replaced with submillimeter arrays which can have up to
20 times the surface impact of construction of a standard telescope and
still count as one telescope. Furthermore, development of
interferometers on Mauna Kea may continue under the current management
plan since they do not count as ``telescopes.'' Interferometers are
specialized antennae for observing astronomical occurrences, and the
resulting structure impacts at least as much surface area as a large
telescope. Based on imminent threats of a high magnitude, we assigned
this species a listing priority number of 2.
Whulge checkerspot butterfly (Euphydrayas editha taylori)--The
following summary is based on information contained in our files and
the petition received on December 24, 2002. Whulge checkerspots are
small, colorfully checkered butterflies that, historically, were known
from more than 70 locations: 23 in British Columbia, 34 in Washington,
and 13 in Oregon. In Fall 2002, only five populations were known; four
are located in the south Puget Sound region and one is in the
Willamette Valley. Surveys in 2001 and 2002 of the three known British
Columbia sites failed to locate any Whulge checkerspots. Whulge
checkerspots are threatened by changes in the vegetation structure and
composition of native grassland-dominated plant communities. Native
grassland communities have been lost to conversion for agriculture and
development for residential and commercial purposes. Threats to
grassland vegetation also threaten habitat for the Whulge checkerspot.
Habitat has been degraded and encroached on by nonnative woody shrubs,
including Scot's broom (Cytisus scoparius) and several species
identified by Washington State as noxious weeds, such as leafy spurge
(Euphorbia esula) and knapweed (Centaurium). As grasslands have been
converted, the availability of host plants for feeding and nectaring by
larvae and adults has declined. The application of Bacillus
thuringiensis var kurstaki (Btk) for control of the Asian gypsy moth
(Lymantria dispar) likely contributed to the extirpation of three
historic locales for this subspecies in Pierce County. Spraying of Btk
is known to have adverse affects to nontarget lepidopteran species
(butterflies and moths). The Whulge checkerspot was designated a
candidate species by Washington State in 1991. However, candidate
status within Washington State has no protective measures associated
with it. No protection or restrictions on direct take is provided to
these butterflies on any lands administered by any city, county, State
or Federal agencies. Because of the extremely small size of remaining
populations and the reduction in distribution of the species from its
former range, there is the potential for one episode of any of several
potential threats to occur at any time (e.g., a single period of severe
weather at a critical life stage of the Whulge checkerspot) that could
eliminate the entire subspecies. Therefore, due to imminent threats of
a high magnitude, we assigned this subspecies a listing priority number
of 3.
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 appears
to have been extirpated from Iowa and Illinois, as well as many sites
within States with extant locations. The species is threatened by the
large-scale conversion of native prairie to agricultural purposes, as
well as fire management, grazing, plant invasion, and fragmentation of
habitat leading to local extirpations. Although the species is listed
as threatened by the State of Minnesota, this designation lacks the
habitat protections needed for long-term conservation. The species is
listed as endangered by the province of Manitoba. However, the
protections in Manitoba are not sufficient to remove the threats to the
species. Due to efforts that have been made to preserve habitat through
conservation easements at some of the known locations, the threats to
the species are low to moderate and nonimminent. Therefore, we assigned
a listing priority number of 11 to the species.
Mardon skipper (Polites mardon)--The following summary is based on
information contained in our files and the petition received on
December 24, 2002. The Mardon skipper (Polites mardon) is a small,
nonmigratory butterfly species and is currently known from four widely
separated locations: the southern Puget Trough region, the southern
Washington Cascades, the Siskiyou Mountains in southern Oregon, and
coastal northern California. In Washington, the historic range and
abundance of Mardon skippers is not known, and there are no known
estimates of abundance prior to 1980, but Mardon skippers are
apparently extirpated from five historic sites (four in the Puget
Prairie and one in the South Cascades). Oregon populations occupy small
(less than 0.25-4 ha (0.5-10 ac)) high-elevation (1,372-1,555 m (4,500-
5,100 ft)) grassy meadows within mixed conifer forests. The California
population is located on a serpentine bald dominated by Festuca spp.
Mardon skippers were present at the California site in 1997, but there
were no surveys in 1998. In good years, dozens of individuals are found
in the 0.4 to 0.8 ha (1 to 2 ac) core area and along a ridge for 3-5 km
(2-3 mi). Because the Mardon skipper is nonmigratory, and thus
relatively sedentary, maintaining occupied habitat quality is
essential. Threats to the Mardon skipper include any factor that
degrades its obligate grassland habitats, including
[[Page 24892]]
development, overgrazing, herbicides, the encroachment of invasive
nonnative and native vegetation, and succession from grassland to
forest. Prairies, which once covered hundreds of thousands of acres of
the southern Puget Sound region prior to settlement, have been lost to
development, fire suppression, and invasion by native and nonnative
plant species. Today, less than 3 percent of the original prairie
landscape remains, and much of this has competing human uses.
Additionally, insect collecting is a potential threat since rare
butterflies, such as the Mardon skipper, are desirable to collectors,
and most skipper populations are small and easily accessible. Because
of the small size of all populations and their disjunct distribution,
loss of any population could lead to extirpation of the species at any
of these locations. Based on nonimminent threats of a high magnitude,
we assigned this species a listing priority number of 5.
Flowering Plants
Christ's paintbrush (Castilleja christii)--The following summary is
based on information contained in our files and the petition received
on January 2, 2001. Christ's paintbrush is endemic to subalpine meadow
and sagebrush habitats in the upper elevations of the Albion Mountains,
Cassia County, Idaho. The single population of this species, which
covers only 81 ha (200 ac), is restricted to the summit of Mount
Harrison. The population appears to be stable, although the species is
threatened by a variety of activities, including unauthorized ORV use
that results in erosion of the plant's habitat and mortality of
individual plants. Livestock grazing can adversely affect Christ's
paintbrush by allowing trampling and consuming of plants, which results
in reduced reproductive success. In addition, road maintenance
activities and trampling by hikers potentially affect this species.
Most threats involve seasonal impacts from off-road travel and
occasional livestock trespass. The Forest Service is proposing to
construct additional fencing that, when completed, would eliminate the
threat of seasonal livestock trespass impacts for most of the Mt.
Harrison summit area. The Forest Service is also adding more rock
barriers along the unpaved road through Christ's paintbrush habitat to
further discourage off-road vehicle use. Because the nonimminent
threats are of a low to moderate magnitude, we assigned this species a
listing priority number of 11.
San Fernando Valley spineflower (Chorizanthe parryi var.
fernandina)--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 December 14, 1999.
Graham beardtongue (Penstemon grahamii)--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
8, 2002.
White River beardtongue (Penstemon scariosus albifluvis)--The
following summary is based on information contained in our files and
the petition 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 three known populations. 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 ORV use, and road, pipeline, and well-
site construction in connection with oil and gas development. With such
a small population and limited occupied habitat, any destruction,
modification, or curtailment of the habitat could have a highly
negative impact on the species. Additionally, the species is heavily
grazed by wildlife and livestock and is vulnerable to livestock
trampling. Based on current information, we are retaining the listing
priority number of 6.
Lemmon fleabane (Erigeron lemmonii)--The following summary is based
on information contained in our files and the petition received in July
1975. The species is now known only from one site on the Fort Huachuca
Military Reservation of southeastern Arizona. Approximately 70
individuals are at this site. The single largest threat to the species
is from catastrophic wildfire in the canyon where the plant occurs. An
intense wildfire in the narrow canyon would almost certainly desiccate
plants on the cliff face, possibly directly killing individuals or
stressing plants thereby leading to lower reproductive output. Ft.
Huachuca is willing to develop a conservation agreement for this
species. Measures have been taken to reduce the threat of wildfire and
also the threats from recreational rappelling, which is not allowed on
the cliff faces occupied by the plant. Therefore, due to the
nonimminent threats of high magnitude, we assigned this species a
listing priority number of 5.
Guadalupe fescue (Festuca ligulata)--The following summary is based
on information contained in our files and the petition received in July
1975. The only known U. S. population (which has fluctuated from 51 to
several hundred individuals), is in Big Bend National Park (BBNP).
Historically, this fescue was reported in the Guadalupe Mountains as
well. There are also two historical records and two known extant
populations in Coahuila, Mexico. In both Mexico and the U.S., plants
are found scattered in patches in the dense understory of pine-oak-
juniper woodlands around 5,000 ft. The status of the two populations in
Mexico, which occur on private land, is unknown. There is a 1998
conservation agreement between BBNP and the Service, but this does not
remove the need to consider listing. Over a 10-year period, 1993-2002,
monitoring data have revealed that numbers have steadily declined at
BBNP. In both the U. S. and Mexico, individuals are uncommon. Even
though there is only one U. S. population, it does occur on protected
National Park land, hence the magnitude has been considered moderate to
low. We will be assessing the threat posed by fire, as there is
uncertainty whether it is a fire-dependent plant species. Due to the
nonimminent threats of moderate magnitude, we assigned this species a
listing priority number of 11.
Parish's checkerbloom (Sidalcea hickmanii ssp. parishii)--The
following summary is based on information contained in our files and
the petition received in 1975. Parish's checkerbloom is known from
three counties in southern California. The only San Bernardino County
location is within a 2-hour drive of 14 million people and is popular
with recreationalists. No more than a dozen plants have been found at
this location in the last decade. Recreational use and development in
San Bernardino National Forest and adjacent private inholdings
continues in a manner that is likely to preclude the opportunity to
preserve existing plants and conduct prescribed burns to promote the
persistence of this species. The populations in Santa Barbara and San
Luis Obispo Counties are more remote from developed recreational areas.
In these locations, opportunities still exist to conduct prescribed
burns in a manner that would promote the persistence of this species.
Because this portion of the species' range is exposed to less severe
threats, we conclude that the magnitude of threat is moderate to low.
However, we conclude these pose an imminent threat to this species in
the
[[Page 24893]]
southernmost portion of its range. Therefore, we assigned this species
a listing priority number of 9.
Acuna cactus (Echinomastus erectrocentrus var. acunensis)--The
following summary is based on information contained in our files and
the petition received on October 30, 2002. This cactus is known only
from six sites on well-drained gravel ridges and knolls on granite
soils in Sonoran Desert scrub association at 1300-2000 feet elevation.
Habitat destruction has been and will continue to be a threat to this
cactus. New roads and other illegal activities have not yet directly
affected the populations at Organ Pipe Cactus National Monument
(OPCNM), but areas very close to known populations have been altered.
Populations that exist in the Florence area have not been monitored,
but the area is experiencing urban growth and populations may be in
danger of habitat loss. Urban development, in the Ajo, Arizona, area as
well as in Sonoyta, Mexico, will continue to be a significant threat to
this species. Populations of the Acuna cactus on OPCNM have shown a 50
percent mortality rate in recent years. The reason(s) for the mortality
are not known, but continuing drought conditions are thought to play a
role. Arizona Plant Law and the Convention on International Trade in
Endangered Species of Wild Fauna and Flora protect this cactus.
However, illegal collection is a primary threat to this cactus variety,
as has been documented on OPCNM. Due to the nonimminent threats of high
magnitude, we assigned this species a listing priority number of 6.
Orcutt's hazardia (Hazardia orcuttii)--See above in ``Summary of
New Candidates.'' The above summary is based on information contained
in our files and the petition received on March 8, 2001.
Tahoe yellow cress (Rorippa subumbellata)--The following summary is
based on information contained in our files and the petition 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.
Based on presence/absence information, it has been determined that the
Tahoe yellow cress has been extirpated from 10 of 52 historical
locations. Data collected over the last 24 years suggest a relationship
between lake level and site occupancy by Tahoe yellow cress. The data
generally indicate that species occurrence fluctuates yearly as a
function of both lake level and the amount of exposed habitat. Records
kept since 1900 indicate preponderance of years with high lake levels
that would 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. In addition, there has been widespread and intensive use
of the shore zone since European settlement. Today, use of the
shoreline is from heavy recreational use, boating, construction of
piers and boat launches, and dam operations that change the lake
elevation. In 1993, a low-water year when lake elevation averaged 1,897
m (6,223 ft), plants numbering in the thousands were documented at 35
general locations, the largest number of occurrences ever documented in
one year, until 2002. Subsequent years saw higher lake levels and the
number of occupied sites declined, apparently due in part to habitat
inundation. Factors other than inundation played a part in the decline,
because populations were also absent from some higher elevation sites
that were not inundated.
Most of the remaining 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. Both
the U.S. Forest Service and California Department of Parks and
Recreation have management programs for Tahoe yellow cress that include
monitoring, fenced exclosures, 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 completed conservation strategy contains
goals and objectives for the strategy, a research and monitoring
agenda, and will serve as the foundation for an adaptive management
program. Efforts to minimize or eliminate impacts to this species and
its habitat are ongoing; however, at this time, there is no evidence to
suggest that the threats to the species have been adequately addressed.
Despite the relatively high number of populations observed during the
2001 and 2002 surveys, the increasing and intense recreational use and
further development of the shore zone at Lake Tahoe are current, high-
magnitude threats; therefore, the Service is maintaining the current
LPN of 2 for the Tahoe yellow cress.
Siskiyou mariposa lily (Calochortus persistens)--The following
summary is based on information contained in our files and the petition
received on September 10, 2001. Siskiyou mariposa lily is a narrow
endemic that is restricted to two disjunct ridge tops in the Klamath-
Siskiyou Range on the California-Oregon border. In California, this
species is currently found at 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. In 2002, four Siskiyou mariposa
lily plants at the Oregon site were located. These are the first plants
reported from that area since the population was discovered in 1998.
Major threats include fire suppression resulting in shading;
competition by native and non-native species; increased fuel loading;
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 and exotic weed and grass species introduction as
a result of heavy recreational use. Dyer's woad (Isatis tinctoria), a
plant thought to prevent Siskiyou mariposa lily seedling establishment,
is now found throughout the California population, affecting 90 percent
of the known lily habitat. 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.
Unpublished data show that there has been no successful
reproduction of Siskiyou mariposa lily in the last 5 years. The
combination of restricted range, apparent loss of one of two disjunct
populations, poor competitive ability, short seed dispersal distance,
slow growth rates, extremely low or absent seed production, and
competition from exotic plants threaten the continued existence of this
species. Due to imminent threats of a high magnitude, we assigned a
listing priority number of 2 to this species.
Ferns and Allies
Slender moonwort (Botrychium lineare)--The following summary is
based on information contained in our files and the petition received
on July 28, 1999. See also the 12-month petition finding published on
June 6, 2002 (67 FR 39035). The slender moonwort is currently known
from a total of 12 widely disjunct populations in six states: three in
Colorado (El Paso and Lake Counties), one in Idaho (Custer County), two
in Oregon (Wallowa County), three in Montana (Glacier County), two in
Nevada (Clark County) and one in Washington (Ferry County). Historic
populations, previously known from Idaho (Boundary County),
[[Page 24894]]
Montana (Lake County), California (Fresno County), Colorado (Boulder
County), and Canada (Quebec and New Brunswick), have not been seen for
several years and may be extirpated. The total number of individuals
observed at the 12 extant population sites varies, with observations
ranging from 2 to 162 individuals. Identifiable threats to various
populations of this species include road maintenance, herbicide
application, recreation, timber harvest, trampling, and development.
The slender moonwort may also be affected by grazing from livestock or
wildlife, but specific effects of grazing on the species are unknown.
However, if grazing by livestock or wildlife species occurs prior to
the maturation and release of spores, the capacity for sexual
reproduction of affected plants may be compromised.
The slender moonwort is considered a sensitive species in Regions
2, 5, and 6 of the U. S. Forest Service, which include extant and
historical slender moonwort sites found in Colorado, Oregon,
Washington, and California. Regional sensitive species lists fall under
Forest Service regulations that address protection of sensitive
species. Forest Service Regions 1 and 4, which include extant and
historical sites found in Montana and Idaho, do not have slender
moonwort on their regional sensitive species lists and it is,
therefore, not given any special consideration. Although the slender
moonwort is considered to be rare and imperiled by the State Natural
Heritage Programs in Colorado, Montana, Oregon, and Washington, the
State Natural Heritage Program rankings are not legal designations and
do not confer State regulatory protection to this species. Because we
concluded that the overall magnitude of threats to the slender moonwort
throughout its range is moderate and the overall immediacy of these
threats is non-imminent, we assigned this species a listing priority
number of 11.
Petitions To Reclassify Species Already Listed
We have also previously made ``warranted but precluded'' findings
on five petitions that sought to reclassify threatened species to
endangered status. Because these species are already listed, they are
not technically candidates for listing and are not included in Table 1.
However, this notice and associated assessment forms also constitutes
the resubmitted petition findings for these species. We find that
reclassification to endangered status for the species listed below is
currently warranted but precluded by work identified above (see
``Petition for a Candidate Species'' above). In addition, these species
are currently listed as threatened under the Act and therefore receive
protection 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., 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 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.
(1) North Cascades ecosystem DPS of the grizzly bear (Ursus arctos
horribilis) (Region 6) (see 63 FR 30453, June 4, 1998, and the
candidate form (see ADDRESSES) for a discussion on why reclassification
is warranted);
(2) Cabinet-Yaak DPS of the grizzly bear (Region 6) (see 64 FR
26725, May 17, 1999, and the candidate form (see ADDRESSES) for a
discussion on why reclassification is warranted);
(3) Selkirk grizzly DPS of the grizzly bear (Region 6) (see 64 FR
26725, May 17, 1999, and the candidate form (see ADDRESSES) for a
discussion on why reclassification is warranted);
(4) Spikedace (Meda fulgida) (Region 2) (see 59 FR 35303, July 11,
1994, and the candidate form (see ADDRESSES) for a discussion on why
reclassification is warranted); and
(5) Loach minnow (Tiaroga cobitis) (Region 2) (see 59 FR 35303,
July 11, 1994, and the candidate form (see ADDRESSES) for a discussion
on why reclassification is warranted).
Current Notice of Review
We gather data on plants and animals native to the United States
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 species include species and subspecies of fish,
wildlife, or plants and distinct population segments (DPSs) of
vertebrate animals. In issuing this compilation, we rely 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 are arranged list animals alphabetically by common
names under the major group headings, then 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: flowering plants and 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 species that we regard as candidates for listing
and all species proposed for listing under the Act. We emphasize that
we are not proposing these candidate species for listing by this
notice, but we anticipate developing and publishing 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.
Species in Table 1 of this notice are assigned to several status
categories, noted in the ``category'' column at the left side of the
table. We explain the codes for the Table 1 category status column of
species below:
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, exclusive of
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-
[[Page 24895]]
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). We
identify the species for which we are not making a ``warranted-but-
precluded'' finding on a resubmitted petition by the code ``C+'' in the
category column. We have not updated our finding with regard to these
species since we have received important new information that we are
currently analyzing.
The column labeled ``Priority'' indicates the listing priority
number (LPN) for each candidate species. We use LPNs to determine the
most appropriate use of our available resources, with the lowest
numbers having 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 comments or questions (see addresses at the
end of the SUPPLEMENTARY INFORMATION section). We provided the comments
received in response to the 2002 CNOR to the Region having lead
responsibility for each candidate species mentioned in the comment. 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).
Comments received will become part of the administrative record for the
species, which is maintained at the appropriate Regional Office.
Following the scientific name (fourth column) and the family
designation (fifth column) is the common name (sixth column). The
seventh column provides the known historical range for the species or
vertebrate population (for vertebrate populations, this is the
historical range for the entire species or subspecies and not just the
historical 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 species we included either as
proposed species or as candidates in the 2002 CNOR. Since the 2002
CNOR, we added 14 of these species to the Lists of Endangered and
Threatened Wildlife and Plants, we removed the 1 species from candidate
status, and we withdrew 4 proposed rules to list for the reasons as
indicated by the codes. The first column indicates the present status
of the 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. The reduction in threats could be due, in
part or entirely, to actions taken under a conservation agreement.
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.
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;
(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;
(8) Noting any mistakes, such as errors in the indicated historical
ranges.
Submit your 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. California, Hawaii, Idaho, Nevada, 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, Oregon 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, New Mexico 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
Snellling, Minnesota 55111-4056 (612/13-5334).
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, Georgia
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, Massachusetts 01035-9589 (413/253-615).
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,
Colorado 80225-0486 (303/236-7400).
Region 7. Alaska. Regional Director (TE), U.S. Fish and Wildlife
Service, 1011 East Tudor Road, Anchorage, Alaska 99503-6199 (907/786-
3505).
Our practice is to make comments, including names and home
addresses of respondents, available for public inspection. Individual
respondents may
[[Page 24896]]
request that we withhold their home address from the public record,
which we will honor to the extent allowable by law. In some
circumstances, we can also withhold from the public record a
respondent's identity, as allowable by law. If you wish for us to
withhold your name and/or address, you must state this request
prominently at the beginning of your comments. However, we will not
consider anonymous comments. We will make all submissions from
organizations or businesses, and from individuals identifying
themselves as representatives or officials of organizations or
businesses, available for public inspection in their entirety.
Authority
This document is published under the authority of the Endangered
Species Act (16 U.S.C. 1531 et seq.).
Dated: April 19, 2004.
Steve Williams,
Director, Fish and Wildlife Service. ,
Table 1.--Candidate Notice of Review
[Animals and plants]
----------------------------------------------------------------------------------------------------------------
Status
------------------------------ Lead region Scientific name Family Common name Historic range
Category Priority
----------------------------------------------------------------------------------------------------------------
Mammals
PT............... 3 R1 Pteropus Pteropodidae... Bat, Mariana Western Pacific
mariannus fruit Ocean, U.S.A.
mariannus. (=Mariana (GU, MP).
flying fox)
(Aguijan,
etc.).
C................ 3 R1 Emballonura Emballonuridae. Bat, sheath- U.S.A. (MP,
semicaudata tailed. GU).
rotensis.
C................ 3 R1 Emballonura Emballonuridae. Bat, sheath- U.S.A. (AS).
semicaudata tailed
semicaudata. (American
Samoa DPS).
C*............... 6 R1 Martes pennanti Mustelidae..... Fisher, (west U.S.A. (CA, OR,
coast DPS). WA).
PT............... 3 R7 Enhydra lutris Mustelidae..... Otter, Northern U.S.A. (AK).
kenyoni. Sea (southwest
Alaska DPS).
C................ 6 R1 Thomomys mazama Geomyidae...... Pocket gopher, U.S.A. (WA).
Mazama.
C+............... 11 R6 Cynomys Sciuridae...... Prairie dog, U.S.A. (AZ, CO,
ludovicianus. black-tailed. KS, MT, NE,
NM, ND, OK,
SD, TX, WY),
Canada,
Mexico.
C................ 6 R1 Spermophilus Sciuridae...... Squirrel, U.S.A. (CA).
tereticaudus Coachella
chlorus. Valley round-
tailed ground.
C*............... 6 R1 Spermophilus Sciuridae...... Squirrel, U.S.A. (ID).
brunneus Southern Idaho
endemicus. ground.
C*............... 2 R1 Spermophilus Sciuridae...... Squirrel, U.S.A. (WA,
washingtoni. Washington OR).
ground.
Birds
C................ 6 R1 Porzana Rallidae....... Crake, spotless U.S.A. (AS),
tabuensis. (American Fiji,
Samoa pop.). Marquesas,
Polynesia,
Philippines,
Australia,
Society
Islands,
Tonga, Western
Samoa.
C................ 5 R1 Oreomystis Fringillidae... Creeper, Kauai. U.S.A. (HI).
bairdi.
C*............... 6 R1 Coccyzus Cuculidae...... Cuckoo, yellow- U.S.A. (AZ, CA,
americanus. billed CO, ID, MT,
(Western U.S. NM, NV, OR,
DPS). TX, UT, WA,
WY), Canada,
Mexico,
Central and
South America.
C................ 6 R1 Gallicolumba Columbidae..... Dove, friendly U.S.A. (AS),
stairi. ground Fiji, Tonga,
(American Western Samoa.
Samoa DPS).
C................ 6 R1 Ptilinopus Columbidae..... Dove, many- U.S.A. (AS).
perousii colored fruit.
perousii.
C*............... 2 R6 Centrocercus Phasianidae.... Grouse, U.S.A (AZ, CO,
minimus. Gunnison sage. KS, OK, NM,
UT).
C*............... 6 R1 Centrocercus Phasianidae.... Grouse, greater U.S.A. (OR,
urophasianus. sage (Columbia WA), Canada
basin DPS). (BC).
C................ 6 R1 Eremophila Alaudidae...... Horned lark, U.S.A. (OR,
alpestris streaked. WA), Canada
strigata. (BC).
C*............... 5 R7 Brachyramphus Alcidae........ Murrelet, U.S.A. (AK),
brevirostris. Kittlitz's. Russia.
C*............... 5 R1 Synthilboramphu Alcidae........ Murrelet, U.S.A. (CA),
s hypoleucus. Xantus's. Mexico.
[[Page 24897]]
C*............... 8 R2 Tympanuchus Phasianidae.... Prairie- U.S.A. (CO, KA,
pallidicinctus. chicken, NM, OK, TX).
lesser.
C*............... 3 R1 Oceanodroma Hydrobatidae... Storm-petrel, U.S.A. (HI).
castro. band-rumped
(Hawaii DPS).
C................ 5 R4 Dendroica Emberizidae.... Warbler, elfin U.S.A. (PR).
angelae. woods.
PE............... 6 R1 Zosterops Zosteropidae... White-eye, Rota U.S.A. (MP).
rotensis. bridled.
Reptiles
C*............... 2 R2 Sceloporus Iguanidae...... Lizard, sand U.S.A. (TX,
arenicolus. dune. NM).
C................ 9 R3 Sistrurus Viperidae...... Massasauga U.S.A. (IA, IL,
catenatus (=rattlesnake) IN, MI, MO,
catenatus. , eastern. MN, NY, OH,
PA, WI),
Canada.
C................ 6 R4 Pituophis Colubridae..... Snake, black U.S.A. (AL, LA,
melanoleucus pine. MS).
lodingi.
C*............... 5 R4 Pituophis Colubridae..... Snake, U.S.A. (LA,
ruthveni. Louisiana pine. TX).
C*............... 5 R2 Graptemys Emydidae....... Turtle, Cagle's U.S.A. (TX).
caglei. map.
C................ 3 R2 Kinosternon Kinosternidae.. Turtle, Sonoyta U.S.A. (AZ),
sonoriense mud. Mexico.
longifemorale.
Amphibians
C*............... 3 R1 Rana Ranidae........ Frog, Columbia U.S.A. (ID, NV,
luteiventris. spotted (Great OR).
Basin DPS).
C*............... 3 R1 Rana muscosa... Ranidae........ Frog, mountain U.S.A. (CA,
yellow-legged NV).
(Sierra Nevada
DPS).
C*............... 2 R1 Rana pretiosa.. Ranidae........ Frog, Oregon U.S.A. (CA, OR,
spotted WA), Canada
(Entire). (BC).
C*............... 5 R1 Rana onca...... Ranidae........ Frog, relict U.S.A. (AZ, NV,
leopard. UT).
C................ 6 R4 Cryptobranchus Crytobranchidae Hellbender, U.S.A. (AR,
alleganiensis Ozark. MO).
bishopi.
C................ 2 R2 Eurycea Plethodontidae. Salamander, U.S.A. (TX).
waterlooensis. Austin blind.
PT............... 3 R1 Ambystoma Ambystomatidae. Salamander, U.S.A. (CA).
californiense. California
tiger (Entire).
C................ 2 R2 Eurycea Plethodontidae. Salamander, U.S.A. (TX).
naufragia. Georgetown.
C................ 2 R2 Eurycea Plethodontidae. Salamander, U.S.A. (TX).
chisholmensis. Salado
(Entire).
C*............... 3 R6 Bufo boreas Bufonidae...... Toad, boreal U.S.A. (CO, NM,
boreas. (Southern WY).
Rocky
Mountains DPS).
C*............... 11 R1 Bufo canorus... Bufonidae...... Toad, Yosemite. U.S.A. (CA).
C................ 5 R4 Necturus Proteidae...... Waterdog, black U.S.A. (AL).
alabamensis. warrior
(Sipsey Fork).
Fishes
PE............... 3 R1 Gila bicolor Cyprinidae..... Chub, Cowhead U.S.A. (CA).
vaccaceps. Lake tui.
PE............... 2 R2 Gila intermedia Cyprinidae..... Chub, Gila..... U.S.A. (AZ,
NM), Mexico.
C................ 11 R6 Etheostoma Percidae....... Darter, U.S.A. (AR, CO,
cragini. Arkansas. KS, MO, OK).
C................ 6 R4 Etheostoma Percidae....... Darter, U.S.A. (KY,
nigrum susanae. Cumberland TN).
johnny.
C................ 5 R4 Percina aurora. Percidae....... Darter, Pearl.. U.S.A. (LA,
MS).
C................ 5 R4 Etheostoma Percidae....... Darter, rush... U.S.A. (AL).
phytophilum.
C................ 2 R4 Etheostoma Percidae....... Darter, U.S.A. (AR).
moorei. yellowcheek.
C*............... 3 R6 Thymallus Salmonidae..... Grayling, U.S.A. (MT,
arcticus. Fluvial arctic WY).
(upper
Missouri River
DPS).
C................ 2 R4 Noturus sp..... Ictaluridae.... Madtom, chucky U.S.A. (TN).
(Entire).
C................ 2 R3 Cottus sp...... Cottidae....... Sculpin, grotto U.S.A. (MO).
C................ 5 R2 Notropis Cyprinidae..... Shiner, U.S.A. (TX).
oxyrhynchus. sharpnose.
C................ 5 R2 Notropis Cyprinidae..... Shiner, U.S.A. (TX).
buccula. smalleye.
C................ 3 R2 Catostomus Catostomidae... Sucker, Zuni U.S.A. (AZ,
discobolus bluehead. NM).
yarrowi.
PSAT............. N/A R1 Salvelinus Salmonidae..... Trout, Dolly U.S.A. (AK, OR,
malma. Varden. WA), Canada,
East Asia.
Clams
C................ 5 R4 Villosa Unionidae...... Bean, Choctaw.. U.S.A. (AL,
choctawensis. FL).
[[Page 24898]]
C................ 2 R3 Villosa fabalis Unionidae...... Bean, rayed.... U.S.A. (AL, IL,
IN, KY, MI,
NY, OH, TN,
PA, VA, WV),
Canada.
C................ 5 R4 Pleurobema Unionidae...... Clubshell, U.S.A. (AL, GA,
troschelianum. Alabama. TN).
C................ 5 R4 Pleurobema Unionidae...... Clubshell, U.S.A. (AL, GA,
chattanoogaens painted. TN).
e.
C................ 2 R4 Fusconaia Unionidae...... Ebonyshell, U.S.A. (AL,
(=Obovaria) round. FL).
rotulata.
C................ 2 R2 Popenaias popei Unionidae...... Hornshell, U.S.A. (NM,
Texas. TX), Mexico.
C................ 5 R4 Ptychobranchus Unionidae...... Kidneyshell, U.S.A. (AL, KY,
subtentum. fluted. TN, VA).
C................ 2 R4 Ptychobranchus Unionidae...... Kidneyshell, U.S.A. (AL,
jonesi. southern. FL).
C................ 5 R4 Lampsilis Unionidae...... Mucket, Neosho. U.S.A. (AR, KS,
rafinesqueana. MO, OK).
C................ 2 R3 Plethobasus Unionidae...... Mussel, Entire.
cyphyus. sheepnose.
C................ 2 R4 Margaritifera Margaritiferida Pearlshell, U.S.A. (AL).
marrianae. e. Alabama.
C................ 5 R4 Lexingtonia Unionidae...... Pearlymussel, U.S.A. (AL, KY,
dolabelloides. slabside. TN, VA).
C................ 5 R4 Pleurobema Unionidae...... Pigtoe, fuzzy.. U.S.A. (AL,
strodeanum. FL).
C................ 5 R4 Pleurobema Unionidae...... Pigtoe, Georgia U.S.A. (AL, GA,
hanleyanum. TN)
C................ 5 R4 Fusconaia Unionidae...... Pigtoe, narrow. U.S.A. (AL,
escambia. FL).
C................ 11 R4 Quincuncina Unionidae...... Pigtoe, tapered U.S.A. (AL,
burkei. FL).
C................ 5 R4 Lampsilis Unionidae U.S.A. (AL,
australis. Sandshell, FL)..
southern.
C................ 4 R3 Cumberlandia Margaritiferida Spectaclecase.. U.S.A. (AL, AR,
monodonta. e. IA, IN, IL,
KY, MO, NE,
OH, TN, VA,
WI).
C................ 5 R4 Elliptio Unionidae...... Spinymussel, U.S.A. (GA)
spinosa. Altamaha.
Snails
C................ 9 R6 Oreohelix Oreohelicidae.. Mountainsnail, U.S.A. (UT)
peripherica Ogden Deseret.
wasatchensis.
C................ 2 R6 Stagnicola Lymnaeidae..... Pondsnail, U.S.A. (UT).
bonnevilensis. Bonneville.
C................ 2 R1 Pyrgulopsis Hydrobiidae.... Pyrg, elongate U.S.A. (NV).
notidicola. mud meadows.
C................ 5 R4 Leptoxis downei Pleuroceridae.. Rocksnail, U.S.A. (GA,
Georgia. AL).
C................ 2 R1 Ostodes Potaridae...... Sisi........... U.S.A. (AS).
strigatus.
C................ 2 R2 Tryonia Hydrobiidae.... Snail, Diamond U.S.A. (TX)
adamantina. Y Spring.
C................ 2 R1 Samoana Partulidae..... Snail, fragile U.S.A. (GU,
fragilis. tree. MP).
C................ 2 R1 Partula Partulidae..... Snail, Guam U.S.A. (GU).
radiolata. tree.
C................ 2 R1 Partula gibba.. Partulidae..... Snail, Humped U.S.A. (GU,
tree. MP).
PE............... 2 R2 Tryonia kosteri Hydrobiidae.... Snail, Koster's U.S.A. (NM).
tryonia.
C................ 2 R1 Partulina Achatinellidae. Snail, Lanai U.S.A. (HI).
semicarinata. tree.
C................ 2 R1 Partulina Achatinellidae. Snail, Lanai U.S.A. (HI).
variabilis. tree.
C................ 2 R1 Partula Partulidae..... Snail, U.S.A. (MP).
langfordi. Langford's
tree.
PE............... 2 R2 Assiminea pecos Assimineidae... Snail, Pecos U.S.A. (NM,
assiminea. TX), Mexico
C................ 2 R2 Cochliopa Hydrobiidae.... Snail, Phantom U.S.A. (TX).
texana. Lake cave.
C................ 2 R1 Eua zebrina.... Partulidae U.S.A. (AS)....
Snail, Tutuila
tree.
C*............... 2 R2 Pyrgulopsis Hydrobiidae.... Springsnail, U.S.A. (NM).
chupaderae. Chupadera.
C*............... 11 R2 Pyrgulopsis Hydrobiidae.... Springsnail, U.S.A. (NM).
gilae. Gila.
C................ 2 R2 Tryonia Hydrobiidae.... Springsnail, U.S.A. (TX).
circumstriata( Gonzales.
=stocktonensis
).
C................ 5 R2 Pyrgulopsis Hydrobiidae.... Springsnail, U.S.A. (AZ),
thompsoni. Huachuca. Mexico.
C*............... 11 R2 Pyrgulopsis Hydrobiidae.... Springsnail, U.S.A. (NM).
thermalis. New Mexico.
C*............... 5 R2 Pyrgulopsis Hydrobiidae.... Springsnail, U.S.A. (AZ).
morrisoni. Page.
C................ 2 R2 Tryonia Hydrobiidae.... Springsnail U.S.A. (TX).
cheatumi. (=Tryonia),
Phantom.
[[Page 24899]]
PE............... 2 R2 Pyrgulopsis Hydrobiidae.... Springsnail, U.S.A. (NM).
roswellensis. Roswell.
C................ 2 R2 Pyrgulopsis Hydrobiidae.... Springsnail, U.S.A. (AZ).
trivialis. Three Forks.
C................ 5 R1 Newcombia Achatinellidae. Tree snail, U.S.A. (Hl).
cumingi. Newcomb's.
Insects
C................ 11 R6 Zaitzevia Elmidae........ Beetle, Warm U.S.A. (MT).
thermae. Springs
Zaitzevian
Riffle.
C*............... 2 R1 Nysius Lygaeidae...... Bug, Wekiu..... U.S.A. (HI).
wekiuicola.
C................ 3 R1 Hypolimnas Nymphalidae.... Butterfly, U.S.A. (GU,
octucula Mariana eight- MP).
mariannensis. spot.
C................ 2 R1 Vagrans Nymphalidae.... Butterfly, U.S.A. (GU,
egestina. Mariana MP).
wandering.
PE............... N/A R2 Euphydryas Nymphalidae.... Butterfly, U.S.A. (NM).
anicia Sacramento
cloudcrofti. Mountains
checkerspot.
C*............... 6 R1 Euphydryas Nymphalidae.... Butterfly, U.S.A. (OR,
editha taylori. whulge WA), Canada
checkerspot (BC)
(=Taylor's).
C................ 5 R4 Glyphopsyche Limnephilidae.. Caddisfly, U.S.A. (TN).
sequatchie. Sequatchie.
C................ 5 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (KY).
us major. beaver.
C................ 5 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (KY).
us caecus. Clifton.
C................ 11 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (TN).
us Coleman.
colemanensis.
C................ 5 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (TN).
us fowlerae. Fowler's.
C................ 5 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (KY).
us pholeter. greater Adams.
C................ 5 R5 Pseudanophthalm Carabidae...... Cave Beetle, U.S.A. (VA).
us holsingeri. Holsinger's.
C................ 5 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (KY).
us frigidus. icebox.
C................ 5 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (TN).
us inquisitor. inquirer.
C................ 5 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (TN).
us insularis. Insular.
C................ 5 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (KY).
us cataryctos. lesser Adams.
C................ 5 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (KY).
us troglodytes. Louisville.
C................ 5 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (TN).
us paulus. Noblett's.
C................ 11 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (KY).
us surprising.
inexpectatus.
C................ 5 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (TN).
us tiresias. Soothsayer
(=Indian Grave
Point).
C................ 5 R4 Pseudanophthalm Carabidae...... Cave beetle, U.S.A. (KY).
us parvus. Tatum.
C................ 9 R1 Megalagrion Coenagrionidae. Damselfly, U.S.A. (HI).
nigrohamatum blackline
nigrolineatum. Hawaiian.
C................ 2 R1 Megalagrion Coenagrionidae. Damselfly, U.S.A. (HI).
leptodemus. crimson
Hawaiian.
C................ 2 R1 Megalagrion Coenagrionidae. Damselfly, U.S.A. (HI).
nesiotes. flying earwig
Hawaiian.
C................ 2 R1 Megalagrion Coenagrionidae. Damselfly, U.S.A. (HI).
oceanicum. oceanic
Hawaiian.
C................ 8 R1 Megalagrion Coenagrionidae. Damselfly, U.S.A. (HI).
xanthomelas. orangeblack
Hawaiian.
C................ 2 R1 Megalagrion Coenagrionidae. Damselfly, U.S.A. (HI).
pacificum. Pacific
Hawaiian.
C................ 5 R1 Phaeogramma sp. Tephritidae.... Gall fly, U.S.A. (HI).
Po'olanui.
C................ 5 R1 Ambrysus Naucoridae..... Naucorid bug U.S.A. (CA.).
funebris. (=Furnace
Creek),
Nevares Spring.
[[Page 24900]]
PE............... 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
aglaia. [unnamed].
C................ 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
attigua. [unnamed].
PE............... 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
differens. [unnamed].
C................ 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
digressa. [unnamed].
PE............... 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
hemipeza. [unnamed].
PE............... 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
heteroneura. [unnamed].
PE............... 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
montgomeryi. [unnamed].
PE............... 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
mulli. [unnamed].
PE............... 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
musaphila. [unnamed].
PE............... 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
neoclavisetae. [unnamed].
PE............... 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
obatai. [unnamed].
PE............... 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
ochrobasis. [unnamed].
PE............... 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
substenoptera. [unnamed].
PE............... 2 R1 Drosophila Drosophilidae.. Pomace fly, U.S.A. (HI).
tarphytrichia. [unnamed].
C................ 5 R2 Heterelmis Elmidae........ Riffle beetle, U.S.A. (AZ).
stephani. Stephan's.
C*............... 11 R3 Hesperia Hesperiidae.... Skipper, Dakota U.S.A. (MN, IA,
dacotae. SD, ND, IL),
Canada.
C*............... 5 R1 Polites mardon. Hesperiidae.... Skipper, Mardon U.S.A. (CA, OR,
WA).
C*............... 9 R6 Cicindela Cicindelidae... Tiger beetle, U.S.A. (UT).
limbata Coral Pink
albissima. Sand Dunes.
C................ 5 R4 Cicindela Cicindelidae... Tiger beetle, U.S.A. (FL).
highlandensis. highlands.
C................ 3 R6 Cicindela Cicindelidae... Tiger beetle, U.S.A. (NE).
nevadica Salt Creek.
lincolniana.
Arachnids
C................ 2 R2 Cicurina Dictynidae..... Meshweaver, U.S.A. (TX).
wartoni. Warton's cave.
Crustaceans
PE............... N/A R2 Gammarus Gammaridae..... Amphipod, U.S.A. (NM).
desperatus. Noel's.
C................ 11 R4 Fallicambarus Cambaridae..... Crayfish, Camp U.S.A. (MS).
gordoni. Shelby
burrowing.
C................ 2 R1 Metabetaeus Alpheidae...... Shrimp, U.S.A. (HI).
lohena. anchialine
pool.
C................ 2 R1 Antecaridina Atyidae........ Shrimp, U.S.A. (HI),
lauensis. anchialine Mozambique,
pool. Saudi Arabia,
Japan.
C................ 2 R1 Calliasmata Alpheidae...... Shrimp, U.S.A. (HI),
pholidota. anchialine Funafuti
pool. Atoll, Saudi
Arabia, Sinai
Peninsula,
Tuvalu.
C................ 2 R1 Palaemonella Palaemonidae... Shrimp, U.S.A. (HI).
burnsi. anchialine
pool.
C................ 2 R1 Procaris Procarididae... Shrimp, U.S.A. (HI).
hawaiana. anchialine
pool.
C................ 2 R1 Vetericaris Procaridae..... Shrimp, U.S.A. (HI).
chaceorum. anchialine
pool.
C................ 5 R4 Typhlatya monae Atyidae........ Shrimp, U.S.A. (PR),
troglobitic Barbuda,
groundwater. Dominican
Republic.
Flowering Plants
C................ 11 R1 Abronia alpina. Nyctaginaceae.. Sand-verbena, U.S.A. (CA).
Ramshaw
Meadows.
C................ 11 R6 Alicellia Polemoniaceae.. Alice-flower, U.S.A. (UT).
caespitosa. wonderland.
C................ 11 R4 Arabis Brassicaceae... Rockcress, U.S.A. (AL,
georgiana. Georgia. GA).
C................ 11 R4 Argythamnia Euphorbiaceae.. Silverbrush, U.S.A. (FL).
blodgettii. Blodgett's.
C................ 3 R1 Artemisia Asteraceae..... Wormwood, U.S.A. (OR,
campestris northern. WA).
var.
wormskioldii.
C................ 2 R1 Astelia Liliaceae...... Pa'iniu........ U.S.A. (HI).
waialealae.
C................ 5 R4 Aster Asteraceae..... Aster, Georgia. U.S.A. (AL, FL,
georgianus. GA, NC, SC).
C................ 8 R6 Astragalus Fabaceae....... Milk-vetch, U.S.A. (UT).
equisolensis. horseshoe.
C................ 8 R6 Astragalus Fabaceae....... Milk-vetch, U.S.A. (CO).
tortipes. Sleeping Ute.
C................ 5 R1 Bidens Asteraceae..... Ko'oko'olau.... U.S.A. (HI).
amplectens.
C................ 6 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 Asteraceae..... Ko'oko'olau.... U.S.A. (HI).
conjuncta.
[[Page 24901]]
C................ 6 R1 Bidens Asteraceae..... Ko'oko'olau.... U.S.A. (HI).
micrantha
ctenophylla.
C................ 5 R4 Brickellia Asteraceae..... Brickell-bush, U.S.A. (FL).
mosieri. Florida.
C................ 5 R1 Calamagrostis Poaceae........ Reedgrass, U.S.A. (HI).
expansa. [unnamed].
C................ 5 R1 Calamagrostis Poaceae........ Reedgrass, U.S.A. (HI).
hillebrandii. [unnamed].
C................ 5 R4 Calliandra Mimosaceae..... No common name. U.S.A. (PR).
locoensis.
C*............... 2 R1 Calochortus Liliaceae...... Mariposa lily, U.S.A. (CA,
persistens. Siskiyou. OR).
C................ 5 R4 Calyptranthes Myrtaceae...... No common name. U.S.A. (PR).
estremerae.
C................ 5 R1 Canavalia Fabaceae....... 'Awikiwiki..... U.S.A. (HI).
napaliensis.
C................ 2 R1 Canavalia Fabaceae....... 'Awikiwiki..... U.S.A. (HI).
pubescens.
C................ 8 R6 Castilleja Scrophulariacea Paintbrush, U.S.A. (UT).
aquariensis. e. Aquarius.
C*............... 11 R1 Castilleja Scrophulariacea Paintbrush, U.S.A. (ID).
christii. e. Christ's.
C................ 6 R4 Chamaecrista Fabaceae....... Pea, Big Pine U.S.A. (FL).
lineata partridge.
keyensis.
C................ 6 R4 Chamaesyce Euphorbiaceae.. Sandmat, U.S.A. (FL).
deltoidea pineland.
pinetorum.
C................ 6 R4 Chamaesyce Euphorbiaceae.. Spurge, wedge.. U.S.A. (FL).
deltoidea
serpyllum.
C................ 5 R1 Chamaesyce Euphorbiaceae.. 'Akoko......... U.S.A. (HI).
eleanoriae.
C................ 6 R1 Chamaesyce Euphorbiaceae.. 'Akoko......... U.S.A. (HI).
remyi var.
kauaiensis.
C................ 6 R1 Chamaesyce Euphorbiaceae.. 'Akoko......... U.S.A. (HI).
remyi var.
remyi.
C................ 5 R1 Charpentiera Amaranthaceae.. Papala......... U.S.A. (HI).
densiflora.
C*............... 6 R1 Chorizanthe Polygonaceae... Spineflower, U.S.A. (CA).
parryi var. San Fernando
fernandina. Valley.
C................ 5 R4 Chromolaena Asteraceae..... Thoroughwort, U.S.A. (FL).
frustrata. Cape Sable.
C................ 2 R4 Consolea Cactaceae...... Cactus, Florida U.S.A. (FL).
corallicola. semaphore.
C................ 2 R4 Cordia rupicola Boraginaceae... No common name. U.S.A. (PR),
Anegada.
C................ 2 R1 Cyanea Campanulaceae.. Haha........... U.S.A. (HI).
asplenifolia.
C................ 5 R1 Cyanea calycina Campanulaceae.. Haha........... U.S.A. (HI).
C................ 2 R1 Cyanea Campanulaceae.. Haha........... U.S.A. (HI).
eleeleensis.
C................ 2 R1 Cyanea kuhihewa Campanulaceae.. Haha........... U.S.A. (HI).
C................ 5 R1 Cyanea Campanulaceae.. Haha........... U.S.A. (HI).
kunthiana.
C................ 5 R1 Cyanea Campanulaceae.. Haha........... U.S.A. (HI).
lanceolata.
C................ 2 R1 Cyanea obtusa.. Campanulaceae.. Haha........... U.S.A. (HI).
C................ 5 R1 Cyanea Campanulaceae.. Haha........... U.S.A. (HI).
tritomantha.
C................ 2 R1 Cyrtandra Gesneriaceae... Ha'iwale....... U.S.A. (HI).
filipes.
C................ 5 R1 Cyrtandra Gesneriaceae... Ha'iwale....... U.S.A. (HI).
kaulantha.
C................ 5 R1 Cyrtandra Gesneriaceae... Ha'iwale....... U.S.A. (HI).
oenobarba.
C................ 2 R1 Cyrtandra Gesneriaceae... Ha'iwale....... U.S.A. (HI).
oxybapha.
C................ 2 R1 Cyrtandra Gesneriaceae... Ha'iwale....... U.S.A. (HI).
sessilis.
C................ 6 R4 Dalea Fabaceae....... Prairie-clover, U.S.A. (FL).
carthagenensis Florida.
floridana.
C................ 5 R4 Digitaria Poaceae........ Crabgrass, U.S.A. (FL).
pauciflora. Florida
pineland.
C................ 6 R1 Dubautia Asteraceae..... Na'ena'e....... U.S.A. (HI).
imbricata
imbricata.
C................ 3 R1 Dubautia Asteraceae..... Na'ena'e....... U.S.A. (HI).
plantaginea
magnifolia.
C................ 5 R1 Dubautia Asteraceae..... Na'ena'e....... U.S.A. (HI).
waialealae.
C*............... 6 R2 Echinomastus Cactaceae...... Cactus, Acuna.. U.S.A. (AZ),
erectocentrus Mexico.
var. acunensis.
C................ 11 R1 Erigeron Asteraceae..... Daisy, basalt.. U.S.A. (WA).
basalticus.
C*............... 5 R2 Erigeron Asteraceae..... Fleabane, U.S.A. (AZ).
lemmonii. Lemmon.
C................ 2 R1 Eriogonum Polygonaceae... Buckwheat, U.S.A. (WA).
codium. Umtanum Desert.
C................ 2 R1 Eriogonum Polygonaceae... Buckwheat, U.S.A (NV).
diatomaceum. Churchill
Narrows.
C................ 5 R1 Eriogonum Polygonaceae... Buckwheat, Red U.S.A. (CA).
kelloggii. Mountain.
C................ 5 R1 Festuca Poaceae........ No common name. U.S.A. (HI).
hawaiiensis.
C*............... 11 R2 Festuca Poaceae........ Guadalupe U.S.A. (TX),
ligulata. fescue. Mexico.
[[Page 24902]]
C................ 5 R1 Gardenia remyi. Rubiaceae...... Nanu........... U.S.A. (HI).
C................ 5 R1 Geranium Geraniaceae.... Nohoanu........ U.S.A. (HI).
hanaense.
C................ 8 R1 Geranium Geraniaceae.... Nohoanu........ U.S.A. (HI).
hillebrandii.
C................ 2 R1 Geranium Geraniaceae.... Nohoanu........ U.S.A. (HI).
kauaiense.
C................ 5 R4 Gonocalyx Ericaceae...... No common name. U.S.A. (PR).
concolor.
C*............... 2 R1 Hazardia Asteraceae..... Orcutt's U.S.A. (CA),
orcutti. hazardia. Mexico.
C................ 5 R1 Hedyotis Rubiaceae...... Kampua'a....... U.S.A. (HI).
fluviatilis.
C................ 11 R4 Helianthus Asteraceae..... Sunflower, U.S.A. (AL, GA,
verticillatus. whorled. TN).
C................ 5 R2 Hibiscus Malvaceae...... Rose-mallow, U.S.A. (TX).
dasycalyx. Neches River.
C................ 6 R4 Indigofera Fabaceae....... Indigo, Florida U.S.A. (FL).
mucronata
keyensis.
C................ 5 R1 Ivesia webberi. Rosaceae....... Ivesia, Webber. U.S.A. (CA,
NV).
C................ 3 R1 Joinvillea Joinvilleaceae. Ohe............ U.S.A. (HI).
ascendens
ascendens.
C................ 5 R1 Korthalsella Viscaceae...... Hulumoa........ U.S.A. (HI).
degeneri.
C................ 5 R1 Labordia Loganiaceae.... Kamakahala..... U.S.A. (HI).
helleri.
C................ 5 R1 Labordia pumila Loganiaceae.... Kamakahala..... U.S.A. (HI).
C................ 5 R1 Lagenifera Asteraceae..... No common name. U.S.A. (HI).
erici.
C................ 5 R1 Lagenifera Asteraceae..... No common name. U.S.A. (HI).
helenae.
C................ 2 R2 Leavenworthia Brassicaceae... Gladecress, U.S.A. (TX).
texana. Texas golden.
C................ 5 R4 Lesquerella Brassicaceae... Bladderpod, U.S.A. (IN, KY,
globosa. Short's. TN).
C................ 5 R1 Lesquerella Brassicaceae... Bladderpod, U.S.A. (WA).
tuplashensis. White Bluffs.
C................ 2 R4 Linum arenicola Linaceae....... Flax, sand..... U.S.A. (FL).
C................ 3 R4 Linum carteri Linaceae....... Flax, Carter's U.S.A. (FL).
carteri. small-flowered.
C................ 5 R1 Lysimachia Primulaceae.... Makanoe lehua.. U.S.A. (HI).
daphnoides.
C................ 5 R1 Melicope Rutaceae....... Alani.......... U.S.A. (HI).
christophersen
ii.
C................ 2 R1 Melicope Rutaceae....... Alani.......... U.S.A. (HI).
degeneri.
C................ 2 R1 Melicope Rutaceae....... Alani.......... U.S.A. (HI).
hiiakae.
C................ 2 R1 Melicope Rutaceae....... Alani.......... U.S.A. (HI).
makahae.
C................ 2 R1 Melicope Rutaceae....... Alani.......... U.S.A. (HI).
paniculata.
C................ 5 R1 Melicope Rutaceae....... Alani.......... U.S.A. (HI).
puberula.
C................ 5 R1 Myrsine Myrsinaceae.... Kolea.......... U.S.A. (HI).
fosbergii.
C................ 2 R1 Myrsine mezii.. Myrsinaceae.... Kolea......... U.S.A. (HI).
C................ 5 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................ 5 R1 Nothocestrum Solanaceae..... 'Aiea.......... U.S.A. (HI).
latifolium.
C................ 2 R1 Ochrosia Apocynaceae.... Holei.......... U.S.A. (HI).
haleakalae.
C................ 5 R5 Panicum hirstii Poaceae........ Panic grass, U.S.A. (DE, GA,
Hirsts'. NC, NJ).
C................ 11 R2 Paronychia Caryophyllaceae Whitlow-wort, U.S.A. (TX).
congesta. bushy.
C................ 6 R2 Pediocactus Cactaceae...... Cactus, U.S.A. (AZ).
peeblesianus Fickeisen
fickeiseniae. plains.
C................ 5 R6 Penstemon Scrophulariacea Beardtongue, U.S.A. (CO).
debilis. e. Parachute.
C*............... 2 R6 Penstemon Scrophulariacea Beardtongue, U.S.A. (CO,
grahamii. e. Graham. UT).
C*............... 6 R6 Penstemon Scrophulariacea Beardtongue, U.S.A. (CO,
scariosus e. White River. UT).
albifluvis.
C................ 2 R1 Peperomia Piperaceae..... 'Ala 'ala wai U.S.A. (HI).
subpetiolata. nui.
C................ 2 R1 Phacelia Hydrophyllaceae Brand's U.S.A. (CA),
stellaris. phacelia. Mexico
C................ 11 R6 Phacelia Hydrophyllaceae Phacelia, U.S.A. (CO).
submutica. DeBeque.
C................ 2 R1 Phyllostegia Lamiaceae...... No common name. U.S.A. (HI).
bracteata.
C................ 5 R1 Phyllostegia Lamiaceae...... No common name. U.S.A. (HI).
floribunda.
C................ 2 R1 Phyllostegia Lamiaceae...... No common name. U.S.A. (HI).
hispida.
C................ 5 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................ 6 R1 Platydesma Rutaceae....... No common name. U.S.A. (HI).
cornuta
cornuta.
C................ 6 R1 Platydesma Rutaceae....... No common name. U.S.A. (HI).
cornuta
decurrens.
C................ 2 R1 Platydesma Rutaceae....... No common name. U.S.A. (HI).
remyi.
[[Page 24903]]
C................ 5 R1 Platydesma Rutaceae....... Pilo kea lau U.S.A. (HI).
rostrata. lii.
C................ 5 R1 Pleomele Agavaceae...... Hala pepe...... U.S.A. (HI).
forbesii.
C................ 2 R1 Pleomele Agavaceae...... Hala pepe...... U.S.A. (HI).
fernaldii.
C................ 5 R1 Potentilla Rosaceae....... Cinquefoil, U.S.A. (NV).
basaltica. Soldier
Meadows.
C................ 5 R1 Pritchardia Asteraceae..... Lo'ulu, U.S.A. (HI).
hardyi. (=Na'ena'e).
C................ 6 R1 Pseudognaphaliu Asteraceae..... 'Ena'ena....... U.S.A. (HI).
m
(=Gnaphalium)
sandwicensium
var.
molokaiense.
C................ 2 R1 Psychotria Rubiaceae...... Kopiko......... U.S.A. (HI).
grandiflora.
C................ 3 R1 Psychotria Rubiaceae...... Kopiko......... U.S.A. (HI).
hexandra
oahuenis.
C................ 2 R1 Psychotria Rubiaceae...... Kopiko......... U.S.A. (HI).
hobdyi.
C................ 5 R1 Pteralyxia Apocynaceae.... Kaulu.......... U.S.A. (HI).
macrocarpa.
C................ 5 R1 Ranunculus Ranunculaceae.. Makou.......... U.S.A. (HI).
hawaiensis.
C................ 2 R1 Ranunculus Ranunculaceae.. Makou.......... U.S.A. (HI).
mauiensis.
C*............... 2 R1 Rorippa Brassicaceae... Cress, Tahoe U.S.A. (CA, NV)
subumbellata. yellow.
C................ 2 R1 Schiedea Caryophyllaceae No common name. U.S.A. (HI).
attenuata.
C................ 2 R1 Schiedea Caryophyllaceae Ma'oli'oli..... U.S.A. (HI).
pubescens.
C................ 2 R1 Schiedea Caryophyllaceae No common name. U.S.A. (HI).
salicaria.
C................ 5 R1 Sedum Crassulaceae... Stonecrop, Red U.S.A. (CA).
eastwoodiae. Mountain.
C................ 5 R1 Sicyos Cucurbitaceae.. 'Anunu......... U.S.A. (HI).
macrophyllus.
C*............... 9 R1 Sidalcea Malvaceae...... Checkerbloom, U.S.A. (CA).
hickmanii Parish's.
parishii.
C................ 9 R4 Sideroxylon Sapotaceae..... Bully, U.S.A. (FL).
reclinatum Everglades.
ssp.
austrofloriden
se.
C................ 5 R1 Solanum Solanaceae..... Popolo......... U.S.A. (HI).
nelsonii.
C................ 2 R1 Stenogyne Lamiaceae...... No common name. U.S.A. (HI).
cranwelliae.
C................ 2 R1 Stenogyne Lamiaceae...... No common name. U.S.A. (HI).
kealiae.
C................ 2 R1 Zanthoxylum Rutaceae....... 'Ae............ U.S.A. (HI).
oahuense.
Ferns and Allies
C*............... 11 R1 Botrychium Ophioglossaceae Moonwort, U.S.A. (CA, CO,
lineare. slender. ID, MT, OR,
WA), Canada
(BC, NB, QC).
C................ 5 R1 Christella Thelypteridacea No common name. U.S.A. (HI).
boydiae (= e.
Cyclosorus
boydiae var.
boydiae +
Cyclosorus
boydiae
kipahuluensis).
C................ 2 R1 Doryopteris Pteridaceae.... No common name. U.S.A. (HI).
takeuchii.
C................ 3 R1 Microlepia Dennstaedtiacea Palipali....... U.S.A. (HI).
strigosa var. e.
mauiensis
(=Microlepia
mauiensis).
C................ 2 R1 Phlegmariurus Lycopodiaceae.. Wawaeiole...... U.S.A. (HI).
stemmermanniae.
----------------------------------------------------------------------------------------------------------------
Note: See end of SUPPLEMENTARY INFORMATION for an explanation of symbols used in this table.
Table 2.--Animals and Plants Formerly Candidates or Formerly Proposed for Listing
----------------------------------------------------------------------------------------------------------------
Status
------------------------------ Lead region Scientific name Family Common name Historic range
Code Expl.
----------------------------------------------------------------------------------------------------------------
Mammals
E................ L R1 Brachylagus Leporidae...... Rabbit, pygmy U.S.A. (CA, ID,
idahoensis. (Columbia MT, NV, OR,
Basin DPS). UT, WA, WY).
E................ L R1 Urocyon Canidae........ Fox, San Miguel U.S.A. (CA).
littoralis Island.
littoralis.
E................ L R1 Urocyon Canidae........ Fox, Santa U.S.A. (CA).
littoralis Catalina
catalinae. Island.
E................ L R1 Urocyon Canidae........ Fox, Santa Cruz U.S.A. (CA).
littoralis Island.
santacruzae.
[[Page 24904]]
E................ L R1 Urocyon Canidae........ Fox, Santa Rosa U.S.A. (CA).
littoralis Island.
santarosae.
Birds
Rp............... A R6 Charadrius Charadriidae... Plover, U.S.A.
montanus. mountain. (western),
Canada,
Mexico.
Amphibians
E................ L R1 Ambystoma Ambystomatidae. Salamander, U.S.A. (CA).
californiense. California
tiger (Sonoma
County DPS).
E................ L R1 Rana muscosa... Ranidae........ Frog, mountain U.S.A. (CA, NV)
yellow-legged including San
(southern Diego, Orange,
California Riverside, San
DPS). Bernardino,
and Los
Angeles
Counties.
Fishes
Rp............... A R1 Oncorhynchus Salmonidae..... Trout, coastal U.S.A. (AK, CA,
clarki clarki. cutthroat OR, WA).
(southwestern
WA/Columbia
River DPS).
Snails
E................ L R3 Antrobia Hydrobiidae.... Cavesnail, U.S.A. (MO).
culveri. Tumbling Creek.
Insects
E................ L R1 Pseudocopaeodes Hesperiidae.... Skipper, Carson U.S.A. (CA,
eunus obscurus. wandering. NV).
Flowering Plants
E................ L R1 Ambrosia pumila Asteraceae..... Ambrosia, San U.S.A. (CA),
Diego. Mexico.
Rp............... A R1 Lepidium....... Brassicaceae Peppergrass, U.S.A. (ID)
papilliferum. Slick spot.
E................ L R1 Limnanthes Limnanthaceae.. Meadowfoam, U.S.A. (OR).
floccosa large-flowered
grandiflora. wooly.
E................ L R1 Lomatium cookii Apiaceae....... Lomatium, U.S.A. (OR).
Cook's.
E................ L R1 Nesogenes Verbenaceae.... No common name. U.S.A. (MP).
rotensis.
E................ L R1 Osmoxylon Araliaceae..... No common name. U.S.A. (MP).
mariannense.
Rp............... N R1 Tabernaemontana Apocynaceae.... No common name. U.S.A. (GU,
rotensis. MP).
Ferns and Allies
Rc............... A R1 Dryopteris Dryopteridaceae No common name. U.S.A. (HI).
glabra var.
pusilla
(=Dryopteris
tenebrosa).
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Note: See end of SUPPLEMENTARY INFORMATION for an explanation of symbols used in this table.
[FR Doc. 04-9893 Filed 5-3-04; 8:45 am]
BILLING CODE 4310-55-P