Jump to main content.


Endangered and Threatened Wildlife and Plants; 90-Day Finding on a Petition To List the Jollyville Plateau Salamander as Endangered

Note: EPA no longer updates this information, but it may be useful as a reference or resource.


 [Federal Register: February 13, 2007 (Volume 72, Number 29)]
[Proposed Rules]
[Page 6699-6703]
From the Federal Register Online via GPO Access [wais.access.gpo.gov]
[DOCID:fr13fe07-8]

-----------------------------------------------------------------------

DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17

Endangered and Threatened Wildlife and Plants; 90-Day Finding on
a Petition To List the Jollyville Plateau Salamander as Endangered

AGENCY: Fish and Wildlife Service, Interior.
ACTION: Notice of 90-day petition finding and initiation of status review.

-----------------------------------------------------------------------

SUMMARY: We, the U.S. Fish and Wildlife Service (Service), announce a
90-day finding on a petition to list the Jollyville Plateau salamander
(Eurycea tonkawae) as endangered under the Endangered Species Act of
1973, as amended (Act). We find that the petition presents substantial
scientific or commercial information indicating that listing the
Jollyville Plateau salamander may be warranted. Therefore, with the
publication of this notice, we are initiating a status review to
determine if listing the species is warranted. To ensure that the
status review of the Jollyville Plateau salamander is comprehensive, we
are soliciting information and data regarding this species.

DATES: The finding announced in this document was made on February 13,
2007. To be considered in the 12-month finding for this petition,
comments and information should be submitted to us by April 16, 2007.

ADDRESSES: The complete supporting file for this finding is available
for public inspection, by appointment, during normal business hours at
the Austin Ecological Services Field Office, U.S. Fish and Wildlife
Service, 10711 Burnet Road, Suite 200, Austin, TX 78758 or via
electronic mail at http://www.fws.gov/southwest/es/Library/ The
petition is available at http://www.fws.gov/southwest/es/Library/.
Submit new information, materials, comments, or questions concerning
this petition and our finding to the above address.

FOR FURTHER INFORMATION CONTACT: Robert Pine, Field Supervisor, Austin
Ecological Services Field Office (see ADDRESSES section) (telephone
512/490-0057; facsimile 512/490-0974). Persons who use a
telecommunications device for the deaf (TDD) may call the Federal
Information Relay Service (FIRS) at 800-877-8339.

SUPPLEMENTARY INFORMATION:

Public Information Solicited

    When we make a finding that substantial information is presented to
indicate that listing a species may be warranted, we are required to
promptly commence a review of the status of the species. To ensure that
the status review is complete and based on the best available
scientific and commercial information, we are soliciting information on
the Jollyville Plateau salamander. We request any additional
information, comments, and suggestions from the public, other concerned
governmental agencies, Tribes, the scientific community, industry, or
any other interested parties concerning the status of the Jollyville
Plateau salamander. We are seeking information regarding the species'
historical and current status and distribution, its biology and
ecology, ongoing conservation measures for the species and its habitat,
and threats to the species and its habitat.
    We will base our 12-month finding on a review of the best
scientific and commercial information available, including all
information received during the public comment period. If you wish to
comment or provide information, you may submit your comments and
materials concerning this finding to the Field Supervisor, Austin
Ecological Services Field Office (see ADDRESSES section). Please note
that comments merely stating support or opposition to the actions under
consideration without providing supporting information, although noted,
will not be considered in making a determination, as section 4(b)(1)(A)
of the Act directs that determinations as to whether any species is a
threatened or endangered species shall be made ``solely on the basis of
the best scientific and commercial data available.'' At the conclusion
of the status review, we will issue the 12-month finding on the
petition, as provided in section 4(b)(3)(B) of the Act.
    Our practice is to make comments, including names and home
addresses of respondents, available for public review during normal
business hours. Individual respondents may request that we withhold
their names and home addresses, etc., but if you wish us to consider
withholding this information, you must state this prominently at the
beginning of your comments. In addition, you must present rationale for
withholding this information. This rationale must demonstrate that
disclosure would constitute a clearly unwarranted invasion of privacy.
Unsupported assertions will not meet this burden. In the absence of
exceptional, documentable circumstances, this information will be
released. We will always make submissions from organizations or
businesses, and from individuals identifying themselves as
representatives of or officials of organizations or businesses,
available for public inspection in their entirety.

Background

    Section 4(b)(3)(A) of the Endangered Species Act of 1973, as
amended (16 U.S.C. 1531 et seq.), requires that we make a finding on
whether a petition to list, delist, or reclassify a species presents
substantial scientific or commercial information to indicate that the
petitioned action may be warranted. We base this finding on information
provided in the petition, supporting information submitted with the
petition, and information otherwise available in our files at the time
we make the determination. To the maximum extent practicable, we make
this finding within 90 days of receipt of the petition, and publish our
notice of this finding promptly in the Federal Register.

[[Page 6700]]

    Our standard for substantial information within the Code of Federal
Regulations (CFR) with regard to a 90-day petition finding is ``that
amount of information that would lead a reasonable person to believe
that the measure proposed in the petition may be warranted'' (50 CFR
424.14(b)). If we find that substantial information was presented, we
are required to promptly commence a review of the status of the species.
    In making this finding, we relied on information provided by the
petitioner that we determined reliable after reviewing sources
referenced in the petition and information otherwise available in our
files at the time of petition review. We evaluated that information in
accordance with 50 CFR 424.14(b). Our process in making this 90-day
finding under section 4(b)(3)(A) of the Act and Sec.  424.14(b) of our
regulations is limited to a determination of whether the information in
the petition meets the ``substantial information'' threshold.

Petition

    On June 13, 2005, we received a formal petition, dated June 10,
2005, from Save Our Springs Alliance (SOSA) requesting that the
Jollyville Plateau salamander (Eurycea tonkawae) be listed as an
endangered species in accordance with section 4 of the Act.
    Action on this petition was precluded by court orders and
settlement agreements for other listing actions that required all of
our listing funds for fiscal year 2005 and a substantial portion of our
listing funds for fiscal year 2006. On September 29, 2005, we received
a 60-day notice of intent to sue from SOSA for failing to make a timely
90-day finding. On December 1, 2005, we sent a letter to SOSA informing
them that we would not likely make a petition finding during the fiscal
year of 2006 due to funding limitations. Subsequently, funding became
available to act on the petition. On August 10, 2006, SOSA filed a
complaint against the Service for failure to issue a 90-day petition
finding under section 4 of the Act for the finding on the Jollyville
Plateau salamander. In our December 11, 2006, motion for summary
judgment, we informed the court that based on current funding and
workload projections, we believed that we could complete a 90-day
finding by February 6, 2007, and if we determined that the petition
provided substantial scientific and commercial data, we could make a
12-month warranted or not warranted finding by February 6, 2008. This
notice constitutes our 90-day finding for the petition to list the
Jollyville Plateau salamander.

Species Information

    The petitioners presented sufficient, reliable information related
to the taxonomic status of the Jollyville Plateau salamander. This
species was first described as Eurycea tonkawae in the scientific
journal Herpetological Monographs by Chippendale et al. (2000, pp. 1-
48) based on morphological characteristics and genetic analysis. We
found no information in our files to refute the taxonomic status of the
Jollyville Plateau salamander as a species or a listable entity under
the Act. The Jollyville Plateau salamander is a neotenic member of the
family Plethodontidae. Neotenic salamanders do not metamorphose into a
terrestrial form. They retain external gills and are aquatic throughout
their lives (City of Austin 2001, p. 3). Jollyville Plateau salamanders
are approximately 1.5 to 2 inches (38 to 51 millimeters) at maturity
(City of Austin 2001, p. 5).
    Jollyville Plateau salamanders are distributed within springs,
spring-runs, and water-bearing karst formations in the Jollyville
Plateau area of the Edwards Aquifer in Travis and Williamson counties,
Texas (City of Austin 2001, p. 3). Karst is defined as ``a type of
terrain that is formed by the slow dissolution of calcium carbonate
from limestone bedrock by mildly acidic groundwater. This process
creates numerous cave openings, cracks, fissures, fractures, and
sinkholes, and the bedrock resembles a honeycomb'' (Veni and Associates
2002, p. 70). The salamander's surface habitat is characterized by a
typical depth of less than one foot (0.31 meters) of cool, well
oxygenated water containing clean, loose substrates of boulder, cobble,
and gravel (City of Austin 2001, p. 128). Eurycea species in Texas have
been found to eat a variety of benthic macroinvertebrates (insects in
their larval stage that are found at the bottom of a body of water),
such as amphipods and chironomid larvae (midges) (City of Austin 2001,
pp. 5-6).

Threats Analysis

    Section 4 of the Act and its implementing regulations (50 CFR 424)
set forth the procedures for adding species to the Federal List of
Endangered and Threatened Wildlife and Plants. A species may be
determined to be an endangered or threatened species due to one or more
of the five factors described in section 4(a)(1) of the Act: (A) The
present or threatened destruction, modification, or curtailment of its
habitat or range; (B) overutilization for commercial, recreational,
scientific, or educational purposes; (C) disease or predation; (D) the
inadequacy of existing regulatory mechanisms; or (E) other natural or
manmade factors affecting its continued existence. The Act identifies
the five factors to be considered, either singly or in combination, to
determine whether a species may be threatened or endangered. In making
this finding, we evaluated whether threats to the Jollyville Plateau
salamander presented in the petition and other information available in
our files at the time of the petition review may pose a concern with
respect to its survival. The following evaluation of these threats was
based on information provided or cited in the petition and found to be
reliable. Unless otherwise indicated in this threats analysis section,
the references cited were cited in the petition. The petition cited the
draft Barton Springs Salamander Recovery Plan that was not finalized at
the time we received the petition. However, we verified the information
using the finalized, signed version (Service 2005), and we reference
the page numbers from the finalized version in this finding. The
petition also cites the Service's draft 2002 Candidate Listing and
Priority Assessment Form for the Jollyville Plateau Salamander, which
was never finalized, and our 1997 Final Rule to list the Barton Springs
salamander (62 FR 23377) as endangered.

A. Present or Threatened Destruction, Modification, or Curtailment of
the Species' Habitat or Range

    The petition states that Jollyville Plateau salamanders are found
only within the rapidly developing counties of Travis and Williamson,
Texas, where they are dependent upon a constant supply of clean water
from the northern segment of the Edwards Aquifer (City of Austin 2001,
p. 3). Flows may also originate from the Trinity Aquifer during
droughts (Cole 1995, pp. 23-33). As of 2006, City of Austin data
reflect that central Texas watersheds occupied by Jollyville Plateau
salamanders include Brushy Creek, Bull Creek, Buttercup Creek, Lake
Creek, Lake Travis, Shoal Creek, South Brushy Creek, Walnut Creek, and
West Bull Creek. The petitioner notes that the Edwards and Trinity
aquifers are localized, small, and highly susceptible to pollution,
drying, or draining (Chippendale et al. 2000, p. 36).
    Information, including a map, provided with the petition depict
that the majority of Jollyville Plateau salamander habitat is found in

[[Page 6701]]

urbanized areas or areas scheduled for development (City of Austin
2005a, map; O'Donnell 2005, slide 12; Cole 1995, p. 28). The petition
states that once natural vegetation in a watershed is replaced with
impervious cover, rainfall is converted to surface runoff instead of
filtering through the ground (Schueler 1991, p. 114). Impervious cover
is any surface material, such as roads, rooftops, sidewalks, patios,
paved surfaces, or compacted soil, that prevents water from filtering
into the soil (Arnold and Gibbons 1996, p. 244). The petition cites an
assessment by The Center for Watershed Protection that impervious cover
exceeding 10 percent causes a loss of sensitive aquatic organisms,
reduction in stream biodiversity, water quality degradation, stream
warming, and channel instability within a watershed (Schueler 1994, pp.
100-106).
    The City of Austin 2001 report (pp. 16-39), which was cited in the
petition, indicates that six of the nine tributaries included in a
Jollyville Plateau salamander monitoring study conducted by the City of
Austin from 1996 to the present have impervious cover estimates greater
than 15 percent. The petition states that more than half of the
salamander's known localities are located within the Bull Creek
watershed. The Bull Creek watershed contains varying degrees of urban
development (City of Austin 2001, pp. 21-33): As a whole, it is more
than 50 percent developed and has an average impervious cover estimate
of 21-24 percent (City of Austin 1999, p. ii). However, where the main
stem of Bull Creek flows through the Balcones Canyonland Preserve
(BCP), some of the best quality habitat remaining for the Jollyville
Plateau salamander exists (O'Donnell 2005, slide 4; O'Donnell 2006).
    The petition states that developed tributaries occupied by the
Jollyville Plateau salamander had higher levels of chloride, nitrate-
nitrogen, specific conductance, magnesium, potassium, sodium, sulfate,
and fecal coliform compared to undeveloped tributaries (p <  0.05) over
the course of the City of Austin's monitoring study (City of Austin
2001, p. 59). Developed tributaries also experienced lower mean adult
and juvenile Jollyville Plateau salamander abundances per square meter
of wetted surface over the course of the study when compared to
undeveloped tributaries (p <  0.05) (City of Austin 2001, p. 99).
Information provided by the petitioner citing lower salamander
abundances and decreased water quality in developed tributaries is
corroborated by information in our files.
    The petition presents information about the negative effects of
sedimentation on urban stream ecosystems and aquatic organisms.
Sediments are mixtures of silt, sand, clay, and organic debris that are
washed into tributaries during storm events (White and White 1968, p.
116; Ford and Williams 1989, p. 537; Mahler and Lynch 1999, p. 13). Due
to high organic carbon content, sediments can act as a sink and/or
transport mechanism for contaminants. Contaminant compounds such as
polycyclic aromatic hydrocarbons (PAHs), petroleum hydrocarbons, and
pesticides can be absorbed into sediment particles in concentrations
that are orders of magnitude greater than found in the water column
(Mahler and Lynch 1999, p. 12). The petition adds that PAH exposure can
cause impaired reproduction, reduced growth and development, and tumors
or cancer in species of amphibians and reptiles. PAH exposure can also
cause reduced survival, altered physiological function, and changes in
species populations and community composition of freshwater
invertebrates (Albers 2003, p. 352). The petition does not present
evidence that these contaminant compounds are affecting the Jollyville
Plateau salamanders specifically. However, information on the effects
of sedimentation and contaminant compounds on amphibians, reptiles, and
other aquatic organisms provided by the petitioner is corroborated by
information in our files. Contamination from sedimentation has been
documented to negatively affect reproduction, growth, and development
in amphibians and reptiles, and has been shown to reduce survival for
aquatic invertebrates, the salamander's food source.
    The petition also states that sediments suspended in water can clog
gill structures of aquatic organisms and impair their ability to avoid
predators or locate food sources and potential mates (Garton 1977, p.
443; Schueler 1987, p. 1.5). Excessive deposition of sediment can
physically reduce the amount of available habitat and protective cover
for aquatic organisms by clogging spaces under or between the pebbles
and rocks that are used for protective cover (Welsh and Ollivier 1998,
p. 1128). Sedimentation from construction events that began in 2000 has
affected one of the two City of Austin reference sites used in the
aforementioned salamander monitoring study. The site, used as a control
for the study due to its undeveloped status at the beginning of the
study in 1996, can no longer be used as an undeveloped control due to
the impacts corresponding to an increase in active construction
upstream, including loss of salamander, benthic macroinvertebrate, and
aquatic plant habitat (O'Donnell 2005, slide 14). We verified the
petitioner's claim with information in our files indicating that,
following construction, the City observed a decline in Jollyville
Plateau salamander sightings in this tributary from more than 70
individuals per survey before the construction to rarely more than 1
after the construction began (O'Donnell 2006). The City of Austin
monitoring study provides evidence that, as sediment deposition
increases, salamander abundances significantly decrease (p <  0.01)
(City of Austin 2001, pp. 101, 126). In addition, the petition cites
observations by City of Austin biologists involved in the study that
indicated that once a sediment layer is established, Jollyville Plateau
salamander habitat is lost (O'Donnell 2005, slide 23). Information
provided by the petitioner on the effects of sedimentation is
corroborated by information in our files.
    The petition suggests that frequent human visitation and gas line
or sewage spills associated with developed tributaries may negatively
affect Jollyville Plateau salamanders and their habitat. The petition
cites documentation from the City of Austin of disturbed vegetation,
vandalism, and the destruction of travertine deposits by foot traffic
at one of their salamander monitoring sites in the Bull Creek
watershed. The drainage area was also impacted by a construction
sediment spill in 1994 (City of Austin 2001, p. 21). Several sewage
spills occurred in another drainage area within the Bull Creek
watershed during the mid-1990s, and the area still contains a
subsurface sanitary sewer line that, if a leak occurs, could affect the
salamanders living downstream (City of Austin 2001, pp. 21, 74). The
petition also provides information regarding several spills affecting a
tributary supporting Jollyville Plateau salamanders located in the
Shoal Creek watershed, including a 50-gallon gas spill that occurred in
1987, a several gallon hydraulic fluid spill in 1995, followed by a 50-
gallon diesel spill in 1996. There is at least one leaking underground
storage tank located in this tributary (City of Austin 2001, p. 16).
Information provided by the petitioner regarding gas, sediment, and
sewage spills in the range of the Jollyville Plateau salamander is
corroborated by information in our files.
    The petition states that Jollyville Plateau salamander deformities,
mainly in the form of curvature of the spine,

[[Page 6702]]

have been found at two of the City's Bull Creek watershed monitoring
sites (City of Austin 2001, p. 120). The petition states that the City
of Austin documented elevated levels of nutrients, particularly
nitrates, at these sites and suggested that this was the cause of the
deformities (O'Donnell et al. 2005, p. 11). The petition discusses
these deformities as part of listing factor C, ``Disease or
Predation.'' But, because the petition suggests that elevated nitrates
are the likely cause of the spinal curvatures, we are including this
information under Factor A, as a form of habitat modification.
Information in our files states that possible sources of spinal
curvature in amphibians include pathogens, inadequate nutrition, and
contamination. After several labs conducted necropsies on some of the
affected Jollyville Plateau salamanders, no obvious pathogens emerged
as the cause (O'Donnell et al. 2005, p. 11). Information in the City's
report indicates that nitrate levels at both of these sites have
averaged six times greater than undeveloped Edwards Aquifer springs
(City of Austin 2001, p. 120; O'Donnell et al. 2005, p. 11). Other
studies cited in the City's report include documentation of salamander
larvae and tadpoles developing bent tails, body swelling, and other
deformities when continuously exposed to similar nitrate levels for
more than five days (City of Austin 2001, p. 123; O'Donnell et al.
2005, pp. 11-12). Thus, environmental toxins are suspected by City
biologists as a leading cause of the spinal curvature (O'Donnell et
al., 2005, p. 11). Information in our files demonstrates that
deformities continue to be observed, include missing eyes, limbs, and
digits (O'Donnell et al. 2005, pp. 11-12). Information provided by the
petitioner regarding the documented elevated nitrates and Jollyville
Plateau salamander deformities is corroborated by information in our files.
    The petition states that the City of Austin has plans to build a
Water Treatment Plant in the Balcones Canyonland Preserve (BCP) above
the main stem of Bull Creek, which is considered one of the best
undeveloped habitats remaining for the Jollyville Plateau salamander
(O'Donnell 2005, slide 4, slide 12; O'Donnell 2006). Although most of
the creek's watershed is developed or slated for development, the main
stem of the creek runs through the BCP, which has been providing water
quality protection for the salamander by preventing development along
that part of the creek (O'Donnell 2005, slide 4; O'Donnell 2006). The
petition states the new plant will likely degrade the water quality of
the creek as well as increase sediment loads within the salamander's
habitat (O'Donnell 2006). Information provided by the petitioner on a
new water treatment plant slated for development above the main stem of
Bull Creek is corroborated by information in our files. We consider the
petition to present substantial information that the Jollyville Plateau
salamander may be threatened by habitat-based threats such as water
quality degradation.
    The petition also reports that increasing demand on the northern
segment of the Edwards Aquifer for local human water consumption and
diversion of surface runoff that would otherwise recharge the aquifer
could result in lower spring surface discharge. Hundreds of springs
have dried up in Texas due to human impacts on the aquifers, such as
over-pumping, increases in impervious cover, and surface run-off
diversion (Schram 1995, p. 90). To exacerbate this issue, the portion
of the Edwards Aquifer underlying the Jollyville Plateau is relatively
shallow, with a high elevation, thus being likely to dry out at the
surface during periods of drought (Cole 1995, pp. 26-27). Information
provided by the petitioner regarding increasing demand for water from
the segment of the aquifer containing the Jollyville Plateau
salamander, the susceptibility of that portion of the aquifer to dry
out at the surface, and the documented effects of human impacts and
over-pumping on aquifer systems in Texas is corroborated by information
in our files. Previous Service documents have discussed reduced spring
flow as a potential threat to similar Eurycea salamanders occurring in
the Edwards Aquifer (Service 2005, pp. 1.6-22, 1.6-23). We are not
making a finding on whether the petitioners have presented substantial
information that the Jollyville Plateau salamander may be threatened by
habitat-based threats associated with aquifer depletion. We will
consider information related to this issue during the status review.

B. Overutilization for Commercial, Recreational, Scientific, or
Educational Purposes

    According to the petition, overutilization is not considered a
threat to the Jollyville Plateau salamander at this time.

C. Disease or Predation

    The petition contends that City of Austin biologists found
Jollyville Plateau salamander abundances were negatively correlated
with the abundance of predatory centrarchid fish (carnivorous
freshwater fish belonging to the sunfish family), such as black bass
(Micropterus spp.) or sunfish (Lepomis spp.) (City of Austin 2001, p.
102). Information provided by the petitioner on the negative
correlation documented between salamander abundances and the abundance
of predatory fish is corroborated by information in our files. There
have been no direct observations of negative interactions between
Jollyville Plateau salamanders and centrachid fish. Predation could
have an additive effect to other threats occurring and may be
significant in combination with those threats.

D. Inadequacy of Existing Regulatory Mechanisms

    The petitioner states that there is currently no protection for the
Jollyville Plateau salamander provided by Texas State Law. The species
is not listed on the Texas State List of Threatened or Endangered
Species. There were no sources cited in the petition regarding this
statement, but this was verified by reviewing the State's list of
threatened and endangered species (TPWD 2006, pp. 2-3).
    The Balcones Canyonland Preserve (BCP) offers some water quality
benefits to portions of the Bull Creek, West Bull Creek, Buttercup
Creek, and Lake Travis watersheds through preservation of open space
over their recharge zones (Service 1996a, pp. 2-28-2-29). However, some
of the sites known to be occupied by the Jollyville Plateau salamander
within the BCP can be affected by changes in land use and subsequent
water quality degradation occurring in portions of contributing
watersheds outside of the preserved tracts. Specifically, the preserved
tracts within the BCP do not appear to be effective at reducing
nutrient levels at some salamander sites (City of Austin 1999, p. 6-
11). In addition, Jollyville Plateau salamanders are not a covered
species under the section 10(a)(1)(B) permit under which the preserves
were established (Service 1996b, pp. 1-10).
    The petition states that the City of Austin's water quality
ordinances provide some water quality regulatory protection to the
salamander's habitat, but do not appear to be effective at reducing
nutrient levels. The petition also notes that less than 20 percent of
all development in the Bull Creek watershed is subject to the most
stringent regulations, while the other 80 percent was developed prior
to the passage of these regulations in 1993 (City of Austin 1999, p. 6-
11). Additionally, regulations aimed at limiting impervious cover over the

[[Page 6703]]

Edwards Aquifer have been exempted by numerous grandfathering laws
(Chapter 245 of the Texas Local Government Code as discussed in Service
2005, p. 1.6-17).
    There are several State regulations, such as the Texas Commission
on Environmental Quality's (TCEQ) Edwards Rules, along with some
municipal ordinances, that are designed to minimize water quality
degradation from new development. The Edwards Rules regulate activities
that may pollute the Edwards Aquifer. The Edwards Rules do not address
land use, impervious cover limitations, nonpoint source pollution, or
application of fertilizers and pesticides over the recharge zone (The
Edwards Aquifer Rules as discussed in 62 FR 23389; The Edwards Aquifer
Rules as discussed in Service 2005, p. 1.6-16). Based on trend data
that shows degradation of water quality at Barton Springs over the
years, existing regulations for maintaining water quality in the
Edwards Aquifer may not adequately protect the salamander (City of
Austin 2005b, p. 20 as cited in Service 2005, p. 1.6-16). Information
provided by the petitioner on the inadequacies of existing regulatory
mechanisms is corroborated by information in our files. Data indicate
that water quality degradation in streams occupied by the Jollyville
Plateau salamander and other areas in the Edwards Aquifer such as
Barton Springs continue to occur despite the existence of current
regulatory mechanisms. Therefore, we consider the petition to present
substantial information that inadequacy of existing regulatory mechanisms
poses a substantial threat to the Jollyville Plateau salamander.

E. Other Natural or Manmade Factors Affecting the Species' Continued
Existence

    The petition states that natural factors negatively affecting the
Jollyville Plateau salamander include its limited distribution and
amphibians' sensitivity to water quality degradation. Amphibians,
especially their eggs and larvae, are sensitive to many pollutants
including heavy metals, insecticides, nitrates, salts, and petroleum
hydrocarbons (Harfenist et al. 1989, pp. 4-57). In addition,
crustaceans on which the Jollyville Plateau salamander feeds are
especially sensitive to water pollution (Phipps et al. 1995, p. 282).
Information provided by the petitioner on the Jollyville Plateau
salamander's limited distribution and amphibian sensitivity to
pollutants is corroborated by information in our files. As discussed
under Factor A, the present or threatened destruction, modification, or
curtailment of the species' habitat or range, Jollyville Plateau
salamanders exhibit potential sensitivities to certain aspects of water
quality degradation such as increased sedimentation from construction
events (O'Donnell 2006) and/or abnormal development in areas with high
nitrate levels (O'Donnell et al. 2005, pp. 11-12). Thus, we find that
the petition presents substantial information that natural factors may
increase susceptibility to other threats.

Finding

    We have reviewed the petition and literature cited in the petition,
and evaluated that information we deemed reliable to make this finding.
We used other reliable information that was readily available in our
files or readily available to us at the time of the petition review to
evaluate the reliability of information in the petition. The petition
presents evidence of water quality degradation resulting in lower
salamander abundances, a loss in salamander habitat, and possible
salamander deformities within urbanized areas of their habitat. The
petition also presents evidence of expanding urbanization throughout
their range, including areas that are currently considered protected.
The information in our files supports the petition's statements
regarding these threats to the salamander. Thus, we believe that the
petition presents substantial information indicating water quality
degradation combined with the species' limited distribution may
increase extinction risk. In addition, existing available regulatory
mechanisms appear potentially insufficient to control water quality
levels in salamander habitat and prevent the progressive decline of the
habitat upon which the Jollyville Plateau salamander depends. On the
basis of this review and evaluation, we find that the petition presents
substantial information indicating that listing the Jollyville Plateau
salamander may be warranted. As such, we are initiating a further
status review of the Jollyville Plateau salamander to determine whether
listing the species under the Act is warranted.
    We have also reviewed the available information to determine if the
existing and foreseeable threats pose an emergency to this species. The
immediacy of the threats described in the petition do not appear to be
so great to a significant portion of the total population that the
routine listing process would not be sufficient to prevent large losses
that could otherwise result in extinction. Furthermore, we do not
believe that expected losses of the salamander during the normal
listing process would risk the continued existence of the entire listed
species. For these reasons, we have determined that an emergency
listing is not warranted at this time. However, if at any time we
determine that emergency listing of the Jollyville Plateau salamander
is warranted, we will seek to initiate an emergency listing process.

References Cited

    A complete list of all references cited herein is available, upon
request, from the Austin Ecological Services Field Office (see
ADDRESSES section).

Author

    The primary author of this notice is the Austin Ecological Services
Field Office (see ADDRESSES section).

Authority

    The authority for this action is section 4 of the Endangered
Species Act of 1973, as amended (16 U.S.C. 1531 et seq.).

    Dated: February 6, 2007.
Kenneth Stansell,
Acting Director, U.S. Fish and Wildlife Service.
[FR Doc. E7-2289 Filed 2-12-07; 8:45 am]
BILLING CODE 4310-55-P 

 
 


Local Navigation


Jump to main content.