Overview

Distribution

Range Description

This species can be found in Barton Springs, Edwards Aquifer, Austin, and Travis County, Texas, USA; it occurs in four hydrologically connected spring outlets (see Chippindale et al. [1993] for further details). Barton Springs is fed by the Barton Springs segment of the Edwards Aquifer; this segment occurs in portions of Blanco, Hays, and Travis counties.
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Geographic Range

Barton Springs of Zilker Park in Austin, Travis County, Texas. E. sosorum is restricted to and only found in two (Parthenia and Eliza) of the four hydrologically connected pools collectively named Barton Springs. E. sosorum is the only extant salamander species found in these two pools. No evidence exists that indicates E. sosorum is found anywhere else. This means that E. sosorum has the smallest habitat of any vertebrate in the world. (Chippindale et al 1993; Deanna Chamberlain, personal communication)

Biogeographic Regions: nearctic (Native )

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endemic to a single state or province

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National Distribution

United States

Origin: Native

Regularity: Regularly occurring

Currently: Present

Confidence: Confident

Type of Residency: Year-round

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Global Range: (<100-250 square km (less than about 40-100 square miles)) Barton Springs, Edwards Aquifer, Austin, Travis County, Texas; occurs in three of four hydrologically connected spring outlets (see Chippindale et al. [1993] for further details). Barton Springs is fed by the Barton Springs segment of the Edwards Aquifer; this segment occurs in portions of Blanco, Hays, and Travis counties.

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Historic Range:
U.S.A. (TX)

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Physical Description

Morphology

Physical Description

The average length of the Barton Springs salamander is 6.35 cm. The organism is small and is known for its fairly small head, reduced eyes (with a golden iris and black mottling), shovel-nosed snout, slender body and elongate limbs. E. sosorum has a very distinctive dorsal coloration known as the "salt and pepper" effect. Dorsal color varies in life from dark through medium gray to purplish gray or gray-brown to yellowish brown to yellowish cream. The varied degrees of blotched and mottled specks are attributed to an irregular mixture of (or lack of) melanophores, iridophores and pigment gaps. Overall, the mottled pattern gives the salamander olive brown specks with a base color of yellowish cream. The presence of silvery-white iridophores enhances the salamanders' luster. Some salamanders appear pale due to the lack of melanophores. The trunk of E. sosorum is finely speckled with melanophores while the ventral surface is creamy to translucent in color. Sometimes the stomach contents, as well as the presence of eggs in females, can be seen through the translucent skin. Dorsally, the limbs of E. sosorum, are unevenly speckled as well as the toes. Ventrally, the limbs are not speckled. In addition the relatively short tail of E. sosorum has an uneven distribution of melanophores. On the ventral surface of the tail the salamander has a narrow, orange-yellow strip from the posterior margin of cloacal vent to the tip. Furthermore, unique traits of barton spring salamanders include: three pairs of brightly-colored, red gills, four fingers on each hand, five toes on each foot and 16 pre-sacral vertebrae. These traits set Eurycea sosorum apart from other Central Texas Eurycea. (Petranka 1998; Deanna Chamberlain, personal communication; Chippindale et al 1993)

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Size

Length: 6 cm

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Diagnostic Description

Dorsal coloration is distinctive in most specimens; the combination of pigment gaps (pale areas due to an absence of melanophores) and frequently high concentrations of silvery-white dorsal iridophores apparently is unique (Chippindale et al. 1993). Slight "shovel-nose" evident in most specimens is not as extreme as in Tridentifera, but this characteristic does distinguish most individuals from members of surface populations that currently are assigned to Neotenes and E. NANA (Chippindale et al. 1993). Eyes are significantly reduced in comparison to individuals from other surface-dwelling populations of central Texas Eurycea; also, limbs of SOSORUM generally are proportionately longer (Chippindale et al. 1993). Eurycea sosorum typically has 16 presacral vertebrae, in contrast to the 17 typically present in surface-dwelling members of the Neotenes species group. Differs from other populations of central Texas Eurycea and TYPHLOMOLGE RATHBUNI also by a unique combination of alleles (see Chippindale et al. 1993).

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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
It is a spring dweller, occurring in the fourth largest spring in Texas. It inhabits spring outlets impounded/retained by concrete structures. Evidently, this species occurs primarily in non-subterranean waters; they are unlikely to range extensively underground but can live in subterranean waters (Chippindale et al. 1993). They are usually found under rocks or in gravel in about 0.1-5m of water; it also takes refuge among aquatic vascular plants, vegetative debris, and algae when such habitat is available (Chippindale et al. 1993). Spring habitat flows throughout the year and maintains a fairly constant temperature of 20 degrees celsius. This species is completely aquatic and does not metamorphose. Breeding is unknown in the wild; some other spring-dwelling species of central Texas Eurycea are thought to deposit eggs in gravel substrate. Captive breeding has been achieved at the Dallas Aquarium and the City of Austin facility. Females appear to deposit the eggs randomly on cobble, gravel, aquatic macrophytes, and the glass sides and bottom of the aquaria (L. Ables, D. Chamberlain pers. comm.).

Systems
  • Freshwater
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Habitat

E. sosorum prefers clear waters and is mostly concentrated near the spring openings where food supplies are abundant, water chemistry and temperatures are constant and access to surface and subsurface habitats is available. Barton Springs salamanders are also found under rocks and gravel immediately adjacent to main spring outflows and within aquatic vegetation and algae mats. E. sosorum lives in water depths ranging from 0.1 to 5 meters. The springs where the salamanders are found flow year long and remain at a constant temperature of twenty degrees Celsius. E. sosorum in generally not found on exposed on limestone surfaces or in silted areas within the pools. Monthly population counts done by the city of Austin show that the Parthenia pool population may range anywhere from 90 - 150 salamanders and the Eliza pool has an average population of 30 salamanders. (Deanna Chamberlain personal communication; Rogers 1997)

Aquatic Biomes: rivers and streams

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Comments: Spring dweller; occurs in the fourth largest spring in Texas; inhabited spring outlets are impounded/retained by concrete structures. Evidently, this species occurs primarily in nonsubterranean waters; unlikely to range extensively underground but can live in subterranean waters (Chippindale et al. 1993). Usually found under rocks or in gravel in about 0.1-5 m of water; also takes refuge among aquatic vascular plants, vegetative debris, and algae when such habitat is available (Chippindale et al. 1993). Spring habitat flows throughout the year and maintains a fairly constant temperature of 20 C. See Federal Register (17 February 1994, p. 7969-7970) for hydrological information on the Barton Springs segment of the Edwards Aquifer. Oviposition likely occurs in subsurface habitat (Federal Register, 4 September 1996, p. 46609).

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Migration

Non-Migrant: Yes. At least some populations of this species do not make significant seasonal migrations. Juvenile dispersal is not considered a migration.

Locally Migrant: No. No populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).

Locally Migrant: No. No populations of this species make annual migrations of over 200 km.

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Trophic Strategy

Food Habits

The diet of E. sosorum consists primarily of the small invertebrate Hyalla azteca, an amphipod. E. sosorum also feeds on snails, crustaceans, black worms, leeches and bug larvae. In captivity the salamanders feed on earthworms, brine shrimp, white worms and commercial food pellets. Predators of E. sosorum are small fish and crayfish. (Deanna Chamberlain, personal communication; Bishop 1967; Rogers 1997)

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Comments: Diet apparently consists almost entirely of amphipods and other small invertebrates.

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Population Biology

Number of Occurrences

Note: For many non-migratory species, occurrences are roughly equivalent to populations.

Estimated Number of Occurrences: 1 - 5

Comments: Only one occurrence.

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Life History and Behavior

Reproduction

Reproduction

Not many details of the reproduction of E. sosorum are known. This is due to the secretive and nocturnal nature of salamanders in general. In the wild, females have been found holding, at the maximum, forty eggs from September through January. It is known that females carry their eggs for a year before depositing them It takes one year for larvae to reach sexual maturity and all sexually mature individuals that have been found have been longer than 22.5 mm. Also in their native habitat, young hatchlings have been found in November, March and April. This evidence suggests that breeding takes place year round. In the wild, no deposited eggs have ever been found or seen. It is believed the E. sosorum may deposit it's eggs in the Edwards Aquifer which feeds the pools where they live. The Edwards Aquifer is a karst aquifer which means that it is very porous. Due to the small size of the salamander this hypothesis could be true. However, in captivity Barton Spring salamanders deposit their eggs on plastic plants in string-like clusters. The eggs are 1.5 mm in diameter and are surrounded by two jelly layers. They are easily observed because of their white color and iridiscent properties.

(Deanna Chamberlain, personal communication; Bishop 1967; Petranka 1998)

As of 1999, in captive-breeding programs, females have deposited eggs twenty times. Of the eggs deposited, larvae only developed twice and none survived to sexual maturity. What has been noted in the embryos is that after 19 days eyes develop and then, after 38 days, limb bud and gill structure is observed.

(Deanna Chamberlain, personal communication)

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Recently hatched young have been found in November, March, and April, and females with well-developed eggs have been found from September through January; in captivity, one female retained well-developed eggs for over a year (Chippindale et al. 1993). Apparently breeds year-round.

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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
VU
Vulnerable

Red List Criteria
D1+2

Version
3.1

Year Assessed
2004

Assessor/s
Geoffrey Hammerson, Paul Chippindale

Reviewer/s
Global Amphibian Assessment Coordinating Team (Simon Stuart, Janice Chanson, Neil Cox and Bruce Young)

Justification
Listed as Vulnerable because its population size is estimated to be less than 1,000 mature individuals, and it is known from only a single location.

History
  • 1996
    Not Evaluated
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Conservation Status

Barton Springs salamanders have been proclaimed an endangered species by the U.S. Fish and Wildlife Service. E. sosorum was first found in Barton Springs during the 1940's, and numbered in the hundreds. However, in the past decade, fewer than 20 specimens were observed over six month periods and none at other times. In addition, the number of dead salamanders found was increasing. The drastic decrease in the E. sosorum population was credited to the decrease in water quality and quantity of the Edwards Aquifer and even more specifically the Barton Creek Watershed which feeds the aquifer. This decline is the result of increased urbanization and environmental pollution. Also, improper cleaning of the Parthenia pool of Barton Springs (used for recreational swimming) drastically disturbed the chemical and physical equilibriums of the salamanders' habitat. In the past two to three years environmental activists have petitioned for environmentally safer ways for cleaning the pool, bringing greatly needed attention to the water quality and quantity issues concerning Barton Springs as well as the Edwards aquifer. (Rogers 1997; Deanna Chamberlain, personal communication)

US Federal List: endangered

IUCN Red List of Threatened Species: vulnerable

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National NatureServe Conservation Status

United States

Rounded National Status Rank: N1 - Critically Imperiled

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NatureServe Conservation Status

Rounded Global Status Rank: G1 - Critically Imperiled

Reasons: Occurs in spring outlets in only one location in Travis County, Texas; vulnerable to water contamination.

Intrinsic Vulnerability: Highly to moderately vulnerable.

Environmental Specificity: Very narrow. Specialist or community with key requirements scarce.

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Current Listing Status Summary

Status: Endangered
Date Listed: 04/30/1997
Lead Region:   Southwest Region (Region 2) 
Where Listed:


Population detail:

Population location: entire
Listing status: E

For most current information and documents related to the conservation status and management of Eurycea sosorum , see its USFWS Species Profile

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Population

Population
The total population size is unknown. The observable population in Eliza Pool was dozens or hundreds in the 1970s, 15 in November 1992, 0 from December 1993 to May 1995, 0-28 between June 1995 and July 1996. They were reportedly abundant in Barton Springs Pool in 1946, about 150 were seen in November 1992, and survey counts between April 1995 and April 1996 ranged from 3-45 individuals. No more than 20 have been observed during any one survey of the Sunken Garden Springs outlet, but this site is difficult to survey. See population updates by Chippindale and Price (2005). They declined during the 1970s and 1980s, probably due in part to cleaning procedures used by the City of Austin at Barton Springs Pool; new maintenance procedures at Barton Springs resulted in habitat recovery (e.g., re-establishment of vascular plants) and salamander population increases in the early 1990s, although the number of individuals located has been highly variable from year to year and the most recent data suggest a decline in numbers in 2000. The current population trend is unknown.

Population Trend
Stable
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Threats

Threats

Major Threats
It is vulnerable to extinction due to its very limited distribution within a sensitive habitat; the primary threat is contamination of the waters that feed Barton Springs. The Barton springs Aquifer has been designated by the Texas Water Commission as one of the aquifers most vulnerable to pollution in Texas (Chippindale et al. 1993). Excessive groundwater withdrawal is a potential threat. Under pool maintenance procedures in place as of 1992, human use of the Barton Springs Pool for swimming did not conflict with the continued existence of the salamander (Chippindale et al. 1993). Recreational swimming in the Barton Springs Pool does not pose a threat.
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Degree of Threat: B : Moderately threatened throughout its range, communities provide natural resources that when exploited alter the composition and structure of the community over the long-term, but are apparently recoverable

Comments: Vulnerable to extinction due to very limited distribution within a sensitive habitat; primary threat is contamination of the waters that feed Barton Springs (see Federal Register, 17 February 1994, for detailed discussion). The Barton springs Aquifer has been designated by the Texas Water Commission as one of the aquifers most vulnerable to pollution in Texas (Chippindale et al. 1993). Excessive groundwater withdrawal is a potential threat. Under pool maintenance procedures in place as of 1992, human use of the Barton Springs Pool for swimming did not conflict with the continued existence of the salamander (Chippindale et al. 1993). Recreational swimming in the Barton Springs Pool does not pose a threat.

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Management

Conservation Actions

Conservation Actions
Barton Springs is in Zilker Park, which is owned and operated by the City of Austin. City property is managed as a park and pool. Various agencies of the state of Texas have committed to expedite developing and implementing conservation measures needed for the species and the Barton Springs segment of the Edwards Aquifer, as set forth in the "Barton Springs Salamander Conservation Agreement and Strategy," signed 13 August 1996 (see Federal Register 61(172):46608-46616, 4 September 1996, for details). The City of Austin has established a captive breeding program for this species. This species is listed as Endangered by both the state of Texas and the Federal Government.
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Management Requirements: Successful spawning of captives has been accomplished at the Dallas Aquarium and at the National Biological Service's Midwest Science Center in Missouri, but hatching success has been very low.

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Global Protection: None. No occurrences appropriately protected and managed

Comments: Barton Springs is in Zilker Park, which is owned and operated by the City of Austin. City property is managed as a park and pool. Various agencies of the State of Texas have committed to expedite developing and implementing conservation measures needed for the species and the Barton Springs segment of the Edwards Aquifer, as set forth in the "Barton Springs Salamander Conservation Agreement and Strategy," signed 13 August 1996 (see Federal Register 61(172):46608-46616, 4 September 1996, for details). This agreement resulted in temporary USFWS withdrawal of proposed endangered status for this salamander.

Needs: Protect the single EO and its water supply (see "Barton Springs Salamander Conservation Agreement and Strategy").

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Relevance to Humans and Ecosystems

Benefits

Economic Importance for Humans: Negative

Since the placement of E. sosorum on the U.S. ESA endangered species list, major restrictions have taken place on the urban development within the main watersheds of the Edwards Aquifer in Austin, TX. (Rogers 1997)

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Wikipedia

Barton Springs Salamander

The Barton Springs salamander (Eurycea sosorum) is an endangered lungless salamander that only lives in the habitat of Barton Springs in Austin, Texas, USA. Barton Springs salamanders are average-sized (adults grow to approximately 2.5 inches (6.4 cm) in length) and have mottled coloration varying from darkish purple to light yellow.

Contents

Environmental Impact

Amphibian species worldwide have been in decline due to climate change including but not limited to: increased UV radiation, change in precipitation, and various pathogen outbreaks (chytrid fungus[1] which causes Chytridiomycosis[2]). However, habitat destruction, degradation, and pollution on a local scale have resulted mainly from land and watershed urbanization. These changes, in turn, affect, among others, water quality and biological community composition of rivers and water systems in the surrounding environment. The wide effects of contamination and degradation on these water systems make analyzing their specific sources difficult since the interactions of factors and overlapping effects may occur. Nonetheless, it is important to study these consequences so that future impact on this and other species may be reduced.[3]

Oxygen Absorption

Dissolved oxygen (DO) is required at specific levels to maintain healthy aquatic life. To do this, a “national ambient water quality criteria”[4] has been set by The U.S. Environmental Protection Agency and measurements have been made since 1969, albeit inconsistently. Hypoxia, a state of reduced oxygen, may hinder embryonic and fetal development as well as decrease oxygen consumption in adults. Apart from prenatal developments, physiological responses may also arise from a lack of oxygen. Some of the known responses include “Increases in heart rate and buccal pumping, behavioral hypothermia, and gill hypertrophy”.[5]

Since this species is an obligately aquatic neotene retains its gills through its adult life, it must absorb oxygen through its gills or skin. However, the method in which it performs this absorption has yet to be determined. One study found that when presented with a low DO level, this salamander increases its body movement. They theorized 2 explanations for this reaction: 1) low and high DO levels may be found in relatively close proximities therefore movement will allow this species to migrate to a higher DO environment, 2) the physical movement causes a decrease between boundary layers adjacent to skin and gills which allows for greater flow of oxygen.[6]

Diet and Behavior

Much of the Barton Springs Salamander's life history remains unknown at this time. It appears that they feed primarily on small aquatic crustaceans, but can supplement their diet with other items, such as earthworms.[7] In addition, aquatic vegetation has been shown to be a critical component to the salamander's habitat; their numbers dropped precipitously after the removal of much of the vegetation from Barton Springs, and have recovered after habitat restoration programs were implemented.[8]

Etymology

The species epithet (sosorum) is an acronym for "Save Our Springs" (a preservation group)[9] combined with a Latin genitive plural ending.[citation needed]

Conservation status

Preserved specimen

Despite inhabiting an urban area, E. sosorum was not described until 1993.[citation needed] It was put on the federal List of Threatened and Endangered Species in 1997.[citation needed] The salamander's listing prevented the City of Austin from cleaning the Barton Springs Pool as it had for 70 years--with bleach. As a result, the City of Austin applied for and was issued an Incidental Take Permit under Section 10(a)(1)(b) of the Endangered Species Act by the U.S. Fish and Wildlife Service in 1998. The permit has a term of 15 years and allows incidental taking of salamanders during pool cleaning and maintenance. As a mitigation measure, the City offered to direct 10 percent of revenue generated through pool entry fees into a conservation fund that is used for research and habitat enhancement.

References

  • Chippindale, P.T.; A.H. Price, & Hillis, D.M. (1993). "A new species of perennibranchiate salamander (Eurycea, Plethodontidae) from Austin, Texas". Herpetologica 49: 242–259. 
  • Chippindale, P.T.; A.H. Price, Wiens, J.J. & Hillis, D.M. (2000). "Phylogenetic relationships of central Texas hemidactyliine plethodontid salamanders, genus Eurycea, and a taxonomic revision of the group". Herpetological Monographs 14: 1–80. 
  • Hillis, D.M.; Chamberlain, D.A., Wilcox, T.P., & Chippindale, P.T. (2001). "A new species of subterranean blind salamander (Plethodontidae: Hemidactyliini: Eurycea: Typhlomolge) from Austin, Texas, and a systematic revision of central Texas paedomorphic salamanders". Herpetologica 57: 266–280. 
  • Hammerson & Chippindale (2004). Eurycea sosorum. 2006. IUCN Red List of Threatened Species. IUCN 2006. www.iucnredlist.org. Retrieved on 11 May 2006. Database entry includes a range map, a brief justification of why this species is vulnerable, and the criteria used
  • Woods, H.A.; Poteet, M.F., Hitchings, P.D., Brain, R.A., & Brooks, B.W. (2010). "Conservation Physiology of the Plethodontid Salamanders Eurycea nana and E. sosorum: Response to Declining Dissolved Oxygen". Copeia 2011(4): 540-553. 
  • Gaertner, J.P.; Forstner, M.R.J, O'Donnell, L., & Hahn, D. (2009). "Detection of Batrachochytrium dendrobatidis in Endemic Salamander Species from Central Texas". Ecohealth 6: 20-26. 

Notes

  1. ^ Gaertner, J.P.; Forstner, M.R.J, O'Donnell, L., & Hahn, D. (2009). "Detection of Batrachochytrium dendrobatidis in Endemic Salamander Species from Central Texas". Ecohealth 6: 20-26. 
  2. ^ Gaertner, J.P.; Forstner, M.R.J, O'Donnell, L., & Hahn, D. (2009). "Detection of Batrachochytrium dendrobatidis in Endemic Salamander Species from Central Texas". Ecohealth 6: 20-26. 
  3. ^ Woods, H.A.; Poteet, M.F., Hitchings, P.D., Brain, R.A., & Brooks, B.W. (2010). "Conservation Physiology of the Plethodontid Salamanders Eurycea nana and E. sosorum: Response to Declining Dissolved Oxygen". Copeia 2011(4): 540-553. 
  4. ^ Woods, H.A.; Poteet, M.F., Hitchings, P.D., Brain, R.A., & Brooks, B.W. (2010). "Conservation Physiology of the Plethodontid Salamanders Eurycea nana and E. sosorum: Response to Declining Dissolved Oxygen". Copeia 2011(4): 540-553. 
  5. ^ Woods, H.A.; Poteet, M.F., Hitchings, P.D., Brain, R.A., & Brooks, B.W. (2010). "Conservation Physiology of the Plethodontid Salamanders Eurycea nana and E. sosorum: Response to Declining Dissolved Oxygen". Copeia 2011(4): 540-553. 
  6. ^ Woods, H.A.; Poteet, M.F., Hitchings, P.D., Brain, R.A., & Brooks, B.W. (2010). "Conservation Physiology of the Plethodontid Salamanders Eurycea nana and E. sosorum: Response to Declining Dissolved Oxygen". Copeia 2011(4): 540-553. 
  7. ^ "Barton Springs Salamander". http://www.tpwd.state.tx.us/huntwild/wild/species/bartonspringssalamander/. Retrieved 15 January 2012. 
  8. ^ "Barton Springs Salamander". http://www.tpwd.state.tx.us/huntwild/wild/species/bartonspringssalamander/. Retrieved 15 January 2012. 
  9. ^ "Biodiversity". Sosalliance.org. 2010-09-13. http://www.sosalliance.org/community/about-save-our-springs-alliance/sos-program-summary/preserving-biodiversity. Retrieved 2011-07-29. 
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Names and Taxonomy

Taxonomy

Comments: Sweet (1984) found this salamander to be structurally intermediate between Neotenes and Tridentifera. Chippindale et al. (1993, 2000) determined that this species is morphologically and biochemically distinct from all known species of plethodontids. Included in Neotenes by Brown (1950, 1967).

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