Batrachoseps relictus

Brame and Murray, 1968

Relictual Slender Salamander

G1Critically Imperiled Found in 4 roadless areas NatureServe Explorer →
G1Critically ImperiledGlobal Rank
Critically endangeredIUCN
HighThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.889920
Element CodeAAAAD02070
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNCritically endangered
Endemicendemic to a single state or province
KingdomAnimalia
PhylumCraniata
ClassAmphibia
OrderCaudata
FamilyPlethodontidae
GenusBatrachoseps
Concept Reference
Jockusch, E. L., I. Martínez-Solano, R. W. Hansen, and D. B. Wake. 2012. Morphological and molecular diversification of slender salamanders (Caudata: Plethodontidae: Batrachoseps) in the southern Sierra Nevada of California with descriptions of two new species. Zootaxa 3190:1-30.
Taxonomic Comments
Jockusch et al. (1998) redefined B. relictus; B. diabolicus, B. regius, B. kawia, all formerly included in B. relictus, were recognized as distinct species.

Batrachoseps altasierrae (Jockusch et al. 2012) formerly was encompassed in B. relictus, which now has a much more restricted distribution.
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2026-01-20
Change Date2014-08-22
Edition Date2026-01-20
Edition AuthorsHammerson, G. (2013); rev. R. L. Gundy (2026)
Threat ImpactHigh
Range Extent<100 square km (less than about 40 square miles)
Number of Occurrences1 - 5
Rank Reasons
This species has an extremely limited range in five drainages on a single mountain in the lower Sierra Nevada Mountains of California. Populations at lower elevations have been extirpated, reducing abundance and range extent by at least 50%. It continues to be threatened by habitat loss and degradation from trampling by livestock and human foot traffic.
Range Extent Comments
The known historical range spans only 15 km in the vicinity of Breckenridge Mountain, including the lower Kern River Canyon and higher elevations on Breckenridge Mountain, in the southern Sierra Nevada of California, (Jockusch et al. 2012, Moss et al. 2025). It has since been extirpated from the lower Kern River Canyon. Surveys that took place from 2021-2023 throughout the historical range of the species found that the historical range extent was approximately 88 km² while the current range extent is limited to 33 km² (Moss et al. 2025).
Occurrences Comments
This species is known from 13 sites within 5 drainages along Breckenridge Mountain (Moss et al. 2025).
Threat Impact Comments
Destruction of the limited seepage stream habitat is the primary threat impacting this species. Road building has been implicated as the main source of habitat destruction or degradation (Jockusch et al. 2012, Moss et al. 2025). Jockusch et al. (2012) reported that a site east of Squirrel Meadow, discovered in 1979, was later severely degraded by the construction of a logging road through the seepage area. A subsequent fire and timber harvest further compromised this site, and salamanders were not found there despite multiple searches over the next 22 years. Visits during the 2000s suggested that the population rebounded somewhat, but prime seep habitat is quite small. Soil compaction from both livestock and human foot traffic are also detrimental to the habitat (Moss et al. 2025).

Climate change presumably could negatively affect this species if it results in reduced water availability at springs and seeps.
Ecology & Habitat

Habitat

All recent sightings have been from two small high elevation populations in pine-fir forest (Jockusch et al. 2012). These salamanders are very closely associated with water, sometimes being found actually in water (e.g., in springs) (Jockusch et al. 2012). Rarely they have been found beyond surface water; two adults were found within a moist log about 45 meters upslope from a seep, and at a Breckenridge Mountain site (headwater seepage of Lucas Creek, elevation 1,665-1,700 meters), all specimens have been found under cover objects directly beside the stream over a distance of about 750 meters (Jockusch et al. 2012). Eggs are laid in wet/moist locations under rocks and probably other secluded sites. In mid-June, Hansen found a communal nest consisting of about 125 eggs in a large mass beneath a rock resting in seepage; approximately 20 adult salamanders were present (this record was first reported by Stebbins [1985] in his account of B. simatus) (Jockusch et al. 2012). Ten of the 13 known extant sites are characterized by montane conifer forest, with a canopy of sugar pine (Pinus lambertiana), white fir (Abies concolor), and ponderosa pine (Pinus ponderosa). The 3 remaining sites occur in Canyon Live Oak woodland, where the overstory is predominantly canyon live oak (Quercus chrysolepis) and California black oak (Quercus kelloggii). In contrast, historical localities along the Lower Kern River Canyon are in riparian corridors dominated by California sycamore (Platanus racemosa) and California buckeye (Aesculus califomica).

Reproduction

Terrestrial breeder. Available evidence indicates that oviposition occurs in June (Jockusch et al. 2012). This species lays eggs communally with clusters of over 100 eggs from multiple females in a single nest (Moss et al. 2025).
Terrestrial Habitats
Forest - HardwoodForest - Conifer
Palustrine Habitats
Riparian
Other Nations (1)
United StatesN1
ProvinceRankNative
CaliforniaS1Yes
Threat Assessments
ThreatScopeSeverityTiming
2 - Agriculture & aquacultureLarge - restrictedModerate - slightHigh (continuing)
2.3 - Livestock farming & ranchingLarge - restrictedModerate - slightHigh (continuing)
4 - Transportation & service corridorsRestricted (11-30%)Extreme - seriousHigh (continuing)
4.1 - Roads & railroadsRestricted (11-30%)Extreme - seriousHigh (continuing)
5 - Biological resource useRestricted (11-30%)Serious or 31-70% pop. declineHigh (continuing)
5.3 - Logging & wood harvestingRestricted (11-30%)Serious or 31-70% pop. declineHigh (continuing)
6 - Human intrusions & disturbanceRestricted (11-30%)Moderate - slightHigh (continuing)
6.1 - Recreational activitiesRestricted (11-30%)Moderate - slightHigh (continuing)
11 - Climate change & severe weatherPervasive (71-100%)UnknownHigh (continuing)
11.2 - DroughtsPervasive (71-100%)UnknownHigh (continuing)

Roadless Areas (4)
California (4)
AreaForestAcres
Greenhorn CreekSequoia National Forest28,226
Greenhorn CreekSequoia National Forest28,226
Mill CreekSequoia National Forest27,643
Mill CreekSequoia National Forest27,643
References (12)
  1. Crother, B. I. (editor). 2012. Scientific and standard English names of amphibians and reptiles of North America north of Mexico, with comments regarding confidence in our understanding. 7th edition. SSAR Herpetological Circular 39:1-92.
  2. Crother, B. I. (editor). 2017. Scientific and standard English names of amphibians and reptiles of North America north of Mexico, with comments regarding confidence in our understanding. 8th edition. SSAR Herpetological Circular 43:1-104. [Updates in SSAR North American Species Names Database at: https://ssarherps.org/cndb]
  3. Frost, D.R. 2020. Amphibian Species of the World: an Online Reference. Version 6.0. American Museum of Natural History, New York, USA. Online: http://research.amnh.org/herpetology/amphibia/index.html
  4. Jockusch, E. L., D. B. Wake, and K. P. Yanev. 1998. New species of slender salamanders, <i>Batrachoseps </i>(Amphibia: Plethodontidae), from the Sierra Nevada of California. Natural History Museum of Los Angeles County Contributions in Science 472:1-17.
  5. Jockusch, E. L., I. Martínez-Solano, R. W. Hansen, and D. B. Wake. 2012. Morphological and molecular diversification of slender salamanders (Caudata: Plethodontidae: <i>Batrachoseps</i>) in the southern Sierra Nevada of California with descriptions of two new species. Zootaxa 3190:1-30.
  6. Moss, C. D., R. W. Hansen, N. R. Van Gilder, and E. L. Jockusch. Distribution, natural history, and conservation status of the relictual salamander (<i>Batrachoseps relictus</i>). Northwestern Naturalist 105(1): 32-47.
  7. Thompson, R.C., A.N. Wright, and B.H. Shaffer. 2016. California Amphibian and Reptile Species of Special Concern. Relictual Salamander Species Account. Oakland, California: University of California Press. https://nrm.dfg.ca.gov/FileHandler.ashx?DocumentID=190354&inline (Accessed 22 June 2023).
  8. U.S. Fish and Wildlife Service (USFWS). 2015. Endangered and Threatened Wildlife and Plants; 90-Day Findings on 31 Petitions. Federal Register 80(126):37568-37579.
  9. U.S. Fish and Wildlife Service (USFWS). 2022. Endangered and Threatened Wildlife and Plants; 12-Month Finding for the Kern Plateau Salamander; Threatened Species Status With Section 4(d) Rule for the Kern Canyon Slender Salamander and Endangered Species Status for the Relictual Slender Salamander; Designation of Critical Habitat. Federal Register 87(200):63150-63199.
  10. U.S. Fish and Wildlife Service (USFWS). 2022. Species Status Assessment Report for the Relictual Slender Salamander (<i>Batrachoseps relictus</i>), Kern Canyon Slender Salamander (Batrachoseps simatus), and Kern Plateau Salamander (Batrachoseps robustus). U.S. Fish and Wildlife Service, Sacramento Field Office, Sacramento, CA. 91 pp. https://ecos.fws.gov/ServCat/DownloadFile/222488 (Accessed 21 June 2023).
  11. U.S. Fish and Wildlife Service (USFWS). 2025. Endangered and Threatened Wildlife and Plants; Review of Species That Are Candidates for Listing as Endangered or Threatened; Annual Notification of Findings on Resubmitted Petitions; Annual Description of Progress on Listing Actions. Candidate notice of review (CNOR). Federal Register 90(209):48912-48937.
  12. Wright, A.N., R.J. Hijmans, M.W. Schwartz, and H.B. Shaffer. 2013. California Amphibian and Reptile Species of Future Concern: Conservation and Climate Change. Final Report to the California Dept. of Fish and Wildlife, Nongame Wildlife Program, Task 12, Contract No. P0685904. https://nrm.dfg.ca.gov/FileHandler.ashx?DocumentID=141383&inline