Desmognathus balsameus
Pyron and Beamer, 2022
Great Balsams Mountain Dusky Salamander
G4Apparently SecureGlobal Rank
LowThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.1322045
Element CodeAAAAD03300
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
Endemicendemic to a single state or province
KingdomAnimalia
PhylumCraniata
ClassAmphibia
OrderCaudata
FamilyPlethodontidae
GenusDesmognathus
Concept ReferencePyron, R. A., and D. A. Beamer. 2022e. Systematics of the Ocoee Salamander (Plethodontidae: Desmognathus ocoee), with description of two new species from the southern Blue Ridge Mountains. Zootaxa 5190: 207-240 (https://doi.org/10.11646/zootaxa.5190.2.3).
Taxonomic CommentsPyron and Beamer (2022) conducted molecular and morphometric studies and recognized five species within the Desmognathus oconee group: D. apalachicolae, D. adatsihi, D. balsameus, the resurrected D. perlapsus, and D. ocoee. Desmognathus balsameus comprises the ocoee B lineage defined by Kozak et al. (2005), Beamer and Lamb (2020), and Pyron et al. (2020, 2022) (Pyron et al. 2022).
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2024-09-12
Change Date2024-09-12
Edition Date2024-09-12
Edition AuthorsGundy, R. L. (2024)
Threat ImpactLow
Range Extent1000-5000 square km (about 400-2000 square miles)
Number of Occurrences21 - 80
Rank ReasonsThis species has a very limited range in the southeastern United States. It is widespread within the range, nearly all occurrences are protected, and no major threats are known at this time.
Range Extent CommentsThis species is found at elevations above ~1000 m in the southeastern United States in the Great Balsam Mountains of western North Carolina, primarily in Haywood, Jackson, and Transylvania Counties, but possibly extending into western Buncombe and Henderson Counties (Pyron and Beamer 2022). Using iNaturalist (2024) records, range extent is estimated to be 1,548 km².
Occurrences CommentsApplying a 3 km separation distance to iNaturalist (2024) records, there are approximately 22 occurrences.
Threat Impact CommentsNo major threats are known at this time (Pyron and Beamer 2022). Logging activities in national forests have the potential to degrade habitat and reduce populations (Petranka et al. 1993).
Ecology & Habitat
Diagnostic Characteristics
This species is small (~19–47mm SVL), with a tail shorter than the body (up to ~90% SVL) that is round in cross section along its length. It is differentiated from D. santeetlah by the lack of any keeling on the dorsal surface of the tail (vs. presence in santeetlah), which is the only species in its range with which it is likely to be confused. D. balsameus exhibits a wide range of color patterns, with most individuals possessing a partially or mostly complete dorsal stripe with wavy or undulating edges (vs. usually straight in D. adatsihi), formed from the irregular invasion of melanophore patches between the remnants of paired larval spots, with a brownish, yellowish, or reddish coloration against a darker lateral ground color, and a general lack of any regular patterning along the mid-dorsal line. Ontogenetic darkening seems to be relatively more common and at smaller sizes than in related species, with individuals as small as ~33mm SVL exhibiting overall dark brown to blackish coloration obscuring the dorsal pattern (Pyron and Beamer 2022).
Habitat
This species is found above 1000 m elevation in the Great Balsam Mountains in montane forests with cool, clear-flowing headwater streams and seepages (Pyron and Beamer 2022, Petranka et al. 2024). The species can be abundant on wet rock faces (Huheey and Brandon 1973). It is more terrestrial at higher elevations and is a characteristic inhabitant of the floor of spruce-fir forests (Petranka 1998, Pyron and Beamer 2022). Individuals frequently climb plants on rainy nights (Petranka 1998). Eggs are laid in wet rock crevices or under rocks, logs, or moss in seepage areas or near small streams, usually at or slightly above the water surface (Pope 1924, Huheey and Brandon 1973, Forester 1979, Petranka 1998).
Ecology
Population density on rock faces was 11-22 adults and 7-19 juveniles per square meter (Huheey and Brandon 1973). Rock-face densities generally exceed those of streamside habitats (Petranka 1998). Individuals in a rock-face population averaged 40-45 cm between successive captures (Huheey and Brandon 1973).
Reproduction
Mating occurs in spring and late summer-fall (Huheey and Brandon 1973, Forester 1979). Egg laying occurs in July and early August or as late as early September (Huheey and Brandon 1973). Females attend their clutches through hatching, and this may contribute significantly to nesting success (Forester 1979, Petranka 1998). Multiple females often nest close together (Pope 1924, Forester 1979). The larval period lasts at least 9 months in rock face populations (Huheey and Brandon 1973).
Terrestrial HabitatsForest - HardwoodForest - ConiferForest - MixedBare rock/talus/screeCliff
Palustrine HabitatsBog/fenRiparian
Other Nations (1)
United StatesNNR
| Province | Rank | Native |
|---|
| North Carolina | SNR | Yes |
| Indiana | SNR | Yes |
References (12)
- Beamer, D. A., and T. Lamb. 2020. Towards rectifying limitations on species delineation in dusky salamanders (<i>Desmognathus</i>: Plethodontidae): An ecoregion-drainage sampling grid reveals additional cryptic clades. Zootaxa 4734: 1-61.
- Forester, D. C. 1979. The adaptiveness of parental care in <i>Desmognathus</i><i> ochrophaeus</i> (Urodela: Plethodontidae). Copeia 1979: 332-341.
- Huheey, J. E., and R. A. Brandon. 1973. Rock-face populations of the mountain salamander, <i>Desmognathus ochrophaeus</i>, in North Carolina. Ecological Monographs 43: 59-77.
- iNaturalist. 2024. Online. Available: https://www.inaturalist.org (accessed 2024).
- Kozak, K. H., A. Larson, R. M. Bonett, and L. J. Harmon. 2005. Phylogenetic analysis of ecomorphological divergence community structure, and diversification rates in Dusky Salamanders (Plethodontidae: <i>Desmognathus</i>). Evolution 59:2000-2016.
- Peterman, W. E., J. A. Crawford, and R. D. Semlitsch. 2008. Productivity and significance of headwater streams: population structure and biomass of the black-bellied salamander (<i>Desmognathus quadramaculatus</i>). Freshwater Biology 53: 347–357.
- Petranka, J. W. 1998. Salamanders of the United States and Canada. Smithsonian Institution Press, Washington, D.C.
- Petranka, J. W., M. E. Eldridge, and K. E. Haley. 1993. Effects of timber harvesting on southern Appalachian salamanders. Conservation Biology 7(2): 363-370.
- Petranka, J. W., S. Hall, and T. Howard, with contributions from H. LeGrand. 2024. Amphibians of North Carolina [Internet]. Raleigh (NC): North Carolina Biodiversity Project and North Carolina State Parks. Available from https://auth1.dpr.ncparks.gov/amphibians/index.php
- Pope, C. H. 1924. Notes on North Carolina salamanders, with especial reference to the egg-laying habits of <i>Leurognathus </i>and <i>Desmognathus</i>. American Museum Novitates 153:1-15.
- Pyron, R. A., and D. A. Beamer. 2022e. Systematics of the Ocoee Salamander (Plethodontidae: <i>Desmognathus ocoee</i>), with description of two new species from the southern Blue Ridge Mountains. Zootaxa 5190: 207-240 (https://doi.org/10.11646/zootaxa.5190.2.3).
- Pyron, R. A., K. A. O'Connell, E. M. Lemmon, and A. R. Lemmon. 2020. Phylogenomic data reveal reticulation and incongruence among mitochondrial candidate species in Dusky Salamanders (<i>Desmognathus</i>). Molecular Phylogenetics and Evolution 146(106751):1-13.