Ambystoma tigrinum

(Green, 1825)

Eastern Tiger Salamander

G5Secure Found in 3 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Least concernIUCN
MediumThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.889738
Element CodeAAAAA01146
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassAmphibia
OrderCaudata
FamilyAmbystomatidae
GenusAmbystoma
COSEWICXT,E
Synonyms
Ambystoma tigrinum tigrinum(Green, 1825)
Other Common Names
Eastern Tiger Salamander (EN) Salamandra (ES) Salamandre tigrée de l'Est (FR) tiger salamander (EN)
Concept Reference
Collins, J. T. 1990. Standard common and current scientific names for North American amphibians and reptiles. 3rd ed. Society for the Study of Amphibians and Reptiles. Herpetological Circular No. 19. 41 pp.
Taxonomic Comments
This taxon is questionably distinct as a species separate from Ambystoma tigrinum. Shaffer and McKnight (1996) provided molecular phylogenetic data indicating that the eastern and western tiger salamanders should be regarded as distinct species and treated the western forms as subspecies of Ambystoma mavortium. Lannoo (2005) includes A. mavortium in A. tigrinum (Crother 2017). Johnson et al. (2011) also implied that A. mavortium is a synonym of A. tigrinum.
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-01-22
Change Date2001-10-02
Edition Date2010-01-25
Edition AuthorsHammerson, G.
Threat ImpactMedium
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences> 300
Range Extent Comments
See Church et al. (2003) for a map of the county distribution of the eastern tiger salamander.
Occurrences Comments
This species is represented by a large number of occurrences (subpopulations) and locations (as defined by IUCN).
Threat Impact Comments
Most remaining populations are exposed to low level threats from habitat loss and degradation, though quantitative information is lacking.

Local populations commonly incur massive mortality of adults on roads near breeding sites (Clevenger et al. 2001).
Ecology & Habitat

Description

Coloration geographically variable to an extreme, often mottled, blotched, or spotted; adults are stocky, with 11-14 (usually 12-13) costal grooves, a broad head, small eyes, and tubercles on the soles of the feet; pond-type larva (but lacks balancers), with three large pairs of gills, vomerine teeth in U-shaped pattern, and dorsal fin extending to region of axilla; adults usually are about 15-22 cm in total length (to about 34 cm) (Stebbins 1951, 1985; Behler and King 1979; Conant and Collins 1991).

Diagnostic Characteristics

The following pertains to metamorphosed adults. Differs from A. MACRODACTYLUM in lacking a distinct dorsal stripe or stripelike row of spots. Differs from A. GRACILE in having distinct dorsal markings and tubercles on the underside of the feet and by lacking parotoid glands and a glandular ridge on the tail. Differs from A. ANNULATUM in lacking a light grayish stripe along the lower side of the body and generally lacking narrow light bands across the body. Differs from A. MACULATUM and A. OPACUM in having large light blotches on the sides. Differs from A. TALPOIDEUM in having sharply defined spots and usually more than 11 costal grooves (vs. 10-11). Differs from all other North American AMBYSTOMA in having tubercles on the soles of the feet. Differs from plethodontid salamanders in lacking a nasolabial groove.

Habitat

Tiger salamanders can be found in virtually any habitat, providing there is a terrestrial substrate suitable for burrowing and a body of water nearby suitable for breeding. Terrestrial adults usually are underground, in self-made burrows or in those made by rodents, shrews, or other animals. In New York, adults on land used wooded areas and avoided grassy areas (Madison and Farrand 1998). At high elevations in the Rocky Mountains, metamorphosed adults commonly occur in ponds throughout the summer. Breeding occurs in a wide range of environments, ranging from clear mountain ponds to temporary, manure-polluted pools in the lowlands, generally in sites where predatory fishes are absent. In the mountains of western Colorado, tiger salamanders are associated with ponds that have silty bottoms, low alkalinity, and no fishes (Geraghty and Willey 1992). In the southeastern U.S., this species breeds in open, grassy, usually temporary, ponds (Jensen et al. 2008). Eggs are attached to submerged objects or pond bottoms.

Ecology

Drying of breeding pond may result in total reproductive failure in some years (Semlitsch 1983). May incur heavy egg predation by eastern newt in some areas. See Worthylake and Hovingh (1989) for information on recurrent mass mortality associated with bacterial infection in mountains of Utah; it was suggested that nitrogen augmentation due in part to sheep grazing may be involved.

In New York, frequent predation occurred in small mammal runways, probably by short-tailed shrews (Madison and Farrand 1998).

Reproduction

In general, breeding occurs in spring in the north and at high elevations, in winter in the southern U.S., in late winter/spring and/or summer in the Southwest, and in late winter-early spring in the mid-Atlantic states. Typically the female oviposits within two days after picking up a spermatophore. Individual female deposit up to 1,000 eggs. Eggs hatch in about 2-5 weeks, depending on the temperature. Larvae metamorphose in their first or second summer, or they may not metamorphose at all (become sexually mature as gilled larvae). Reproductive success may be highly dependent on seasonal patterns of rainfall and temperature (Mitchell 1991). In South Carolina, reproductive success varied greatly in different years; little or no recruitment occurred during drought periods (Pechmann et al. 1991). Breeding aggregations may include a few or up to several hundred adults.
Terrestrial Habitats
Forest - HardwoodForest - ConiferForest - MixedWoodland - HardwoodWoodland - ConiferWoodland - MixedShrubland/chaparralSavannaGrassland/herbaceousDesertCropland/hedgerowSuburban/orchard
Palustrine Habitats
TEMPORARY POOLHERBACEOUS WETLANDFORESTED WETLANDBog/fenRiparian
Other Nations (2)
CanadaN1
ProvinceRankNative
OntarioSXYes
ManitobaS3Yes
United StatesN5
ProvinceRankNative
Navajo NationS5Yes
MissouriS3Yes
IowaS5Yes
WashingtonS3Yes
OhioS4Yes
WisconsinS4Yes
IndianaS4Yes
New MexicoS5Yes
MontanaS4Yes
VirginiaS1Yes
GeorgiaS3Yes
KansasS5Yes
IllinoisS5Yes
UtahS4Yes
NevadaSNANo
North CarolinaS2Yes
MarylandS1Yes
KentuckyS5Yes
LouisianaS1Yes
North DakotaSNRYes
South CarolinaS2Yes
PennsylvaniaSXYes
TexasS3Yes
South DakotaS5Yes
MinnesotaS5Yes
New JerseyS1Yes
TennesseeS5Yes
ArkansasS3Yes
OregonS2Yes
DelawareS1Yes
AlabamaS3Yes
New YorkS1Yes
MichiganS3Yes
NebraskaSNRYes
FloridaS3Yes
OklahomaSNRYes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentHigh (continuing)
1.1 - Housing & urban areasHigh (continuing)
1.2 - Commercial & industrial areasHigh (continuing)
2 - Agriculture & aquacultureHigh (continuing)
2.1 - Annual & perennial non-timber cropsHigh (continuing)
4 - Transportation & service corridorsHigh (continuing)
4.1 - Roads & railroadsHigh (continuing)
5 - Biological resource useHigh (continuing)
5.3 - Logging & wood harvestingHigh (continuing)
7 - Natural system modificationsHigh (continuing)
7.2 - Dams & water management/useHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesHigh (continuing)
8.1 - Invasive non-native/alien species/diseasesHigh (continuing)

Roadless Areas (3)
Tennessee (1)
AreaForestAcres
Bald MountainCherokee National Forest11,743
Virginia (2)
AreaForestAcres
Kelley MountainGeorge Washington National Forest7,590
Three RidgesGeorge Washington National Forest4,745
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