Ambystoma maculatum

(Shaw, 1802)

Spotted Salamander

G5Secure Found in 71 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Least concernIUCN
UnknownThreat Impact
Spotted Salamander (Ambystoma maculatum). Photo by John Abrams, CC BY 4.0, via iNaturalist.
John Abrams, CC BY 4.0
Spotted Salamander (Ambystoma maculatum). Photo by Dominic, CC BY 4.0, via iNaturalist.
Dominic, CC BY 4.0
Spotted Salamander (Ambystoma maculatum). Photo by Anna Hess, CC BY 4.0, via iNaturalist.
Anna Hess, CC BY 4.0
Spotted Salamander (Ambystoma maculatum). Photo by JD Flores, CC0 1.0, via iNaturalist.
JD Flores, CC0 1.0
Identity
Unique IDELEMENT_GLOBAL.2.104612
Element CodeAAAAA01090
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
Other Common Names
Salamandre maculée (FR) spotted salamander (EN) Yellow-spotted Salamander (EN)
Concept Reference
Frost, D. R. 1985. Amphibian species of the world. A taxonomic and geographical reference. Allen Press, Inc., and The Association of Systematics Collections, Lawrence, Kansas. v + 732 pp.
Taxonomic Comments
See Kraus (1988), Shaffer et al. (1991), and Jones et al. (1993) for phylogenetic analyses of North American Ambystoma.
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-01-22
Change Date2002-07-09
Edition Date2010-01-25
Edition AuthorsHammerson, G.
Threat ImpactUnknown
Range Extent200,000 to >2,500,000 square km (about 80,000 to >1,000,000 square miles)
Number of Occurrences> 300
Range Extent Comments
Range extends throughout most of the eastern United States (except Florida) and adjacent southern Canada; west to eastern Iowa and eastern Texas (Conant and Collins 1991).
Occurrences Comments
Throughout the range, occurrences are many and/or large.
Threat Impact Comments
Threats to local populations include intensive timber harvesting practices that reduce canopy closure, understory vegetation, uncompacted forest litter, or coarse woody debris (moderately to well-decayed) in areas surrounding breeding sites (deMaynadier and Hunter 1999). Dispersing juveniles tend to avoid open canopy habitat, so deforestation and fragmentation likely reduce dispersal rates between local populations and could negatively impact population persistence in altered landscapes (Rothermal and Semlitsch 2002). Negative impacts of intensive timber harvesting extend at least 25-35 m into uncut forest (deMaynadier and Hunter 1998).
Many populations are becoming increasing isolated as deforestation and loss of vernal pools reduce gene flow among demes (Petranka 1998). This may result in inbreeding depression and reduce the probability of reestablishment of extirpated populations.
Local populations may be heavily impacted by excessive mortality of adults caused by vehicles on roads near breeding sites. Roads negatively impact salamander abundance in roadside habitat and may serve as partial barriers to movement (deMaynadier and Hunter 2000).
Embryo mortality generally decreases as pH deceases below 6.0, though in some areas successful reproduction has occurred at a relatively low pH (Cook 1983, Blem and Blem 1989). In central Pennsylvania, low pH was associated with deleterious sublethal effects on larvae (Sadinski and Dunson 1992).
High concentrations of various chemical elements, unfavorable temperatures, or low oxygen content may result in reproductive failure; see Blem and Blem (1991) and Albers and Prouty (1987). Deicing salts that contaminate roadside vernal pools result in reduced embryonic survival (Turtle 2000).
Ecology & Habitat

Description

Spotted salamanders have smooth skin with vertical grooves on each side of the torso, a broad head, and small eyes. The upper side is black with numerous rounded yellow or orange spots. The belly is slate gray. Maximum total length is about 9.8 inches (25 cm). Large larvae have large external gills, a reticulated pattern on the upper surface, small dark spots on the lower sides, and a pale belly; they lack dark stippling on the throat. Egg masses are up to several inches in diameter, have clear to milky or green jelly, and contain usually several dozen eggs.

Habitat

Spotted salamanders inhabit hardwood and mixed forests, in the vicinity of swamps and vernal pools. They are usually underground or under soil surface objects except during the breeding period. Logs, stumps, and mammal burrows provide important cover (Faccio 2003). In New York, distribution apparently is influenced by soil pH (Wyman 1988).

Eggs usually are attached to submerged stems or other objects in vernal pools and semipermanent or permanent ponds in or adjacent to forest. In many areas, the species breeds mainly in ponds inaccessible to predatory fishes; however on the Atlantic Coastal Plain of the southeastern United States, spotted salamanders breed in sloughs or backwater lowland areas along streams that frequently contain or are easily colonized by predatory fishes that opportunistically feed on amphibian larvae (Semlitsch 1988). Eggs may be laid in ponds when they are ice-covered if salamanders already are present in the pond (States et al. 1988).

Ecology

Larvae may be preyed on by larval A. opacum where the two occur together. Predation on larvae by fishes may prohibit successful reproduction (Ireland 1989). In a Massachusetts pond, survival to metamorphosis was 3.1% for 10,000+ embryos in a year when pond did not dry; up to 13% survival recorded in other studies (see States et al. 1988). In West Virginia, larvae of the caddisfly Banksiola dossuaria preyed on embryos (Stout et al. 1992). In Pennsylvania, larvae of the caddisfly Ptilostomis postica sometimes preyed heavily on embryos (Rowe et al. 1994).

See Semlitsch (1988) for information on factors affecting ecological distribution in southeastern U.S.

The egg masses of spotted salamanders sometimes contain green algae that use the carbon dioxide produced by the embryos and in turn produce oxygen that the salamander embryos can use.

Reproduction

Rain and warming temperatures stimulate migrations to breeding ponds in winter or early spring (Grace and Church 2003). Migrations to breeding sites occur in March-April in the northern part of the range, mainly December-February in the south. In eastern Missouri, migration to ponds occurred after the first week of February on all days when mean 3-day temperature was at least 5.5 C and precipitation at least 4 mm (Sexton et al. 1990). After arriving in the breeding pools, females pick up sperm from the spermatophores that males deposit on the pool bottom. Soon thereafter females attach masses of eggs to submerged stems or other submerged objects. Individual females deposit up to 250 eggs (average <100); eggs of an individual females may be laid in one large mass or divided among several masses of about 50-90 eggs. Hundreds of females may deposit eggs in a single pool, and the egg masses of different females often exhibit an aggregated dispersion pattern. Larvae hatch in 1-2 months.In a pond in Ohio, hatching rate over 4 years was 60-72%, and the number of larvae that hatched ranged from 232,000 to 527,000 (Brodman, 1995, J. Herpetol. 29:111-113). Larvae metamorphose in 2-4 months or sometimes overwinter in the pond. In eastern Missouri, metamorphosis occurred mainly by October in some years, in spring after overwintering in other years (Phillips 1992). In Massachusetts, mean time from hatching to exit from pond was 98 days (States et al. 1988). Newly metamorphosed individuals live on land for a few years before returning to water to breed (usually in their natal pool).

In Quebec, most individuals caught in temporary ponds in spring were between 2 and 18 years old; most females were mature by the age 7 years at SVL greater than 78 mm whereas many males reached maturity between the ages of 2 and 6 years at SVL greater than 63 mm (Flageole and Leclair 1992).

Many individuals usually breed in a single pool (e.g., in eastern Massachusetts, 196 males and 132 females entered a pond with a surface area of about 30 square meters; 118 egg masses were found (States et al. 1988). Harris (Copeia 1980:719-722) found 237 egg masses in one pond.
Terrestrial Habitats
Forest - HardwoodForest - MixedWoodland - HardwoodWoodland - MixedBare rock/talus/scree
Palustrine Habitats
TEMPORARY POOLSCRUB-SHRUB WETLANDFORESTED WETLANDRiparian
Other Nations (2)
CanadaN5
ProvinceRankNative
QuebecS5Yes
New BrunswickS5Yes
OntarioS4Yes
Prince Edward IslandS5Yes
Nova ScotiaS5Yes
United StatesN5
ProvinceRankNative
PennsylvaniaS4Yes
New HampshireS5Yes
MissouriS5Yes
LouisianaS5Yes
New JerseyS3Yes
Rhode IslandS4Yes
West VirginiaS5Yes
OhioSNRYes
IllinoisS4Yes
ArkansasS5Yes
WisconsinS4Yes
ConnecticutS5Yes
VirginiaS5Yes
MississippiS5Yes
TennesseeS5Yes
MinnesotaS3Yes
MassachusettsS5Yes
North CarolinaS5Yes
IndianaS4Yes
KentuckyS5Yes
TexasS4Yes
MaineS5Yes
District of ColumbiaS4Yes
AlabamaS5Yes
VermontS5Yes
MarylandS5Yes
MichiganS4Yes
DelawareS2Yes
OklahomaS3Yes
GeorgiaS5Yes
South CarolinaS5Yes
New YorkS5Yes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentHigh (continuing)
1.1 - Housing & urban areasHigh (continuing)
4 - Transportation & service corridorsHigh (continuing)
4.1 - Roads & railroadsHigh (continuing)
5 - Biological resource useHigh (continuing)
5.3 - Logging & wood harvestingHigh (continuing)
9 - PollutionHigh (continuing)
9.5 - Air-borne pollutantsHigh (continuing)

Roadless Areas (71)
Alabama (1)
AreaForestAcres
Blue MountainTalladega National Forest4,986
Arkansas (5)
AreaForestAcres
Blue MountainOuachita National Forest9,755
Devils CanyonOzark-St. Francis National Forest1,877
East ForkOzark-St. Francis National Forest13,037
Gee CreekOzark-St. Francis National Forest7,957
Indian CreekOzark-St. Francis National Forest7,855
Michigan (1)
AreaForestAcres
Bear SwampHuron-Manistee National Forest3,915
New Hampshire (10)
AreaForestAcres
Carr MountainWhite Mountain National Forest17,110
Dartmouth RangeWhite Mountain National Forest9,233
Great Gulf Ext.White Mountain National Forest15,110
KilkennyWhite Mountain National Forest28,766
Kinsman MountainWhite Mountain National Forest8,999
PemigewassetWhite Mountain National Forest32,255
Pemigewasset ExtWhite Mountain National Forest15,840
Presidential - Dry River ExtWhite Mountain National Forest10,555
Sandwich RangeWhite Mountain National Forest16,797
Wild RiverWhite Mountain National Forest46,878
North Carolina (7)
AreaForestAcres
BearwallowPisgah National Forest4,113
Dobson KnobPisgah National Forest6,111
Linville Gorge AdditionPisgah National Forest2,809
Little Indian (addition)Nantahala National Forest640
Lost CovePisgah National Forest5,944
South Mills RiverPisgah National Forest8,588
Wilson CreekPisgah National Forest4,863
Pennsylvania (3)
AreaForestAcres
Allegheny FrontAllegheny National Forest7,430
Clarion RiverAllegheny National Forest3,821
Tracy RidgeAllegheny National Forest9,034
Tennessee (5)
AreaForestAcres
Bald MountainCherokee National Forest11,743
Big Laurel Branch AdditionCherokee National Forest5,577
Flint Mill GapCherokee National Forest9,494
Sampson Mountain AdditionCherokee National Forest3,064
Stone MountainCherokee National Forest5,367
Vermont (5)
AreaForestAcres
Bread LoafGreen Mountain and Finger Lakes National Forests1,768
Devil's Den 09083Green Mountain and Finger Lakes National Forests9,169
Griffith Lake 09084Green Mountain and Finger Lakes National Forests1,833
Lye Brook Addition 09085Green Mountain and Finger Lakes National Forests1,111
Wilder Mountain 09082Green Mountain and Finger Lakes National Forests8,759
Virginia (20)
AreaForestAcres
Adams PeakGeorge Washington National Forest7,135
Beards MountainGeorge Washington National Forest7,505
Broad RunJefferson National Forest10,971
Brush MountainJefferson National Forest6,002
Crawford MountainGeorge Washington National Forest9,892
Gum RunGeorge Washington National Forest12,620
Hoop HoleJefferson National Forest4,652
Kelley MountainGeorge Washington National Forest7,590
Laurel ForkGeorge Washington National Forest9,967
Little RiverGeorge Washington National Forest27,292
North MountainJefferson National Forest8,377
Northern MassanuttenGeorge Washington National Forest9,444
Oak KnobGeorge Washington National Forest10,882
Price MountainJefferson National Forest9,119
Ramseys Draft AdditionGeorge Washington National Forest12,781
Saint Marys AdditionGeorge Washington National Forest1,454
Seng MountainJefferson National Forest6,428
The PriestGeorge Washington National Forest5,737
Three RidgesGeorge Washington National Forest4,745
Three SistersGeorge Washington National Forest8,149
West Virginia (12)
AreaForestAcres
Canaan LoopMonongahela National Forest7,867
Cranberry AdditionMonongahela National Forest11,123
Cranberry Glades Botanical AreaMonongahela National Forest785
Dolly Sods Roaring PlainMonongahela National Forest13,392
East Fork Of GreenbrierMonongahela National Forest7,167
Falls Of Hills CreekMonongahela National Forest6,925
Gauley MountainMonongahela National Forest13,285
Glady ForkMonongahela National Forest3,239
Laurel ForkMonongahela National Forest1,172
Little MountainMonongahela National Forest8,172
Mcgowan MountainMonongahela National Forest10,504
Seneca CreekMonongahela National Forest22,287
Wisconsin (2)
AreaForestAcres
09011 - Flynn Lake Study AreaChequamegon-Nicolet National Forest5,951
09154 - St. Peters DomeChequamegon-Nicolet National Forest4,002
References (43)
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