|Scientific Name:||Ambystoma tigrinum|
|Species Authority:||(Green, 1825)|
Amblystoma conspersum Cope, 1859
Amblystoma copeianum Hay, 1885
Amblystoma obscurum Baird, 1868
Amblystoma xiphias Cope, 1868
Ambystoma bicolor Hallowell, 1858
Ambystoma episcopus Baird, 1850
Ambystoma ingens (Green, 1831)
Ambystoma tigrina (Green, 1825)
Heterotriton ingens (Green, 1831)
Salamandra tigrina Green, 1825
Salamandra ingens Green, 1831
Triton ingens (Green, 1831)
Triton tigrinus (Green, 1825)
|Taxonomic Notes:||Populations east of the Apalachicola River Basin and Appalachian Mountains have been diverging from western populations (the form mavortium) for approximately 1 million years. Collectively, eastern populations might constitute a distinct species (Church et al. 2003).|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Assessor(s):||Hammerson, G.A., Shaffer, H.B., Church, D., Parra-Olea, G. & Wake, D.|
|Reviewer(s):||Stuart, S.N., Chanson, J.S., Cox, N.A. & Young, B.E.|
Listed as Least Concern in view of its wide distribution, tolerance of a broad range of habitats, presumed large population, and because it is unlikely to be declining fast enough to qualify for listing in a more threatened category.
|Range Description:||This species can be found throughout much of the USA, southern Canada to northern Mexico in the Sierra Madre Occidental. It is absent from most of the Great Basin, New England, and the Appalachian mountains. From sea level to around 3,660m asl in the Rocky mountains. Introduced populations occur in central California [not mapped here], where they hybridise with A. californiense (Riley et al., 2003); in the western U.S. populations are sometimes moved in association with the fish bait industry. In Mexico, the species apparently has a limited distribution in the northwest, where its interactions with A. velasci require additional investigation.|
Native:Canada; Mexico; United States
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||This is one of the most abundant Ambystoma species. The total adult population size is unknown but surely exceeds 1,000,000. Tiger salamanders occur throughout their historical range in the Rocky Mountains and Great Plains of Colorado and adjacent states. They remain easy to find and locally abundant in suitable habitat statewide. Ponds often contain up to several thousand larvae. Recent surveys found no evidence of significant declines in distribution or abundance (Corn, Stoltzberg, and Bury 1989; Hammerson 1989a, 1992; Corn, Jennings, and Muths 1997). In the Rocky Mountains, a local decline in numbers over several years, reported by Harte and Hoffman (1989), turned out to be a temporary fluctuation from which the population subsequently recovered (Wissinger and Whiteman 1992). Hovingh (1986) reported that tiger salamanders remain quite common in aquatic systems in glaciated portions of the Uinta Mountains in northeastern Utah. The widespread creation of small, fishless artificial bodies of water has provided much suitable habitat where previously there were little, and these salamanders have been quick to colonize it (Norris 1973; pers. obs.). Populations east of the Appalachians are highly patchy in distribution with several local extirpations having been documented over the past 20 years. Remaining eastern populations are small in size and several are in decline (Church 2003, Semlitsch et al. 1996, Zappalorti 1994). In Mexico this species is generally not uncommon.|
|Habitat and Ecology:||It 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. Eggs are attached to submerged objects or pond bottom. Breeds in a wide range of environments, ranging from clear mountain ponds to temporary, manure-polluted pools in the lowlands. Always breeds in sites where predatory fishes are absent. In the mountains of western Colorado, associated with ponds that have silty bottoms, low alkalinity, and no fishes (Geraghty and Willey 1992). In the southeastern U.S., requires relatively flatwoods ponds that do not contain fishes.|
In Mexico it has been observed that in some localities this species can resist conditions of pollution and other kinds of alteration of the environment. Many mountain lakes formerly inhabited by tiger salamanders now have few or none of these amphibians due to the stocking of trout, which easily consume and deplete the larval populations (e.g., Blair 1951; pers. obs.). Geraghty and Willey (1992) found that fish absence was the most important factor influencing tiger salamander presence in Gunnison County and vicinity, and Corn, Jennings, and Muths (1997) reported that trout and tiger salamanders rarely occur together in Rocky Mountain National Park. Trout and tiger salamanders do occasionally coexist in some lakes (Dartt 1879; Blair 1951), but only where vegetated shallows provide habitat not easily accessible to the fishes. Some have suggested that breeding-pond acidification related to atmospheric pollution might cause periodic failure of tiger salamander reproduction in the mountains of Colorado (Harte and Hoffman 1989, 1994). Low pH, even if not fatal to salamander larvae, might result in reduced growth rates and ultimately could diminish salamander populations through decreased survival or feeding success (Kiesecker 1996). However, recent water chemistry data, together with information on acid tolerances of salamander larvae, suggest that eggs and embryos in the wild do not experience harmful levels of acidification (Corn, Stoltzenburg, and Bury 1989; Corn and Vertucci 1992; Wissinger and Whiteman 1992; Vertucci and Corn 1994). Under certain conditions, larval populations might be vulnerable to bacterial infections associated with livestock grazing. In the mountains of Utah, Worthylake and Hovingh (1989) observed recurrent mass mortality of larvae associated a bacterial infection and suggested that increased nitrogen levels due in part to sheep grazing might have been involved. Bryant (1995) observed a mass mortality event in the summer of 1993 that appeared to be associated with an opportunistically pathogenic bacterium. In Arizona, similar die-offs, apparently associated with bacterial pathogens, have been reported (Pfennig, Loeb, and Collins 1991). Cannibal morphs seemed particularly vulnerable, probably due to their feeding on diseased larvae. Again, fecal contamination of ponds by introduced livestock was suggested as a possible cause of the fatal outbreaks. In contrast to these reports, larvae sometimes do thrive in large numbers in manure-laden ponds in Colorado (Hammerson 1999). Nevertheless, die-offs of larvae, apparently associated with pathogenic bacteria, have been observed in Colorado (Hammerson 1999). Populations in the southeastern USA have been detrimentally affected by deforestation and loss of wetland habitats and appear to be declining (Petranka 1998). Population viability analyses of populations in the eastern USA have shown that demographically isolated populations are highly susceptible to extinction, particularly under conditions of high weather variability (Church 2003).
This species is sometimes found in the international pet trade but at levels that do not currently constitute a major threat.
|Conservation Actions:||Needed measures include basic habitat protection and policies/regulations that discourage/prohibit the introduction of predatory fishes into habitats where they are not native. Further research on phylogeographic patterns and taxonomic status of major population segments is needed. This species is protected under the category Pr (Special protection) by the Government of Mexico.|
Allison, L.J., Brunkow, P.E. and Collins, J.P. 1994. Opportunistic breeding after summer rains by Arizona tiger salamanders. Great Basin Naturalist: 376-379.
Bartlett, R.D. and Bartlett, P.P. 1999. A Field Guide to Florida Reptiles and Amphibians. Gulf Publishing Company, Houston, TX, USA.
Baxter, G.T. and Stone, M.D. 1985. Amphibians and Reptiles of Wyoming. Second Edition. Wyoming Game and Fish Department, Wyoming.
Bishop, S.C. 1941. The salamanders of New York. New York State Museum Bulletin: 1-365.
Blackburn, L., Nanjappa, P. and Lannoo, M.J. 2001. An Atlas of the Distribution of U.S. Amphibians. Ball State University, Muncie, IN, USA.
Church, D.R. 2003. Population ecology of Ambystoma tigrinum (Caudata: Ambystomatidae) and occupancy dynamics in an Appalacian pond-breeding amphibian assemblage. Ph.D. Dissertation, University of Virginia.
Church, S.A., Kraus, J.M., Mitchell, J.C. Church, D.R. and Taylor, D.R. 2003. Evidence for multiple pleistocene refugia in the postglacial expansion of the eastern tiger salamander, Ambystoma tigrinum tigrinum. Evolution: 372-383.
Clevenger, A.P., McIvor, M., McIvor, D., Chruszcz, B. and Gunson, K. 2001. Tiger salamander, Ambystoma tigrinum, movements and mortality on the Trans-Canada Highway in southwestern Alberta. Canadian Field-Naturalist: 199-204.
Collins, J.P., Jones, T.R. and Berna, H.J. 1988. Conserving genetically distinctive populations: the case of the Huachuca tiger salamander (Ambystoma tigrinum stebbinsi Lowe). In: Szaro, R., Severson, K. and Patton, D. (eds), Management of Amphibians, Reptiles and Small Mammals in North America, pp. 45-53. USDA For. Serv., Gen. Tech. Rep. RM-166.
Collins, J.P., Mitton, J.B. and Pierce, B.A. 1980. Ambystoma tigrinum: a multispecies conglomerate? Copeia: 938-941.
Collins, J.T. 1993. Amphibians and reptiles in Kansas. Third edition, revised. University of Kansas Museum of Natural History, Public Education Series No. 13.
Conant, R. and Collins, J.T. 1991. A Field Guide to Reptiles and Amphibians: Eastern and Central North America. Third Edition. Houghton Mifflin Company, Boston, Massachusetts.
Corkran, C.C. and Thoms, C. 1996. Amphibians of Oregon, Washington and British Columbia. Lone Pine Publishing, Edmonton, Alberta.
Corn, P.S. and Vertucci, F.A. 1992. Descriptive risk assessment of the effects of acidic deposition on Rocky Mountain amphibians. Journal of Herpetology: 361-369.
Degenhardt, W.G., Painter, C.W. and Price, A.H. 1996. Amphibians and Reptiles of New Mexico. University of New Mexico Press, Albuquerque, New Mexico.
Fernandez, P.J. and Collins, J.P. 1988. Effect of environment and ontogeny on color pattern variation in Arizona tiger salamanders (Ambystoma tigrinum nebulosum Hallowell). Copeia: 928-938.
Frost, D.R. 1985. Amphibian Species of the World: A Taxonomic and Geographic Reference. Allen Press and the Association of Systematic Collections, Lawrence, Kansas.
Gehlbach, F.R. 1967. Ambystoma tigrinum. Catalogue of American Amphibians and Reptiles: 1-4.
Geraghty, C. and Willey, R. 1992. Current habitat status of and anthropogenic impacts on the tiger salamander, Ambystoma tigrinum nebulosum. Abstract, 6th Annual Meeting of the Society for Conservation Biology: 61.
Hammerson, G.A. 1982. Amphibians and Reptiles in Colorado. Colorado Division of Wildlife, Denver, Denver.
Hammerson, G.A. 1999. Amphibians and reptiles in Colorado. Second edition. University Press of Colorado, Boulder.
Harding, J.H. 1997. Amphibians and Reptiles of the Great Lakes Region. University of Michigan Press, Ann Arbor, Michigan.
Harte, J. and Hoffman, E. 1989. Possible effects of acidic deposition on a Rocky Mountain population of the tiger salamander Ambystoma tigrinum. Conservation Biology: 149-158.
Irschick, D.J. and Shaffer, H.B. 1997. The polytypic species revisited: morphological differentiation among tiger salamanders (Ambystoma tigrinum) (Amphibia: Caudata). Herpetologica: 30-49.
IUCN. 2008. 2008 IUCN Red List of Threatened Species. Available at: http://www.iucnredlist.org. (Accessed: 5 October 2008).
Johnson, T.R. 2000. The Amphibians and Reptiles of Missouri. Second Edition. Missouri Department of Conservation, Jefferson City.
Jones, T.R. and Collins, J.P. 1992. Analysis of a hybrid zone between subspecies of the tiger salamander (Ambystoma tigrinum) in central New Mexico. Journal of Evolutionary Biology: 375-402.
Jones, T.R., Collins, J.P., Kocher, T.D. and Mitton, J.B. 1988. Systematic status and distribution of Ambystoma tigrinum stebbinsi Lowe (Amphibia: Caudata). Copeia: 621-635.
Jones, T.R., Kluge, A.G. and Wolf, A.J. 1993. When theories and methodologies clash: a phylogenetic reanalysis of the North American ambystomatid salamanders (Caudata: Ambystomatidae). Systematic Biology: 92-102.
Jones, T.R., Routman, E.J., Begun, D.J. and Collins, J.P. 1995. Ancestry of an isolated subspecies of salamander, Ambystoma tigrinum stebbinsi Lowe: the evolutionary significance of hybridization. Molecular Phylogenetics and Evolution: 194-202.
Kraus, F. 1985. A new unisexual salamander from Ohio. University of Michigan Museum of Zoology, Occasional Papers: 1-24.
Kraus, F. 1988. An empirical evaluation of the use of the ontogeny polarization criterion in phylogenetic inference. Systematic Zoology: 106-141.
Kraus, F., Ducey, P.K., Moler, P. and Miyamoto, M.M. 1991. Two new triparental unisexual Ambystoma from Ohio and Michigan. Herpetologica: 429-439.
Larson, K.L., Duffy, W., Johnson, E., Donovan, M.F. and Lannoo, M.J. 1999. Paedocannibal morph barred tiger salamanders (Ambystoma tigrinum mavortium) from eastern South Dakota. American Midland Naturalist: 124-139.
Leonard, W.P., Brown, H.A., Jones, L.L.C., McAllister, K.R. and Storm, R.M. 1993. Amphibians of Washington and Oregon. Seattle Audubon Society, Seattle, Washington.
Lowcock, L.A., Licht, L.E. and Bogart, J.P. 1987. Nomenclature in hybrid complexes of Ambystoma (Urodela: Ambystomatidae): no case for the erection of hybrid "species". Systematic Zoology: 328-336.
Madison, D.M. and Farrand, L. 1998. Habitat use during breeding and emigration in radio-implanted tiger salamanders, Ambystoma tigrinum. Copeia: 402-410.
Martof, B.S., Palmer, W.M., Bailey, J.R. and Harrison III, J.R. 1980. Amphibians and Reptiles of the Carolinas and Virginia. University of North Carolina Press, Chapel Hill, North Carolina.
Minton Jr, S.A. 1972. Amphibians and Reptiles of Indiana. Indiana Academy of Science Monographs 3, Indianapolis, IN, USA.
Minton Jr, S.A. 2001. Amphibians and Reptiles of Indiana, revised second edition. Indiana Academy of Science, Indianapolis, IN, USA.
Mitchell, J.C. 1991. Amphibians and reptiles. In: Terwilliger, K. (ed.), Virginia's Endangered Species: Proceedings of a Symposium, pp. 411-476. McDonald and Woodward Publishing Company, Blacksburg, Virginia.
Mount, R.H. 1975. The Reptiles and Amphibians of Alabama. Auburn University Agricultural Experiment Station, Auburn, Alabama.
Nussbaum, R.A., Brodie, Jr., E.D. and Storm, R.M. 1983. Amphibians and Reptiles of the Pacific Northwest. University Press of Idaho, Moscow, ID, USA.
Oldfield, B. and Moriart, J.J. 1994. Amphibians and Reptiles Native to Minnesota. University of Minnesota Press, Minneapolis.
Pechmann, J.H.K., Scott, D.E., Semlitsch, R.D., Caldwell, J.P., Vitt, L.J. and Gibbons, J.W. 1991. Declining amphibian populations: the problem of separating human impacts from natural fluctuations. Science: 892-895.
Pfingsten, R.A. and Downs, F.L. 1989. Salamanders of Ohio. Bulletin of Ohio Biological Survey: 1-315.
Phillips, C.A., Brandon, R.A. and Moll, E.O. 1999. Field Guide to Amphibians and Reptiles of Illinois. Illinois Natural History Survey Manual 8, Illinois.
Pierce, B.A. and Mitton, J.B. 1980. Patterns of allozyme variation in Ambystoma tigrinum mavortium and A.t. nebulosum. Copeia: 594-605.
Redmond, W.H. and Scott, A.F. 1996. Atlas of Amphibians in Tennessee (Miscellaneous Publication Number 12). The Center for Field Biology, Austin Peay State University, Miscellaneous Publication Number 12, Clarksville, TN, USA.
Semlitsch, R.D. 1983. Structure and dynamics of two breeding populations of the eastern tiger salamander, Ambystoma tigrinum. Copeia: 608-616.
Semlitsch, R.D., Scott, D.E., Pechmann, J.H.K. and Gibbons, J.W. 1996. Structure and dynamics of an amphibian community: evidence from aa 16-year study of a natural pond. In: Cody, M.L. and Smallwood, J.A. (eds), Long term studies of vertebrate communities, Academic Press, San Diego, California.
Shaffer, H.B. and McKnight, M.L. 1996. The polytypic species revisited: genetic differentiation and molecular phylogenetics of the tiger salamander (Ambystoma tigrinum) (Amphibia: Caudata) complex. Evolution: 417-433.
Shaffer, H.B., Clark, J.M. and Kraus, F. 1991. When molecules and morphology clash: a phylogenetic analysis of the North American ambystomatid salamanders (Caudata: Ambystomatidae). Systematic Zoology: 284-303.
Smith, P.W. 1961. The amphibians and reptiles of Illinois. Illinois Natural History Survey: 1-298.
Stebbins, R.C. 1985. A Field Guide to Western Reptiles and Amphibians. Second Edition. Houghton Mifflin Company, Boston, Massachusetts.
Tobey, F.J. 1985. Virginia's amphibians and reptiles: a distributional survey. Virginia Herpetological Survey, Virginia.
Vogt, R.C. 1981. Natural History of Amphibians and Reptiles of Wisconsin. Milwaukee Public Museum, Milwaukee, WI, USA.
Wissinger, S.A. and Whiteman, H.H. 1992. Fluctuation in a Rocky Mountain population of salamanders: anthropogenic acidification or natural variation? Journal of Herpetology: 377-391.
Worthylake, K.M. and Hovingh, P. 1989. Mass mortality of salamanders (Ambystoma tigrinum) by bacteria (Acinetobacter) in an oligotrophic seepage mountain lake. Great Basin Naturalist: 364-372.
Zappalorti, R.T. 1994. Results of a 5-year monitoring study and a translocation, repatriation, and conservation project with the tiger salamander (Ambystoma tigrinum) in southern New Jersey. Herpetological Associates File No. 94.03-B.
|Citation:||Hammerson, G.A., Shaffer, H.B., Church, D., Parra-Olea, G. & Wake, D. 2008. Ambystoma tigrinum. The IUCN Red List of Threatened Species. Version 2015.2. <www.iucnredlist.org>. Downloaded on 31 July 2015.|
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