|Scientific Name:||Lithobates sylvaticus|
|Species Authority:||(LeConte, 1825)|
Lithobates sylvatica LeConte, 1825
Rana sylvatica LeConte, 1825
|Taxonomic Source(s):||Frost, D.R. 2014. Amphibian Species of the World: an Online Reference. Version 6.0 (7 July 2014). Electronic Database. American Museum of Natural History, New York, USA. Available at: http://research.amnh.org/herpetology/amphibia/index.html.|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Assessor(s):||IUCN SSC Amphibian Specialist Group|
|Facilitator/Compiler(s):||Angulo, A. & Hobin, L.|
Listed as Least Concern in view of the large extent of occurrence, large number of sub-populations and localities, and large population size.
|Previously published Red List assessments:|
|Range Description:||This species occurs in North America (Canada and United States) from Alaska to Labrador (Chubbs and Phillips 1998), south to New Jersey, northern Georgia and northern Idaho; it has a spotty distribution south to northern Colorado in Rocky Mountains, there are also disjunctive sub-populations in Arkansas-Missouri (Conant and Collins 1991, Stebbins 2003). It ranges farther north than any other North American amphibian.|
Native:Canada (Alberta, British Columbia, Labrador, Manitoba, New Brunswick, Newfoundland I, Northwest Territories, Nova Scotia, Nunavut, Ontario, Prince Edward I., Québec, Saskatchewan, Yukon); United States (Alabama, Alaska, Arkansas, Colorado, Connecticut, Delaware, District of Columbia, Georgia, Illinois, Indiana, Iowa, Kentucky, Maine, Maryland, Massachusetts, Michigan, Minnesota, Missouri, Montana, New Hampshire, New Jersey, New York, North Carolina, North Dakota, Ohio, Oklahoma, Pennsylvania, Rhode Island, Tennessee, Vermont, Virginia, West Virginia, Wisconsin, Wyoming)
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||It is abundant and widespread, with a stable population.|
|Current Population Trend:||Stable|
|Habitat and Ecology:||It occurs in various kinds of forest/woodland habitats; edges of ponds and streams; also willow thickets and grass/willow/aspen associations. When inactive, it hides in logs, humus, leaf-litter or under logs and rocks. Eggs are laid and larvae develop usually in small fish-free ponds, temporary or permanent, in wooded (usually) or open areas. In the Shenandoah Mountains, breeding adults were 100% faithful to the ponds in which they first bred; approximately 18% of the juveniles dispersed to breed in ponds other than the one of origin (Riha and Berven 1991). Experiments and field observations by Hopey and Petranka (1994) indicate that adults are able to assess the presence of fishes in ponds and may change breeding sites accordingly to avoid those with predatory fishes. In northern Minnesota, successful reproduction in acidic bog water either does not occur or is a rare event (Karns 1992).|
|Use and Trade:||
There are no records of this species being utilized.
|Major Threat(s):||Threats to local sub-populations include intensive timber harvesting practices that reduce canopy closure, understorey vegetation, uncompacted forest litter or coarse woody debris (moderately to well-decayed) in areas surrounding breeding sites (deMaynadier and Hunter Jr. 1999). Negative impacts of intensive timber harvesting extend at least 25-35 m into uncut forest (deMaynadier and Hunter Jr. 1998). It is not considered likely to be at risk from present acidification inputs in the Rocky Mountains (Corn and Vertucci 1992).|
No species-specific conservation actions are needed. It occurs in many protected areas.
|Citation:||IUCN SSC Amphibian Specialist Group. 2015. Lithobates sylvaticus. The IUCN Red List of Threatened Species 2015: e.T58728A78907321.Downloaded on 28 May 2017.|
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