Brown to olive brown on back. Inky black spots, usually well defined, on back.
Dark spotting on legs. Few or no black flecks between spots. Lower abdomen and
underside of rear legs yellow, orange-yellow, or yellowish tan. Groin usually
bright yellow with dark mottling. Lower sides yellowish or cream. Dorsolateral
folds. Male has darkened and enlarged thumb base (Stebbins 1985). Males
measure 50-60 mm in snout-vent length, females, 50-75 mm
(Ronald and Dumas 1971).
Range overlaps slightly with ranges of Rana pretiosa (Spotted frog)
and R. Aurora (Red-legged frog). R. pretiosa has a more
conspicuous light-colored upper jaw
stripe and nostrils that are set closer together an higher on the snout than
R. cascadae. R. Aurora usually has red mottling on its groin
and generally has smoother skin than R. cascadae (Stebbins 1985)..
Distribution and Habitat
Country distribution from AmphibiaWeb's database: United States
U.S. state distribution from AmphibiaWeb's database: California, Oregon, Washington
Cascade Mts., from northern Washington south through Oregon to California
border. Isolated populations in Olympic Mts. of Washington, Mt. Shasta and
Lassen Peak area of California, and Trinity Mts. of California. Lives at
elevations of 800-2740 m, almost to timberline. Inhabits small streams,
meadow puddles, ponds, and lakes, usually in open coniferous forest. Found in
water or among grass, ferns and riparian vegetation (Stebbins 1985).
Life History, Abundance, Activity, and Special Behaviors
Call is either a low-pitched, grating, chuckling sound, resembling that
of Rana aurora (Red-legged Frog), with 4-5 notes per second, or a series
of rapid clucks or
double clucks, each about .5 seconds long. Calls from above or below water's
Diurnal (active during the day). Breeds from March to
mid-Aug., soon after pond ice begins to thaw (Stebbins 1985).
Trends and Threats
Declining in much of its range.
Rapid decline in southernmost portion of range began after 1978. Apparently,
Rana cascadae had mostly vanished from the vicinity of Lassen Volcanic National
Park in California
by 1993. Fellers and Drost (1993) searched 16 historical and 34 additional
sites in this area in 1991 and found only one male and one female frog, both in a stream
draining into Crumbaugh Lake. Causes of the decline here seem to be a
combination of introduced predators and habitat destruction.
Non-native predatory trout restrict habitat and limit dispersal. Drought dries
up the ponds, streams, and pools which serve as breeding habitat.
And the succession of meadows and their associated streams and open pools to
forests also destroys breeding habitat (Fellers and Drost 1993).
and Washington, numbers are very high in suitable habitat (Nussbaum et al. 1983).
Nevertheless, the frog has declined extremely in Oregon. Although abundant there in the
early 1970's, 80% of 30 Oregon populations that Andrew Blaustein has monitored since the mid 1970's
have disappeared (Blaustein and Wake 1990). Blaustein et al. found
embryos to display low photolyase activity when reared in the lab. Lack of high levels of
photolyase may inhibit the repair of DNA damaged by UV-B radiation, leaving the embryos vulnerable
UV-B-induced mortality. Blaustein et al. also conducted experiments at two sites in the Oregon Cascades, at elevations
of 1190 and 2000 m, and found that R. cascadae embryos shielded from ambient
UV-B radiation hatch with better success than those exposed to direct sunlight,
suggesting that UV-B induced embryo mortality may be responsible for
population declines (Blaustein et al. 1994). A similar experiment by Blaustein et al.
(1995) found a synergism between ambient UV-B and disease. In the Oregon
Cascades, at two sites (elevations of 1220 and 2000 m) ambient UV-B and the
algal pathogen Saprolegnia ferax were both observed to be factors that reduced
hatching success of R. cascadae embryos, but the reduction was amplified when
embryos were exposed to both factors.
Relation to Humans
In the vicinity of Lassen Volcanic National Park, the common management
practices in parks and wilderness of suppressing natural fire regimes and
cessation of cattle grazing has sped the natural invasion of shrubs and trees into
open meadows, thereby filling in or choking with vegetation the ponds, streams,
and marshes where the frog used to breed (Fellers and Drost 1993).
Possible reasons for amphibian decline
General habitat alteration and loss
Climate change, increased UVB or increased sensitivity to it, etc.
The Cascades frog is rather non-mobile in its behavior, often allowing one to
inspect it closely (Stebbins 1985).
See another account at californiaherps.com.
This species was featured as News of the Week on December 22, 2014:
While Rana cascadae is relatively widespread in montane habitats from northern California into southern British Columbia, declines attributed to the chytrid fungus Batrachochytrium dendrobatidis (Bd) seem focused in northern California populations. Piovia-Smith et al. (2014) studied virulence of Bd from two lakes suffering declines, finding that isolates from the midst of the decline were more virulent and induced greater mortality of juvenile frogs than Bd isolated from a more stable frog population. In genomic studies, the virulent isolate showed unusual features, including chromosomal differences. Specific genomic and phenotypic features of Bd might account for differences in mortality within species from different localities, as well as differences among species of amphibians (Written by David Wake).
Altig, R., and Dumas, P. C. (1971). ''Rana cascadae Slater. Cascades Frog.'' Catalogue of American Amphibians and Reptiles. Society for the Study of Amphibians and Reptiles, 105.1-105.2.
Badarco (1962). "Wildlife observation on file at Lassen Volcanic National Park, Mineral, California."
Blaustein, A. R., Hoffman, P. D., Hokit, D. G., Kiesecker, J. M., Walls, S. C., and Hays, J. B. (1994). "UV repair and resistance to solar UV-B in amphibian eggs: A link to population declines?" Proceedings of the National Academy of Sciences of the United States of America, 91(5), 1791-1795.
Blaustein, A. R., and Wake, D. B. (1990). ''Declining amphibian populations: A global phenomenon?'' Trends in Ecology and Evolution, 5(7), 203-204.
Borrel, A. E. (1924). "Field notes on file at the Museum of Vertebrate Zoology, University of California, Berkeley."
Fellers, G. M., and Drost, C. A. (1993). ''Disappearance of the Cascades Frog Rana cascadae at the southern end of its range, California, USA.'' Biological Conservation, 65(2), 177-181.
Grinnell, J. (1925). ''Field notes on file at the Museum of Vertebrate Zoology, University of California, Berkeley.''
Grinnell, J., Dixon, J., and Linsdale, J. M. (1930). Vertebrate natural history of a section of northern California through the Lassen Peak region. Univ. California Press, Berkeley, California.
Kiesecker, J. M., and Blaustein, A. R. (1995). "Synergism between UV-B radiation and a pathogen magnifies amphibian embryo mortality in nature." Proceedings of the National Academy of Sciences of the United States of America, 92(24), 11049-11052.
Nussbaum, R. A., Brodie, E. D., Jr., and Storm, R. M. (1983). Amphibians and Reptiles of the Pacific Northwest. University of Idaho Press, Moscow, Idaho.
Sage, R. D. (1974). "Field notes on file at the Museum of Vertebrate Zoology, University of California, Berkeley."
Stebbins, R. C. (1951). "Field notes on file at the Museum of Vertebrate Zoology, University of California, Berkeley."
Stebbins, R. C. (1952). "Field notes on file at the Museum of Vertebrate Zoology, University of California, Berkeley."
Stebbins, R. C. (1985). A Field Guide to Western Reptiles and Amphibians. Houghton Mifflin, Boston.
Originally submitted by: John Romansic (first posted 1999-02-16)
Edited by: Vance Vredenburg (2018-11-26)
Species Account Citation: AmphibiaWeb 2018 Rana cascadae: Cascades Frog <https://amphibiaweb.org/species/4998> University of California, Berkeley, CA, USA. Accessed May 7, 2021.
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Citation: AmphibiaWeb. 2021. <https://amphibiaweb.org> University of California, Berkeley, CA, USA. Accessed 7 May 2021.
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