TAILED FROG Name: Code: Status: Ascaphus truei A-ASTR Red-listed. DISTRIBUTION Provincial Range Tailed frogsoccur along the west coast of North America from north-western California to southern British Columbia. Tailed frogs are found in the CWH, ESSF, ICH and MH zones at elevations from sea level to over 1000 m (Province of BC 1999; Tera Planning Ltd. 1999). In BC, they are found from Penticton north to Portland Canal (Province of BC 1999). Elevational Range The tailed frog has been found from sea level to near timberline (0-1150 m; Province of BC 1999). Provincial Context Tailed frog population status is unknown in the province, although it is considered vulnerable due to its highly specialised life history. ECOLOGY AND KEY HABITAT REQUIREMENTS General The tailed frog is a small amphibian endemic to the Pacific north-west. The coastal population is blue-listed in British Columbia. The tailed frog inhabits clear, cold mountain streams, which run through forested habitats. Tailed frogs have a number of unusual characteristics, including a short tail found on adult males, vertical pupils in the eyes, the lack of external eardrums, and inability to vocalize. Adult frogs range from 2.5 5.1 cm long (U. C. Davis 1999). Tailed frogs are relatively long-lived (15-20 years). Adult frogs are not sexually mature until at least 7 years of age (Daugherty and Sheldon 1982). Adults mate in late summer or fall, and the females store the sperm until the following summer. Females lay eggs in July, attaching 37-85 eggs in strings underneath stones in the bottom of the creek (Tera Planning Ltd. 1999). Eggs require 4-6
weeks before hatching (Noble and Putnam 1931; Brown 1990). The hatchlings remain under boulders until they are relatively large (Tera Planning Ltd. 1999). Development to adulthood requires 1-4 years. Adult tailed frogs feed on arthropods, spiders, snails, ticks, mites, colembolans, dipterans, moths, ants, mayflies, crickets and lacewings (Metter 1964). Most of these food items are obtained on land within 100 m of the creek. Adult tailed frogs leave the water only at night and only at times of high humidity (Nussbaum et al. 1986). Tadpoles eat diatoms from submerged rocks, algae and desmids. Tailed frogs move very little throughout the year and from season to season, usually remaining in the same 20-m stream segment over a number of years (Daugherty and Sheldon 1982). Tadpoles may be washed downstream by flooding. However, occupied streams are separated from each other by drier habitats, and there appears to be little gene flow between sub-populations (Metter 1967). Hatler (1995) reported finding tailed frog tadpoles in a ditch near the Interfor mill. Hatler s find remains the only record for this species in the study area, and voucher specimens were not collected to confirm his identification. Important habitat features for tailed frogs are summarised in Table 24. Table 1. Important Habitat feature for tailed frogs. Season Habitat Features All Streams with : few or no fish present Well developed riparian vegetation for shading Stable substrate of rocks and boulders cold water temperatures perennial flow adjacent moist, old or mature forest Habitat Use-Life Requisites Tailed frog habitat will be rated for Living (LI) in all seasons. Living habitat requirements are described below.
Living Habitat Stream reaches occupied by tailed frog tadpoles flow year-round and have coarse substrates. On the coast tailed frogs are found in small (<15 m wide), steep headwater streams but in the interior streams with slopes as low as 4% may be occupied. Hawkins et al. (1988) found a higher relative abundance of tadpoles in streams with substrates between 10 and 30 cm diameters than in stream reaches with smaller bed material. Sand and pebble substrates (<5-36 mm diameter) were used less than gravel and rock substrates (55-124 mm diameter) in laboratory studies (Altig and Brodie 1972). Both eggs and tadpoles have narrow temperature requirements of between 5 and 18.5ºC (UC Davis 1999) and fish are usually absent. Creeks with the preferred characteristics, which are shaded by significant understory may be particularly important. Tailed frogs may be abundant in particular watersheds or creeks due to their clustered distribution pattern. They are not associated with any particular plant species (Metter 1964). Tailed frogs have been found in many different habitat types in the interior of BC, including ESSF and ponderosa pine habitats (L. Dupuis, pers. comm.). Habitat Use and Ecosystem Attributes Table 1 outlines how tailed frog habitat requirements relate to specific ecosystem attributes. Table 1. TEM-r relationships for tailed frog life requisites. Life Requisite Living TEM Attribute site: slope, structural stage vegetation: canopy closure Ratings A 4-class ratings scheme will be used. Provincial Benchmark Ecosection: Biogeoclimatic Zone: Unknown. Unknown Habitats: Shaded clear-water creeks with cobble and rock substrates, little or no fish presence and low water temperatures. Feeding habitat is wet, shady forest within 100 m of a suitable creek.
Ratings Assumptions 1. Tailed frogs are assumed to be limited to creeks with little or no fish presence, which in the Mission Tree Farm area are defined as streams with gradients of 16% or greater. 2. Structural stages 3 or greater are assumed to provide sufficient shade for tailed frogs. Ratings Adjustments Terrestrial habitats not within 100 m of suitable stream habitat should be rated nil (N).
LITERATURE CITED Altig, R., and E. D. Jr. Brodie. 1972. Laboratory behaviour of Ascaphus truei tadpoles. J. Herp. 6(1):21-24. Brown, H. A. 1990. Morphological variation and age-class determination in overwintering tadpoles of the tailed frog Ascaphus truei. J. Zool. Lond. 220:171-184. Daugherty, C. H., and A. L. Shelton. 1982. Age-specific movement patterns of the frog Ascaphus truei. Herpetologica 38(4) 468-474. Ecowatch. 1999. Ascaphus truei. http://www.cciw.ca/ecowatch/dapcan/tour/glossary/ailfrog/tailfro2.htm. Hatler, D. 1995. Wildlife Resources in the Interfor Interest Area at Adams Lake, British Columbia: A Reconnaissance Study for Forest Renewal Deliberations. Report to Interfor, Adams Lake Lumber Division. Hawkins, C. P., L. J. Gottschalk and S. S. Brown. 1988. Densities and habitat of tailed frog tadpoles in small streams near Mt. St. Helens following the 1980 eruption. J. N. Am. Benthol. Soc. 7(3): 246-252. Metter, D. E. 1967. Variation in the ribbed frog Ascaphus truei Stejneger. Copeia 3:634-649. Metter, D. E. 1964. A morphological and ecological comparison of two populations of the tailed frog, Ascaphus truei Stejneger. Copeia 1:181-204. Noble, G. K., and P. G. Putnam. 1931. Observations on the life history of Ascaphus truei Stejneger. Copeia 3:97-101. Nussbaum, R. A., E. D. Brodie and R. M. Storm. 1983. Reptiles and amphibians of the Pacific Northwest. University Press of Idaho, Moscow, Idaho. Tera Planning Ltd. Tailed frog inventory and assessment- West Vancouver, BC. http://www.teraplanning.com/proj005.html.
UC Davis. Ascaphus truei- Tailed Frog. http://ice.ucdavis.edu/toads/texthtml/truei.html.