Editorial Type:
Article Category: Research Article
 | 
Online Publication Date: 01 Feb 2004

Asymmetrical Effects of Introduced Bullfrogs (Rana catesbeiana) on Native Ranid Frogs in Oregon

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Page Range: 11 – 20
DOI: 10.1643/CE-03-010R2
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Abstract

Introduced American Bullfrogs (Rana catesbeiana) have become widely established in the Pacific Northwest over the last century and are thought to be an important predator of native amphibians throughout the western United States. The Northern Red-Legged Frog (Rana aurora aurora) and Oregon Spotted Frog (Rana pretiosa) historically coexisted in portions of the Pacific Northwest now invaded by R. catesbeiana, but R. pretiosa has declined more severely than R. a. aurora. We investigated whether microhabitat and behavioral differences that facilitate sympatric coexistence of the natives predict which species is more susceptible to predation by introduced R. catesbeiana. Our laboratory experiments demonstrate that R. catesbeiana adults prefer aquatic microhabitats, that R. pretiosa juveniles are more aquatic than R. a. aurora, and that adult R. catesbeiana consume more R. pretiosa than R. a. aurora juveniles. Mean and maximum jump distances of R. pretiosa were shorter than equally sized R. a. aurora, and the difference between these two species increased with larger frog sizes. Our examination of field survey data indicates that R. pretiosa coexist with R. catesbeiana less frequently than R. a. aurora. We conclude that R. catesbeiana is a greater threat to survival of R. pretiosa than to R. a. aurora and suggest that microhabitat use and escape abilities of native ranid frogs may be linked to this asymmetrical effect. Analysis of behavioral and microhabitat differences among related native species may be a useful tool in predicting the effects of introduced predators on amphibians and can assist in developing conservation priorities for these species.

Copyright: The American Society of Ichthyologists and Herpetologists
 Fig. 1.
 Fig. 1.

Mean and SE of juvenile native frog survival per tank with free Rana catesbeiana predator (n = 24 tanks; one-tailed paired t-test, t = 1.933, df = 11, P = 0.040)


 Fig. 2.
 Fig. 2.

Number of native ranid frogs consumed and size of Rana catesbeiana predator in 12 tanks. The best fitting regression model was Number of Natives Consumed/Mass = 0.108 + 0.008(Species)− 0.019[ln(Mass)] where Mass is the mass of R. catesbeiana (g) prior to the experiment and Species is 0 for Rana aurora aurora and 1 for Rana pretiosa. R2 = 0.36


 Fig. 3.
 Fig. 3.

Mean (A) and maximum (B) jump distances of juvenile Rana aurora aurora and Rana pretiosa on runways in the laboratory


Contributor Notes

United States Geological Survey, Forest and Rangeland Ecosystem Science Center, 3200 Southwest Jefferson Way, Corvallis, Oregon 97331. christopher_pearl@usgs.gov

Accepted: 16 Sept 2003
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