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M. Cody, J. Diamond (1976)
Ecology and Evolution of CommunitiesNature, 260
J. Terborgh (1974)
Preservation of Natural Diversity: The Problem of Extinction Prone SpeciesBioScience, 24
J. Diamond (1972)
Biogeographic kinetics: estimation of relaxation times for avifaunas of southwest pacific islands.Proceedings of the National Academy of Sciences of the United States of America, 69 11
E. Willis, E. Eisenmann (1979)
A revised list of birds of Barro Colorado Island, Panama
B. Morgan, P. North, C. Ralph, J. Scott (1981)
Estimating Numbers of Terrestrial Birds.Biometrics, 39
D. Schemske, N. Brokaw (1981)
Treefalls and the Distribution of Understory Birds in a Tropical ForestEcology, 62
Ecology, 63(6), 1982, pp. 1975-1978 22 000-ha tract of lowland forest on the mainland ad © 1982 by the Ecological Society of America jacent to BCI. At its nearest point, BCI is =200 m from a peninsular extension of that forest, although less-disturbed forest is not so close. As many as 50-- 60 species of forest birds are missing from BCI (Karr POPULATION VARIABILITY AND 1982), well above earlier conclusions that 15-18 forest EXTINCTION IN THE AVIFAUNA OF species are extinct on BCI (Terborgh 1974, Willis 1974, A TROPICAL LAND BRIDGE ISLAND Wilson and Willis 1975, Willis and Eisenmann 1979). The approach used in earlier estimates of avian ex James R. Karr tinctions on BCI led to underestimation of extinction rates. Further, the high extinction rate seems to be Newly created oceanic islands slowly accumulate due to the restricted habitat mosaic of BCI relative to species. In contrast, habitat islands created by rising that found on a similar-sized mainland area. Under water level or by human reduction of the area of a growth and ground species and species associated with habitat (for example, by deforestation) support a full foothill forest are especially prone to extinction (Karr complement of local
Ecology – Wiley
Published: Dec 1, 1982
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