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Last modified
7/14/2009 5:02:31 PM
Creation date
5/20/2009 10:53:37 AM
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UCREFRP
UCREFRP Catalog Number
7842
Author
Knopf, F. L.
Title
Biological Diversity in Wildlife Management.
USFW Year
1992.
USFW - Doc Type
1992.
Copyright Material
NO
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GUAM' RAILS <br />200 <br />W <br />N_ <br />cn 150 <br />Z <br />O <br />H <br />100 <br />IL <br />O <br />CL <br />LJ <br />50 <br />t= <br />CL <br />Q <br />U <br />0 <br />FROM THE WILD <br />REINTRODUCED <br />40 <br />30 <br />2Q 2 <br />10 Z <br />0 <br />1980 1982 1984 1986 1988 1990 1992 <br />YEAR <br />Figure 2C. continued <br />ations to truly evaluate the success of this program.) Thus, the lack of an ideal <br />number of founders is not justification for abandoning or failing to initiate a captive <br />breeding program. <br />The target size also depends upon the generation length of the taxon under con- <br />sideration and how rapidly the population can grow from the founding phase to the <br />target size: given the same goal, fewer individuals will be required if the taxon has <br />a relatively long generation time or could grow more rapidly each generation (Ballou <br />1987, Soule et at. 1986). In the golden lion tamarin, if generation time could be <br />artificially extended from 6 to 10 years (e.g., by delaying age of first reproduction) <br />the target size would be 290 rather than 550. <br />In addition to genetic and demographic factors, the target population size also <br />must consider the number of spaces available in zoos. Populations of species that <br />are difficult to exhibit, c.g., the Guam rail, may be limited by the number of zoos <br />that can participate in the captive breeding program. The target size therefore may <br />Managing Genetic Diversity ? 271
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