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<br /> <br />veat is that the luxuries of confidence limits and certainty are ones that <br />conservation biologists cannot now afford, given the rate of habitat de- <br />struction documented in many of the chapters of this book. Constructive <br />criticism is welcome, but to embrace the purist's motto of "insufficient <br />data" is to abandon the bleeding patient on the operating table. <br /> <br />SUMMARY <br /> <br />1. Conservation genetics can be applied to three distinct survival <br />problems occurring on three time scales. In order of increasing temporal <br />duration these problems are (1) immediate fitness; (2) adaptation within <br />a phyletic line; and (3) speciation, the generation of evolutionary novelty <br />by the splitting of phyletic lines. <br />2. Data from natural populations supports the inference that rela- <br />tively heterozygous individuals have greater viability and, in some cases, <br />fecundity, than relatively homozygous individuals. Within populations, <br />relatively heterozygous individuals are observed to have high growth <br />rates, high survivorship and greater morphological stability. In general, <br />individuals from relatively polymorphic populations, compared to those <br />from less polymorphic populations, seem to have similar advantages. <br />3. Inbreeding experiments provide another body of information rele- <br />vant to conservation genetics. A review of the literature shows that even <br />a small amount of inbreeding typically undermines fecundity and viabil- <br />ity; a 10 percent increase in homozygosity may reduce total reproductive <br />performance by as much as 25 percent. Most lines that are inbred become <br />extinct after three to 20 generations, and the chance of surviving a bout <br />of inbreeding may be virtually nil in some species fresh from nature. <br />4. Based on a rule of thumb employed by animal breeders, the basic <br />rule of conservation genetics is that the maximum allowable rate of in- <br />breeding is one percent, which corresponds to a genetically effective size <br />of 50. In the world of real (in contrast to ideal) populations, several times <br />this number may be needed. <br />5. The basic rule applies only to the maintenance of short-term <br />fitness, because population sizes of this order of magnitude do not pre- <br />vent the gradual erosion of genetic variation, and with it the raw material <br />for future evolution. <br />6. Data from island populations of lizards support the thesis that nat- <br />ural populations suffer attrition of genetic variation when their numbers <br />drop below a few hundred. <br />7. Even the largest nature reserves are probably too small to guaran- <br />tee the permanent survival of large herbivores and carnivores. <br />8. This century will see the end of significant evolution oflarge plants <br />and terrestrial vertebrates in the tropics. Nature reserves are too small <br />for the necessary isolation required by allopatric speciation. Further, it is <br /> <br />168 <br />