PREDICTING EFFECTS OF PREDATION ON CONSERVATION OF ENDANGERED PREY

In parts of the world such as the Pacific Islands, Australia, and New Zealand,introduced vertebrate predators have caused the demise of indi genous mammal and bird species. A number of releases for reestablishme nt of these mammal species in mainland Australia have failed because p redators extirpated the new populations. The nature of the decline of both extant populations and reintroduced colonies provides information on the dynamics of predation. Predator-prey theory suggests that the effects of predation are usually inversely dependent on density (depen satory) when the prey are not the primary food supply of exotic predat ors. Thus, such predators can cause extinction of endemic prey species . Three types of evidence can be deduced from the predator-prey intera ctions that allow predictions for conservation: (1) whether per capita l rates of change for prey increase or decrease with declining prey de nsities, (2) whether predation is depensatory or density-dependent, an d (3) the overall magnitude of predation. If this magnitude is too hig h for coexistence, then the degree of predator removal required can be predicted. If the magnitude of predation is sufficiently low, then th e threshold density of prey that management must achieve to allow pred ator and prey to coexist can also be predicted. We analyzed published reports of both declining populations and reintroduced colonies of end angered marsupial populations in Australia. The observed predation cur ves conformed to the predictions of predator-prey theory. Some, such a s the black-footed rock-wallaby (Petrogale lateralis), were classic al ternate prey and were vulnerable below a threshold population size. Ot hers, such as the brush-tailed bettong (Bettongia penicillata), have a refuge at low numbers and thus offer the best chance for reintroducti on. Our predictions suggest a protocol for an experimental management program for the conservation of sensitive prey species: (1) determinat ion of net rates of change of prey with declining population, (2) impr ovement of survivorship through habitat manipulation, (3) improvement of survivorship through predator removal, (4) determination of the thr eshold density above which reintroductions can succeed, and (5) manipu lations to change interactions form Type II to Type III. The task in t he future is to determine how to change the vulnerability of the prey so that they can have a refuge at low numbers.