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Strategic Planning for Species Conservation: A Handbook - IUCN

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68<br />

8. Actions<br />

Table 8.7 Real-world examples of Actions which have been subjected to experimental<br />

testing on surrogate species.<br />

<strong>Species</strong> of concern Surrogate species Action and results Reference<br />

Chatham Island black<br />

robin<br />

Petroica traversi<br />

Piping plover<br />

Charadrius melodus<br />

Black-footed ferret<br />

Mustela nigripes<br />

8.3.5 Tests on captive animals<br />

South Island robin<br />

Petroica australis<br />

Killdeer plover<br />

Charadrius vociferus<br />

Steppe polecat<br />

Mustela eversmanni<br />

A few <strong>for</strong>ms of management under consideration <strong>for</strong> wild populations may be first tested on<br />

captive individuals. While this approach is not relevant to all Actions, it can be extremely<br />

valuable in some cases. Examples are given in Table 8.8.<br />

Table 8.8 Real-world examples of Actions being considered <strong>for</strong> use in the wild which<br />

were tested using captive animals<br />

8.3.6 Tests based on model simulation<br />

South Island robins’ responses to<br />

being transported were investigated<br />

to determine how far black robins<br />

might safely be moved, in<strong>for</strong>ming the<br />

selection of a translocation site.<br />

Behaviour, growth rates and survival<br />

were compared across wild, captive<br />

reared, and cross-fostered killdeer,<br />

to determine the most promising<br />

method <strong>for</strong> use in piping plovers.<br />

Effects of different pre-release<br />

training regimens on survival and<br />

behaviour post-release were<br />

investigated using sterilised polecats<br />

be<strong>for</strong>e testing on ferrets.<br />

Butler and<br />

Merton 1992<br />

Powell and<br />

Cuthbert 1993<br />

Biggins et al.<br />

1999<br />

<strong>Species</strong> of concern Action Outcome Reference<br />

Bighorn sheep<br />

Ovis canadensis<br />

Asian elephant<br />

Elephas maximus<br />

Several mammal<br />

species<br />

Vaccination against<br />

parainfluenzavirus III<br />

Estimation of population<br />

size by counting dung<br />

densities.<br />

Estimation of population<br />

size using camera trapping.<br />

Vaccine was safe and caused<br />

seroconversion in captivity (but did<br />

not reduce mortality of wild sheep).<br />

Defecation rates of elephants in<br />

natural habitats were measured<br />

using tame elephants and used to<br />

calibrate dung counts <strong>for</strong> wild<br />

elephants.<br />

Density estimates calculated using a<br />

new method <strong>for</strong> analysing camera<br />

trap data correlated with known<br />

densities in an enclosed area.<br />

Jessup, De<br />

Forge and<br />

Sandberg<br />

1991<br />

Tyson et al.<br />

in review<br />

Rowcliffe et<br />

al. 2008<br />

Mathematical models may provide a valuable tool <strong>for</strong> evaluating some Actions. There are<br />

several ways in which such models may be used.<br />

Occasionally, a species’ biology may be sufficiently well characterized to allow population<br />

dynamic models (often PVA models) to be constructed. These models can then be used to<br />

simulate the effects of certain management interventions. Such model-based approaches<br />

will never produce results as reliable as those derived from empirical assessments of the<br />

outcomes of action, not least because it is rarely possible to be completely confident that<br />

population models have the appropriate structure and are correctly parameterized.<br />

Nevertheless, such simulations can be very useful in some circumstances. PVA modelling

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