Abstract

Since 1963 the International Union for Conservation of Nature (IUCN) Red List has pro- vided the world with a credible and effective call to action for preventing species extinction. How- ever, the criteria for assigning categories of threat (e.g. 'critically endangered,' 'endangered,' 'vulner- able'), particularly the 'decline criteria' (Criteria A), often exaggerate the real risks of extinction and are thus not accurate. This is exemplified here by hawksbill turtles Eretmochelys imbricata, but the problem is more widespread. There is an expectation by scientists that these accuracy problems will be rectified, yet this is by no means a minor adjustment for the Red List to make, because the Red List itself operates under significant constraints. The Red List is expected to meet the requirements of sci- entists and advocates, to be consistent with historical precedents, to pursue new directions at the bio- diversity level, to meet the often conflicting views and values of diverse IUCN members, and still has to weather the stormy politics of conservation. Proposed changes to listing procedures would need to be scientifically justified, politically acceptable and as benign as possible to ongoing processes, such as biodiversity monitoring. The decline criteria are perhaps the most problematic, and these are examined in more detail here. A fundamental weakness is that they respond more to the challenge of reinstating historical abundance than to avoiding global extinction per se. This could potentially be overcome by using the current decline criteria to make an objective first stage determination based solely on decline (e.g. 'critically declined'), thereby overcoming almost all scientific objections con- cerning accuracy. A second-stage assessment could then examine the significance of that decline, in terms of allocating species to the existing extinction risk categories or retaining them as critically declined. There is an increasing conservation and humanitarian expectation that the IUCN, through the Red List, will become more involved with species that are critically declined but well-buffered against global extinction. To use global extinction as the gatekeeper to the IUCN's involvement in conservation issues today is difficult to justify.

Highlights

  • The International Union for Conservation of Nature (IUCN) was founded in 1948, as the International Union for the Protection of Nature (IUPN)

  • In 1956 the IUPN changed its name to the International Union for the Conservation of Nature and Natural Resources (IUCN)

  • If a species had been reduced to 5% of its historical abundance, which is common with crocodilians (Ross 1998, Webb 2002), investing in conservation action that increased the population by 300%, would make no difference to the critically endangered label

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Summary

INTRODUCTION

The International Union for Conservation of Nature (IUCN) was founded in 1948, as the International Union for the Protection of Nature (IUPN). Draft IUCN information papers on status (Meylan 2001, 2002) presented clear data indicating positive population trends (Table 1), proceeded to downplay the obvious conclusions and embellish the view that E. imbricata were really critically endangered (as against being classified as such by the Red List) because of scattered insights into historical abundance This confusion was overcome in the official final information paper (CITES 2002), which superseded the early draft reports and recognised the accuracy problem: that an 80+% decline in 3 generations per se had little bearing on risk of extinction. (4) NGOs and others using the endangered status of wild species to raise funds for conservation and even research, may not support changes to the Red List criteria (scientifically justified or not), that threaten the ability of high profile ‘endangered’ species, such as marine turtles to find a place in the IUCN Red List

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