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Methods<br />
All cetacean species were assessed in 1996 against the 1994 criteria (Baillie and Groombridge 1996), and<br />
some species, subspecies and geographical populations (‘subpopulations’) have been reassessed since then<br />
against the 2001 criteria (see Reeves et al. 2003: their Table 1.1; also http://www.redlist.org). As explained in the<br />
Guidelines for Application of IUCN Red List Criteria at Regional Levels (http://www.iucn.org/themes/ssc/redlists/<br />
regionalguidelines.htm; also see Gärdenfors et al. 2001), listing of a species at the global population level can<br />
differ from listings at the subspecies or ‘subpopulation’ level.<br />
The scope of the present workshop was defined and delimited on a geographical basis, with the intent to assess<br />
the status of all cetaceans in the Mediterranean and Black Seas, some of which constitute endemic subspecies<br />
and others of which form geographically distinct ‘subpopulations’. For some or many of the species considered,<br />
an uncertain amount of genetic and/or demographic interchange with populations in the North Atlantic was either<br />
known or suspected to occur. ‘Units for assessment’ were therefore considered on a species-by-species basis.<br />
The decision to conduct complete assessments for 12 of these units was made on the basis of prior knowledge,<br />
as summarised by Notarbartolo di Sciara (2002). The Mediterranean subpopulation of Short-beaked Common<br />
Dolphins had already been assessed against the 2001 criteria and therefore was not reassessed (Bearzi 2003;<br />
see Annex 7). In addition to the eleven new complete assessments, available information on five ‘visitor’ 1 species<br />
(Common Minke Whale, Humpback Whale, Killer Whale, False Killer Whale and Rough-toothed Dolphin; see<br />
Annex 4), eight ‘vagrant’ 2 species (Sei Whale, North Atlantic Right Whale, Northern Bottlenose Whale, Dwarf<br />
Sperm Whale, Sowerby’s Beaked Whale, Blainville’s Beaked Whale, Gervais’ Beaked Whale and Indo-Pacific<br />
Humpback Dolphin; see Annex 5) and one introduced species (Beluga; see Annex 6) was summarised as<br />
background for this report. Information on visitor and vagrant species is limited to occurrences within the Black<br />
and Mediterranean Seas, including the western entrance to the Strait of Gibraltar up to a line between Cape<br />
Trafalgar, Spain (36° 10’ 57.34” N, 006° 02’ 00.80” W), and Cape Spartel, Morocco (35° 47’ 27.88” N, 005° 55’<br />
33.06” W). Finally, a brief account is given in Annex 8 of species that have been reported in the region but for<br />
which such reports are considered invalid or doubtful.<br />
IUCN criteria refer to reproductively mature individuals in a given population and it is therefore essential to use<br />
this measure rather than total population size. Reliable data and analyses of vital rates are generally unavailable<br />
for the populations of cetaceans in the Mediterranean and Black Seas. Therefore, the workshop made use of<br />
a draft table of “default” values prepared by Barbara L. Taylor of the Southwest Fisheries Science Center in La<br />
Jolla, California (pers. comm.). Based on her preliminary calculations and consistent with the views of workshop<br />
participants, 20 years was accepted as a sensible round number to use, at least provisionally, as the default<br />
generation time for dolphins.<br />
1 A taxon that does not reproduce within a region but regularly occurs within its boundaries either now or during<br />
some period of the last century (IUCN 2003).<br />
2 A taxon that is currently found only occasionally within the boundaries of a region (IUCN 2003).<br />
2