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Dolphins, Whales and Porpoises: 2002-2010 Conservation - IUCN

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1996 Red List (again, using the 1996 categories<br />

<strong>and</strong> criteria). The Antarctic stock was listed as<br />

Endangered because its abundance in the early<br />

1990s was estimated to be only in the midhundreds,<br />

with the reasonable possibility that less<br />

than 250 mature individuals were alive at the time.<br />

The North Pacific stock was classified as Lower<br />

Risk/<strong>Conservation</strong> Dependent, mainly because the<br />

population was estimated at about 2000 in the<br />

early 1990s <strong>and</strong> evidence suggested an increase off<br />

California. The North Atlantic stock was listed as<br />

Vulnerable because available survey <strong>and</strong> photoidentification<br />

data suggested a total population of<br />

no more than about 1500, of which less than 1000<br />

would have been mature. Finally, the pygmy blue<br />

whale, centered in the Sub-Antarctic Zone of the<br />

Indian Ocean between 0º <strong>and</strong> 80ºE, was listed as<br />

Data Deficient because of uncertainty about its<br />

taxonomic status <strong>and</strong> abundance. Of particular<br />

concern in this assessment was that more than<br />

8000 pygmy blue whales had been taken illegally<br />

by Soviet whalers in the 1960s <strong>and</strong> 1970s<br />

(Clapham et al. 1999).<br />

Blue whales require continued protection <strong>and</strong><br />

close monitoring into the foreseeable future. There does not<br />

appear to be any immediate intention to resume commercial<br />

whaling for them, nor is there any other well-defined threat<br />

from human activities. As noted by Clapham et al. (1999),<br />

however, their nearly exclusive dependence upon euphausiids,<br />

especially krill (Euphausia superba) in the Antarctic,<br />

could make blue whales vulnerable to large-scale changes in<br />

ocean productivity caused, for example, by climate change.<br />

Fin whale, Balaenoptera physalus<br />

Like the blue whale, the fin whale was severely reduced<br />

worldwide by modern commercial whaling. Nearly threequarters<br />

of a million fin whales were reportedly taken in the<br />

Southern Hemisphere alone between 1904 <strong>and</strong> 1979 (IWC<br />

1995, p.129–130). Their current status is poorly known in<br />

most areas outside the North Atlantic (including the<br />

Mediterranean Sea), where recent studies indicate that there<br />

is a series of geographical “stocks” with limited genetic<br />

exchange (Bérubé et al. 1998), totaling more than 40,000<br />

animals. Fin whales are currently hunted only in Greenl<strong>and</strong>,<br />

but they would likely also become a principal target in<br />

Icel<strong>and</strong> if whaling were to resume there. Fin whales are<br />

rarely encountered today in those areas of the Southern<br />

Hemisphere where they were taken in large numbers. The<br />

species was classified as Endangered (under the 1996 categories<br />

<strong>and</strong> criteria) on the basis of an estimated decline of at<br />

least 50% worldwide over the last three generations<br />

(assumed generation time was 20–25 years). As in the case<br />

of blue whales, the greatest decline was in the Southern<br />

Hemisphere, which had the largest original population.<br />

Figure 15. There are definitely two species of Bryde’s whale, but their<br />

taxonomy <strong>and</strong> nomenclature remain unresolved. The smaller of the<br />

two species, generally called the pygmy Bryde’s whale, occurs in<br />

near-shore waters of southern Asia. The individual shown here was<br />

photographed off Loh Dasami Rinca, Komodo National Park,<br />

Indonesia, April 2000. Genetic analysis of a biopsy from the animal<br />

confirmed its identity as a pygmy Bryde’s whale.<br />

Photo: Benjamin Kahn.<br />

Ship-strikes are a major cause of fin whale mortality (Laist<br />

et al. 2001).<br />

Humpback whale, Megaptera<br />

novaeangliae<br />

Humpback whales have a cosmopolitan distribution that<br />

generally involves long migrations between high-latitude<br />

summer feeding grounds <strong>and</strong> tropical breeding grounds<br />

(Clapham 2000). Although commercial whaling seriously<br />

depleted all humpback stocks, the species has demonstrated<br />

remarkable resilience <strong>and</strong> many of those stocks are recovering<br />

(Clapham et al. 1999). As coastal <strong>and</strong> charismatic<br />

animals, humpbacks are major tourist attractions in some<br />

areas. They are also the subjects of numerous local population<br />

studies (e.g., Steiger <strong>and</strong> Calambokidis 2000;<br />

Razafindrakoto et al. 2001) as well as basin-scale research<br />

programs (Baker et al. 1998; Smith et al. 1999). Although<br />

they are certainly vulnerable to ship collisions, entanglement<br />

in fishing gear, <strong>and</strong> disturbance (even serious injury)<br />

from industrial noise, humpbacks seem able to adapt, or at<br />

least tolerate, living in close proximity to a considerable<br />

variety <strong>and</strong> amount of human activities. They are actively<br />

hunted today only at Bequia, St. Vincent <strong>and</strong> the<br />

Grenadines, in the eastern Caribbean Sea. With growing<br />

humpback populations, however, pressure to resume commercial<br />

whaling in at least a few areas is likely to mount.<br />

The species was listed as Vulnerable (under the 1996 categories<br />

<strong>and</strong> criteria) based on the fact that, although most<br />

monitored stocks had shown evidence of fast recovery <strong>and</strong><br />

may have increased to more than 50% of their levels three<br />

generations ago (1930s, assuming a 20-year generation<br />

36

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