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

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

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around the world. There are estimated to be some 150,000 in<br />

the eastern tropical Pacific (Wade <strong>and</strong> Gerrodette 1993) <strong>and</strong><br />

about 850 in the northern Gulf of Mexico (Waring et al.<br />

2001). Rough-toothed dolphins are notorious for stealing<br />

bait <strong>and</strong> catch from fishing lines, making them unpopular<br />

with many recreational <strong>and</strong> commercial fishermen.<br />

Common bottlenose dolphin, Tursiops<br />

truncatus<br />

The common bottlenose dolphin occurs in all tropical <strong>and</strong><br />

temperate waters, including the littoral zone, inshore lagoons,<br />

estuaries, <strong>and</strong> bays, <strong>and</strong> the offshore realm (Wells<br />

<strong>and</strong> Scott 1999; Reynolds et al. 2000). In some areas where<br />

the species has been studied closely, offshore animals are<br />

distinguishable from coastal animals on the basis of morphology<br />

<strong>and</strong> ecological markers (e.g., Mead <strong>and</strong> Potter 1995).<br />

Moreover, the two forms in the North Atlantic have fixed<br />

genetic differences <strong>and</strong>, therefore, eventually may be assigned<br />

to different species (Leduc <strong>and</strong> Curry 1997; Hoelzel<br />

et al. 1998). Coastal <strong>and</strong> isl<strong>and</strong>-centered populations are<br />

especially vulnerable to hunting, incidental catch, <strong>and</strong> habitat<br />

degradation (Curry <strong>and</strong> Smith 1997 for a review).<br />

Acute conservation problems are known or suspected in at<br />

least: (a) the Mediterranean <strong>and</strong> Black seas, where past<br />

hunting, incidental catches, <strong>and</strong> environmental degradation<br />

have caused population declines (IWC 1992); (b) Sri Lanka,<br />

where this is one of the principal species taken by harpoon<br />

<strong>and</strong> gillnet for fishbait <strong>and</strong> human food (Leatherwood <strong>and</strong><br />

Reeves 1989); (c) Peru (<strong>and</strong> possibly Chile), where both<br />

directed (mainly the inshore form) <strong>and</strong> incidental (mainly<br />

the offshore form) killing occurs (Read et al. 1988; Van<br />

Waerebeek et al. 1990; K. Van Waerebeek, pers. comm.);<br />

(d) Taiwan, where there was a recent drive <strong>and</strong> harpoon<br />

fishery on the Penghu Isl<strong>and</strong>s (Hammond <strong>and</strong> Leatherwood<br />

1984; Perrin 1988) <strong>and</strong> where exploitation for meat on the<br />

east coast apparently continues (Wang et al. 1999); <strong>and</strong> (e)<br />

Japan, where large numbers (e.g., nearly 3400 in 1980) have<br />

been taken in some years in the drive <strong>and</strong> harpoon fisheries<br />

(Miyazaki 1983) <strong>and</strong> where more than 4000 were culled for<br />

fishery protection at Iki Isl<strong>and</strong> from 1977 to 1982 (Kasuya<br />

1985). The culling off northern Kyushu has declined in<br />

recent years, but the take in drive <strong>and</strong> h<strong>and</strong>-harpoon fisheries<br />

along the Pacific coast has increased since the early<br />

1980s (IWC 1992; Kishiro <strong>and</strong> Kasuya 1993). Tens of<br />

bottlenose dolphins are killed in some years in pilot whale<br />

drives in the Faroe Isl<strong>and</strong>s. On the east coast of the United<br />

States <strong>and</strong> in the northern Gulf of Mexico, large-scale dieoffs<br />

of bottlenose dolphins have occurred, but the causes are<br />

not fully understood (Geraci et al. 1999).<br />

The common bottlenose dolphin is the species most often<br />

held in captivity; hence, problems concerning the welfare of<br />

cetaceans in captivity often center on it. Unregulated livecapture<br />

fisheries can contribute to the depletion of wild<br />

populations. A regime is in place for managing live-capture<br />

operations in the south-eastern United States (Scott 1990),<br />

but captures in Cuba, mainl<strong>and</strong> Latin America, <strong>and</strong> elsewhere<br />

are poorly documented <strong>and</strong> often unregulated<br />

(Chapter 5, Project 38).<br />

Indo-Pacific bottlenose dolphin,<br />

Tursiops aduncus<br />

This coastal, mainly tropical <strong>and</strong> subtropical species has<br />

only recently been accorded full species status. Much of the<br />

literature on bottlenose dolphins (including Reeves <strong>and</strong><br />

Leatherwood 1994a) makes no distinction between the common<br />

<strong>and</strong> Indo-Pacific species. The Indo-Pacific bottlenose<br />

dolphin is known from southern Japan southward to<br />

Australia <strong>and</strong> along the entire rim of the Indian Ocean<br />

(including the Indo-Malay archipelago) to Cape Agulhas in<br />

south-eastern Africa, including the Red Sea. Although not<br />

considered to be endangered as a species, its very near-shore<br />

distribution makes this dolphin vulnerable to environmental<br />

degradation, direct exploitation, <strong>and</strong> fishery conflicts (Curry<br />

<strong>and</strong> Smith 1997; Wells <strong>and</strong> Scott 1999). In the recent past,<br />

large numbers were killed in a Taiwanese drive fishery. Although<br />

this deliberate killing is now prohibited in Taiwan,<br />

gillnet mortality continues to be a problem there <strong>and</strong><br />

throughout most of the species’ range. Large numbers of<br />

Indo-Pacific bottlenose dolphins died in a Taiwanese<br />

driftnet fishery in the Arafura Sea, off north-western<br />

Australia, during the early 1980s (Harwood <strong>and</strong> Hembree<br />

1987). In South Africa <strong>and</strong> Australia, Indo-Pacific bottlenose<br />

dolphins also suffer considerable mortality in the<br />

large-mesh nets set to protect bathers from sharks (cf.<br />

Peddemors 1999). As a preferred species in captive displays,<br />

there is substantial, <strong>and</strong> growing, dem<strong>and</strong> for this dolphin<br />

in the exp<strong>and</strong>ing oceanarium trade throughout southern<br />

Asia (Wang et al. 1999).<br />

4.6 Monodontids<br />

White whale or Beluga,<br />

Delphinapterus leucas<br />

This circumpolar species was formerly abundant throughout<br />

the Arctic <strong>and</strong> Subarctic. There may still be in the order of<br />

150,000 white whales in total (IWC 2000a; NAMMCO<br />

2000b), but many of the 29 stocks provisionally recognized<br />

by the IWC Scientific Committee have been seriously reduced<br />

by hunting. Even these depleted populations continue<br />

to be hunted <strong>and</strong> are therefore at risk of being extirpated.<br />

They include the belugas in Cook Inlet, Alaska (c.350<br />

individuals); Ungava Bay, Canada (

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