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

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Brahmaputra-Megna, <strong>and</strong> Karnaphuli-Sangu river systems,<br />

the Platanista river dolphins have declined in abundance<br />

<strong>and</strong> in the extent of their range. These cetaceans must<br />

compete with humans for shrinking water resources. Largescale<br />

engineering projects that give people hope for<br />

economic development <strong>and</strong> relief from flood <strong>and</strong> famine<br />

pose dire threats to river cetaceans <strong>and</strong> other aquatic wildlife.<br />

Freshwater populations of Irrawaddy dolphins are also<br />

threatened by development projects in the Mekong river<br />

system of Vietnam, Cambodia, <strong>and</strong> Laos, <strong>and</strong> probably also<br />

in the Ayeyarwady (formerly Irrawaddy) River of Myanmar<br />

<strong>and</strong> the Mahakam River of Indonesia. Freshwater cetaceans<br />

are also threatened by the enormous pollutant loads carried<br />

in Asian waterways (Dudgeon 1992), <strong>and</strong> by destructive<br />

fishing activities, which result in high mortality from bycatch<br />

<strong>and</strong> reduced availability of prey. These animals are<br />

perhaps more vulnerable to these threats, in comparison to<br />

marine cetaceans, because their habitat requirements often<br />

place them in areas where human activities are most intense<br />

(Smith <strong>and</strong> Smith 1998).<br />

Little is known about the status of most coastal cetacean<br />

populations in Asia. In many areas, even the most basic<br />

information, such as what species are present, is lacking.<br />

Particular problems relate to distinct populations (e.g.,<br />

dwarf spinner dolphins) <strong>and</strong> poorly documented species<br />

(e.g., pygmy Bryde’s whale). Recent projects in Vietnam<br />

(Smith et al. 1997b; Andersen <strong>and</strong> Kinze 2000), Thail<strong>and</strong><br />

(Andersen <strong>and</strong> Kinze 1999), Myanmar (Smith et al. 1997a),<br />

Indonesia (Rudolph et al. 1997), <strong>and</strong> the Philippines <strong>and</strong><br />

Malaysia (Dolar et al. 1997) have revealed diverse inshore<br />

cetacean faunas, but also serious threats, including fishery<br />

bycatch, deliberate killing, <strong>and</strong> possibly reduced prey due to<br />

overfishing. Throughout the continent, there is an urgent<br />

need for better information on the status of species <strong>and</strong><br />

populations, <strong>and</strong> for the development of local expertise to<br />

help devise, advocate, <strong>and</strong> implement conservation programs<br />

(Perrin et al. 1996). Information is particularly lacking<br />

for western Asia (e.g., Iran <strong>and</strong> the Arabian peninsula),<br />

<strong>and</strong> the absence of projects for this region represents a<br />

significant gap that should be filled in subsequent action<br />

plans.<br />

Projects<br />

1. Monitor <strong>and</strong> evaluate ongoing threats to the<br />

Irrawaddy dolphins in the Mahakam River of<br />

Indonesia<br />

The Critically Endangered Irrawaddy dolphins in the<br />

Mahakam River of East Kalimantan range in the mainstem<br />

from about 180km to 600km upstream of the mouth, seasonally<br />

entering several tributary rivers <strong>and</strong> lakes (Kreb<br />

<strong>2002</strong>). The total population was estimated to number fewer<br />

than 50 individuals based upon eight surveys of their entire<br />

range conducted in 1999 <strong>and</strong> 2000. The dolphins were found<br />

56<br />

primarily in deep pools located near confluences <strong>and</strong> me<strong>and</strong>ers,<br />

which are also primary fishing grounds <strong>and</strong> subject<br />

to intensive motorized vessel traffic. Between 1997 <strong>and</strong><br />

1999, 16 deaths were recorded (ten from gillnet entanglement,<br />

three probably from vessel strikes, <strong>and</strong> three<br />

deliberate)(D. Kreb, pers. comm.). From 1997 to 1998, at<br />

least seven dolphins were also illegally live-captured from<br />

the river <strong>and</strong> taken to oceanaria, <strong>and</strong> plans exist to capture<br />

more animals for a new oceanarium to be built in<br />

Tenggarong (D. Kreb, pers. comm.). Intensive fishing with<br />

gillnets, electricity, <strong>and</strong> poison, <strong>and</strong> the accidental introduction<br />

of an exotic piscivorous fish, locally known as ikan<br />

toman, may have depleted the dolphins’ prey (D. Kreb, pers.<br />

comm.). The high density of gillnets used in Semayang <strong>and</strong><br />

Melintang lakes causes physical obstruction to dolphin<br />

movements, thereby reducing available habitat. This problem,<br />

together with sedimentation caused by devegetation of<br />

the surrounding shorelines, has probably resulted in the<br />

elimination of these lakes as primary habitat as reported by<br />

Tas’an <strong>and</strong> Leatherwood (1984). Leaks from dams in the<br />

upper reaches that retain mining wastes, including mercury<br />

<strong>and</strong> cyanide, occurred in 1997 <strong>and</strong> resulted in a massive fish<br />

kill (D. Kreb, pers. comm.).<br />

An ongoing program, started in 1997 <strong>and</strong> conducted jointly<br />

by the University of Amsterdam <strong>and</strong> the East Kalimantan<br />

Nature <strong>Conservation</strong> Authority (Balai Konservasi Sumber<br />

Daya Alam Kal), has involved extensive monitoring of the<br />

Mahakam dolphins. This program should be continued <strong>and</strong><br />

exp<strong>and</strong>ed to include toxicological <strong>and</strong> genetic analyses of<br />

tissues obtained from str<strong>and</strong>ed or incidentally killed dolphins,<br />

investigations of factors that continue to degrade<br />

dolphin habitat, <strong>and</strong> further efforts to monitor abundance.<br />

The involvement of local scientists is vital. Because of this<br />

population’s Critically Endangered status, every effort<br />

should be made to prevent any further catches (including<br />

live-capture) <strong>and</strong> improve the quality of the riverine environment<br />

(Chapter 6).<br />

2. Investigate the status of cetaceans in the<br />

Indonesian archipelago<br />

Indonesia is a huge country, with tens of thous<strong>and</strong>s of isl<strong>and</strong>s<br />

<strong>and</strong> extensive, varied marine habitats (Figure 25). Indonesia’s<br />

marine waters harbor a greater variety of species than any area<br />

of comparable size in the world (Gray 1997). Species of<br />

particular conservation interest in Indonesian near-shore<br />

waters include the Irrawaddy dolphin, Indo-Pacific humpbacked<br />

dolphin, Indo-Pacific bottlenose dolphin, finless porpoise,<br />

<strong>and</strong> small-type (pygmy) Bryde’s whale. Relatively little<br />

is known, however, about the abundance <strong>and</strong> distribution of<br />

cetaceans in the region (Rudolph et al. 1997). Research has<br />

been limited primarily to the two whaling villages of Lamalera<br />

<strong>and</strong> Lamakera on the isl<strong>and</strong>s of Lembata <strong>and</strong> Solor, respectively<br />

(Barnes 1991, 1996); the small freshwater population<br />

of Irrawaddy dolphins in the Mahakam River (Project 1,<br />

above); waters near Manado, at the northern tip of Sulawesi

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