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Pheasants: Status Survey and Conservation Action Plan ... - IUCN

Pheasants: Status Survey and Conservation Action Plan ... - IUCN

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The cheer pheasant lives in<br />

small patches of successional<br />

grassl<strong>and</strong>, <strong>and</strong> is under severe<br />

pressure from humans through<br />

hunting <strong>and</strong> changing l<strong>and</strong>-use<br />

patterns.<br />

© Lynx Edicions<br />

patchy <strong>and</strong> irregular canopy. Associated problems, such<br />

as damage to residual trunks <strong>and</strong> soil compaction, are<br />

discussed by Whitmore (1984), while Marshall <strong>and</strong> Swaine<br />

(1992) offer a more complete review of the effects of<br />

selective logging on tropical forests in particular.<br />

<strong>Survey</strong> work on the satyr tragopan in Singhalila National<br />

Park in India indicated that birds were avoiding areas near<br />

human habitation, presumably due to habitat disturbance<br />

or degradation. These areas were heavily grazed by cattle,<br />

trees were lopped for firewood, <strong>and</strong> bamboo was removed<br />

for construction (Khaling et al. 1998).<br />

Whilst habitat degradation is generally considered to<br />

be the result of the removal of some part of the vegetation<br />

in rather stable climax communities, it is important to<br />

remember that lack of significant disturbance will render<br />

successional habitats less suitable for species that<br />

particularly thrive in such temporary or managed<br />

situations. For example, the cheer pheasant occupies<br />

localities in the western Himalayan foothills that are<br />

dominated by grassl<strong>and</strong> <strong>and</strong> scrub habitats prevented<br />

from developing into pine <strong>and</strong> oak forests through a<br />

combination of stock grazing, hay harvesting, <strong>and</strong> stubble<br />

burning (Kaul 1989, Kalsi 1998). In the Margalla Hills<br />

National Park in Pakistan, where cheer pheasants occurred<br />

naturally until 1976 (Severinghaus et al. 1979), the<br />

ab<strong>and</strong>onment of a management regime designed to produce<br />

grass has resulted in the invasion of formerly open slopes<br />

by a dense thorn scrub forest. This has rendered the site<br />

unsuitable for the re-introduction of the cheer pheasant,<br />

although it now supports a dense population of whitecrested<br />

kalij pheasant (Garson et al. 1992).<br />

Hunting<br />

Although, for many animal species, the effects of direct<br />

exploitation are considered relatively minor, pheasants<br />

are often subject to very high harvest rates. Almost all wild<br />

Galliformes have been, or still are being, extensively hunted<br />

for subsistence, sport, or trade (Aebischer 1997a). In<br />

practice, however, it can be very difficult to distinguish the<br />

effects of direct exploitation from those due to habitat<br />

loss, which is considered the primary cause for declines in<br />

several European bird species, despite the fact that they<br />

are also widely hunted (Aebischer 1997b). The impact of<br />

hunting is also hard to quantify because much of it is illegal<br />

<strong>and</strong>, therefore, covert. Nevertheless, direct exploitation<br />

appears to be having serious negative effects on populations<br />

of several pheasant species.<br />

All three of the pheasant species classified as<br />

Endangered in this <strong>Action</strong> <strong>Plan</strong> appear greatly threatened<br />

by the activities of local hunters. Trappers were responsible<br />

for the recent rediscovery of the Edwards’s pheasant (Eve<br />

1997) <strong>and</strong> the captive population of the Vietnamese<br />

pheasant consists largely of confiscated birds (Dang Gia<br />

Tung in litt.). Through an interview survey of villagers in<br />

Kalimantan (Indonesia), O’Brien et al. (1998) found that<br />

snaring of the endangered Bornean peacock-pheasant for<br />

food was sufficiently widespread to be regarded as an<br />

important threat to this species.<br />

Recent surveys have established that the green peafowl<br />

is now absent over much of its former range in Vietnam<br />

(Brickle et al. 1998) <strong>and</strong> Laos (Evans <strong>and</strong> Timmins 1996).<br />

In both places, the declines are too rapid <strong>and</strong> widespread to<br />

be solely the result of the forest fragmentation that has been<br />

so rampant in Indochina over the last 30 years <strong>and</strong>, thus,<br />

over-hunting is considered to be the major cause. Direct<br />

exploitation for its meat, feathers, <strong>and</strong> eggs is also thought<br />

to be the main reason for its decline in Java (van Balen et<br />

al. 1995). Its extirpation from Peninsular Malaysia was<br />

caused ultimately by hunting <strong>and</strong>, in many regions, green<br />

peafowl continue to avoid areas near human habitation<br />

(McGowan et al. 1998b). The situation of the Congo<br />

peafowl must also give cause for concern. Much of its<br />

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