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