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Wildlife of Lao PDR: 1999 Status Report - IUCN

Wildlife of Lao PDR: 1999 Status Report - IUCN

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• Lophura diardi Siamese Fireback. Conservation Significance:<br />

Globally Threatened - Vulnerable; Potentially At Risk<br />

in <strong>Lao</strong> <strong>PDR</strong>; endemic to Indochina and parts <strong>of</strong> Thailand.<br />

Documented Range and Habitat: Resident; north, centre,<br />

south B14 . Forest (evergreen and, locally, deciduous areas),<br />

scrub, secondary growth, mostly below 500 m, exceptionally<br />

up to 800 m and possibly 1150 m (Showler et al. 1998a).<br />

<strong>Status</strong> Information: Records prior to 1997 were reviewed by<br />

Thewlis et al. (1998). The species has been recorded in at<br />

least 14 recent survey areas from Sangthong District to the<br />

far south <strong>of</strong> the country (Table 11). Particularly large<br />

populations remain in Xe Pian and Dong Ampham NBCAs<br />

and in other parts <strong>of</strong> the Xe Kong basin. Large populations<br />

were also found or suspected in most other survey areas with<br />

a substantial area below 500 m altitude, including Xe Bang-<br />

Nouan and Phou Xiang Thong NBCAs, Dong Khanthung<br />

PNBCA and Sangthong District. Smaller numbers occur in<br />

those recent surveys areas primarily at higher altitude but<br />

with parts below 500 m. Occurrence at Phou Khaokhoay<br />

NBCA has recently been confirmed (T. Hansel verbally 1998).<br />

Despite being widespread and locally abundant, the species<br />

is subject to very heavy snaring and is commonly sold in<br />

food markets and is therefore categorised as Potentially At<br />

Risk in <strong>Lao</strong> <strong>PDR</strong>. (Plate 11)<br />

Polyplectron bicalcaratum Grey Peacock Pheasant. Resident;<br />

north, centre, south B14 . Evergreen forests, tolerant <strong>of</strong><br />

degradation, from lowlands up to 1850 m. Records prior to<br />

1997 were reviewed by Thewlis et al. (1998). In view <strong>of</strong> the<br />

species’s secure status, it was dropped from the recommended<br />

list <strong>of</strong> key species. Special Significance: CITES Appendix<br />

II.<br />

• Rheinardia ocellata Crested Argus. Conservation Significance:<br />

Globally Threatened - Vulnerable; At Risk in <strong>Lao</strong><br />

<strong>PDR</strong>; CITES Appendix I; endemic to Malaysia (R. o.<br />

nigrescens; see Mamat and Yasak 1998) and Vietnam and<br />

<strong>Lao</strong> <strong>PDR</strong> (R. o. ocellata). Documented Range and Habitat:<br />

Resident; north, centre, south B14 . Evergreen forest, particularly<br />

climatically wet forest, at 350-1500 m. <strong>Status</strong> Information:<br />

Records prior to 1997 were reviewed by Thewlis et al.<br />

(1998). Distribution in <strong>Lao</strong> <strong>PDR</strong> is local: it occurs in four<br />

recent survey areas along the Annamites (Table 11). There<br />

are no certain recent records from elsewhere. Numbers were<br />

only found to be high in climatically wet forest, as in the<br />

Nam Theun Extension PNBCA. Snaring may be an extreme<br />

threat to some populations. (Plates 6, 11)<br />

• Pavo muticus Green Peafowl. Conservation Significance:<br />

Globally Threatened - Vulnerable; At Risk in <strong>Lao</strong> <strong>PDR</strong>;<br />

CITES Appendix II. Documented Range and Habitat: Resident;<br />

north B14 , centre (provisionally, McGowan et al. 1998;<br />

historically B22 ), south B14 . Open forest and edge, rocky savanna,<br />

forest river banks, secondary growth; lowlands and<br />

Birds<br />

foothills. <strong>Status</strong> Information: The status <strong>of</strong> the species in <strong>Lao</strong><br />

<strong>PDR</strong> was reviewed by Evans and Timmins (1996, 1997) and<br />

Thewlis et al. (1998). McGowan et al. (1998) set the <strong>Lao</strong><br />

records in a global context. While common and widespread<br />

throughout <strong>Lao</strong> <strong>PDR</strong> only 50 years ago, populations are<br />

known today in only six areas; there are reports from 10 others<br />

(Table 11). Formerly the species was so abundant that<br />

Harmand (1878-1879) characterised the worst place for wildlife<br />

he went as lacking even peafowl and junglefowl. Few<br />

areas are likely to retain populations large enough to be<br />

viable. Phou Khaokhoay, Xe Pian and Phou Xiang Thong<br />

NBCAs and Dong Khanthung PNBCA perhaps hold the most<br />

practically conservable populations. A previously unpublished<br />

record is <strong>of</strong> one heard calling by the Xe Pian river upstream<br />

<strong>of</strong> Ban Sompoy (Xe Pian NBCA) in early 1998 (RJTiz).<br />

(Plates 6, 11)<br />

Conservation Management and Research Proposed for<br />

Phasianidae:<br />

• Complete protection from hunting for Green Peafowl,<br />

Crested Argus and arguably Siamese Fireback.<br />

• Cessation <strong>of</strong> snaring in NBCAs, with action prioritised<br />

to those retaining Green Peafowl, Crested Argus and large<br />

populations <strong>of</strong> Siamese Fireback.<br />

• Establishment <strong>of</strong> sustainable hunting practices for other<br />

species. Birds <strong>of</strong> this family, especially Red Junglefowl,<br />

are frequently eaten in rural <strong>Lao</strong> <strong>PDR</strong> (Table 1).<br />

• Assessments <strong>of</strong> the effects <strong>of</strong> snaring (and procedure for<br />

control where necessary) on all species in areas outside<br />

NBCAs.<br />

• Assessment <strong>of</strong> the effects on Green Peafowl in <strong>Lao</strong> <strong>PDR</strong><br />

<strong>of</strong> trade in peafowl train feathers. Peafowl train feathers<br />

are traded in large numbers along the <strong>Lao</strong>-Thailand border,<br />

but it is unclear how many, if any, are from wild<br />

Green Peafowl (McGowan et al. 1998).<br />

• Monitoring and control <strong>of</strong> trade in these species and their<br />

parts. Birds <strong>of</strong> this family, especially Red Junglefowl,<br />

are widely sold in urban markets (Annex 1) and<br />

junglefowl claws are used as an ingredient in traditional<br />

medicine (Martin 1992, Annex 1). International trading<br />

seems likely (Compton in prep. b).<br />

• Co-ordinated recovery programme for Green Peafowl,<br />

involving education programmes, stronger legislation<br />

with more effective enforcement, and assessment <strong>of</strong><br />

progress by a population monitoring programme. The<br />

peafowl monitoring and protection project in Phou<br />

Khaokhoay NBCA (in which most <strong>of</strong> the local people<br />

are participating) should be replicated (with appropriate<br />

modification) in Xe Pian and Phou Xiang Thong NBCAs<br />

and in Dong Khanthung PNBCA.<br />

• Co-ordinated conservation programme for Crested Argus,<br />

involving education programmes, stronger legislation<br />

with more effective enforcement, an investigation <strong>of</strong> the<br />

threat posed by trade, and assessment <strong>of</strong> progress by a<br />

93

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