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Wildlife of Lao PDR: 1999 Status Report - IUCN

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<strong>Wildlife</strong> <strong>of</strong> <strong>Lao</strong> <strong>PDR</strong>: <strong>1999</strong> <strong>Status</strong> <strong>Report</strong><br />

Cervidae: Deer (7 species in <strong>Lao</strong> <strong>PDR</strong>; 43 worldwide)<br />

• Cervus eldii (= C. eldi M1, M2, M7 ) Eld’s Deer (= Brow-antlered<br />

Deer M2 ; = Thamin M1, M4, M5 ). Conservation Significance: Globally<br />

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

Appendix I. Documented Range and Habitat: North (provisionally,<br />

historically, Deuve 1972), centre (historically,<br />

RJTim), south (Round 1998). Dry dipterocarp forests and<br />

other open plains habitats. <strong>Status</strong> Information: The only recent<br />

confirmation <strong>of</strong> Eld’s Deer is from Dong Khanthung<br />

PNBCA, where it inhabits only one small area and is under<br />

intense threat (Round 1998; Plate 16). Evidence from elsewhere<br />

in <strong>Lao</strong> <strong>PDR</strong> is equivocal (Annex 5). Xe Pian NBCA<br />

and the plains immediately south and east <strong>of</strong> the Xe Kong<br />

are perhaps the most likely other areas to retain the species.<br />

Two sets <strong>of</strong> antlers in an Attapu shop in 1997 were obtained<br />

at least a decade previously (Davidson et al. 1997), and one<br />

<strong>of</strong> two sets displayed in Xe Kong town was reportedly over<br />

50 years old (Showler et al. 1998a). A pair <strong>of</strong> antlers was<br />

observed in Phou Xang He NBCA by Boonratana (1998b),<br />

where the species was reported to have been common in the<br />

1960s. None <strong>of</strong> the few other antlers observed on display<br />

(Annex 1) was reportedly <strong>of</strong> recent origin. Schaller (1997)<br />

found no interviewees in Attapu Province claiming knowledge<br />

<strong>of</strong> extant Eld’s Deer. A specimen from the Nakai Plateau<br />

is held in the American Museum <strong>of</strong> Natural History<br />

(RJTim). Deuve (1961a, 1972) reported the species from five<br />

provinces: Salavan (valley <strong>of</strong> the Xe Kong), Champasak<br />

(Mekong plains, to the Cambodian border, where also recorded<br />

by Engelbach 1932), Savannakhet (Mekong plain and<br />

the road to Xe Pon), Khammouan (Ban Bok and Ban Phonsi)<br />

and Louang-Namtha; he traced no record from north <strong>Lao</strong> <strong>PDR</strong><br />

after 1938. A rapid population decline was underway even<br />

by 1940 (Delacour 1940) and villagers in 1988-1993 reported<br />

wide disappearance from much <strong>of</strong> its <strong>Lao</strong> range between 1940<br />

and 1980. This was clearly caused mainly by hunting, as extensive<br />

suitable habitat remains but is bereft <strong>of</strong> Eld’s Deer.<br />

Antlers are sold along the <strong>Lao</strong>/Thai border (Srikosamatara et<br />

al. 1992, Srikosamatara and Suteethorn 1994). Many parts<br />

<strong>of</strong> the animal are used in traditional medicines (Baird 1995b).<br />

The Indochinese subspecies C. e. siamensis is listed as Data<br />

Deficient (Global) by <strong>IUCN</strong> (1996); however it is unquestionably<br />

globally endangered, perhaps critically so. Of all<br />

large mammals still known to occur in <strong>Lao</strong> <strong>PDR</strong>, this is probably<br />

the species closest to national extinction. Taxonomic issues:<br />

The known distribution <strong>of</strong> C. e. thamin suggests that it<br />

may have occurred in north-west <strong>Lao</strong> <strong>PDR</strong> (C. P. Groves in<br />

litt. <strong>1999</strong>). It was reported for Ban Houayxai (Bokeo Province)<br />

by Deuve (1961a) and, provisionally, Louang-Namtha<br />

by Deuve (1972), but there are no confirmed records <strong>of</strong> the<br />

species from this part <strong>of</strong> <strong>Lao</strong> <strong>PDR</strong>, and no recent reports.<br />

This race is much less threatened, globally, than is C. e.<br />

siamensis (Wemmer 1998).<br />

206<br />

• Cervus unicolor Sambar (= Sambar Deer M3 ). Conservation<br />

Significance: Potentially At Risk in <strong>Lao</strong> <strong>PDR</strong>. Documented<br />

Range and Habitat: North M9 , centre M8 , south M8 .<br />

Wooded areas, perhaps commonest in broken areas amid<br />

semi-evergreen forest, but also uses open deciduous forest<br />

and unbroken evergreen forest; to at least 1650 m (Nakai-<br />

Nam Theun NBCA; Tobias 1997). <strong>Status</strong> Information:<br />

Sambar was described as very common throughout the<br />

wooded parts <strong>of</strong> <strong>Lao</strong> <strong>PDR</strong> by Delacour (1940), but sightings<br />

on recent surveys are very rare, and while calls heard by night<br />

and signs indicate a wide distribution (Table 12), numbers<br />

are heavily depressed. Sambar has survived better in <strong>Lao</strong> <strong>PDR</strong><br />

than have Eld’s and Hog Deer. This reflects its wide altitudinal<br />

range and its use <strong>of</strong> denser forest where hunting is more difficult<br />

(although compared with e.g. muntjacs it is still best<br />

considered an animal <strong>of</strong> broken and more open forest types).<br />

Only in Nam Et/Phou Louey NBCAs did Sambar seem at<br />

least locally commoner than muntjacs (Davidson 1998). The<br />

Nakai Plateau and Nam Ghong Provincial PA also support<br />

relatively high densities (Steinmetz 1998b, Fernando in prep.).<br />

Many field signs in Table 12 were only identified as Cervus<br />

/ Axis sp., but in most survey areas trophy antlers confirmed<br />

the presence <strong>of</strong> Sambar. The species was reported during 86%<br />

<strong>of</strong> 1988-1993 village interviews (n = 328) and was still widespread<br />

throughout, except in the most heavily settled areas<br />

(Annex 5). It is a common and preferred food in rural areas<br />

(Table 1), and an occasional crop pest (Table 2). Antlers are<br />

widely displayed as trophies and are used in traditional medicine<br />

(Martin 1992, Baird 1995b). Their market value means<br />

that, compared with muntjacs, a much higher proportion is<br />

sent to town; for example, only two sets <strong>of</strong> antlers were seen<br />

in houses in and around Dong Ampham NBCA as against 37<br />

sets in Attapu town (Davidson et al. 1997). Many are sold<br />

openly in tourist centres such as Louangphabang (C. Poole<br />

verbally 1998). Fresh and dried meat is sold in urban markets<br />

(Annex 1) and exported to Thailand (Baird 1993), but it<br />

is imported from Cambodia to southern <strong>Lao</strong> <strong>PDR</strong> (Nash<br />

1997). Many antlers are taken to Thailand for sale as trophies;<br />

dealers in Pakxe reportedly buy up antlers from southern<br />

<strong>Lao</strong> <strong>PDR</strong> and Cambodia for bulk shipments to Thailand,<br />

and a consignment in June 1993 reportedly weighed one ton<br />

(Baird 1993, La-Ong et al. 1997). Antlers are also traded<br />

through Phongsali to China (WGR). The species is clearly<br />

Potentially At Risk in <strong>Lao</strong> <strong>PDR</strong> until the issues <strong>of</strong> hunting<br />

are addressed. (Plate 16)<br />

• Axis porcinus (= Cervus porcinus M2, M4 ) Hog Deer. Conservation<br />

Significance: Conditionally At Risk in <strong>Lao</strong> <strong>PDR</strong>;<br />

CITES Appendix I. The Indochinese subspecies A. p.<br />

annamiticus is listed as Data Deficient (Global). Documented<br />

Range and Habitat: Unclear. North and centre (provisionally,<br />

historically, Deuve 1972), south (historically, Robichaud<br />

1998e). Marshy areas, open forest, great grassy glades;<br />

always near water, and moving into the hills from flooded

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