Wildlife of Lao PDR: 1999 Status Report - IUCN
Wildlife of Lao PDR: 1999 Status Report - IUCN
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