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 />
1997 were reviewed by Thewlis et al. (1998). In view <strong>of</strong> the<br />
species’s apparently secure status (widespread and locally<br />
common in five survey areas, and recorded from a further<br />
two), it was dropped from the list <strong>of</strong> key species. However, it<br />
has only been found subsequently in one further survey area,<br />
Nam Xam NBCA (Showler et al. 1998b) and it appears to be<br />
restricted in <strong>Lao</strong> <strong>PDR</strong> to eastern parts. The species’s conservation<br />
status should be reconsidered at regular intervals.<br />
Special Significance: Endemic to <strong>Lao</strong> <strong>PDR</strong>, Vietnam<br />
and Hainan (south China) with outlying populations in southern<br />
Thai/Myanmar border area.<br />
• Pica pica Black-billed Magpie. Conservation Significance:<br />
Little Known in <strong>Lao</strong> <strong>PDR</strong>. Documented Range and Habitat:<br />
Presumed resident; north (historically B18 ), south (provisionally,<br />
historically, Engelbach 1927). Habitat unknown in <strong>Lao</strong><br />
<strong>PDR</strong>. <strong>Status</strong> Information: There is only one confirmed record<br />
from <strong>Lao</strong> <strong>PDR</strong>: a male at Phongsali on 26 April 1929 (Bangs<br />
and Van Tyne 1931). Engelbach (1927) considered the species<br />
‘very common’ in south <strong>Lao</strong> <strong>PDR</strong>, yet later when summing<br />
up his observations in the area (Engelbach 1932), he<br />
did not mention it. It beggars belief that a mistake could have<br />
been made in the earlier identification, yet Delacour and<br />
Jabouille (1940) also make no reference to the 1927 record.<br />
Thus, the magnitude <strong>of</strong> decline in <strong>Lao</strong> <strong>PDR</strong> is unclear. The<br />
species has declined drastically in Vietnam. Delacour et al.<br />
(1928) noted that the species was ‘very common’ in Vietnam,<br />
but did not occur south <strong>of</strong> Cap Varela (about 13ºN). It<br />
is now extremely rare (J. C. Eames verbally 1998). The factors<br />
which have driven its decline in Vietnam are likely also<br />
to have operated in <strong>Lao</strong> <strong>PDR</strong>, if the species was formerly<br />
widespread here. It should therefore be considered Little<br />
Known in <strong>Lao</strong> <strong>PDR</strong>.<br />
Corvus macrorhynchos Large-billed Crow. Resident;<br />
north B2 , centre B10 , south B2 . Open country, secondary growth,<br />
especially near large slow-flowing rivers and other extensive<br />
water bodies. Sibley and Monroe (1990) separated C.<br />
levaillanti Jungle Crow as a separate species. Both races <strong>of</strong><br />
crow known to inhabit <strong>Lao</strong> <strong>PDR</strong>, C. m. macrorhynchos and<br />
C. m. colonorum, belong under C. macrorhynchos (s.s.), but<br />
levaillanti might also occur, as its distribution includes northern<br />
Thailand and Myanmar. Crows are scarce in most <strong>of</strong> <strong>Lao</strong><br />
<strong>PDR</strong>, tending to be less scarce in areas away from large human<br />
settlements. As a large bird <strong>of</strong> non-forest areas, it is vulnerable<br />
to human pressure in various forms. The species’s<br />
conservation status should be reconsidered at regular<br />
intervals.<br />
Artamus fuscus Ashy Woodswallow. Resident; north B9 ,<br />
centre B10 , south B2 . Open wooded areas predominantly <strong>of</strong> secondary<br />
regrowth and cultivation from 150 m up to 1400 m.<br />
Records prior to 1996 were reviewed by Duckworth et al. (1998a).<br />
130<br />
Oriolus chinensis Black-naped Oriole. Largely winter visitor;<br />
north, centre, south B2 , breeding in the north B21 . Most habitats<br />
with trees, from evergreen forest to stands <strong>of</strong> trees amid<br />
cultivation; lowlands to at least 1000 m.<br />
Oriolus tenuirostris Slender-billed Oriole. Seasonal status<br />
unclear, breeds in some areas; north B8 , south B9 . Open forest,<br />
at one site with pines, up to at least 1150 m; probably rare in<br />
lowlands. Records prior to 1996 were reviewed by Duckworth<br />
et al. (1998a). Difficulties <strong>of</strong> separation from Black-naped<br />
Oriole hamper status assessment <strong>of</strong> this species.<br />
Oriolus xanthornus Black-hooded Oriole. Resident; north<br />
(Pasquet 1997), centre, south B2 . Forests, mainly open, deciduous<br />
and below 800 m.<br />
Oriolus traillii Maroon Oriole. Resident (O. t. traillii) and<br />
winter visitor (O. t. nigellicauda); north B1 , centre B10 , south B2 .<br />
Forests, mainly evergreen and above 500 m, but dispersing<br />
as low as 150 m in winter.<br />
Coracina macei Large Cuckooshrike (included in C.<br />
novaehollandiae Large Cuckooshrike by ^K). Resident;<br />
north B10 , centre, south B2 . Open evergreen and mixed deciduous<br />
forest, forest edge, glades in heavy forest and ridges in<br />
montane forest, up to at least 2000 m.<br />
Coracina polioptera Indochinese Cuckooshrike. Resident;<br />
north (historically B21 ), centre (historically B22 ), south B2 . Open<br />
deciduous forest and secondary growth, chiefly <strong>of</strong> lowlands,<br />
foothills and plateaux, up to 850 m. Separation from C.<br />
melaschistos can be difficult; it is possible that this is responsible<br />
for the lack <strong>of</strong> recent records <strong>of</strong> this species over<br />
most <strong>of</strong> the country. Special Significance: Endemic to<br />
Indochina, Thailand and Myanmar.<br />
Coracina melaschistos (= C. melaschista, ^K, ^T) Blackwinged<br />
Cuckooshrike. Mainly winter visitor; north, centre,<br />
south B2 , also resident in north B21 . Forests, tall dense secondary<br />
growth; migrants appear in even heavily fragmented areas<br />
and town gardens. Occurs up to at least 1480 m.<br />
Pericrocotus roseus Rosy Minivet. Passage migrant and perhaps<br />
winter visitor; north B2 , south B2 . Forests, tall dense secondary<br />
growth.<br />
• Pericrocotus cantonensis Swinhoe’s Minivet (= Brownrumped<br />
Minivet, ^Sm); (included in P. roseus Rosy Minivet<br />
by ^K, ^T). Conservation Significance: Globally Near-Threatened.<br />
Not At Risk in <strong>Lao</strong> <strong>PDR</strong>. Documented Range and Habitat:<br />
Winter visitor; north, centre, south B14 . Open deciduous<br />
forests and secondary growth, occasionally in evergreen forest,<br />
up to at least 870 m. <strong>Status</strong> Information: Records prior to<br />
1997 were reviewed by Thewlis et al. (1998). Small numbers