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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have been recorded from 11 widely-scattered recent survey<br />
areas (Table 11). Post-1996 records include a small flock in<br />
Nam Kading NBCA in January <strong>1999</strong> (TDE).<br />
Pericrocotus divaricatus Ashy Minivet. Winter visitor;<br />
north B2 , centre B9 , south B2 . Forests, secondary growth and trees<br />
amid cultivation; generally lowlands and foothills.<br />
Pericrocotus cinnamomeus Small Minivet. Resident; north B7 ,<br />
centre B10 , south B2 . Dry dipterocarp and other open deciduous<br />
forests, up to 550 m.<br />
Pericrocotus solaris Grey-chinned Minivet. Resident;<br />
north B10 , centre B7 , south B2 . Evergreen forest, occasionally in<br />
pines; above 500 m.<br />
Pericrocotus ethologus Long-tailed Minivet. Seasonal<br />
status unclear; north B8 , centre (historically, see below), south<br />
(provisionally B3 ). Evergreen forest including pine forest and<br />
secondary growth, generally above 1000 m, some moving<br />
lower in winter. Skins collected by David-Beaulieu in<br />
Savannakhet Province, but apparently not recorded by him<br />
as any species in David-Beaulieu (1949-1950), were reexamined<br />
by B. F. King and found to be Long-tailed Minivet.<br />
Furthermore, the listings in King et al. (1975) for this species<br />
in north and south <strong>Lao</strong> <strong>PDR</strong> were apparently erroneous<br />
(E. C. Dickinson in litt. to T. P. Inskipp 1997). Field separation<br />
<strong>of</strong> Long-tailed and Short-billed Minivets can be difficult.<br />
Pericrocotus brevirostris Short-billed Minivet. Resident;<br />
north B7 , centre B10 , south (provisionally B3 ). Evergreen forest<br />
above 1080 m. Records <strong>of</strong> this species in Davidson et al.<br />
(1997) and Showler et al. (1998a) should refer to Short-billed<br />
/ Long-tailed Minivet.<br />
Pericrocotus flammeus Scarlet Minivet. Resident; north B1 ,<br />
centre, south B2 . Evergreen and deciduous forest, and adjacent<br />
wooded areas and secondary growth, up to at least 1600 m.<br />
Hemipus picatus Bar-winged Flycatcher-shrike. Resident;<br />
north, centre, south B2 . Evergreen forest, forest edge and tall<br />
regrowth; rare in open deciduous forest except where bordering<br />
evergreen streamside forest. Occurs up to at least 1350 m.<br />
Rhipidura hypoxantha Yellow-bellied Fantail. Resident,<br />
north B8 . Montane evergreen forest; probably breeds above<br />
2000 m. The only records are from two sites in Xiangkhouang<br />
Province (David-Beaulieu 1944) and the summit <strong>of</strong> Phou<br />
Louey mountain, Phou Louey NBCA, where the species was<br />
common in May 1998 (Davidson 1998). Thewlis et al. (1998)<br />
considered the bird Little Known in <strong>Lao</strong> <strong>PDR</strong>. This is no<br />
longer appropriate as there is no clear threat to the species or<br />
its habitats.<br />
Birds<br />
Rhipidura albicollis White-throated Fantail. Resident;<br />
north, centre B10 , south B2 . Evergreen forest, secondary growth,<br />
bamboo; mainly in hills and mountains, but locally down to<br />
200 m.<br />
Rhipidura aureola White-browed Fantail. Resident; centre<br />
(historically B22 ), south B2 . Dry dipterocarp forest <strong>of</strong> lowlands<br />
and foothills, but apparently absent from some large areas <strong>of</strong><br />
this habitat. Records from prior to 1994 were summarised in<br />
Thewlis et al. (1996).<br />
Rhipidura javanica Pied Fantail. Presumed resident; north<br />
(Robson 1997b). Dense scrub and vegetation in disturbed<br />
areas, <strong>of</strong>ten near water, e.g. gardens, cultivation. Duckworth<br />
et al. (1998a) hypothesised that the Mekong represented a<br />
dispersal barrier to this species. There seems no other clear<br />
explanation for the difference in status on the Thai bank (at<br />
Nong Khai, where it is abundant) and in <strong>Lao</strong> <strong>PDR</strong> (Vientiane<br />
area), where the species was first recorded in 1997 (Robson<br />
1997b) and it remains very local.<br />
Dicrurus macrocercus Black Drongo. Locally resident, more<br />
widespread in winter; north, centre, south B2 . Open country<br />
including towns and cultivation; generally lowlands.<br />
Dicrurus leucophaeus Ashy Drongo. Locally resident, augmented<br />
by winter visitors; north, centre, south B2 . Forests,<br />
scrub, agricultural land, towns, from lowlands to at least<br />
1800 m.<br />
Dicrurus annectans Crow-billed Drongo. Wet-season<br />
breeding visitor and probable passage migrant; north B9 ,<br />
centre B2 , south B9 . Evergreen forests and tall regrowth from<br />
lowlands to at least 960 m. Breeders were found in Dong<br />
Ampham NBCA in the late dry - early wet season 1997<br />
(Davidson et al. 1997). Records from prior to 1994 were summarised<br />
in Thewlis et al. (1996).<br />
Dicrurus aeneus Bronzed Drongo. Resident; north, centre,<br />
south B2 . Evergreen forests and tall secondary growth up to at<br />
least 1800 m.<br />
Dicrurus remifer Lesser Racket-tailed Drongo. Resident,<br />
some dispersing to lower altitudes in winter; north, centre,<br />
south B2 . Evergreen forests, generally above 500 m in breeding<br />
season; outside this season, <strong>of</strong>ten in tall secondary growth<br />
and down to plains.<br />
Dicrurus hottentottus Spangled Drongo (= Hair-crested<br />
Drongo, ^Sm, ^T). Resident, undertaking at least local movements;<br />
north, centre, south B2 . Forests, secondary growth,<br />
flowering trees amid cultivation; up to at least 1700 m.<br />
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