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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 />

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

north (historically B21 ), centre (historically B22 ), south B14 .<br />

Open and lightly wooded country. <strong>Status</strong> Information:<br />

Records prior to 1997 were reviewed by Thewlis et al. (1998).<br />

This species was historically widespread and common but<br />

recent records come only from southern Champasak and<br />

Attapu Provinces. Numbers are small (the largest flock seen<br />

recently comprised at least ten birds). Most records are from<br />

within or adjacent to proposed or existing NBCAs (Table<br />

11), but the species has also been seen recently near Ban<br />

Hangkhon (Champasak Province; Cunningham 1998) and<br />

between Senamsai and Ban Sompoy (Xe Pian NBCA), Attapu<br />

Province (1-13 in December 1997; Robichaud 1998e).<br />

Circaetus gallicus Short-toed Snake Eagle (= Short-toed<br />

Eagle, ^K, ^T). Winter visitor; north B9 , south B2 . Potentially<br />

over most open habitats. First recorded for <strong>Lao</strong> <strong>PDR</strong> in 1993<br />

(Thewlis et al. 1996); two subsequent records (Duckworth<br />

et al. 1998a, Round 1998). Special Significance: CITES<br />

Appendix II.<br />

Spilornis cheela Crested Serpent Eagle. Resident, making<br />

local movements; north, centre, south B2 . Evergreen and<br />

deciduous forests, including degraded and fragmented areas;<br />

up to at least 1800 m. S. bassus was separated as a species by<br />

Stepanjan (1992). Although no records were given from <strong>Lao</strong><br />

<strong>PDR</strong>, the distribution elsewhere indicates that it would<br />

occur. However, further details are needed to assess the<br />

validity <strong>of</strong> this separation. Special Significance: CITES Appendix<br />

II.<br />

Circus aeruginosus Eurasian Marsh Harrier (named as a<br />

subspecies C. a. spilonotus Eastern Marsh Harrier by ^K;<br />

separated as C. spilonotus Eastern Marsh Harrier by ^Sm,<br />

^T). Winter visitor; north B9 , centre B10 , south B2 . Open country,<br />

overwhelmingly wetlands. All <strong>Lao</strong> records are <strong>of</strong> C. a.<br />

spilonotus; C. a. aeruginosus might also occur as a rare visitor.<br />

The two forms are <strong>of</strong>ten regarded as separate species (see<br />

Inskipp et al. 1996). Special Significance: CITES Appendix<br />

II.<br />

Circus cyaneus Hen Harrier (= Northern Harrier, ^K, ^Sm,<br />

^T). Winter visitor; north (Salter 1989a), centre B9 . Open country,<br />

especially wetlands. Records prior to 1996 were reviewed<br />

by Duckworth et al. (1998a). Special Significance: CITES<br />

Appendix II.<br />

Circus melanoleucos Pied Harrier. Winter visitor; north B2 ,<br />

centre (provisionally B10 ; historically B22 ), south B2 . Open country,<br />

especially wetlands. Special Significance: CITES Appendix<br />

II.<br />

Accipiter trivirgatus Crested Goshawk. Resident; north,<br />

centre, south B2 . Evergreen forests, even quite encroached<br />

120<br />

areas, up to at least 1750 m. Special Significance: CITES<br />

Appendix II.<br />

Accipiter badius Shikra. Resident; north, centre, south B2 .<br />

Open wooded areas, <strong>of</strong>ten near cultivation and villages;<br />

among natural habitats, it seems to be commonest in open<br />

mixed deciduous forest. Generally low-mid altitudes. Special<br />

Significance: CITES Appendix II.<br />

Accipiter soloensis Chinese Sparrowhawk (= Chinese Goshawk,<br />

^K, ^Sm, ^T). Passage migrant and local winter visitor;<br />

north, centre, south B9 . May be seen over any habitat.<br />

Records prior to 1996 were reviewed by Duckworth et al.<br />

(1998a). Special Significance: CITES Appendix II.<br />

Accipiter gularis Japanese Sparrowhawk. Presumed passage<br />

migrant; north B7 , south B2 . Any habitat, including towns.<br />

<strong>Status</strong> assessment is handicapped by difficulties <strong>of</strong> identification,<br />

particularly from Besra. Delacour and Jabouille (1940)<br />

implied that the species occurs in central <strong>Lao</strong> <strong>PDR</strong>, but we<br />

have not traced a primary source. Special Significance: CITES<br />

Appendix II.<br />

Accipiter virgatus Besra. Seasonal status unclear, but presumed<br />

resident; north B9 , centre B7 , south B2 . Forested and<br />

wooded areas from 200 to at least 1240 m. <strong>Status</strong> assessment<br />

is handicapped by difficulties <strong>of</strong> identification. Special<br />

Significance: CITES Appendix II.<br />

Accipiter nisus Eurasian Sparrowhawk (= Northern<br />

Sparrowhawk, ^K, ^T). Winter visitor; north (provisionally B9 ;<br />

historically B21 ), centre (provisionally B9 ; historically B22 ). Habitat<br />

use in <strong>Lao</strong> <strong>PDR</strong> unclear. <strong>Status</strong> assessment is handicapped<br />

by difficulties <strong>of</strong> identification. South <strong>Lao</strong> <strong>PDR</strong> was included<br />

in the species’s range by Delacour and Jabouille (1940), but<br />

we have not traced a primary record. Special Significance:<br />

CITES Appendix II.<br />

• Butastur liventer Rufous-winged Buzzard. Conservation<br />

Significance: Globally Near-Threatened; CITES Appendix<br />

II. Not At Risk in <strong>Lao</strong> <strong>PDR</strong>. Documented Range and Habitat:<br />

Resident; north, centre, south B14 . Open deciduous wooded<br />

areas (particularly dry dipterocarp forest) and open secondary<br />

growth, chiefly <strong>of</strong> lowlands and lower hills. <strong>Status</strong> Information:<br />

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

al. (1998). Small numbers remain widespread (there are<br />

records from 11 recent survey areas; Table 11), both within<br />

and outside NBCAs. Phou Xang He, Xe Bang-Nouan and<br />

Xe Pian NBCAs and Dong Khanthung PNBCA all support<br />

large populations. Historically it was relatively common in<br />

suitable habitats. This is still so and as the species occupies<br />

degraded habitats, it should be considered Not At Risk in<br />

<strong>Lao</strong> <strong>PDR</strong>.

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