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Wildlife of Lao PDR: 1999 Status Report - IUCN

Wildlife of Lao PDR: 1999 Status Report - IUCN

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National risk status categories are based upon ‘The conservation<br />

status <strong>of</strong> birds in <strong>Lao</strong>s: a review <strong>of</strong> key species’<br />

(Thewlis et al. 1998), issued as a special supplement <strong>of</strong> the<br />

journal Bird Conservation International. Species are categorised<br />

into At Risk in <strong>Lao</strong> <strong>PDR</strong>, Potentially At Risk in <strong>Lao</strong><br />

<strong>PDR</strong> and Little Known in <strong>Lao</strong> <strong>PDR</strong>. Some species were considered<br />

by Thewlis et al. (1998) to be Not At Risk in <strong>Lao</strong><br />

<strong>PDR</strong>, but many species were not assessed. Their analysis was<br />

limited to species <strong>of</strong> global conservation concern (in Collar<br />

et al. 1994, or its predecessor Collar and Andrew 1988), those<br />

highlighted by Round (1988) and/or Treesucon and Round<br />

(1990) as being At Risk or Rare in Thailand, and those for<br />

which, within remaining habitat in <strong>Lao</strong> <strong>PDR</strong>, a clear decline<br />

was perceptible when recent records were compared with<br />

those in historical sources.<br />

Thewlis et al. (1998) did not consider information gathered<br />

after 31 December 1996. Therefore the present work<br />

modifies their list to incorporate information and insights up<br />

to 28 February <strong>1999</strong>. Only 11 presumed resident species<br />

recorded historically in <strong>Lao</strong> <strong>PDR</strong> have not been found in the<br />

field since 1990 and were not listed by Thewlis et al. (1998)<br />

as key species. All 11 are categorised here as Little Known<br />

in <strong>Lao</strong> <strong>PDR</strong>. While for some <strong>of</strong> these species there is no a<br />

priori reason to assume that they are not secure in <strong>Lao</strong> <strong>PDR</strong><br />

(particularly montane species), listing as Little Known is intended<br />

to stimulate publication <strong>of</strong> any recent records so that<br />

a considered judgement can be made in future. This policy is<br />

confined to resident species, as many non-breeding visitors<br />

to <strong>Lao</strong> <strong>PDR</strong> occur only irruptively or irregularly. Little purpose<br />

would be served by designating as key species all those<br />

lacking recent records. Other key species newly listed as such<br />

here have populations which seem at lower density than would<br />

be expected and/or (using the criteria in Thewlis et al. 1998)<br />

a clear threat is operating. Limited <strong>Lao</strong> range alone has not<br />

been considered a sufficient criterion, because for some such<br />

species (e.g. Yellow-vented Bulbul) there is no evidence that<br />

they are at risk. All unclassified species are considered to be<br />

Not At Risk in <strong>Lao</strong> <strong>PDR</strong>, but this categorisation is stated<br />

explicitly in the species accounts only for those species<br />

considered to be Globally Threatened or Near-Threatened<br />

by Collar et al. (1994).<br />

Assessments are made only for species. The limited information<br />

available on threat levels for subspecies has been<br />

included and referenced to source, but no original synthesis<br />

has been attempted here. A revised list <strong>of</strong> key species in <strong>Lao</strong><br />

<strong>PDR</strong> is given in Annex 6. Table 10 details changes to the<br />

classification from that <strong>of</strong> Thewlis et al. (1998).<br />

Several species are still recorded frequently and are under<br />

no immediate threat, but if apparent or likely recent declines<br />

continue, they may merit conservation attention. The<br />

historical and recent status <strong>of</strong> these should be reviewed in<br />

the style <strong>of</strong> Thewlis et al. (1998) as soon as possible. These<br />

species include: Lesser Whistling-duck, Oriental Pied<br />

Hornbill, Red-breasted Parakeet, Grey-headed Parakeet, Red<br />

Birds<br />

Collared Dove, Red-wattled Lapwing and Large-billed Crow.<br />

The status <strong>of</strong> several other species remains unclear, and they<br />

could plausibly be under decline. These include: Brown Wood<br />

Owl, Savanna Nightjar, Wedge-tailed Green Pigeon, Mountain<br />

Imperial Pigeon, Slaty-breasted Rail, Ruddy-breasted<br />

Crake, Greater Painted-snipe, Collared Falconet, Vinousbreasted<br />

Starling and Hwamei. Additionally, the status <strong>of</strong><br />

Ratchet-tailed Treepie and Hill Myna should be assessed at<br />

regular intervals. Compilers <strong>of</strong> future survey reports could<br />

usefully detail information on these species to aid future<br />

review.<br />

A status summary, usually with detail for less widely<br />

available records, is included under each key species account.<br />

Key species occurrence in each recent survey area is given<br />

in Table 11. Thewlis et al. (1998) detailed all records, historical<br />

and recent, <strong>of</strong> which they were aware for all species<br />

included in their review, and information for the 1992-1996<br />

period is specifically referenced to this source only where<br />

necessary to prevent ambiguity. It is envisaged that a similar<br />

treatment will be published elsewhere for the species newly<br />

designated here as key species. Therefore, information here<br />

is merely in sufficient detail to validate the categorisation.<br />

Proposed Conservation Management and Research<br />

Measures<br />

A synopsis <strong>of</strong> conservation requirements is given for key<br />

species. Major needs for action are usually summarised by<br />

group. As well as the specific recommendations, there is a<br />

general need for further information on (1) the distribution,<br />

abundance and particularly the seasonality <strong>of</strong> many species<br />

and (2) trade in all species, to allow refinement <strong>of</strong> conservation<br />

measures. Many species require active management <strong>of</strong><br />

<strong>Lao</strong> <strong>PDR</strong>’s protected area system to maintain viable<br />

populations. National species conservation priorities are identified<br />

in Table 6.<br />

CITES-listed and Restricted-range Species<br />

CITES information is from WCMC (1998). Species are<br />

indicated as being listed in Appendices I or II as appropriate<br />

(see Conventions). As many CITES-listed species are common<br />

and widespread, surveyors have not specifically detailed<br />

field records <strong>of</strong> all species in survey reports. Therefore, comprehensive<br />

review <strong>of</strong> status information <strong>of</strong> the latter species<br />

is impracticable and anyway would be <strong>of</strong> limited use. All<br />

species in these appendices which are known from <strong>Lao</strong> <strong>PDR</strong><br />

are listed in Annex 3.<br />

Breeding ranges are given for resident species with restricted<br />

global ranges (local or regional endemics), to indicate<br />

the significance <strong>of</strong> the <strong>Lao</strong> range to the conservation <strong>of</strong><br />

the species. Extralimital ranges are not therefore given for<br />

other species, which are all more widespread. World ranges<br />

are taken from Sibley and Monroe (1990) with modifications.<br />

Indochina indicates <strong>Lao</strong> <strong>PDR</strong>, Cambodia and Vietnam. Southeast<br />

Asia includes Myanmar, Thailand and peninsular Malaysia<br />

as well as Indochina.<br />

75

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