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 />
or other grey literature. The former have generally been<br />
checked more carefully prior to final printing. References<br />
frequently cited for distribution are abbreviated thus (recent):<br />
M8 Duckworth et al. (1994), M14 Bergmans (1995), M15 WCS<br />
(1995b), M9 Duckworth (1996a), M10 Timmins and Evans<br />
(1996), M11 Davidson et al. (1997), M12 Duckworth (1997a),<br />
M13 Duckworth (1998), M16 Showler et al. (1998b), M17 Robinson<br />
and Webber (1998a), and (historical) M18 Osgood (1932).<br />
Distribution maps would be <strong>of</strong> limited use for most species<br />
<strong>of</strong> large mammal at this stage. Confirmed records <strong>of</strong> most<br />
species are positioned essentially randomly across their range.<br />
There is no indication that the survey areas with records represent<br />
those in which the species is most common. Similarly,<br />
it is so difficult to see or otherwise find, say, Marbled Cats,<br />
that there is no reason to believe them absent from those survey<br />
areas with no records. Recent village-interview data are<br />
not amenable to mapping in the semi-quantitative style <strong>of</strong><br />
the first edition <strong>of</strong> this work (Salter 1993b, repeated here as<br />
Annex 5). Maps <strong>of</strong> predictive distribution would be entirely<br />
inappropriate in a work <strong>of</strong> this nature.<br />
Habitats are assigned from personal experience <strong>of</strong> the<br />
authors, using a loose classification (see Introduction).<br />
As habitat use <strong>of</strong>ten varies across a species’s range, every<br />
attempt is made to present information specific to <strong>Lao</strong> <strong>PDR</strong>,<br />
or derived from adjacent parts <strong>of</strong> Thailand, Cambodia and<br />
Vietnam. If there is no information from <strong>Lao</strong> <strong>PDR</strong>, this is<br />
stated.<br />
Key Species <strong>of</strong> Special Conservation Significance<br />
Key species (those <strong>of</strong> special conservation significance)<br />
are bulletted (• ). Global status information is from the 1996<br />
<strong>IUCN</strong> Red List <strong>of</strong> threatened animals (<strong>IUCN</strong> 1996). Globally<br />
Threatened species are listed (in increasing order <strong>of</strong> threat)<br />
as Vulnerable, Endangered or Critical. Globally Near-<br />
Threatened species are not yet believed to be Globally Threatened,<br />
but may soon be so if current trends continue. Data<br />
Deficient species are too poorly known for their conservation<br />
status to be assessed (see Conventions).<br />
National risk status categories have been assigned specifically<br />
for this report, the evaluations having been made by<br />
the authors in discussion with a number <strong>of</strong> experienced<br />
observers (R. J. Tizard, R. Steinmetz, S. Sawathvong, W. G.<br />
Robichaud and T. D. Evans). Species <strong>of</strong> large mammal confirmed<br />
or assumed to be still extant in <strong>Lao</strong> <strong>PDR</strong> are categorised<br />
as At Risk in <strong>Lao</strong> <strong>PDR</strong>, Potentially At Risk in <strong>Lao</strong> <strong>PDR</strong>,<br />
Little Known in <strong>Lao</strong> <strong>PDR</strong> or Not At Risk in <strong>Lao</strong> <strong>PDR</strong> (see<br />
Conventions). Assessments were made, following the guidelines<br />
<strong>of</strong> Thewlis et al. (1998), on the basis <strong>of</strong> observed and<br />
perceived threats to the species or its habitat together with<br />
perception <strong>of</strong> the species’s population level relative to the<br />
apparent carrying capacity <strong>of</strong> the habitat.<br />
Species Conditionally At Risk in <strong>Lao</strong> <strong>PDR</strong> are those which<br />
are not confirmed to occur in <strong>Lao</strong> <strong>PDR</strong> in the late 1990s but<br />
which, if present, are clearly at risk, e.g. rhinoceroses, Hog<br />
162<br />
Deer and Hairy-nosed Otter. They cannot logically be categorised<br />
as at risk, as this term would imply their presence in<br />
<strong>Lao</strong> <strong>PDR</strong>. If there is no clear rationale for a species with no<br />
confirmed <strong>Lao</strong> records to be considered at risk in <strong>Lao</strong> <strong>PDR</strong>,<br />
it is not assigned a national risk category, even if it is currently<br />
considered Globally Threatened (e.g. Red Panda).<br />
All species <strong>of</strong> large mammal with confirmed records for<br />
<strong>Lao</strong> <strong>PDR</strong> and not assigned a risk category are considered to<br />
be Not At Risk in <strong>Lao</strong> <strong>PDR</strong> at the current time. If any species<br />
unconfirmed to occur in <strong>Lao</strong> <strong>PDR</strong> is recorded in the future,<br />
its national risk category would need to be established. Most<br />
such species would be likely to qualify for at least Little<br />
Known in <strong>Lao</strong> <strong>PDR</strong>.<br />
Four species listed as <strong>of</strong> special conservation concern in<br />
the first edition (Salter 1993b) were not retained as key species<br />
in this edition. Recent surveys show that Leopard Cat,<br />
Variable Squirrel and Cambodian Striped Squirrel are clearly<br />
not at risk. There is neither evidence that Intermediate Loris<br />
inhabits <strong>Lao</strong> <strong>PDR</strong>, nor grounds for assuming that if it does, it<br />
is at risk. The supposition that Grey Wolf occurred in <strong>Lao</strong><br />
<strong>PDR</strong> may have been an error.<br />
A recommended list <strong>of</strong> key species <strong>of</strong> mammals for use<br />
in future work in <strong>Lao</strong> <strong>PDR</strong> is given in Annex 6. National<br />
species conservation priorities are presented in Table 6. Key<br />
species occurrence in each recent survey area is given in<br />
Table 12. A status summary, usually with detail for less widely<br />
available records, has been included under each key species<br />
account.<br />
Proposed Conservation Management and Research<br />
Measures<br />
A synopsis <strong>of</strong> proposed conservation measures is provided<br />
for key species, usually presented by group. As well as<br />
the specific recommendations, there is a general need for<br />
further information on the distribution, abundance and particularly<br />
the habitat-use and altitudinal range <strong>of</strong> many species,<br />
and for active management <strong>of</strong> <strong>Lao</strong> <strong>PDR</strong>’s protected area<br />
system to maintain viable populations <strong>of</strong> mammals.<br />
CITES-listed and Restricted-range Species<br />
CITES information is from the Checklist <strong>of</strong> CITES<br />
species (WCMC 1998). Except for Northern Treeshrew and<br />
Leopard Cat, all CITES-listed species occurring in <strong>Lao</strong> <strong>PDR</strong><br />
(Annex 3) are key species and so receive a status review.<br />
Species with restricted ranges (local or regional endemics)<br />
are highlighted, to indicate the significance <strong>of</strong> the <strong>Lao</strong> range<br />
to the conservation <strong>of</strong> the species. Extralimital ranges are<br />
not given for other, more widespread, species.<br />
Historical Sources<br />
There is little historical information on mammals <strong>of</strong> <strong>Lao</strong><br />
<strong>PDR</strong>. Osgood (1932) summarised the then available material<br />
and several subsequent reviews <strong>of</strong> taxonomic groups<br />
include <strong>Lao</strong> material (e.g. diurnal squirrels: Moore and Tate