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Wildlife of Lao PDR: 1999 Status Report - IUCN

Wildlife of Lao PDR: 1999 Status Report - IUCN

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1965), but no detailed fauna has yet been written. Delacour<br />

(1940) wrote an interim list, as he was concerned that various<br />

mammal-related publications included fantasy. His own<br />

important collection <strong>of</strong> 1938-1939 was not then fully documented,<br />

and we have not traced any subsequent published<br />

overview <strong>of</strong> it. There are other post-Osgood collections which<br />

have never been written up. Examination <strong>of</strong> the accounts for<br />

‘big game’ species in Osgood (1932) indicates how scientific<br />

collectors ignored them in favour <strong>of</strong> the smaller ones,<br />

the assumption being that the ‘sportsmen’ would take care <strong>of</strong><br />

knowledge concerning them. There are indeed various hunting<br />

books on Indochina, some including <strong>Lao</strong> <strong>PDR</strong>, but nobody<br />

has yet produced a modern analysis <strong>of</strong> the faunistic<br />

information that they contain, or its reliability. Information<br />

as available has been incorporated here.<br />

The more recent Les mammifères du <strong>Lao</strong>s (the mammals<br />

<strong>of</strong> <strong>Lao</strong> <strong>PDR</strong>; Deuve 1972) built on a series <strong>of</strong> papers in the<br />

former <strong>Lao</strong> national scientific journal (Deuve 1961a, 1961b,<br />

Deuve and Deuve 1962a-1964d). However, the validity <strong>of</strong><br />

this work is compromised as methodology (how much fieldwork<br />

was undertaken and where, how much use was made<br />

<strong>of</strong> secondary reports, how identifications were confirmed,<br />

etc.) was not discussed. Deuve’s earlier papers show that some<br />

species were listed for <strong>Lao</strong> <strong>PDR</strong> simply because they were<br />

implied to be there in sources such as Tate’s (1947) Mammals<br />

<strong>of</strong> eastern Asia. Furthermore, Deuve largely ignored<br />

previous major works on the mammals <strong>of</strong> Indochina, e.g. he<br />

stated that no otters had been identified to species in north<br />

and south <strong>Lao</strong> <strong>PDR</strong>, but Osgood (1932) and Delacour (1940)<br />

listed various specimens from these regions. Even where<br />

Deuve’s work appears to have been original, trenchant errors<br />

with conspicuous species (for example those concerning<br />

the distribution, subspecies and <strong>Lao</strong> name <strong>of</strong> Douc<br />

Langur; Timmins and Duckworth in press) urge consideration<br />

<strong>of</strong> these records as unconfirmed.<br />

Recent Information<br />

Field surveys <strong>of</strong> large mammals for periods exceeding a<br />

week took place in 32 areas during 1991-1998 (Table 12,<br />

Fig. 7). The types <strong>of</strong> methodology used on these surveys and<br />

the balance between them varied widely between sites,<br />

depending on factors such as season, duration and goals <strong>of</strong><br />

the survey, characteristics <strong>of</strong> the survey area, and previous<br />

experience and personal inclination <strong>of</strong> the surveyor(s). In few<br />

areas could it be considered that a wide enough range <strong>of</strong> methods<br />

was used in sufficient depth to give a balanced overall<br />

view <strong>of</strong> the large mammal community. In many areas the<br />

backbone <strong>of</strong> mammal survey has been incidental opportunistic<br />

observation by day. Little direct nocturnal observation<br />

was undertaken at sites north <strong>of</strong> Phou Khaokhoay National<br />

Biodiversity Conservation Area (NBCA). Intensive sign<br />

searching was patchy. Camera-trapping (Plates 1, 14) was<br />

used at only a few sites. Mammal remains in village houses<br />

were examined extensively in relatively few areas.<br />

Large Mammals<br />

This list seeks to lay a reliable baseline for future work.<br />

Thus if there is any reasonable doubt over a piece <strong>of</strong> information,<br />

it is better left out. This situation is very different<br />

from that faced by the author <strong>of</strong> a management-oriented survey<br />

report, where any plausible information on key species<br />

should be included. If it is not, the species’s needs are unlikely<br />

to be incorporated into future management activities.<br />

Many indirect methods are used to record mammals, some<br />

<strong>of</strong> which do not give information <strong>of</strong> absolute reliability.<br />

Authors therefore phrase their findings appropriately. For<br />

example, Boonratana (1998a) wrote for Fishing Cat in Dong<br />

Hua Sao NBCA that “scats found on boulders close to streams<br />

... suggest that they belong to this species”. This indicates<br />

clearly that management <strong>of</strong> the NBCA should cater for the<br />

needs <strong>of</strong> Fishing Cat, even though the presence <strong>of</strong> the species<br />

remains to be confirmed. By contrast, defining the national<br />

range (geographical, altitudinal, habitat) <strong>of</strong> Fishing Cat<br />

can use only reliable records. What constitutes acceptable<br />

information varies between species, and depends also on the<br />

experience <strong>of</strong> the surveyor.<br />

Below follows some information about the two chief<br />

methods <strong>of</strong> indirect recording, local information and signs.<br />

Assessing local information about mammals has never been<br />

experimentally validated in Indochina. Some problems could<br />

be reduced by interviewers noting (in <strong>Lao</strong> script) the name<br />

used locally for the animal under discussion, rather than<br />

merely their assessment <strong>of</strong> which species they believe is under<br />

discussion. Even so, a given name may mean different<br />

animals in different areas. Furthermore, even with an unambiguous<br />

name, not all informants will know perfectly the identification<br />

characteristics <strong>of</strong> the animals about which they are<br />

speaking. Conceptual differences between scientifically based<br />

surveyors rooted in concepts such as gene-pools and diagnosable<br />

morphological characteristics, and rural hunters unconcerned<br />

by such things, are widespread. Considerable further<br />

work is necessary to understand the assumptions involved<br />

in using local information. The reliability <strong>of</strong> basic information<br />

concerning high pr<strong>of</strong>ile species (those valuable in trade,<br />

as food sources, dangerous to people and/or damaging to crops<br />

etc.) seems to be relatively high, especially if they are also<br />

visually distinctive (Annex 5). Reliability is low for species<br />

<strong>of</strong> little direct relevance to local informants, or where there<br />

are several closely-similar species, even when the species<br />

are economically important (e.g. muntjacs; Timmins et al.<br />

1998).<br />

Various recent incidents in <strong>Lao</strong> <strong>PDR</strong> exemplify the dangers<br />

<strong>of</strong> uncritical acceptance <strong>of</strong> local information, including:<br />

a charred gibbon skeleton (Plate 5) claimed to be that <strong>of</strong> a<br />

Douc Langur; the investigation at one site <strong>of</strong> recent Saola<br />

sightings by two people independently, which produced two<br />

lists <strong>of</strong> specific records (related to time and locality) with<br />

little congruence; claims several years apart from the same<br />

area that a certain event happened ‘recently, for the first time’;<br />

and others. These deliberately elementary examples (clearly,<br />

163

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