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Kim Hy Proposed Nature Reserve - Frontier-publications.co.uk

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substratum was jagged limestone. Collection generally took place between 0800 and<br />

1600 hours, on <strong>co</strong>nsecutive days where possible.<br />

Canopy traps: As described by Austin and Riley (1995). These were used at all survey<br />

sites within the limestone forest area in order to ac<strong>co</strong>unt for those species which feed<br />

(and therefore tend to fly) in the upper/upper middle storeys of the forest. They were<br />

generally hung at between 15 and 20m above ground level. Over-ripe fruit, fermented<br />

al<strong>co</strong>hol, sugar and sugar-based food was used as bait, both independently and mixed, and<br />

to varying levels of success. Traps were checked at sunrise and sunset.<br />

In both of the above methods, butterfly specimens were taken after a preliminary field<br />

identification by applying pressure to the thorax to kill the individual, and storing the<br />

specimens in airtight <strong>co</strong>ntainers <strong>co</strong>ntaining drying agents paradichlorobenzene and silica<br />

gel.<br />

Identifications were made by A. Monastyrskii of the Vietnam-Russia Tropical Centre in<br />

Hanoi. Taxonomy and Nomenclature follow Pinratana (1977-96) and Corbet and<br />

Pendlebury (1992), with variations in<strong>co</strong>rporated from more recent works.<br />

4.1.3 Results<br />

A total of 93 species of butterfly (from 403 identifications) were re<strong>co</strong>rded for this survey<br />

period: a full list of these is provided in Appendix 3. The species <strong>co</strong>mprise nine families:<br />

the Papilionidae (11 species), Pieridae (12 species), Danaidae (7 species), Satyridae (13<br />

species), Amathusiidae (4 species), Nymphalidae (24 species), Acraeidae (1 species),<br />

Lycaenidae (16 species) and Hesperiidae (5 species).<br />

4.1.4 Discussion<br />

4.1.4.1 Species richness<br />

The number of butterfly species re<strong>co</strong>rded in <strong>Kim</strong> <strong>Hy</strong> proposed <strong>Nature</strong> <strong>Reserve</strong> was<br />

significantly lower than other sites of similar forest type and habitat quality. For example,<br />

<strong>Frontier</strong> surveys of a similar length at Na Hang <strong>Nature</strong> <strong>Reserve</strong> (Hill, 1997), Ben En<br />

National Park (Tordorff et al, 2000) and Ba Be National Park (Hill et al, 1997) yielded<br />

143, 168 and 167 species respectively. In <strong>co</strong>ntrast to Huu Lien <strong>Nature</strong> <strong>Reserve</strong>, which<br />

<strong>co</strong>ntains a wealth of butterfly species - 181 were re<strong>co</strong>rded on the <strong>Frontier</strong> survey there in<br />

2000 (Furey et al, 2002) – <strong>Kim</strong> <strong>Hy</strong> was not found to be especially diverse on this survey,<br />

which spanned both wet and dry seasons and all existing habitats. The reasons for this are<br />

unclear, as survey effort may be <strong>co</strong>nsidered to be <strong>co</strong>mparable to the above mentioned<br />

surveys It seems at this stage premature to <strong>co</strong>nclude that this result indicates an actual<br />

poverty in species diversity, and may be more linked with the predominant habitat type<br />

surveyed on the <strong>Frontier</strong> expeditions (see section 4.1.4.3 on habitat preferences below).<br />

More than 90% of captures were made using hand nets, which may mean that a number<br />

of canopy species were missed in this survey. It is highly unlikely that the species list<br />

<strong>Frontier</strong> Vietnam Forest Research Programme Technical Report No.24. 43

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