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

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3.4 Discussion<br />

3.4.1 Description of vegetation types found within the regeneration and<br />

administrative zones (II and III) of <strong>Kim</strong> <strong>Hy</strong> P.N.R.<br />

The north and north-eastern region of the proposed nature <strong>Reserve</strong>, which <strong>co</strong>mprise the<br />

regeneration and administrative areas and which are to a greater extent excluded in the<br />

proposal by FREC, are <strong>co</strong>mprised of a patchwork of vegetation types, largely derivatives<br />

of, or directly threatened by, human activity. The land-<strong>co</strong>ver has been classified by FIPI<br />

(1997) into various categories depending primarily upon level of human impact and<br />

potential for regeneration or rehabilitation. Aside from hill cultivation and the relatively<br />

extensive areas of paddy rice adjoining highway 279 and its associated settlements in<br />

Luong Thuong and Lang San, the principle FIPI categories are summarised in Figure 3.5<br />

overleaf. Much of the northern area is classified on FIPI maps as ‘non-permanent forest’,<br />

indicating the mosaic of regenerative habitats, and which has been included in the<br />

classification of ‘scrub with scattered trees’ in Map 3 of this report.<br />

The areas of scrub with few or no trees are mainly in Luong Thuong and Lang San’s<br />

northern and eastern areas as well as much of eastern An Tinh, which <strong>co</strong>mprises the main<br />

body of the administrative/service zone, i.e. much of the accessible east and south-east of<br />

the P.N.R. This habitat is also found scattered in northern parts of <strong>Kim</strong> <strong>Hy</strong> <strong>co</strong>mmune<br />

(sub-regions 172 and 165), and it is largely a <strong>co</strong>nsequence of previous slash and burn<br />

practices of local populations during the 1980s and to a lesser extent the 1990s. It has had<br />

little chance to regenerate and the ferralitic soil supporting it is typically dry and<br />

exhausted, with little water retention capacity. This results in the many grassland species<br />

growing there, such as Ormosia balansae and Psychotria sp., which regularly dry out in<br />

the winter months. These areas also typically support herbaceous <strong>co</strong>mmunities of<br />

Mimosa, Crotalaria and Desmodium (Fabaceae). In some areas, this scrub savannah is<br />

adjacent to areas of settlement, rice paddy and hill cultivation, and is currently serving as<br />

fallow ground awaiting future cultivation, or as grazing for domestic ruminants (buffalo<br />

and, to a lesser degree, cattle). In cases where grazing of ruminants is not regulated<br />

(leading to over-grazing), grass species of low forage value such as Chrysopogon sp. and<br />

Paspalum <strong>co</strong>njugatum tend to <strong>co</strong>lonise. Invasions of inedible Imperata cylindrica and<br />

Chromolena odorata more <strong>co</strong>mmonly invade when the pastures are not maintained<br />

(Castella et al, 2001). In the FREC revised proposal’s south-western area in Bach Thong<br />

district, degraded scrub land forms much of the land area bordering the poor forest and<br />

the relatively extensive areas of hill cultivation in Cao Son <strong>co</strong>mmune, due to a historical<br />

shortage of paddy land and lack of technical development in agriculture in that region,<br />

which has led to the intensive use of the non-karst hillsides.<br />

<strong>Frontier</strong> Vietnam Forest Research Programme Technical Report No.24. 29

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