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A Feasibility Study for the Establishment of Xuan Lien Nature ...

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4. Management Considerations<br />

4.1 Physical Factors<br />

Topography. The topography <strong>of</strong> <strong>the</strong> proposed nature reserve is deeply dissected by a number <strong>of</strong> stream and<br />

rivers, which flow into <strong>the</strong> Cao River in <strong>the</strong> north and into <strong>the</strong> Khue River in <strong>the</strong> south (both are tributaries <strong>of</strong><br />

<strong>the</strong> Chu River). Such steep topography creates difficulties <strong>for</strong> constructing <strong>the</strong> infrastructure necessary <strong>for</strong> a<br />

protected area, such as guard stations, and <strong>for</strong> carrying out management activities, such as en<strong>for</strong>cement <strong>of</strong> <strong>for</strong>est<br />

rules and regulations. Adequate planning <strong>of</strong> both <strong>the</strong> location and type <strong>of</strong> infrastructure is required, and particular<br />

consideration should be given to <strong>the</strong> steep topography.<br />

Climate. The area has a tropical monsoon climate, with rainfall concentrated in <strong>the</strong> three months from July to<br />

September and <strong>the</strong> highest rainfall during August. Floods <strong>of</strong>ten occur at <strong>the</strong>se times, causing obstacles to <strong>the</strong><br />

management and protection <strong>of</strong> <strong>the</strong> nature reserve. The dry season is from November to April, and accounts <strong>for</strong><br />

only 10% <strong>of</strong> <strong>the</strong> total annual rainfall. During <strong>the</strong> dry season, <strong>the</strong> area is exposed to hot, dry winds blowing from<br />

Laos. During this period, <strong>the</strong>re is an increased risk <strong>of</strong> <strong>for</strong>est fire, caused by slash-and-burn agricultural practices.<br />

Consequently, <strong>the</strong> nature reserve management must implement measures to prevent and control <strong>for</strong>est fires,<br />

particularly in <strong>for</strong>est areas below 700 m. These measures should include raising awareness about <strong>the</strong> dangers <strong>of</strong><br />

fire and establishing fire-prevention teams in each commune.<br />

4.2 Biological Factors<br />

Management <strong>of</strong> Forest Patches. The majority <strong>of</strong> mammals and birds in <strong>the</strong> proposed nature reserve depend<br />

upon evergreen <strong>for</strong>est. The only significant undisturbed areas <strong>of</strong> this habitat type occur above 700 m. The first<br />

priority in establishing and managing <strong>the</strong> nature reserve should be to protect and conserve existing primary<br />

<strong>for</strong>est patches in order to provide a refuge <strong>for</strong> species dependent upon evergreen <strong>for</strong>est. These species include<br />

Tiger, Clouded Leopard, Asiatic Black Bear, Roosevelt’s Muntjac, and White-cheeked Gibbon.<br />

Fur<strong>the</strong>r Research. Although populations <strong>of</strong> several threatened and endemic mammal and bird species have been<br />

found in <strong>the</strong> proposed nature reserve, <strong>the</strong>se populations have not been studied in sufficient detail to understand<br />

<strong>the</strong>ir distribution and ecology. The biodiversity data outlined in this report are only initial results and a more<br />

detailed research programme is essential in order to provide data <strong>for</strong> effective conservation management. Such a<br />

programme should include detailed surveys <strong>of</strong> mammal, bird, reptile and amphibian populations, with particular<br />

attention given to Roosevelt’s Muntjac and threatened species. Future biodiversity survey work should take place<br />

in <strong>the</strong> spring when conditions are most favourable.<br />

4.3 Socio-cultural Factors<br />

Hunting and Trapping. At present, <strong>the</strong>re is insufficient in<strong>for</strong>mation on <strong>the</strong> populations <strong>of</strong> nationally or globally<br />

threatened animal species to develop a long-term plan <strong>for</strong> <strong>the</strong>ir conservation. However, hunting and trapping <strong>of</strong><br />

mammals and birds by villagers continues in Ban Vin village, and it will be necessary to take measures reduce and<br />

possibly eliminate <strong>the</strong> impact <strong>of</strong> <strong>the</strong>se unlawful activities. These measures should include en<strong>for</strong>cement <strong>of</strong> regulations<br />

on <strong>the</strong> possession <strong>of</strong> firearms and patrols to check trap laying during <strong>the</strong> trapping season from September to<br />

March.<br />

Logging and Forest Clearance. Forest areas above 700 m have steep slopes and soils prone to erosion if <strong>the</strong><br />

vegetation cover is removed. Once soil erosion has taken place, regeneration <strong>of</strong> <strong>the</strong> natural vegetation is impeded.<br />

The nature reserve management must seek to control <strong>for</strong>est clearance at higher elevations, in order to protect <strong>the</strong><br />

integrity <strong>of</strong> <strong>the</strong> <strong>for</strong>est. Fur<strong>the</strong>rmore, it will be necessary to control logging and <strong>for</strong>est clearance along <strong>the</strong> Chu<br />

and Khao Rivers by local people from Hon Yen and Ban Vin villages if <strong>the</strong> catchments <strong>of</strong> <strong>the</strong>se important water<br />

sources are to be protected.<br />

The conifers Fokienia hodginsii and Cunninghamia konishii have high economic value and, consequently, most<br />

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