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7.4.5 Other Development Activities<br />

7.4.5.1 NTFPs<br />

While planning and carrying out the assessment of NTFPs, the following issues should be studied:<br />

7.4.5.2 TOF<br />

1. Identify and list the tree associated NTFP products, which can be surveyed as a part of the standard <strong>FRA</strong>, i.e.<br />

bark, leaves, fruit, etc.<br />

2. Find the NTFPs, whose habitat is known. Group these according to habitat types: altitude, east-west and habitat<br />

type matrix.<br />

3. Define indicators, which characterize these habitats. Indicators should preferably be such that they can be<br />

detected by means of remote sensing. Concise habitat mapping provides some information concerning<br />

production and harvest potential of these NTFP’s. Habitats can be used as sample units for further analysis and<br />

field surveys.<br />

4. The survey and its design should be made in close cooperation with local forest officials, traders, local healers,<br />

collectors, community forest user groups, local people, etc.<br />

5. Importance values and Prominence values will be used for the quantification of NTFPs.<br />

TOF can be classified according to occurrence as follows.<br />

Physiological<br />

shrubland<br />

Shrubland<br />

Degraded<br />

forests<br />

TOF<br />

Farmland, village squares,<br />

roadsides, terraces, etc.<br />

Other lands<br />

Forest patches/tree groups smaller than<br />

the defined minimum area for forests<br />

Basically, the standard field sample should cover the shrub land. In case of other areas, the advantage of more intensive use<br />

of high resolution satellite images (VHR) should be studied. As soon as the VHR images are available, the development of<br />

the method can be started. The final approach should be incorporated in the standard <strong>FRA</strong> applying two phase sampling with<br />

the necessary modifications in the field work procedures. It is assumed that TOF inventory can be incorporated in the<br />

national <strong>FRA</strong> from the beginning of the field inventory.<br />

7.4.5.3 Biodiversity<br />

Biological diversity in <strong>Nepal</strong> is very high. Thus, assessment of biodiversity is an extremely complex work. The assessment<br />

will concentrate on forest ecosystem, vegetation composition, forest types and habitats. The first activity will be to assess the<br />

appropriateness of the existing forest habitat classification in <strong>Nepal</strong>. The next activity would be the description of the habitat<br />

specific indicators (soil, climatic conditions, altitude range, associated indicator species, etc.).<br />

The key output of biodiversity assessment will be forest habitat and forest type classifications. Moreover, name of each forest<br />

type will be determined by ordering the Importance Values of each tree species. Importance Value will be obtained by<br />

summation of the relative frequency, relative density, and relative dominance (Krebs 1994). Relative dominance of trees will<br />

be determined by calculating the basal area. The coverage of ground flora will be calculated by converting the recorded cover<br />

percentage to midpoint cover classes according to Zobel et al. 1987.<br />

In case of grassland and shrub land Prominence Values (Dinerstein 1979) will be used for classification. Prominence Value<br />

will be calculated by multiplying mean percent cover with square root of frequency of same species. Further, the ultimate<br />

objective is to incorporate the biodiversity assessment (area and distribution of habitats) in the national <strong>FRA</strong> system.<br />

The project staffs responsible for implementation:<br />

CTA, NPC, Biodiversity Mapping Experts, Project Field Manager, JTA and respective short term experts and national<br />

counterparts will bear the responsibility.<br />

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