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Ecological, Social and Commercial Role of Lichens in India with ...

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Acdemia Arena 2010, Supplement 0201<br />

http://www.sciencepub.net<br />

Potentilla fulgens - 92000 54000 - 425 - - 114000<br />

Sellag<strong>in</strong>ella sp - - 172800 - - - - -<br />

Lentanasp - - 100800 - - - 100800 18400<br />

Saxifraga <strong>and</strong>ersonii - - - 16800 30800 - - -<br />

Potentilla fulgens - - - 32800 - - - -<br />

Valeriana jatamansi - - - 100800 - - 16000 44800<br />

Impat<strong>in</strong>s thomsonii - - - 378000 - 68800 - -<br />

Pteris cretica - - - - - - 104000 60000<br />

Gaultheria nummylariodes - - - - - - - 290800<br />

Nardostachys jatamansi - - - - - - - 74800<br />

• Locally identified<br />

DISCUSSION<br />

The present study area is located <strong>in</strong> the altitud<strong>in</strong>al range <strong>of</strong> 2500-3500m <strong>and</strong> divisible <strong>of</strong> 8<br />

different study sites on the basis <strong>of</strong> various disturbances such as graz<strong>in</strong>g, brows<strong>in</strong>g, litter removal<br />

<strong>and</strong> lopp<strong>in</strong>g. Quercus semecarpifolia <strong>and</strong> Rhododendron arboreum are the dom<strong>in</strong>ant tree species <strong>in</strong><br />

all study sites. Giri, et al (2008) reported, the total tree density ranged from 320 to 1560 <strong>in</strong>d ha⎯¹ <strong>in</strong><br />

Quercus leucotrichophora forest <strong>and</strong> 320 to 1960 <strong>in</strong>d ha⎯¹ <strong>in</strong> Quercus floribunda forest, but it was<br />

not recorded <strong>in</strong> Quercus semecarpifolia forest. The total tree density ranged from 323-2488 <strong>in</strong>d<br />

ha⎯¹, total sapl<strong>in</strong>g density from 0-645 <strong>in</strong>d ha⎯¹ <strong>and</strong> seedl<strong>in</strong>g density from 0-692 <strong>in</strong>d ha⎯¹ were<br />

recorded <strong>in</strong> present study sites. The tree density was comparatively high than the value <strong>of</strong> other oak<br />

reported by Giri, et al (2008). Anthropogenic disturbances change the vegetation structure <strong>and</strong><br />

regeneration status <strong>of</strong> a particular forest. The anthropogenic pressure on Quercus semecarpifolia<br />

forest for firewood, fodder <strong>and</strong> timber, play an important role <strong>in</strong> decl<strong>in</strong>ation <strong>of</strong> forest together <strong>with</strong><br />

lichen moss collection. Various levels <strong>of</strong> disturbances cause the <strong>in</strong>crease <strong>in</strong> community species<br />

richness. This is because disturbances prevents dom<strong>in</strong>ance by a few competitive species <strong>and</strong> allows<br />

opportunistic species to <strong>in</strong>vade.<br />

In the present years the awareness regard<strong>in</strong>g to conservation <strong>of</strong> flora <strong>and</strong> fauna among the<br />

local community <strong>and</strong> <strong>in</strong> people resid<strong>in</strong>g <strong>in</strong> the forest has helped <strong>in</strong> a large extend <strong>in</strong> protect<strong>in</strong>g the<br />

forest <strong>in</strong> this area. The tendency <strong>of</strong> the people have changed as they are earn<strong>in</strong>g their livelihood<br />

regularly from forest by some alternative (sell<strong>in</strong>g milk, firewood by utiliz<strong>in</strong>g the forest foliage)<br />

<strong>in</strong>stead <strong>of</strong> destroy<strong>in</strong>g trees.<br />

32

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