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Vegetation Changes along Altitudinal Gradients in Human Disturbed Forests of Uttara Kannada, Central Western Ghats
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1Energy and Wetlands Research Group, Centre for Ecological Sciences [CES], Indian Institute of Science, Bangalore – 560012, India.
2Department of applied Botany, Mangalore University, Mangalore
*Corresponding author:
cestvr@ces.iisc.ernet.in

MATERIAL AND METHODS

The study was carried out along altitudinal gradient from the coast (Ankola taluk, Uttara Kannada district) through undulating terrains of Yellapur (in Uttara Kannada district) to plains (Kalghatgi taluk bordering the Deccan plains in the Dharwad district). The vegetation was studied through sampling at 10 (S1, S2, to S10) different localities using point center quadrat (William 2006) along the varying topographies with diverse vegetation (Fig. 1, Table 1). The sampling localities S1 to S4 (Ankola to Ramanguli stretch with lower altitudes) comprised of a variety of terrestrial vegetation types, especially semi-evergreen to moist deciduous forests with several degraded and denuded areas with lateritic surface. The localities S5 to S7, (mid altitudes) located in the Ghats proper comprised of lofty evergreen to semi-evergreen forests forming a mosaic with other forest types such as moist deciduous and scrub savannah, the products of degradation of the original forest type.  The samples S8 to S10 (mid altitudes) fall in the eastern plains of Uttara Kannada and in Dharwar district which are mostly dotted with moist deciduous to dry deciduous forests owing to lower rainfall (Fig. 2).


Figure 1: Study area altitudinal gradient from coast to plains (Uttara Kannada and part of Dharwad district) with vegetation sampling points

Table 1: The geographical co-ordinates and vegetation types of the sectors in study area

S. No. Sectors Sampling points Taluk Altitude (m) Habitat type
1 S1 Kattangadde Ankola 59 Moist deciduous forest
2 Navgadde Ankola 108 Evergreen to Semi-evergreen forest
3 Agasur Ankola 56 Semi-evergreen to moist deciduous forest
4 S2 Balaikoppa Ankola 33 Moist deciduous forest
5 Mundigadde Ankola 28 Teak mixed moist deciduous forest
6 Badgon Ankola 28 Moist deciduous forest
7 S3 Hegdekoppa Ankola 48 Moist deciduous forest
8 Sabguli Ankola 96 Semi-evergreen
9 Kasinmakki Ankola 77 Moist deciduous forest
10 S4 Nuglegudda-Vajralli Yellapur 154 Semi to moist deciduous forest
11 Ramanguli Ankola 125 Moist deciduous forest
12 Mundegali Ankola 157 Moist deciduous forest
13 S5 Near Gidgar Yellapur 455 Semi-evergreen to moist deciduous forest
14 Kattangadde-Tarepal Yellapur 297 Moist deciduous forest
15 Yammalli Yellapur 438 Evergreen forest
16 S6 Tarekunte-Mattihakal Yellapur 394 Evergreen to semi-evergreen forest
17 Birgadde Yellapur 367 Semi-evergreen to evergreen forest
18 After Mulesal Yellapur 442 Semi-evergreen forest
19 S7 Arlihonda-Near Idugundi Yellapur 463 Evergreen to semi-evergreen forest
20 Kumarmane Yellapur 499 Moist deciduous forest
21 Nandvalli Yellapur 547 Semi-evergreen to moist deciduous forest
22 S8 Yellapur -Mundgod road Yellapur 536 Moist deciduous forest
23 Hosgadde Yellapur 548 Moist deciduous forest
24 Mavalli Yellapur 547 Moist deciduous forest
25 S9 Kunginkoppa Yellapur 543 Teak mixed moist deciduous forest
26 Near Kiruwathi Yellapur 534 Dry deciduous forest
27 After Kiruwathi Yellapur 524 Teak mixed moist deciduous forest
28 S10 After Sangtikoppa Dharwad 541 Teak mixed moist to dry deciduous forest
29 Before Devikoppa Dharwad 533 Teak mixed moist to dry deciduous forest
30 After Devikoppa Dharwad 530 Bamboo planted area


Fig. 2. Topographic features and vegetation associated with different sectors in the study region

The tree diversity in the sampling sites was studied using Point Centred Quarter sampling technique (Fig. 3) (James 2006). Each linear block of forested tract measured 13 km long area along the Ankola-Yellapur-Kalghatgi direction. Ten such linear blocks, totally covered 130 km long terrain from the coast, crossing the Ghats to the eastern plains (Fig. 1).  In each of this 13 km long block, three transects of 500 m length each were laid, thereby covering a survey area of 1.5 km in each sector. In each transect of 500 m length 10 point centred quarter samples were studied keeping an interval of 50 m between any two points. In each sample, in each of the four quarters demarcated on the ground, the distance to the nearest tree (minimum GBH of 30 cm) from the central point was measured. Thus data was derived on four trees at each point and the distances to these four trees from the central point. The mean distance to the trees was estimated by dividing the total distances to four trees by four from the point. The GBH and the height of the trees were noted down. At every 3rd point, the shrub layer (including shrubs and tree saplings above 1 m height) of 5 x 5 m was studied. The method was used for its fastness in coverage of long stretches of forest vegetation of heterogeneous and fragmented vegetation on account of centuries of human impacts like slash and burn cultivation, pastoralism, clear felling of timber for raising monocultures of mainly teak and eucalyptus and Acacias in later times and routine extraction of biomass for agricultural and domestic needs.  As the method has inherent quality of passing through all grades of forests in case of unbiased application along a longitudinal sampling course, a quick view on vegetation status, especially in terms of tree density and dominant species could be gained in limited time. The tree density was estimated by using the formula: Area/d2 and expressed in numbers per/ha; d is the average distance to the nearest trees in the four quarters of a cross from its central point, considering the average distances of all such points along any single transect.  Other ecological parameters such as Evergreeness, Endemism, Diversity etc., were computed. The various plant species encountered along the transect line and its periphery were also recorded so as not to miss the overall diversity. Other details regarding landscape type, altitude, vegetation disturbances, NTFP collections, fire occurrence, streams etc., were also noted. The revenue lands with cultivation, homesteads and grazing areas were excluded from the forest survey.


Fig.  3. Point centered Quadrat (Trees; i, ii, iii, iv- First, second, third and fourth quadrant; A-Direction of transect; B-distance of nearest trees from center of point centered quadrat)

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Citation : Rao G.R., Krishnakumar G., Sumesh N. Dudani, Subash Chandran M.D. and Ramachandra. T.V, 2013. Vegetation Changes along Altitudinal Gradients in Human Disturbed Forests of Uttara Kannada, Central Western Ghats., J Biodiversity, 4(2): 61-68 (2013).
* Corresponding Author :
Dr. T.V. Ramachandra
Energy & Wetlands Research Group, Centre for Ecological Sciences, Indian Institute of Science, Bangalore – 560 012, India.
Tel : +91-80-2293 3099/2293 3503 [extn - 107],      Fax : 91-80-23601428 / 23600085 / 23600683 [CES-TVR]
E-mail : cestvr@ces.iisc.ernet.in, energy@ces.iisc.ernet.in,     Web : http://wgbis.ces.iisc.ernet.in/energy, http://ces.iisc.ernet.in/grass
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