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Forestry research activities |
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7.ECOLOGICAL STUDIES |
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7.1 LINEAR Tree Increment Plots (LTI Plots) |
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Concerted effort all over the country for laying Tree increment plots took shape subsequent to the adoption of the resolution in the third Silvicultural Conference held at Deharadun in the year 1929. It recommended establishment of plots on a long-term basis. During the 1930s' Forest Research Institute, Deharadun laid a large number of plots in different parts of the country in evergreen forests. Another effort was made in 1950s' when Mr. Quereshi the then Silviculturist, Pune, set up 16 Linear Tree Increment plots around Dandeli in Uttara Kannada district. Now there are altogether 15 LTI plots in moist deciduous forests, 7 in evergreen forests and 5 preservation plots in Karnataka. Once in 5 years growth data is being recorded. The main object is to study the diameter incremental of different species under natural conditions. Besides, status of natural regeneration is also being studied in these plots. The details of LTI plots in the state are given in Table 33. |
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Dr. S.N.Rai, with the assistance of UNESCO reviewed the 'Long Term Research Sites of Tropical Forests of India ' in the year 1996, and the study was published as a book by UNESCO Delhi titled “Long Term Research Sites in Tropical Forest of India”. |
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Linear Tree Increment and Preservation plots in Karnataka |
Sl.No |
LTI Plot No. |
Locality |
Range |
Year of formation |
Breadth & length in chain |
Extent in
ha |
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1 |
1 |
Raulwada |
Barchi |
1950 |
1 x 80 |
3.20 |
2 |
2 |
Usoda |
Barchi |
1950 |
1 x 80 |
3.20 |
3 |
3 |
Shingatgeri |
Barchi |
1950 |
1 x 80 |
3.20 |
4 |
4 |
Karka |
Dandeli |
1950 |
1 x 80 |
3.20 |
5 |
6 |
Bailpur |
Virnoli |
1950 |
1 x 80 |
3.20 |
6 |
7 |
Veerampalli |
Virnoli |
1950 |
1 x 80 |
3.20 |
7 |
8 |
Aurla |
Gund |
1950 |
1 x 80 |
3.20 |
8 |
9 |
Shiroli |
Virnoli |
1950 |
1 x 80 |
3.20 |
9 |
10 |
Phansoli |
Virnoli |
1950 |
1 x 80 |
3.20 |
10 |
11 |
Jambagali |
Kulagi |
1950 |
1 x 70 |
2.80 |
11 |
12 |
Kulagi |
Kulagi |
1950 |
1 x 80 |
3.20 |
12 |
13 |
Bhagawati |
Bhagawati |
1950 |
1 x 80 |
3.20 |
13 |
14 |
Adkehosur |
Sambrani |
1950 |
1 x 80 |
3.20 |
14 |
15 |
Bhagawati |
Bhagawati |
1950 |
1 x 80 |
3.20 |
15 |
16 |
Mainal |
Sambrani |
1950 |
1 x 80 |
3.20 |
Wet Evergreen Forests |
16 |
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Agumbe |
Agumbe |
1940 |
1 x 87 |
3.48 |
17 |
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Devimane * |
Janmane |
1939 |
1 x 67 |
2.68 |
18 |
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Katlekan * |
Siddapur |
1939 |
1 x 27 |
1.08 |
19 |
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Malemane * |
Siddapur |
1939 |
1 x 68 |
2.72 |
20 |
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Kodkani |
Gersoppa |
1939 |
1 x 60 |
2.40 |
21 |
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Bannadpare |
Makut |
1939 |
1 x 84 |
3.36 |
22 |
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Chippehole |
Makut |
1937 |
1 x 60 |
2.40 |
23 |
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Talageri |
Yellapur |
1937 |
1 x 60 |
2.40 |
* These plots are also preservation plots.
Note: LTI plot no. 5 was lost due to submersion. |
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7.2 HYDROLOGICAL STUDIES IN EUCALYPTUS PLANTATIONS |
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The large scale planting of exotic species like Eucalyptus and Australian Acacias have caused concern to local people in the state. The plantations were thought to have adverse environmental impact particularly in relation to nutrient depletion and high water use from ground table. |
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To investigate and quantify these environmental impacts, certain field studies were designed to measure the water use and nutrient uptake vis-à-vis growth rates of Eucalyptus in Karnataka in the year 1987. The study was taken up in collaboration with Mysore Paper Mills (MPM), Institute of Hydrology , UK , Oxford Forestry Institute (OFI) and University of Agricural Sciences (UAS), Bangalore . The British Overseas Development Administration (ODA) funded the studies. |
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1. |
At Puradal, the water use of young Eucalyptus plantation was no greater than that of the indigenous dry deciduous forest trees. |
2. |
At both Puradal and Devabal, the annual water use of Eucalyptus and indigenous forest trees was equal to the annual rainfall (within the experimental measurement uncertainty of about 10 per cent) |
3. |
The water use of the forest was about twice that of agricultural crops. |
4. |
At the Hoskote site there were indications that the water use, over the three (dry) years of measurement was greater than the rainfall. At none of the places there was any indication of roots taking water directly from the water table. The Hoskote findings showed that the water use was considerably greater than the rainfall. High priority was given to confirm these results and also to determine the source of this “Extra” water. One hypothesis invoked was soil water “Mining”. If from the day of planting, roots penetrate successively into deeper layers of the soil every year, at the rate of about one meter per year, the water “Mined” from the successively deeper soil layer would be sufficient to account for most of this “Extra” water. An alternative hypothesis is that the trees are drawing water stored in this soil from years with higher than average rainfall. The first hypothesis implies a non-sustainable system in the long term. The second hypothesis would, of course, imply a sustainable system. Further study over a long term may resolve this issue. |
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7.3 HYDROLOGICAL STUDIES IN ACACIA AURICULIFORMIS PLANTATIONS |
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A study in collaboration with National Institute of Hydrology, Belgaum was taken-up to study hydrological changes induced by various forest interventions in Uttar Kannada district especially in Acacia auriculiformis plantations. The study was undertaken between the years 1995 and 1999 with financial help from UNESCO. The following are the salient findings of the study: |
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a). |
Infiltration rate is high in coastal areas where Acacia auriculiformis plantations were raised on lateritic soils or on laterite sheet. The rate was found to be 270 - 440mm per hour at Hattikeri. The least infiltration was noticed in grasslands (7mm per hour) at Yettinabail. |
b). |
Rate of infiltration in clayey soils was low (3-6mm per hour) compared to other type of soils. When afforestation works were taken up, infiltration rate was about 40-180mm per hour in red soils at Urthota. Whereas infiltration rate in the agricultural land was 190-390mm per hour in alluvial soil at Haldipur. |
c). |
The hydraulic properties of soils showed considerable seasonal variations. It was observed that infiltration rate in dry season is more as compared to wet season. |
d). |
It was observed that the hydraulic property of undisturbed evergreen forests was 30-240mm per hour followed by a site on which gap regeneration was taken up. The least infiltration rate was observed in grasslands. |
e). |
Type of the plantation and their age had influence on the hydraulic conductivity of the soil. In case of 10-year-old Acacia plantation, hydraulic conductivity was 58mm per hour followed by 10-year-old Casuarina equisetifolia plantation where it was 22.5mm per hour. It was surprising to note that the infiltration rate was very low in 67-year-old Teak plantation. |
f). |
Type of soil influences the hydraulic conductivity considerably. Coastal sandy soil has a hydraulic conductivity of 132mm per hour, where as clay soil has the least which is 2mm per hour. |
g). |
Management activities on forest soils affect its physical properties, which in turn influence soil hydraulic properties. |
h). |
Interception of precipitation by plants and accumulation of litter lead to variation in infiltration. |
i). |
Soil moisture status shows a considerable increase on reforested degraded land. |
j). |
Organic matter and other chemical parameters influence the soil characteristics very much. Undisturbed soils with high organic matter content induce higher rate of infiltration. |
k). |
Mineralogy of soils also plays a role in soil hydraulic properties. |
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8.SOIL AND MOISTURE CONSERVATION |
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8.1. Moisture conservation |
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An experiment was undertaken to assess the effect of unfilled contour trenches of size 10m x 0.6m x 0.6m at an interval of 20 to 25m on the growth and regeneration of degraded forests at Tadas and Chordi in Dharwad and in Shimoga Research ranges. This was also combined with the application of small doses (10kg/ha) of Phosphatic fertilizer (Diammonium phosphate). The treatments were carried out over an area of about 5.00 ha in each location. The experiment included, control moisture conservation trenches, only fertilizer application (10kg/ha) and moisture conservation trenches with fertilizer application. |
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8.2.Effect of different soil preparations on moisture conservation |
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In the year 1986-87, an experiment was conducted to monitor the effect of different soil preparations viz; pitting, trenching, saucer shape pits and ploughing on the growth of seedlings of different species. |
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8.3 Soil conservation |
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The normal practice of trenching all along the contour lines across the slopes is an old method of soil and water conservation in dry areas. However, systematic experiments have not been carried out to assess the different types of soil conservation measures. In the year 1987-88, construction of check dams and gully plugs was undertaken along with planting of various species in Nandi hills as a measure to conserve soil and moisture. It is gratifying to note that the area is slowly getting stabilized. The accumulation of silt near check dams is considerable indicating that soil erosion is getting arrested. Besides, planting of Agave and Bamboo has helped in stabilizing the gullies. There was also an attempt to plant Khus grass to check soil erosion. It has proved successful in some of the eroded areas. |
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8.4 Agave Plantation |
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Agave plantations were done on degraded sites over hillocks with steep slopes. The three species of Agave viz; Agave cantala , Agave americana and Agave sisalana were tried with different spacing and planting techniques, at Turalligudda of Channapatna Research center and at B.G.Kere of Challakere Research center. The rate of growth, number of leaves per plant and the rate of silt accumulation etc. are under observation. |
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9.BIO FERTILIZERS |
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9.1 Vermicompost |
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Vermi-compost refers to the manure prepared by the action of earthworms on any organic matter like cow dung, vegetable matter, leaf litter etc. Earthworms are voracious feeders of any organic matter and assimilate only 10-15 per cent of the feed. The worm cast is very rich in nutrients, containing 0.52 per cent Nitrogen, 0.9 per cent Phosphorous and 0.2 to 0.5 per cent Potassium. Another advantage is that these nutrients are in readily available form because of mineralization. In every forest nursery, production of vermi-compost can be taken up at relatively low cost. |
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The technique of preparation of vermi-compost is not cumbersome. Cement tanks or wooden trays of convenient sizes can be used for this purpose. Saw dust or husk or coir or gunny and fine sand are used as the bedding material and spread in 3cm thick layers. On this, organic matter is spread. Initially a small quantity of cow dung has to be mixed to make the feed more palatable for worms. This has to be spread uniformly on the surface to a height of not more than 5cm, as worms are surface feeders. Then worms are introduced. They feed on the organic matter. The feed is to be supplemented as and when required. The worm casts should be taken out, air-dried and sieved to remove cocoons and small worms, which can be reintroduced. The cast or the vermi-compost is stored for use as manure. The foundation bed is to be changed once in 3-6 months. Care is to be taken to protect the worms from ants, termites etc. Water logging of the beds should be prevented. Through this technique, continuous production of vermi-compost is possible to meet the requirement of the nurseries. |
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9.1.1 Vermicompost at Gungargatti (Dharwad ) |
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To produce vermi-compost about 4000 worms from Ralegaon Siddhi ( Maharashtra ) were brought and introduced in the beds prepared for this purpose. The beds were prepared with green leaves, bagasse, cow dung etc. They were kept moist all the time, otherwise there are chances of worms going down into the soil below in search of moisture. The beds were covered with overhead thatches. After 3 months the compost is ready for harvest. Before harvesting, the beds are allowed to dry so that worm goes down into the underlying soil. The manure is then removed. The compost beds are formed again in the same place. The worms return on their own to the beds and restart the process. Through this process about 4 tonnes of vermi-compost is prepared every year and is being used in the nurseries. |
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9.2 mycorrhizae and its application |
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Bio-fertilizer is a good environment friendly substitute for chemical fertilizer. Nitrogen fixing bacteria like Rhizobium, Azolla , Blue Green Algae, Phosphorous solubilising mycorrhizae are some of the important bio-fertilizers being used in forest plantations and nurseries. There is a symbiotic relationship between bio-fertilizers and the plants. |
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Some of the endo-mycorrhizal species, which are tried at Dharwad Silviculture laboratory during 1993-94, are the following. Glomus mosseae is mainly specific to Tamarind whereas Gigaspora is specific to Leucaena leucocephala and Casuarina equisetifolia , though there are reports that they perform well on a wide range of forest species. The starter culture was obtained from UAS, Bangalore and taken-up for further multiplication in the laboratory by using soil rite perlite as rooting media and maize as host plant. A plant nutrient solution that contained all major & minor nutrients and trace elements for the balanced growth of the plant was used. After raising the maize and mycorrhizal crop for about 100 days, it was harvested and tested for spore formation at UAS, Dharwad. The culture produced was of high standard, which was taken up for field trial to study its efficacy and also further multiplication. |
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9.3 field experiment using bio-fertilizer |
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An experiment was set up during 1994-95 at Gungargatti to evaluate the relative efficacy of Vesicular Arbuscular Mycorrhizal (VAM) fungi on various forest species. It was also sought to find out the optimum dosage of VAM and to assess the relative performance of seedlings raised with and without the application of bio-fertilizer. The forest species tested were Jackfruit, Tamarind, Amla, Neem, Mango, Eucalyptus and dosages adopted were 50cc and 100cc of culture. |
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9.4 VAM culture at Bangalore Research Center |
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VAM was also cultured at Doresanipallya and tried on Acacia auriculiformis and Tamarind in 1993-94. |
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10.PESTS AND DISEASES |
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10.1 BIOLOGICAL CONTROL of Teak skeletOnizer |
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The laboratory for production of Trichogamma, an egg parasite of Teak Skeletoniser, was established in the year 1986. An experiment over an area of 4.00 ha was carried out by releasing 4 lakhs eggs at the rate of 1 lakh egg/ha in the 1982 Teak plantation of Haliyal division. A total of 19 releases at an interval of 10 days were made between June 1987 and December 1987. Samples of 20 leaves each were taken, both from treated and control plots at monthly intervals. A visual assessment of leaf damage was made, average number of larvae present per leaf and percentage of parasitisation of eggs was worked out. It could be seen that there were fewer larvae per leaf and correspondingly less damage in the treated plot. |
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Another experiment on biological control for Teak skeletoniser Hapalia machaeralis (Lepidoptera: Pyralidae) was initiated in the year 1988- 89 in the Teak plantation of Karka in Haliyal Range . One-hectare plot was selected and demarcated for the release of Trichogamma egg parasite and the remaining area of the plantation was considered as the control plot. |
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The egg parasites produced at Forest Research Laboratory, Dharwad were released at the rate of four lakh parasites/ha (Twenty cards each containing about 20,000 eggs) at 10 days intervals. A total of 20 releases were made from 8.6.1989 to 26.12.89. The egg parasite cards were randomly distributed in the selected one ha of Teak plantation, 24 hours before adult emergence. |
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The following procedure was adopted for assessing the efficiency of parasite release and its effect on Teak skeletoniser. |
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Selection of 20 Teak leaves from different plants at random in the treated plot and untreated plot. |
2). |
Recording of average number of eggs that hatched into larvae in both the plots. |
3). |
Recording of number of eggs parasitised and the percentage of parasitisation. |
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The incidence of pests during the year of study appeared to have been low on account of continuous heavy rains with few sunny days. |
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