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  4.PROVENANCE TRIALS  
  Provenance is defined as the geographical source or place of origin from where a given lot of seed or plants are collected, often restricted to refer to material from a specified race.  
     
 

Trial of different provenances of various species for their performance in different agro-climatic regions of the State has been taken-up in different locations. Exotics that are selected for large-scale multiplication need to go through this type of trial in the new region. Fruit bearing trees like Annona squamosa, Annona reticulata, Annona muricata, Emblica officinalis, Syzygium cumini, Zizyphus jujuba, Aegle marmelos, Artocarpus heterophyllus, Tamarindus indica, Garcinia spp and timber trees like Pterocarpus santalinus, Pterocarpus marsupium, Dalbergia latifolia, Tectona grandis, Gmelina arborea, Indian Acacias, Santalum album, Bamboo spp, Azadirachta indica, Ficus spp, Wrightia tinctoria, Semecarpus anacardium, Acacia concinna, Mangifera indica (Appemidi), Swietenia mahagoni, Eucalyptus, Pinus, Australian Acacias, Leucaena leucocephala, Casuarina equisetifolia, Gliricidia spp, Grevillea robusta etc., have been tried.

 
     
 

Cordia alliodora

 
 

Cordia alliodora is native to wet tropical forest of Costa Rica and Honduras . It is a fast growing and high quality timber tree. Provenance trial of this species was conducted in July 1986 at Alur in Dandeli.

 
     
 

Santalum album

 
 

Provenance trial of Sandal was taken-up at Jarakabande in the year 1984. The different provenances were from Bangalore , Hanagal (Dharwad), Rayalpad(Kolar), Shikaripura (Shimoga) Shantisagar and Kurumbapatti (in Tamil Nadu). These were laid out in randomized complete block design with 4 replications. Each replication comprised of 36 plants in 24 blocks. Analysis of variance does not show any significant difference among the six provenances.

 
 
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5.PRODUCTIVITY AND NUTRIENT CYCLING STUDIES

 
  5.1 Productivity OF DIFFERENT SPECIES  
 

5.1.1. Growth and Productivity of Leucaena leucocephala

 
 

Three varieties of Leucaena leucocephala K8, K-67 and Cunninghaii plantations were raised at Maninagar in 1983. The plantations were cut in the year 1987. The objective was to study the coppicing ability of the trees as their growth had stagnated due to poor fertility of the site. The biomass production (above ground) was estimated by weighing those parts (including branches), which could be used as fuel. The productivity (utilizable fuel) per ha of three varieties varied between 1.35 to 7.62 t/ha.

 
     
 

5.1.2. Growth and Productivity of Prosopis juliflora

 
 

An experiment to assess the coppicing ability of a natural stand of Prosopis was undertaken at Anantapura in Badami Range . The stand was cut after 90, 180, 270 and 365 days successively. The stand was first clear felled on 1-10-1986 . The production of utilizable fuel varied from 6.18 to 9.18 t/ha/yr.

 
     
 

5.1.3. Growth and Productivity of Acacia auriculiformis

 
 

Large-scale plantations of Acacia auriculiformis have been undertaken in grassy blanks and in the degraded forest areas of the Western Ghats . In some of these areas plant density was 5000 plants per ha at an espacement of 2m x 1m. A study was under taken to assess the growing stock (GS) and the mean annual increment (MAI) of these plantations.

 
     
 

Regression equations of the type Y=a+bx, were worked out, where x represents d 2 H. The regression equations were worked out for different components viz ; stem, branch, twigs & rachis, leaves and total biomass. The regressions arrived were significant at 0.01 probability.

 
     
 

5.1.4. Growth and Productivity of Bamboo

 
 

Due to repeated hacking and browsing, the bamboo clumps in natural forests have become malformed, congested and have lost their vigour of production. There is no management principle prescribed to improve the production from such clumps. Hence an experiment was under taken in the natural forests of Sambrani Range (Compartment IX-24) during 1988 rains to study the response of clumps to various treatments. The various treatments were as under:

 
 

C 0 – Cutting control
C 1 - Cutting congested clumps by clear felling
C 2 – Decongesting and retaining 10 culms per clump
C 3 - Decongesting and retaining 20 culms per clump

 
  Types of earthwork provided was: F 0 Control and E 1 circular earth work around the clump (50cm digging)  
     
  Thus, in all 16 treatments (4x2x2) were replicated three times. Each plot was of 30m x 20m. This experimental plot was maintained during 1989 as prescribed in the proposed treatments. The culm production was observed and recorded.  
     
 

On account of clearance done around the clumps for facilitating soil working and application of fertilizer, monkeys and other wild animals damaged most of the new shoots that had emerged. Besides, there was heavy damage by elephants. Further it appeared that the low production of new culms was due to the fact that clumps were nearing physiological maturity as sporadic flowering was noticed in this locality. Hence, the future culms production will not indicate the true correlation to the various treatments. The number of culms counted (damaged and dead ones) during the year in 16 treatments is given .From the above figures it is evident that the culms production was more in plots where application of fertilizer was done.

 
     
 

5.1.5. Growth and Productivity of Prosopis juliflora

 
 

The experiment initiated in 1986-87 to study the coppicing ability and production by harvesting at regular intervals was continued and the measurements recorded. The results of productivity of natural stand of Prosopis juliflora when cut at intervals of 90,180,270 and 365 days have been recorded.

 
     
 

5.1.6. Growth and Productivity of Calliandra calothyrsus

 
 

This species was introduced at Jarakabande in the year 1986 at a spacing of 2m x 2m with 1600 plants. During the year 1987 and 1988, Phytomass/Biomass was computed by adopting single tree destructive sampling method. The result showed that the average height of plants was 3.15m and average stem dry weight was 2.18 kg in the year 1988.

 
     
 

5.1.7. Calliandra calothyrsus

 
 

A row of plantation was cut every month from November to March in the Calliandra calothyrsus plot at Nallal ( Hoskote Research Center ) in the year 1983. The biomass of the average tree was recorded.

 
     
 

5.1.8. Productivity under irrigation

 
 

At Mudagere Research Centre , an experiment was carried out to find the effect of irrigation on the biomass production of fast growing forest species. Irrigation was provided twice a week by flooding. After 15 months, the biomass of each species was estimated through destructive sampling method. The estimation of biomass was repeated twice on 21 st and 31 st month to know the effect of seasonality on the rate of growth. Among the species tried in the experiments, Dalbergia sissoo showed maximum response followed by Acacia falcataria and Acacia nilotica . Acacia auriculiformis showed least response to irrigation.

 
     
 

5.2 . Nutrient cycling

 
 

5.2.1 Moist Deciduous Forest :

 
 

With a view to assess the quantum of leaf litter fall and thereby to assess the nutrient recycling, an experiment was carried out in September 1989. This was carried out in 5 LTI plots namely; Usoda, Karka, Bailapur, Phansoli and Mainal of the moist deciduous forests of Haliyal forest division. In each of the LTI Plots, 8 bamboo baskets of 1m x 1m size and 0.3m in height were placed at random. Once a month all the leaves, fruits, twigs and bark that fell in the basket were collected species wise. The litter of each species was weighed separately and recorded every month. These were then brought to research laboratory where the oven dry-weight of each species was also recorded. The samples were analyzed in order to find the nutrient contents namely C, N, P, K, Ca and Mg.

 
     
 

5.2.2 Leaf litter and Nutrient Cycling in Plantations

 
 

Leaf litter collection for different species was taken up over an area of 25 m 2 between August 1985 and July 1987, at Devbal in Shimoga Range . The species studied were: Acacia auriculiformis, Anthocephalus cadamba, Lagerstroemia lanceolata, Cassia siamea, Duabanga sonneratoides and Casuarina equisetifolia.

 
     
 

The litter was separated into leaves, branches, flowers and pods. A sample of 500g each was sent to Forest Laboratory at Dharwad for recording oven dry weight and to carry out an analysis for different nutrients.

 
 
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  6. GRASS LAND AFFORESTATION AND UNDER PLANTING TRIALS  
  6.1 GRASS LAND afforestation  
 

6.1.1. Grassy blank afforestation experiments in Southern Zone Madikeri

 
 

In order to make the vast stretches of grasslands more productive, efforts are being made to afforest them by introducing tree species at various localities. The details of such experiments are given below:

 
 
a).

Grassland afforestation at Monnageri : At Monnageri in Kodagu district three trial plots of 2.75 ha each were laid out with Acrocarpus fraxinifolius, Cryptomeria japonica, Dalbergia sissoo , Elaeodendron paniculata , Syzygium cumini , Swietenia mahagoni, Samanea saman, Terminalia bellerica and Terminalia tomentosa. Observation shows that only Acrocarpus fraxinifolius, Elaeodendron paniculata and Emblica officinalis have come up well in grassy blanks .

b).

Miscellaneous species trial plot at Monnangeri: In another trial at Monnangeri, afforestation of exposed lateritic grassy blanks of 6.5 ha was under taken with indigenous and exotic species viz; Acrocarpus fraxinifolius, Acacia auriculiformis, Dalbergia sissoo, Emblica officinalis, Syzygium cumini, Ceiba pentandra, Spathodea campanulata and Elaeodendron paniculata. Initially, during 1986 all plants established except Ceiba pentandra and Acrocarpus fraxinifolius as these two species were found to die back. Subsequently in 1992, only two species were found to be surviving in this area viz; Spathodea campanulata and Emblica officinalis .

c).

Acacia mearnsii, Calliandra calothyrsus, Acacia mangium , and Pinus kesia were tried at Monnangeri (Madikeri) in 2.1 ha of grassland. It was observed that Acacia mearnsii and Acacia mangium failed to establish. Whereas Calliandra calothyrsus and Pinus kesia have survived with average growth.

d).

Bambusa vulgaris and Acrocarpus fraxinifolius were tried in grassy blanks in an area of 2 ha . It was observed that both Bambusa vulgaris and Acrocarpus fraxinifolius have failed to establish either due to animal damage or due to die back.

e).

Afforestation of 2 ha of area with indigenous and exotic species at Aiengeri (Madikeri) was taken-up. The species planted were Acacia mearnsii, Casuarina equisetifolia Calliandra calothyrsus and Elaeodendron paniculata. It was observed that all the species had put on good height growth except Elaeodendron paniculata.

f).

Introduction of Bambusa vulgaris and Dendrocalamus strictus in grassy blanks was done in an area of 2.0 ha at Ummathur in 1985. Both the bamboo species are performing well with 85-90 per cent survival. It was observed that new culms were produced during 1992.

g).

Introduction of Bambusa vulgaris in grassy blanks was done in 1986 ( 2 ha .) in high rainfall area at Ummathur. It was observed that Bambusa vulgaris responded well to the environment in the grassy blanks. Vigorous new culms were produced. During 1992, 59 per cent survival was noticed with an average of 3 culms per clump.

h).

To study the efficacy of planting in terraces for afforestation of grassy blanks, a plantation in an area of 8 ha was taken-up in 1985 at Ummathur. Species tried were Acacia auriculiformis, Acrocarpus fraxinifolius, Casuarina equisetifolia, Calliandra species, Dalbergia latifolia, Emblica officinalis, Grevillea robusta, Swietenia mahogany and Parkinsonia aculeata. All the species tried have performed well except Parkinsonia aculeata and Dalbergia latifolia . Acrocarpus fraxinifolius is also struggling to establish. Calliandra calothyrsus has shown good performance.

i).

To introduce Pinus caribeae in Phoenix infested grassy blanks, a trial plot was established in an area of 0.27 ha in 1985 at Hanbal Achardi. The plants have established well with 90 per cent survival.

j).

To introduce wattles (Acacia mearnsii) in grassy blanks, a trial plot of 8.0 ha in high rainfall zone at Ummathur was established. Initially seedlings responded well but later the entire plantation failed.

k).

Introduction of Pinus oocarpa in Phoenix infested grassy blanks was done over an area of 0.25 ha in high rainfall area to assess its performance at Hanbal Achardi. Seedlings have showed good performance in the local environment, with 84 per cent survival in 1987. During 1992, 40 per cent survival was noticed with an average height of 4.0m and average girth of 0.15m.

l).

A Trial plot of MFP in grassy patches at Vallalhalli, Madikeri over an area of 5.0 ha was established in 1988. Species tried were Emblica officinalis, Artocarpus integrifolia, Azadirachta indica, Madhuca indica, Sapindus emarginatus, Tamarindus indica, Syzygium cumini, and Mangifera indica. All the plants are growing well.

m).

To find the suitability of fruit yielding species in grasslands, a trial plot of 2.5 ha was established at Watehalla with Syzygium cumini and Mangifera indica in 1993. All the plants are coming up well with an average height of 1.5m.

n).

At Ullal, in the year 1984, coastal area afforestation experiments were taken up with Acacia auriculiformis, Bauhinia racemosa, Cassia fistula, Casuarina equisetifolia, Calliandra calothyrsus and Dalbergia latifolia. Only Casuarina equisetifolia was found to be suitable for coastal areas.

o).

An experiment in swampy areas of Thithimathi and Nagerhole Ranges of Hunsur Division was taken-up with Acrocarpus fraxinifolius, Albizzia lebbek, Artocarpus hirsuta, Bombax ceiba, Chickrassia tabularis, Syzygium cumini, Swietenia mahagoni, Kydia calycina, Spondias mangifera etc . Except Syzygium cumini , all other species have failed in these waterlogged areas.

 
     
  6.1.2 Grassy blank Afforestation experiments in Northern Zone, Dharwad  
 
a).

There are extensive grassy blanks in the evergreen belt of Western Ghats . With a view to raise some tree species, various afforestation techniques involving a large number of exotics as well as indigenous species have been taken up since 1975. They are:

 

Evergreen species

-

Anthocephalus cadamba, Calophyllum elatum, Acrocarpus fraxinifolius, Vateria indica, Syzygium cumini, Artocarpus hirsuta, Michelia champaca.

Deciduous species

-

Terminalia tomentosa, Lagerstroemia lanceolata, Pterocarpus marsupium, Dalbergia latifolia, Santalum album, Gmelina arborea.


Exotics

-

Acacia auriculiformis, Casuarina equisetifolia, Khaya senegalensis, Tropical pines , Grevillea robusta, Albizzia moluccana Leucaena leucophloea, Samanea saman, and Delonix regia.

 
Acacia auriculiformis and Casuarina equisetifolia are found to be suitable performance of wattles, Albizzia moluccana , Tropical pines and Khaya species needs to be studied further to find-out their suitability.
 
d).

At Hosur near Agumbe, twenty-five species belonging to evergreen, deciduous and exotic categories were tried in the year 1976. Both naked seedlings and seedlings raised in polybags were tried. It was observed that only Acacia auriculiformis and Casuarina equisetifolia were doing well in grassy blanks. Acacia auriculiformis is the most suited species for afforestation of grassy blanks in the humid tropics of the Western Ghats .

e).

At Mense forty different species of evergreen, deciduous and exotics were tried in the year 1979 for assessing their suitability to the grasslands. Only Acacia auriculiformis and Casuarina equisetifolia were found to be successful.

f).

At Neeluvagilu an experiment of six different species namely, Acacia auriculiformis, Syzygium cumini, Grevillea robusta, Casuarina equisetifolia, Anacardium occidentale and Bambusa vulgaris at different spacing of 2m x 2m, 2.5m x 2.5m, 3m x 3m and 4m x 4m in different blocks were taken up in the year 1982. Acacia auriculiformis , Casuarina equisetifolia and Bambusa vulgaris are doing well with an average height of 5.8m, 5.0m, 3.5m and girth of 15.5cm, 18.8cm, and 14.1cm respectively.

g).

At Nagatirtha an experiment with Acacia auriculiformis and Casuarina equisetifolia with three different soil preparations was laid out. The three different soil preparations were advance pitting, advance trenching and monsoon pitting. The best average height and average girth were obtained in the monsoon-pitting block. Acacia auriculiformis did better than Casuarina equisetifolia.

h).

At Heggarakudiga 10 different exotics and some evergreen species were planted in the year 1982. The species were: Syzygium cumini, Acacia auriculiformis, Casuarina equisetifolia, Anthocephalus cadamba, Gmelina arborea, Swietenia mahagoni, Dalbergia latifolia, Grevillea robusta and Bambusa vulgaris. The growth of Acacia auriculiformis and Casuarina equisetifolia is outstanding.

 
     
  6.2 UNDER PLANTING TRIALS:  
  6.2.1. Under-planting of Evergreen & Semi Evergreen species  
  In evergreen and semi evergreen forest zones, grasslands have been successfully planted with Acacia auriculiformis . In these older plantations of Acacia auriculiformis, under planting of evergreen and semi evergreen species were tried. Under-planting trials started from 1985 in Acacia plantations of Thirthahalli (Shimoga), Terakahanally (Sirsi), Udane (Sakaleswar), Mallipatna (Thittimathi) and Boliyar (Mudabidri). In case of Mallipatna, under planting was taken up in Teak plantation to suppress Eupatorium weed growth. Among the evergreen, semi-evergreen and deciduous tree species planted in under planting trials, Mesua ferrea, Vateria indica, Calophyllum spp , Michelia champaca, Garcinia cambogia, Hopea parviflora, Poeciloneuron indicum and Artocarpus hirsuta have come up well with high survival percentage ranging from 85 to 100. However, Tectona grandis, Terminalia tomentosa, Pterocarpus marsupium, Dalbergia latifolia, Emblica officinalis, Terminalia bellerica and Dendrocalamus strictus have not shown promising results.  
     
  6.2.2. Under planting of Canes in Acacia plantations  
  Cane is an integral part of the moist tropical forest eco-system. Many species of canes are under severe threat due to destruction of their habitat, over exploitation and other factors. Commercial cane plantations have to be taken-up if the cottage industries are to survive. About 2,00,000 ha of degraded and grassy blank areas in high rainfall region of Western Ghats have been planted with Acacia auriculiformis . As cane forms lower and middle storey in evergreen forest, cane harvest can be a by-product yielding interim revenue. With this background under planting of four species of canes viz; Calamus prasinus (Ontibetha), Calamus thwaitesii (Handibetha), Calamus vattayila (Devarbetha) and Calamus nagbettai (Nagarbetha) was taken up in the Acacia plantations of the Western Ghats. The results achieved in cane under planting trials at Salur were good. Average height of cane was 11.40m by the end of the 8 th year. The average height of Calamus thwaitesii was 8.10m. In Calamus thwaitesii culms production was also noticed from 3 rd year onwards and on an average two culms were added every year. Fruiting started in 1997 and natural regeneration was also noticed in older under planting areas. Among all the four species of canes Calamus prasinus is most promising followed by Calamus nagbettai . Wild animal damage is more in Calamus vattayila and Calamus thwaitesii , than in Calamus nagbettai . Calamus nagbettai has long spines, which are present all over the stem and hence they prevent animal damage.  
     
  In conclusion it can be said that canes can be grown successfully as under plantings in Acacia plantations in those areas where they were originally present. Planting of two to three year old cane seedlings with well-developed rhizomes coupled with good protection from wild animals is vital for raising successful cane plantations. Acacia plantations raised as monoculture are not well accepted by the environmentalists, therefore these could be converted into well-diversified plantations resembling natural forests of the region to a large extent through under planting of canes and other suitable evergreen and semi-evergreen species.  
     
   
     
   
 
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