<?xml version='1.0' encoding='UTF-8'?><?xml-stylesheet href="http://www.blogger.com/styles/atom.css" type="text/css"?><feed xmlns='http://www.w3.org/2005/Atom' xmlns:openSearch='http://a9.com/-/spec/opensearchrss/1.0/' xmlns:georss='http://www.georss.org/georss' xmlns:gd='http://schemas.google.com/g/2005' xmlns:thr='http://purl.org/syndication/thread/1.0'><id>tag:blogger.com,1999:blog-34347796</id><updated>2011-10-24T00:07:05.371-07:00</updated><title type='text'>Forestry and Environment Sympoisum 2002, Sri Lanka</title><subtitle type='html'></subtitle><link rel='http://schemas.google.com/g/2005#feed' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/posts/default'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default?max-results=100'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/'/><link rel='hub' href='http://pubsubhubbub.appspot.com/'/><author><name>Dr. Hiran Amarasekera</name><uri>http://www.blogger.com/profile/06988028276424542318</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='31' height='32' src='http://2.bp.blogspot.com/_spj17clkJ1E/ScJ379yWqUI/AAAAAAAAABM/yklcilYuJ9E/S220/sakya-brochure.jpg'/></author><generator version='7.00' uri='http://www.blogger.com'>Blogger</generator><openSearch:totalResults>58</openSearch:totalResults><openSearch:startIndex>1</openSearch:startIndex><openSearch:itemsPerPage>100</openSearch:itemsPerPage><entry><id>tag:blogger.com,1999:blog-34347796.post-115874576939136107</id><published>2006-09-20T02:38:00.000-07:00</published><updated>2006-09-20T02:49:29.546-07:00</updated><title type='text'>DIFFERENTIAL BIO-ECOLOGY OF ANOPHELINE SIBLING SPECIES: A RELEVANCE TO MALARIA CONTROL IN SRI LANKA</title><content type='html'>&lt;strong&gt;S.N. Surendran 1, B.G.D.N.K. De Silva2 &amp; R. Ramasami3&lt;br /&gt;&lt;/strong&gt; 'Dept. of Zoology, University of Jaffna&lt;br /&gt;2Dept of Zoology, University of Sri Jayewardenepura&lt;br /&gt;3National Science Foundation, Colombo&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;Human intervention by various means has altered natural ecosystems and thus paved way for emergence of new vectors and their propagation leading to the spread of malaria world wide. Vector ecological studies have been undertaken in order to locate risk areas for malaria and to formulate appropriate strategy for vector control. The prevalence and abundance of mosquito immature stages in various breeding sites reflect the oviposition reference of females and it can be attributed at inter specific and intra specific levels. Knowledge, especially at intra specific level, on bio-ecology of vectors is an essential prerequisite for formulating effective environmental management interventions for the control of malaria.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Morphologically more or less similar but reproductively isolated members of a taxon are termed sibling species and the taxon are species complex. Sibling species exhibit differences with respect to feeding and resting preference, rate of development of resistance to insecticide, susceptibility to parasites and seasonal prevalence.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Among known malaria vectors in Sri Lanka, &lt;em&gt;Anopheles culicifacies&lt;/em&gt;, the major vector of malaria, &lt;em&gt;An. Subpictus&lt;/em&gt; and &lt;em&gt;An. Annularis&lt;/em&gt;, the subsidiary vectors are reported to be existing as species complex in the Indian subcontinent. Studies on the bionomics of the two sibling species B and E of &lt;em&gt;An. Culicifacies&lt;/em&gt; in Sri Lanka reveal that these two sympatric populations are diverged in certain bio- ecological aspects which are essential for implementing a successful vector control program. Laboratory infective studies showed that species E could support the extrinsic cycle of &lt;em&gt;Plasmodium vivax&lt;/em&gt; and &lt;em&gt;P. falciparum&lt;/em&gt;. Studies on the age structure of species B and E revealed that species E has entered the epidemiologically dangerous age. Both siblings showed differential susceptibility to Malathion. Studies on the limnological characterization of larval breeding sites of species B and E showed that species E prevailed in variety of breeding habitats, an indication of high level of adaptive variation of species E. Sibling species status of &lt;em&gt;An. Annularis&lt;/em&gt; in Sri Lanka is yet to be revealed. A study on the sibling species of &lt;em&gt;An. Subpitus&lt;/em&gt; from a locality in North Western province of Sri Lanka revealed that species B is predominant in coastal and species C in inland areas.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115874576939136107?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115874576939136107/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115874576939136107' title='4 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115874576939136107'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115874576939136107'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/differential-bio-ecology-of-anopheline.html' title='DIFFERENTIAL BIO-ECOLOGY OF ANOPHELINE SIBLING SPECIES: A RELEVANCE TO MALARIA CONTROL IN SRI LANKA'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>4</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115874507763339613</id><published>2006-09-20T02:23:00.000-07:00</published><updated>2006-09-20T02:37:57.836-07:00</updated><title type='text'>IN VITRO PROPAGATION OF ANTNURlUM (Anfhurium andraeanum L)</title><content type='html'>&lt;strong&gt;S.P.P.WEERASEKARA &amp; Y.M.H.B. YAPABANDARA&lt;/strong&gt;&lt;br /&gt; Department of Crop Science, Faculty of Agriculture, University of Ruhuna&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;Callus induction and shoot regeneration were studied using leaf and petiole explants of in vitro cultures of white Anthurium and leaf ex plants of green house grown nine Anthurium cultivars (Cassino, Tropical, SHP, Samangi, Maringue Lady Jane, White, Magic Red and Pierot).&lt;br /&gt;&lt;br /&gt;Leaves from in vitro cultures of Anthurium were cultured in MS medium supplemented with 1.0mg/L BA 0,0.2 &amp; 0.5 mg/L IAA and incubated in dark at 25° C temperature. The effect of IAA was significant for callus induction and shoot regeneration. The highest callus quantity (6.75) showed in 0.2mg/L IAA while only 2 shoots regenerated from Omg/1 IAA. Petioles from in vitro cultures of Anthurium were also cultured NIS medium supplemented with combination of 2 levels of BA (1 or 2mg/L) and 3 IAA levels (0,0.2 &amp;amp; 0.5 mg/L). Cultures were incubated in dark at 25° C temperature. Significant differences were found between the two BA levels and 3 IAA levels for callus production and shoot regeneration. The highest callus quantity (5.6) was given in 1mg/L BA with 0.2mg/L IAA than other combinations. Higher shoot regeneration was achieved in 0.2 and 0.5 mg/L IAA with 1 or 2 mg/L BA (2.7-2.9 shoots per explants).&lt;br /&gt;&lt;br /&gt;Leaf pieces (lcm*lcm) from green house grown 9 cultivars were sterilized and cultured in MS medium supplemented with l mg/L BA and 0, 0.2 or 0.5 mg/L IAA and incubated dark at 25° C temperature. Significantly higher callus quantity was observed in 0.2 mg/L IAA while the lowest callus quantity was from 0mg/L IAA level. A significant difference was observed among 9 cultivars from callus production. The highest callus quantity (4.74) was observed from the cultivars "Lady Jane" while the lowest callus quantity (1 from cultivar) "Pierot". Shoot regeneration was observed in some cultivars after d-5 months. For example, cultivar "Meringue" produced 3 shoots per explants in 0.5mg/L IAA level and cultivar "Cassino" produced 1 shoot per explants in 0.2mg/L IAA level. Shoot regeneration was not achieved in other cultivars.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115874507763339613?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115874507763339613/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115874507763339613' title='1 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115874507763339613'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115874507763339613'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/in-vitro-propagation-of-antnurlum.html' title='IN VITRO PROPAGATION OF ANTNURlUM (Anfhurium andraeanum L)'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>1</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115874417938945284</id><published>2006-09-20T02:12:00.000-07:00</published><updated>2006-09-20T02:22:59.516-07:00</updated><title type='text'>COMPARISON OF LONG-TERM TRANSPIRATION OF DIFFERENT TREE SPECIES IN SEPARATE CANOPY LAYERS IN A KANDYAN FOREST GARDEN</title><content type='html'>&lt;div align="left"&gt;&lt;strong&gt;W.A.J.M.DeCosta, K.S.P. Amaratunga &amp;&lt;/strong&gt; &lt;/div&gt;&lt;div align="justify"&gt;&lt;strong&gt;M.R.H.L. &lt;strong&gt;&lt;/strong&gt;&lt;span&gt;Karunasinghe  &lt;/span&gt;&lt;/strong&gt;                                             &lt;br /&gt;Faculty of Agriculture, University of  Peradeniya, Peradeniya&lt;br /&gt;&lt;br /&gt;Kandyan Forest Gardens (KFG s) are a specific vegetation type covering a considerable land area of the Central Province of Sri Lanka. Therefore, water use by KFG s form an important component of the catchment water balance of this area. KFG s consist of a mixture of tree species whose canopies are arranged in different vertical layers.&lt;br /&gt;&lt;br /&gt;The study was conducted in a typical Kandyan Forest Garden located at Pilapitiya, Pilimathalawa within the agro ecological region WM2. A vegetation survey was carried out in this garden and it showed 201 trees belonging to 24 different species. Out of these, two tree species were selected to represent upper and middle canopy layers. They were Jak (&lt;em&gt;Artocarpus heterophyllus&lt;/em&gt;) and toona (&lt;em&gt;Cedrella toona&lt;/em&gt;). Transpiration of these trees was measured as the sap flow in their trunk using thermal dissipation probes. Measurements of the weather parameters were also taken. The incident solar radiation was measured using the tube solarimeters. Relative humidity in the open and inside the KFG was measured by two solid state sensors. The soil moisture content at five soil depths (i.e. 20, 40, 60, 80 and 100 cm) was measured by gravimetric sampling All the data except soil moisture were taken at 30 second time intervals integrated over five minutes and stored in the data logger. The measurements that were taken during the period from 25.12.2001 to 20.02.2002 were analyzed.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Both species showed a similar pattern of daily variation of sap flow. However, the sap flow was substantially greater in Jak than in toona. The total water use of Jak for the experimental period was 3881.25 kg/tree. The corresponding value of toona was 462.83 kg/tree. The upper canopy Jak received a greater irradiance than middle canopy toona. There was a linear relationship between the radiation incident on Jak and toona canopies.&lt;br /&gt;&lt;br /&gt;Daily water use of the upper canopy jak showed a clear linear relationship with daily irradiance on its canopy. However, the water use of toona did not show such a relationship. In both species, there were significant negative linear relationships between daily sap flow and daily mean relative humidity. However, air temperature did not have a significant effect on sap flow of both jak and toona trees. The canopy leaf area of jak remained more or less constant during the experimental period, But in toona, the canopy leaf area increased during the latter part of the experimental period. Water use of both jak and toona did not show a significant relationship with the variation of soil moisture content of the top lm of the soil profile. This indicated that the trees were extracting water from the deeper layers of the soil profile. It can be concluded from results of the present study that water use of a KFG is dominated by large upper canopy trees and that it is largely determined by the incident solar radiation. This study also showed that large trees in this ecosystem maintain their high levels of water use even during dry periods of the year by extracting water from deeper layers of the soil profile.&lt;br /&gt;&lt;br /&gt; &lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115874417938945284?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115874417938945284/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115874417938945284' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115874417938945284'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115874417938945284'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/comparison-of-long-term-transpiration.html' title='COMPARISON OF LONG-TERM TRANSPIRATION OF DIFFERENT TREE SPECIES IN SEPARATE CANOPY LAYERS IN A KANDYAN FOREST GARDEN'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115874349221975753</id><published>2006-09-20T02:06:00.000-07:00</published><updated>2006-09-20T02:11:32.360-07:00</updated><title type='text'>EVALUATION OF GROWTH PERFORMANCES OF SELECTED TREE SPECIES ON</title><content type='html'>&lt;div align="justify"&gt;&lt;strong&gt;S Subasinghe &amp; Aruna Kumara&lt;br /&gt;&lt;/strong&gt;Department of Crop Science, Faculty of Agriculture, University of Ruhuna&lt;br /&gt;&lt;br /&gt;Five separate field experiments were conducted at Hungama in the Hambantota district, Sri Lanka, to evaluate the growth performances of selected five tree species i.e.Tamarind (&lt;em&gt;Tamarindus indica&lt;/em&gt;), Wood apple (&lt;em&gt;Feronoa limonia&lt;/em&gt;), Kottamba (&lt;em&gt;Terminalia catappa&lt;/em&gt;), Kathurumurunga (&lt;em&gt;Sesbania grandiflora&lt;/em&gt;) and Katuandara (&lt;em&gt;Acasia leucoploea&lt;/em&gt;) mainly available in the salt-affected areas. Each tree species consisted of six treatments which were differentiated with three potting mixtures (i.e. top soil, sub soil and a mixture of top soil - cattle manure) filled in planting holes and again with mulching and without mulching. The experimental design for a11 experiments were Randomized Complete Block Design (RCBD) with four replicates. Two months old plants raised in poly bags were used in all the experiments. Plant height and dry matter yield of plants were determined as growth parameters, once in three months.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The experimental site was near the Hungama Lake and salinity of the soil is about 9.5 mm hos/cm at topsoil and 8.3 mmhos/cm at 30 cm depth. All the plants have shown good growth performances in all treatments. Growth performances were not significantly affected by mulching for all plant species. Tamarind, Wood apple and Kottamba, which were grown in planting holes filled with subsoil, showed significantly higher growth performances. But in Kathurumurunga, the better performances were observed in the treatment, which used a potting mixture of cattle manure - top soil while in Katuandara, plants grew well in all the treatments irrespective of the treatment effect. Therefore all five tree species, which were used for the experiment, may be recommended as salt tolerant tree species.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115874349221975753?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115874349221975753/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115874349221975753' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115874349221975753'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115874349221975753'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/evaluation-of-growth-performances-of.html' title='EVALUATION OF GROWTH PERFORMANCES OF SELECTED TREE SPECIES ON'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115874313417387817</id><published>2006-09-19T23:09:00.000-07:00</published><updated>2006-09-20T02:05:34.783-07:00</updated><title type='text'>IMPORTANCE OF IMPROVING BIOLOGICAL ACTIVITY OF TEA SOILS IN SOUTHERN PROVINCE OF SRI LANKA</title><content type='html'>&lt;strong&gt;Keerthi M. Mohotti 1, A. R. Prathapasinghe2, N. G. N. Rasangi 2, Shantha Jayasinghe 1, P. K. Jayawickrema 1 &amp; K. L. Wasantha Kumara2&lt;br /&gt;&lt;/strong&gt;1 Tea Research Institute of Sri Lanka, Talawakele,&lt;br /&gt;2 Faculty of Agriculture, University of Ruhuna, Mapalana, Kamburupitiya.&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;The detrimental effects of soil pesticides :au. soil micro biota and biodiversity of the tea ecosystem are poorly understood. In the current study, microbial activity in southern tea soils of Sri Lanka as affected by application of commonly used soil pesticides and certain cultural practices was evaluated by measuring the soil respiration in vitro and in vivo.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;CO2 evolution rates in Southern tea soils were generally low as compared to soils in other areas. Herbicide and formalin applications significantly (p=0.005) suppressed the biological activity of Southern tea soils; the nematicide tested was less effective. Incorporation of compost and tea waste significantly (p=0.005) elevated CO2 evolution rate in tea soils than that of in undisturbed, virgin forest soils. Forking strengthened microbial biomass through improved soil physical conditions, Soil biornass was positively correlated with growth of the test plants viz. tea and tomato.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Southern tea soils with low organic matter contents are exposed to repeated application of herbicides and negligence of important agronomic practices due to labor shortage. Such malpractices could aggravate potential build up of pesticide residues in the soil. Thus, improvement of soil organic matter status by incorporation of various organic amendments, establishment of green manure crops, rehabilitation of old tea soils and more importantly, restricted usage of agro-chemicals &lt;a href="http://etc.is/"&gt;&lt;span style="color:#000000;"&gt;etc. is&lt;/span&gt;&lt;/a&gt; essential. These practices will assure long-term sustainable productivity and quality of soils as well as help degrade accumulated chemical residues and elevate densities of soil microbial communities. As a consequence, increased efficacy of bio control of nematodes and soil borne pathogens and proper administration of natural nutrient cycles could be envisaged.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115874313417387817?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115874313417387817/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115874313417387817' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115874313417387817'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115874313417387817'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/importance-of-improving-biological.html' title='IMPORTANCE OF IMPROVING BIOLOGICAL ACTIVITY OF TEA SOILS IN SOUTHERN PROVINCE OF SRI LANKA'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115873256678398652</id><published>2006-09-19T23:05:00.000-07:00</published><updated>2006-09-19T23:09:26.980-07:00</updated><title type='text'>THE APPLICATION OF SUB INDEX AGGREGATION METHOD TO ASSESS THE HEALTH OF A WATER BODY</title><content type='html'>&lt;div align="justify"&gt;&lt;strong&gt;Lisa Crowley &amp; Niranjali Jayasuriya&lt;br /&gt;&lt;/strong&gt;School of Civil and Chemical Engineering, RMIT University, Melbourne, Australia&lt;br /&gt;&lt;br /&gt;The environmental health of inland water bodies can be described using water quality parameters that describe the physical, chemical and biological status of the water. Each of these parameters reflect different characteristics of the water body and can be assessed by comparing with threshold values detailed in water quality guidelines such as the Fresh Water and Marine Water Quality Guidelines. Assessing the status of a water body using a suite of water quality parameters is cumbersome: and fraught with difficulty, as for a given location some parameters may fall under threshold values whilst others exceed guideline values. To simplify and unify the interpretation based on individual water quality parameters, these can be combined into a single dimensionless number by considering each measured water quality concentration and its corresponding guideline value. This single number is called the `water quality index' (WQI) and is used to assess the overall status of the water body quantitatively and objectively.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Many methods have been derived over the years to determine the WQI for different applications. These methods are grouped into two categories; 'sub-index' and `statistical'. As to-date, no guidelines have been specified on the selection of a methodology. However, it has been acknowledged that the method used to derive the WQI should retain valuable information from each parameter and retain its contribution to determining the overall health during the combining process.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;This paper reviews methods available to determine WQIs for a range of applications. The paper will describe the application of the SIA method to a set of water quality data along the Yarra River in Victoria, Australia. The, results were useful in identifying the trend in WQ variation. The Sub Indices Aggregation (SIA) method could be used by Authorities for rapid assessment of water bodies to identify their suitability for different purposes based on the quality of water. Application of the method can also assist with locating critical areas that could urgently require rehabilitation.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115873256678398652?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115873256678398652/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115873256678398652' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115873256678398652'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115873256678398652'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/application-of-sub-index-aggregation.html' title='THE APPLICATION OF SUB INDEX AGGREGATION METHOD TO ASSESS THE HEALTH OF A WATER BODY'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115873227135790251</id><published>2006-09-19T22:59:00.000-07:00</published><updated>2006-09-19T23:04:31.433-07:00</updated><title type='text'>ANALYSIS OF WATER QUALITY PARAMETERS IN WELL WATER IN THE VICINITY OF AN INDUSTRIAL ZONE AND ANALYSING SOURCES AND EFFECTS</title><content type='html'>&lt;strong&gt;U.M.S. Priyanka &amp; &lt;/strong&gt;&lt;a href="http://n.j.g.j.bandara/"&gt;&lt;strong&gt;N.J.G.J. Bandara&lt;/strong&gt;&lt;/a&gt;&lt;br /&gt; Department of Forestry and Environmental Science,&lt;br /&gt; University of Sri Jayewardenepura&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;The Ratmalana - Moratuwa area located in the south of Colombo has developed as an industrial residential suburb of Colombo in the 1950's. It has been revealed that the environmental problems in the area are very acute due to the activities of large number of industries. About 150 industries arc densely packed, within this area. Most of the industries are non-agro based industries. They can be categorised into several groups such as paint industries, galvanizing industries, asbestos industries, dyeing and finishing, pharmaceutical industries and battery manufacturing industries. According to an investigation of discharges produced in the area was found that major part of the effluent was released via surface drainage to Lunawa and Bolgoda Lake. The main issue associated with this industrial pollution is water contamination. Even though many studies have been carried out on surface water contamination, studies on ground water contamination have not been done in detail. The intention of this study was to, analyze ground water samples at various sites of the industrial zone and to relate the results to the present industrial activities of the area. From these Studies it was found that the chemical oxygen demand (COD), levels far exceed the acceptable portable water quality standards, indicating high chemical pollution. In addition it was found that Chemical pollutants arc present in the ground water. Biological Oxygen Demand (BOD) has exceeded the tolerant limits for portable water level at several locations. The trace metals that exceed the levels are Zn, Fe, Cd, Pb, and Ni which had not been noted in a previous study done by De Silva et al. (1986).&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Low pH values-in some of the samples indicate water contamination with acids. Sonic samples have been contaminated with acids and it was revealed by low pH of some samples. Most industries in the area dispose their effluents directly in to the drainage system without any prior treatments. Ground water contamination is thought to be a direct consequence of these inefficient effluent systems. This study discusses the analytical results of water samples taken from various locations of the industrial area and described the industrial activities in the area that might have caused this ground water contamination, and discusses possible health effects due to use of polluted water as a source of portable water in this well water.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115873227135790251?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115873227135790251/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115873227135790251' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115873227135790251'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115873227135790251'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/analysis-of-water-quality-parameters.html' title='ANALYSIS OF WATER QUALITY PARAMETERS IN WELL WATER IN THE VICINITY OF AN INDUSTRIAL ZONE AND ANALYSING SOURCES AND EFFECTS'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115873137596157966</id><published>2006-09-19T22:49:00.000-07:00</published><updated>2006-09-19T22:54:23.170-07:00</updated><title type='text'>QUANTIFICATION OF TOTAL CHROMIUM AND HEXAVALENT CHROMIUM IN WATER BY ELECTROTHERMAL ATOMIC ABSORPTION SPECTROMETRY</title><content type='html'>&lt;strong&gt;B.S. Jayasinghe 1, M.LF.P. Jayawardene 1 &amp;amp; K.A.S.Pathiratne2&lt;br /&gt;&lt;/strong&gt;1 Department of Biochemistry, Faculty of Medical Sciences, University of Sri Jayewardenepura&lt;br /&gt;2Department of Chemistry, University of Kelaniya&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;The two primary oxidation states of chromium in natural waters, Cr(III) and Cr(VI), differ significantly in biological, geochemical and toxicological properties. Whereas Cr(III) is considered essential for human in glucose, lipid and protein metabolism, Cr(VI) is toxic because of its ability to oxidize other species and its adverse effects on the lung, liver and kidney. Because of the different toxicities and bioavailability of Cr(III) and Cr(VI), determination of the total chromium content does not give full information about possible health hazard. Hence monitoring of the concentration of the separate chromium species is of great importance. Many different techniques have been in use for Cr containing samples preparation and metal ions speciation: ion chromatography, flow injection analysis, and atomic absorption spectrometry (AAS).&lt;br /&gt;&lt;br /&gt;Procedures for the quantification of total chromium and hexavalent chromium in water samples are presented. For the quantification of total chromium and hexavalent chromium in water Chromabond NH2 columns (aminopropyl phase with a 3ml volume and 500mg of sorbent) obtained from Machary- Nagel (Duren, Germany) were used.&lt;br /&gt;&lt;br /&gt;The pH value of the water sample was adjusted to 5.5 using acetic acid or sodium acetate and sample was aspirated through the previously conditioned column. The column contents were dried under vacuum and the hexavalent chromium selectively linked was eluted with nitric acid and quantification was performed by Electrothermal Atomic Absorption Spectrometry (ETAAS). For the detection of total chromium, Cr(III) was transformed into Cr(VI) by oxidizing the sample with 1% K2S2O8 solution and AgN03 at 100°C for 15 min. Oxidized solution was eluted through a Chromabond column and total Cr level was quantified by ETAAS using the same instrumental conditions as for hexavalent chromium. Total chromium was also quantified directly in the water samples using ETAAS. The temperature programme of the graphite furnace, the use of chemical modifiers, the atomic technique employed and the effectiveness of deuterium background correction were investigated. Chromium was reliably determined by without chemical modifiers or background correction.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The detection limits were 0.4 and 0.5µg/l for total chromium and hexavalent chromium respectively.. The linearity changed under the optimized conditions was 0.4 - 50µg/l and 0.5-50µg/l and the relative standard deviation was less than 3.5%. The validation of both procedures was performed by the standard addition method and the recoveries were higher than 96% in all cases. It is proved that the method can be successfully employed as an alternative to the commonly used preconcentration and speciation analytical techniques. The direct procedure was adopted for the estimation of total chromium in water samples because both procedures applied for total chromium gave similar results. The methods were applied to the determination of total chromium and hexavalent chromium in 40 water samples.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115873137596157966?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115873137596157966/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115873137596157966' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115873137596157966'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115873137596157966'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/quantification-of-total-chromium-and.html' title='QUANTIFICATION OF TOTAL CHROMIUM AND HEXAVALENT CHROMIUM IN WATER BY ELECTROTHERMAL ATOMIC ABSORPTION SPECTROMETRY'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115872863819380882</id><published>2006-09-19T21:57:00.000-07:00</published><updated>2006-09-19T22:03:58.563-07:00</updated><title type='text'>ASSESSMENT OF THE COMPOSITION AND THE VOLUME OF BIOGAS LIBERATION FROM AGRICULTURAL WASTES</title><content type='html'>&lt;strong&gt;G. Y. Jayasinghe, K. D. N. Weerasinghe, &amp; S. R. W. Pathiranage&lt;/strong&gt;&lt;br /&gt;Department of Agricultural Engineering, Faculty of Agriculture,&lt;br /&gt; University of Ruhuna&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;Study was conducted in the Faculty of Agriculture, University of Ruhuna, Mapalana to assess the composition and the volume of biogas liberation pattern from different agricultural raw materials.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;In the Sri Lankan batch type biogas. generator (volume 6m3), first batch of straw (1000kg) was filled in September 1999 and second and third batch in October 2000, April 2001 respectively. It was revealed that average gas production from the, digester was 1.0 m3 /day with a peak value of 1.8m3/day. Total gas production during four and half month period of digestion was 166.85 m3. The maximum average methane percentage and the average lag phase during the digestion were 50% and 20 days respectively.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;In order to assess the biogas liberation pattern and composition of each material, a laboratory test unit was designed using a 20 L plastic gallon as the digester and experiment was conducted using straw, cow dung and market garbage (vegetable) as raw materials. Gas volumes, pH value of slurry and methane percentage were measured while maintaining the temperature between 35°C-37°C using electric bulbs.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;N,P,K compositions, C/N ratio and dry matter percentages of different raw materials were analyzed. Total biogas liberated per unit weight of dry matter was 8.15 L, 58.7 L and 15.797L for dung, vegetable and straw respectively. The duration of digestion period was 55-60 days. Average methane percentages of the liberated gases were 53%, 54% and 50% for dung, vegetable and straw respectively. It was revealed that market garbage had the highest digestibility value, which had the highest gas production with high methane percentage.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115872863819380882?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115872863819380882/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115872863819380882' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115872863819380882'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115872863819380882'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/assessment-of-composition-and-volume.html' title='ASSESSMENT OF THE COMPOSITION AND THE VOLUME OF BIOGAS LIBERATION FROM AGRICULTURAL WASTES'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115864716672864152</id><published>2006-09-18T23:24:00.000-07:00</published><updated>2006-09-18T23:26:06.890-07:00</updated><title type='text'>AGROA-CLIMATIC POTENTIAL ASSESSMENT FOR CROP INTENSIFICATION IN SOUTHERN SRI LANKA - A CASE STUDY IN MATARA DISTRICT</title><content type='html'>&lt;div align="justify"&gt;&lt;strong&gt;C.M. Navaratne &amp; K.D.N. Weerasinghe&lt;br /&gt;&lt;/strong&gt;Department of Agricultural Engineering, Faculty of Agriculture,&lt;br /&gt;University of Ruhuna&lt;br /&gt;&lt;br /&gt;The climatic potential in respect to onset, duration and magnitude of the rainfall were assessed using the rainfall probability concepts and the climatic water balance approach. The rainfall data for 45 consecutive years (1950 - 1995) were collected from 10 stations in different agro climatic regions of Matara district. The limits of 10 mm weekly rain at 75% probability and Hargreave's Moisture Availability Index of 0.34 in weekly basis were used to demarcate wet and dry weeks of the area.&lt;br /&gt;&lt;br /&gt;The 1st – 10th  and the 26th  - 36th  weeks of the calendar year are recorded as dry weeks in the selected regions except, in Anninkanda. The duration of wet period during Yala and Maha seasons in the selected regions differs from, 1 week to 21 weeks and it is closely related with the mean annual rainfall of the regions. Among all selected regions, the longest wet period is recorded in Anninkanda whereas the shortest wet period is recorded in Kekanadura and Dandeniya.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The onset of rain in Yala and Maha seasons falls during 9th  – 20th  and 34th  - 40th  meteorological weeks respectively in all the selected regions. The early onset of rain is expected in the locations where the annual rainfall is high. The duration and magnitude of rainfall increase from south to north and from east to west in the district.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115864716672864152?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115864716672864152/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115864716672864152' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115864716672864152'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115864716672864152'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/agroa-climatic-potential-assessment_18.html' title='AGROA-CLIMATIC POTENTIAL ASSESSMENT FOR CROP INTENSIFICATION IN SOUTHERN SRI LANKA - A CASE STUDY IN MATARA DISTRICT'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115864691606624514</id><published>2006-09-18T23:09:00.000-07:00</published><updated>2006-09-18T23:32:53.430-07:00</updated><title type='text'>COMPARATIVE STUDIES ON RAPID AND COST EFFECTIVE PROPAGATION METHODS AND INITIAL ESTABLISHMENT OF THE MEDICINAL PLANT Phyllanthus debilis KLIN EX WILLD</title><content type='html'>&lt;strong&gt;K. N. S. Perera 1 &amp; K. U. Tennakoon2&lt;br /&gt;&lt;/strong&gt;1 Faculty of Applied Sciences, Sabaragamuwa University of Sri Lanka&lt;br /&gt;2Department of Botany, Faculty of Science, University of Peradeniya&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;&lt;em&gt;Phyllanthus debilis&lt;/em&gt; Klein ex Willd. (Sinhala - Elapitawakka) is a widely used annual herb used in Ayurvedic medicine. The main objective of this study was to develop simple and cost effective propagation methods and growth media for initial establishment of &lt;em&gt;P. debilis.&lt;/em&gt;&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The experimental design was a completely randomized design. Fresh fruit samples at four different stages (light green, dark green, blackish green and brownish yellow) of maturity were used to determine the best maturity stage that gives the highest percentage. Seeds obtained from blackish green fruits gave the highest percentage germination (92 %) when grown on wet filter paper. Percentage of seed germination in dark green and brownish yellow fruits on wet filter paper were 26 % and 65 % respectively and 22 % and 12 % respectively when coir dust: sand (1; 1) medium was used. Seeds obtained from light green fruits did not germinate. Upper and lower stem cuttings of &lt;em&gt;P. debilis&lt;/em&gt; showed very low percentage success 2 % and 7 % respectively. Seed moisture content was determined using four seed samples (n = 100) dried at 103*C for 17 hours. The average moisture content of a seed was 15 t 1 %. Hence it can be regarded as an "intermediate" seed type. The seed. viability was tested at weekly intervals for nine weeks. The highest percentage of germination (82 %) was observed in one-week-old seeds. Seed viability decreased gradually over the nine-week period and none of the seeds germinated after nine weeks of storage. Nine different potting media were tested for the initial establishment of &lt;em&gt;P. debilis&lt;/em&gt;. Plants grown (n = 20) in the medium comprising top soil: compost: sand (1: 1: 1) performed well in terms of plant height, leaf number and root collar diameter than in the other potting media.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;&lt;em&gt;Financial Assistance provided by Sri Lanka Conservation and Sustainable Use of Medicinal Plants Project is gratefully acknowledged.&lt;/em&gt;&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115864691606624514?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115864691606624514/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115864691606624514' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115864691606624514'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115864691606624514'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/comparative-studies-on-rapid-and-cost.html' title='COMPARATIVE STUDIES ON RAPID AND COST EFFECTIVE PROPAGATION METHODS AND INITIAL ESTABLISHMENT OF THE MEDICINAL PLANT Phyllanthus debilis KLIN EX WILLD'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115857207265215980</id><published>2006-09-18T02:19:00.000-07:00</published><updated>2006-09-18T02:34:32.743-07:00</updated><title type='text'>VEGETATIVE PROPAGATION OF Scyphiphora hydrophyllacea GAERTN F. FOR CONSERVATION</title><content type='html'>&lt;strong&gt;P. L. Hettiarachchi1, P. A. G. W. Premathilake1 &amp; S. Hettiarachchi 2 &lt;/strong&gt;&lt;br /&gt;&lt;strong&gt;1 Department of Botany, University of Sri Jayewardenepura&lt;br /&gt;2 Department of Botany, University of Ruhuna&lt;/strong&gt;&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;&lt;em&gt;Scyphiphora hydrophyllacea&lt;/em&gt; is a highly threatened true mangrove confined to Jaffna and a single locality in private land in Kalpitiya, Sri Lanka. It produces fruits and seeds, but seedlings and young plants are absent ir: the natural habitat. Conservation has become essential and urgent to prevent local extinction of the species. Seed germination using moist filter paper method with habitat water varying from 0% - 100% concentration totally failed in a previous study. This investigation therefore, aims at the possibility of propagating &lt;em&gt;S. hydrophyllacea&lt;/em&gt; by vegetative means viz. stem cuttings, girdle cuttings and air layering. Stem cuttings of three stages of maturity (first 5 nodes, 6-9 nodes, 10-13 nodes) were used. Distilled water, water from natural habitat and its 75%, 50% to and 25% dilutions with and without IAA and activated charcoal (0.25g/100m1) were tested for rooting. Further, dipping of the cut base of the cuttings in commercial rooting powders namely Secto containing NAA, Seridox tnd Clonex both containing IBA and different concentrations of IAA (0.5mg/1 -2.0mg/a) prior to leaving for rooting was also carried out. Air layering was done by enclosing one-nuonth-old girdles in moist rooting media (three different mixtures and habitat soil). After one month 50ml of half strength Hogland solution was injected to the medium. Another set of layers were treated by applying a paste of Secto on the trimmed edge of the girdle, mixing the same powder with the rooting medium and injecting IAA to the root ball after one month. Rooted cuttings, girdles and layers were transferred to soil substrate in pots and maintained under green house conditions. Rooting was observed only in distilled water, in both stem and girdle cuttings. There was no significant effect by exogenous IAA and commercial rooting powders. Charcoal improved rooting from girdle cuttings up to 75%. Stage 11 (6-9 nodes from the apex) cuttings gave highest percentage (40%) of rooting. A maximum of 60% of layers had rooted in one month. Use of IAA and rooting powder did not improve the rooting percentage in layers. The plantlets obtained are established in pots in the green house under natural temperature and light. The results satisfactorily show that &lt;em&gt;S. hydrophyllacea&lt;/em&gt; can be vegetatively propagated by using, appropriate methods. This is important in conservation, as they do not produce scedlings from seeds. Experiments in hardening of the plantlets to grow in their natural habitat are in progress.&lt;br /&gt;&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115857207265215980?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115857207265215980/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115857207265215980' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115857207265215980'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115857207265215980'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/vegetative-propagation-of-scyphiphora.html' title='VEGETATIVE PROPAGATION OF Scyphiphora hydrophyllacea GAERTN F. FOR CONSERVATION'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115857115716375211</id><published>2006-09-18T02:18:00.000-07:00</published><updated>2006-09-18T02:19:17.263-07:00</updated><title type='text'>FACTORS LIMITING SEED GERMINATION IN Scyphiphora hydrophyllacea GAERTN f. AND Pemphis acidula J R &amp; FORST</title><content type='html'>&lt;div align="justify"&gt;&lt;br /&gt;&lt;strong&gt;P L Hettiarachchi &amp; R K Jayaratne&lt;br /&gt;Department of Botany, University of Sri Jayewardenepura&lt;br /&gt;&lt;/strong&gt;&lt;br /&gt;Scyphiphora hydrophyllacea is a highly threatened true mangrove confined to Jaffna and a single locality in Kalpitiya (Trillion 1974; Dassanayake and Clayton 1998). &lt;em&gt;Pemphis acidula&lt;/em&gt; is restricted to small pockets in few coastal areas. Both produce fruits and seeds nevertheless, seedlings were not observed in their natural habitats. Factors governing seed germination in these two species were studied. For all experiments, randomly collected ripe , seed samples were used within two weeks of collection. Moist filter paper method was used and daily observations were recorded.&lt;br /&gt;&lt;br /&gt;In &lt;em&gt;P. acidula&lt;/em&gt;, seed production was 100%. Percentage of fruit bearing seeds was 10% in S&lt;em&gt;. hydrophyllacea&lt;/em&gt;, but none of them gave rise to healthy seedlings. Seed germination of both species was 0%in water collected from respective natural habitats. In &lt;em&gt;P. acidula&lt;/em&gt; %gerrnination was 35% in 75% and 40% in 87.5% dilution of water from natural habitat. In distilled water, 65% of the seeds germinated. Continuous washing of seeds in running tap water increased percentage germination to 75%.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Dormancy breaking treatments such as heat treatment, seed nicking, acid base treatment, cold treatment and treatment with gibberrelic acid did not increase germination above normal 65% value. &lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Exposure to natural light, photoperiod and oxygen level also affected seed germination. Analysis of data consisted of ANOVA at 5% level of significance using Minitab package. In &lt;em&gt;P. acidula&lt;/em&gt;, salinity of soil water (up to 34 ppt) and salt deposits on seed coat seem to be major causes hindering seed germination in natural habitat. Seeds buried in sand may also not receive adequate amount of light (Isikava 1962; Fujii 1962). Oxygen concentration may not be enough when the ground is covered with water during tides. Lack of seedlings may therefore be due to lack of seed germination under natural conditions.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;In &lt;em&gt;S. hydrophyllacea&lt;/em&gt;, very low percentage of seed bearing fruits and inability to produce healthy seedlings explain why it has become highly threatened. Production of large number of seedless fruits and inability to produce normal seedlings could be due to genetic disorder in seeds, which is a very common pheraorncnon known as inbreeding depression in isolated, small populations.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Presence of self-sterility and the absence of pollinator right be some other reasons. Hence, studies on the possibility of propagating &lt;em&gt;S. hydrophyllacea &lt;/em&gt;by vegetative means are urgently needed to conserve this highly threatened tree species.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115857115716375211?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115857115716375211/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115857115716375211' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115857115716375211'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115857115716375211'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/factors-limiting-seed-germination-in_18.html' title='FACTORS LIMITING SEED GERMINATION IN Scyphiphora hydrophyllacea GAERTN f. AND Pemphis acidula J R &amp; FORST'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115857113123388579</id><published>2006-09-18T02:06:00.000-07:00</published><updated>2006-09-18T02:18:51.393-07:00</updated><title type='text'>FACTORS LIMITING SEED GERMINATION IN Scyphiphora hydrophyllacea GAERTN f. AND Pemphis acidula J R &amp; FORST</title><content type='html'>&lt;div align="justify"&gt;&lt;br /&gt;&lt;strong&gt;P L Hettiarachchi &amp; R K Jayaratne&lt;br /&gt;Department of Botany, University of Sri Jayewardenepura&lt;br /&gt;&lt;/strong&gt;&lt;br /&gt;Scyphiphora hydrophyllacea is a highly threatened true mangrove confined to Jaffna and a single locality in Kalpitiya (Trillion 1974; Dassanayake and Clayton 1998). &lt;em&gt;Pemphis acidula&lt;/em&gt; is restricted to small pockets in few coastal areas. Both produce fruits and seeds nevertheless, seedlings were not observed in their natural habitats. Factors governing seed germination in these two species were studied. For all experiments, randomly collected ripe , seed samples were used within two weeks of collection. Moist filter paper method was used and daily observations were recorded.&lt;br /&gt;&lt;br /&gt;In &lt;em&gt;P. acidula&lt;/em&gt;, seed production was 100%. Percentage of fruit bearing seeds was 10% in S&lt;em&gt;. hydrophyllacea&lt;/em&gt;, but none of them gave rise to healthy seedlings. Seed germination of both species was 0%in water collected from respective natural habitats. In &lt;em&gt;P. acidula&lt;/em&gt; %gerrnination was 35% in 75% and 40% in 87.5% dilution of water from natural habitat. In distilled water, 65% of the seeds germinated. Continuous washing of seeds in running tap water increased percentage germination to 75%.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Dormancy breaking treatments such as heat treatment, seed nicking, acid base treatment, cold treatment and treatment with gibberrelic acid did not increase germination above normal 65% value.    &lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Exposure to natural light, photoperiod and oxygen level also affected seed germination. Analysis of data consisted of ANOVA at 5% level of significance using Minitab package. In &lt;em&gt;P. acidula&lt;/em&gt;, salinity of soil water (up to 34 ppt) and salt deposits on seed coat seem to be major causes hindering seed germination in natural habitat. Seeds buried in sand may also not receive adequate amount of light (Isikava 1962; Fujii 1962). Oxygen concentration may not be enough when the ground is covered with water during tides. Lack of seedlings may therefore be due to lack of seed germination under natural conditions.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;In &lt;em&gt;S. hydrophyllacea&lt;/em&gt;, very low percentage of seed bearing fruits and inability to produce healthy seedlings explain why it has become highly threatened. Production of large number of seedless fruits and inability to produce normal seedlings could be due to genetic disorder in seeds, which is a very common pheraorncnon known as inbreeding depression in isolated, small populations.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Presence of self-sterility and the absence of pollinator right be some other reasons. Hence, studies on the possibility of propagating &lt;em&gt;S. hydrophyllacea &lt;/em&gt;by vegetative means are urgently needed to conserve this highly threatened tree species.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115857113123388579?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115857113123388579/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115857113123388579' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115857113123388579'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115857113123388579'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/factors-limiting-seed-germination-in.html' title='FACTORS LIMITING SEED GERMINATION IN Scyphiphora hydrophyllacea GAERTN f. AND Pemphis acidula J R &amp; FORST'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115857037848000499</id><published>2006-09-18T01:58:00.000-07:00</published><updated>2006-09-18T02:06:21.256-07:00</updated><title type='text'>INVESTIGATION OF THE EFFECTIVENESS OF MOTHER ENZYME ON MODEL ORGANIC WASTE MATERIAL BY ENZYME DEGRADATION</title><content type='html'>&lt;strong&gt;A.G. I . I . Wimaladharma1, N.J.G.J.Bandara1 &amp;amp; A.H.D.O. Bammunuarachchi2&lt;br /&gt;1 Department of Forestry and Environmental Science, University of Sri jayewardenepura&lt;br /&gt;2 Department of Chemistry&lt;br /&gt;University of Sri Jayewardenepura&lt;/strong&gt;&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;Continuous disposal of solid waste arid their collection creates a severe environmental and health hazard. In Sri Lanka the major percentage of municipal solid waste is organic waste. Hence, one-way of over coming this problem is to increase the rate degradation of organic material in which enzyme and microorganisms play a big role. Mother Enzyme (ME) is said to be one such mixture of enzymes and microorganisms.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Objectives of this research was to identify the constituents of the ME, to determine the effectiveness of the ME on degradation' of different types of organic wastes, and to determine the effective levels of ME for different types of organic wastes.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Macconkey agar, Nutrient agar and Sabouraud Dextrose Agar were used to find the total number and the types of microorganisms present in the ME. Effect of Mother enzyme an different of organic waste were done by using Farm (cattle and poultry) waste, kitchen wastes and fruit industry wastes in the presence and in the absence of ME with replication. Weight reduction with time was noted down. To estimate the effect of ME on model organic waste, wheat flour, egg yolk and coconut oil were used. Alanine, Glucose and Acid value estimation were done to estimate the rate of degradation of the macromolecules in the presence of and in the absence of ME. In order to find out the effective levels of ME farm (cattle and poultry), kitchen wastes and fruit industry wastes were used with replication. 2g/lkg and O.5g/lkg of mother enzyme was introduced and weight reduction was noted down.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Form the Microbiological analysis, &lt;em&gt;Staphylococcus aureus&lt;/em&gt;, &lt;em&gt;Esscherichia colli&lt;/em&gt;, and &lt;em&gt;Mucor&lt;/em&gt;, were found to be present in ME and the total number of organisms present was 13x10-14 .&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;From the study it was revealed that the break down of model organic matter - fats and proteins occur quite fast in the presence of another enzyme. But mother enzyme does not significantly increase breaking down of carbohydrates.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Increased or decreased levels of ME have no significant effect on mixed organic wastes. Due to our consumption pattern most of organic wastes generated in Sri Lanka are of carbohydrate origin. This may be the reason why there is no significant effect due to ME on mixtures of organic wastes found in Sri Lanka.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115857037848000499?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115857037848000499/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115857037848000499' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115857037848000499'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115857037848000499'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/investigation-of-effectiveness-of.html' title='INVESTIGATION OF THE EFFECTIVENESS OF MOTHER ENZYME ON MODEL ORGANIC WASTE MATERIAL BY ENZYME DEGRADATION'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115856988404752296</id><published>2006-09-18T01:51:00.000-07:00</published><updated>2006-09-18T01:58:04.136-07:00</updated><title type='text'>FUTURE OF BITUMEN EMULSION AS-AN ENVIORNMENTAL FRIENDLY ROAD CONSTRUCTION MATERIAL</title><content type='html'>&lt;strong&gt;H.L.D.M.A. Judith &amp; J.M.S.J.Bandara&lt;br /&gt;Department of Civil Engineering, University of Moratuwa.&lt;/strong&gt;&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;Bitumen emulsion is a thermodynamically unstable- heterogeneous system in which finely ground bitumen particles are dispersed in an aqueous medium. In most parts of the world usage of bitumen emulsion as a road construction material has increased during the recent past partially replacing penetration grade bitumen (tar) and cutback bitumen due to environmental reasons. In Sri Lanka bitumen emulsion is used for certain road construction work. However, still there is somewhat reluctance among road engineers to use bitumen emulsion as a substitute for other types.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;There are numerous uses for bitumen emulsion utilizing highly varied techniques, which results in several different formulations; namely cationic and anionic depending on particle charges and rapid setting, medium setting and slow setting depending on its speed of separation of bitumen from aqueous medium. In Sri Lanka, cationic type bitumen emulsion is used, as majority of the available local aggregates are acidic except Jaffna limestone.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Bitumen emulsion is suitable to the requirements of all road maintenance work. Ease of storage and transport make it possible to set up numerous depots and its ease and facility of use enable work to be done quickly causing minimum disturbance to the users. It may be the first choice bituminous material for all maintenance work on road pavements due to environmental friendliness, provided that correct proportions and standard specifications are being used.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Bitumen emulsion has proven itself as a binder, which utilizes very low energy consumption in road maintenance and laying of surface dressings. Penetration grade bitumen requires heating at construction sites, which emit smoke with chemicals and also it needs fuel, which is a non-renewable resource. Kerosene that is used for cutting back the viscosity of bitumen is also a non-recoverable waste when curing takes place on the road.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;This paper identifies the advantages of using bitumen emulsion over other traditional alternatives and investigates the reasons for the reluctance to use locally. The paper proposes suitable remedial measures to overcome the perceived disadvantages and increase the use of bitumen emulsion as an environment friendly alternative.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115856988404752296?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115856988404752296/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115856988404752296' title='1 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856988404752296'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856988404752296'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/future-of-bitumen-emulsion-as.html' title='FUTURE OF BITUMEN EMULSION AS-AN ENVIORNMENTAL FRIENDLY ROAD CONSTRUCTION MATERIAL'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>1</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115856947893511858</id><published>2006-09-18T01:21:00.000-07:00</published><updated>2006-09-18T01:51:19.066-07:00</updated><title type='text'>DEVELOPMENT OF AN ENVIRONMENT FRIENDLY METHOD TO REMOVE THE COLORED COMPONENTS FROM INDUSTRIAL WASTE WATER</title><content type='html'>&lt;strong&gt;Dinesh Pandithawidansa &amp; K.R. Ranjith Mahanama &lt;/strong&gt;&lt;br /&gt;&lt;div align="justify"&gt;&lt;strong&gt;Department of Chemistry, University of Colombo&lt;br /&gt;&lt;br /&gt;&lt;/strong&gt;Nowadays, synthetic dye context is a vital component in the textile and dyeing industries. The garment factories in the free trade zone that are discharging dyes and other coloured compounds into waterways pollute the environment. In this project, attempts were made to design an environment friendly methodology to degrade Azo dyes by means of Eco-&amp;shy;efficient techniques. Optimum conditions were evaluated for the redox-degradation of the Azo dye; and some of the dyes that are used in garment industry. The fidelity of the proposed mechanism was confirmed by the; spectroscopic and GC analyses. As a reducing agent, metallic iron has fulfilled all the requirements that are prescribed for green chemical concepts.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The results presented in this report clearly demonstrate that Anthroquinone-2-sulphonic acid is a powerful catalyst, capable of ,accelerating the reaction rate by orders of magnitude. The powdered form of charcoal amalgamated with metallic iron has facilitated as a better substrate to adsorb the dye component improving the contacts of reactant molecules with the catalyst and dye molecules. The experimental results revealed that pH 4 is the optimum condition for the redox degradation of the dye, which is confirmed by electrochemical, and thermodynamic calculations. The elevation of the reaction temperature has accelerated the reaction by several orders of magnitude. To demonstrate the applications in real world; a continuous flow reduction apparatus was designed and constructed.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115856947893511858?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115856947893511858/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115856947893511858' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856947893511858'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856947893511858'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/development-of-environment-friendly.html' title='DEVELOPMENT OF AN ENVIRONMENT FRIENDLY METHOD TO REMOVE THE COLORED COMPONENTS FROM INDUSTRIAL WASTE WATER'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115856766238606999</id><published>2006-09-18T01:12:00.000-07:00</published><updated>2006-09-18T01:21:02.496-07:00</updated><title type='text'>HIGH RATE BIO METHANATION OF MUNICIPAL SOLID WASTE</title><content type='html'>&lt;div align="justify"&gt;&lt;strong&gt;Upali Wanigaratne, Sanja Gunawardena, Kapila Perera &amp; Ajith De Alwis&lt;br /&gt;Department of Chemical and Process Engineering,&lt;br /&gt;University of Moratuwa&lt;br /&gt;&lt;/strong&gt;&lt;br /&gt;Growing urbanization and industrialization have led to the generation of large quantities of solid wastes, which can be broadly classified as MSW (Municipal Solid Waste) and ISW (Industrial Solid Waste). Among the options available for solid waste management, biomethanation appears to be the most desirable because it is a technology with triple benefits yields biogas which can replace conventional fuels, provides digested sludge which can be used as a soil conditioner and manages the environment.&lt;br /&gt;&lt;br /&gt;This work involved the development of a three-stage leachate based bioreactor system for solid waste management. The first stage involves extraction of high organic strength (high in chemical oxygen  demand - COD) liquid called leachate from the solids. This stage is known as the hydrolyzing stage. Acid formation takes place in the second or the acidification stage in a separate reactor known as the acidification reactor. Biogas is generated by treating the acidified leachate in an upflow anaerobic filter (AF) reactor in the third (or the methanation) stage.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Three stage anaerobic systems are increasingly finding its place in biogas generation. Two kinetically dissimilar groups of bacteria, acetogenesis and methanogenesis are physically separated in acetogenic reactor and methanogenic reactor. This separation allows optimization of both acetogenesis and methanogenesis stages making the process control easier.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;In this method, the organic solid waste is cut into small pieces, fed into the hydrolyzing reactor with water and circulated at a fixed rate to wash off organic acids formed until high organic strength is obtained. This is then fed in to the acidification reactor. The acidification phase has retention time of 6 days. Anaerobic conditions prevail inside the reactor during the whole process. The residue left inside from the first reactor is subjected to drying for manure preparation.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The final concentrated leachate obtained after G days is fed in to the AF reactor for methanation. This phase has retention time of 5 days. The microbial consortia present in the AF sludge destroys high amount of COD, forming biogas comprising of 65% - 75% methane. This system is economically viable, the total space and the time required for the process is low compared to conventional single&amp;shy; phase processes that takes 30-40 days. The system has low water consumption because of the reuse of the AF reactor overflow to the acidification reactor.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115856766238606999?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115856766238606999/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115856766238606999' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856766238606999'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856766238606999'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/high-rate-bio-methanation-of-municipal.html' title='HIGH RATE BIO METHANATION OF MUNICIPAL SOLID WASTE'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115856711081360193</id><published>2006-09-18T01:04:00.000-07:00</published><updated>2006-09-18T01:11:50.876-07:00</updated><title type='text'>AN INVESTIGATION INTO THE ECOTOURISM DEVELOPMENT POTENTIAL IN ILLUKKUMBURA AREA IN THE KNUCKLES RANGE</title><content type='html'>&lt;div align="justify"&gt;&lt;strong&gt;C. Maelge &amp; D.M.S.H.K.Ranasinghe&lt;br /&gt;Department of Forestry and Envirobmental Science,&lt;br /&gt;University of Sri Jayewardenepura&lt;br /&gt;&lt;/strong&gt;&lt;br /&gt;Knuckles National Heritage Wilderness Area is approximately 155 km2 and is located in the Central Province of Sri Lanka. Knuckles forested area has high endemic biodiversity and possesses a rich cultural history. !It falls under the administration of the Forest Department, The area has been separated into three different zones, for systematic implementation of ecotourism activities. Illukkumbura is one such ecotourism zone of the Knuckles forested area.&lt;br /&gt;&lt;br /&gt;Objectives of the study are  to explore  the ecotourism    development  potential  of Illukkumbura area, promotion of local. community participation in ecotourism and recommendation of strategies to promote Illlukkumbura area in the global tourism market. Comprehensive literature survey was conducted to gather secondary data, with regard to ecotourism and its subject matter. Primary data was collected initially through a reconnaissance survey, to demarcate the study site, familiarize with key decision makers of the villages and provided the basis to select the study area and participant for the Participatory Rural Appraisal as well as decide on the time duration of the Participatory Rural Appraisal. To gather in depth primary data Participatory Rural Appraisal was conducted in the selected villages, with a questionnaire assisted interview process. The respondents were selected using random sample techniques, which comprised of SU participants. Field observations were carried out in all ecotourism attractions at Illukkumbura area. Specific attention was given to the site selection for suitable ecotourism activities, especially suited for various ecotourists.&lt;br /&gt;&lt;br /&gt;Study revealed that Illukkumbura zone is patronized by tourist both domestic and foreign at present mainly for trekking, swimming and camping. Study resulted in evaluating the importance of the each nature trail for ecotourism, exploring other ecotourism sites in the area, exploring the potential of community participation in ecotourism, developing a communication strategy for the area and drawing up proposed guidelines for a ecotourism development plan in the Illukkumbura area. Recommendations were made in line to promote continuous research with relation to ecotourism and adapt better management ecotourism practices for sustainable development.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115856711081360193?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115856711081360193/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115856711081360193' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856711081360193'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856711081360193'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/investigation-into-ecotourism.html' title='AN INVESTIGATION INTO THE ECOTOURISM DEVELOPMENT POTENTIAL IN ILLUKKUMBURA AREA IN THE KNUCKLES RANGE'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115856661273194328</id><published>2006-09-18T00:55:00.000-07:00</published><updated>2006-09-18T01:03:32.896-07:00</updated><title type='text'>FORMULATION OF SUSTAINABLE AGRO FORESTRY MODELS FOR NORTH CENTRAL DRY ZONE OF SRI LANKA</title><content type='html'>&lt;strong&gt;U. Lakshmani1 &amp; D.M.S.H.K.Ranasinghe2&lt;br /&gt;1 Department of Agriculture&lt;br /&gt;2 Department of Forestry &amp;amp; Environmental Science,&lt;br /&gt;University of Sri Jayewardenepura&lt;/strong&gt;&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;Increase of human population and clearing of forests for their requirements has been a local as well as global environmental crisis. In Sri Lanka, forest cover has dwindled at an alarming rate from 70% in 1990 to 22% as of present. Deforestation and degradation of land due to many reasons including poverty related land management practices such as shifting cultivation and forest encroachments, conversion of forest estate to other more economically profitable land uses are some of the reasons for the loss of forest. Agroforestry has been identified all over the world as an appropriate alternative which provides sustainability.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;According to the Forestry Sector master Plan (1995) the necessity of utilizing the sparsely&amp;shy; used scrub lands for agroforestry ventures to improve the tree cover and socio-economic status of the people has been identified. Forest Department too in its Participatory Forestry Project has ventured into establishment of farmers woodlots with the active participation of communities and this programme is wide spread in many parts of the country especially in the dry zone. However, the composition of these farmers woodlots still not complete to incorporate diversity and sustainability. Therefore, the objective of this present study is to formulate sustainable tree-crop models for a wide range of land classes in the north central dry zone of Sri Lanka.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Ipalogama divisional Secretariat in Anuradhapura District was identified for the study. Field studies were done in handsomely selected 3 traditional tank based villages namely Sangattewa, Puliyankulama and Dampeleassagama. Information was gathered through a questionnaire survey, field visits and personnel interviews with villagers. Randomely selected 44 households or 14.8% of the total households in the 3 villages were subjected to the survey. The species composition and vertical and horizontal diversity, light requirements, multiple uses, financial returns/ha, prevalence of local/indigenous tree species and farmer's choice were taken into consideration in the formulation of the agroforestry models for the various land classes sampled e.g. Alluvial plains, middle slopes and upper slopes etc.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115856661273194328?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115856661273194328/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115856661273194328' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856661273194328'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856661273194328'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/formulation-of-sustainable-agro.html' title='FORMULATION OF SUSTAINABLE AGRO FORESTRY MODELS FOR NORTH CENTRAL DRY ZONE OF SRI LANKA'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115856609447405548</id><published>2006-09-18T00:44:00.000-07:00</published><updated>2006-09-18T00:54:59.480-07:00</updated><title type='text'>EVALUATION OF SLOPING AGRICULTURAL LAND TECHNOLOGY (SALT) AS A MEANS OF ENSURING SUSTAINABILITY OF TEA YIELDS IN THE UP- COUNTRY WET ZONE (WU2) OF SRI</title><content type='html'>&lt;strong&gt;W.A.J.M. De Costa &amp;amp; P. Surenthran&lt;br /&gt;Department of Crop Science, Faculty of Agriculture, University of Peradeniya&lt;/strong&gt;&lt;br /&gt;&lt;strong&gt;&lt;div align="justify"&gt;&lt;br /&gt;&lt;/strong&gt;Sloping Agricultural Land Technology (SALT) is a system of land management that has been introduced to arrest the decline of soil fertility and sustain yields of tea plantations on sloping terrain in the central highlands of Sri Lanka. SALT involves the incorporation of fast-growing, mostly leguminous tree species as hedgerows along contours at pre-determined distances among tea rows. 'The hedgerows are expected to increase soil fertility by reducing erosion and providing organic matter through frequent addition of prunings. However, SALT hedges could compete with tea for essential growth resources such as water, nutrient and light and consequently reduce tea yields. Therefore, the main objective of this study was to quantify the positive and negative effects of SALT hedges and to determine their net impact on tea yields and parameters of soil fertility.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Two long-term, on-farm field experiments were conducted at Helbodde Estate, Pussellawa in the Up-Country Wet Zone (WU2). The effects of six tree species (&lt;em&gt;Calliandra calothyrsus, Cassia spectabilis, Euphatorium innulifolium, Flemingia congesta, Gliricidia sepium&lt;/em&gt; and &lt;em&gt;Tithonia diversifolia&lt;/em&gt;) growing as contour hedgerows on the long-term yields of mature tea (i.e. in the second pruning cycle) and young tea (i.e. first pruning cycle) were quantified in Experiments 1 and 2 respectively. These experiments also measured the yield response to the addition of mulch material. from different tree species. Continuous yield measurements were done at weekly intervals since November 1998.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Continuous tea yield measurements that were done at weekly intervals were compiled and analyzed over a three-year pruning cycle from November 1998 to October, 2001. In Experiment 1, yield of mature tea growing with &lt;em&gt;Euphatorium&lt;/em&gt; hedgerows was significantly greater titan the yield of tea growing without hedgerows (i.e. control plots). However, yields of nature tea growing with all other laadgerow species were significantly lower than in the cor.trol. Mature tea yields of all hedgerow plots increased significantly in response to the addition of the respective hedgerow prunings as mulch. These results show that although all hedgerow species contribute to the improvement of soil fertility, all hedgerow species except &lt;em&gt;Euphatorium&lt;/em&gt; exert significant resource competition, which exceeds their respective positive fertility effects. In Experiment 2, yields of young tea growing with all hedgerow species, including &lt;em&gt;Euphatorium &lt;/em&gt;showed significant reductions as compared to the yield of sole cropped young tea. This shows that young tea is less able to withstand resource competition from hedgerows than mature tea. However, in Experiment 2, the least yield red action was shown in tea growiag with Euphatorium. Among the different hedgerow tree species tested, Euphatorium showed the highest yield increase due to the addition of prunings as mulch in both'experiments.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115856609447405548?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115856609447405548/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115856609447405548' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856609447405548'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856609447405548'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/evaluation-of-sloping-agricultural.html' title='EVALUATION OF SLOPING AGRICULTURAL LAND TECHNOLOGY (SALT) AS A MEANS OF ENSURING SUSTAINABILITY OF TEA YIELDS IN THE UP- COUNTRY WET ZONE (WU2) OF SRI'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115856544949540820</id><published>2006-09-18T00:37:00.000-07:00</published><updated>2006-09-18T00:44:09.593-07:00</updated><title type='text'>IMPROVEMENT OF SOIL CHARACTERISTICS UNDER CROP - STOCK INTEGRATION</title><content type='html'>&lt;strong&gt;S.H.R. Priyadarshani &amp; Thakshala Seresinhe &lt;/strong&gt;&lt;br /&gt;&lt;strong&gt;Dept of Animal Science, Faculty of Agriculture, University of Ruhuna&lt;/strong&gt;&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;Soil characteristics and vegetation properties of Diggassawela farm belong to Diddenipotha plantation Limited (approximately 10 km from Kamburupitiya) was studied in view of evaluating the impact of crop - stock long term integration. Crop - stock integration has been practiced in this farm for more than a decade. Compost and farmyard waste were intensively used for tea replanting purposes and pasture cultivation respectively. Soil samples were collected randomly from (3 replicate/location) cattle courtyard, pasture land and compared with an abandoned tea land soil in the same area.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The soil pH ranged from 8.06 for pastureland and 4.53 for an abandoned tea land (P &lt;&gt;0.05). The soil characteristics of pastureland compared with other two sites shows improvement due to nutrient recycling via dairy washings and litter accumulation.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The observations also revealed that the grass yield and longevity of the pastures and fodder were improved significantly with application of farmyard waste. Application of compost also improved the soil properties and increased the rate of survival of tea plants (replanting).&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The results suggest that the waste materials such as excreta, residues of feeding materials, bedding and dairy washings thus produced various benefits with passage of time and demonstrated potential for the sustainability of a crop - livestock integration system. It is suggested that crop - livestock integration could be successfully used for the rehabilitation of tea lands on a long-term basis.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115856544949540820?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115856544949540820/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115856544949540820' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856544949540820'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856544949540820'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/improvement-of-soil-characteristics.html' title='IMPROVEMENT OF SOIL CHARACTERISTICS UNDER CROP - STOCK INTEGRATION'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115856503550684765</id><published>2006-09-18T00:36:00.000-07:00</published><updated>2006-09-18T00:37:15.710-07:00</updated><title type='text'>SPECIES COMPOSITION AND SOIL CHARACTERISTICS BETWEEN GRAZING FORAGE SYSTEMS AND CUT AND REMOVED FORAGE SYSTEMS IN WALAWE REGION</title><content type='html'>S.N. Muditha Manjula &amp; Thakshala Seresinghe&lt;br /&gt;Department of Animal Science, Faculty of Agriculture, University of Ruhuna&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;Botanical composition and soil parameters of grazing and cut and removed forage systems in five villages (Barawakumbuka, Manadala, Nonagama, Bolana, Ambalantotoa) Walawe region were studied to observe the impact of different management systems on the productivity of plant and soil characteristics. Herbage and soil samples were collected randomly using a quadrate (50*5Ocm2) from five grazing and five cut and removed sites. Samples (3 replicates) were collected three times from each locations during the following periods. Herbage from grazing lands consisted 85% grasses and 15% other species. Prostrate grass species such as &lt;em&gt;Eleusine indica&lt;/em&gt; and &lt;em&gt;Chrysopgon aciculatus&lt;/em&gt;, were dominant and improved groundcaver. Moisture (20.04%) retention in the grazed soil was significantly increased due to the improvement of ground cover with increasing the potential for soil conservation. Herbage collected from cut and removed sites consisted 70% grasses and 30% other species.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Dominant plants were tufted species such as &lt;em&gt;Pennisetum polystachyon&lt;/em&gt;; &lt;em&gt;Grewia corpinifolia&lt;/em&gt; and &lt;em&gt;Leucaena leucocepha&lt;/em&gt;. Moisture (6.13%) retention in these sites was significantly lower as compared with grazed sites. &lt;/div&gt;&lt;div align="justify"&gt; &lt;/div&gt;&lt;div align="justify"&gt;Soil collected from grazing sites had higher pH (7.88) as compared to the cut and removed sites (6.13). This may be due to recycling of nutrients via dung and urine. Threading by animals, which may cause a packing of the soil particles and loss of the large pores in the soil mass increased the bulk density (1.34 g/cm3) of the grazing sites as compared with the soil of cut and removed sites (1,16 g/em3). This would have been reduced the porosity of the soil in grazing sites (24.96%) as compared to the soil in cut and removed sites (46.86%). Although the bulk density of the grazing soils was negatively affected by threading, ground cover, moisture retention and spatial redistribution of mineral nutrients are influenced by grazing management as compared with cut and removed systems. Therefore, it can be suggested that grazing management is more suitable for low input output subsistence farming systems in the Walawc region.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115856503550684765?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115856503550684765/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115856503550684765' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856503550684765'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856503550684765'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/species-composition-and-soil.html' title='SPECIES COMPOSITION AND SOIL CHARACTERISTICS BETWEEN GRAZING FORAGE SYSTEMS AND CUT AND REMOVED FORAGE SYSTEMS IN WALAWE REGION'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115856175242022414</id><published>2006-09-17T23:28:00.000-07:00</published><updated>2006-09-17T23:42:32.496-07:00</updated><title type='text'>GROWTH PERFORMANCE OF LARGE DIAMETER RATTAN (Calamus) PLANTED UNDER PINE PLANTATIONS AT SINHARAJA BUFFERZONE.</title><content type='html'>H. S. Gammanpila1, B.M.P. Singhakumara1 &amp; P.M.S. Ashton2&lt;br /&gt;1 Department of Forestry and Environmental Science,&lt;br /&gt;University of Sri ,Jayawardenepura&lt;br /&gt;2 School of Forestry and Environmental  Studies, Yale University, USA.&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;Rattans can be considered as the most important non-timber forest product. Due to heavy exploitation from the wild, the resource is declining at an alarming rate. The present study examined the growth performance in terms of plant height, total lengths of stems, diameter, clump formation and number of live leaves and average growth rates of three large diameter rattan species, namely &lt;em&gt;Calamus zeylanicus&lt;/em&gt; Becc., &lt;em&gt;Calamus thwaitesii&lt;/em&gt; Becc., and &lt;em&gt;Calamus ovoideus&lt;/em&gt; Twa. ex Trim, planted under pine plantations in the buffer zone of Sinharaja, Sri Lanka. Four sites of rattan plantations in ages, 8, 9, 10 and 12 years were selected with each site consisting of five plots. Lengths of stems were estimated and stem diameter was measured without the sheath. Number of live leaves and stems in a clump were counted in each plant. Number of pine trees of each site was counted and soil analysis was carried out to depict the site quality.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The highest stem lengths were recorded in the oldest site and the highest mean height recorded after 12 years was 20 m. Results showed that the height increases with the age and the average growth rate decreases. The highest average growth rate, 1.87 in per year was recorded in the 8 year old plantation and the lowest, 1.75 m was recorded in the 12 year old plantation. Average number of stems in a plant varies from 1 to 4 stems per plant in all four sites. Average diameter of stems in all sites was in the range of 1.8 to 2.1 cm, irrespective of the age of the plantation. The average number of leaves declined with the age of the plantation. In conclusion it is possible to say that although the stem length increases with the age of the plantation, the average growth rate decreases. Average stem diameter and number of stems in a plant have not shown any relationship with the age.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115856175242022414?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115856175242022414/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115856175242022414' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856175242022414'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856175242022414'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/growth-performance-of-large-diameter.html' title='GROWTH PERFORMANCE OF LARGE DIAMETER RATTAN (Calamus) PLANTED UNDER PINE PLANTATIONS AT SINHARAJA BUFFERZONE.'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115856071880897513</id><published>2006-09-17T22:57:00.000-07:00</published><updated>2006-09-17T23:25:19.216-07:00</updated><title type='text'>IMPACT OF SAMBAR DEER (Cervus unicolor unicolor) ON THE VEGETATION AT THE HORTON PLAINS NATIONAL PARK</title><content type='html'>&lt;p align="justify"&gt;L.K.Rajapakse 1, U.K.ta.K.Padmalal  1 &amp; S.W.Kotagama 2&lt;br /&gt;1Department of Zoology, The Open University of Sri Lanka&lt;br /&gt;2Department of Zoology, University of Colombo&lt;br /&gt;&lt;br /&gt;A survey was carried out at the Horton Plains National Park to investigate the influence of sambar deer on grassland and forest vegetation., The method adopted was, comparison of the dominant grassland communities, and seedlings in the forested areas with and without the effect of deer. Three enclosures (20 m x 5 m) were erected in the grassland and four enclosures (20 m x 15 m) were erected in the forest to serve as controls (no grazing). Similar areas adjoining the plots were marked with pegs as test areas (with grazing). Field surveys were carried out during the years 1997 and 1998. Incidence and extent of bark damage by sambar deer was also examined using a scoring method on six transects each measuring 250 m. GSN (Grazing Susceptibility Number) was used as an indicator of the the phytosociological behaviour of sambar in the grassland. Summed Dominance Ratio (SDR) was used to calculate the GSN. During the months of January, March, July and October 1997, GSN values for dominant species in the grassland viz Pennicetum and Chrysopogon were 18.4, 20, 23.75, -3.06 and 18.6, 8.1, 17.23, 19.0 respectively. The minus GSN value of 3.06 indicates that during October Pennicetum grass was not damaged by deer which coincided with the flowering period of that species. Grazing pressure values obtained during the periods July-Sep 97, Sep-Nov 97 , Nov-Jan 98, Jan-Mar 98 for Pennicetum and Chrysopogon were 1.7, 5.6, -17.6, 5.8 and 1, 1, 1, -0.5, 0.9 respectively. Here the minus values indicates heavy grazing. During the periods of less rain and also during peak lactation periods of sambar, the grazing pressure is high (July-September and November-January) compared to positive values of grazing pressure which coincides well with the comparatively high rainfall periods. Studies of the forest vegetation revealed that after a period of two years (1997-1999) 88% of seedlings survived (N=1499) in the enclosure but only 73% of the seedlings survived (N=1488) in the open area. Bark damage is distinct an plants like &lt;em&gt;Cinnaniolnum ovalifolium, Neolitsea fucata, Calophyllum walkeri, Eurya japonica, Eleocarpus subvillosus, Syzigium revolutum,&lt;/em&gt; and &lt;em&gt;Hedyotis lawsoniae&lt;/em&gt; all of which have high IVI (Importance Value Indices). Trees with average dbh 28 cm and average height 7 m were more prone to damage by deer. Only 5% of a total of 921 trees were dead due to bark damage.&lt;br /&gt; &lt;/p&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115856071880897513?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115856071880897513/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115856071880897513' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856071880897513'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115856071880897513'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/impact-of-sambar-deer-cervus-unicolor.html' title='IMPACT OF SAMBAR DEER (Cervus unicolor unicolor) ON THE VEGETATION AT THE HORTON PLAINS NATIONAL PARK'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115829721700204076</id><published>2006-09-14T22:08:00.000-07:00</published><updated>2006-09-14T22:29:19.820-07:00</updated><title type='text'>ESTIMATING THE ABUNDANCE OF SAMBAR DEER( Cervus unicolor unicolor) AT THE HORTON PLAINS NATIONAL PARK Of SRI LANKA</title><content type='html'>&lt;div align="justify"&gt;&lt;strong&gt;LK.Rajapakshe 1, U.K.G.K. Padmalal 1, S.W. Kotagama 2 &amp;amp; N.K. Athulathmudali3&lt;/strong&gt;&lt;br /&gt;1Department of Zoology, The Open University of Sri Lanka&lt;br /&gt;2Department of Zoology, University of Colombo&lt;br /&gt;1National Zoological Garden, Dehiwala&lt;br /&gt;&lt;br /&gt;A study was conducted during the period 1997-2000 to estimate the sambar population at the Horton Plains National Park of Sri Lanka using direct and indirect method. Vehicle based spot light technique was used as the direct method and fecal accumulation method was used as the indirect method. The defecation rate of sambar used in the indirect method was estimated by, a study carried out in the National Zoological Garden Dehiwala, using eight-penned sambar. The mean defecation rate of sambar deer for the eight focal sampling at the Zoological Garden - Dehiwala was twenty-one pellet groups / sambar/ day (range = 20,17- 30). Results of ANOVA revealed that there is a significant variation in defecation rate with age (P&lt;0.05, sig-0.02)but it is not significant sex (P&lt;0.05, Sig-0.09)&lt;br /&gt;&gt;&lt;br /&gt;Altogether 688 transects were run for the direct method. For the indirect method, 200 quadrats measuring 25m*25m size were sampled. Standard equations were used for the population analysis. The estimated sambar population, crude density and ecological density of the direct and indirect methods are 2102.5=B1845, 66.5/km2, 223.5/km2 and 3154=B 11096, 98.9km2, 350/km2 respectively.&lt;br /&gt;&lt;br /&gt;Results indicated that the values obtained by the indirect method are higher than the values obtained from the direct method. The reliability of the indirect method depends on the actual daily defecation rate of sambar deer, which depends on the habitat use. Direct methods are more reliable but not feasible at all times. However indirect method can be used to obtain information on population trends. The results of this study indicate an increase in sambar deer population at the Horton. Plains National Park when compared with estimates made in 1991.&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115829721700204076?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115829721700204076/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115829721700204076' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829721700204076'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829721700204076'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/estimating-abundance-of-sambar-deer.html' title='ESTIMATING THE ABUNDANCE OF SAMBAR DEER( Cervus unicolor unicolor) AT THE HORTON PLAINS NATIONAL PARK Of SRI LANKA'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115829647140768774</id><published>2006-09-14T21:46:00.000-07:00</published><updated>2006-09-14T22:07:12.083-07:00</updated><title type='text'>BIO DIVERSITY IN THE CLOUD FORESTS OF THE KNUCKLES RANGE</title><content type='html'>&lt;div align="justify"&gt;&lt;a href="http://d.r.n.s.rajapakshal/"&gt;&lt;strong&gt;D.R.N.S. Rajapaksha&lt;/strong&gt;&lt;/a&gt;&lt;strong&gt; 1 &amp; &lt;/strong&gt;&lt;a href="http://v.a.m.p.k.samarawickrama2/"&gt;&lt;strong&gt;V.A.M.P.K. Samarawickrama2&lt;/strong&gt;&lt;/a&gt;&lt;br /&gt;I University of Peradeniya&lt;br /&gt;2 IUCN -The World Conservation Union&lt;br /&gt;&lt;br /&gt;The Knuckles Mountain Range is situated in the Intermediate Zone between the latitudes 70°18'-7034' and longitudes 80°41'-80 55' within a 915-1906m elevation range in the Matale District. The slopes directly exposed to monsoon winds receive a high amount of rainfall (2725-4470 mm) per annum. Temperature in the area ranges between 25°C and 27°C at lower altitudes and 18 C-20 C at higher altitudes.&lt;br /&gt;&lt;br /&gt;Data were collected in the two localities Nawanagala and Deenston Nature trail in the sub&amp;shy;&lt;br /&gt;montane 2002and montane forests on the west facing slopes from 6 a.m. to 6 p.m. on 17th-18th August 2002. &lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The trees are low in stature (&lt;em&gt;Syzyium sp&lt;/em&gt;&lt;/em&gt;.), Rutaceac (&lt;em&gt;Toddalia sp&lt;/em&gt;.), Clusiaceae (&lt;em&gt;Calophyllum sp&lt;/em&gt;.), Orcltidaceae (&lt;em&gt;Eria bicolour&lt;/em&gt;) and Liliaceae (&lt;em&gt;Asparagus sp&lt;/em&gt;.). The total number of species observed exceed 35.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The animal life is highly diveres too. The total number of species identified in study area was 124 with 67 bird species (9 endemic), 2 fish (1 endemic), 20 butterflies (2 endemic), 16 mammals (4 endemic), amphibians (6 endemic) and 19 reptiles.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;The Nawanagala and Deenston nature trail are unique areas of island's bio diversity heritage. There are more plant and animal species, especially amphibians yet to be identified. The area faces the threat of periodic fires triggered by People. Moreover, the Deenston nature trail experiences the problem of garbage. Therefore, the bio diversity of this unique area has to be conserved for future generations.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115829647140768774?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115829647140768774/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115829647140768774' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829647140768774'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829647140768774'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/bio-diversity-in-cloud-forests-of.html' title='BIO DIVERSITY IN THE CLOUD FORESTS OF THE KNUCKLES RANGE'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115829554188596068</id><published>2006-09-14T21:38:00.000-07:00</published><updated>2006-09-14T21:45:41.956-07:00</updated><title type='text'>BEHAVIOR OF Ceratophora tennentii GUNTHER,1834 IN RELATION TO AMBIENT TEMPERATURE IN A SELECTED HABITAT !N KNUCKLES FOREST RANGE OF SRI LANKA</title><content type='html'>&lt;strong&gt;P.R.K. Rodrigo1, U.K.G.K. Padmalal 1, LU.P. Samaraweera 1 &amp; &lt;/strong&gt;&lt;a href="http://j.u.l.d.ayantha/"&gt;&lt;strong&gt;J. U. L.D. ayantha&lt;/strong&gt;&lt;/a&gt;&lt;strong&gt; 2&lt;/strong&gt;&lt;br /&gt;1 Faculty of Natural Science, The Open University of Sri Lanka&lt;br /&gt;2 Faculty of Veterinary Medicine and Animal Science,&lt;br /&gt;University of Peradeniya&lt;br /&gt;&lt;div align="justify"&gt;&lt;br /&gt;A research was conducted in the eastern slope of the northern flank of the Knuckles forest range for a period of 3 months from March - June 2002 with the objective of studying the general behavior of &lt;em&gt;C. tennentii&lt;/em&gt; related to the ambient temperature. Data was collected for a period of 10 days between 0800 to 1800 hrs using focal sampling method. Juvenile (J), male (M) and female (F) lizards were observed and the ambient temperature of the substrate used in the habitat was recorded. An average temperature in the study site fluctuated from 16.80°C in the morning, 24.25°C at noon and 16.25°C in the evening. Activity of all lizards was high around noon (1100-1300 hrs) and it was observed that they are relatively inactive in the morning and evening when the ambient temperatures were minimum. All the groups spent more time on resting (J = 50.83%, M = 42% and F = 55.83%). The most preferred substrates were tree trunks and cardamom plants (J = 34.3%, 33.5%; M = 37.3%, 28.2%; F = 13.5%, 32.2% respectively). It can be concluded that the general behavior of &lt;em&gt;C. tennentii&lt;/em&gt; correlates with the ambient temperature where a high degree of activity was observed during the daytime. The optimum range could be 20°C&amp;shy;- 24°C for captive management of these lizards. They preferred substrates exposed to sunlight such as tree trunks and cardamom plants where there were numerous insects during the flowering season.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115829554188596068?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115829554188596068/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115829554188596068' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829554188596068'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829554188596068'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/behavior-of-ceratophora-tennentii.html' title='BEHAVIOR OF Ceratophora tennentii GUNTHER,1834 IN RELATION TO AMBIENT TEMPERATURE IN A SELECTED HABITAT !N KNUCKLES FOREST RANGE OF SRI LANKA'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115829507372602752</id><published>2006-09-14T21:36:00.000-07:00</published><updated>2006-09-14T21:37:53.850-07:00</updated><title type='text'>DISTRIBUTION OF SNAKES IN HANTANA RANGE AND PERADENIYA UNIVERSITY PARK</title><content type='html'>&lt;div align="justify"&gt;&lt;a href="http://v.a.m.p.k.samarawickram/"&gt;&lt;strong&gt;V. A. M.P.K. Samarawickram&lt;/strong&gt;&lt;/a&gt;&lt;strong&gt;a, V Chandrasegaran &amp; K.B.Ranawana&lt;/strong&gt;&lt;br /&gt;Department of Zoology, Faculty of Science, University of Peradeniya&lt;br /&gt;&lt;br /&gt;Sri Lanka is blessed with a diverse serpentine fauna, and the island harbours 93 snake species in 46 genera and 26 families.&lt;br /&gt;Seven major habitat types namely Grasslands, Natural forest patches, Streams and water ways, Pinus plantations, Riverine forests, Agricultural lands, and managed landscape in the Hantana range and Peradeniya University Park were surveyed for six months from November 2001 to April 2002. Day arid night-time survey was carried out to locate snakes and to record their microhabitats. Species identification was done in the held and photographs of snakes were taken whenever necessary.&lt;br /&gt;&lt;br /&gt;Twenty snake species (25% of the total; including six endemics were recorded from the seven sites during the survey. Highest number of species (16) was recorded from the grasslands. Agricultural lands, Riverine forests and Natural forest held the second highest number of species with nine and eight respectively. The number of species in the grassland represents 30% of the total number present in the country.&lt;/div&gt;&lt;div align="justify"&gt;&lt;br /&gt;Hantana Range and the University land are subjected to severe degradation due to human activities. The natural forests have reduced to a greater extent due to the illegal felling, and the grasslands and Pinus plantations are subjected to annual fires. Therefore, the most snake species found in the grasslands are heavily threatened. Study and planning programs should be initiated to conserve the diverse habitats types in the area to protect and conserve the diverse snake fauna of the area.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115829507372602752?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115829507372602752/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115829507372602752' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829507372602752'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829507372602752'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/distribution-of-snakes-in-hantana.html' title='DISTRIBUTION OF SNAKES IN HANTANA RANGE AND PERADENIYA UNIVERSITY PARK'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115829457058583304</id><published>2006-09-14T21:28:00.000-07:00</published><updated>2006-09-14T21:29:30.713-07:00</updated><title type='text'>SUPPORTING THE SRI LANKAN NATIVE BIRD SPECIES JUNGLE FOWL IN ANALOG FORESTRY</title><content type='html'>&lt;div align="justify"&gt;&lt;strong&gt;AM Lokuge &amp; &lt;/strong&gt;&lt;a href="http://k.l.g.h.sanjeewa/"&gt;&lt;strong&gt;K.L.G.H. Sanjeewa&lt;/strong&gt;&lt;/a&gt;&lt;br /&gt;Neo Synthesis Research Station&lt;br /&gt;&lt;br /&gt;An experiment done at model Analog Forestry of Belipola Estate, Mirahawatte, Sri Lanka indicates that an array of native and exotic crops determined by studies and trials made jungle fowl to re-establish, carry out main life activities and thrive in this of proper design.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115829457058583304?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115829457058583304/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115829457058583304' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829457058583304'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829457058583304'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/supporting-sri-lankan-native-bird.html' title='SUPPORTING THE SRI LANKAN NATIVE BIRD SPECIES JUNGLE FOWL IN ANALOG FORESTRY'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115829446982303128</id><published>2006-09-14T21:26:00.000-07:00</published><updated>2006-09-14T21:27:49.966-07:00</updated><title type='text'>FINANCING FOR SUSTAINABLE DEVELOPMENT: SOLUTIONS OF WORLD SUMMIT ON SUSTAINABLE DEVELOPMENT</title><content type='html'>&lt;div align="justify"&gt;&lt;strong&gt;Thosapala Hewage &amp; B.M.S Batagoda&lt;/strong&gt;&lt;br /&gt;Ministry of Environment and Natural Resources&lt;br /&gt;&lt;br /&gt;The World Summit on Sustainable Development (WSSD) held in Johannesburg, South Africa 2002 has given significant priority to finance and trade issues since funding has been identified as key constraints for the implementation of Agenda 21. The Summit adopted some ambitious programs specifically for poverty eradication such as halving the proportion of the world's people whose income is less than $1 a day, proportion of people who suffer from hunger, proportion of people who are without access to safe drinking water and sanitation by 2015. Obviously, the implementation of all its decisions depends on the success of addressing development finance issues that covers a vast range, from official development assistance to Commercial loans by multilateral financial institutions and private banks, foreign direct investment, domestic credits, investment and government transfers. The objective of this paper is to investigate whether the WSSD presents a solution to the financing for sustainable development taking Sri Lanka as a case study.&lt;br /&gt;&lt;br /&gt;The study observed that between 1992-2000 Official Development Assistant (ODA) has fallen steadily from 0.33 % of donor country GNP to 0.22 % although at the Earth Summit developed countries agreed to provide 0.7% of GNP as ODA. This decline has affected the least developed countries (LDCs), who are highly dependant on ODA, which constitutes on the average almost 90% of their total long term capital inflows. However during this period, Foreign Direct Investment (FDI) has significantly increased. FDI to developing countries has increased from US$ 36 billion in 1991 to US$ 185 billion in 1999, but declined to US$ 175 billion in 2000. This is however is only a small portion of the global FDl flows, which amounted to US$ 1.1 trillion in 2000. In 2000, 80% of FDl went to only ten developing countries and LDCs attracted only 2.5 % of all FDI flows to developing countries. In Sri Lanka, foreign direct investments have dropped from US$ 129 Mn in 1977 to US$ 82 Mn 2001. Total outstanding foreign debt has rose from Rs. 235,358 Mn in 1992 to Rs. 634,622 Mn in 2001. This indicates serious debt crises in developing countries, which is not a favorable condition for attracting further FDI to developing countries.&lt;br /&gt;&lt;br /&gt;At the same time measures taken by the international community to treat the excessive debt burdens of 41 heavily indebted poor countries (HIPC) have not delivered the expected results. Thought the IMF and the World Bank have approved debt reduction programs for 22 countries in December 2000, only Uganda was able to clear the prerequisite the creditors. This evidently suggests that the proposed financing measures at the WSSD will also face implementation problems. Unless all debtors and creditors work positively without demanding unreasonable prerequisite for debt relief measures, the objectives of the WSSD cannot be achieved.&lt;br /&gt;&lt;br /&gt;&lt;br /&gt; &lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115829446982303128?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115829446982303128/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115829446982303128' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829446982303128'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829446982303128'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/financing-for-sustainable-development.html' title='FINANCING FOR SUSTAINABLE DEVELOPMENT: SOLUTIONS OF WORLD SUMMIT ON SUSTAINABLE DEVELOPMENT'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115829436353800956</id><published>2006-09-14T21:25:00.000-07:00</published><updated>2006-09-14T21:26:03.656-07:00</updated><title type='text'>EVALUATION OF POLLUTION DAMAGE COST IN BELLANVILA ATTIDIYA WETLAND</title><content type='html'>&lt;div align="justify"&gt;&lt;strong&gt;S.H.B.N.P. Herath &amp;amp; &lt;/strong&gt;&lt;a href="http://ij.a.d.p.gunawardene/"&gt;&lt;strong&gt;U.A.D.P. Gunawardene&lt;/strong&gt;&lt;/a&gt;&lt;br /&gt;Department of Forestry and Environmental Science,&lt;br /&gt;University of Sri Jayewardenepura&lt;br /&gt;&lt;br /&gt;Management of waste, both liquid and solid has become a critical environmental concern particularly in the more urbanized areas in Sri Lanka and this problem is most severe in the densely populated areas of Western province. Bellanwila Attidiya wetland is also one of the places, which is used as open dumpsites. It has bad effects on the health, air quality, bio diversity water, and land.&lt;br /&gt;&lt;br /&gt;The main objective of the present study was to evaluate the pollution damage cost of the wetland. In addition peoples views were also obtained on possibility of recreation in the wetland.&lt;br /&gt;&lt;br /&gt;In the present study the Contingent Valuation Method was used to evaluate tile pollution damage cost of the wetland. Data was derived from a Contingent Valuation survey carried out among the residents of the area and commuters who travel along the road which passes through the wetland. The results were consistent with theory and an aggregate cost of wetland pollution was estimated to be 2870.00 million rupees per year. People expressed their willingness for proposals of developing the wet land as a recreation site.&lt;br /&gt;&lt;br /&gt;The valuation may be useful in cost benefit analysis of wetland management and other related policy and planning programmes related to wetlands. This could be used as an instrument to get the local and international attention and draw funds for the wetland conservation. &lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115829436353800956?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115829436353800956/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115829436353800956' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829436353800956'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829436353800956'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/evaluation-of-pollution-damage-cost-in.html' title='EVALUATION OF POLLUTION DAMAGE COST IN BELLANVILA ATTIDIYA WETLAND'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115829415571389269</id><published>2006-09-14T21:22:00.000-07:00</published><updated>2006-09-14T21:32:12.236-07:00</updated><title type='text'>ECOLOGICAL ECONOMICS: A BETTER FRAMEWORK FOR SUSTAINABLE DEVELOPMENT</title><content type='html'>&lt;div align="justify"&gt;&lt;strong&gt;U.A.D.P. Gunawardena&lt;br /&gt;&lt;/strong&gt;Department of Forestry and Environmental Science,&lt;br /&gt;University of Sri Jayewardenepura&lt;br /&gt;&lt;br /&gt;Sustainable development has been the focus and the target of many resource management related issues. However, proper definitions and frameworks of action have seemed to be greatly unexplored. This paper aims at providing a framework for sustainable development based on concepts of ecological economics. The main focus will be on the issues of intra and inter generational equity on natural resource use and maintaining non-declining levels of critical natural capital.&lt;br /&gt;&lt;br /&gt;The conventional economic view is generally optimistic about the ability of the economic system to overcome natural resource depletion with the help of the technological progress. However, conventional approaches in resource economics limit themselves to only optimal rate of exploitation of a natural resource and determination of optimal pollution discharges. Although such approaches are sensitive to scale issues at the micro level, it is insensitive to the macro level scale of the whole economy relative to the ecosystem. Although the market provides space for substituting abundant resources for scarce ones, it is not able to overcome entropy constraints. Such issues are not reflected in Pareto optimality since optimal allocation is independent of whether or not the scale of physical throughput is ecologically sustainable.&lt;br /&gt;&lt;br /&gt;Therefore is important to recognize the existence of a new constraint on the physical scale of the economy relative to the ecosystem. This constraint has to be set according to the criteria of sustainability and under such constraint, the market will be able to achieve prices which reflect the social value of sustainability.&lt;br /&gt;&lt;br /&gt;Unique natural environments and other critical natural capital need special considerations in economic analysis since technology can do little to replicate their ecological, physical and geographical characteristics. In order to determine the social cost and benefits of a decision to develop a previously undeveloped area, it is necessary to know both the preferences of present and future generations who may be affected by that decision. The existing valuation frameworks and discounting in cost benefit analysis have inherent biases against future generations. Recognition of such facts and identifying the means of minimizing such biases are essential in achieving sustainable development.&lt;br /&gt;&lt;br /&gt;Ecological economic framework is essentially an extension of environment and resource economics in to the explicit analysis of biophysical constraints and equity among generations.&lt;br /&gt;&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115829415571389269?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115829415571389269/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115829415571389269' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829415571389269'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115829415571389269'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/ecological-economics-better-framework.html' title='ECOLOGICAL ECONOMICS: A BETTER FRAMEWORK FOR SUSTAINABLE DEVELOPMENT'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115828635231797132</id><published>2006-09-14T19:12:00.000-07:00</published><updated>2006-09-14T19:12:32.553-07:00</updated><title type='text'>Forestry and Environment Symposium 2005, Sri Lanka: POTENTIAL OF AGROFORESTRY IN SUSTAINABLE DEVELOPMENT IN SRI LANKA</title><content type='html'>&lt;a href="http://forestrysymposium2005.blogspot.com/2006/09/potential-of-agroforestry-in.html"&gt;Forestry and Environment Symposium 2005, Sri Lanka: POTENTIAL OF AGROFORESTRY IN SUSTAINABLE DEVELOPMENT IN SRI LANKA&lt;/a&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115828635231797132?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115828635231797132/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115828635231797132' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115828635231797132'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115828635231797132'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/forestry-and-environment-symposium.html' title='Forestry and Environment Symposium 2005, Sri Lanka: POTENTIAL OF AGROFORESTRY IN SUSTAINABLE DEVELOPMENT IN SRI LANKA'/><author><name>Dr. Hiran Amarasekera</name><uri>http://www.blogger.com/profile/06988028276424542318</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='31' height='32' src='http://2.bp.blogspot.com/_spj17clkJ1E/ScJ379yWqUI/AAAAAAAAABM/yklcilYuJ9E/S220/sakya-brochure.jpg'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115823003547470349</id><published>2006-09-14T03:23:00.000-07:00</published><updated>2006-09-14T03:38:24.563-07:00</updated><title type='text'>EXTENDED COST BENEFIT ANALYSIS OF SAMANALAWEWA HYDROELECTRIC PROJECT</title><content type='html'>&lt;div align="justify"&gt;E.P.N. Udaya Kumara &amp; &lt;a href="http://u.a.d.p.gunawardena/"&gt;U.A.D.P. Gunawardena&lt;/a&gt;&lt;br /&gt;Department of Forestry and Environmental Science,&lt;br /&gt;University of Sri Jayewardenepura&lt;br /&gt;&lt;br /&gt;The Samanalawewa Hydro Electric Project and its water commanding area is the subject of this study. This project is a single purpose hydropower project, which harnesses the waters of the Walawe Ganga by damming the river at the confluence of the Belihul Oya and Walawe Ganga at an elevation of 400m Mean Sea Level. The reservoir covers an extent of 897 ha at normal high water level and its catchment covers an area of 341.7 km.&lt;br /&gt;&lt;br /&gt;As this was a single purpose project, much attention was not paid to other aspects such as supplying irrigation water for down stream, and other environmental impacts. Therefore this study sought to estimate the economic loss due to the reduction of land area and paddy yield at selected down stream areas, In ad;,li0on, it aims to estimate the economic value of lost carbon sequestration function of the Samanalawewa reservoir submerged area and to incorporate the above values in an extended Cost/Benefit analysis for the Samanalawewa project.&lt;br /&gt;&lt;br /&gt;Primary and secondary data were used for this study, which involved a farm household survey. This research disclosed that the scarcity of water due to the dam has resulted in 11.64% of yield reduction (equivalent to 3ti944.38 bushels or Rs. 10.5 million) and 24.8)% of land become uncultivated (equivalent to 444.27 acres or Rs.11.7 million) annually. The global warming damage costs due to °he lost carbon sequestration function of the submerged area is estimated to be Rs. 0.22 million annually. The estimated economic value of surplus water in terms of foregone power generation from the leak at paddy harvesting periods (April, September and October) is Rs. 95.33 million.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115823003547470349?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115823003547470349/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115823003547470349' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115823003547470349'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115823003547470349'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/extended-cost-benefit-analysis-of.html' title='EXTENDED COST BENEFIT ANALYSIS OF SAMANALAWEWA HYDROELECTRIC PROJECT'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115822905972730062</id><published>2006-09-14T03:17:00.000-07:00</published><updated>2006-09-14T21:13:43.200-07:00</updated><title type='text'>LOCAL TOURISTS OF RUHUNA (YALA) NATIONAL PARK: ZONAL VISITATION, TRAVEL COST AND WILLINGNESS TO PAY</title><content type='html'>&lt;div align="justify"&gt;&lt;strong&gt;U. M. I. R. K. Weerasinghe, Dayananda Kariyawasam &amp;amp; Mangala De Zoysa&lt;/strong&gt;&lt;br /&gt;Faculty of Agriculture, University of Ruhuna&lt;br /&gt;&lt;br /&gt;Ruhuna (Yala) National Park, a strict nature reserve which lies on the southern coast of Sri Lanka, covers 97,878 hectares of land. The park comprises of secondary forest where many species of mammals, avifauna, reptiles and birds are living in substantial numbers. The Park has achieved the international reputation. Evidently, all categories of some 100,000 tourists, 70 percent of which are local tourists visit the Park annually. Tourism in a sanctuary is both nature based and sustainable, and sustainability incorporates environmental, socio-cultural and economic dimensions. There should be a control of supply-oriented management securing the environmental and economic benefits. The public interest and enthusiasm in the Park could be used not only to market the product but also to conserve the resources. Hence, the study attempted to analyze the local demand of the tourists for Ruhuna National Park with the view of improving Ruhuna National Park as an attractive tourist's destination.&lt;br /&gt;&lt;br /&gt;The local demand of the tourists for Ruhuna National Park is measured as zonal visitation rate, travel cost, and their willingness to pay. The highest visitation rate is recorded from Badulla (5.6) while the lowest rate is recorded from Matale (2.1). The visitors from Matale have the highest total travel cost (Rs. 732.50). Hambantota visitors spend Rs. 115.04 as the total travel cost. However, the multiple regression analysis shows that the visitation rate with income, age, educational level and 1oIa1 travel cost excluding the visitors from Matara and Hambantota districts, is highly correlated (r 2 = 0.935). However, the age is significantly correlated with visitation rate while total travel cost has a significant negative correlation with the visitation rate. According to the local visitors, the willingness to pay per person per year is calculated as Rs. 116.41.&lt;br /&gt;&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115822905972730062?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115822905972730062/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115822905972730062' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822905972730062'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822905972730062'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/local-tourists-of-ruhuna-yala-national.html' title='LOCAL TOURISTS OF RUHUNA (YALA) NATIONAL PARK: ZONAL VISITATION, TRAVEL COST AND WILLINGNESS TO PAY'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115822880611344417</id><published>2006-09-14T03:13:00.000-07:00</published><updated>2006-09-14T03:13:26.290-07:00</updated><title type='text'>THE LEVEL OF VARIATION IN YIELD AND YIELD DETERMINING FACTORS AND THEIR RELATIONSHIP IN DIFFERENT HEVEA GENOTYPES.</title><content type='html'>&lt;div align="justify"&gt;E.S. Munasinghe &amp;amp; A. Nugawela&lt;br /&gt;Rubber Research Institute of Sri Lanka&lt;br /&gt;&lt;br /&gt;Natural rubber produced by &lt;em&gt;Hevea brasiliensis&lt;/em&gt; &lt;a href="http://muell.arg.is/"&gt;Muell. Arg. is&lt;/a&gt; an industrially important raw material for which demand continues both locally and internationally. It is produced from the latex extracted/tapped from the rubber tree.&lt;br /&gt;In this study, variation in yield and some yield determining factors, i.e. girth, depth of tapping cut, tapping height and tapping angle and their relationships were studied on three genotypes (clones) of Hevea PB 217, RRIC 117 and RRIC 102. Clones have been planted in 1988 in a commercial estate in Sri Lanka and tapping began in 1994. From each clones, an area having ca. 100 trees was selected for the study.&lt;br /&gt;Yield measured as latex volume was found to be highly significant clonal character. Among the three clones tested, the highest mean latex volume per tree per tapping was recorded in RRIC 102 whilst the lowest in PB 217.&lt;br /&gt;Further, a significant tree-to-tree variation in yield within a clone was observed in all three clones. The maximum co-efficient of variation was found in PB 217 while minimum was in RRIC 102. Yield varied through different ranges in each of the three clones and PB 217 had more low yielding trees whilst RR1C 102 and 12It1C 117 had more medium yielding trees. Yield determining factors i.e. girth, depth of tapping cut found to vary within a clone in all three clones. Further, they were significantly and positively correlated to the yield. Tapping height and tapping angle also varied within a clone and they too contributed to the yield variation within a clone.&lt;br /&gt;Out of the yield determining factors considered above, girth was the most important factor which governed the yield and it was further significantly and positively correlated to the depth of tapping cut.&lt;br /&gt;It was clearly evident that yield determining factors used in the present study play a major role in determining rubber yield. Those arc mainly governed by the rootstock of the plant, environment conditions and agro management practices. Therefore by the adaptation of the correct agro management practices and technically correct tapping, such variations within clones can be minimized and it will enhance the existing productivity levels in Sri Lanka rubber plantations.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115822880611344417?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115822880611344417/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115822880611344417' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822880611344417'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822880611344417'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/level-of-variation-in-yield-and-yield.html' title='THE LEVEL OF VARIATION IN YIELD AND YIELD DETERMINING FACTORS AND THEIR RELATIONSHIP IN DIFFERENT HEVEA GENOTYPES.'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115822845479781092</id><published>2006-09-14T03:07:00.000-07:00</published><updated>2006-09-14T03:07:35.036-07:00</updated><title type='text'>EXTRACTING VEGETATION INFORMATION FROM SATELLITE DATA FOR THE NILWALA CATCHMENT AREA, SOURTHERN SRI LANKA</title><content type='html'>&lt;div align="justify"&gt;S. Pathirana&lt;br /&gt;School of Environmental Science &amp;amp; Management,&lt;br /&gt;Southern Cross University, Lismore NSW 2450 – Australia&lt;br /&gt;&lt;br /&gt;It is evident that increasing human activities on forest resources can lead to floods, soil erosion, loss of bio diversity, and increase in atmospheric gases causing global warming. Sustainable management of forest resources requires accurate data on the current status of tile environment as well as tools to support the decision making process. Remote Sensing and Geographical Information Systems have increasingly been used as decision support tools. Particularly, recent advancements in satellite remote sensing have facilitated acquiring valuable data and information in assessing (lie current status of the environment at varying levels of detail. The purpose of this study is to assess the potential of satellite remote sensing in vegetation mapping of the Nilwala catchments area of Southern Sri Lanka. The paper presents tile preliminary work amid at extracting vegetation information from Landsat TM and ETM data. The maps produced applying image processing techniques such as image differencing, Normalised Difference Vegetation Index (NDVI), ISOCLUSS unsupervised classification and Tasseled Cap Transformation show the extent, quality and change of vegetation in the catchments area. Information derived from satellite data can further be used in rnodeling erosion potential in agricultural areas, mapping the flood risk, and land cover and land use change analysis when combine with geographical information.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115822845479781092?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115822845479781092/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115822845479781092' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822845479781092'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822845479781092'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/extracting-vegetation-information-from.html' title='EXTRACTING VEGETATION INFORMATION FROM SATELLITE DATA FOR THE NILWALA CATCHMENT AREA, SOURTHERN SRI LANKA'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115822377789441739</id><published>2006-09-14T01:49:00.000-07:00</published><updated>2006-09-14T01:49:38.020-07:00</updated><title type='text'>WATER SUPPLY PLANNING AND SIMULATION SOFTWARE PACKAGE - REALM</title><content type='html'>&lt;div align="justify"&gt;B.J.C. Perera&lt;br /&gt;School of the Built Environment, Victoria University,&lt;br /&gt;PO Box 14428 MCMC, Victoria 8001, Australia&lt;br /&gt;&lt;br /&gt;REALM (REsource ALlocation Model) is a generalised computer simulation package that models harvesting and bulk distribution of -water resources within a water supply system. A wide range of operating rules can be modelled either directly or indirectly by exploiting the attributes of node and carrier types that arc!, used to configure the system. It uses a fast network linear programming algorithm to optimise the water allocation within the network during each simulation time step, in accordance with user-defined operating rules. REALM has strong water allocation capabilities but with limited water quality features. Nevertheless, these water quality-modelling capabilities are sufficient to model the water quality issues experienced in most urban water supply and irrigation systems. REALM has been developed and enhanced in response to user requirements and feedback from the users, and therefore has developed into a comprehensive tool far water supply planning and management. It has been used to model the planning and management of sustainable water systems, and environmental flow requirements. This paper describes the main features of REALM so that the potential users will have an appreciation of its capabilities. It also describes a case study dealing with main features.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115822377789441739?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115822377789441739/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115822377789441739' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822377789441739'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822377789441739'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/water-supply-planning-and-simulation.html' title='WATER SUPPLY PLANNING AND SIMULATION SOFTWARE PACKAGE - REALM'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115822329212079790</id><published>2006-09-14T01:41:00.000-07:00</published><updated>2006-09-14T01:41:32.576-07:00</updated><title type='text'>GRANITE QUARRYING PROJECTS AND THEIR IMPACT ON THE ENVIRONMENT</title><content type='html'>&lt;div align="justify"&gt;K N J Katupotha&lt;br /&gt;Department of Geography,&lt;br /&gt;University of Sri Jayewardenepura&lt;br /&gt;&lt;br /&gt;Surface and subsurface charnockitic gneissic boulders of the Kolonna Divisional Secretariat area have been separated and detached using bores and compressor machines to produce "blocks" for export. Four granite-quarrying projects were in operation at the Lanka-Beriya Estate, Bulutota Kadamuduna, near the Circuit Bungalow at Bulutota Kadamuduna and at Udahakanda village (Pitakanda). However quarrying in the above four sites has been abandoned stopped consequent to pressure brought by the public. Only one project is active at the Aigburth Estate in Suriyakanda to date.&lt;br /&gt;This study aims at identifying the &lt;a href="http://exista.ng/"&gt;existing&lt;/a&gt; problems of the quarrying projects, examines how these quarrying projects can contribute to slope failure in the future; and makes recommendations as mitigatory measures for better understanding of uses and the management of resources. Accordingly, following conclusions can be made regarding the exploitation activities in the sites:&lt;br /&gt;(a) local relief and other geographical parameters (physical and social) have not been given and concern prior to exploitation of the resources&lt;br /&gt;(b) damaged and destroyed boulders and fragments have been dispersed and have dumped in the sites&lt;br /&gt;(c) reserv4tions made by Ordinances and Laws for natural streams (Poddana, Bulutota and Ittakanda GNDs), electrical transmission lines and cemeteries (Ittakanda GND) have been ignored during these exploration&lt;br /&gt;(d) after removal of boulders, pits burrows have not been filled properly with compacted earth&lt;br /&gt;(e) trees and vegetative species have been destroyed and growth retarded due to operations carried out (Bulutota Kadamuduna, Aigbirth Estate and Udahakanda village&lt;br /&gt;(f) vibration during drilling and dynamiting (dynamiting is not presently used) have created surface cracks in the area immediately behind the boulders&lt;br /&gt;(g) dust from drilling operations are removed by wind and create environmental and health hazards&lt;br /&gt;(h) development of gullies and surface erosion is caused by heavy rains after blocks are removed; and&lt;br /&gt;(i) closed pits as well as the open pits of the area are able to create gullies by surface erosion and can store an extensive volume of water increasing sub-surface erosion It is evident from detailed field inspections and slope analysis around the sites that illegal and unmethodical quarrying of these boulders in whatever form contributes to slope failure and exerts a negative impact on the environment. The threats to human life and property as well as the degradation of the environment has contributed to a strong opposition by the public to the operation of quarries.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115822329212079790?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115822329212079790/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115822329212079790' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822329212079790'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822329212079790'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/granite-quarrying-projects-and-their.html' title='GRANITE QUARRYING PROJECTS AND THEIR IMPACT ON THE ENVIRONMENT'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115822290486689607</id><published>2006-09-14T01:27:00.000-07:00</published><updated>2006-09-14T01:35:04.866-07:00</updated><title type='text'>ENVIRONMENTAL DEGRADATION DUE TO INLAND CORAL MINING IN AKURALA, SOUTHWESTERN COASTAL ZONE</title><content type='html'>&lt;div align="justify"&gt;&lt;a href="http://m.m.r.k.jayarathne/"&gt;M.M.R.K. Jayarathne&lt;/a&gt; &amp; S.N. Wickramarathne&lt;br /&gt;Departmert of Geography,&lt;br /&gt;University of Peradeniya&lt;br /&gt;&lt;br /&gt;The Akurala coastal stretch (approx. 87-.90 km from Colombo) provides an excellent example of environmental degradation due to human exploitation of coastal resources. Holocene corals are found 2.5 - 3.0 m below, the surface in a stretch extending about 1 km inland from the coast. The objectives of the present study were to assess the degree of environmental degradation resulting from inland coral mining in this stretch. It was based on a field survey, air photo interpretation and GIS application.&lt;br /&gt;&lt;br /&gt;Although inland coral mining in Akurala records a history of over two hundred years, this activity has intensified over the past fifty years. The remaining pits vary in size (small: 10&amp;shy; - 465 m2, medium: 465 -1365 m2 and large: 1 365-929 (1m2). Mangrove plants and mangrove associates invade these pits. The commonest are Acrosticum aureum, Bruguiera sexangula and Lumnitzera racemosa. Among the mangrove associates and non-mangrove species are, Cerbera mangas, Hibiscus tiliaceus, Pandanus sp. Premna servatifolia and several sedge species (Cyperaceae). There are also such invasive plants as Annona glabra, Salvinia molesta, and panicu.s maximum growing in and around the pits.&lt;br /&gt;&lt;br /&gt;The buried coral beds are a valuable resource providing employment in mining and associated activities to 45% of the area's population. Yet, coral mining has created many problems. The threats of deep pits to people, land subsidence and damages to houses are the main problems. Proliferation of invasive plants and mosquito breeding destroy the aesthetic value.&lt;br /&gt;&lt;br /&gt;Among the recommendations emanating from the study, the closing of abandoned pits is most relevant. Also aquaculture in large pits can be viable. Planting mangroves in some parts too can help restore Sri Lanka's dwindling mangroves.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115822290486689607?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115822290486689607/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115822290486689607' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822290486689607'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822290486689607'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/environmental-degradation-due-to.html' title='ENVIRONMENTAL DEGRADATION DUE TO INLAND CORAL MINING IN AKURALA, SOUTHWESTERN COASTAL ZONE'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115822243248853041</id><published>2006-09-14T01:04:00.000-07:00</published><updated>2006-09-14T01:27:12.496-07:00</updated><title type='text'>CONSERVATION OF HISTORICAL RESIDENTIAL BUILDINGS IN URBAN SETTINGS</title><content type='html'>&lt;div align="justify"&gt;Janakie Edirisinghe 1 &amp; Malik Ranasinghe 2&lt;br /&gt;1Department of Estate Mgt. and Valuation,&lt;br /&gt; University of Sri Jayewardenepura&lt;br /&gt;2 Faculty of Engineering, University of Moratuwa&lt;br /&gt;&lt;br /&gt;Historical areas and built heritage are important elements which contribute to create image and identity of a city. Its creativity and diversity are evidence of human progress and essential factor in development. Residential  properties constitute a considerable portion of the built heritage and it is the major land use in a city's functional structure.&lt;br /&gt;&lt;br /&gt;The characteristics such as architectural features, internal design, materials used for construction of houses enrich our knowledge and understanding of the way we used to live. Those historical structures give pleasure to people, form a valuable economic, social and educational resource. They are also legacies of our past.&lt;br /&gt;&lt;br /&gt;Many residential properties of important historical value in urban settings are confronted with a situation where they are either neglected or destroyed due to various reasons. The values inherent in such properties are rarely recognized and appreciated. The issues and difficulties in conservation and management of old residential buildings in the context of urban development are analyzed and discussed in this paper.&lt;br /&gt;&lt;br /&gt; &lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115822243248853041?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115822243248853041/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115822243248853041' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822243248853041'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822243248853041'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/conservation-of-historical-residential.html' title='CONSERVATION OF HISTORICAL RESIDENTIAL BUILDINGS IN URBAN SETTINGS'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115822101664757063</id><published>2006-09-14T00:57:00.001-07:00</published><updated>2006-09-14T01:03:36.650-07:00</updated><title type='text'>COMPARISON OF TOP HEIGHT AND DOMINANT HEIGHT WITH TREE VARIABLES AT THE EVEN AGED Pinus caribaea (MORELET) PLANTATION AT YAGIRALA</title><content type='html'>&lt;div align="justify"&gt;Kandasami Pirapaharan &amp;amp; &lt;a href="http://s.m.c.u.p.subasinghe/"&gt;S.M.C.U.P.Subasinghe&lt;/a&gt;&lt;br /&gt;Department of Forestry and Environment Science&lt;br /&gt;University of Sri Jayewardenepura&lt;br /&gt;&lt;br /&gt;Top height and dominant heights are confusedly interpret in many countries. The main aim of this study was find the similarity of above two terms and to build some models to predict them.&lt;br /&gt;&lt;br /&gt;The study was carried out in Yagirala 25 year old even aged &lt;em&gt;Pinus caribaea&lt;/em&gt; plantation. Top height and dominant heights were compared with other tree variables. Stratified random sampling without replacement was used to select the sampling unit. Circular plots of 0.05 hectare with slope correction and boundary adjustment were used to obtain the required tree measurements.&lt;br /&gt;&lt;br /&gt;Diameter at breast height, total height, lower and upper crown height were measured and basal area and crown depth were calculated. Top height and dominant height were also estimated.&lt;br /&gt;&lt;br /&gt;Results indicated that there is a significant difference between top and dominant heights. Also two separate equations to predict these two heights were developed. According to the results initially ten equations were selected. Five equations described the relationship between top and total height while the o1her five described the relationship between dominant height and total height. Finally the best two equations were selected using coefficient of variation values and the distributions of standard residuals.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115822101664757063?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115822101664757063/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115822101664757063' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822101664757063'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822101664757063'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/comparison-of-top-height-and-dominant_14.html' title='COMPARISON OF TOP HEIGHT AND DOMINANT HEIGHT WITH TREE VARIABLES AT THE EVEN AGED Pinus caribaea (MORELET) PLANTATION AT YAGIRALA'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115822098947968824</id><published>2006-09-14T00:57:00.000-07:00</published><updated>2006-09-14T01:03:09.480-07:00</updated><title type='text'>COMPARISON OF TOP HEIGHT AND DOMINANT HEIGHT WITH TREE VARIABLES AT THE EVEN AGED Pinus caribaea (MORELET) PLANTATION AT YAGIRALA</title><content type='html'>&lt;div align="justify"&gt;Kandasami Pirapaharan &amp; &lt;a href="http://s.m.c.u.p.subasinghe/"&gt;S.M.C.U.P.Subasinghe&lt;/a&gt;&lt;br /&gt;Department of Forestry and Environment Science&lt;br /&gt;University of Sri Jayewardenepura                 &lt;br /&gt;&lt;br /&gt;Top height and dominant heights are confusedly interpret in many countries. The main aim of this study was find the similarity of above two terms and to build some models to predict them.&lt;br /&gt;&lt;br /&gt;The study was carried out in Yagirala 25 year old even aged Pinus caribaea plantation. Top height and dominant heights were compared with other tree variables. Stratified random sampling without replacement was used to select the sampling unit. Circular plots of 0.05 hectare with slope correction and boundary adjustment were used to obtain the required tree measurements.&lt;br /&gt;&lt;br /&gt;Diameter at breast height, total height, lower and upper crown height were measured and basal area and crown depth were calculated. Top height and dominant height were also estimated.&lt;br /&gt;&lt;br /&gt;Results indicated that there is a significant difference between top and dominant heights. Also two separate equations to predict these two heights were developed. According to the results initially ten equations were selected. Five equations described the relationship between top and total height while the o1her five described the relationship between dominant height and total height. Finally the best two equations were selected using coefficient of variation values and the distributions of standard residuals.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115822098947968824?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115822098947968824/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115822098947968824' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822098947968824'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822098947968824'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/comparison-of-top-height-and-dominant.html' title='COMPARISON OF TOP HEIGHT AND DOMINANT HEIGHT WITH TREE VARIABLES AT THE EVEN AGED Pinus caribaea (MORELET) PLANTATION AT YAGIRALA'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115822056742744136</id><published>2006-09-14T00:54:00.000-07:00</published><updated>2006-09-14T00:56:07.430-07:00</updated><title type='text'>SURVEY OF THE PRESENT STATUS OF STREET TREE PLSNTING IN</title><content type='html'>&lt;div align="justify"&gt;S. Sornalingam1 &amp; D. &lt;a href="http://m.s.h.k.ranasinghe2/"&gt;M. S. H. K. Ranasinghe2&lt;/a&gt;&lt;br /&gt;1Ministry of Irrigation &amp;amp; Water Management&lt;br /&gt;2Department of Forestry and Environmental Science,&lt;br /&gt;University of Sri Jayewardenepura&lt;br /&gt;&lt;br /&gt;Urban Forestry embraces parks, avenue planting or street trees, boulevards, cemeteries, parking places etc. It plays an important role by providing aesthetic beauty and environmental pollution by absorbing vehicular emission. Colombo, which is the commercial capital of Sri Lanka, is plagued with high population density and high commercial activities. Urban forestry has a significant potential in improving aesthetic &amp; environmental aspects of the city.&lt;br /&gt;Objectives of this research project were to identify the existing situation of the street tree planting in the 15 sub divisions of the Colombo Municipal Council Area and to give some recommendations for improvements. 2 trunk roads were selected per division randomly and the status of trees in these roads was recorded. Measurements of crown size, height, diameter at breast height, height of the first branching, widths of roads, sidewalks, and center medians were measured and recorded. Observations done in status of maturity, pest disease attack, root pattern, foliage characteristics such as whether easily decayable or moderately decayable and small or large leaves, land use patterns such as commercial, service &amp;amp; administration, residential and recreational land use &amp; recorded.&lt;br /&gt;&lt;br /&gt;According to the results, a difference in the status of street trees in the 15 sub divisions in the Colombo Municipal Council Area was identified. The sub divisions can be ranked according to the total crown area per kilometer as follows: sub divisions 7, 14, 3, 11, I, 2, 5, 10, G, 13, 12, 15, 8, 9 &amp; 4. The sub divisions can be ranked according to the number of trees per kilometer as follows: sub divisions 7,10,14,1,13,2,5,6,12,11,3,15,8,9 &amp;amp; 4. The sub divisions can be ranked according to the number of species diversity per kilometer as follows: sub divisions 7,13,12,14,1,S,a,:;1,15,8,10,6,3,4 and 9. &lt;em&gt;Terminalia Catappa&lt;/em&gt; (Kottang), &lt;em&gt;Polyalthya longifolia&lt;/em&gt; (Willow): &lt;em&gt;Samanea Saman&lt;/em&gt; (paramara), &lt;em&gt;Delonix regia&lt;/em&gt; (Maimara), &lt;em&gt;Casia fistula&lt;/em&gt; (Ehala) &amp;amp; &lt;em&gt;Plumeriya spp&lt;/em&gt;. ( Araliya) represent 5 or more than 5 % in the sample survey. 56 tree species were identified in the study area.&lt;br /&gt;Out of 30 selected street sites, 7 were identified as sites, which need immediate planting programs and another 17 sites needs planting program. 9 street sites need immediate pruning operations as they have trees with first branching height of less than 2.00 meters, which may interrupt the traffic flow. 6 street sites were identified as sites, which need immediate removal and replacement operations as they have over-matured trees, which may become hazardous trees if necessary actions are not taken. Out of 15 sub divisions surveyed, 7 were identified as affected with pest-disease attack. Further, some recommendations are identified as to improve the existing situation of' the street tree planting in the study area and a draft action plan for 5 years was drawn. Further scientific studies such as species, which can reduce soil erosion, pollutants absorbers, etc. are needed for better management of urban trees.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115822056742744136?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115822056742744136/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115822056742744136' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822056742744136'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822056742744136'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/survey-of-present-status-of-street.html' title='SURVEY OF THE PRESENT STATUS OF STREET TREE PLSNTING IN'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115822024406570144</id><published>2006-09-14T00:46:00.000-07:00</published><updated>2006-09-14T00:50:44.066-07:00</updated><title type='text'>VARIATION OF SPECIFIC GRAVITY WITHIN Eucalyptus grandis TREES GROWING IN DIFFERENT SITE CLASSES.</title><content type='html'>&lt;div align="justify"&gt;N.D. Ruwanpathirana 1, H.S. Arnarasekara2 &amp; M.P. De Silva3&lt;br /&gt; &lt;/div&gt;&lt;div align="justify"&gt;1State Timber Corporation, Sampathpaya, Battaramulla&lt;br /&gt;2 Department of Forestry &amp; Environmental Science,&lt;br /&gt; University of Sri Jayewardenepura&lt;br /&gt;3Faculty of Science, .University of Ruhuna&lt;br /&gt;&lt;br /&gt;Wood is a very remarkable material with variability and flexibility. The variability of wood increases its utility. It may be also a major drawback to its efficient use as raw material. Therefore understanding of pattern of wood properties within the tree has become important. In addition, growth rate and its v1fect on wood properties are of practical importance to maximize wood and fiber prcoc3~nction. In this study, variations of specific gravity within the trees of 30-years old Eucalyptus grandis extracted from Pattipola, Santhipura and Piduruthalagala in Nuwara-Eliya districts were studied. Data were collected in relation to site class (growth rate) as determined by tree height. The objective of the study was to find out whether specific ; gravity is affected by growth rate of tree. Specific gravity values were collected in a systematic manner, which are essential in commercial utilization of this species. Three sites, namely Slow Growth Site (SGS), Medium Growth Site (MGS) Fast Growth Sit; (FGS) were chosen. Five trees from each site were taken for the investigation. Tree height difference between SGS (33.8 meters ) FGS (45 meters) was significantly different (P_&lt;0.05) but not between SGS and MGS (38.7 meters).&lt;br /&gt;&lt;br /&gt;Variation patterns of specific gravity in radial direction were studied using two linear sections extracted across the diameter of every sample disc, from north to south and cast to west at different height levels at breast height a !ad at 20%, 40%, 60%a and 80'% of total tree height. 3021 wood samples of 2*2*1 cm dimensions were used for specific gravity determination.&lt;br /&gt;&lt;br /&gt;In general, low specific gravity values were observed at pith in all three sites. In fast growth site, specific gravity increased from pith; thereafter it remained constant towards the bark with small fluctuation. In slow and medium growth sites, however specific gravity increased gradually towards the bark. Fast Growth site maintained the highest specific gravity values throughout piths to bark. The specific gravity of SGS and MGS increased rapidly with increasing distance from pith.&lt;br /&gt;&lt;br /&gt;In general, specific gravity increased with tree height in all sites except at 20% height level in SGS and MGS. Mean specific gravity values in SGS at breast height, 20%, 40'%, 60% and 80% height levels were 0.432, 0.431, 0 433, 0.468 and 0.475 respectively. Specific gravity values for these levels in MGS were 0.4,41, 0.435, 0.467, 0.477,0.542 and Specific gravity values were 0.479, 0.482, 0.493, 0.525, 0.553 for FGS respectively.&lt;br /&gt;&lt;br /&gt;&lt;br /&gt; &lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115822024406570144?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115822024406570144/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115822024406570144' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822024406570144'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115822024406570144'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/variation-of-specific-gravity-within.html' title='VARIATION OF SPECIFIC GRAVITY WITHIN Eucalyptus grandis TREES GROWING IN DIFFERENT SITE CLASSES.'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115821999321144852</id><published>2006-09-14T00:42:00.000-07:00</published><updated>2006-09-14T00:46:33.213-07:00</updated><title type='text'>PRESERVATIVE TREATMENT OF JAK (Artocarpus heterophyllus) SAPWOOD USING CCA &amp; BORON PRESERVATIVES</title><content type='html'>&lt;div align="justify"&gt;G. M. K. Perera 1 &amp; Hiran S Amarasekera2&lt;br /&gt;1 Central Environment Authority&lt;br /&gt;2 Department of Forestry and Environmental Science,&lt;br /&gt;University of Sri Jayewardenepura&lt;br /&gt;&lt;br /&gt;In Sri Lanka Jak timber is listed as a special class timber. Jak timber has high demand for construction and furniture. Jak heartwood is highly durable. However, sapwood is susceptible to borer attack. This study was conducted to determine the suitable and practical treatment method for Jak sapwood to improve its durability. Different aged 10 trees of Jak (Artocarpus heterophyllus) were selected for the study. Sapwood samples and heartwood control samples were extracted from each tree.&lt;br /&gt;Jak sapwood was treated by three methods: Boron (Cold) diffusion and Boron (Hot &amp; Cold) open tank method using 25% boron solution and Pressure Impregnation Full-cell process using 2.8% CCA (Copper Chrome Arsenate) solution. The treatability of different aged trees was evaluated by measuring the preservative retention and depth of penetration. Effectiveness of the treatment was evaluated by percentage weight loss in field exposure test.&lt;br /&gt;According to the results, retention in CCA pressure treated samples was higher compared with boron diffusion methods. Boron (Hot &amp;amp; Cold) open tank method gave higher retention compared with boron (cold) method. Spot test showed full depth of penetration (100%) in both boron treatments and 46% penetration in CCA pressure process.&lt;br /&gt;In field exposure test, the highest weight loss was recorded in boron (Hot &amp;amp; Cold) treated samples and second weight loss was recorded in boron (Cold) treated samples. There was no significant difference in the weight loss between two boron treatment methods. Weight loss of the CCA pressure treated samples was very small. Although full depth of penetration was not achieved with CCA pressure impregnation, it was found more effective for the preservation of Jak sapwood.&lt;br /&gt;Based on the results, it is clear that Jak sapwood can be fully treated with boron diffusion methods and effectively treated with CCA pressure impregnation method. Diffusion methods using boron solution is recommended for the interior joinery and CCA pressure impregnation is recommended to use Jak sapwood in exterior construction activities.&lt;br /&gt;However, sapwood of Jak showed other undesirable characters in terms of utilization: compared with heartwood, density of sapwood was low, and shrinkage was higher.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115821999321144852?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115821999321144852/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115821999321144852' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821999321144852'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821999321144852'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/preservative-treatment-of-jak.html' title='PRESERVATIVE TREATMENT OF JAK (Artocarpus heterophyllus) SAPWOOD USING CCA &amp; BORON PRESERVATIVES'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115821967988185812</id><published>2006-09-14T00:36:00.000-07:00</published><updated>2006-09-14T00:42:10.496-07:00</updated><title type='text'>RELATIONSHIP BETWEEN STEM BIOMASS AND VOLUME OF Pinus caribaea IN THE YAGIRALA FOREST RESERVE</title><content type='html'>&lt;div align="justify"&gt;A.M.R. Haripriya &amp;amp; &lt;a href="http://s.m.c.u.p.subasinghe/"&gt;S.M.C.U.P.Subasinghe&lt;/a&gt;&lt;br /&gt;Department of Forestry and Environmental Science,&lt;br /&gt;University of Sri Jayewardenepura&lt;br /&gt;&lt;br /&gt;The biomass is an important measurement in commercial forestry maintained to produce pulp, paper, chips, fuel wood products etc. The estimation of the biomass of the tree is not an easy task and few studies were carried out so far.&lt;br /&gt;The present study was conducted in the 25 years old &lt;em&gt;Pinus caribaea&lt;/em&gt; plantation in Yagirala Forest Reserve, which is in the low country wet zone. According to the geographical differences in the plantation, i.e., valley, slopes and ridge, stratified random sampling was carried out and two 0.05 ha circular plots were established in each stratum. Altogether 6 plots were used for the data collection.&lt;br /&gt;The diameter at breast height (dbh), total height were measured for all the trees in these plots and after dividing the tree stem into several sections, the length and end and mid diameters of each section was measured using the Spiegel relaskop.&lt;br /&gt;The volume of the stem was estimated by calculating section volumes. Smalian's and Newton 's formula were used to estimate the section volumes except for the final section at the top, which was assumed as a cone. In order to save time, one plot was measured for Newton's formula and the rest was measured for Smalian's formula. Then a relationship was build to estimate Newton's volume (Ne) using Smalian's volume (Sm) as the explanatory variable (equation 1). The R2 value was 99.9%.&lt;br /&gt;Ne=0.976*Sm (1)&lt;br /&gt;Biomass of the tree was estimated by extracting core samples at the breast height and mid height of the tree. The density of the core samples were estimated using oven dry weight and the green volume of the core samples. When tested, there was no significant difference of the density along the stem. Therefore stem biomass was estimated using the density at the breast height, and the total stem volume. Also there was no significant density differences between three sites.&lt;br /&gt;The regression analysis was used with the pooled data to find out the relationship between the stem biomass (W) and the volume (V). Using variable of stem volume and the biomass and its transformations developed the several models: The best model was selected by checking the R2 value, standard residual distribution, modelling efficiency and bias. The best relationship for the biomass and volume was the equation 2, which has R2 value of &lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115821967988185812?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115821967988185812/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115821967988185812' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821967988185812'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821967988185812'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/relationship-between-stem-biomass-and.html' title='RELATIONSHIP BETWEEN STEM BIOMASS AND VOLUME OF Pinus caribaea IN THE YAGIRALA FOREST RESERVE'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115821936144375556</id><published>2006-09-14T00:34:00.000-07:00</published><updated>2006-09-14T00:36:01.446-07:00</updated><title type='text'>PUBLIC RELATIONS (PR) IN FOREST MANAGEMENT: CONCEPTS AND STRATEGIES FOR</title><content type='html'>&lt;div align="justify"&gt;Mangala De Zoysa&lt;br /&gt;Department of Agricultural Economics,&lt;br /&gt;Faculty of Agriculture, University of Ruhuna&lt;br /&gt;&lt;br /&gt;Public relations have gained much recognition in the last three decades assuming an increasingly important &lt;a href="http://role.as/"&gt;role as&lt;/a&gt; a forest management function in most of the developed countries. However, Public Relations (PR) continues to be a less important, less understood function in forestry sector in many developing countries. The PR is considered as a serious tool for damage control and crisis management measures, which is better done under PR than under other disciplines.&lt;br /&gt;&lt;br /&gt;The various remedial measures adopted to meet basic needs of the increasing population have resulted with rapid degradation ~and depletion of forest resources in Sri Lanka. However, the Forest Authority have to take a fair share of the blame for the unsuccessful or failed forestry development activities for not adequately shouldering the responsibility of creating a required environment and facilitative conditions. The public is inadequately informed the economic problems aria' functions of forestry, and would like more information. Modern PR gives professional status to professional practice in forestry sector. The paper defines the public and the public relations and, accordingly, the environment required for PR is identified. The management objectives, functions and basic elements required for PR functions, and evaluating, results of public relations are discussed. Further, promotion of forester as PR officer and the matters needed for analysis are suggested.&lt;br /&gt;volume for all&lt;br /&gt; &lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115821936144375556?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115821936144375556/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115821936144375556' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821936144375556'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821936144375556'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/public-relations-pr-in-forest.html' title='PUBLIC RELATIONS (PR) IN FOREST MANAGEMENT: CONCEPTS AND STRATEGIES FOR'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115821924060158606</id><published>2006-09-14T00:31:00.000-07:00</published><updated>2006-09-14T00:34:00.603-07:00</updated><title type='text'>CONSTRUCTION OF A GROWTH MODEL TO PREDICT THE INDIVIDUAL STEM VOLUME OF Eucalyptus grandis HILL EX MAIDEN (TOOLUR) IN SRI LANKA</title><content type='html'>&lt;div align="justify"&gt;S.M.C.U.P. Subasinghe&lt;br /&gt;Department of Forestry &amp; Environmental Science,&lt;br /&gt;University of Sri Jayewardenepura&lt;br /&gt;&lt;br /&gt;Toolur (&lt;em&gt;Eucalyputs grandis&lt;/em&gt; Hill ex Maiden) belongs to family Myrtaceae has been planted widely in the hill country of Sri Lanka for high duality timber and fuel wood. For [lie present study a growth model was constructed to predict the total stem volume of individual toolur trees. Data were obtained using temporally sampled plots from the tree plantations in Badulla forest division and 6 plantations in Nuwara-Eliya forest division.&lt;br /&gt;Data were first partitioned according to the quality of the site. An index developed using a top height / plantation age was used for site classification and three significantly different sites could be identified. In order to construct the model, 75% of sample plots from each plantation was used and the rest was reserved for the purpose of validating the constructed model with independent data.&lt;br /&gt;&lt;br /&gt;The basic model structure was developed using the relationship between volume and form factor, basal area and total height. Form factor is difficult to measure because it varies with age, site quality, density etc. even for the same species. Therefore keeping the other two variables, it was tried to replace the form factor using other explanatory variables, which can be measured easily.          &lt;br /&gt;&lt;br /&gt;All possible combinations of the explanatory variables were tested in order to obtain the best models. The performance of the models was observed using statistical tests and standard residual distributions. For the selected models, the intercept was not significantly different from zero and number of trees per hectare and total basal area tested to represent the stand density was also not significant.&lt;br /&gt;&lt;br /&gt;After selecting the four suitable models at the first stage, the possibility of using one set of parameters instead of separate parameters sets for different site types was tested. First the parameters were estimated for the pooled data. Using the resulted models, normal residuals were calculated separately for three site types, Then the significance of the residuals was tested using analysis of variance for select the final model  with common set of parameters. A selected model contained basal area and total height of individual trees and a site quality factor as explanatory variables. It was then , compared directly with the particular observed values. After all the tests, the results indicated that the model constructed in this study proved its strength on predicting the total volume of individual stems precisely because it indicated a very low bias and a high modeling efficiency of over 0.09.&lt;br /&gt;The resultant model which can be used to predict the individual toolur stein volume for all site types is: (&lt;em&gt;Volume&lt;/em&gt;)1/2 =0.5946*(&lt;em&gt;basal area * total height&lt;/em&gt; )1/2 +0.0356 *(&lt;em&gt;total basal area /top&lt;/em&gt; height).&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115821924060158606?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115821924060158606/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115821924060158606' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821924060158606'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821924060158606'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/construction-of-growth-model-to.html' title='CONSTRUCTION OF A GROWTH MODEL TO PREDICT THE INDIVIDUAL STEM VOLUME OF Eucalyptus grandis HILL EX MAIDEN (TOOLUR) IN SRI LANKA'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115821909782218199</id><published>2006-09-14T00:29:00.000-07:00</published><updated>2006-09-14T00:31:37.826-07:00</updated><title type='text'>HABITAT UTILISATION PATTERN OF Lantana camara IN UDAWALAWE NATIONAL PARK IN SRI LANKA</title><content type='html'>&lt;div align="justify"&gt;W.N.N.U. Gunatilleke 1 &amp; &lt;a href="http://d.m.s.h.k.ranasinghe2/"&gt;D.M.S.H.K. Ranasinghe2&lt;/a&gt;&lt;br /&gt;1 Department of Wildlife Conservation&lt;br /&gt;2 Department of Forestry &amp;amp; Environmental Science,&lt;br /&gt;University of Sri Jayewardenepura&lt;br /&gt;&lt;br /&gt;&lt;em&gt;Lantana camara&lt;/em&gt; of the family Verbenaceae is native to the tropical and sub tropical regions of Central and South America. It grows in a wide range of habitats, from exposed dry hillsides to wet heavily shaded gullies. It was introduced to Sri Lanka in 1926 through the Royal Botanic Gardens and currently i? has spread across the island significantly and has become an invasive species in most of the habitats including the Udawalawe National Park. Through its invasive nature it has become a threat to fauna and flora of the Park due to habitat invasion and loss. Therefore, the main objective of this study is to assess the habitat utilization pattern of &lt;em&gt;L. camara&lt;/em&gt; in the Park.&lt;br /&gt;For this, the extent of the species in the 3 selected habitats of the Park ie. Scrub grassland, Medium height scrub and Scrub forest transitions was studied using field survey using GPS instruments. This data was mapped subsequently in order to get an overall idea of the habitat utilization of the species in the Park. Further, the relative abundance of this species in each of the 3 habitats selected was studied using 10 x 10 m quadrates replicated 3 times for better accuracy. Field observations were carried out in &lt;em&gt;L. camara&lt;/em&gt; trees on the following parameters; presence of flowers and seeds on the tree, time taken to start flowering, seed dispersal mechanism, seed germination and spreading ability. Seeds were also germinated in the green house of the University of Sri Jayewardenepura to assess the germination period and germination energy.&lt;br /&gt;&lt;br /&gt;The results showed significant variation was observed between the habitat types sampled in the extent of &lt;em&gt;L. camara&lt;/em&gt;; the figures being 75% in the Scrub grassland, 65% in Medium height scrub and 45% being in the Scrub forest transitions. When these results were mapped, it showed 20% invasion of &lt;em&gt;L. camara&lt;/em&gt; in the Park especially into the vegetation types sampled in the study. When taken t5 an overview, the main road and Veheragolla, Seenuggala, Mau ara, Thimbiriyamankada and 5`h mile post are the most densely and continuously distributed areas.&lt;br /&gt;&lt;br /&gt;The relative abundance and height of &lt;em&gt;L. camara&lt;/em&gt; was highest in the Medium height scrub grassland (92%) while the lowest was observed in the Scrub forest transitional area (87%). The species produced large number of flowers and seeds (20 - 30/cluster). The germination ability of the plant was very high (85 %). Therefore, the present study highlights the invasive nature of the plant especially in open scrub areas and the need to effectively mange the same to secure the biodiversity of the Park.&lt;br /&gt;&lt;br /&gt; &lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115821909782218199?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115821909782218199/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115821909782218199' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821909782218199'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821909782218199'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/habitat-utilisation-pattern-of-lantana.html' title='HABITAT UTILISATION PATTERN OF Lantana camara IN UDAWALAWE NATIONAL PARK IN SRI LANKA'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115821895626518121</id><published>2006-09-14T00:26:00.000-07:00</published><updated>2006-09-14T00:29:16.266-07:00</updated><title type='text'>EFFECT OF SHADING ON SURVIVAL AND GROWTH OF Mesua (CLUSIACEAE) AND Shorea (DIPTEOCARPACEAE) SEEDLINGS ACROSSTOPOGRAPHIC GRADIENT IN SINHARAJA RAIN FOR</title><content type='html'>&lt;div align="justify"&gt;E.P.S.K. Ediriweera 1, B.M.P.Singhakumara 1 &amp; P.M.S.Ashton2&lt;br /&gt;1 Department of Forestry and Environmental Science,&lt;br /&gt;University of Sri Jayewardenepura&lt;br /&gt;2 Yale University, New Haven, U.S.A.&lt;br /&gt;&lt;br /&gt;The effect of shading on survival and growth of two species of &lt;em&gt;Mesua&lt;/em&gt; (&lt;em&gt;Clusiaceae)&lt;/em&gt; and four species of &lt;em&gt;Shorea&lt;/em&gt; &lt;em&gt;(Dipteocarpaceae)&lt;/em&gt; planted seedlings were investigated at different topographic positions in Sinharaja rain forest.. All occur together as canopy dominant trees in Sinharaja rain forest. Twelve-understory sites were selected, four each on different topographic positions: valley, midslope and ridgetop. Measurements of height, number of leaves, root collar diameter and the mortality were recorded over a five-year period. Hemispherical canopy photographs were taken to calculate Indirect Site Factor (ISF), Direct Site Factor (DSF), and the Leaf Arin Index (LAI). Analysis of photographs demonstrated that LAI decreased from valley to ridge top while DSF and ISF increased from the valley to ridge top. After five years thirty-four (34 %) seedlings died in the ridge top and the lowest mortality was recorded in the midslope. Seedlings of &lt;em&gt;Mesua ferrea&lt;/em&gt; L. had the highest survival than other species in all understory conditions and the lowest survival rate recorded for &lt;em&gt;Shorea trapeaifo!ia&lt;/em&gt; (Thw.) Ashton. Results showed clear differences in survival and growth among species. These differences appeared related to availability of soil moisture and understory radiation regimes.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115821895626518121?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115821895626518121/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115821895626518121' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821895626518121'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821895626518121'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/effect-of-shading-on-survival-and.html' title='EFFECT OF SHADING ON SURVIVAL AND GROWTH OF Mesua (CLUSIACEAE) AND Shorea (DIPTEOCARPACEAE) SEEDLINGS ACROSSTOPOGRAPHIC GRADIENT IN SINHARAJA RAIN FOR'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115821871235549602</id><published>2006-09-13T23:50:00.000-07:00</published><updated>2006-09-14T00:25:12.366-07:00</updated><title type='text'>NATURAL REGENERATION IN KEKILLA FERNLANDS IN THE PERIPHERY OF SINHARAJA WORLD HERITAGE SITE</title><content type='html'>&lt;div align="justify"&gt;S.P.Kumara &amp; B.M.P.Singhakumara&lt;br /&gt;Department of Forestry and Environmental Science,&lt;br /&gt; University of Sri Jayewardenepura&lt;br /&gt;&lt;br /&gt;In tropical moist climate &lt;em&gt;Dicranopteris linearis&lt;/em&gt; (Kekilla) fernland can develop as a result of rain forest clearance followed by frequent burning. In Sri Lanka &lt;em&gt;D. linearis&lt;/em&gt; fernlands are capable of suppressing the . natural regeneration of rain forest. Sinharaja World Heritage Site is one of the least disturbed and biologically unique lowland rain forest now remaining in Sri Lanka. Some areas of the periphery of Sinharaja are covered with &lt;em&gt;D. lenearis&lt;/em&gt; fern. Natural regeneration dynamics of soil seed banks need to be studied as a possible source of regeneration for forest restoration in these fern lands.&lt;br /&gt;This study was carried out to understand the natural regeneration of soil seed bank in Kekilla fernland with reference to surface soil disturbance and topographic levels in the periphery of Sinharaja World Heritage Site.&lt;br /&gt;Three sites of Kekilla fernlands were selected for the study. Two surface soil disturbance treatments were applied to each site. The first treatment (Root Removal) was applied at the beginning of the study. The next treatment (Till) was applied to each site after six months from the first treatment. Seeds in the soil were allowed to germinate and seedlings were counted once in two weeks during the first four months. After four months the seedlings were recorded once a month. Transects were laid out in each site to understand the 1loristic composition in surrounding vegetation of' &lt;em&gt;D. lenearis&lt;/em&gt; fernlands.&lt;br /&gt;&lt;br /&gt;Seedlings of 35 taxa were identified during the period of study. The study revealed that both soil disturbance treatments can facilitate the establishment of herbs, shrubs and trees in the fern land dominated by &lt;em&gt;D. lenearis&lt;/em&gt;, Results showed that herbs, shrubs, grasses represented the greater proportions of seedling recruitment than pioneer trees. Seedlings of primary forest species were not existent.&lt;br /&gt;&lt;br /&gt;Species composition of soil seed bank in three-topographic positions was not significantly different. Numbers of species and seedling density were greatest in root removal treatment. Seedlings of primary forest species found in surrounding vegetation were not regenerating in the plots studied. Only few pioneer tree seedlings were found in the plots, representing surrounding vegetation of Kekilla fernland.&lt;br /&gt;&lt;br /&gt;&lt;br /&gt; &lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115821871235549602?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115821871235549602/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115821871235549602' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821871235549602'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821871235549602'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/natural-regeneration-in-kekilla.html' title='NATURAL REGENERATION IN KEKILLA FERNLANDS IN THE PERIPHERY OF SINHARAJA WORLD HERITAGE SITE'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115821658226959282</id><published>2006-09-13T23:47:00.000-07:00</published><updated>2006-09-13T23:49:42.270-07:00</updated><title type='text'>THE SEED BANK DYNAMICS OF TWO DIFFERENT FOREST TYPES</title><content type='html'>&lt;div align="justify"&gt;P.A. Sunil, &lt;a href="http://m.k.t.k.arnarasinghe/"&gt;M.K.T.K. Arnarasinghe&lt;/a&gt; &amp; R.Senaratne&lt;br /&gt;Department of Crop Science, Faculty of Agriculture, University of Ruhuna&lt;br /&gt;&lt;br /&gt;The floristic composition and regeneration potential of natural forests in wet zone (Wilpita) and dry zone (Hambanthota) was investigated by sampling in the top l0cm of the soil using special design samples (30cm *30cm* l0cm) along the transects and enumerating the number of seedlings emerge from the soil during the period of two months. The seedlings were transferred into poly bags once a week and allowed to grow for few months to determine the floristic composition.&lt;br /&gt;The mean number of seeds germinated per square meter in Wilpita in Hambanthota were 162 and 146 respectively. The composition of the seedlings from Wilpita and Hambanthota forests was not similar, though the population density was generally higher in the Wilpita forests. The floristic composition at the Wilpita forests was observed and &lt;em&gt;Alstonia macrophila&lt;/em&gt; (Hawarinuga), &lt;em&gt;Macaranga Peltata&lt;/em&gt; (Kande), &lt;em&gt;Trema orientalis&lt;/em&gt; (Gedumba) and &lt;em&gt;Melastoma malabathricum&lt;/em&gt; (Bovitiya) were prominent species among the tree species. Affinity analysis showed that the Al.stonia was the most prominent tree species in Wilpita forest. There was no significant difference observed in the number of seedlings per square meter among the samples collected along the transects.&lt;br /&gt;This study shows that the regeneration potential of the rain forests in the wet zone (Wilpita) is much higher than forests in the dry zone.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115821658226959282?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115821658226959282/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115821658226959282' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821658226959282'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821658226959282'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/seed-bank-dynamics-of-two-different.html' title='THE SEED BANK DYNAMICS OF TWO DIFFERENT FOREST TYPES'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115821633273953999</id><published>2006-09-13T23:36:00.000-07:00</published><updated>2006-09-13T23:45:32.743-07:00</updated><title type='text'>SAND DUNE VEGETATION SUCCESSION: CASE STUDY OF PANAMA VILLAGE IN</title><content type='html'>&lt;div align="justify"&gt;S.N. Wlckramaratne 1 &amp; H. I. Tillekaratne 2&lt;br /&gt;1 Department of Geography, University of Peradeniya&lt;br /&gt;2Department of Botany, University of Peradeniya&lt;br /&gt;&lt;br /&gt;Coastal sand dunes harbour special successional plant communities and are of immense ecological value. Henry Cowels, one of the pioneers to study ecological succession in the late 19`h century was inspired by the sand dunes of the shores of Lake Michigan.&lt;br /&gt;&lt;br /&gt;In Sri Lanka coastal sand dunes occur along the dry zone coast. The stretch extending northward from Hambantota has a well-developed dune system in Panama in the Ampara District. The objective of the present -study, was to investigate the composition, structure and zonation of vegetation in the sand dune system of Panama between Kumbukkan Oya estuary and Arugam Bay. It was carried out in April 2002 by random plot sampling.&lt;br /&gt;The dunes supporting the vegetation are more or less parallel to the shore and occur within 300m from the shoreline (berm). They rise in four successive levels up to about 8m from the berm level. The first three dunes are within 50m from the berm, while the fourth one is between 150 and 300m from the berm.&lt;br /&gt;The vegetation shows a zonation in conformity with the successive dunes. The first zone (0-7m from berm) has creeping vegetation consisting of Spini,fex littoreus etc. The second zone (7-14m) has low herbs (e.g. &lt;em&gt;Scaeovola sericea, Sesamum prostratum&lt;/em&gt;) in addition to creeping forms. These two zones together have 16 plant species. The third zone is a more stabilized terrain with 17 plant species exceeding 15cm of height (&lt;em&gt;Scaeovola, Crlnum&lt;/em&gt; sp. and &lt;em&gt;Calotropis gigantean&lt;/em&gt; etc.). The fourth zone is wider and more stabilized. It has about ten stunted tree species such as &lt;em&gt;Crateva adansoni, Strychnos potatorum&lt;/em&gt; and &lt;em&gt;Grewia carpinlfolia&lt;/em&gt;.&lt;br /&gt;&lt;br /&gt;The taller plants are swept in a southwest-northeast direction indicating the dominant wind direction.&lt;br /&gt; &lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115821633273953999?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115821633273953999/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115821633273953999' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821633273953999'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821633273953999'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/sand-dune-vegetation-succession-case.html' title='SAND DUNE VEGETATION SUCCESSION: CASE STUDY OF PANAMA VILLAGE IN'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115821575854500555</id><published>2006-09-13T23:18:00.000-07:00</published><updated>2006-09-13T23:42:27.050-07:00</updated><title type='text'>MANGROVE VEGETATION: CASE STUDY OF PANAMA LAGOON IN EASTERN SRI LANKA</title><content type='html'>&lt;div align="justify"&gt;H. I. Tillekaratne1 &amp; S.N.Wickramaratne2&lt;br /&gt;1Department of -Botany, University of Peradeniya&lt;br /&gt;2Department of Geography, University of Peradeniya&lt;br /&gt;Although most of mangroves of the western and southwestern coast of Sri Lanka have been destroyed or degraded, those in Panama have not been noticeably affected by human activities. Mangroves of Panama occur in scattered patches in estuaries and lagoons between Wila Oya estuary and Okanda.&lt;br /&gt;However, those in the Panama Lagoon of' Wila Oya estuary are more prominent. The present study was carried out to examine the distribution and composition of the Mangroves in the Wila Oya estuary. It was based on a random rapid field survey. This shallow lagoon is characterized with two islets (areas: 10 and 1 ha. approx.) and the margins of the lagoon as well as the- islets have fringing mangroves that extend into the estuary.&lt;br /&gt;There are six dominant woody obligate mangrove species in the area; &lt;em&gt;Aegiceras corniculatum&lt;/em&gt;, &lt;em&gt;Bruguiera gymnorrhiza, Ceriops tagal, Excvecaria agallocha, Lumnitzera racemosa&lt;/em&gt; and &lt;em&gt;Rhizophora mucronata&lt;/em&gt; along with three mangrove associates; &lt;em&gt;Calophyllurn inophyllum, Garcinia spicata&lt;/em&gt; and &lt;em&gt;Thespesia populnea&lt;/em&gt;. Absence of the mangrove fern &lt;em&gt;Acrostichum aureum&lt;/em&gt; and the palm &lt;em&gt;Nipa fruticans&lt;/em&gt; is a striking feature.&lt;br /&gt;Human activities in the Panama Lagoon and Wila Oya estuary are confined to fishing. Also occasional anchoring of small sea-going vessels is seen. At present the mangroves of Panama are unique as an undisturbed coastal wetland system near a populated area. Nevertheless, a recent proposal to exploit these fragile mangroves for `prawn culture' indicate the possibility of their future disruption.&lt;br /&gt;Therefore, development of non-extractive ways such as water-based Eco-tourism in Panama Lagoon can be a better alternative. Location of Panama relative to Arugam Bay, Kumana, Lahugala and 12uhuna national parks and Okanda gives this potential to this area.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115821575854500555?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115821575854500555/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115821575854500555' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821575854500555'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821575854500555'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/mangrove-vegetation-case-study-of.html' title='MANGROVE VEGETATION: CASE STUDY OF PANAMA LAGOON IN EASTERN SRI LANKA'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115821467261331447</id><published>2006-09-13T23:16:00.000-07:00</published><updated>2006-09-13T23:30:43.326-07:00</updated><title type='text'>DIVERSITY OF TERRESTRIAL FERN SPECIES IN A SUBMONTANE SECONDARY FOREST AT UPPER HANTANA</title><content type='html'>&lt;div align="justify"&gt;G.A.D. Perera1, I. Withanachchi2  &amp;amp; S.W. Ranasinghe1&lt;/div&gt;&lt;div align="justify"&gt;1Department of Botany, University of Peradeniya&lt;br /&gt;2Post Graduate Institute of Science, University of Peradeniya&lt;br /&gt;&lt;br /&gt;Although there are many fern species at the secondary forest of Upper Hantana area, their distribution and the diversity has not been studied adequately. In the Upper Hantana area many of the habitats are under threat due to human activities and therefore, most of these fern species are at a risk. Therefore, it is very important to conserve these fern species and for this purpose, it is necessary to identify all the ferns in the area and their distribution. The objectives of this study were to find out the fern diversity in the Upper Hantana area and to find out microhabitat requirements of these fern species.&lt;br /&gt;Forty-five, 2x4cm2 quadrates were established at different sites i.e, at the roadside, streamside and in the forest interior of-the study site. All the fern species in these quadrates were identified and recorded.&lt;br /&gt;&lt;br /&gt;Results revealed that the species, genera and family diversities were high at Upper Hantana area. A total of 29 species belonging to 17 genera and 13 families were recorded from the area. Out of 29 species 53% were recorded from roadside while 34% and 17% were recorded from streamside and forest interior respectively. With respect to the 13 families recorded 48% were found at roadside, 35°'® from the streamside and 17% from the forest interior.&lt;br /&gt;As there were more fern species at roadside, these may easily be disturbed with increased human activities.&lt;/div&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115821467261331447?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115821467261331447/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115821467261331447' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821467261331447'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115821467261331447'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/diversity-of-terrestrial-fern-species.html' title='DIVERSITY OF TERRESTRIAL FERN SPECIES IN A SUBMONTANE SECONDARY FOREST AT UPPER HANTANA'/><author><name>Mayuri Withanage</name><uri>http://www.blogger.com/profile/13194759032461098573</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='16' height='16' src='http://img2.blogblog.com/img/b16-rounded.gif'/></author><thr:total>0</thr:total></entry><entry><id>tag:blogger.com,1999:blog-34347796.post-115816854990862064</id><published>2006-09-13T10:24:00.000-07:00</published><updated>2006-09-13T10:29:09.920-07:00</updated><title type='text'>Abstracts of the papers presented at Forestry and Environmenet symposium 2002</title><content type='html'>Read all the abstracts of the papers presented at Forestry and Environmenet symposium, organized by Department of Forestry and Environment Science, University of Sri Jayewardenapura, Sri Lanka.&lt;br /&gt;&lt;br /&gt;This was the 8th symposium in this series of &lt;a href="http://www.environmentlanka.com/sympo"&gt;annual symposia&lt;/a&gt;. Theme of the symposium was: Sustainable Environmental Management Towards a Better Quality of Life. This was held on 13- 14 December at Coral Gardens Hotel, Hikkaduwa&lt;/span&gt;&lt;div class="blogger-post-footer"&gt;&lt;img width='1' height='1' src='https://blogger.googleusercontent.com/tracker/34347796-115816854990862064?l=forestry2002.blogspot.com' alt='' /&gt;&lt;/div&gt;</content><link rel='replies' type='application/atom+xml' href='http://forestry2002.blogspot.com/feeds/115816854990862064/comments/default' title='Post Comments'/><link rel='replies' type='text/html' href='http://www.blogger.com/comment.g?blogID=34347796&amp;postID=115816854990862064' title='0 Comments'/><link rel='edit' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115816854990862064'/><link rel='self' type='application/atom+xml' href='http://www.blogger.com/feeds/34347796/posts/default/115816854990862064'/><link rel='alternate' type='text/html' href='http://forestry2002.blogspot.com/2006/09/abstracts-of-papers-presented-at.html' title='Abstracts of the papers presented at Forestry and Environmenet symposium 2002'/><author><name>Dr. Hiran Amarasekera</name><uri>http://www.blogger.com/profile/06988028276424542318</uri><email>noreply@blogger.com</email><gd:image rel='http://schemas.google.com/g/2005#thumbnail' width='31' height='32' src='http://2.bp.blogspot.com/_spj17clkJ1E/ScJ379yWqUI/AAAAAAAAABM/yklcilYuJ9E/S220/sakya-brochure.jpg'/></author><thr:total>0</thr:total></entry></feed>
