{"id":654,"date":"2013-06-13T02:54:38","date_gmt":"2013-06-13T02:54:38","guid":{"rendered":"http:\/\/envafs.dungnq.local\/2013\/06\/13\/vietnam-journal-of-forest-science-number-2-2011\/"},"modified":"2019-09-26T10:27:41","modified_gmt":"2019-09-26T03:27:41","slug":"vietnam-journal-of-forest-science-number-2-2011","status":"publish","type":"post","link":"https:\/\/vafs.gov.vn\/en\/2013\/06\/vietnam-journal-of-forest-science-number-2-2011\/","title":{"rendered":"Vietnam Journal of Forest Science Number 2-2011"},"content":{"rendered":"<p><!-- [if gte mso 9]&gt;--><\/p>\n<p><strong><a title=\"_Toc285824725\" name=\"_Toc285824725\"><\/a>DIVERSITY of MEDICINAL PLANTS\u00a0 IN MUONG TE DISTRICT, LAI CHAU PROVINE<br \/>\n<\/strong><\/p>\n<p><strong>Hoang Thanh Son, Nguyen Hoang Nghia, Pham Quang Tuyen, Trinh Ngoc Bon<\/strong><\/p>\n<p><em>Forest<br \/>\nSciene Institute of Vietnam<\/em><\/p>\n<p><strong>Summary<\/strong><\/p>\n<p>Total number of medicinal plant species<br \/>\nfound during the surveys conducted in Muong Te district, Lai Chau province is<br \/>\n213 species of 169 genera and 83 families. Among these species, there are 206<br \/>\nspecies (96,71%) of Magnoliophyta, 6 species (2,82%) of Polypodiophyta and 1<br \/>\nspecies (0.47%) of Lycopodiophyta. The 8 richest families include 78 species<br \/>\n(36.62% of total species in the surveyed area) and 51 genera (30.2% of total<br \/>\ngenera). They are Euphorbiaceae (24 species), Verbenaceae (13), Asteraceae<br \/>\n(11), Moraceae (8), Fabaceae (6), Araceae (6), Rubiaceae (5), and Araliaceae<br \/>\n(5). Medicinal plants in Muong Te are found in main four life-forms; herb<br \/>\nplants have 58 species (27.23%), wooden plants have 57 species (26.76%), shrubs<br \/>\nhave 56 species (26.29%) and climbing plants have 42 species (19.72%). The<br \/>\nwhole plant or parts of plants of these species have been used as medicine such<br \/>\nas the whole plant: 71 species (40.85%), leaves: 33.33%, roots: 25.82%, bark:<br \/>\n10.33%, and fruits: 8.92%. Plants have also been used to treat different kinds<br \/>\nof diseases. There are 36 species (16.9%) related to treatment of digestion<br \/>\nsystem; 23 species (10.8%) to treatment of women problems; 21 species to<br \/>\ntreatment of bones. There are 5 species found in the area to be listed in Red<br \/>\nBook of Vietnam, 2007.<\/p>\n<p><strong>Keywords:<\/strong> Medicinal plant<br \/>\ndiversity, Muong Te, Lai Chau<\/p>\n<p>&nbsp;<\/p>\n<p><strong>ALLOMETRIC EQUATIONS FOR BIOMASS ESTIMATION<br \/>\nOF INDIVIDUAL TREE OF PINUS KESIYA IN HOANG SU PHI DISTRIC, HA GIANG PROVINCE<\/strong><\/p>\n<p><strong>Vu Tan Phuong<\/strong><\/p>\n<p><em>Forest<br \/>\nSciene Institute of Vietnam<\/em><\/p>\n<p><strong>SUMMARY<\/strong><\/p>\n<p>To support the implementation of forest<br \/>\ncarbon stock of Pinus kesyia plantation,<br \/>\nthe study on development of allometric equations, BEF and root shoot ratio for<br \/>\nbiomass estimation was carried out as the base for quantifying carbon stock of<br \/>\nthe plantations. The study site is Hoang Su Phi district, Ha Giang province.<br \/>\nDestructive method was used to measure fresh biomass and drying method was<br \/>\nemployed for dried mass analysis. The sample trees were selected representing<br \/>\nfor site condition, growth and age of the stand. The analysis was made based on<br \/>\n26 sample trees with age from 5 to 26 years old. The results show that biomass<br \/>\nof different organs of trees (stem, branch, leave, root, total biomass, above<br \/>\nground biomass) has a close correlation with DBH (0,9 \u2264 r &lt; 1). The BEF<br \/>\nvalue is 0,737\u00b10,155 and the R\/S value is 0,177 \u00b1 0,025.<\/p>\n<p><strong>Keyword:<\/strong> carbon, biomass, Pinus keysia,<br \/>\nHoang Su Phi<\/p>\n<p>&nbsp;<\/p>\n<p><strong>Assesment the growth of Acacia<br \/>\nSPECIES AT the demonstration model of the forest development project in Thua<br \/>\nThien Hue<br \/>\nprovince<\/strong><\/p>\n<p><strong>Hoang Vang Thang, Nguyen Toan Thang, Phan Minh Quang<\/strong><\/p>\n<p><em>Forest Sciene Institute of Vietnam<\/em><\/p>\n<p><strong>SUMMARY<\/strong><\/p>\n<p>Two years after planted, all Acacia mangium and Acacia hybrids (A. mangium x<br \/>\nA.auriculiformis, from cutting propagation and tissue culture) at the<br \/>\nsilviculture demonstration models in Phong Dien, Huong Tra and Phu Loc<br \/>\ndistricts, Thua Thien Hue province reach up to 95 percentage of the survival<br \/>\nrate. In general, their growth is relatively good as after two years, the<br \/>\naverage growth of Acacia hybrids from tissue culture is 6,6cm in diameter and<br \/>\n7,3m in height, while average growth of Acacia hybrids from cutting propagation<br \/>\nis 6,1cm in diameter, 6,6m in height and average growth of Acacia mangium is 6,0cm in diameter, 5,8m in height. After two<br \/>\nyears applied pruning, the impact of the practise is not significant, as only<br \/>\n25% individuals have different growht with the control model (no pruning) on<br \/>\ndiameter and height, but 75% are not diffrent .<\/p>\n<p><strong>Keyword:<\/strong> Acacia, growth, demonstration models, Thua Thien Hue<br \/>\nprovince.<\/p>\n<p>&nbsp;<\/p>\n<p><strong>BIOMASS STRUCTURE OF PINUS KESIYA PLANTATION IN LAM<br \/>\nDONG PROVINCE<\/strong><\/p>\n<p><strong>\u00a0<\/strong><\/p>\n<p><strong>Vu Tan Phuong, Vo Dai Hai<\/strong><\/p>\n<p><em>Forest Sciene Institute of Vietnam<\/em><\/p>\n<p><strong>SUMMARY<\/strong><\/p>\n<p>In<br \/>\nrecent years, the role of forest in carbon sequestration and mitigation of<br \/>\ngreen house gases emission has been receiving special interests of<br \/>\ninternational communities and Vietnam.<br \/>\nStudies on biomass and carbon sequestration are becoming urgent tasks for green<br \/>\nhouse gases inventory and carbon trading. This study was carried out in Lam<br \/>\nDong province where Pinus kesiya plantation areas are widely distributed. The<br \/>\nstudy focuses on biomass and biomass structure in Pinus kesiya stands that include biomass of forest trees, biomass<br \/>\nof ground vegetation and litter layer by plantation ages and site quality<br \/>\nconditions. The study results show that total biomass of plantation on site<br \/>\nclass I is about 348 tons\/ha; on site class II is 258 tons\/ha; on site class<br \/>\nIII is 171 tons\/ha; on class IV is 120 tons\/ha; and on site class V is tons\/ha.<br \/>\nBiomass structure of forest trees of the stands is estimated of 86% (range from<br \/>\n82 \u2013 94%) of total stand biomass; biomass of ground vegetation is 3,9 % (from<br \/>\n1,3 \u2013 7,7%) of total stand biomass; and biomass of litter layer is 10,5% (from<br \/>\n4,6 \u2013 16,6%) of total stand biomass.<\/p>\n<p><strong>Keyword:<\/strong><br \/>\nBiomass, Pinus kesiya, Lam Dong.<\/p>\n<p>&nbsp;<\/p>\n<p><strong>SILVICULTURAL<br \/>\nCHARACTERISTICS OF POPULATION AND REGENERATION ABILITY\u00a0 OF Cinnamomum<br \/>\nobtusifolium IN XUAN SON NATIONAL PARK, PHU THO PROVINCE<\/strong><\/p>\n<p><strong>\u00a0<\/strong><\/p>\n<p><strong>Nguyen<br \/>\nVan Tien<\/strong><\/p>\n<p><em>Forests<br \/>\nProtection Department<\/em><\/p>\n<p><strong>Nguyen<br \/>\nHuy Son<\/strong><\/p>\n<p><em>Forestry<br \/>\nScience Institute of Vietnam\u00a0\u00a0\u00a0<\/em><\/p>\n<p><strong>SUMMARY<\/strong><\/p>\n<p>Cinnamomum obtusifolium is a big and evergreen broadleaved tree species.<br \/>\nThere are 21-25 tree species occupied the dominant storey in IIb forest in Xuan Son National Park,<br \/>\nPhu Tho Province, of which<br \/>\n4 to 6 species are the most dominant, icluding: C. obtusifolium, Castanopsis phuthoensis,<br \/>\nCinnadenia paniculata,<br \/>\nSyzygium wightianum, Pometia<br \/>\npinnata, Engelhardtia<br \/>\nchrysolepis&#8230; with the IV index varies from 8.48-21.97%.<br \/>\nThe density of the forest is from<br \/>\n340-390 trees\/ha. Among these species, C. obtusifolium contributes about 60-75<br \/>\ntrees\/ha. The regenerated seedling composition of the<br \/>\nforest consists of from 21-22 species and the density is about 14,080-15,360 individuals\/ha. In<br \/>\nparticular, the seedling density of C. obtusifolium is from 1,040 &#8211; 2,640 individuals\/ha,<br \/>\nthe certain number of potential regeneration trees reaches 640-880 individuals\/ha.<br \/>\nC. obtusifolium is one of the four species with the IV(%)<br \/>\nhighest index, including: C. obtusifolium,<br \/>\nCastanopsis phuthoensis, Cinnadenia paniculata, Syzygium wightianum. The<br \/>\nnumber of regenerated seedling of C. obtusifolium is highest at the canopy cover of 0.25-0.30,<br \/>\nfollowing by the canopy cover from 0.40- 0.45, and the lowest under the canopy<br \/>\ncover \u2265 0.65. The number of potential regenerated seedlings decreases steadily<br \/>\nfrom low canopy cover to high ones (0.25-0.30; 0.40-0.45 and \u2265 0.65).<\/p>\n<p><strong>Keywords:<br \/>\n<\/strong>Cinnamomum obtusifolium,\u00a0 natural regeneration, species composition.<\/p>\n<p>&nbsp;<\/p>\n<p><strong>PARAMETERS ESTIMATING METHODS OF CHUMACHER<br \/>\nGROWTH FUNCTION<\/strong><\/p>\n<p><strong>\u00a0<\/strong><\/p>\n<p><strong>Nguyen Van Them<\/strong><\/p>\n<p><em>Nong Lam<br \/>\nUniversity<\/em><\/p>\n<p>SUMMARY<\/p>\n<p>This paper<br \/>\nintroduces the differences from the analysis results and predicts the growing<br \/>\nprocess of individual tree using Schumacher function by the influence of three<br \/>\nparameters estimating methods of Schumacher function and the selection of stop<br \/>\ncriteria or evaluating suitable level criteria of the model. To do this, the<br \/>\nauthor related the tree-trunk volume data of Pinus keysia Royle ex Gordon 60 years old with \u00a0Schumacher function, in which the parameters was<br \/>\nestimated by two methods: linear regression and non-linear regression. In each<br \/>\nmethod, the most estimating suitable function of model was selected based on 5<br \/>\ncriteria as follows: (1) Maximum determinant coefficient (R-squared), (2)<br \/>\nMinimum standard error of the estimate (SEmin), (3) Minimum mean<br \/>\nabsolute error (MAEmin), (4) Minimum mean absolute percent error<br \/>\n(MAPEmin), (5) Residual sum of squares (SSRmin). The<br \/>\nresearch results show that: (1) If using residual sum of squares (SSRmin)<br \/>\nmethod to estimate the parameters of Schumacher function, the fixed parameter m<br \/>\ngive more precise results than the fixed parameter c. (2) The parameters of<br \/>\nSchumacher function estimated by non-linear correlation regression are attained<br \/>\nhigher degree of confident than Residual Sum of Squares (SSRmin)<br \/>\nmethod. (3) If selecting parameters estimating of Schumacher function method<br \/>\nand different stop criteria, the most estimating suitable function is also<br \/>\ndistinct.<\/p>\n<p><strong>Keywords:<\/strong> Method of minimum standard error, method of trial and<br \/>\nerror, parameter estimation, Schumacher function, stop criteria.<\/p>\n","protected":false},"excerpt":{"rendered":"<p><!--[if gte mso 9]&gt;--><\/p>\n<p>Normal<br \/>\n0<\/p>\n<p>false<br \/>\nfalse<br \/>\nfalse<\/p>\n<p>MicrosoftInternetExplorer4<\/p>\n<p><span>Total number of medicinal plant species found<br \/>\nduring the surveys conducted in Muong Te district, Lai Chau province is 213<br \/>\nspecies of 169 genera and 83 families. Among these species, there are 206<br \/>\nspecies (96,71%) of Magnoliophyta, 6 species (2,82%) of Polypodiophyta and 1<br \/>\nspecies (0.47%) of Lycopodiophyta.<\/span><!--[if gte mso 9]&gt;--><\/p>\n<p><!--[if gte mso 10]&gt;--><\/p>\n<p>\/* Style Definitions *\/<br \/>\ntable.MsoNormalTable<br \/>\n{mso-style-name:&#8221;Table Normal&#8221;;<br \/>\nmso-tstyle-rowband-size:0;<br \/>\nmso-tstyle-colband-size:0;<br \/>\nmso-style-noshow:yes;<br \/>\nmso-style-parent:&#8221;&#8221;;<br \/>\nmso-padding-alt:0in 5.4pt 0in 5.4pt;<br \/>\nmso-para-margin:0in;<br \/>\nmso-para-margin-bottom:.0001pt;<br \/>\nmso-pagination:widow-orphan;<br \/>\nfont-size:10.0pt;<br \/>\nfont-family:&#8221;Times New Roman&#8221;;<br \/>\nmso-ansi-language:#0400;<br \/>\nmso-fareast-language:#0400;<br \/>\nmso-bidi-language:#0400;}<\/p>\n","protected":false},"author":2,"featured_media":0,"comment_status":"open","ping_status":"open","sticky":false,"template":"","format":"standard","meta":[],"categories":[26],"tags":[],"_links":{"self":[{"href":"https:\/\/vafs.gov.vn\/en\/wp-json\/wp\/v2\/posts\/654"}],"collection":[{"href":"https:\/\/vafs.gov.vn\/en\/wp-json\/wp\/v2\/posts"}],"about":[{"href":"https:\/\/vafs.gov.vn\/en\/wp-json\/wp\/v2\/types\/post"}],"author":[{"embeddable":true,"href":"https:\/\/vafs.gov.vn\/en\/wp-json\/wp\/v2\/users\/2"}],"replies":[{"embeddable":true,"href":"https:\/\/vafs.gov.vn\/en\/wp-json\/wp\/v2\/comments?post=654"}],"version-history":[{"count":2,"href":"https:\/\/vafs.gov.vn\/en\/wp-json\/wp\/v2\/posts\/654\/revisions"}],"predecessor-version":[{"id":1678,"href":"https:\/\/vafs.gov.vn\/en\/wp-json\/wp\/v2\/posts\/654\/revisions\/1678"}],"wp:attachment":[{"href":"https:\/\/vafs.gov.vn\/en\/wp-json\/wp\/v2\/media?parent=654"}],"wp:term":[{"taxonomy":"category","embeddable":true,"href":"https:\/\/vafs.gov.vn\/en\/wp-json\/wp\/v2\/categories?post=654"},{"taxonomy":"post_tag","embeddable":true,"href":"https:\/\/vafs.gov.vn\/en\/wp-json\/wp\/v2\/tags?post=654"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}