Báo cáo nghiên cứu khoa học " ACACIA PLANTATIONS FOR SAWLOG PRODUCTION: SOME SIVILCULTURAL MEASURES AND RECOMMENDED SUITABLE AND PROFITABLE ACACIA SPECIES " pdf

Collaboration for Agriculture and Rural Development (CARD) Program 186 ACACIA PLANTATIONS FOR SAWLOG PRODUCTION: SOME SIVILCULTURAL MEASURES AND RECOMMENDED SUITABLE AND PROFITABLE ACACIA SPECIES Project title: Sustainable and profitable development of acacia plantations for sawlog production in Vietnam Project c ode : C ARD 032/05 VIE Authors : Phi Hong Hai 1 *, Chris Harwood 2 , Chris Beadle 2 , Sadanandan Nambiar 2 , Khongsak Pinyopusarerk 2 , Vu Dinh Huong 3 , Dang Thinh Trieu 4 , Pham Xuan Dinh 5 , Trieu Thai Hung 5 Project Implementing organisations : 1 Research Centre for Forest Tr ee Improvement - FSIV 2 CSIRO – Sustainable Ecosystems , Private Bag 12, Hobart 7001, Australia 3 Sub - Institute of Forestry Research in the South - FSIV 4 Silvicultural Technical Division - FSIV 5 Center for Forestry Science and production in Northern Centr al regions - FSIV * Responsible author (phi.hong.hai@fsiv.org.vn) SUMMARY Studies on thinning response to diameter growth, pruning response to log defects and response to phosphorus (P) of acacia hybrid growth in Quang Binh and Quang Tri showed that: (1) thinning method increased diameter growth of acacia hybrids; (2) pruning decreased log defects of acacia hybrids; (3) fertilisation of 10 g of elemental phosphorus (as 143 g superphosphate/tree) at planting time was sufficient for increasing of height grow of acacia hybrids at early stage in Quang Tri. In sawn timber plantations, Acacia mangium, A. auriculiformis, A. crassicarpa and Acacia hybrids (A. mangium x A. auriculiformis) were proved to be suitable species. A. crassicrapa was a promising species and performed well in inland sands in the central Vietnam. A. mangium was a suitable species in lowland in the northern Vietnam. While, A. auriculiformis was preferred planting in the southern Vietnam. Acacia hybrids could be planted in many sites from the No rth to the South. National clones, and technological advanced clones that approved by Ministry of Agriculture and Rural Development were suggested for using in commercial plantations of A. auriculiformis and acacia hybrids. For A. mangium and A. crassicarp a, seed sources from seed production areas and seed orchards were recommended to use. 1. Introduction Needs on timber for processing industry in Vietnam in 2010 is expected to be 9.35 million m3 (MARD, 1999). But now the natural forests are limited for e xploitation, so the annual timber volume from this kind of timber sources will only provide less than 300,000 m3 per year (MARD, 1999). Timber from plantation forest and imports is expected as the compesating source for this deficit. To meet the demand of industrial wood and to increase forest coverage to 43%, the reforestation program has planned to plant 5 million hectares of forest by 2010. Among them, more than 2 million hectares are production forests, this source can provide industrial wood. Increasin g forest productivity through improved seeds and silvicultural techniques will play a crucial role to meet the demand for CARD 032/05 – Acacia planation for sawlog production 187 timber and and to reduce the volume of imported wood. Acacia species have been imported into Vietnam since middle of 20th Century, mai nly from Papua New Guinea (PNG) and Queensland, Australia (Nguyen Hoang Nghia, 2003). In Vietnam, in 2005, the total area of acacia plantation reached 400,000 hectares, including 200,000 hectares of acacia hybrid (Ha Huy Thinh, 2005). Productivity and sust ainability of plantation of Acacia species are crucial to improving the country's economy, the development of rural areas, and the creation of pulp and sawlog. The CARD project 032/05 VIE titled “Sustainable and profitable development of acacia plantatio ns for sawlog production in Vietnam" was implemented from 2006 - 2009 by a research collaboration between the Forestry Science Institute of Vietnam and the CSIRO, funded by the Collaboration for Agriculture and Rural Development (CARD) Program. The project a pplied a diversified approach, combining research to improve breeds, site and forest management, and economic evaluation. Assessment of improved varieties for Acacia has been made to identify the acacia species suitable for plantion for sawlog production, and other propagation techniques suitable for these varieties. Besides, silvicultural techniques for reforestation and forest management have also been evaluated by this project. In addition, two trials evaluating appropriate silvicultural techniques have been built at the Central region. The first is thinning trials to assess the impact of thinning technique on diameter growth, thus helping increase the diameter enough for sawlog requirements. The second is sustainable silvicultural trials to test the long - term effects of different site management techniques on sustainability of forest productivity over several forest rotations. This paper summarises some key results from thinning and pruning trials and testing sustainable silviculture. Also, the evaluation of improved varieties for Acacia and silvicultural techniques for acacia plantation, as well as suitable Acacia species for sawlog production are also discussed and recommended. 2. Research materials and methods 2.1 Thinning and pruning trial A mixed pl antation forest of hybrid acacia clones of 2.5 years old in Dong Hoi - Quang Binh has been selected for thinning trial. Plantation model was built in December 2003, with a mixture of the hybrid Acacia clones BV10, BV16 and BV32. The trees in this model are remarkably of good growth and good form. The plantation is well stocked (1000 trees/ha), healthy, average height of trees reached 8 meters, and crown lift is minimal. With this growth rate, it is predicted that forest productivity is 20m3/ha/year for a pu lp production rotation. For all these reasons, this plantation already meets the criteria that define an ideal site for managing an Acacia stand for solid wood. Thinning response trial was established in June 2006. Four thinning treatments, including the control (unthinning) has been used in the study (Table 1). The basic design of the trial is randomized complete block, with four replications. All the trees in the experimental treatments were pruned to 2.3 m from the root. Pruning is carried out carefully so that the stems are cut close to the original branch and not harmful to the original branch. Lift prunning in the Dong Hoi thinning trial P . H . H ả i, C . Harwood, C . Beadle, S . Nambiar , V . Đ . Hư ở ng, Đ . T . Tri ề u , P . X . Đ ỉ nh, T . T . Hưng 188 Table 1 . Thinning treatments and plot sizes at Dong Ha Thinning Trial Treatments (Stems/ha) Gross (Trees /plot) Net (Trees /plot) 1000 (unthinned, control ) 63 35 600 38 21 450 28 16 300 19 11 Plot size (ha) 0.063 0.035 Dimensions (m × m) 28 × 22.5 20 × 17.5 2.2 Sustainable s ilviculture demonstration trial A site for the silvicultural trial was chosen at Dong Ha - Quang Tri, manage d by the Science Center and North Central production - Forestry Science Institute of Vietnam, to establish sustainable silvicultural trials for long - term track . This site was planted with hybrid Acacia, with the yield of 19 m3/ha/year at the 9th year. Aft er extraction, the area was fenced off to avoid the effects of animal grazing. Leaves and twigs after the first pruning is kept on the site. Soil analysis results before planting showed that the soil at this site is degraded, with low total nitrogen, phosp horus and pH. Six hybrid acacia clones (BV10, BV16, BV32, BV71, BV73 and BV75), being the national seed and technical advance, have been used to establish the sustainable silvicultural trials. The experiment was designed in randomized complete block (5 exp erimental treatments and 4 replicates). The experimental plot size is 21.5 x 20 m (6 rows x 10 trees/row). Experimental plots are separate from one another by three rows of trees in both dimensions. The experimental treatments are as shown in Table 2 to e xamine the impact of the increase in the amount of phosphate fertilizer to the increase in stem diameter, and the effectiveness of different weeding methods (method of using herbicides Roundup and manual weeding two times per year). The amount of phosphate fertilizer for each plant was determined from analysis of soil and leaf nutrient testing before establishment of the siviculture experiment . 2.3 Record keeping and statistical analysis Records on both thinning trial and sustainable silviculture experime nt are kept and assessed every six month beginning from thining activity and plantation. Diameter at breast height (Dbh) and height (Ht) of all trees in each experimental plots were collected. The statistical analysis was processed on the average value plo ts and using mathematical fixed - effects model, where the replicate blocks and the experimental treatments are considered constant. Measuring stem taper in the Dong Hoi thinning trial CARD 032/05 – Acacia planation for sawlog production 189 Table 2. Experimental treatments applied for siviculture trial in Dong Ha Treatment ID Nutrition treatment Vegetation m anagement T1 Control – no fertilizer Pre - planting herbicide spray and two sprays per year to give complete weed control, with a rate of 4l ha - 1 Roundup herbicide per application T2 P 1 10 g elemental P applied as superphosphate T3 P 2 20 g elemental P applied as superphosphate T4 P 3 (=P 2 + 10 g K per tree applied as potassium sulphate) T5 Control – no fertilizer No herbicide application. Two hand weeding per year as per standard practice at Dong ha Station 3. Research results and discussions 3. 1 Impact of thinning on individual tree diameter Results of demonstration pruning trial in Dong Hoi, Quang Binh have confirmed that pruning can improve growth in diameter of the Acacia hybrid in the trial. After 2 years of thinning, the trees in the tria l plot reached an average diameter at breast height of over 16cm, while the trees in control plots (no thinning) has the diameter of 14.5 cm (Table 3). The individual tree diameter and wood volume in the treatment plots of thinning down to 300 stems/ha and 450 stems/ha are larger than that in the plot of 600 stems/ha, but the phenomenon of tree top fracture and early separation of stems is quite common. Therefore, thinning down to the density of 300 stems/ha and 450 stems/ ha is not suitable for sawlog plant ation . Table 2. Individual tree growth and stand basal area 24 months after thinning treatments imposed, i.e. stand age 4.5 years, in the trial at Dong Hoi, Quang Binh Thinning treatment (stems/ha) Tree height (m) Diameter at breast height (cm) Basal a rea (m 2 /ha) % wood volume 300 16.8 17.1 7.4 28 450 17.2 16.3 9.6 23 600 17.3 15.9 11.9 19 1000 17.2 14.5 14.1 7 Statistical error none P<0.001 P<0.001 P<0.001 Basal area in the 600 stems/ha treatment (11.9 m2/ha) is not much lower than that of the unthinned control plot 1000 stems/ha (14.1 m2/ha) (Table 3), i.e. the total wood volume in the 600 stems/ha treatment is little lower than that in the unthinned control plot. The calculations based on full field measurement shows that the proportion of tim ber can be used for sawlog (Mean diameter at breast height ≥ 15cm) in the 600 stems/ha treatment is 19%, while it is only 7% in unthinned control plots. Thus, the thinning treatments have created a proportion of wood with suitable diameter for sawlog much higher than where the thinning is not conducted. Prices of sawlog are usually double the normal prices of pulp wood, so the value wood sale from the thinned plots may be equivalent to the unthinned plots, even after over four years of plantation. If the tr ee that have been pruned can be sold as pulp wood, the total value of the 600 stems/ha plot will be higher than that of the control plots, and the profitability could be even higher when exploiting at the age of 6 - 7 years old. P.H. H ả i, C. Harwood, C. Beadle, S. Nambiar, V. Đ. Hư ở ng, Đ. T. Tri ề u, P.X. Đ ỉ nh, T. T. Hưng& P.Khongsak 190 Most of Acacia forests in Vie tnam were planted with initial density from 1000 to 1600 stems /ha (i . e. planting distances 4 x 2m, 3 x 3m, 3 x 2.5 m and 3 x 2 m) (Nguyen Thi Lieu, 2004; Pham The Dung, et.al, 2005; Vu Dinh Huong et. al, 2006; Nguyen Huy Son et. al, 2006; Nguyen Duc Minh e t. al, 2004). The thicker density , the stronger competition between the trees in the forest. Therefore, early pruning is very important to promote growth in diameter of the trees in the forest . On the well - established forest site , if the good seed s are pl anted with appropriate silvicultural management, including weeding and fertilizing, the by - product from pruning at the age of 2.5 to 3 years old can be sold as pulp wood, and the remaining trees can provide sawlog after a short - rotation of 5 - 6 years. 3. 2 Impact of thinning on tree def ect A sawing study was conducted on logs to study the effects of pruning on tree defect. 15 thinned trees from thinning treatment plots and 15 unthinned trees from the surrounding plantation (at the same age) were cut down. The two sets of trees were matched for size and covered the range of log diameter large enough for sawing (dbh over bark range from 20 cm upwards. Butt logs of 2 m in length were sawn on a bandsaw to produce from 4 to 6 boards per log, of about 30 mm in th ickness. Defects (mostly associated with branches and associated dead and discoloured wood) were marked on each board. All boards were photographed. The numbers of defects in the outer wood, laid down after pruning, and the inner wood laid down before pru ning were scored (Table 4). As expected, the average number of defects on the inner part of the game is similar between the trees is not pruning and pruning trees (4.9 and 5.0, respectively). Because the inner timber boards were formed before pruning is d one. In contrast, the planks are sawn from the tree pruning is 0.5 defects / Snowboarding at the outer boards, while boards from tree pruning is 1.2 defects / boards. Such pruning trees have fewer defects than. Handling changes to test the effects of pruni ng to defects in the outer wood planks showed clear differences (P <0.001). Boards from unpruned tree No. 3 Boards from pruned tree No. 5 Inner - wood defects in boards from pruned tree no. 11 Table 4. Number of defects per b oard in the outer and inner wood, for pruned and unpruned logs Parameter Unpruned logs Pruned logs Significance of treatment effect Diameter at breast height (cm) 21.3 19.5 not significant Knotty core wood 5.0 4.9 not significant Number of defect in the outer wood 1.2 0.5 P<0.001 The results of this study can draw two conclusions as follows: (1) First pruning to be conducted at the age of 2.5 years, when the diameter at breast height reaches 9.5 cm to avoid defect in the outer wood. At the age of 3.5 years, pruning to be conducted for second time. The unpruned trees have higher defect rates in the outer wood, created by branches CARD 032/05 – Acacia planation for sawlog production 191 causing death knotty core on the surface of sawn boards. (2) First pruning should be done earlier, when the lower branches of a tree are alive. Such pruning associated with pruning dead branches will avoid the small defects on the sawn boards. However, the good combination between early pruning to remove the defects and the risk of limited growth rate due to pruning activity sho uld be noted. If the tree diameter at breast height is 7 cm and its height is 7 meters, it is needed to prune to a height of just 2.4 meters above the ground , meaning that pruning reduces one third of tree canopy (assuming that there is no phenomenon self - trimmed canopy). The experiments are being conducted in the framework of ACIAR project FST 2006/87 and will provide a more complete pruning appropriate time. 3.3 Impact of phosphate fertilizer on growth of the tree Sustainable silvicultural trials in the Dong Ha experimental station in Quang Tri have been successfully conducted, with survival rate of over 80% in all plots at 24 months old. Growth of hybrid acacia in all 3 experimental treatments with phosphate fertilizer application is significantly faster than the growth in two control treatments for the control (Table 5). Silvicultural sustainability trial in Dong Ha, 10 months after planting, showing growth difference between unfertilized (left) and fertilized (right) plot Clear impact of phosphate to the growth of hybrid acacia in the age of 2 years has been demonstrated. The average height of hybrid acacia in the second rotation is approximately 7 m at 2 years old and is considered quite promising in the treatment of supporting phosphate fertilizer at Dong Ha, Quang Tri. The difference between the control treatment and phosphate fertilizer application is clear and the differences at 1% (P <0.001). Supporting 10 g of phosphate elements (of the superphosphate) may be enough to impact positively on growth in height in the early stages, on the poor soil and actually more sustainable than the previous rotation. Fertilizer application amount is equivalent to 143 g of superphosphate per tree or 200 kg of superphosphate / ha. Explaination of the positive effect of phosphate to the growth of hybrid acacia is probably because Acacia species are capable of nitrogen fixation and nitrogen fixation process have a positive reaction from elemental phosphorus fertilizer (Vance et al., 2002). Then phosphate fertilizer als o improves nitrogen for Acacia hybrid and help plants grow better. Moreover, Vu Dinh Huong et. al, 2004 concluded that setting up site management (soils and the fall) is significance between business rotation to ensure sustainability of A. auriculiformis p lanted forest. Leaves and twigs from the first lumber is kept on site. Impact on the land is minimised. Leaves and twigs will create a thin layer of topsoil protection. This m anagement measures is contrary to the traditional methods which are being applied (vegetation is burned and fully plowed). Traditiona m anagement measures would lose the organic matter s , nutrients and increase soil erosion, thereby reducing forest productivity and water pollution (Nambiar, 1999). P.H. H ả i, C. Harwood, C. Beadle, S. Nambiar, V. Đ. Hư ở ng, Đ. T. Tri ề u, P.X. Đ ỉ nh, T. T. Hưng& P.Khongsak 192 Table 5. Survival rate, Diameter at b reast height (Dbh) and Height (Ht) of Acacia hybrid in sustainable sivilcuture experiment in Dong Ha after 2 years of age Treatments Ht (m) Dbh (cm) Survival (%) Control – no fertilizer 6.16 7.47 80.0 P 1 10 g elemental P applied as superphosphate 6.98 8. 57 80.4 P 2 20 g elemental P applied as superphosphate 6.95 8.53 76.3 P 3 (=P 2 + 10 g K per tree applied as potassium sulphate) 6.89 8.70 82.1 Control – no fertilizer 6.41 7.88 80.0 Statistical significance P<0.001 P<0.001 none Standard error 0.15 0.23 3.4 Recommendation of suitable Acacia species suitable for sawlog production In Vietnam, Acacia mangium , Acacia crassicarpa and Acacia auriculiformis show best grows in testing of tropical Acacia species (Le Dinh Kha, 2003). A. crassicarpa is a promi sing variety for sawlog production but it has not been proven yet . A. auriculiformis grows too slowly to be considered for profitable sawlog - producing plantations in northern Vietnam, and acacia hybrid and A. mangium are therefore preferred for sawlog prod uction in the lowlands of northern Vietnam. A. mangium is not favoured by production enterprises in the south of Vietnam, who consider it to have inferior wood quality and susceptible to wind damage. They prefer to plant A. auriculiformis and acacia hybr id. There may be differences in wood quality of A. mangium grown in northern and southern Vietnam, but this has not yet been studied . So far, the Ministry of Agriculture and Rural Development (MARD) has approved three following provenances of acacia as Tec hnological Advanced Germplasms for mass planting in suitable ecological zones:  Acacia auriculiformis : Coen River (Qld), Morehead River (Qld) and Mibini (PNG);  Acacia crassicarpa : Mata province (PNG), Deri - Deri (PNG) and Dimisisi (PNG);  Acacia mangium : Iron Range (Qld), Cardwell (Qld) and Pongaki (PNG ). Results from other tropical countries support the superior ranking of most of these provenances, with the exception of the Cardwell provenance of A. mangium . Provenance and progeny trials of A. mangium in many countries including Australia, China, Indon esia and Malaysia (Harwood and Williams 1992), and the Philippines (Arnold and Cuevas 2003) have confirmed that Cardwell is not a fast - growing provenance of this species, when compared with most provenances from Papua New Guinea , and provenances from the F ar North Queensland region (Claudie River/Iron Range, Olive River and Pascoe River). We recommend that Cardwell should no longer be classed as a superior provenance of A. mangium . It is also noted that there are other provenances of A. auriculiformis , A. c rassicarpa and A. mangium not tested in provenance trials in Vietnam which have performed equally well as those identified by MARD. Some of these provenances are represented in the seedlings seed orchards and seed production areas subsequently established by Forestry Science Institute of Vietnam ( FSIV) . To date, the Ministry of Agriculture and Rural Development has recognized 10 seedlings seed orchards as national nurseries. List of nurseries has been posted on the website of the General Department of Fore stry. These nurseries have been providing high - quality seeds for production and research in the future. 3.4.1 Acacia auriculiformis clones Acacia auriculiformis is the tropical Acacia species that is best suited for sawlog production, because this species has a high density (0.58 g/cm 3 ), the appropriate mechanical properties (ratio of radial and tangential shrinkage - T / R is 1.8; MoE is 19.8 GPa), beautiful colors and very high percentage of heartwood (Pinyopusarerk, 1990, charges the Red Sea, 2009). So o ver the years, many authors focused selective superior clones for Acacia auriculiformis . To date, 20 clones of Acacia auriculiformis have been CARD 032/05 – Acacia planation for sawlog production 193 approved by MARD as National Germplasms and Technological - Advanced Germplasms. These clones have fast growth and good quality stems. For example, the clones BVlt25, BVlt81, BVlt 83, and BVlt 85, selected from Coen River provenance planted in Ha Noi that have achieved average productivity (MAI) from 10.5 to 13.1 m 3 /ha/year in Ha Tay and Quang Tri (Le Dinh Kha, 2006). However, 11 other superior clones were selected from Acacia auriculiformis nurseries in Binh Phuoc (as Clt7, Clt18, Clt19, Clt26, Clt43, Clt57, Clt64, Clt98, Clt133, Clt1F, and Clt171) have higher productivity (MAI : 15 - 30m 3 /ha/year in Quang Binh and Bin h Duong) (Fees Red Sea, 2009a). In addition, the AA1, AA9, and AA15 have both good disease resistance and high growth, the productivity is from 25 - 33.6 m 3 /ha/year in Dong Nai and Binh Phuoc (Nguyen Hoang Nghia, 2007). Clone trial of A. auriculiformis clo nes at Bau Bang, age 4.5 years after planting In addition to increasing productivity of Acacia auriculiformis forest , improvement of the shrinkage of Acacia auriculiformis wood has been studied and contributed to increase usable proportion of wood for proc essing (Phi Hong Hai, 2009). Some clones like Clt7, Clt12, Clt18 and Clt25 have both fast growth and low degree of shrinkage, therefore, these clones are recommended for use in sawlogs plantation (Phi Hong Hai, 2009). However, genetic interactions - the si tuation of growth and stem quality is meaningful for plantation of Acacia auriculiformis clones in Vietnam (Phi Hong Hai, 2009). This means that when using the 20 above clones of Acacia auriculiformis it is necessary to pay special attention to ecological zones suitable for each clone. 3.4.2 Acacia hybrid clones Currently, the clones of hybrid acacia ( A. Mangium x A. auriculiformis ) have been widely grown in Vietnam. Hybrid acacia wood can be used for sawlog, because they have an average wood density (0.45 g/cm 3 ), and bending properties is 90 - 103 kg/m2. The best clone of acacia hybrids shows superiority in growth than its two parent species in all trials in the lowlands in Northern, Central and South Vietnam (Le Dinh Kha, 2001). In most suitable sites in t he southern and central regions, the acacia hybrid clones can achieve productivity of 35 - 40 m3/ha/year after the rotation of 5 - 7 years (Le Dinh Kha, 2001). Even on the infertile and thin topsoils sites in Ba Vi - Ha Noi, the productivity of Acacia hybrid c an achieve 15 m 3 /ha/year, while Acacia mangium reaches only 9 m 3 /ha/year (Doan Ngoc Dao, 2003). Acacia hybrid clones have very high uniformity of growth. Seventeen clones of hybrid acacia (BV10, BV16, BV29, BV32, BV33, BV71, BV73, BV75, M8, MA1, AM3, AM2, AH1, AH7, TB1, TB7 and TB11) has been approved for mass production. New clones of hybrid acacia also continue to be selected to provide extra diversity to seed collection and to limit pests and diseases for planted forests. Many clones of the Acacia hybrid will be recognized in the future. 3.4.3 Propagation for suitables Acacia species Selection and use of outstanding individual genotypes in clonal plantations enables exploitation of both additive and non - additive genetic variation and thus maximises genet ic gain in the production plantations (Eldridge et al. 1993). This makes clonal forestry the most attractive propagation option where it is feasible. However, clonal forestry is not considered feasible for A. crassicarpa and A. mangium . Although a majori ty of individuals of A. crassicarpa and A. mangium a can be clonally propagated from basal coppice, and P.H. H ả i, C. Harwood, C. Beadle, S. Nambiar, V. Đ. Hư ở ng, Đ. T. Tri ề u, P.X. Đ ỉ nh, T. T. Hưng& P.Khongsak 194 hedge plants can be established, hedge plant maturation appears to be more rapid than for A. auriculiformis and acacia hybrid. Experience from Indonesia shows that poor rooting vigour of cuttings and slow growth of cuttings in the field is typically found in these species (Yang et. Al, 2006). Thus, by planting high quality seeds (from nurseries and seed production) is recommended for Acacia mangium and A. crassicarpa . Family Clonal Forestry can also be an option for plantation of these two Acacia species. A. auriculiformis and Acacia hybrid can be propagated easily from basal coppice and can be preserved for long - term rejuvenation in the tissue culture room. Then, the plant tissue is used as hedge plant for mass propagation for production. The steps of propagation of Acacia hybrid cuttings were described in detail (Le Dinh Kha, 2001) and can be a pplied to A. auriculiformis . But in almost remote and isolated areas, where vegetative propagation system has not really been developed, seeds from seedling seed orchards of Acacia auriculiformis should be used. Seed collected from acacia hybrid trees mus t never be used because the performance of the resulting advanced generation interspecific hybrids has been shown to be very variable from tree to tree and much poorer than that of the selected F 1 hybrid clones (Le Dinh Kha, 2001). 4. Conclusions and reco mmendations Appropriate density in the common acacia plantations is 1000 - 1600 stems / ha. Thinning increases in the diameter of the tree. Thinning to 600 stems / ha in Acacia hybrid plantation in Quang Binh is most appropriate. Pruning also remarkably re duces defects in the wood. Therefore, thinning and pruning are important silvicultural measures for sawlog plantation to make sufficiently large diameter and defect - free wood. Elemental phosphate fertilizer application of 10g / tree (equivalent to 143 g s uperphosphate per tree) is sufficient to create differences in height growth of hybrid acacia in the first stage in Quang Tri and actually ensure sustainability throughout the rotation. A. Mangium, A. Auriculiformis, A. Crassicarpa and Acacia hybrid are th e Acacia species suitable for sawlog plantation. A. Crassicarpa is promising species, particularly on the problem land areas such as sandy field in the central region. Acacia mangium and Acacia hybrid are suitable with sawlog plantations in the lowlands in the north. While, A. Auriculiformis and Acacia hybrid are most favorite species in the South. The seeds supplied for mass production are national germplasms or technological advanced germplasms for A. Auriculiformis and Acacia hybrid, and the seeds from s eed orchards and seed production for A. Mangium and A. Crassicarpa . Reference 1. Arnold, R. J.; Cuevas, E. (2003). Genetic variation in early growth, stem straightness and survival in Acacia crassicarpa , A. mangium and Eucalyptus urophylla in Bukidnon provinc e, Philippines. Journal of Tropical Forest Science 15 (2): 332 - 351 2. Đoàn Ng ọ c Dao (2003). Ti ế p t ụ c so sánh sinh trư ở ng và kh ả năng c ả i t ạ o đ ấ t c ủ a Keo lai v ớ i hai loài b ố m ẹ sau 5 tu ổ i. Lu ậ n văn th ạ c s ĩ. Trư ờ ng đ ạ i h ọ c lâm nghi ệ p. 69 trang 3. Hà Huy Th ị nh (2005). Nghiên c ứ u ch ọ n, t ạ o gi ố ng có năng su ấ t và ch ấ t lư ợ ng cao cho m ộ t s ố loài cây tr ồ ng r ừ ng ch ủ l ự c. Vi ệ n Khoa h ọ c lâm nghi ệ p Vi ệ t Nam. 161 trang 4. Harwood, C.E. and Williams, E.R. (1992). A review of provenance variation in the growth of Acacia mangium . pp. 22 - 30 in Carron, L.T. and Aken, K. eds. Breeding Technologies f or Tropical Acacias. ACIAR Proceedings No. 37. Australian Centre for International Agricultural Research, Canberra. 5. Le Dinh Kha (2001). Studies on the use of natural hybrids between Acacia auriculiformis and Acacia mangium in Vietnam. Agriculture Publis hing House, Hanoi. 171 trang 6. Lê Đ ình Kh ả (2003). Ch ọ n t ạ o gi ố ng và nhân gi ố ng cho m ộ t s ố loài cây tr ồ ng r ừ ng ch ủ y ế u ở Vi ệ t Nam. Nhà xu ấ t b ả n Nông nghi ệ p, Hà N ộ i. 171 trang 7. Lê Đ ình Kh ả (2006). Báo cáo công nh ậ n gi ố ng m ộ t s ố dòng Keo lá tràm. Vi ệ n Khoa h ọ c Lâm nghi ệ p Vi ệ t Nam, Hà N ộ i. 17 trang. 8. Nambiar S. (1999). New forests: wood production and environmental services. CSIRO publishing. 256 trang. 9. Nguy ễn Đức Minh, Nguyễn Thị Thu H ương, và Đoàn Đ ình Tam (2004). Nghiên c ứu nhu CARD 032/05 – Acacia planation for sawlog production 195 c ầu dinh d ư ỡng khoáng (N,P,K) v à ch ế độ nư ớc của một số d òng keo lai (acacia hybrid) và b ạch đ àn ( Eucalyptus urophylla ) trong giai đo ạn v ư ờn ươm và r ừng non. Báo cáo tổng kết đ ề t ài. Vi ện Khoa học lâm nghiệp Việt Nam. 10. Nguy ễ n Hoàng Ngh ĩa (2003). Phát tri ể n các loài Keo Acacia ở Vi ệ t Nam. Nhà xu ấ t b ả n Nông nghi ệ p, hà N ộ i. 121 trang 11. Nguy ễ n Hoàng Ngh ĩa (2007). Báo cáo công nh ậ n m ộ t s ố dòng Keo lá tràm. Vi ệ n Khoa h ọ c Lâm nghi ệ p Vi ệ t Nam, Hà N ộ i. 20 trang 12. Nguy ễ n Huy Sơn, Nguy ễ n Xuân Quát và Đoàn Hoài Nam (2006). K ỹ thu ậ t tr ồ ng r ừ ng thâm canh m ộ t s ố loài cây g ỗ nguyên li ệ u. Nhà xu ấ t b ả n th ố ng kê, 128 trang 13. Nguy ễn Thị Liệu (2004). Điều tra tập đo àn cây tr ồng v à xây d ựng mô h ình tr ồng rừng keo lư ỡi liềm Acacia crassicarpar tr ên cát n ội đồng vùng B ắc Trung Bộ. Viện Khoa học Lâm nghi ệp Việt Nam. 14. Ph ạm thế Dũng, Ngô Văn Ngọc, Hồ Văn Phúc, Nguy ễn Thị Lề, Nguyễn Thị Nhuần, Ph ạm Viết T ùng và Nguy ễn Thanh B ình (2005). Nghiên c ứu một số biện pháp kỹ thuật thâm canh r ừng cho các d òng keo lai đư ợc tuy ển chọn tr ên đ ất ph ù sa c ổ tại tỉnh B ình Phư ớc l àm nguyên li ệu giấy. Viện Khoa học Lâm nghi ệp Việt Nam. 15. Phi Hong Hai (2009). Genetic improvement of plantation - grown Acacia auriculiformis for sawn timber production. Doctoral thesis No.2009:56. Swedish University of Agricultural Science. 16. Phí H ồ ng H ả i, Hà Huy Th ị nh và Đ ỗ H ữ u Sơn (2009a). Tri ể n v ọ ng phát tri ể n c ủ a m ộ t s ố dòng Keo lá tràm trong tr ồ ng r ừ ng g ỗ x ẻ . T ạ p chí Nông nghi ệ p và phát tri ể n nông thôn (12): 173 - 179. 17. Pinyopusarerk, K. (1990). Acacia auriculiformis: an annotated bibliography . Bangkok, Thailand: Winrock International - F/FRED and ACIAR, 154 p. 18. Vance C. P., Graham P. H. và Allan D.L. (2002). Biological Nitrogen Fixation: Phosphorus - A Critical Future Need? . Current Plant Science and Biotechnology in Agriculture (Ed. Pedrosa F.O., Hungria M., Yates G.and Newton W.E.). Springer Netherlands : 509 - 514. 19. Yang M., Xie X., He X. and Zhang F. (2006). Plant regeneration from phyllode explants of Acacia crassicarpa via organogenesis. Plant Cell, Tissue and Organ Culture (85): 241 - 245. . Collaboration for Agriculture and Rural Development (CARD) Program 186 ACACIA PLANTATIONS FOR SAWLOG PRODUCTION: SOME SIVILCULTURAL MEASURES AND RECOMMENDED SUITABLE AND PROFITABLE ACACIA SPECIES Project. significance P<0.001 P<0.001 none Standard error 0.15 0.23 3.4 Recommendation of suitable Acacia species suitable for sawlog production In Vietnam, Acacia mangium , Acacia crassicarpa and Acacia auriculiformis show best. nurseries and seed production) is recommended for Acacia mangium and A. crassicarpa . Family Clonal Forestry can also be an option for plantation of these two Acacia species. A. auriculiformis and Acacia