Nguyen Xuan Lieu[8]
Central Forest Seed Company, Hanoi, Vietnam
The geography and ecology of Vietnam
Vietnam lies on the eastern coast of the Indochinese peninsula in Southeast Asia. The country covers an area of about 331,000km2, much of which is hilly and mountainous. The Truong Son mountain range stretches from the north to the south of the country. In northeast Vietnam, the mountains reach an average height of 1000m above sea level. The highest peaks in the watersheds of the Chay, Lo and Gam rivers are over 2000m in height. The mountains in the northwest of Vietnam are the country's highest, reaching over 3000m. These slope down to the southeast, where they terminate in the Red River delta. Vietnam has over 2500 rivers longer than 10km. On average, every 20km of coastline has one estuary.
Annual levels of rainfall vary between 1700mm and 1800mm, but can reach as much as 3000mm in mountainous areas. Because of the monsoon regime, rainfall is regulated into distinct dry and rainy seasons. In the southern part of the central coastal region, the rainy season lasts for only 3-4 months. In the north, the central highlands and the south, the rainy season continues from May to October. Up to 80-85% of Vietnam's annual rainfall comes during the rainy season.
Although Vietnam is situated entirely in the tropics, climatic conditions vary considerably owing to wide variations in longitude and elevation. Average temperatures increase gradually from 22°C in the north of the country to 25°C in the south, though temperatures at higher elevations are lower.
Major forest formations
Vietnam's topography, climate and soils combine to produce an extremely diverse and abundant forest vegetation. The country has a wide range of forest types typical of the monsoon tropics. The dominant forest formations are described below.
Tropical evergreen broadleaf forest. Mixed stands of tropical tree families such as Fabaceae, Fagaceae and Lauraceae occur in hilly and mountainous areas below 800m in the north and 1000m in the south. In addition to the dominant woody species, medium-sized trees and shade-tolerant vegetation thrive under the forest canopy. Many epiphytic plants, such as orchids, lianas and various woody climbers, are found in these forests. Tropical evergreen broadleaf forests are a source of commercially valuable wood and non-wood forest products. These forests are also of special value as reservoirs of biological diversity.
Tropical evergreen broadleaf forest on limestone karst. The relatively diverse vegetation on limestone karst is dominated by evergreen species with a mix of deciduous species. The endemic woody species found in this formation, including Excentrodendron tonkinensis, Dacrydium pierrei, Fagraea fragrans and Diospyros mun, supply valuable furniture timber. Limestone karst forests also shelter vulnerable wildlife species such as fox, civet cat, antelope, monkey, squirrel and large birds such as pheasant and grey peacock. The remains of ancient hunter-gatherer communities have been found in limestone caves in Bac Son, Hoa Binh and Cuc Phuong. Vietnam's first national park is also situated in Cuc Phuong.
Subtropical evergreen broadleaf alpine forest. This formation occurs at elevations over 800m in the north of the country. Families represented include Fagaceae, Lauraceae, Ericaceae and Bambusaceae. Epiphytes such as orchids, Asplenium nidus, Drynaria bonii and other medicinal plants are also common. Ground conditions are favourable for the cultivation of many valuable medicinal herbs, in particular Euonymus cochinchinensis, Cinnamomum cassia and Panax ginseng.
Dry dipterocarp forest. This occurs in parts of the central plateau and the southeast of Vietnam, including the south coast. In general, dry dipterocarp forests are found at elevations below 1000m with pronounced seasonal variations in rainfall. They include both deciduous and evergreen species, but are dominated by dipterocarps. Most dry forests in the central highlands are waterlogged during the rainy season and affected by forest fires in the dry season. These forests are open with scattered and slow-growing trees. On slopes with moderate rainfall or deeper soils, however, dry dipterocarp forests form a multi-layered canopy with species such as Sindora cochinchinensis, Dalbergia cochinchinensis, Dalbergia oliveri, Pterocarpus pedatus, Anisoptera cochinchinensis, Hopea spp. and Dipterocarpus spp. Dipterocarp forests provide habitats for a number of rare and endangered mammal species, including elephants, tigers and panthers.
Coniferous forest. Coniferous species, namely Pinus merkusii and Pinus kesiya, grow at elevations above 1000m. In many cases, pines grow among subtropical evergreen stands at similar elevations and rainfall regimes. The Lam Dong highlands are famous for their large areas of natural pine forest. Pine forests provide wood for poles, veneers, furniture and pulp. Pine resin is tapped to produce turpentine for domestic use and export. Coniferous forests also support other valuable tree species such as Fokienia hodginsii and Cunninghamia sinensis, particularly in the Hoang Lien Son and Long mountain ranges.
Mangrove forest. Species typical of mangrove forests include Rhizophora conjugata, Sonneratia alba and Bruguiera gymnorhiza. On the southernmost cape of Nam Can, the two dominant species B. gymnorhiza and S. alba often reach heights of 10-15m and form large stretches of mangrove forest covering many thousands of hectares. Mangrove forests also harbour a wide range of aquatic and semi-aquatic species.
Melaleuca forest. Melaleuca cajuputi grows on acid soils in the south of Vietnam, particularly in Kien Giang, Dong Thap and other provinces in the southwest. At one time, stands of M. cajuputi reaching 15-20m covered many thousands of hectares. The tree grows fast and yields large volumes of wood for poles, firewood and charcoal. Its flowers are also a valuable resource for the bee-keeping industry. In addition, M. cajuputi forests help to ameliorate acid soils and protect freshwater resources.
Bamboo forest. Bamboos grow either in pure stands or mixed with trees in evergreen or deciduous forests throughout Vietnam. They are water-tolerant, light-demanding and fast-growing, and develop steadily on flat lands, hills and along streams with a short rotation of 2-4 years. There are many economically important varieties of bamboo. Neohouzeaua dullooa in the north, Bambusa procera in the south, Dendrocalamus membranaceus in Thanh Hoa and Arundinaria spathiflora in Bac Can and Cao Bang provinces are grown on a large scale and have great potential for intensive plantation development.
The flora of Vietnam
Vietnam lies at the crossroads of the Chinese, Himalayan and Indonesian vegetation zones. Notwithstanding the loss of forests over many years, the country's flora is still diverse and includes many economically valuable species. Vietnam's forests have many species with outstanding physical properties, suitable for fine handicrafts and furniture making. These include Dalbergia cochinchinensis, Diospyros mun, Chukrasia tabularis, Sindora cochinchinensis, Dalbergia oliveri, Fokienia hodginsii and Dacrydium pierrei. Other species such as Markhamia pierrei, Erythrophleum fordii, Madhuca pasquieri, Vatica tonkinensis and Burretiodendron hsienmu are resistant to certain pests and diseases.
According to an inventory by the Forest Inventory and Planning Institute (FIPI), Vietnam has about 12,000 plant species, of which about 1000 are known to be endemic. Some 354 tree species are regarded as commercially important with over 50 species providing high-quality timber. Forty-two tree species registered as rare and precious plants in Vietnam.
Among the large number of bamboo species, about 40 are commercially valuable. There are an estimated 40 species of rattan, and the annual harvest of rattan is about 50,000 tons. Inventory data indicate that two-thirds of Vietnam's 1800 medicinal herb species are found in natural forests. Preliminary inventories have shown that 76 species have aromatic resins, 600 contain tannin, 160 yield essential oils and 260 produce fatty oils. Today, however, many endemic plants are endangered and several species have already become extinct.
Overall status of forests and forest genetic resources
Trends in forest area and coverage
Vietnam's natural forest cover has been depleted by a number of causes, particularly clearance for industrialization and urbanization, war-related damage, shifting cultivation, over-exploitation of timber and repeated burning. Vietnam's forest cover was estimated to be 14.3 million hectares in 1943, or 43% of the national territory. By 1995, the area of forest had declined to 9.3 million hectares, or 28.2% of the national territory. Of this, 8.25 million hectares was natural forest and 1.05 million hectares tree plantations. The total growing stock in 1995 was 583.6 million m3, and the bamboo stock was 6.96 million stems. In 1999, forest cover had grown to 10.9 million hectares, or 33% of the national territory (Table 1).
Table 1. Change in forest area and coverage between 1976 and 1999 (in thousands of hectares). Source: Ministry of Forestry (1995); Forest Inventory and Planning Institute.
Forested land |
1976 |
1980 |
1985 |
1990 |
1995 |
1999 |
Natural |
11,076.7 |
10,186.0 |
9,308.3 |
8,430.7 |
8,252.5 |
9,444.2 |
Plantation |
92.6 |
422.3 |
583.6 |
744.9 |
1,049.7 |
1,471.4 |
Total |
11,169.3 |
10,608.3 |
9,891.9 |
9,175.6 |
9,302.2 |
10,915.6 |
Coverage (%) |
33.8 |
32.1 |
30.0 |
27.8 |
28.2 |
33.2 |
From 1943 to 1997, the overall growth in forest cover concealed both negative and positive changes (Table 2). Between 1943 and 1990, five million hectares of forest were deforested at an annual rate of about 100,000ha. Between 1990 and 1997, 436,300ha were deforested at an annual rate of 60,000ha. However, although natural forests decreased, by 1995 the area of plantation forest had grown considerably.
Table 2. Changes in area of different land uses between 1990 and 1997 (in thousands of hectares). Source: Forest Inventory and Planning Institute.
Land Use |
1990 |
1995 |
1997 |
Area change in period |
||
1990-95 |
1996-97 |
1990-97 |
||||
Forest lands |
9,175.6 |
9,302.2 |
9,432.9 |
126.6 |
130.7 |
257.3 |
Non-forest lands |
9,988.4 |
9,778.6 |
9,552.1 |
-209.8 |
-226.5 |
-436.3 |
Others |
13,872.0 |
14,030.9 |
14,126.7 |
158.9 |
95.8 |
254.7 |
The distribution of natural forest area and forest resources by main zones in Vietnam is as follows:
Table 3. Natural forest resources in three major zones. Source: Ministry of Forestry (1995).
|
Zonea) |
||
North Central |
South Central |
Central Highlands |
|
Natural forests ('1000 ha) |
1,400 |
1,500 |
3,300 |
Volume of standing stemwood ('1000 m3) |
118,200 |
132,100 |
289,300 |
a) Vietnam is divided into nine forestry zones: Northwest, Central North, Northeast, Red River Delta, North Central, South Central, Central Highlands, Southeast and Southwest (Mekong River Delta). The Central Highlands have 39% of the country's forest resources, the South Central zone has 18.1% and the North Central zone has 16.5%. The remaining zones have only 26.4%.
In areas where the forests have not been affected by human activities, the standing volume of timber is still high (up to 500-600m3/ha). These forests are small in area, however, and are found mainly at high elevations in steep, isolated sites.
Table 4. Forest area by forest type in 1997. Source: Nguyen Huy Phon (2000).
Forest Type |
Area ('000 ha) |
Proportion (%) |
|
Natural forest |
8,252.5 |
88.7 |
|
|
Rich and medium |
2,165.3 |
23.3 |
|
Poor and young |
4,621.7 |
49.7 |
|
Bamboo |
846.0 |
9.1 |
|
Mixed |
619.5 |
6.6 |
Plantation |
1,049.7 |
11.3 |
|
Total |
9,302.2 |
100.0 |
Vietnam's natural forest vegetation is divided into three categories: i) production forest, ii) protection forest, and iii) special-use forest (Table 5). Production forests are used mainly for wood and non-wood products, as well as environmental protection. To ensure appropriate management, these forests are split into different groups: timber production forests, industrial forests mainly for pulp, bamboo forests and non-wood product forests. Production forests are distributed as follows: rich forests (9.2%), medium forests (28.8%), poor forests (33.2%) and naturally regenerated forests (34.8%). Rich forests have a growing stock of more than 150m3/ha, whereas that of medium forests is 80-150m3/ha and that of poor forests is less than
Table 5. Area and proportion of each forest category. Source: Ministry of Forestry (1995).
|
Production |
Protection |
Special-Use |
Total |
Area ('000 ha) |
4,925.2 |
3,478.7 |
898.3 |
9,302.2 |
Proportion (%) |
52.9 |
37.4 |
9.7 |
100.0 |
Protection forests are designated to conserve soil and water resources, guard against land erosion and natural hazards, and protect wildlife. The protection forest system is divided into environmental protection forests, watershed forests, wind and soil protection forests and coastal protection forests. Thirty forest areas covering 3.5 million hectares have been designated to prevent sedimentation in reservoirs, protect hydroelectric power plants and water construction projects, and regulate large, nationally significant water bodies.
The development of protection forests along the central and western coasts of southern Vietnam aims to reduce wind flow and sand movements. Many protection forests have also been established around industrial zones in densely populated areas, and special attention has been paid to creating green belts around the cities of Hanoi and Ho Chi Minh. In addition, protection forests have also been established to maintain sources of water for consumption and industrial use. Special-use forests are set aside for nature conservation, research, maintaining historical and cultural relics, beauty spots and for recreation and tourism. These forests include national parks and nature reserves.
Over half of Vietnam's natural forests are of low quality and many special-use forests have been and will be removed from the protected list. War and unsustainable logging have damaged large areas of forest. Many valuable plant species have become endangered because of uncontrolled harvesting. There is an urgent need, therefore, for biodiversity and wildlife conservation measures, including plant genetic resources conservation.
Current activities in conservation, use and management of forest genetic resources
The five million hectares reforestation programme
Aware of the value of forests, the Vietnamese government, the Ministry of Agriculture and Rural Development (MARD) and the whole nation have taken action to protect existing forests and support sustainable forest sector development (CFSC 1998; MARD 1998; Nguyen Ngoc Binh 2000). The government has banned logging in natural forests in an effort to minimize further degradation. It has also launched major initiatives to rehabilitate forest cover, such as the five million hectare reforestation programme (5MHRP). The objectives of this programme, which is supported largely by international donors and institutions, are to:
Rehabilitate degraded lands and bring them into effective production to alleviate poverty;
Establish five million hectares of new forest and protect existing forests to increase forest cover from 28.2% (1995) to 43% by 2010; and
Protect the environment, decrease the severity of natural disasters, increase water availability, preserve plant genetic resources and protect biodiversity.
Programme targets are:
Two million hectares of protection and special-use forests will be planted. This will increase the total area of watershed forests to 6,515,000ha, windbreak forests to 130,000ha, wave-break forests to 155,000ha and special-use forests to 1,000,000ha.
Three million hectares of production forests, of which two million hectares will be industrial forests and one million hectares cash crops and fruit trees.
Promote scattered tree planting for environmental improvement and self-sufficiency in wood. An average of 350-400 million trees will be planted annually for this purpose.
Table 6 details the specific planting targets of 5MHRP in 1998-2000, 2001-2005 and 2006-2010.
Table 6. 5MHRP planting targets (in thousands of hectares).
Period |
Assisted natural regeneration |
Reforestation |
Total |
1998-2000 |
350 |
700 |
1,050 |
2001-2005 |
650 |
1,300 |
1,950 |
2006-2010 |
- |
2,000 |
2,000 |
Total |
1,000 |
4,000 |
5,000 |
The forest tree seed sector
Forest plantations expanded throughout the 1990s. In 1991, the area of plantations was 126,576ha and in 1997 it was 240,000ha. Other tree planting activities have also consumed about 300 million seedlings every year. Consequently, the demand for forest seed has grown substantially.
Providing enough forest seed and seedlings to meet demand, while at the same time maintaining quality, has proved difficult. There is only enough good-quality seed in the country to satisfy 25-30% of the demand from new forest plantations. To increase the supply of seed, MARD has re-organized the National Forest Seed and Planting Material Company into the Central Forest Seed Company (CFSC). In addition to existing seed orchards, many natural forests and well-planted forests consisting of selected species have been converted into seed-production areas. Seed sources are listed in Appendix 2.
A programme to develop vegetative propagation technology (tissue culture and cutting methods) has made good progress. A vegetative propagation centre has been established, high-yielding clones have been selected and human resources in this area have been developed. Seven Regional Forest Seed Enterprises under the CFSC, the Forest Tree Improvement Research Centre of the Forest Science Institute of Vietnam, the Yen Lap Forestry Research and Technical Experimental Centre in Quang Ninh Province and the Phu Ninh Forestry Research Centre in Phu Tho have contributed to the programme. Their success has had great benefits for the implementation of 5MHRP.
Tables 7 and 8 detail the projected seed demand of 5MHRP, calculated on the basis of 45 target species and the programme's planting targets.
Table 7. Demand of seed and seedlings for production forests. Source: Nguyen Duong Tai (2000).
Stage |
Seed demand (kg) |
Seedling demand ('000 stems) |
Annual average (1st stage) |
117,362 |
248,172 |
Annual average (2nd stage) |
152,037 |
321,496 |
Annual average (3rd stage) |
257,663 |
544,851 |
Total |
2,400,588 |
5,076,255 |
Table 8. Demand of seed and seedlings for the establishment of special-use forests and protection forests. Source: Nguyen Duong Tai (2000).
Stage |
Seed demand (kg) |
Seedling demand ('000 stems) |
Annual average (1st stage) |
128,308 |
226,057 |
Annual average (2nd stage) |
103,648 |
182,584 |
Annual average (3rd stage) |
115,494 |
203,451 |
Total |
1,480,634 |
2,608,350 |
To meet this demand with high-quality seed and seedlings, the major challenges for seed supply development are: i) establishing and managing seed networks from regional to national levels, ii) establishing and managing seed sources, and iii) establishing nurseries to produce large amounts of high-quality seedlings.
Ex situ conservation
Ex situ conservation in Vietnam is confined mainly to establishing a seed source system and demonstration plots. The major seed sources are listed in Appendix 2.
The protected area system as an in situ conservation system
The Vietnamese government has approved the extension of the reserve system to 107 protected areas, including 10 national parks, 65 nature reserves and 32 cultural, historic, scenic and environmental forests, covering a total area of almost one million hectares (Vietnam Scientific and Technical Association of Forestry 1995). In future, the reserve system is expected to increase to two million hectares (including 0.5 million hectares in buffer zones), and will protect a representative sample of almost all of the country's ecosystems.
The first national park of Vietnam, Cuc Phuong, was established in 1962. Covering a total area of 22,200ha, it represents low-mountain forests with a diverse flora of 987 genera in 217 families. Hoang Lien Son and Muong Nhe reserves were established to protect alpine forest ecosystems, whereas Yok Don national park was established to protect dry dipterocarp forest ecosystems. Cat Ba national park covers both forest and marine ecosystems, including many islands.
In future, there are plans to expand and develop ecotourism facilities across the country to attract local and foreign tourists. Management regulations for special-use forests, however, will be strictly controlled. Early in situ conservation efforts were carried out only in special-use forests, and ex situ conservation efforts were limited to the seed source system and some ex situ stands. There is now a strong need to develop and strengthen these conservation efforts.
Conclusions
For the time being, conservation efforts should focus on the following priority species:
Endangered species with high economic value;
Endangered species with high scientific value;
Valued local species for reforestation; and
Valued exotic species for reforestation.
In situ conservation measures should be applied in tandem with ex situ measures. The following measures should be implemented to improve conservation of forest genetic resources in Vietnam:
Botanical and genetic surveys;
Collection, evaluation and publication of data;
In situ and ex situ conservation measures; and
Improved use.
Identification of priority areas and species for conservation should based on the following factors:
Diversity;
Representativeness;
Endemism;
Degree of endangerment; and
Scientific and economic values.
References
CFSC (1998) Project document on production and supply of forest seed for the five million ha reforestation programme. Central Forest Seed Company, Hanoi.
MARD (1998) Project document on five million ha reforestation programme. Ministry of Agriculture and Rural Development, Hanoi.
Ministry of Forestry (1995) Vietnam Forestry. Ministry of Forestry, Hanoi.
Nguyen Duong Tai (2000) Seed quality for reforestation. In Schmidt, L. & Nguyen Xuan Lieu (eds.), Proceedings of National Seminar on Priority Tree Species, Hanoi, 7-8 September 2000. Indochina Tree Seed Programme/Central Forest Seed Company, Hanoi.
Nguyen Hoang Nghia (2000) Integrated strategies and conservation of forest genetic resources in Vietnam. In Schmidt, L. & Nguyen Xuan Lieu (eds.), Proceedings of National Seminar on Priority Tree Species, Hanoi, 7-8 September 2000. Indochina Tree Seed Programme/Central Forest Seed Company, Hanoi.
Nguyen Huy Phon (2000) Discussion on Priority Species in Contemporary Vietnamese Forestry and Tree Seed Aspects. Presentation at the Second Regional Consultation for Danish Supported Tree Seed Projects in South East Asia. Hanoi, February 2000.
Nguyen Ngoc Binh (2000) Introduction to 5 million ha reforestation programme. In Schmidt, L. & Nguyen Xuan Lieu (eds.), Proceedings of National Seminar on Priority Tree Species, Hanoi, 7-8 September 2000. Indochina Tree Seed Programme/Central Forest Seed Company, Hanoi.
Nguyen Xuan Lieu (2000) Summary and key findings of regional priority species workshops. In Schmidt, L. & Nguyen Xuan Lieu (eds.), Proceedings of National Seminar on Priority Tree Species, Hanoi, 7-8 September 2000. Indochina Tree Seed Programme/Central Forest Seed Company, Hanoi.
Vietnam Scientific and Technical Association of Forestry (1995) National Parks and Nature Reserves in Vietnam. Vietnam Scientific and Technical Association of Forestry, Hanoi.
Appendix 1. Value and use of target, important species in Vietnam
Species Name |
Value Codea) |
Present, future or potential useb) |
|||||||||||
ti |
po |
wo |
nw |
pu |
fo |
fd |
sh |
ag |
co |
am |
xx |
||
Afzelia xylocarpa |
1 |
Ö |
|
|
|
|
|
|
|
|
|
|
|
Aleurites montana |
2 |
|
|
|
Ö |
|
|
|
|
|
|
|
|
Aquilaria crassna |
1 |
|
|
|
Ö |
|
|
|
|
|
Ö |
Ö |
|
Bambusa sp. |
1 |
|
|
|
|
Ö |
Ö |
Ö |
Ö |
Ö |
Ö |
Ö |
|
Calamus rudentum |
2 |
|
|
|
Ö |
|
|
|
|
Ö |
|
Ö |
|
Calamus tenuis |
2 |
|
|
|
Ö |
|
|
|
|
Ö |
|
Ö |
|
Camellia sasanqua |
2 |
|
|
|
Ö |
|
Ö |
|
|
Ö |
|
|
|
Canarium spp. |
1 |
Ö |
|
|
Ö |
|
Ö |
|
|
Ö |
Ö |
Ö |
|
Cassia glauca |
2 |
Ö |
|
|
|
|
|
|
|
|
|
Ö |
|
Cassia siamea |
1 |
Ö |
|
|
|
|
|
|
Ö |
Ö |
Ö |
|
|
Castanopsis/Quercus spp. |
2 |
Ö |
|
Ö |
|
|
Ö |
|
Ö |
Ö |
Ö |
|
|
Chukrasia tabularis |
1 |
Ö |
|
|
|
|
|
|
|
Ö |
Ö |
Ö |
|
Cinnamomum balansae |
1 |
|
|
|
Ö |
|
|
|
|
|
Ö |
|
|
Cinnamomum cassia |
1 |
|
|
|
Ö |
|
Ö |
|
|
Ö |
|
|
|
Cinnamomum parthenoxylon |
1 |
Ö |
Ö |
|
|
|
|
|
|
|
Ö |
|
|
Cocos nucifera |
2 |
|
|
|
Ö |
|
Ö |
|
Ö |
|
|
|
|
Cunninghamia lanceolata |
1 |
Ö |
Ö |
|
|
|
|
|
|
|
|
Ö |
|
Dendrocalamus membranaceus |
1 |
|
|
|
|
Ö |
Ö |
Ö |
Ö |
Ö |
Ö |
|
|
Dimocarpus longan |
2 |
Ö |
|
|
|
|
Ö |
|
Ö |
Ö |
Ö |
|
|
Dipterocarpus alatus |
1 |
Ö |
Ö |
|
|
|
|
|
Ö |
|
|
|
|
Dracontomelon mangiferum |
2 |
Ö |
Ö |
|
|
|
Ö |
|
Ö |
Ö |
Ö |
|
|
Endospermum chinense |
2 |
Ö |
|
|
|
|
|
|
|
|
Ö |
|
|
Erythrophleum fordii |
1 |
Ö |
|
|
|
|
|
|
|
|
Ö |
|
|
Hopea odorata |
1 |
Ö |
Ö |
|
|
|
|
|
|
|
|
|
|
Illicium verum |
1 |
|
|
|
Ö |
|
Ö |
|
Ö |
Ö |
Ö |
Ö |
|
Litchi sinensis |
2 |
Ö |
|
|
|
|
Ö |
|
Ö |
Ö |
Ö |
|
|
Litsea sebifera |
2 |
|
|
|
Ö |
|
|
|
|
Ö |
|
|
|
Madhuca pasquieri |
2 |
Ö |
|
|
Ö |
|
Ö |
|
Ö |
Ö |
Ö |
|
|
Mangifera minor |
2 |
Ö |
|
|
|
|
Ö |
|
Ö |
Ö |
Ö |
Ö |
|
Manglietia glauca |
1 |
Ö |
Ö |
|
|
Ö |
|
|
Ö |
|
Ö |
Ö |
|
Parashorea chinensis |
1 |
Ö |
Ö |
|
|
|
|
|
Ö |
|
Ö |
Ö |
|
Paulownia fortunei |
2 |
|
|
|
|
Ö |
|
|
|
Ö |
|
|
|
Peltophorum ferrugineum |
2 |
Ö |
Ö |
|
|
|
|
|
|
Ö |
Ö |
|
|
Phoebe cuneata |
2 |
Ö |
Ö |
|
|
|
|
|
|
|
Ö |
|
|
Pinus kesiya |
1 |
Ö |
Ö |
|
Ö |
Ö |
|
|
|
|
|
|
|
Pinus massoniana |
1 |
Ö |
Ö |
|
Ö |
|
|
|
|
|
|
|
|
Pinus merkusii |
1 |
Ö |
Ö |
|
Ö |
|
|
|
|
|
|
|
|
Pterocarpus spp. |
1 |
Ö |
|
|
|
|
|
|
|
|
Ö |
|
|
Rhizophora spp. |
1 |
Ö |
Ö |
Ö |
|
|
|
|
|
|
Ö |
|
|
Schima wallichii |
2 |
Ö |
|
|
|
|
|
|
|
Ö |
Ö |
|
|
Sindora siamensis |
1 |
Ö |
|
|
|
|
|
|
|
|
Ö |
|
|
Sterculia lychnophora |
2 |
Ö |
|
|
Ö |
|
|
|
|
|
Ö |
|
|
Styrax tonkinensis |
1 |
|
|
|
Ö |
Ö |
|
|
|
|
|
|
|
Talauma gioi |
1 |
Ö |
|
|
|
|
|
|
Ö |
|
Ö |
Ö |
|
Tarrietia javanica |
1 |
Ö |
Ö |
|
|
|
|
|
|
Ö |
Ö |
|
|
Tectona grandis |
1 |
Ö |
Ö |
|
|
|
|
|
|
|
|
|
|
Toona sinensis |
2 |
Ö |
Ö |
|
Ö |
|
|
|
Ö |
|
Ö |
|
|
a) 1 = Species of current socio-economic importance; 2 = Species with clear potential or future value, 3 = Species of unknown value given present knowledge and technology.
b) ti = timber production; po = posts, poles, roundwood; pu = pulp and paper; wo = fuelwood, charcoal; nw = non-wood products (gums, resins, oils, tannins, medicines, dyes etc.); fo = food; fd = fodder; sh = shade, shelter; ag = agroforestry systems; co = soil and water conservation; am = amenity, aesthetic, ethical values; xx = other.
Appendix 2. Area of selected forest seed sources in Vietnam (in hectares)
Species Name |
Total Area |
Regional distribution |
||||||
NW |
CN |
NE |
NC |
SC |
CH |
S |
||
Pinus massoniana |
352 |
50 |
100 |
202 |
|
|
|
|
Pinus merkusii |
710.6 |
|
|
30 |
409.2 |
11.4 |
260 |
|
Pinus caribaea |
57.1 |
|
|
|
57.1 |
|
|
|
Pinus kesiya |
1,720 |
80 |
|
|
|
|
1,640 |
|
Cunninghamia lanceolata |
140 |
|
80 |
60 |
|
|
|
|
Chukrasia tabularis |
70 |
57 |
3 |
|
10 |
|
|
|
Aleurites montana |
174 |
174 |
|
|
|
|
|
|
Canarium album |
275 |
20 |
|
|
|
|
255 |
|
Castanopsis spp. |
286 |
|
|
190 |
96 |
|
|
|
Manglietia glauca |
217 |
|
217 |
|
|
|
|
|
Styrax tonkinensis |
92 |
|
92 |
|
|
|
|
|
Erythrophleum fordii |
196 |
|
86 |
|
110 |
|
|
|
Alnus nepalensis |
28 |
|
28 |
|
|
|
|
|
Schima wallichii |
108 |
|
76 |
32 |
|
|
|
|
Tectona grandis |
379 |
20 |
|
|
|
|
9 |
350 |
Dendrocalamus membranaceus |
80 |
80 |
|
|
|
|
|
|
Schleichera oleosa |
24 |
12 |
|
|
12 |
|
|
|
Cinnamomum cassia |
141 |
|
61 |
|
80 |
|
|
|
Illicium verum |
40 |
|
|
40 |
|
|
|
|
Engelhardtia chrysolepis |
50 |
|
|
50 |
|
|
|
|
Toona sinensis |
40 |
|
|
40 |
|
|
|
|
Altingia takhtajanii |
30 |
30 |
|
|
|
|
|
|
Aquilaria crassna |
77.1 |
|
|
|
77.1 |
|
|
|
Talauma gioi |
2 |
|
|
|
2 |
|
|
|
Casuarina equisetifolia |
191.3 |
|
|
|
141.3 |
50 |
|
|
Endospermum chinense |
185 |
|
|
|
15 |
|
170 |
|
Calophyllum saigonense |
20 |
|
|
|
20 |
|
|
|
Symplocos laurina |
66.6 |
|
|
|
66.6 |
|
|
|
Tarrietia javanica |
79 |
|
|
|
79 |
|
|
|
Acacia auriculiformis |
273.5 |
|
|
|
55.5 |
18.3 |
50 |
150 |
Acacia mangium |
144.5 |
5 |
37.6 |
|
31.9 |
|
50 |
20 |
Sindora tonkinensis |
170 |
|
|
|
170 |
|
|
|
Neolitsea cambodiana |
33.3 |
|
|
|
33.3 |
|
|
|
Madhuca pasquieri |
182 |
|
|
|
182 |
|
|
|
Camellia sasanqua |
30 |
|
|
|
30 |
|
|
|
Lagerstroemia cochinchinensis |
130 |
|
|
|
70 |
|
60 |
|
Pterocarpus macrocarpus |
230 |
|
|
|
40 |
|
70 |
120 |
Xylia dolabriformis |
282 |
|
|
|
|
212 |
70 |
|
Dipterocarpus alatus |
175 |
|
|
|
|
55 |
|
120 |
Hopea odorata |
160 |
|
|
|
|
50 |
|
110 |
Cassia siamea |
106 |
|
|
|
|
|
106 |
|
Dalbergia cochinchinensis |
60 |
|
|
|
|
10 |
50 |
|
Eucalyptus spp. |
182 |
|
8 |
|
|
110 |
50 |
13 |
Anisoptera cochinchinensis |
100 |
|
|
|
|
|
|
100 |
Anacardium occidentale |
36 |
|
|
|
|
36 |
|
|
Hopea dealbata |
7 |
|
|
|
|
|
7 |
|
Dipterocarpus dyeri |
120 |
|
|
|
|
|
|
120 |
Sindora cochinchinensis |
100 |
|
|
|
|
|
|
100 |
Rhizophora conjugata |
543 |
|
|
|
|
|
|
543 |
Melaleuca leucadendron |
327 |
|
|
|
|
|
|
327 |
Dacrydium pierrei |
50 |
|
|
|
|
|
50 |
|
Fokienia hodginsii + Pinus excelsa |
50 |
|
|
|
|
|
50 |
|
Michelia mediocris |
218 |
|
|
|
|
|
218 |
|
Shorea cochinchinensis |
150 |
|
|
|
|
150 |
|
|
Others |
27 |
|
|
|
27 |
|
|
|
Total |
9,716.8 |
528 |
788.9 |
644 |
1,814.5 |
703.7 |
3,165 |
2,073 |
Appendix 3. List of priority tree species for gene conservation in Vietnam. Source: Nguyen Xuan Lieu (2000).
Species Name |
Region |
|||||||
NW |
CN |
NE |
NC |
SC |
CH |
SE |
SW |
|
Afzelia xylocarpa |
|
|
|
|
Ö |
Ö |
Ö |
|
Altingia takhtajanii |
Ö |
Ö |
|
|
|
|
|
|
Anisoptera cochinchinensis |
|
|
|
|
|
|
Ö |
|
Aquilaria crassna |
Ö |
Ö |
Ö |
Ö |
Ö |
|
Ö |
Ö |
Bruguiera gymnorhiza |
|
|
|
|
|
|
|
Ö |
Burretiodendron hsienmu |
Ö |
Ö |
Ö |
|
|
|
|
|
Calocedrus macrolepis |
|
|
|
|
Ö |
Ö |
|
|
Cephalotaxus hainanensis |
|
|
|
|
|
|
|
|
Cestrum nocturnum |
|
|
|
Ö |
|
|
|
|
Chukrasia tabularis |
Ö |
Ö |
Ö |
Ö |
|
Ö |
|
|
Cinnamomum balansae |
Ö |
Ö |
Ö |
Ö |
|
Ö |
|
|
Cinnamomum polyadelphum |
|
|
|
|
|
|
|
Ö |
Cupressus funebris |
Ö |
Ö |
|
|
|
|
|
|
Cupressus torulosa |
|
|
Ö |
|
Ö |
|
|
Ö |
Dacrydium pierrei |
|
|
|
|
|
Ö |
|
|
Dalbergia annamensis |
|
|
|
Ö |
Ö |
Ö |
|
|
Dalbergia bariensis |
|
|
|
|
|
Ö |
Ö |
|
Dalbergia mammosa |
|
|
|
|
|
Ö |
Ö |
|
Dalbergia spp. |
|
|
|
Ö |
Ö |
Ö |
|
|
Diospyros mun |
Ö |
Ö |
|
Ö |
Ö |
|
|
|
Diospyros siamensis |
|
|
|
|
|
|
Ö |
Ö |
Dipterocarpus alatus |
|
|
|
|
|
|
Ö |
|
Dipterocarpus grandiflorus |
|
|
|
|
|
Ö |
|
|
Dipterocarpus dyeri |
|
|
|
|
|
|
Ö |
|
Dysoxylum cauliflorum |
Ö |
Ö |
|
Ö |
|
|
|
|
Ducampopinus krempfii |
|
|
|
|
Ö |
Ö |
|
|
Erythrophleum fordii |
Ö |
Ö |
Ö |
Ö |
|
|
|
|
Fokienia hodginsii |
Ö |
Ö |
Ö |
Ö |
Ö |
Ö |
|
|
Fagraea fragrans |
|
|
|
|
|
|
Ö |
Ö |
Garcinia fagraeoides |
|
|
Ö |
Ö |
|
|
|
|
Glyptostrobus pensilis |
|
|
|
|
|
Ö |
|
|
Hexaneurocarpon brilletii |
Ö |
Ö |
|
|
|
|
|
|
Hopea odorata |
|
|
|
|
|
|
Ö |
|
Hopea pierrei |
|
|
|
|
|
Ö |
|
Ö |
Lagerstroemia angustifolia |
|
|
|
|
Ö |
|
|
Ö |
Keteleeria davidiana |
Ö |
Ö |
|
|
|
Ö |
|
|
Madhuca pasquieri |
Ö |
Ö |
|
Ö |
|
|
|
|
Magnolia dandyi |
Ö |
Ö |
Ö |
Ö |
|
|
|
|
Markhamia stipulata |
|
|
Ö |
Ö |
|
Ö |
|
|
Michelia spp. |
|
|
|
|
|
|
|
|
Parashorea chinensis |
Ö |
Ö |
|
|
|
|
|
|
Pinus excelsa (Pinus dalatensis) |
|
|
|
|
|
Ö |
|
|
Pinus kwangtungensis |
|
|
|
|
|
Ö |
|
|
Podocarpus fleuryi |
Ö |
Ö |
|
Ö |
|
Ö |
|
Ö |
Podocarpus imbricata |
|
|
Ö |
|
|
Ö |
|
Ö |
Podocarpus neriifolius |
Ö |
Ö |
Ö |
|
|
Ö |
|
|
Pterocarpus pedatus |
|
|
|
|
Ö |
Ö |
Ö |
|
Pterocarpus macrocarpus |
|
|
|
|
Ö |
Ö |
Ö |
|
Renanthera sp. |
|
|
|
|
|
Ö |
|
|
Shorea cochinchinensis |
|
|
Ö |
|
|
|
Ö |
|
Shorea falcata |
|
|
|
|
Ö |
|
|
|
Sindora siamensis |
|
|
|
Ö |
|
Ö |
Ö |
|
Sindora tonkinensis |
|
|
|
Ö |
|
|
|
|
Sterculia lychnophora |
|
|
|
|
Ö |
Ö |
Ö |
|
Talauma gioi |
Ö |
Ö |
Ö |
Ö |
|
|
|
|
Tarrietia javanica |
|
|
|
Ö |
|
|
|
|
Taxus chinensis |
Ö |
Ö |
|
|
|
Ö |
|
|
Utricularia sp. |
|
|
|
|
|
Ö |
|
|
Vatica odorata |
Ö |
Ö |
Ö |
Ö |
|
|
|
|
Xylia dolabriformis |
|
|
|
|
|
Ö |
Ö |
|
Xylocarpus granatum |
|
|
|
|
|
|
|
Ö |
Appendix 4. Endangered species with high economic value in Vietnam. Source: Nguyen Hoang Nghia (2000).
Species |
Family |
Distribution |
Value |
Afzelia xylocarpa |
Leguminosae |
CS |
**** |
Altingia chinensis |
Altingiaceae |
NC |
** |
Aquilaria crassna |
Thymeleaceae |
NCS |
**** |
Chukrasia tabularis |
Meliaceae |
NC |
**** |
Cupressus torulosa |
Cupressaceae |
N |
**** |
Dacrydium pierrei |
Podocarpaceae |
NCS |
*** |
Dalbergia annamensis |
Leguminosae |
CS |
**** |
Dalbergia bariensis |
Leguminosae |
CS |
**** |
Dalbergia cochinchinensis |
Leguminosae |
CS |
**** |
Diospyros mun |
Ebenaceae |
C |
**** |
Erythrophleum fordii |
Leguminosae |
NC |
**** |
Fokienia hodginsii |
Cupressaceae |
NC |
**** |
Keteleeria davidiana |
Pinaceae |
NC |
** |
Madhuca pasquieri |
Sapotaceae |
NC |
**** |
Manglietia fordiana |
Magnoliaceae |
NC |
**** |
Markhamia stipulata |
Bignoniaceae |
NC |
**** |
Parapentace tonkinensis |
Tiliaceae |
N |
**** |
Parashorea chinensis |
Dipterocarpaceae |
NC |
*** |
Podocarpus fleuryi |
Podocarpaceae |
NC |
*** |
Pterocarpus macrocarpus |
Leguminosae |
CS |
**** |
Sindora siamensis |
Leguminosae |
CS |
*** |
Sindora tonkinensis |
Leguminosae |
NC |
*** |
Taxus chinensis |
Taxaceae |
N |
*** |
Taxus wallichiana |
Taxaceae |
C |
**** |
Xylia xylocarpa |
Leguminosae |
CS |
*** |
Appendix 5. Endangered species with high scientific value in Vietnam. Source: Nguyen Hoang Nghia (2000).
Species |
Family |
Distribution |
Value |
Abies nukiangensis |
Pinaceae |
N |
Rare |
Amentotaxus argotaenia |
Taxaceae |
N |
Rare |
Annamocarya sinensis |
Juglandaceae |
N |
Rare |
Bambusa ventricosa |
Poaceae |
NC |
*** |
Calocedrus macrolepis |
Cupressaceae |
NC |
*** |
Carya tonkinensis |
Juglandaceae |
N |
Rare |
Cephalotaxus fortunei |
Cephalotaxaceae |
NCS |
** |
Chimonobambusa quadrangularis |
Poaceae |
N |
*** |
Ducampopinus krempfii |
Pinaceae |
C |
Rare |
Fagus longipetiolata |
Fagaceae |
N |
** |
Fraxinus chinensis |
Oleaceae |
NC |
** |
Garcinia fagraeoides |
Clusiaceae |
NC |
*** |
Glyptostrobus pensilis |
Taxodiaceae |
C |
Rare |
Hopea cordata |
Dipterocarpaceae |
C |
** |
Hopea hainanensis |
Dipterocarpaceae |
C |
** |
Hopea pierrei |
Dipterocarpaceae |
CS |
**** |
Liriodendron chinense |
Magnoliaceae |
N |
*** |
Phyllostachys nigra |
Poaceae |
N |
Rare |
Pinus dalatensis |
Pinaceae |
C |
Rare |
Pinus kwangtungensis |
Pinaceae |
N |
Rare |
Podocarpus neriifolius |
Podocarpaceae |
NCS |
Rare |
Podocarpus pilgeri |
Podocarpaceae |
NS |
Rare |
Rhoiptelea chiliantha |
Rhoipteleaceae |
N |
** |
Tsuga dumosa |
Pinaceae |
N |
Rare |
Appendix 6. Highly valued native species with re/afforestation potential in Vietnam. Source: Nguyen Hoang Nghia (2000).
Species |
Family |
Distribution |
Value |
Anisoptera costata |
Dipterocarpaceae |
CS |
*** |
Bambusa stenostachya |
Poaceae |
NCS |
** |
Canarium sp. |
Burseraceae |
NC |
*** |
Cinnamomum cassia |
Lauraceae |
NC |
**** |
Dendrocalamus flagellifer |
Poaceae |
CS |
** |
Dendrocalamus membranaceus |
Poaceae |
NC |
** |
Dendrocalamus strictus |
Poaceae |
CS |
** |
Dipterocarpus alatus |
Dipterocarpaceae |
CS |
*** |
Hopea odorata |
Dipterocarpaceae |
CS |
*** |
Illicium verum |
Illiciaceae |
N |
**** |
Michelia sp. |
Magnoliaceae |
NC |
*** |
Phyllostachys pubescens |
Poaceae |
N |
*** |
Pinus kesiya |
Pinaceae |
NC |
** |
Pinus merkusii |
Pinaceae |
NC |
** |
Notes to Appendixes 4, 5 & 6:
Distribution: N = North; C = Central (including central highland); S = South.
Value: **** = Very high value; *** = High value; ** = Valuable.
[8] Chief of Technical Section,
Central Forest Seed Company, 62 Cau Dien Township, Tu Liem, Hanoi, Vietnam, Tel:
+84-4-837 2472, Fax: +84-4-837 2470, E-mail: [email protected] |