http://www.fao.org/forestry/site/18314/en/irn/
Introduction
Forest cover map
The designations employed and the presentation of material in this publication do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries.
Map source: Global Forest Resources Assessment 2000, base map: ESRI
The above map is an extract from the Global Forest Cover map produced as part of FRA 2000. Please refer to FRA Working Paper 19 for a background to the production of the map.
Temperate, semi-humid; semi-arid and arid forests cover about 12 400 000 ha. Over 90 percent of them are hardwoods.
Certain types of trees predominate in various geographical regions due to differences in temperature, moisture supply, soil conditions and elevation. Some of the forests have been destroyed or severely degraded.
Five different regional forest types may be distinguished as follows:
The Caspian broadleaved deciduous temperate forests: These forests are also called the Hyrcanian forests. They are located on the south coast of the Caspian Sea and the northern slopes of the Alborz mountain range from sea level to 2 800 m altitude.
The Caspian forests area is about 1 900 000 ha. They extend for 800 km in length and about 25 km in width. Approximately 60 percent of these forests are used for commercial purposes and the rest of them are more or less degraded. The average annual precipitation ranges from 600 to 2 000 mm with a maximum in the west and a minimum in the east. These are the most valuable forests in Iran.
Arasbaran sub-higrophic forest: These forests, located in north-western Iran, look like the Hyrcanian forest but some of species such as Fagus orientalis and Quercus castaneifolia do not grow in the Arasbaran region.
Irano-Toranian evergreen and broadleaved forests: These cover an area of about 3 500 000 ha in the central plateau and mountainus part of the country. The region is arid to semi-arid and the annual precipitation varies between 100 and 400 mm.
Zagrosian broadleaved deciduous forests: The main constituent of these forests is oak, Quercus spp. They stretch from north to south along the Zagros mountains, extending as far as Shiraz. They grow under annual precipitation between 450 and 1 050 mm. They are subject to over-exploitation and degradation due to intensive human activities and overgrazing.
The Khalijo-Ommanian forests: This region comprises the entire southern part of Iran between the southern watersheds of the Zagros, the coast of the Persian Gulf and the sea of Oman. The climate is subtropical with hot summers. The average annual rainfall is less than 200 mm.
http://www.fao.org/countryprofiles/index.asp?lang=en&iso3=IRN&subj=5
closed forest
Broadleaved forests
Dense, two-level Quercus spp. forests grow on the sandy soil of the Caspian plain. The upper story consists of Quercus castaneaefolia. The lower story is very dense and consists of Buxus sempervirens, Gleditschia caspica, Diospyros lotus, and Albizzia julibrissin. In the lower storey and on the ground, the fern Pteris arguta and the grasses Oplismenus undulatifolius and Brachiara eruciformis grow. Great quantities of moss grow on the ground and on the branches of the trees, giving this forest a special appearance.
At the foot of the northern slope of the Alborz mountains in Mazandaran and Gilan provinces where sites are drier the Quercus spp. trees grow with remnants of Carpinus betulus. Towards the northeast, the climate becomes drier and the main species associated with oak is Zelkova carpinifolia.
On the steep slopes of the Caspian the Parrotia persica and Carpinus betulus forest with an abundance of Hypericum androasaemum and Primula heterochroma represents one of the important Caspian forests. Currently it is subject to overexploitation.
Quercus persica forests cover about ^ 850 000 ha. They grow in pure stands, mainly on the southwestern watersheds of the Zagros. On the Persian Gulf they receive annual rainfall of about 400 to 500 mm. They are overgrazed; however, the nomadic Kashkai tribes who use the acorns to make their bread have preserved them.
The larger Quercus spp. trees reach a height of 12 to 15 m and can cover up to 50 percent of the ground.
The characteristic species of this forest are Quercus persica, Acer cinerascens, Lonicera persica, Pyrus glabra, Pistacia Khindjuk, Ephedra ciliata, Ranunculus ficaroides, Gundelia tournefortii, Geranium tuberosum, Anemone biflora, Lris, Carex stenophylla, Astragalus fasciculifolium, Anemone coronaria, Viola modesta, Fritellaria imperialis, Bongardia crisogonum and Helianthemum salicifolium.
In some cooler valleys Platanus orientalis, Fraxinus oxycarpa and Salix aegyptica are found.
The beech forest of Fagus orientalis var. macrophylla is the most productive forest in Iran. Stratification in the canopy is well developed. The beech trees make a canopy 40 m in height and some trees attain 2 m diameter at breast height. There is a mid-level tree and shrub strata if there is adequate light penetrating the upper canopy. When the canopy is closed and the light intensity beneath it is less than 2 percent there is no herbaceous strata. The forest is well preserved.
On rich moist soil Fagus orientalis var. macrophylla grows in association with Epimedium pinnatum, Euphorbia amygdaloides, Sanicula europea, Iraea luteniana, Galium odoratum and Murcuriaris perennis. In this forest, some commercial trees are present at very low density including Acer glabra, Acer velutinum and Acer cappadocicum.
There are small areas of mangrove forests along the tidal zones of the sea of Oman. These have a total area of 15 to 20 thousand hectares of Avicennia marina and Rhizophora mucronata. Originally there were about 200 000 hectares of Avicennia marina forests.
Open forest
Broadleaved
Groups of oak forests dominated by Quercus infectoria, Quercus libani and few other species are located in Kurdestan, West Azarbayjan, Kermanshah and North Lorestan where they constitute very special forests. The trees are scattered with a cushion of plants such as Acantholimon bromifolium var. ilamicum and Acanthophyllum squarosum.
Unfortunately, all these Quercus spp. are not of high wood quality. They grow at altitudes between 1 600 and 2 200 m. At the bottom of the valleys they grow with Juglans regia.
At altitudes over 3 000 m Carpinus orientalis in association with Quercus macranthera forms the highest zone of forest vegetation in the Caspian region. Trees are of small height and of no economic value. This association, with slight modifications, can be found north of Ardabil in Arasbaran.
In the eastern Zagros, at altitudes between 1 800 and 2 200 m, Pistacia mutica forms real forests. In the center of the Zagros Pistacia kKhindjuk joins Pistacia mutica.
The Khalijo-Ommanian vegetation or semi-savanna thorn forests occupy hot, dry regions of the Khalijo-Ommanian zone. These were savanna thorn forests but the drastic transformation of the natural vegetation resulted in the formation of hot, dry areas.
The main tree species are Acacia seyal, A. arabica, A. nubica and A. senegalis. Other plants are Stoksia brahuica, Periploca aphylla, Vitex pseudonegundo, Withania somnifera, Ziziphus nummularia, Olea aucheri, O. cuspidata, Cassia obovata, Thylophora tenuis, Boucerosia aucheriana, Telosma palida, Doemia extensa, Glossonema edula, Callotropis procera, Myrsine buxiflora, Salvadora oleoides, Caryopteris vallidhiana, Clerodendron priva, Euphorbia larica and Dalbergia sisso
Coniferous
Juniperus forests cover the high mountains of the Irano-Turanian region, Zagros and Azerbaidjan at 1 500 to 3 500 m altitude. They grow under 220 to 450 mm rainfall and average annual temperatures of 3 to 12o C.
The main tree species is Juniperus polycarpa with accompanying species Lonicera nummulariifolia, Amygdalus orientalis, Cotoneaster nummulariodes, Daphne mucronata, and Astragalus adsceneds. The forests once covered considerable area but now they are almost destroyed.
Other wooded land
Shrublands of Pistacia mutica are located on the northern slopes of the Albourz mountains at altitudes between 1 600 and 1 800 m. Sporadic trees of Rhus coriaria and Celtis australis grow with them.
On the north-eastern boarder of Iran, north of Meshed, the edible pistachio nut, Pistacia vera, grows. Due to the harsh climate it looks like tall undergrowth.
Below the Quercus spp. forests, tall bushes of Amygdales scoporia and Acer cinerascens grow on the southern slopes of the Zagros. Associated species are Daphne angustifolia, Ebenus stellata, Amygdalus lycioides, Crataegus heterophylla, Phlomis orientalis, Rhamnus spatulifolia, Cotoneaster nummularifolia, and Carrigia orientalis.They are subjected to overgrazing from the point of view of soil protection.
A degraded and overgrazed vegetation of thorny bushes of Amygdalis reuteri, Berberis integrimma and Cratagus spp. also grows on the southern slopes of the Zagros and the southern slopes of the Albourz. The plants of this association that have been able to survive are those left by the animals in addition to a few bushes growing on steep, inaccessible rocks.
There are many Tamarix articulata associations found in the southeast on the borders of Afghanistan and Pakistan. The area is almost desert and slightly salty. About 36 species of Tamarix grow in Iran. Most of them are bushes although a few, such as Tamarix articulata and Tamarix stricta, are tall and of economic importance.
Tamarix macrocarpa and Tamarix tetrandra, for example, are the dominant shrubs in the bushy vegetation close to Lake Ghom. The lower vegetation consists of the herbaceous species Psilliostachys letpostachya, P. spicata and Aeluropus littoralis.
In the valleys with slightly salty soils, Tamarix spp. grow with Aeluropus littoralis, Suaeda spp., Vitex agnus castus, Lycium barbarum and Nitraria scuba.
In the Irano-Toranian region, Haloxylon spp. grow mostly on sand. The vegetation is made up of bushy and very scattered small trees. The following species can be found: Haloxylon ammodendron, H. aphyllum, H. persicum and Calligonum commosum. The haloxylons are very important for stabilization of sand dunes and soil protection.
The Ziziphus spina-christi shrublands are also called the vegetation of the Khalidjian region. This type of shrubland stretches from Qassre-Shirin toward Khuzistan and the coast of the Persian Gulf up to Bandar Abbas in the North. The climate of this area is subtropical. These shrublands are sometimes invaded by Prosopis stephaniana.
Other species include Imperata cylindrica, Cordia mixa, Fortuynis aucheri, Salvadora persica, Ranunculus asiaticus, Populus euphratica, Nerium odorum, Ebenus stellata, Convolvulus leicalycinos, Ochradenus baccata and Physorynchus brachuicus.
References
Anon. Undated. Sustainable management of natural resources: Forests. Teheran. Government press.
Forest and Range Organization. 1997. Some data of forests in Iran. Teheran. Ministry of Jihad-e-Sazandegi. The Islamic Republic of Iran.
Jafari M., Hosseinzadeh A. 1997. Present status of afforestation in I.R. of Iran. Technical publication No.176-1997. Teheran. Research Institute of Forests and Rangelands.
Mobayen S., Tregubov V. 1970. La carte de la végétation naturelle de L´Iran. Bulletin No. 14 Faculté des Forêts et Pâturages. Université de Téhéran.
Forests and the forestry sector
Resources Owing to extremes of climate, the Islamic Republic of Iran is sparsely forested, with around 4.5 percent forest cover and 4.5 percent other wooded land. Most of Iran¿s 7.3 million hectares of forests are found in the north bordering the Caspian coastal plain and on the northern slopes of the Alborz mountain range. The Zagros range in the west of the country also has significant areas of forest, though much of the Zagros has been converted to grazing land. Most of the forests are closed broadleaved deciduous forest, with the dominant species including Quercus castaneifolia and Carpinus spp. At high elevations Juniperus spp. forest is common. Some of the forests have been destroyed or severely degraded. The main factors in this destructive trend are overgrazing, clearcutting and conversion into rangelands, and exploitation for fuelwood. Industrial harvesting occurs only in the Caspian Forest. Because of the severe climatic conditions and forest degradation, forests in other regions are not exploited for industrial wood production. Commercial production in these forests is limited to non-wood forest products, which include natural colorants and dyes, henna, aromatic plants and essential oils, honey, pistachios, walnuts, gum and medicinal plants. Around 60 percent of Iran is arid desert or semi-desert, where vegetation is primarily sparse Acacia and Prosopis scrub.
Iran has an extensive conservation network comprising seven national parks and around 60 other protected areas. These encompass approximately 12 percent of the country¿s forests.
Since 1965, the Forestry and Range Organization has undertaken a number of programmes to establish plantations in the vicinity of large towns as green belts and forest parks. In the early 1980s a new programme was launched for tree planting in irrigated and non-irrigated areas. The aim of these plantations is to meet local needs for timber and environmental protection. An area of about 253 000 ha was planted during the period 1989 to 1992, during the first five-year socio-economic plan. By 2000, the total planted area reached almost 2.3 million hectares.
The government of Iran provides free seedlings to landowners to promote tree planting.
The shortage of adequate water resources is a major constraint to plantation development in arid zones of the country. The cost of site preparation is high and establishment of irrigation facilities is very expensive.
Products
The majority of Iran¿s industrial roundwood production is used for agricultural purposes such as posts and poles. Forest industries in Iran produce sawnwood and wood-based panels, as well as pulp and paper from hardwood species. Moderate volumes of forest products, mainly paper, are imported. Modest quantities of wood are burned as fuel.
Forestry policy, institutions and major programmes
The economic role of forests became important in the nineteenth century when the exploitation of the northern forests of the country, mainly for timber for export, was transferred to foreign contractors. In addition, before the nationalization of the forests in 1962 some landowners exploited their own forest lands. Although the High Council for Forest, Range and Soil was established in 1951 and forest management regulations were ratified in 1958, forest areas continued to be exploited by foreign enterprises and forest owners.
In 1959, the first forest management plan was prepared and implemented in the Caspian area. Forestry plans covered only limited areas until 1963, when nationalization of forests led to the preparation of forestry and exploitation plans on a large scale. Multiple-use forestry plans are now based on non-wood products with wood production exclusively to cover local needs for fuelwood and fine wood industry. Fisheries, apiculture, animal husbandry and fodder production are integrated in forestry planning in suitable areas.
Institutions
In Iran, forestry is in the hands of the Forestry and Range Organization, under the Ministry of Agriculture Jihad-e-Sazandegi. The Forestry and Range Organization gives special importance to rural development and people¿s involvement in harvesting and afforestation activities.
The main administrative and management body for conservation and protected areas is the Department of the Environment, which was established in March 1972. Its responsibilities include the conservation and enhancement of wildlife resources and the prevention of pollution. It also puts forward regulations on habitat management. Existing capacity for the enforcement of conservation legislation and regulations, however, is limited.
The Department of the Environment is divided into a series of divisions dealing with different environmental matters; of these, the Division of Parks and Wildlife is the main body undertaking protected area management. The division prepares recommendations for the establishment of reserves or changes in reserve classification. Before they are presented to the High Council of the Environment for approval, they are reviewed by all appropriate divisions of the Department of the Environment so that all government organizations with jurisdiction over lands proposed for protection have an opportunity to assess the impact on resources administered by their organizations.
Control of grazing and forestry within reserves is determined by regulations adopted jointly by the Forest and Range Organization and the Department of the Environment.
Research is conducted in ministries and universities. Almost all ministries have their own research institutes and centres. The Faculty of Natural Resources, University of Tehran includes the Department of Forestry and of Forest Economics which conducts studies relating to forest status and protection.
Policies
Forest protection is one of the most important objectives of the Forest and Range Organization. The government has a policy to engage local people in all forest activities, especially in forest protection, including fire prevention. Forest fires in Iran are generally caused by humans.
The main objectives of Forest Policy in the Islamic Republic of Iran are:
· preparing integrated plans for all natural resources of the country and applying proper exploitation systems based on modern technology suitable for the sustainability of natural resources and increasing timber and fodder production for economical exploitation;
· preparing and implementing agrosylvipastoral plans, especially in the Zagrosian vegetation region;
· establishing wood industry units to create income-generating possibilities for forest dwellers;
· establishing forest cooperative societies to manage, preserve, rehabilitate, develop and exploit the forest in collaboration with local people and within the conditions and limitations prescribed in the developed plans;
· procuring technical facilities and required investment to develop road networks;
· industrializing the traditional animal husbandry systems in the northern forests by creating income-generating possibilities and procuring animal husbandry facilities in marginal areas outside forested lands;
· procuring the required equipment and inputs to implement the country¿s natural resources development plans;
· improving timber production through mechanization and modern technology, and decreasing waste;
· procuring the required facilities to replace fuelwood by other suitable kinds of fuel;
· determining rational ways of exploiting forest by-products to supply local needs and export the excess materials;
· extending agroforestry, the plantation of multiple-use wood species and the plantation of fast-growing tree species to meet timber needs through short and medium rotations;
· preserving rare forest communities and species as national reserves;
· promotion of State, private and cooperative investment in developing, rehabilitating and utilizing all touristic areas and landscapes of the country;
· promoting training and extension programmes and awareness raising about the importance of natural resources preservation and rehabilitation. Local cooperatives have recently undertaken the implementation of forestry management plans, which helps to prevent conversion of forest lands into agricultural lands and to improve rural people¿s livelihoods. Since 1986, 18 plans covering 130 000 ha have been transferred to 18 cooperatives with more than 5 000 members.
Legislation
Constitutional Act No. 50 states that all citizens are required to honour the conservation of nature and natural resources. The first wildlife reserves were established in 1927. In 1956 the Game Council was created with a policy to set up hunting centres for the protection of endangered species and the control of hunting. In 1967, the Game and Fish Department was empowered by law to declare certain areas for the protection of flora and fauna. The Environmental Protection and Enhancement Act, 1974 identifies four categories of protected natural areas: national park, wildlife refuge, protected area and national nature monument. The Law of Protection and Exploitation of Forest and Range, enacted in 1967, includes specific legislation relating to areas which may be declared as forest parks. They are administered by the Forestry and Range Organization and are maintained as parks designated primarily for recreation, although they often include important representatives of unique woodland stand types.
Geographic description
The designations employed and the presentation of material in this publication do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries.
Map source: Global Forest Resources Assessment 2000, base map: ESRI
The Islamic Republic of Iran is located in south-western Asia and has an area of about 1 633 190 km2. It is bordered on the north by Armenia, Azerbaijan, Turkmenistan, and the Caspian Sea; on the east by Afghanistan and Pakistan; on the south by the Gulf of Oman, the Strait of Hormuz, and the Persian Gulf; and on the west by Iraq and Turkey.
Iran is a land of diverse topography, ranging from high, snow-capped mountains to fertile valleys to barren deserts. The centre of the country is a high (about 1 200 m above sea level) plateau, ringed by mountain chains. Much of the plateau consists of desert, the Dasht-e Kavir, covered mainly with salt, and the Dasht-e Lut, covered largely with sand and rocks.
In the north, to the south of the Caspian Sea, are the Elburz Mountains, forming a barrier between the low Caspian coast and the interior. Mount Damavand rises to 5 604 m, forming Iran´s highest peak. Prevailing winds from the north-west bring plentiful moisture to the Caspian coast and the northern slopes of the mountains.
The Zagros Mountains extend to the south-east from Turkey and Azerbaijan along the country´s western border to the Persian Gulf. Smaller mountain ranges lie along the Gulf of Oman and the borders with Afghanistan and Pakistan. The Khuzistan Plain lies at the north end of the Persian Gulf, between the border of Iraq and the Zagros Mountains.
Iran´s climate is varied due to its topography. The area along the Persian Gulf and the Gulf of Oman can be extremely hot and humid with average summer temperatures up to 35° C. The central highland, because of its elevation, is temperate but extremely arid. Tehran´s average temperature ranges from -3° to 7° C in January and 22° to 37° C in July.
The Elburz Mountains can be very cold, with temperatures occasionally falling as low as -9° C. The Caspian Sea coast, on the other hand, is mild with temperatures seldom above 32° C or below freezing.
Most of the Interior Plateau has a very dry climate. Teheran, which lies at the foot of the Elburz Mountains, receives about 250 mm of rain a year, but the deserts to the south and east average only about 50 mm of rainfall yearly. Abadan, on the Persian Gulf, receives less than 200 mm. The Caspian coast is the one area receives abundant rainfall, averaging 1 000 mm a year.
Ecological zones
The map below shows the ecological zones, as shown on the FAO global map of ecological zones produced as part of the FRA 2000. Please refer to FRA Working Paper 20 for further information on the Global Ecological Zone map.
|
|
|
The designations employed and the presentation of material in this publication do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries.
Map source: Global Forest Resources Assessment 2000, base map: ESRI
Forest area statistics
|
Extent of forest and other wooded land |
||||
|
FRA 2005 categories |
Area (1000 hectares) |
| ||
|
1990 |
2000 |
2005 |
| |
|
Forest |
11,075 |
11,075 |
11,075 |
|
|
Other wooded land |
5,340 |
5,340 |
5,340 |
|
|
Forest and other wooded land |
16,415 |
16,415 |
16,415 |
|
|
Other land |
147,205 |
147,205 |
147,205 |
|
|
...of which with tree cover |
83 |
83 |
83 |
|
|
Total land area |
163,620 |
163,620 |
163,620 |
|
|
Inland water bodies |
1,200 |
1,200 |
1,200 |
|
|
Total area of country |
164,820 |
164,820 |
164,820 |
|
Data source: FAO, Global Forest Resources Assessment 2005.
|
Characteristics of forest and other wooded land |
|||||||
|
FRA 2005 categories |
Area (1000 hectares) |
| |||||
|
Forest |
Other wooded land |
| |||||
|
1990 |
2000 |
2005 |
1990 |
2000 |
2005 |
| |
|
Primary |
200 |
200 |
200 |
- |
- |
- |
|
|
Modified natural |
10,031 |
10,031 |
10,031 |
5,340 |
5,340 |
5,340 |
|
|
Semi-natural |
228 |
228 |
228 |
- |
- |
- |
|
|
Productive plantation |
616 |
616 |
616 |
- |
- |
- |
|
|
Protective plantation |
- |
- |
- |
- |
- |
- |
|
|
Total |
11,075 |
11,075 |
11,075 |
5,340 |
5,340 |
5,340 |
|
Data source: FAO, Global Forest Resources Assessment 2005.
Growing stock
|
Growing stock in forest and other wooded land |
|||||||
|
FRA 2005 categories |
Volume (million cubic meters over bark) |
| |||||
|
Forest |
Other wooded land |
| |||||
|
1990 |
2000 |
2005 |
1990 |
2000 |
2005 |
| |
|
Growing stock in forest and other wooded land |
516 |
517 |
527 |
- |
- |
- |
|
|
Commercial growing stock |
405 |
407 |
416 |
- |
- |
- |
|
Data source: FAO, Global Forest Resources Assessment 2005.
|
Biomass stock in forest and other wooded land |
|||||||
|
FRA 2005 categories |
Biomass (million metric tonnes oven-dry weight) |
| |||||
|
Forest |
Other wooded land |
| |||||
|
1990 |
2000 |
2005 |
1990 |
2000 |
2005 |
| |
|
Above-ground biomass |
505 |
507 |
516 |
- |
- |
- |
|
|
Below-ground biomass |
150 |
150 |
153 |
- |
- |
- |
|
|
Total living biomass |
655 |
657 |
669 |
- |
- |
- |
|
|
Dead wood |
92 |
92 |
94 |
- |
- |
- |
|
|
Total |
747 |
749 |
763 |
- |
- |
- |
|
Data source: FAO, Global Forest Resources Assessment 2005.
|
Carbon stock in forest and other wooded land |
|||||||
|
FRA 2005 categories |
Carbon (million metric tonnes) |
| |||||
|
Forest |
Other wooded land |
| |||||
|
1990 |
2000 |
2005 |
1990 |
2000 |
2005 |
| |
|
Carbon in above-ground biomass |
253 |
253 |
258 |
- |
- |
- |
|
|
Carbon in below-ground biomass |
74 |
75 |
76 |
- |
- |
- |
|
|
Carbon in living biomass |
327 |
328 |
334 |
- |
- |
- |
|
|
Carbon in dead wood |
46 |
46 |
47 |
- |
- |
- |
|
|
Carbon in litter |
- |
- |
- |
- |
- |
- |
|
|
Carbon in dead wood and litter |
46 |
46 |
47 |
- |
- |
- |
|
|
Soil carbon |
- |
- |
- |
- |
- |
- |
|
|
Total |
373 |
374 |
381 |
- |
- |
- |
|
Data source: FAO, Global Forest Resources Assessment 2005.
|
Composition of growing stock |
|||||
|
Rank |
Common name |
Scientific name |
Growing stock in Forests (million cubic meters) |
| |
|
1990 |
2000 |
| |||
|
1st |
- |
Carpinus betulus |
126 |
125 |
|
|
2nd |
- |
Fagus orientalis |
132 |
123 |
|
|
3rd |
- |
Alnus sp. |
31 |
36 |
|
|
4th |
- |
Quercus castaneafolia |
34 |
36 |
|
|
5th |
- |
Acer sp. |
30 |
27 |
|
|
6th |
- |
Pavotia persica |
16 |
21 |
|
|
7th |
- |
Tillia sp |
11 |
11 |
|
|
8th |
- |
Diospyrus lotus |
6 |
10 |
|
|
9th |
- |
Fraxinus sp. |
1 |
1 |
|
|
10th |
- |
- |
- |
- |
|
|
Remaining |
|
|
17 |
16 |
|
|
Total |
|
|
405 |
407 |
|
Data source: FAO, Global Forest Resources Assessment 2005.
Description of plantation resources
Introduction
In the last 25 years, programmes were established to plant irrigated and non-irrigated areas to meet local needs for timber and environmental protection. By the year 1999, the total planted area reached 2 221 100 ha. The main purposes are to supply wood for forest industry and to minimize impacts on the natural forests of the country (Mohammad, 1999).
Development of forest plantations
Since 1965, the Forest and Range Organization has undertaken a number of programmes to establish plantations in the vicinity of large towns as green belts and forest parks. Before the mid 1970s there was practically no experience in plantation establishment.
In the early 1980s a new programme of tree planting was launched. An area of 252 829 ha was planted during the period 1989-1992 during the first five-year socio-economic plan. By 1994, it was unofficially estimated that there were more than 466 197 ha of plantations (Jafari and Hossinzadeh, 1997).
The government of Iran provides free seedlings to landowners to promote tree planting.
Species composition
The species planted are generally limited to indigenous or well-established exotic species such as Acer negundo, Cupressus arizonica, Fraxinus rotundifolia, Pinus eldarica, Robinia pseudoacacia, Eucalyptus camaldulensis, Ailanthus glandulosa, Prosopis juliflora, Albizzia lebbek, Terminalia spp., Melia indica, Parkinsonia aculeata and Ficus benghalensis for the southern part of Iran.
Species such as Pinus nigra, Pinus sylvestris, P. brutia, P. taeda, P. elliottii, P. pinea, Cryptomeria japonica, Cedrus spp., Cupressus arizonica, Abies nordmanniana, Larix europea, Taxodium distichum and Pseudotsuga spp. are used in the Caspian zone. Haloxylon spp., Tamarix spp. and Zygophyllum spp. are planted in the desert zone (Jafari and Hossinzadeh, 1997).
Trend
The government has various assistance programmes to promote private plantations. For example, the government provides free seedlings to encourage planting. (Jafari and Hossinzadeh, 1997)
Issues
The shortage of adequate water resources is a major constraint in arid zones of the country. The cost of site preparation is high and establishment of irrigation facilities is very expensive.
References
Jafari, M. & Hossinzadeh, A. 1997. Present status of afforestation in I.R. of Iran. Cited from four articles on forests. Technical Publication No. 176. Research Institute of Forests and Rangeland, Iran.
Mirsadeghi, M. A.; Biglarbeigi, B.; Zamani, J. A.; Rastaghi, M. E. & Majid Saifollahian. 1999. Forest data of Iran, FRA 2000 country report. Teheran. Forest and Range Organization.
Forest health
|
Disturbances affecting forest and other wooded land |
|||||
|
FRA 2005 categories |
Average annual area affected (1000 hectares) |
| |||
|
Forest |
Other wooded land |
| |||
|
1990 |
2000 |
1990 |
2000 |
| |
|
Disturbance by fire |
10 |
6 |
- |
- |
|
|
Disturbance by insects |
111 |
220 |
- |
- |
|
|
Disturbance by diseases |
- |
- |
- |
- |
|
|
Other disturbances |
- |
- |
- |
- |
|
Data source: FAO, Global Forest Resources Assessment 2005.
Management
This site contains information on the organisation, content and status of strategic planning processes in forestry for countries throughout the world.
National forest programmes (nfps) are recognised internationally as effective instruments for planning, implementing and monitoring forestry strategies that are inclusive and participatory. This site enables the user to compare and contrast progress and approach in different countries and to appreciate and support these initiatives
The content of the site is maintained by the countries themselves in some instances, and by the FAO where no country correspondent is currently available. In these cases it is compiled from various secondary sources such as country reports to international conventions
HOW TO NAVIGATE THIS SITE: First select the country of interest from the dropdown box where it says "select a country". Then click an item on the left hand menu to view the content for that country
Iran, Islamic Rep of
Chronology of the nfp process
Following UNCED in June 1992, the National Committee on Sustainable Development (NCSD) was formed in 1996 to follow up and achieve UNCED main objectives.
In 1993, formulation of a National Strategy for Environment and Sustainable Development (NSE) started under a UNDP and World Bank funded Capacity 21. national reports were prepared on 20 cross-sectoral environmental issues and a NSE framework was fashioned from these reports. The NSE is linked to the National Development Plan (NDP), which is prepared every five years and delineates Iran's principal environment development objectives, establishing linkages with cross-sectoral plans. The environmental objectives of the second NDP (prepared in 1994) recommended: coordination of environmental activities; development and amendments to environmental norms, standards, criteria and legislation, as well as adjustments to the structure and mandate of the department of Environment (DOE). In keeping with these objectives, Iran has decided to formulate a national Biodiversity Strategy and Plan (BSAP) as a priority action to complement and achieve better linkages with the Second National development Plan, NSE and other cross-sectoral plans (GEF, 1997).
The Forest, Range and Watershed Management Organization (FRWO) is responsible for the formulation of the nfp, as emphasized by the National Committee on Sustainable Development. In 1996, FRWO launched the forest management plan for sub-humid forests.
Since 1997, the following economic and policy instruments have been applied to attain sustainable forest management:
- Policy instruments
- Support participatory process in planning, implementation, monitoring and evaluation of forestry plans
- Support and encourage private sector, local communities and NGOs involvement in forestry related activities
- Promote cross- sectoral and international cooperation
- Delineate and specify the boundaries of private forest and range lands
- Organize training programmes and provide technical services to participants
- · Economic instruments
- Provide low-interest loans for plantation programmes particularly, multi purpose tree species
- Provide low-interest loans for forest-related cooperatives
- Eliminate tariffs on wood import
- Entrust low price lands for plantation
The Enabling Activity Project known as "The National Biodiversity Strategy and Action Plan" started in 1998 in collaboration with UNDP, GEF and IUCN. In 2001 four strategies were ratified as follows:
- Promotion of the public awareness and participation
- Formation of biodiversity information systems
- Sustainable use of biodiversity resources
- Integrated conservation of biodiversity
The National Action Programme to Combat Desertification of I.R. of Iran was finalized in 2004.
Formulation of NFP requires capacity building. Recently, many actions have been taken to combat deforestation and forest degradation including transfer of livestock from forests and resettlement of the forest dwellers, forest extension, and rehabilitation of degraded forests as well as replacement of fossil fuels with fuel woods parallel to measures taken to update and enact forest laws (I.R. of Iran, 2005).
Iran, Islamic Rep of
Mechanisms and procedures
In 1999 the open-ended international expert meeting on "Special Needs and Requirements of Low Forest Cover Countries and Unique Types of Forest" was held in Tehran (4 to 8 October). The meeting, a government-led initiative in support of the programme of work of the IFF, was attended by 77 participants from 39 countries and 6 international and bilateral organizations and NGOs (I.R. of Iran, 2005).
Stakeholders involvement
Forest management plans are being implemented by the government, cooperatives and private sector. At present forest and rangeland protection is mainly carried out with the collaboration of local communities.
Private sector involvement in planning, formulation and implementation projects is stipulated by law. Local communities, NGOs and indigenous people involve formally in the process of formulating, planning and implementing forest management plans and forest policy (I.R. of Iran, 2005).
Use of technology
In formulation of forestry plans modern technologies such as GIS are being used in cooperation with the private sector. In fact, the forest policy aims at capacity building of the private sector, local communities and NGOs (I.R. of Iran, 2005).
Awareness raising
Action has been made to raise the awareness of public and policy-makers on forest resources and hazard forest degradation and deforestation in collaboration with other sectors.
In this regard, a number of publications and documentary films funded by FRWO were produced. TV and radio also play a major role in this direction. The Ministry of Education has included subject matters in the curricula to further acquaint students with environmental issues and consequences of forest degradation.
The Bureau of Extension and Public Participation of FRWO also encourages NGOs to play an active role in this regard. The Cabinet and the Parliament support for forest protection illustrate the public awareness towards forest issues (I.R. of Iran, 2005).
Reforestation and restoration initiatives
Plantations have established and managed to meet local needs. In recent years, the areas forested to combat desertification (sand dune fixation) are being managed and their goods and services are utilized. Since 2003, formulation of management plan for these plantations have begun and implemented with the collaboration of local communities and private sector.
In the Caspian region forest policy aims at forest promotion. Therefore, parts of the woodlands in mountainous areas which are converted into summer ranges are being afforested each year. Forest promotion of the Caspian region is of high importance because of wood production, protection of biological diversity and soil and water conservation in watershed basins. The programme was commenced in 2001. Iran is among wood importer countries which has enhanced import volume to support its forests.
FRWO has formulated and implemented a master plan to promote forest resources using single or multipurpose species. To produce wood and non-wood products, the woody species as well as multipurpose trees were planted in private lands as well as state-owned lands which were entrusted to private sector with bank loan. Disadvantages of the plan were shortage of irrigation for new plantations and late-yielding period compared with farming. The main objective of the plan is to support sustainable forest management at national level through meeting the needs for forest goods and services (I.R. of Iran, 2005)
Iran, Islamic Rep of
Main constraints
- Insufficient data and information on the extent of traditional use of forest goods and services by local communities.
- In forestry services valuation, there are some problems with methods of valuation due to their limited application.
Iran, Islamic Rep of
Future actions
- Expansion of forest resources in the private farm lands is not so successful in comparison with farming and crop production. To this end, it is necessary to provide incentives such as bank loans, land transfer and even training and extension.
- The current policy can have positive effects only through involvement of all the stakeholders who provide themselves parts of investment and protection.
Forest policy
The national forest policy and theirs main achievements are hereby pointed out, together with the draft or official policy statement, when available. Two specific sub-sections on forest tenure and financial issues provide a more complete vision on the socio-economic context influencing the forest policy.
Iran, Islamic Rep of
Main achivements
Background
The economic role of forests became important in the nineteenth century when the exploitation of the northern forests of the country, mainly for timber for export, was transferred to foreign contractors. In addition, before the nationalization of the forests in 1962 some landowners exploited their own forest lands. Although the High Council for Forest, Range and Soil was established in 1951 and forest management regulations were ratified in 1958, forest areas continued to be exploited by foreign enterprises and forest owners.
In 1959 the first forest management plan was prepared and implemented in the Caspian area. Forestry plans covered only limited areas until 1963, when nationalization of forests led to the preparation of forestry and exploitation plans on a large scale. Multiple-use forestry plans are now based on non-wood products with wood production exclusively to cover local needs for fuelwood and fine wood industry. Fisheries, apiculture, animal husbandry and fodder production are integrated in forestry planning in suitable areas.
The forest policy
Since forests in Iran cover less than 10% of the total land area (LFCC), the main objective of the national forest policy is to protect forests in natural ecosystem. In the national forest policy and forest protection strategies, priority has been given to rehabilitation and sustainable forest management of environmentally critical areas.
The main objectives of the Forest Policy in the Islamic Republic of Iran are:
- preparing integrated plans for all natural resources of the country and applying proper exploitation systems based on modern technology suitable for the sustainability of natural resources and increasing timber and fodder production for economical exploitation;
- preparing and implementing agrosylvipastoral plans, especially in the Zagrosian vegetation region;
- establishing wood industry units to create income-generating possibilities for forest dwellers;
- establishing forest cooperative societies to manage, preserve, rehabilitate, develop and exploit the forest in collaboration with local people and within the conditions and limitations prescribed in the developed plans;
- procuring technical facilities and required investment to develop road networks;
- industrializing the traditional animal husbandry systems in the northern forests by creating income-generating possibilities and procuring animal husbandry facilities in marginal areas outside forested lands;
- procuring the required equipment and inputs to implement the country's natural resources development plans;
- improving timber production through mechanization and modern technology, and decreasing waste;
- procuring the required facilities to replace fuelwood by other suitable kinds of fuel;
- determining rational ways of exploiting forest by-products to supply local needs and export the excess materials;
- extending agroforestry, the plantation of multiple-use wood species and the plantation of fast-growing tree species to meet timber needs through short and medium rotations;
- preserving rare forest communities and species as national reserves;
- promotion of State, private and cooperative investment in developing, rehabilitating and utilizing all touristic areas and landscapes of the country;
- promoting training and extension programmes and awareness raising about the importance of natural resources preservation and rehabilitation.
In the formulation of forestry policies and programmes all relevant administrative sectors are involved. The new policy, adopted to promote forest resources, was developed in partnership with all stakeholders. Several cross-sectoral measures have taken with other organizations such as the Meteorological Organization, the Ministry of Energy, the Department of Environment and the agricultural sector.
Forest ecosystems play a special role in both the National Action Programme to Combat Desertification and the National Biodiversity Strategy and Action Plan developed by the I.R. of Iran (I.R. of Iran, 2005).
National Action Programme to Combat Desertification
The National Action Programme to Combat Desertification of I.R. of Iran was finalized in 2004. A National Committee (NCCD) was formed, chaired by Minister of Jihad - Agriculture and comprised of deputy ministers of various Ministries and concerned public organizations. The Committee is mandated to coordinate government organizations and institutes as well as to establish the macro policies for anti- desertification activities. The NAP framework consists of four pivots (I.R. of Iran, 2005):
- identification and control of the factors contributing to desertification;
- support for the sustainable use and management of natural resources through conservation and reclamation;
- promotion of sustainable livelihoods in affected areas through job creating, income generation and the improvement of socio-economic standards;
- strengthening the role of rural communities in terms of decision-making, planning, designing, implementation, monitoring and evaluation.
The National Biodiversity Strategy and Action Plan
The Enabling Activity Project known as "The National Biodiversity Strategy and Action Plan" started in 1998 in collaboration with UNDP, GEF and IUCN on the basis of the obligations related to CBD. The activities for identification of the natural resources in Iran have led to the preparation of a series of 28 reports, each assessed by members of the Steering Committee.
According to the approval of both the Steering Committee in February 2001 and the National Committee on Sustainable Development in May 2001, four strategies have been ratified as follows (I.R. of Iran, 2005):
- Promotion of the public awareness and participation
- Formation of bio diversity information systems
- Sustainable use of biodiversity resources
- Integrated conservation of biodiversity
Iran, Islamic Rep of
Forest, trees and land tenure
In 1962, the whole forests of the country became nationalized and are still owned by the government.
Forestry projects are carried out in the framework of forest management plans prepared, approved and supervised by FRWO on the basis of specific principles and guidelines. The existing principles and standards guarantee sustainable forestry at the area unit level.
Customary rights of the indigenous and local communities are recognized in all forestry projects and their involvement in the process of decision making is encouraged. Besides the land tenure right of the local communities is also officially recognized and respected by law.
Wood trade is undertaken and managed according to customs laws and regulations (I.R. of Iran, 2005).
Iran, Islamic Rep of
Forestry legislation
Constitutional Act No. 50 of 1979 states that "all citizens are required to honour the conservation of nature and natural resources".
The Law of Protection and Exploitation of Forest and Range, enacted in 1967, includes specific legislation relating to areas which may be declared as forest parks. They are administered by the Forestry and Range Organization and are maintained as parks designated primarily for recreation, although they often include important representatives of unique woodland stand types.
The Environmental Protection and Enhancement Act, 1974 identifies four categories of protected natural areas: national park, wildlife refuge, protected area and national nature monument. The first wildlife reserves were established in 1927. In 1956 the Game Council was created with a policy to set up hunting centres for the protection of endangered species and the control of hunting. In 1967, the Game and Fish Department was empowered by law to declare certain areas for the protection of flora and fauna.


