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ARMENIA
by Robert Tumanian |
| 1.
INTRODUCTION
Armenia is an ancient country. The ancestors of modern Armenians lived on the Armenian plateau over a vast territory, between Asia Minor and the Iranian upland. Human footprints detected in the area go back to the Old Stone Age. During the Palaeolithic period there was primitive farming on the plateau, and in the Neolithic and the early Bronze Age, animal husbandry developed. Armenia is one of the ancient centres of metal culture/industry; already in the 5th - 4th centuries BC there was copper working in Armenia. Between the 3rd and 2nd centuries BC stock-rearing became a major occupation. The tribes of the Armenian plateau unified to create unions like Uruatri, Nairi, Dayani, and others. Based on these unions the state of Urartu was created, which at the end of ninth eighth centuries BC considerably expanded its boundaries. In the seventh sixth centuries BC, in the valleys of the Armenian mountain ranges, crop production and viticulture were largely developed. On a Babylonian world map (fifth century BC) Armenia was included and in the second half of the second century the Armenian nationality was finally shaped. Being between the greatest conflicting powers of East and West (Persia, Rome, Arabic Caliphate, Byzantium and others) Armenia became an arena of incessant war-fare. It strove for independence for many centuries. In the fourth century BC the basis of the Armenian state was strengthened. Later Christianity was declared the state religion and Armenian national culture flourished. With the emergence of the Dynasty of Bagratids (tenth century) and the Armenian State of Kilikia (eleventh century) medieval society prospered, and the full flowering of its national attributes occurred. In the 12th century Armenia was divided between Turkey and Iran. In the course of the three succeeding centuries Armenians were involved in a liberation movement against the Turkish-Persian powers. At the beginning of the nineteenth century Eastern Armenia joined Russia. However a large part of its territory remained under the sovereignty/control of Turkey. On November 29, 1920 Armenia was declared a Soviet Socialist Republic. After the collapse of the Soviet Union in 1991 Armenia regained its independence. The majority of the population are Armenians. In addition there are Russians, Yezidis, Azeris, Georgians, Kurds, Greeks, Assyrians, Ukrainians, Jews and others. According to the World Factbook the July 2006 population was estimated at 2,976,372 with a growth rate of -0.19%. Geographical location Armenia is in the south of the Caucasus, latitude 380 51´ to 41o18´ North and longitude 43o29´ to 46o37´ East. It occupies the south-eastern part of the Armenian mountain range and the central part of the Small Caucasus. To the north it is bordered by the Republic of Georgia, to the east and south-west by the Republic of Azerbaijan, to the west by Turkey and to the south by Iran. The territory is divided into 37 regions, which after gaining independence in 1991, were regrouped into 10 regions, the so-called "marzes": Aragatsotn, Ararat, Armavir, Gegharkunik, Lori, Kotayk, Shirak, Syunik, Tavush and Vayots Dzor. The capital of the country is Yerevan. The total land area is 297, 000 sq km and it is 270 km wide and 279 km long. The total area of agricultural land is 1,391,377 ha, 494,689 ha of which are arable, 63,766 are perennial plantations, 138,907 ha are grasslands and 694,015 ha are pastures. Livestock. The total number of cattle in 2001 was 497,300 (Table 2) of which 264,900 were cows; also there were 540,000 small ruminants, 68,900 pigs and 11,400 horses. In 1998 some 462,000 tons of milk, about 86,000 tons of meat and 1,922 tons of wool were produced. This production was not sufficient for domestic needs and some products were imported from abroad (Iran, Turkey, India, United Arab Emirates, etc.). By 2004 livestock numbers were 565,800 cattle (including nearly 300,000 cows), 628,500 small ruminants, 85,400 pigs and 12,500 horses; production was 535,831 mt of fresh milk, 54,027 mt of meat and 1,200 mt of wool. Imports of meat and milk in 2004 had increased to 31,051.2 mt (total meat) and 53,962.5 mt (milk equivalents) respectively (Table 3). For full details of livestock numbers and imports see section 4. and
Tables 2 and 3. |
| 5.
THE PASTURE RESOURCE
The total grazing land area is 832,922 ha (see Table 4), of which grass lands occupy 138,904 ha and pastures 694,015 hectares. All the grasslands are of the mountain type. A great diversity of climatic conditions has created vertical transition of the vegetation. Pastures and grass lands are zonally allocated in semi-desert, steppe, steppe-meadow, post-forest, sub-alpine and alpine zones. Within each zone there are also azonal grazing lands (such as swamps with excessive moisture), their total area being about 8,700 ha. Predominant zonal types of grasslands are sub-alpine ones. They comprise about 37 percent of total grass land. Then come post-forest 23 percent, steppe-meadow 22 percent, etc. Predominant zonal types of pastures are again sub-alpine meadows. They occupy about 33 percent of the total pasture area. These are followed by steppe-meadows 20 percent, alpine 18 percent, post-forest 14 percent, steppe 11 percent and semi-desert 5 percent. The typological composition of grass lands and pastures is extremely diverse. It is conditioned by vertical zonality. The formation of natural mountain grasslands and their vertical location is influenced by the relief, the altitude and slope steepness, shape and exposure. A significant impact on changes in highland vegetation is caused by human interference: grazing, mowing, fodder production, irrigation and other practices have altered the nature of grassland and pasture vegetation to such an extent that currently there is no way to tell indigenous types from secondary ones. Numerous highland bio-climatic factors creating a vertical zonality for vegetation develop a great diversity of natural types of grass lands and pastures. Semi-desert range lands occupy the Ararat valley and the enclosed foothill plains. They can be encountered on a small scale in other regions as well at an altitude of 500 1,300 m. This zone is characterized by an insignificant precipitation level (200 300 mm), an uneven seasonal distribution of the latter, high temperatures in summer and low in winter; thus preventing the vegetation from fully exploiting the potential soil fertility. This results in the fact that semi-desert vegetation is not dense. The vegetation is represented by two major divergent ecological types: xerophytes (Chondrilla, Hordeum crinitum, Kochia, Euphorbia marschalliana, Astragalus, Bromus inermis, Androsace, Festuca sulcata, etc.) and ephemerals (Bromus tectorum, Bromus squarrosum). In areas, where highly saline soils solonetz and solonchak are formed, the vegetation is represented by halophytes. The basic vegetation is Artemisia, turf grasses (Bromus tectorum, Bromus squarrosum, Hordeum crinitum, Festuca sulcata), and ephemeroids (Poa bulbosa, Chenopodium humile, Carex stenophilla). Semi-deserts are mainly used for grazing and serve as spring-autumn and winter pastures for sheep. The total area is over 36,000 ha. Steppe lands occupy a substantial territory at altitudes between 1,000 to 1,500 m and sometimes up to 1,800 m. The relief of this zone is extremely varied: gentle slopes, plateaus, valleys, as well as steep and abrupt slopes can be encountered. The climate is typically dry and warm. Among steppe groups dry-steppe lands and genuine steppe can be identified. Turf grasses are predominant in the vegetation of dry steppes. Abundance of ephemerals in spring grass cover is a characteristic feature of dry-steppe groupings. The grass is typically low, sparse, of pasture type. As a rule the soil is very stony and compacted, less melkozem with low capacity, brown or chestnut. The total area of dry-steppe groupings comprises 22,100 ha. Grazing lands on indigenous steppes occupy extended territories at an altitude of 1,200 to 1,500 m sometimes up to 1,800 m. They appear on plateaux with well developed and high capacity melkozem soil, also on steep and slight slopes; this resulting in diverse and vari-coloured vegetation types. Steppe groupings are characterized by highly developed turf-formation processes, and extensive development of mixed grass and legumes; in spring, ephemerals are more or less abundant. Nevertheless turf grasses predominate, affecting the appearance of steppes at the end of summer and the beginning of winter. The total area of steppe groupings comprises about 77,100 ha. Steppe-meadows occupy considerable areas at altitudes between
1,500 1,800 m sometimes up to 2,200 m and more. The climate
of this zone is distinguished by a comparatively damp and less warm summer,
and more equal distribution of precipitation levels in the vegetation
period. In summer there is frequent hail. The frostfree period lasts for
4-4.5 months. Steppe-meadow vegetation creates a clearly defined zone
in almost all mountainous terrains. It is more vivid in southern-facing
slopes but it can also be encountered on slopes with other exposures.
Steppe meadows are particularly developed on slighter slopes, sometimes
they emerge on plateaus with almost flat relief. The total area of steppe-meadow
groupings is about 169,300 ha. Cleared-forest grazing lands are encountered predominantly under gentle relief, on flat and gently sloping areas, in regions distinguished by intersecting relief and often on large steep slopes. The grass cover is dense, with different tiers, comprising both meadow species (Rumex acetosa, Cephalaria tatarica, Agrostis vulgaris, Trifolium pratense, Trifolium ambiguum, Poa pratensis, Koeleria gracilis, Dactylis glomerata, Phleum pratense, etc.) and forest species (Vicia balansae, Deschampsia caespitosa, Arrhenatherum elatius, Agrostis planifolia, Agropyron caninum, Festuca gigantea, etc.). Meadow species are typically predominant. Sometimes meadow species are mixed with forest shrubs or grass. Forest trees: Quercus, Fagus, Carpinus, Tilia, Acer, Ulmus, Fraxinus, Carpinus orientalis, birch Betula, Pinus, Juniperus etc. Nevertheless, beech, oak and hornbeam can be met in almost all types of cleared -forest grasslands. The total area comprises 128,400 ha. Table 4. Zonal distribution of natural grazing lands of Armenia (,000 ha)
Sub-alpine grazing lands occupy a considerable territory and are the major lands in the country used as grasslands and pastures. Both are used in all seasons except winter. It should be mentioned that the tall vegetation (Phleum pratense, Dactylis glomerata, Festuca pratensis, etc.), are used in summer for hay, while the short ones (Festuca ovina, Bromus inermis, Koeleria, Taraxacum, etc.) are used from spring till autumn for grazing. The sub-alpine zone represents a clearly defined zone at an altitude of 2,200 2,800 m. The relief of this zone is diverse: slight and steep slopes, often abrupt ones can be encountered. The climate is montane, the average annual temperature fluctuates from 50 to 20 and below. Annual precipitation level is 800 900 mm. The highest level of rainfalls are observed in early summer and late spring. The vegetation is very rich and diverse which permits the distinction of a great number of diverse species of vegetation groupings. This results in the diversity of pasture land types used as grass lands and pastures. The species of all vegetation groups within the given zone are affected by human interference fodder production and grazing. This has resulted in the emergence and successful growth of many vegetation types, which are actually alien to this mountain range, and has made the diverse vegetation of this area even more complex. The composition by type of sub-alpine hay meadows is very rich; many vegetation groups comprise 120 130 and more species. The major turf-forming and the most predominant plants are grasses. The vegetation of sub-alpine hay meadows is typically rather tall. The soil cover is complete with a high level of sod. The total area is 277,800 ha. Alpine pastures occupy a substantial area and create a clearly defined zone in nearly all areas at altitudes of 2,700 to 3,500 m. The relief is diverse: along with vast valleys and highland plateaus, multiple steep slopes of various exposures, cliffs and parent rocks can be encountered. Vast areas on steep slopes are occupied by talus (stony scarps) and embankments. Typical alpine meadows expand only on slopes and plateaus covered by more or less melkozem soil of mountain meadow type. Alpine vegetation, due to the damp climatic conditions, is low and dense (although somewhat patchy in places) and this is why the upper melkozem layer of mountain meadow soil appears to be densely tied, bound by numerous clusters of roots and secondary tufts. There are few annuals in the alpine zone. Most perennials are distinguished by a fast growing rate. They manage to blossom and fruit in a very short vegetation period and having sprouted up they winter with green leaves. Considered from a floristic point of view alpine vegetation is comparatively poor in species, however it is rich in the groups composing it. This diversity is intensified by regular grazing. The latter has resulted in modification of the appearance of alpine meadows and in the emergence of secondary type vegetation. Because of characteristic features, alpine meadows are purely pasture. Grasses are the most prevailing plants. The height of the grass is low 20 to 25 cm for rich species. Soil cover is complete. The total area comprises 122,200 ha. The current state of pastures Pasture improvement and its proper utilization Cultural measures. A substantial area of pastures, especially in the forest zone is covered by low forest and shrubs. Often due to inadequate utilization tussocks appear. Shrubs and tussocks decrease the useful area, reduce the yield and complicate the grazing and movement of the livestock. Such pastures need to be brought into a proper cultural state: the shrubs cleared, and tussocks, stones and litter (the remnants of plants not eaten by animals remain and the following year they form a litter layer that impedes the reproduction of the plants) removed. The removal of stones can expand the useful area by more than 10 20 percent and can increase land productivity. However, the pastures on mountain slopes, gullies and washes should not be entirely cleaned up, since in such places shrubs and stones are protecting the slopes from erosion. Thus, on dry areas a complete removal of shrubs may undermine the water regime, and dry up the soil and the grass during the hot summer period. Pastures covered by tussocks often occupy large areas. The emergence of tussocks in pastures is caused by various factors, such as being trampled by livestock in the case of excessive grazing on a damp soil; the emergence of dense patterns of shrubs; the existence of shrews, etc. The size of tussocks is 25 40 cm and more, the length is 10 16 cm. It would be appropriate to destroy them separately, if the territory they occupy exceeds 30 percent of the terrain. In case it is more than that, then radical treatment is required. Each year the yield takes out a considerable amount of nutrients from the soil (nitrogen, phosphorus, potassium, calcium, etc.) and the latter is gradually impoverished. Along with this the grass yield is also reduced. Provided fertilizers were regularly applied, it would be possible to achieve a higher yield and to improve the vegetation in a short period of time. The best time for applying fertilizers is in early spring, when the soil contains a sufficient amount of moisture. One basic way to improve the vegetation and achieve better quality feed is the eradication of weeds. They grow quickly supplanting fodder grass and noticeably diminishing grass quality. Fertilization and the organization of adequate grazing schedules are very effective weed control measures. In certain cases it is possible to decrease greatly the amount of weeds by chemical weeding through herbicides. In certain situations the best treatment against intense infestation by the worse weeds is a deep ploughing and cleaning up of cut weeds. On thinned areas, in addition to the removal of tussocks, shrubs and stones, it is necessary to sow seeds of valuable meadow grass. A tangible effect can be achieved by sowing seeds picked from plants on the same plot. In order to get the highest quality fodder it is necessary to use many legumes while sowing, especially white clover (creeping) which is very common in all pasture zones. Pasture improvement measures can be highly effective if they are followed by further natural resource management practices. Natural resource management measures. Pastures and fodder are especially significant for the development of animal production. Due to the high proportion of animal feed derived from pastures the rational utilization of pastures is becoming an important issue. The role of pastures and pasture fodder is increasing due to the extension of the pasture period. In north-west and south-east Armenia it lasts for 7-8 and sometimes even 10-11 months. Considering the important role of pasture grazing, the problem of undertaking organizational and management measures acquires a special urgency. The adequate utilization of pastures and grasslands increases their productivity greatly. Livestock grazing also has tangible effects on soil and vegetation. Grazing is conducive to changes in the vegetation affecting the quantity and quality of species. In the case of inadequate utilization of pastures a number of less valuable species emerge, while fertility levels decline. It can be inferred from the above that the proper utilization of pastures will sharply decrease or eradicate the damage caused by livestock. Grazing time,duration, and the appropriate utilization of pastures are important. The establishment of proper grazing schedules, respecting the starting and closing times are of the utmost importance in their effect on pasture grass cover. If grazing takes place too early or too late, the soil may becomes impacted, thus impeding the further development of plants, affecting also the quality of the grass and soil fertility. This may result in their early degradation. Early grazing sharply impedes the normal process of accumulation and consumption of nutrients by the plants. However, grazing should not take place too late either since the fodder value of the grass declines with the age of the pasture. Cessation of grazing in autumn is also very important. In cases when pasture grazing is caried on late in the autumn the grass productivity may be affected in succeeding years. It would be appropriate to start spring grazing for the livestock 15 20 days after the plants start growing and to stop it 25 30 days before the end of the vegetation period. For the appropriate organization of livestock grazing it is necessary to be well aware of pasture capacity, i.e. to define how many head can be grazed per hectare of land in the course of the pasture grazing period. Further, the grazing time, appropriate pasture grazing techniques, the grazing schedule, pasture rotation, etc. are also very important in pasture utilization and management. |
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| 6. OPPORTUNITIES FOR IMPROVEMENT OF FODDER
RESOURCES
For the promotion of agricultural growth, the improvement and expansion of agricultural production and the efficient utilization of pastures and grasslands, it is necessary:
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7. RESEARCH AND DEVELOPMENT ORGANIZATIONS
AND PERSONNEL
Director Hrachik Hovsepyan. Priority research: Address: Isi- Le-Mulino 1str., Echmiadzin, Armavir region, RA Tel.: (374-031) 5-34-54 Director Hunan Khazaryan Priority research: Address; Isakov str.24, Yerevan, RA Tel.: (374-1) 77-88-90 Director Kim Abelyan Priority research: Address: Hubarashen 2, Yerevan, RA Tel.: (374-1) 47-34-00 Director Sergey Khazaryan Priority research: Address: Furmanov str.39a, Yerevan, RA Tel.: (374-1) 23-45-28 Director Rafik Harutyunyan Research activities: selection and introduction of new bee types and high honey quality Address: Aringe, Kotayk region, RA Tel.: (374-1) 62-66-52 Dean Arshaluys Tarverdyan Activities: Address: Teryan str.74, Yerevan, RA Tel.: (374-1) 52-45-41 Fax: (374-1) 151-930 E-mail: agacad@USDA.am |
8.
REFERENCES
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| 9.
CONTACTS Authors: The profile was prepared in May July 2001 by the Professor of the Armenian Academy of Agriculture Dr. Robert Tumanyan who will update it from time to time. He is a specialist in fodder production, particularly of hay meadows and pastures, on which he has been working for about 39 years. He has authored 38 scientific works on fodder production, pasture and grassland improvement. Address: Tigran Mets str.13, apt.5,Yerevan, Armenia 375010 E-mail: agacad@USDA.am The section on livestock raising and breeding was compiled by the Head of the Department of Private Livestock Breeding of the Armenian Academy of Agriculture, Prof. Shavik Nersesyan. He is an author of 75 scientific works on livestock breeding, particularly cattle breeding and horse-breeding in Armenia. Address: Arabkir str.21, apt.35, Yerevan, Armenia 375051 E-mail: agacad@USDA.am Translator: Karine Avagyan Address: Lvovyan 19str., apt.74, Yerevan, Armenia E-mail: cvagian@yahoo.com [The profile was edited by J.M. Suttie and S.G. Reynolds in September 2001 and slightly modified by S.G. Reynolds in October 2006] |