|Pays, régions, bassins fluviaux|
|Ressources en eau|
|Usages de l'eau|
|Irrigation et drainage|
|Ensembles de données|
|Cartes et données spatiales|
Info pour les médias
|Visualisations et infographies|
|ODD Cible 6.4|
|Year: 2008||Revision date: --||Revision type: --|
|Regional report:||Water Report 34, 2009: English or Arabic|
Armenia, with a total area of 29 800 km2, is a landlocked country in the Caucasus region bordered in the north by Georgia, in the east by Azerbaijan, in the southeast by the Islamic Republic of Iran, and in the southwest and west by Turkey. Until 1995, the country was divided into 37 districts. It is now divided into ten marzes (provinces) plus Yerevan, the capital city.
Armenia is a mountainous country, with 77 percent of its territory located at 1 000 to 2 500 m above sea level and with an average altitude of 1 850 m. The highest point is 4 095 m (Mount Aragats) and 42 percent of the area is unusable for habitation (MNR, 2005). The country has a complex combination of uplands, plateaus, river valleys, depressions, and limited land, water and forest resources, with unfavourable engineering-geological conditions in most of the area (high seismicity, abundance of geodynamic processes). The landform in the centre and north of the country consists of rocky high mountain ranges separating narrow fertile valleys. Towards the south are the broad, flat and fertile Ararat valleys along the left bank of the Araks River forming the border with Turkey. To the west and north of Mount Aragat and around Lake Sevan in the east, the landform is generally rolling with rocky outcrops. In the southeast, a few small irregular-shaped valleys are surrounded by high mountain ranges. Pastures dominate at higher altitudes. The country is divided into two major river basins, the Araks Basin in the southwest and the Kura Basin in the northeast, which converge farther downstream in Azerbaijan. The low-lying areas, such as the Ararat plains, have rich, deep soils, but at higher elevations and on steep slopes, soils tend to be shallow.
Agriculture is greatly influenced by the topography, most of the cultivated land lying within an altitude range of 600–2 500 m. The predominant agricultural soils are generally fertile and deep. The cultivable area is estimated at almost 1.4 million ha, which is 47 percent of the total area of the country. In 2005, the cultivated area was estimated at 555 000 ha, of which 495 000 ha were under annual crops and 60 000 ha under permanent crops (Table 1).
Armenia has a highland continental climate: hot summers and cold winters. The geographical location of the country and its complex mountainous relief have conditioned the diversity of natural conditions across the country. There are six climate zones ranging from dry subtropical to rigorous high mountainous. The average annual temperature is 5.5 °C. Summer in Armenia is moderate, with an average temperature in July of around 16-17 °C, but ranging from 24 to 26 °C in the Ararat Valley. Winters are quite cold; the average winter temperature in Armenia is almost –7 °C. Total annual precipitation is 592 mm. The driest regions are the Ararat Valley and the Meghri region, where the annual precipitation is 200–250 mm. The maximum precipitation is observed in high mountainous areas with more than 1 000 mm annually. The multiyear average for annual evaporation in Armenia is 10–11 million m3, equal to about 350 mm over the entire country (UNDP, 2006).
The total population is slightly more than 3 million (2005), of which about 36 percent is rural (Table 1). The population density is 101 inhabitants/km2. The annual demographic growth rate was estimated at –2.1 percent for the period 2000–2005. In 2006, 91 percent of the population had access to improved sanitation (96 and 81 percent in urban and rural areas, respectively). Access to improved drinking-water sources reached 96 percent (99 and 96 percent for urban and rural population respectively). It is estimated that about half of the population in Armenia lives below the poverty line. The rural population is less vulnerable because of its capacity to provide for basic foodstuffs on a more or less stable basis. The poorest communities in Armenia reside in the mountainous regions and the very poor are principally concentrated in the earthquake zone, in border regions or in regions with a low level of economic activity (FAO and MOA, 2002) More than 90 percent of households have access to an improved/not shared toilet facility (NSS and MOH, 2006).
During the Soviet era, Armenia experienced robust industrial and agricultural development despite its limited natural resources. It became one of the most industrialized republics, providing machinery, chemicals, electronics and software to Russia and other Soviet Republics. In return, Armenia received raw materials and energy.
In December 1988, a devastating earthquake struck Armenia, killing more than 25 000 people and destroying large areas of the industrial heartland. This was followed by the break-up of the Soviet Union in 1991 and the consequent loss of markets and largely subsidized energy. This further led to a rapid decline in industrial output and to high unemployment. By 1993 the Gross Domestic Product (GDP) had fallen by almost two-thirds. Since 1994, however, Armenia has been among the most reform-minded countries of the former Soviet Union. Factors that have contributed to economic growth include: reforms in the electricity sector; growth in exports in specific sectors, such as cut diamonds, metals, electricity, and processed food; housing construction, and a major programme of international assistance. However, the high levels of economic growth have not yet compensated for jobs lost because of downsizing or the closure of Soviet era enterprises (USAID, 2006).
In 2007, Armenia’s GDP was US$9.2 billion and agriculture accounted for 18 percent (Table 1), down from a share of 41 percent in 1994. Industry on the contrary increased its contribution to GDP between 2000 and 2007 from 35 to 44 percent. Just over 50 percent of the population, 1.5 million people – of whom 21 percent is female - is economically active (2005): 162 000 people, or 11 percent of the labour force, are employed in agriculture whereas in 1994 agriculture employed 15 percent of all workers.
In 2003, crops accounted for 55.8 percent and stock breeding 44.2 percent of agriculture compared with 49.4 and 50.6 percent respectively in 1990. Since the beginning of the transition period the grain sowing areas have expanded by more than 20 percent and areas under cultivated potato by about 40 percent. However, the areas under forage plants have decreased by more than 3 times. In 2004, the main agricultural products were cereals, potatoes, vegetables, forage plants and fruit, especially grapes, given the long tradition of viticulture and wine-making. Agriculture has played a very important role in the economy of the country although it depends heavily on irrigation - half the total cultivated area is currently irrigated.
At present, in the agricultural food products sector, there is a free economy system regulated by the market which includes more than 338 000 farms. More than 98 percent of gross agricultural production comes from the private sector. The contribution of the agriculture and food sectors to the Armenia’s international trade has changed considerably since the start of the transition: exports have shrunk while imports have surged. In recent years, there has been a visible and steady trend to sectoral development, but agriculture continues to be vulnerable, mainly because of the relative shortage of suitable land, the lack of sufficient water resources, the small size and detachment of farms formed as a result of land privatizations, the underdeveloped industrial market and social infrastructure, as well as because agriculture does not at present meet the requirements of a market economy.
An important objective of agricultural development is to ensure appropriate levels of food security for the urban and rural population. It is estimated that expenditure on food accounts for between 60 and 70 percent of households’ total consumption. It can be as high as 85 percent for the poorest quintile, while it is 57 percent for the richest quintile. In view of the high share of food expenditure in total consumption, an adequate level of food security for the population requires that food is provided at affordable and stable prices. Given that farmgate prices of agricultural products are low and unfavourable to farmers’ incomes, increasing food security for the population implies improving significantly the efficiency of the processing and marketing chains for agricultural products. This kind of improvement will be attained primarily through better organization of the markets, increased competition in processing and trade and increased safety of marketed products. Investments in market infrastructure need to be carefully assessed in order to avoid unnecessary costs that would increase retail food prices (FAO and MOA, 2002).
The internal renewable surface water resources are estimated at 3.948 km3/year and the internal renewable groundwater resources at 4.311 km3/year. The overlap between surface water and groundwater is estimated at 1.400 km3/year. This gives a total of 6.859 km3 of annual internal renewable water resources (IRWR) (Table 2).
The rivers in Armenia are tributaries of the main rivers of the southern Caucasus, namely the Araks and the Kura. About 76 percent of the total territory is part of the Araks basin and 24 percent of the Kura basin (UNDP/GEF, 2006). Total outflow is equal to the IRWR. The outflow to Georgia through the Debet River is estimated at about 0.89 km3/year and the outflow to Azerbaijan through the Agstay River at about 0.35 km3/year; both these rivers are located in the Kura basin. The total outflow to Azerbaijan through the Araks and its tributaries (Arpa, Vorotan, Vokhchi) is estimated at about 5.62 km3/year. The Araks River forms the border between Turkey and Armenia and further downstream, between the Islamic Republic of Iran and Armenia, it flows into Azerbaijan, joining the Kura River about 150 km before its mouth at the Caspian Sea. The border flow of the Akhuryan (with Turkey) is estimated at 1.03 km3/year and the Araks at 0.79 km3/year. Half of the border flow is accounted for in Armenia’s water balance, bringing the total actual renewable water resources to 7.769 km3/year.
The 14 sub-basins of the two main river basins (Kura and Araks) have been grouped into five basin management areas: Akhuryan, Northern, Sevan-Hrazdan, Ararat and Southern basins (USAID, 2006). About 9 500 rivers and streams with the total length of 23 000 km flow in Armenia. Out of that number 379 rivers are around 10–100 km long, and seven, namely the Akhuryan, Debet, Vorotan, Hrazdan, Aghstev, Arpa and Metsamor-Kasakh, are longer than 100 km. The annual distribution of river flow generated in the country by the 14 river basins and their characteristic features are presented in Table 3 (UNDP, 2006). Armenian rivers are typically of a mountainous nature with sharp seasonal variations, spring freshets and low water flow in summer.
Armenia has more than 100 small lakes, some of which regularly dry out in the dry season. The Sevan and Arpi lakes are the most important in terms of size and economic importance. The Hrazdan and Akhuryan rivers originate from these two lakes, the largest of which is Lake Sevan, located in the centre of the country. It lies at 1 900 m above sea level, which makes it a strategic source of energy and irrigation water. The level of the lake, originally with a surface area of about 1 414 km2 and 58 km3 of stored water, has fallen since the 1930s due to the lake’s increasing use for irrigation and domestic water supply. By 1972, its level had fallen by almost 19 m and its surface area had been reduced to 1 250 km2. At present, it covers an area of about 1 200 km2, has a volume of approximately 34 km3, and plays a central and important hydrological role in the country. It serves the densely populated Hrazdan river basin and the Ararat Valley where Yerevan, the capital, is situated. Through its regulated surface outflow into the Hrazdan River, the lake’s water provides a substantial amount of hydropower and irrigation to croplands in the Ararat Valley. The lake is also an important recreational, natural habitat and cultural resource for the Armenian population (MNP, 2005). Since 1960, two inter-basin transfer schemes were implemented to restore the ecology of the lake and its storage capacity as a strategic water reserve for multipurpose use. A 48 km tunnel was built from 1963 to 1982 to divert some 250 million m3 of water annually from the Arpa River to Lake Sevan. A similar project, to divert 165 million m3 of water annually from the upper Vorotan River to the Arpa River through a 22 km tunnel, was completed in 2004. In the last few years, the lake’s level has risen by about 2.7 m as a result of favourable meteorological conditions and improved management. Electricity generation at the Sevan-Hrazdan Cascade is currently tied to irrigation releases. During the last few years, irrigation releases have ranged from 120 to 150 million m3. The second most important lake is Lake Arpi. It is located in the western part of the Ashotsk depression at an altitude of 2 020 m above sea level. With the construction of a dam to solve irrigation problems, the lake became a reservoir.
Most of the reservoirs were constructed during the Soviet period. In 2004, some 83 reservoirs were operating in Armenia and total capacity was estimated at 1 399 million m3, of which approximately 1 350 million m3 was stored in reservoirs with a capacity of over 5 million m3 each. Most of the water is used for irrigation. Some reservoirs are used for hydropower, recreation, fisheries and environmental protection. In 1995, about 145 million m3 was used for municipal and industrial purposes. The largest reservoir is on the Akhuryan River, which forms the border with Turkey. It has a storage capacity of 525 million m3, is shared with Turkey, and provides water for the irrigation of about 30 000 ha in Armenia. In contrast, many small off-channel reservoirs in the southwest of Aragats (Talish, Talin, Kakavadzor, Bazmaberd, Katnakhpyur), which accumulate spring tide waters, have a capacity of only 10 000–50 000 m3 (UNDP, 2006).
Most river basins are transboundary and through a number of bilateral agreements Armenia assumes obligations related to the development and use of international waters. Armenia has an agreement with Turkey concerning the use of the Araks and Akhuryan rivers, according to which the water of these two transboundary rivers is divided equally between the two countries. Another agreement with Turkey concerns the joint use of the dam and the reservoir of the Akhuryan River. According to an agreement between the Islamic Republic of Iran and Armenia, the water of the Araks River is divided equally between them. Though these agreements were signed by the USSR, Armenia is considered a successor country, and consequently is required to fulfil any related obligations. There have been decrees issued and agreements signed between Armenia and Georgia concerning the Debet River. Corresponding decrees were passed between Armenia and Azerbaijan concerning the use of the water of the Arpa, Vorotan, Aghstay and Tavush rivers.
In 1998, Armenia ratified the agreement with Georgia on environmental protection according to which the governments pledged their cooperation in creating specifically protected areas within the transboundary ecosystems. The Ministry of Nature Protection (MNP) develops and implements international environmental projects, some of which are related to water issues. Part of the Caucasus Initiative, launched by the German Ministry of Cooperation and Development, involves the implementation of the “Ecoregional Nature Protection Programme for the Southern Caucasus”. The programme, covering the three Caucasus countries, is going to be implemented in the very near future and will facilitate the protection and sustainable use of water resources in the region.
In 2002, the Republic of Armenia Commission on Transboundary Water Resources was established, which is chaired by the Head of Water Resources Management Agency. This commission, together with corresponding commissions in neighbouring countries, dealt with issues related to transboundary water resources use and protection.
From 2000 to 2002, USAID, in collaboration with Development Alternatives, Inc. (DAI), implemented the South Caucasus Water Management project which has the aim of strengthening the cooperation among water-related agencies at the local, national and regional levels, to provide integrated water resources management. In parallel, between 2000 and 2006, the EU and the Technical Assistance Commonwealth of Independent States (TACIS) developed the Joint River Management Program on Monitoring and Assessment of Water Quality on Transboundary Rivers, aimed at the prevention, control and reduction of transboundary pollution. The program covers four basins, including the Kura River basin. In addition, regional organisations such as REC and the Eurasia Foundation, as well as numerous local foundations, promote national and regional activities in the field of water resources management and protection (UNDP, 2002). USAID also funded the national project for Sustainable Water Resources Management in Armenia.
From 2002 to 2007, NATO-OSCE developed the South Caucasus River Monitoring Project whose general objectives were “to establish the social and technical infrastructure for an international, cooperative, Transboundary River water quality and quantity monitoring, data sharing and watershed management system among the Republics of Armenia, Azerbaijan and Georgia.” (OSU, 2008).
The project Reducing Transboundary Degradation in the Kura-Araks River Basin, implemented by the UNDP Bratislava Regional Centre in collaboration with the GEF, has involved four of the basin countries - Armenia, Azerbaijan, Georgia and the Islamic Republic of Iran. The project preparation phase lasted 18 months and began in July 2005. It is co-funded by Sweden. The project aims to ensure that the quality and quantity of the water throughout the Kura-Araks river system meets the short and long-term needs of the ecosystem and the communities that rely upon this ecosystem. The project will achieve its objectives by fostering regional cooperation, increasing capacity to address water quality and quantity problems, demonstrating water quality/quantity improvements, initiating the required policy and legal reforms, identifying and preparing priority investments and developing sustainable management and financial arrangements.
There are currently no water treaties between the three South Caucasian countries, a condition directly related to the political situation in the region. Nagorno-Karabakh is one of the main obstacles, making it difficult for Azerbaijan and Armenia to sign a treaty even one relating only to water resource management (Berrin and Campana, 2008).
Since the mid-1980s, there has been a decrease in the total water withdrawal, mainly due to a decrease in agricultural and industrial water withdrawal. In fact, the reduction in water use has been accompanied by a remarkable improvement in surface water quality. In 2006, the total water withdrawal for agricultural, municipal and industrial purposes was 2 827 million m3, of which about 66 percent for agricultural purposes, 30 percent for municipal use and 4 percent for industrial purposes (Table 4 and Figure 1). Agricultural water withdrawal mainly refers to irrigation of crops. Works for the watering of pastures began in 1956, including providing water for cattle in the pasturing period. Sources of pasture watering are springs, mountain melted snow, and non-discharge water bodies (UNDP 2005). Surface water withdrawals represent 78 percent of the total water withdrawals (Figure 2).
In most of Armenia’s territory, it is possible to use groundwater for drinking needs without any additional treatment. Indeed, about 95 percent of the water used for drinking purposes comes from groundwater sources (MNP, 2003). Both surface water and underground springs are used for industrial water supply. Industrial water supply is provided by independently operating water supply systems as well as from the city drinking water supply network. For the past 10–15 years, the water requirements of industrial enterprises have significantly decreased due to the reduction of the activity of many enterprises. It should be mentioned that 40 percent of the industrial enterprises using water are located in Yerevan. The largest water-using industrial enterprise is the Armenian Nuclear Power Plant which uses about 35 million m3/year (UNDP, 2005). There are 35 high and middle capacity hydropower plants in Armenia, nine of which are the plants at the Vorotan and Hrazdan hydropower cascades. As a result of insufficient regulation of volumes, hydropower production is also subject to seasonal variations (MNP, 2005).
While the industrial sector is not considered a major water user, an important problem for this sector is the implementation of industrial wastewater removal and treatment. Most industrial facilities were never equipped individually because they had been connected to the public sewer network during the Soviet Era, and thus were able to access municipal wastewater treatment. Attention should therefore be paid to those industries that have resumed production and from which the wastewater generated is channelled to the municipal wastewater treatment system, where only the mechanical treatment step is currently being operated. Also, the industries that are not connected to a municipal sewerage system discharge their mostly untreated wastewater directly into a stream or river. In general, old industries that resume production are the most polluting.
The total quantity of wastewater produced in 2006 amounted to 363 million m3, of which 89 million m3 was treated.
Irrigation in Armenia started about 3 000 years ago. Clay pipes were used to transport water to orchards and fields and some are still intact. In the fourth century, the total irrigated area was estimated at about 100 000 ha, in 1920 it had dropped to 60 000 ha, and in 1990 it was 320 000 ha (UNDP, 2006). The actually irrigated area declined from more than 300 000 ha in 1985 to 176 000 ha at present. Major factors that have contributed to this decline are the widespread deterioration of the irrigation conveyance systems, high pumping costs, the disintegration of the former collective farms into many small private farms (with a size of 1 to 2 ha), and drainage problems, particularly in the Ararat Valley, where groundwater tables are shallow.
At present, the area equipped for full or partial control irrigation is estimated at almost 274 000 ha (Table 5). The reason for the decrease in recent years has been, on the one hand, the earthquake of 1988 that destroyed part of the area, and on the other, the difficult economic situation due to the transition period, that has made it difficult to keep or maintain the irrigation infrastructure. The major irrigation schemes are located on the left bank of the Araks River.
The irrigation systems of Armenia were mainly established during the Soviet period. The irrigation infrastructure includes 80 reservoirs (77 of which are used only for irrigation and 3 used for both irrigation and drinking water), together with more than 3 000 km of main and secondary canals, about 15 000 km of tertiary canals, over 400 small and large pumps, 1 276 tubewells, and 945 artesian wells. Eight major conveyance systems distribute irrigation water to some 150 000 ha, and minor systems cover the rest of the areas. The conveyance systems are served by main, branch and secondary canals/pipes. Three-quarters of the canals are lined with concrete or are pipes. The main water structures, together with the main and secondary canals, are under state ownership whereas the tertiary level irrigation system (the intra-community irrigation network) was transferred to community ownership with the establishment of the Local Self-Governments in 1997. Around 80 percent of the total irrigated land is irrigated through the main network operated by the “Vorogum-Jrar” Closed Joint Stock Company (CJSC), while the remaining 20 percent is irrigated through the community-owned networks (WB-IBRD, 2004).
Surface irrigation is practised on over 90 percent of the area equipped for irrigation and can be divided into four categories of irrigation: furrow, borderstrip, flooding or basin, and that using hydrants and flexible hose systems (Figure 3).
Flooding is used where soil depth does not permit the grading of either furrows or borderstrips. The water is let out over the land by cutting an irrigation head canal at intervals. In the case of irrigation using hydrants, the hydrants are generally spaced in a 50 x 50 m grid and discharge water directly onto the ground, from where it is distributed by any of the surface irrigation methods. Conveyance of water to the hydrant is by buried steel pipes, but may be by open canals further upstream. Sprinkler irrigation and localized irrigation are practised on the remaining area equipped for full or partial control irrigation.
Groundwater is used for irrigation on 19 percent of the equipped area (Figure 4). The remaining part is irrigated from surface water through reservoirs, river diversion or pumping in rivers.
The irrigation potential has been estimated at about 660 000 ha and 41 percent of this had been equipped for irrigation in 2006. Almost 71 percent of the irrigated area was occupied by annual crops. Cereals, mainly wheat, covered 20 percent, fodder 15 percent, potatoes 14 percent and vegetables 13 percent (Table 5 and Figure 5).
More than 80 percent of total crop production is produced under irrigation. The difference in productivity between irrigated and rainfed agriculture is estimated at about US$900 per hectare. Table 6 gives an illustration of estimated returns for irrigation water at the farmgate by main crop and agro-economic zone.
An analysis based on standardized farm models indicates that even without taking into account changing cropping patterns in response to the increased reliability of irrigation, a 30 percent increase in irrigated land for an average farm will generate sufficient incremental net income to lift a family out of poverty, providing that other sources of income remained unchanged. However, an analysis based on information collected from 54 Water Users’ Associations (WUAs) revealed that although irrigation in 2005 clearly improved in terms of reliability of supply, only 125 000 ha was actually irrigated out of the 228 000 ha equipped for the service. Three main problems explain this situation. First, the high cost of water supply in areas with predominantly pumping irrigation makes irrigation economically non-viable due to very inefficient pumping schemes. Second, water losses in secondary and tertiary canals are reported to be in the order of 40–50 percent, which effectively reduces the total irrigated area, since additional water supplies are unavailable in most cases for technical or/and economic reasons. Third, most of the pumping stations have very high levels of electricity consumption compared with their design parameters and high maintenance costs due to frequent service disruptions beyond what was designed.
Annual irrigation water demand begins to increase in late April, peaks in early July, and drops off in October. Nearly 40 percent of the irrigation area depends on high-lift pumping, with pumping lifts of more than 100 m. For the larger irrigation systems, losses may amount to 50 percent of the water intake. Information about actually irrigated lands is presented in Table 7, containing data provided by WUAs in 2005 on the demand for water for irrigation purposes.
There are pronounced differences between the communities with respect to share of irrigated land. In 2003, 24 percent of rural communities did not have access to irrigation, 5 percent had less than 20 percent of their total arable land under irrigation, 24 percent had between 20 and 80 percent under irrigation, while 47 percent had over 80 percent of their total arable land under irrigation (WB-IBRD, 2004). In 2006, small schemes (< 200 ha) covered 20 percent of total equipped area for irrigation, while large schemes (> 200 ha) covered 80 percent (Figure 6).
Crop budgets were prepared based on the monitoring and evaluation of WUAs in 2004 and prices were obtained through farm surveys. The country was divided into four agro-economic zones (valley, upland, high mountainous and subtropical), in three of which rainfed farming is possible. Composition of crops, yields, incomes per hectare by crop and by zone are presented in Table 8 and Table 9.
In 2006 drainage was practised on 34 457 ha, of which 7 729 ha of horizontal closed drainage, 26 408 ha of horizontal open drainage and 320 ha of vertical drainage. The part of the irrigated land that is waterlogged is 18 722 ha.
The most important institutions involved in water resources development and management are:
Reforms in the water sector have been initiated since the implementation of the World Bank-supported “Integrated Water Resources Management Project” in 1999–2000. The idea of river basin management was also proposed through the introduction of annual and perspective planning mechanisms for water resources. One of the most important steps towards reform in the water sector was the adoption of a new Water Code on 4 June 2002 and, in order to ensure its enforcement, 80 regulations have been adopted by the Government since 2002, which relate, among others, to the procedures for water use permit provisions, transparency and public participation in the decision-making processes, accessibility of information, establishment of the state water cadaster, formation of water resources monitoring, management of transboundary water resources. The Code also contains the idea of integrated river basin management, for which a methodology of developing integrated water basin management plans has been developed, making it possible to use economic tools for water resources management and cost recovery. In order to promote more efficient, targeted and decentralized management of water resources, five territorial divisions (Basin Management Organizations) have been established under the umbrella of the Water Resources Management Agency: Northern, Akhuryan, Araratian, Sevan-Hrazdan and Southern. The Law on “Fundamental Provisions of the National Water Policy” was adopted in 2005; this represents a forward-looking development concept for water resources and water systems’ strategic use and protection. Since 2005 the water basin management principle is being applied in the sector of water resources management. In addition to this, a law concerning the “National Water Programme” has been developed. This law is the main document for the prospective development of water resources and water systems management and protection. As a result of the above-mentioned legal and institutional reforms, Armenia is currently one of the leaders in the region in the sector of water resource management.
By law, local mayors are responsible for providing the water service within a municipality unless the water sources and facilities serve more than one municipality, in which case one of the five State-owned water companies provides the water service. In 2006, about 80 percent of the population was served by the State water companies. The remainder of the population is served by small municipal systems and numerous community-based organizations. The “Yrevan Djur” CJSC is the largest of the five State companies and provides water and sewer services to the city of Yerevan and 28 neighbouring villages, covering around 50 percent of the total population. It operates under a recently signed lease contract with a French water company. The next largest State water company is the Armenian Water and Sewerage Company (AWSC) which operates under the terms of a management contract with another French water company. AWSC provides service to roughly 22 percent of the population. The other three State water companies, Lori, Shirak and Nor Akunk are managed with significant input from foreign consultants under the terms of a financing agreement between the State and a German lending agency. At the beginning of 2006, the average monthly water bill for most residential customers in Armenia was less than US$2. The collection rate has been improving but is still less than desirable.
Hydropower accounts for 20 percent of electricity generation. The total installed hydropower generating capacity of Armenia is about 1 100 MW, of which 1 050 MW is operational. Almost 95 percent of this capacity is installed along two important hydropower cascades: the Sevan-Hrazdan Cascade and the Vorotan Cascade. Electricity generation at the Sevan-Hrazdan Cascade is tied to irrigation releases from Lake Sevan on the basis of an annual water allocation plan (USAID, 2006).
USAID designed the Programme for Institutional and Regulatory Strengthening of Water Management in Armenia (2004-2008) to provide technical assistance, training and equipment to improve water resource management and the regulation of the increasingly decentralized irrigation and municipal water sectors. The programme will lay the foundation for effective water resource management and planned investment in the Armenian drinking water, sewerage, and irrigation sectors and assist the Government and leading water sector agencies to enhance their effectiveness through initiatives based on international best practices adapted for the Armenian context.
Currently, the State funds about 50 percent of the annually assessed Operation and Maintenance (O&M) requirements of the water services for irrigation. For 2005, the O&M requirements were estimated to be US$16 million, with a contribution from the State budget of US$8 million, which essentially covers the electricity costs for operating the pumping stations. The irrigation tariffs that WUAs or other users pay to the Vorogum-Jrar differ by region and mode of water delivery (pumped or gravity) and are capped at approximately US$20/1 000 m3 or US$150/ha. Maintenance is still inadequate to sustain the irrigation systems due to an underestimation of the annual O&M requirements and lower than expected tariff collection rates. The real O&M costs may vary from US$5/1 000 m3 or US$40/ha for gravity schemes to more than US$50/1 000 m3 or US$400/ha for some high-lift pumped schemes. The latter costs are higher than the incremental income earned by many subsistence farmers as a result of irrigation and may range from US$200/ha to US$400/ha per year (USAID, 2006).
Investments, such as the recently approved grant of US$236 million from the US Millennium Challenge Corporation may go a long way toward stabilizing the irrigation subsector. The grant will support a five-year programme of strategic investments in irrigation and rural roads, aimed at increasing agricultural production. The grant will also fund the improvement of drainage facilities, the rehabilitation of irrigation infrastructure, the strengthening of the Vorogum-Jrar and WUAs, and a water-to-market project that will provide training and access to credit for farmers who want to make the transition to more profitable, market-oriented agricultural production (USAID, 2006).
As mentioned in the “Water management” section above, the legal and institutional structure of the water sector is based on the National Water Code adopted in 2002. The Water Code defines three major functions in the water sector: management of water resources, management of water systems, and regulation of water supply and wastewater services.
Most of the drinking water is provided by groundwater, which has high organoleptic properties and is very pure. Due to the poor state of the water supply networks, however, the risk of water contamination is high. Due to the lack of liquid and lime chlorine, and the electric power deficit, in most cases, water is supplied without chlorination. In many places sewage and drinking water supply networks are put together and at present the sewage system is in an emergency situation: 63 percent of the network is more than 20 years old and 22 percent requires immediate renewal. According to the data provided by the Ministry of Health, during 1984–1991, no infection outbreak episodes related to drinking water quality were recorded in Armenia. However, since 1992 such episodes have been periodically registered. During the 1999–2002 period, 18 outbreak episodes related to water pollution were recorded with the total number of 5 690 diseased persons (UNDP, 2005). In 2003, 21 839 incidents were recorded, 5 839 of which (26.7 percent) occurred in Yerevan.
Solonetzic soils, which are characterized by a tough, impermeable hardpan that may vary from 5 to 30 cm or more below the surface soils, are widespread. These soils are most of all exposed to the risk of irrigation-related salinization, mainly as a result of rising groundwater in the plains, where the majority of irrigated lands are located. In the Ararat plain, solonetzic soils cover about 10 percent of the area. In 2006, the part of the irrigated land that is salinized was 20 415 ha, of which 15 137 ha weakly salinized, 2 385 ha medium salinized, and 2 893 ha strongly salinized (MTA, 2007).
The malaria situation was stable in Armenia until 1994. In subsequent years, a downgrading of malaria prevention services and a weakening of the malaria surveillance system resulted in a steady increase in the number of malaria cases, reaching 1 156 by 1998. Over 98 percent of these cases were detected in the Masis district of the Ararat Valley, an area bordering Turkey. In recent years, owing to epidemic control interventions, the number of autochthonous malaria cases has continued to decrease, dropping to 8 in 2003. However, although numbers have been on the decline, the situation must be monitored closely, because of the existence of favourable conditions for malaria transmission. In 2003, Armenia redefined and adjusted the present malaria control strategy, objectives and approaches, bearing in mind the results achieved to date, the extent of the problem, and potential threats in the country (MTA, 2007).
To reduce the burden of high expenditure in the State budget for government bodies engaged in water resource management, steps have been taken to involve the private sector.
Within the framework of the Agricultural Sustainable Development Strategy, the main priorities in the development of crop production are an increase in crop yield and a reduction in expenses per production unit through the application of advanced agro-technologies.
Main and secondary canals with high water losses, the collector-drainage system in the Ararat valley, and the tertiary irrigation systems need rehabilitation. About half of the total amount of the Agreement (US$113 million), signed between US Government Millennium Challenge Corporation and Armenia, will be directed to solve the main problems in the irrigation sector.
The main directions in the development of the irrigation sector are as follows:
Armeniapedia. 2005. Lake Sevan. Available at www.armeniapedia.org.
Berrin, B and Campana, M. 2008. Conflict, Cooperation, and the New ‘Great Game’ in the Kura-Araks Basin of the South Caucasus.
Department of Statistics of the Republic of Armenia. 1995. Summarized data.
FAO. 1993. Irrigation sub-sector review and project identification report. FAO Investment Centre/ World Bank cooperative programme. Report No 79/93 CP - ARM 2. 66p. + 3 annexes.
FAO and Ministry of Agriculture of the Republic of Armenia (MOA). 2002. A Strategy for sustainable agricultural development.
Government of the Republic of Armenia. 2005. Proposal for Millennium Challenge Account (MCA) Assistance.
Hayjirnackhagits Institute. 1993. The program of utilization of water resources within the Republic of Armenia. Ministry of Food and Agriculture.
Ministry of Agriculture of the Republic of Armenia (MOA). 2005. Crop production. Available at www.minagro.am.
Ministry of Food and Agriculture of the Republic of Armenia. The annual reports of `Hayjirthyt' 1975, 1980, 1985, 1988, 1994, 1995.
Ministry of Nature Protection of the Republic of Armenia (MNP). 2005. Reducing tran-boundary degradation of the Kura-Aras River Basin. Available at www.mnpiac.am.
Ministry of Nature Protection of the Republic of Armenia (MNR). 2006. Cooperation. Available at www.mnpiac.am.
Ministry of Nature Protection of the Republic of Armenia(MNR)/UNECE. 2003. National report on the state of the environment in Armeniain 2002.
Ministry of Territorial Administration. 2007. The cadaster of meliorative conditions of irrigated and drained areas of the Republic of Armenia.
National Statistical Service of the Republic of Armenia (NSS) and the Armenian Ministry of Health (MOH). 2006. Armenia demographic and health survey 2005.
Oregon State University (OSU). 2008. South Caucasus River Monitoring Project.
PA Consulting Group/USAID. 2008. Program for institutional and regulatory strengthening of water management in Armenia (2004-2008). Available at www.paconsulting.am.
United Nations Environmental Programme (UNEP). 2002. Caucasus Environment Outlook (CEO).
UNDP. 2005. National objectives for integrated planning & management of the Kura-Aras River Basin.
UNDP. 2006. Irrigation and drainage. TDA Thematical report.
UNDP. 2006. Transboundary diagnostic analysis of water sector in Kura-Aras basin, Republic of Armenia.
UNDP/GEF. 2006. Reducing transboundary degradation in Kura-Araks Basin.
USAID. 2006. An introduction to the Armenia water sector.
World Bank. 1995. Armenia: the challenge of reform in the agricultural sector. A World Bank country study. Washington, D.C. 198 p.
World Bank-International Bank for Reconstruction and Development (WB-IBRD). 2004. Rural infrastructure in Armenia: Addressing GAPS in Service Delivery.
^ haut de page ^
|Citer comme suit: FAO. 2016. Site web AQUASTAT. Organisation des Nations Unies pour l'alimentation et l'agriculture. Site consulté le [aaaa/mm/jj].|
|© FAO, 2016Questions ou commentaires? email@example.com|
|Votre accès à AQUASTAT et l’utilisation de toute information ou donnée est soumis aux termes et conditions spécifiés dans le User Agreement.|