Introduction

Physical and Socio-economic Description of Armenia

The Biological Diversity of Armenia

Endemic, relict, rare and threatened species in Armenia

Agrobiodiversity and Species of Economic Importanc

Landscapes and Ecosystems of Armenia

Threats to, and Impacts on, Biodiversity in Armenia

Existing measures for biodiversity conservation

Existing capacity and programmes for conservation

Biodiversity Strategy for the Republic of Armenia

 

 
 
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Threats to, and Impacts on, Biodiversity in Armenia


While the importance of the biological resources of Armenia is clearly recognised, equally obvious are the threats to these resources. A variety of anthropogenic effects now threaten the plants, animals and ecosystems of Armenia, and increased population pressure is further increasing these impacts on biodiversity. Historically, low human population densities and regulated use of natural resources protected the balance of ecosystems. However, over the last 1000 years human impacts on the land have increased, mainly through deforestation and increased use of pastures. Such problems have intensified over recent years with unprecedented population growth and urbanization since 1920 (Table 6.1, 6.2). The rate of habitat modernization parallels those in Western countries, and exceeds those in the neighbouring countries (Turkey, Iran, Georgia and Azerbaijan). Even the important mountain areas of Armenia are suffering increased anthropogenic pressures.



Table 6.1 Increases in population and human impacts between 1920 and 1990.

Parameter
Factor of increase
Population
5-fold
Urban population
26-fold
Urban spread
14-fold
Industrial districts and centres
30-fold
Irrigated land area
3-fold
Cultivated land area
1.5-fold
Areas under construction (buildings, roads, streets, etc)
20-fold

Table 6.2. Some parameters of current population and human pressures in Armenia

Parameter
Total
Density (average)
Population
3.8 million
232 persons/km2
Populated areas
980 settlements
6 settlements/10km2
Road (rail and car) network
14 thousand km
0.85km/km2
The biological resources of Armenia have undergone permanent change as a result of both internal and external factors. The most important threats to Armenian biodiversity include habitat loss and direct destruction of species, which have resulted in population declines in a number of plants and animals.


Habitat loss and modification

Anthropogenic impacts have affected a large proportion of Armenia, and have led to damage and destruction to natural habitats. Agricultural intensification has resulted in the loss of natural grasslands, and particularly of wetlands; over the last 50 years around 20,000 ha of marsh and wetland has been drained and converted to agricultural use. The effects of habitat loss or modification are also evident at a local scale, and a number of species (including plants and animals) have been affected by activities such as local deforestation, construction and road building. For example a small area of high floristic diversity close to Zvartnots temple has been destroyed following construction and industrial use close to the site, while around 180 species of desert plants that once occurred at a site near Goravan have now disappeared.

Habitat loss poses a particular threat to restricted range species, and those of semi-desert and mountain steppe habitat, many of which occur at the edge of their geographical range in Armenia. Changes in community composition, including decreasing species richness, are recorded in these habitats. The conversion of steppes and semi-deserts for agriculture over the last 50 years have also had important impacts on bird communities, with the disappearance of their natural habitats. Many bird species associated with such habitats are now listed as threatened in Armenia. There are also recorded population declines in reptiles from semi-desert areas, including the spur-thighed tortoise (Testudo graeca), toadhead agama (Phrynocephalis persicus), golden grass mabuya (Mabuya aurata), Caucasian sand boa (Eryx jaculus), Montpellier snake (Malpolon monspessulanus), racerunners (Eremias pleskei and Eremias strauchi), and the snake-eyed lizard (Ophisops elegans) from the Arax Valley. In addition, an important population of the regionally endemic sub-species of racerunner (Eremias arguta transcaucasica) has nearly disappeared from the Sevan basin as a result of agricultural land use, and only 100 individuals now remain within a single site. Similar declines are noted in the dwarf lizard Lacerta parva, another endemic which is now restricted to an area of 5km2 near Spitak.

The decline in the level of Lake Sevan had significant impacts on a number of wetland habitats in the vicinity, which dried out. As a result a number of marshland species (including lizards, waders and mammals) have disappeared from that area. Other water bodies have also suffered anthopogenic impacts. The diversion of water from the Noravank gorge to provide a water supply to a nearby village resulted in the loss of habitat and eventual disappearance of the wildlife of the gorge, including invertebrates, amphibians, reptiles, and mammals, as well as the destruction of an area of natural beauty.

Forest loss in Armenia

Forests, like other habitats, represent a dynamic system, and forest cover in Armenia has undergone significant changes since ancient times, in both species composition and structure. However, the impact of man of the forests of the country is obvious. Archaeological data indicates that around 40% of the land was originally covered in trees, at altitude zones of 500-2000m (Map 13). Since then forest cover has been affected by both changes in climate and by anthropogenic impacts. Increased temperatures resulted in a shift in the altitude zones at which forests were found, with the upper tree line increasing as far as 2200m altitude in the north and 2600m in the south. However, anthropogenic impacts have had more extreme effects on forest habitats, which now represent only 10% of the land surface (a quarter of the previous forest cover; Map 13), and are concentrated in the north-east of the country. A number of regions in Armenia are today totally deforested (Shirak, Armavir and Ararat), while others show very restricted tree cover (<1%; Vaik, Kotaik, and Gegharcunik).

A range of factors have increased pressures on forest resources, including a series of conflicts in the region which resulted in mass migrations of rural populations, and increased pressure on land for grazing and agriculture. Two major periods of timber extraction have occurred during this century. Between the 1930s and 1950s, around 450,000m3 of wood was extracted annually from Armenian forests for industrial use. Although this extraction was supposed to occur through selective logging of post-mature and damaged trees, forest resources were decimated at this time, and most of the mature trees were removed (which accounts for the current lack of mature and post-mature forests stands in Armenia).

Extensive deforestation also took place between 1992-1995, during the period of economic blockade and energy crisis. A combination of poor forest management and illegal felling resulting in damage to around 27,000 ha of forest (more than 8% of the total forest area), and, of this area, around 7000 ha was totally cleared. The effects of the damage to forests are clear in changes in species composition and in the loss of forests on lower slopes. The effects of the energy crisis on forests were particularly severe in the vicinity of urban areas (such as the hills around Yerevan) where pressure for fuelwood resulted in clearance of such woodland, resulting both habitat loss, and increased erosion of soils on hillsides.

Extensive grazing of cattle and pigs in forest habitats in recent years has further contributed to degradation of forests, particularly through its effects on regeneration and understory vegetation.
 
 
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