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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Over-use of biological resources

In Armenia, both habitats and species have suffered from unregulated use. Although few figures are available, concern is expressed about the impacts of over-collection of wild plants and poaching of animals (see Chapter 4). Among species most at risk are plants of edible, medicinal or decorative use, and over-collection of such species has affected the semi-deserts, steppes and meadows in which they occur. Among animals, snakes have suffered over-collection for their venom, while the Armenian mouflon has suffered from poaching in the past. Habitats, particularly pasturelands, have also suffered degradation through over-use.

Overgrazing of grasslands and pastures

Anthropogenic factors have severely affected the pasturelands of Armenia, and a large proportion of grasslands have deteriorated in quality. Management of these lands has been poor to date, leading to substantial declines in areas suitable for grazing. Over-grazing has resulted in land erosion, formation of boggy areas and reduction in plant diversity. The area of natural pasture land has declined from 1.4 million ha in 1940 to 808,000 ha today, and remaining areas have been degraded and have become dominated by rocks (87%), scrub (25%), and inedible (74%) or poisonous plants (47%), while diversity has declined. For example, while between 70 and 80 plant species are normally supported by steppe systems, the number of species found after intensive over-grazing drops to around 15. Similar declines in richness are reported in meadow systems (from 125 to around 25 after over-grazing). Over-grazing has also resulted in changes in species composition, with declines in populations of valuable fodder plants and increases in weeds and poisonous species (such as crowfoot, thistle, creeping thistle, as well as Euphorbia seguieriana, and Astragalus spp.). In addition the over-collection of particular species for human consumption from natural pastures has pushed these species to the edge of extinction.

Changes in grazing regimes post-privatization have led to decreases in floristic diversity in some areas where grazing has declined, but more importantly increased habitat degradation in over-grazed areas. Privatization led to complex problems of access to, and use of, common grazing lands, and consequently the use of natural pastures and hay meadows has declined substantially since then. Over 60% of hay meadows have now been privatized, while pastures are used on a lease basis. Despite the declines in livestock populations since privatization, over use of remaining pastures is still an important problem. Although grazing has been reduced in the highlands (alpine and upper sub-alpine meadows), a two- to three-fold increase in grazing pressure has been recorded in lowland sub-alpine meadows and steppes. The likely intensification of livestock grazing with economic recovery, coupled with the current lack of regulation, means that the issue of over-use of pastures is likely to grow in importance over the coming years. Regulation will be essential to ensure that natural grasslands remain areas where traditional grazing practices can coexist with the protection of natural communities and their inherent genetic diversity.


Pollution


Pollution is a major issue in Armenia, involving not just current emissions, but the legacy from pollution during the Soviet era. Sources of pollution include industrial centres, mining enterprises, chemical and power plants, and vehicle emissions.

Prior to economic crisis substantial pollution was produced by the country's industrial centres, totaling around 245,000 tonnes annually (54,400 tonnes of solid particles and 190,900 tonnes of liquid or gaseous emissions). This included around 50 different pollutants, including sulphate anhydride (58%), nitric oxides (15%) and oxides of carbon (14%). At present only a small proportion of industries remain operational (10-30%), and emissions of pollutants have dropped dramatically to 15,000-20,000 tonnes per year. However, pollution continues to have negative impacts on both natural ecosystems and agricultural lands in the country. Nitrogen-containing compounds (ammonia, nitric oxides) released from the Vanadzor chemical plant have affected up to 22% of surrounding forests (703.7 ha within a 5km radius). The emission of flourides and chlorides from the 'Narit' Reseach Association has resulted in direct damage to crops within a 2km radius and reductions in productivity and quality.

Of great concern is the continued release of toxic waste, including heavy metals (annual outputs in 1980 were equivalent to 18,000 tonnes), and the effects of this pollution are still evident. For example, heavy metal levels in crops around the Alaverdi metallurgical plant are between 20 and 40 times above the maximum allowable level.

Substantial amounts of accumulated industrial waste exist in the country, mainly as a result of mining (estimated as hundreds of millions of cubic metres of waste). Even during the current period of reduced industrial outputs, almost 300,000m3 of industrial waste (including slag) was produced by mining operations in 1996 alone. A number of tailings from extractive and processing operations remain in the country, totaling around 220 million m3 (including 30 million m3 from Zangezour copper-molybdenum plant, 12 million m3 from Ararat gold refinery, and 3 million m3 from the now closed Dastakert copper-molybdenum plant). There is a particular risk of pollutants from these tailings leaching into water systems.

Industrial and mining operations have had a significant impact on water systems of the country. The release of polluted water and industrial effluent directly into some rivers has resulted in widespread loss of natural vegetation and animal life (for example, the lower stream of the River Debed, and the basin of the River Voghji have been affected in this way). Natural ecosystems are affected by both chemical and thermal pollution from industrial plants, and polluted water is also finding its way into irrigation systems, thus affecting agriculture and threatening human health.

Vehicle emissions are a major contributor to pollution in Armenia, representing 94% of total emissions (an increase from 67% of emissions in 1987). In particular, exhaust fumes contain oxides of nitrogen and carbon (Table 6.3), which contribute both to local pollution of natural ecosystems, and to global warming. At present laws regulate several pollutants in vehicle emissions, however overall assessments of pollution from road transport are difficult to quantify accurately from the data available. However, it is clear that pollution level dropped significantly during the energy crisis in the early 1990s, but have now risen dramatically again (Table 6.3).



Table 3 Vehicle emissions of various pollutants, 1987-1995

Pollutant
Emission levels (thousand tonnes)
1987
1988
1989
1990
1991
1992
1993
1994
1995
Nitrogen oxide
23.3
23.8
24.9
23.5
20.9
11.7
8.8
7.9
9.5
Carbon oxide
389.3
392.6
381.3
287.5
349.4
187.8
142.2
126.4
171.9
Hydrocarbons
76.6
75.7
74.0
72.4
62.4
29.6
19.4
16.9
23.1
Total
486.2
492.1
480.2
383.5
432.7
229.0
170.5
151.1
204.5

Introduced and invasive species


A range of species have been introduced to Armenia. Many of these are of commercial value and are maintained within controlled conditions. However, other species, with high ecological adaptiveness, have expanded their ranges to the detriment of native species. The impacts of such species, and their success in entering new ecosystems, is dependent on their morphology, ecology and behaviour.

Most introductions were non-accidental, and include species with economic (agricultural, fisheries, hunting, medical, or technical) or aesthetic value. For instance, American and Canadian poplars have been imported to grow on saline lands, pink geranium is grown for its essential oil, and sweet flag (Acorus) from India and China, has been grown since Medieval times. However, a number of species appear to have been introduced accidentally, and many of these prove damaging to both natural ecosystems and agricultural lands (such as Colorado beetles, and Asian grasshopper). Among the most aggressive invasive plant species are Xanthium, Cirsium, and Galinsoga parviflora, while wormwood ambrosia (Ambrosia artemisiefolia) has expanded its distribution by over 200km2 within the last decade.

Armenia's fisheries have been supported by the introduction of a range of fish species since the 1920s (see Section 2.5.2), and such species now represent the most productive fish in Lake Sevan. However, their interaction with native fish is not well understood. However, the introduction of goldfish (Carassius auratus) to the lake resulted in increasing populations, and high levels of competition with native fish species. River crayfish have also spread dramatically in Lake Sevan since their introduction in the 1980s.

Other species that have become naturalised to Armenia include pheasant (Phasianus colchicus) which is bred in Khosrov reserve and coypu (Myocastor coypus) which have expanded their distribution since 1940, and are now found in most marshlands of the Kur and Arax rivers.

 
 
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