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A network of specially protected areas was first established
in Armenia in 1958 to protect ecosystems, habitats and rare,
endemic and threatened species. There are currently five State
Reserves, 22 State Reservations and one national park registered,
which together cover around 311,000 ha, or 10% of the surface
of the country. Around 60% of Armenian species are represented
within the protected area network, however there is a bias
towards forest habitats, and a need to expand the system to
include better representation of other ecosystems.
State Reserves are established to provide high levels of
protection for important habitats and species, and human use
within reserves is restricted to scientific research. State
Reserves therefore represent strict nature reserves, with
respect to IUCN criteria. The Ministry of Nature Protection
has overall responsibility for State Reserves, and manages
two reserves (Erebuni and Sev Lich). Three more reserves (Dilijan,
Shikahogh and Khosrov) are managed by 'Hayantar' State Enterprise
(under the authority of the Ministry of Nature Protection).
An outline of the five reserves, and their focal habitats
and species is shown in Annex 11.
A number of problems linked to design and effectiveness of
protection affect the State Reserves.
· Use by local people. Despite their designation as
strictly protected areas, local communities have become established
in a number of reserves (including Khosrov, Dilijan, and Shikahogh).
Activities such as tree-cutting, poaching, grazing and plant
collection by surrounding communities affect most reserves
(including Khosrov, and Dilijan). A law developed in 1985
to exclude communities from the reserve and reclaim the appropriated
lands has not been enforced to date. The effects of the energy
crisis in the early 1990s led to increased pressure on forested
areas in reserves - for example, 4000 ha within Dilijan reserve
was felled, mainly around settlements within the reserve.
Erebuni also suffers from being close to urban areas. The
lack of effective buffer zones for reserves is an important
issue when considering the needs for multiple land use in
these areas.
· Lack of resources. The lack of equipment and financial
resources substantially affect the effectiveness of protection
activities, particularly through the inability to regularly
patrol the reserve and regulate poaching and other illegal
activities. Reduced staffing and low wages for park staff
are also major constraints to effective protection, particularly
in Dilijan reserve. Shikahogh reserve urgently requires staff
training, as well as financial and technical assistance.
· Lack of complete gazettement. Until recently Shikahogh
Reserve had not been formally gazetted or managed, and the
park existed only on paper, without formal legal status. No
staff were in place for management, research or support activities.
A management unit was established in 1998, but this still
lacks financial resources and suffers from a weak technical
base, and the reserve has not yet been fully demarcated.
· Poor reserve design. Although Khosrov reserve is
among the best protected, it suffers from being divided into
eight separate sections, the borders of which do not take
account of local topography and landscapes. The migration
routes of many species have not been taken into account in
the design of the reserve (including routes for mouflon, leopard
and wild goats), and the location of water resources has not
been considered in relation to the position of the reserve.
A number of key habitats close to the reserve are not included
within its boundaries. Shikahogh reserve does not incorporate
the important Tsav plane grove, which needs special protection.
· Lack of knowledge. Financial restrictions have limited
the amount of research and inventory work done in reserves,
which in turn has affected the efficiency of management and
the monitoring of biodiversity. Khosrov reserve has been relatively
well studied, but financial cuts have restricted scientific
work in recent years. No survey work has been conducted in
Dilijan for several years, and little research has been conducted
at either Shikahogh or Sev Lich reserves.
State Reservations were established to protect a range of
rare and important habitats and species in Armenia, and to
improve the balance between economic use and nature protection
in the country. In reservations, some economic activities
are allowed, although these are expected to be regulated to
prevent ecological damage. Most reservations are managed by
'Hayantar' State Enterprise, but some are under the jurisdiction
of the Ministry of Nature Protection and Ministry of Agriculture,
and one is managed by the National Academy of Science. Details
of the 22 reservations in Armenia are shown in Annex 11.
Reservations suffer many of the same problems as reserves,
particularly in relation to over-use of biological resources.
· Tree-cutting. Removal of trees is a clear problem
in a number of reservations including those designed to protect
Tsav plane grove, Juniper scrub forests, (where forest has
become thinned and regeneration is limited), Gjulakari grove,
Pine Banksi, Ijevan, Gandzakar - Verin Aghda and rosebay scrub
forests.
· Overgrazing. Illegal use of pasture land within
reservations has affected a number of areas including those
designed to protect Aragats alpine forests, rosebay scrub
forests and Vordan karmir.
· Other activities. Some areas have also been affected
by other activities, including sand extraction (Gorovan sandlands)
and road construction (Gandzakar - Verin Aghdan).
· Design of reservations. For some reservations area
designation appears to have proceeded without full scientific
consideration, and does not take account of either topographical
or ecological factors.
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