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Rila Monastery Nature Park Management Plan - part - usaid

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February 2004<br />

2.0 Threats and limitations<br />

The threats listed below have been identified and confirmed through observations by<br />

the teams who performed the rapid ecological and the rapid landscape assessments as<br />

well as the sociological survey in summer 2001; they were determined on the basis of<br />

recorded activities and practices, and findings regarding impacts. The present<br />

subsection deals with the existing territory of <strong>Rila</strong> <strong>Monastery</strong> <strong>Nature</strong> <strong>Park</strong>, as well as<br />

with some potential territory. Their significance is also determined, on the basis of<br />

expert assessments, in terms of intensity: critical, high, medium, or low; and in some<br />

cases qualified as: potential, local, affecting certain species, or insufficiently studied.<br />

Also stated in the assessments is the estimated significance of each threat for the <strong>Park</strong><br />

at present, based on their actual occurrences during the period under review, as well<br />

as their potential impact.<br />

Part of the described threats affects to a greater extent the facilities and territories in<br />

<strong>Rila</strong> <strong>Monastery</strong> settlement and the territory neighboring the park on the west. These<br />

threats are described here, because of their direct or indirect influence on the <strong>Park</strong>’s<br />

territory and goals.<br />

2.1 Natural threats<br />

Climate changes<br />

The decline in precipitation and the tendency toward drought observed over the past<br />

decade has also affected the <strong>Park</strong> territory, notably the hygrophilic plant habitats and<br />

aquatic or moisture-loving animals, as well as, on the whole, habitats situated along<br />

river banks, lake shores, peat bogs, marshes and other types of wetlands. As a result<br />

of a series of severe droughts during the period following 1982, there have been<br />

negative consequences for the mixed spruce-cum-fir forests, during which there was a<br />

tendency of the common fir and Scots pine to wither and die. Most visible are the<br />

changes occurring in the composition of the vegetation cover with a tendency towards<br />

an increase in areas occupied by plants adapted to dry conditions. Any further drying<br />

of the climate would have an extremely negative impact on the biodiversity of species<br />

and habitats within the <strong>Nature</strong> <strong>Park</strong>.<br />

Significance: potentially high<br />

The Chamaecytisus absinthiodes invasion<br />

The tendency, observed at many locations in the <strong>Park</strong>, for herbaceous cenoses to<br />

become overgrown with Chamaecytisus absinthiodes constitutes a threat to a number<br />

of elements of the <strong>Park</strong>’s biological diversity and conservation significance. The<br />

extent of this invading plant’s spread throughout the territory is shown by the fact that<br />

it has been identified in 50% of all surveyed areas, replacing a number of local<br />

species and altering the cenotic make-up of the local vegetation. Shrub communities<br />

of Chamaecytisus absinthiodes cause the disappearance of natural herbaceous<br />

cenoses and communities of Festuca valida and Calamagrostis arundinacea<br />

<strong>Rila</strong> <strong>Monastery</strong> <strong>Nature</strong> <strong>Park</strong><br />

<strong>Management</strong> <strong>Plan</strong> - Draft<br />

2004 - 2013<br />

157

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