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Europes ecological backbone.pdf

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Protected areas<br />

Box 9.3 Land use development and nature conservation problems in Slovak biosphere reserves<br />

The aim of biosphere reserves (BRs) within UNESCO's Man and Biosphere programme is to reconcile<br />

biodiversity conservation, economic and social development and local cultural values through the<br />

sustainable use of landscapes and their resources (UNESCO, 2008). There are four BRs in Slovakia, all in<br />

mountain areas: Poľana; Tatry and Slovak Karst (both bilateral BRs, with Poland and Hungary respectively);<br />

and East Carpathians (a trilateral BR with Poland and Ukraine). The Slovak Karst and Tatry BRs extend from<br />

basin slopes up to karst plateaus (Slovak Karst) or periglacial high mountain landscapes (Tatry). Though<br />

their natural assets are different, their land-use development has been quite similar. The adjacent basins,<br />

settled in prehistoric and medieval times, were used mainly for crop production and grazing that strongly<br />

affected nearby forests. The areas of the Poľana and the East Carpathians BRs were colonised in the late<br />

16th to 17th centuries, influencing the traditional land use, with smaller villages in narrow valleys with<br />

numerous forest pastures and subsistence based mainly on sheep and cattle grazing.<br />

Until the first half of the 20th century, land use in all four BRs was quite stable and similar, based mainly<br />

on agriculture and forestry. Subsequently, urbanisation, agricultural collectivisation, and the development<br />

of industry and transport were predominantly in more suitable lowlands or basins where land use<br />

intensification prevailed. In higher and remote locations, extensification took place (Olah et al., 2006). The<br />

few exceptions were in areas where land use was affected by new socioeconomic phenomena, such as the<br />

development of tourism centres in the Tatry BR, and the construction of dams and forced emigration in<br />

the East Carpathians BR (Map 9.2). The end of the 20th century and the first decade of this century were<br />

characterised by the rapid acceleration of land-use changes mainly because of socioeconomic changes, but<br />

also because of more frequent climate events.<br />

Land use extensification, or even total abandonment, of these agricultural landscapes results from<br />

unprofitable management and changing social preferences. Most mountain grasslands are secondary<br />

vegetation formations whose continuity demands a certain amount of subsidiary energy through human<br />

activities. The economic regression of the 1990s, combined with negative demographic trends — emigration<br />

to larger towns and the rupture of peasants' links to their land due to 40 years of collectivised property<br />

— has led to land abandonment and secondary succession. Between 1949 and 2003, two-thirds of the<br />

grasslands in Poľana BR were overgrown (Gallayová, 2008). This natural process can lead to the loss of<br />

specialised species whose existence depends on specific management practices, as in the East Carpathians<br />

(Ružičková et al., 2001). Decreases in biodiversity not only mean that the objectives of Natura 2000 are not<br />

achieved, but also cause significant loss of cultural landscapes, their scenery and traditional character (Olah<br />

and Boltižiar, 2009), especially in such extensively used sub-mountain and mountain cultural landscapes<br />

with HNV farmland. Land use intensification — either more intense management (forest monocultures<br />

or clearcutting) or urbanisation — also significantly alters or even completely destroys natural assets in<br />

protected areas. While forestry intensification affects almost all Slovak mountain BRs, the development of<br />

tourism centres and sport infrastructure mainly affects Tatry BR.<br />

Relatively new phenomena affecting land use in the mountains of Slovakia are natural disasters: strong<br />

winds and heavy rain. These have caused wind destruction in forests, resulting in significant economic loss.<br />

While many consider these disasters to be a serious<br />

recent problem, analysis of historical maps shows<br />

that they have occurred several times in the same<br />

areas (Olah et al., 2009). About 12 500 ha of forests<br />

were destroyed in Tatry BR after a wind storm in<br />

2004, and are now a site of conflict between nature<br />

conservation (leaving part of the area to natural<br />

afforestation), forestry (fast clearing of the area and<br />

artificial reforestation), and tourism interests (using<br />

open space for new tourism infrastructure).<br />

Source:<br />

Branislav Olah (EEA).<br />

Photo:<br />

© Martin Boltižiar<br />

Wind destruction area in the Tatry Biosphere<br />

Reserve, Slovakia.<br />

Europe's <strong>ecological</strong> <strong>backbone</strong>: recognising the true value of our mountains<br />

175

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