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==Introduction== | ==Introduction== | ||
The Šumava, which is the Czech name for the [https://en.wikipedia.org/wiki/Bohemian_Forest Bohemian Forest], is currently the largest natural wilderness area in the central European cultural landscape. Since the half of the 20th century the most valuable parts of the Bohemian Forest were recognized by nature conservationists as national parks (NP) – there was declared the first German NP already in 1970 (the Bavarian Forest National Park) which was largely extended in 1997. The neighbouring Šumava Protected Landscape Area (PLA) was declared on the Czech side in 1963, and on its territory the Šumava National Park was established in 1991. This step has gradually caused series of conflicts between nature protectionists with (not only) local inhabitants and enterprises and this situation appeared to have no solution over more than two decades. | The Šumava, which is the Czech name for the [https://en.wikipedia.org/wiki/Bohemian_Forest Bohemian Forest], is currently the largest natural wilderness area in the central European cultural landscape. Since the half of the 20th century the most valuable parts of the Bohemian Forest were recognized by nature conservationists as national parks (NP) – there was declared the first German NP already in 1970 (the Bavarian Forest National Park) which was largely extended in 1997 (present area of 24,218 ha). The neighbouring Šumava Protected Landscape Area (PLA) was declared on the Czech side in 1963 (total area of 167,688 ha), and on its territory the Šumava National Park was established in 1991 (68,064 ha). This step has gradually caused series of conflicts between nature protectionists with (not only) local inhabitants and enterprises and this situation appeared to have no solution over more than two decades (Křenová, Vrba, 2014). | ||
==History of the population of the area== | ==History of the population of the area== | ||
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== Actors == | == Actors == | ||
Cited from (Křenová, Vrba, 2014) | |||
===State administration=== | ===State administration=== | ||
Vulnerable to political (often non-supporting nature protection) interests. Often changing directors of the Park (9 directors in 22 years; in contrast on the German side – 3rd director in 43 year history). Management is not consistent and even legal framework has been changing. | Vulnerable to political (often non-supporting nature protection) interests. Often changing directors of the Park (9 directors in 22 years; in contrast on the German side – 3rd director in 43 year history). Management is not consistent and even legal framework has been changing. | ||
===Šumava NP Council=== | ===Šumava NP Council=== | ||
Under such circumstances, the Šumava NP Council does not create a favourable environment for creative and responsible cooperation between the local representatives and the NP Authority. Mayors of all the municipalities with an area within the NP territory | Under such circumstances, the Šumava NP Council does not create a favourable environment for creative and responsible cooperation between the local representatives and the NP Authority. Mayors of all the municipalities with an area within the NP territory, together with representatives of the two administrative regions and the mountain rescue service, are mandatory members of the Council. These 25 members in total form a relevant majority of the Council. The Council indeed is supposed to negotiate strategic documents of the national park, such as zoning, management plan, or visitor regulation. Instead of approving knowledge-based and science-wise solutions for nature conservation and sustainable life, the Council has become a ‘board of regional regents’ without any accountability. Some full-time mayors often used to act, more or less deliberately, as latent lobbyists for hidden entrepreneurs, developers, or land owners. Some of the Council meetings have served only for tasking the NP directors, or for formal approval of documents fulfilling wishes of regional politicians and developers. The number of scientists, complaining against these practices, was reduced by the political director two years ago to be able control the majority in the Council. The obligatory Council setup in fact allows for overbalancing of such hidden interests and often overrules actual nature conservation in the Šumava NP if the director is not tough enough or even is proactive. | ||
===Šumava and PLA Authority=== | ===Šumava and PLA Authority=== | ||
During the entire history of the Šumava NP, the Authority has largely focused on the NP agenda, such as forestry and pest control, zoning and visitor regulation. Curiously, the Authority has hardly fulfilled the predetermination of the PLA territory as an actual buffer zone for the NP. For instance, the management plans of the NP and PLA have been largely incompatible, sometimes indeed applying contradictory measures to similar habitats, and have never been synchronised either. Similarly, the Authority has so far given up applying the status of the Šumava BR to the joint NP and PLA territory. An obvious reason is the fact that the BR has got no legal framework in the national legislation and, thus, neither financial nor personal support by the Ministry of the Environment or the Czech Government. In our opinion, the UNESCO BR concept would be a good framework for solving the most controversial issues and an excellent tool for sustainable tourism and overall development of the entire region. As a matter of fact, the existence of the Šumava NP represents a great tourism potential not only for the six villages located within the NP or others in its territory but for many other municipalities in the Bohemian Forest region. The Šumava NP and PLA Authority, however, has not made a serious attempt to implement the UNESCO BR concept in the region in the past 23 years. | During the entire history of the Šumava NP, the Protected Landscape Authority has largely focused on the NP agenda, such as forestry and pest control, zoning and visitor regulation. Curiously, the Authority has hardly fulfilled the predetermination of the PLA territory as an actual buffer zone for the NP. For instance, the management plans of the NP and PLA have been largely incompatible, sometimes indeed applying contradictory measures to similar habitats, and have never been synchronised either. Similarly, the Authority has so far given up applying the status of the Šumava BR to the joint NP and PLA territory. An obvious reason is the fact that the BR has got no legal framework in the national legislation and, thus, neither financial nor personal support by the Ministry of the Environment or the Czech Government. In our opinion, the UNESCO BR concept would be a good framework for solving the most controversial issues and an excellent tool for sustainable tourism and overall development of the entire region. As a matter of fact, the existence of the Šumava NP represents a great tourism potential not only for the six villages located within the NP or others in its territory but for many other municipalities in the Bohemian Forest region. The Šumava NP and PLA Authority, however, has not made a serious attempt to implement the UNESCO BR concept in the region in the past 23 years. | ||
The Šumava NP and PLA Authority and the representatives of local municipalities have never become reliable partners. Since the very beginning, the Authority continued its, rather restrictive, nature conservation approach, often neglecting and ignoring problems and expectations of local people, who largely used to rely on the state paternalism in the past. It took a decade or so before the Authority gradually changed its approach that failed either. Thus, in consequence, the local representatives – largely unready for the new situation in the 1990s, i.e., overall political and social changes in the country, opening of the national border, closure of the military training area, and establishment of the Šumava NP – have easily learnt to say: ‘we would like to do this and that, but we cannot do it because of the NP obstacles’. Under such circumstances, the Šumava NP Council does not create a favourable environment for creative and responsible cooperation between the local representatives and the NP Authority. | The Šumava NP and PLA Authority and the representatives of local municipalities have never become reliable partners. Since the very beginning, the Authority continued its, rather restrictive, nature conservation approach, often neglecting and ignoring problems and expectations of local people, who largely used to rely on the state paternalism in the past. It took a decade or so before the Authority gradually changed its approach that failed either. Thus, in consequence, the local representatives – largely unready for the new situation in the 1990s, i.e., overall political and social changes in the country, opening of the national border, closure of the military training area, and establishment of the Šumava NP – have easily learnt to say: ‘we would like to do this and that, but we cannot do it because of the NP obstacles’. Under such circumstances, the Šumava NP Council does not create a favourable environment for creative and responsible cooperation between the local representatives and the NP Authority. | ||
Local people’s expectations and municipalities’ tasks have often gone far beyond the real power of the Šumava NP and PLA Authority. Though it should be rather a partner than a leader in regional development, the Authority has frequently organised (and even funded from its own resources in the past) many regional infrastructures and activities within the Czech Bohemian Forest, such as public transportation by green buses, winter maintenance of white trails for cross-country skiing, or building of cycle tracks. | Local people’s expectations and municipalities’ tasks have often gone far beyond the real power of the Šumava NP and PLA Authority. Though it should be rather a partner than a leader in regional development, the Authority has frequently organised (and even funded from its own resources in the past) many regional infrastructures and activities within the Czech Bohemian Forest, such as public transportation by green buses, winter maintenance of white trails for cross-country skiing, or building of cycle tracks. | ||
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==Village Prášily== | ==Village Prášily== | ||
The Šumava National Park created in 1991 includes the central part of the mountain range along the border with Germany, and partly also with Austria. The area includes seven villages (Srní, Kvilda, Horská Kvilda, Modrava, Stožec, České Žleby and Prášily), as well as several smaller settlements (Filipova Huť, Dobrá, Jelení). ([http://www.vimperk.cz/147/en/normal/the-sumava-national-park/#.V-qEI_mLSHt Tourist information system]) | The Šumava National Park created in 1991 includes the central part of the mountain range along the border with Germany, and partly also with Austria. The area includes seven villages (Srní, Kvilda, Horská Kvilda, Modrava, Stožec, České Žleby and Prášily), as well as several smaller settlements (Filipova Huť, Dobrá, Jelení). ([http://www.vimperk.cz/147/en/normal/the-sumava-national-park/#.V-qEI_mLSHt Tourist information system]) | ||
==Resources== | |||
*Criteria for Sustainable Tourism for the three Biosphere Reserves Aggtelek, Babia Góra and Šumava. Online http://www.tourism4nature.org/results/backdocs/Criteria%20for%20Sustainable%20Tourism.pdf | |||
*Humlíčková, P. (2008) Jaké jsou limity soudní ochrany v Čechách? Sborník mezinárodní konference, Zelený kruh, Praha. ISBN: 978-80-903968-2-1, str. 4-5. Online http://www.zelenykruh.cz/dokumenty/sbornik-limity-soudni-ochrany-web.pdf | |||
*Klos, Č. (2011). Šumava and the rule of law. CzechPosition.com http://www.ceskapozice.cz/node/38923 | |||
*Křenová, Z., & Vrba, J. (2014). Just how many obstacles are there to creating a National Park? A case study from the Šumava National Park. European Journal of Environmental Sciences, 4(1). Online http://ejes.cz/index.php/ejes/article/view/150 | |||
*Johnstone, Ch. (26.07.2011) Czech Šumava National Park turns into battleground. CzechPosition.com. Online http://www.ceskapozice.cz/en/business/energy-green-biz/czech-sumava-national-park-turns-battleground | |||
*Rousek, L. (2011) Hungry Bark Beetle Sparks Czech Political Controversy. The Wall Street Journal. Online http://blogs.wsj.com/emergingeurope/2011/08/03/hungry-beetle-sparks-czech-political-controversy/ | |||
*Schroeder, M. (2003) The Forest is Regenerating after Germany's Worst Spruce Bark Beetle Attack. NewsWoman. Online http://newswoman.de/news/barkbeetle.htm | |||
**other sources about the conflict see Crowdvoice, tracking voices of the protest, http://crowdvoice.org/protests-to-protect-national-park-in-czech-republic?all=true | |||
*Silva Gabreta http://www.npsumava.cz/cz/3241/sekce/table-of-contents/ | |||
*Tourism in UN documents: https://sustainabledevelopment.un.org/topics/sustainabletourism | |||
*Transboundary cooperation: http://www.tourism4nature.org/results/backdocs/ETE_2009_Transboundary_Cooperation.pdf | |||
== References == | == References == | ||
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*Novotná M., Kopp J. 2010. Migrační trendy v regionu Šumava po roce 1990. Silva Gabreta 16: 187–206. | *Novotná M., Kopp J. 2010. Migrační trendy v regionu Šumava po roce 1990. Silva Gabreta 16: 187–206. | ||
*Prach K., Bufková I., Zemek F., Heřman M., Mašková Z. 2000. Grassland vegetation in the former military area Dobrá Voda, the Šumava National Park. Silva Gabreta 5: 103–112. | *Prach K., Bufková I., Zemek F., Heřman M., Mašková Z. 2000. Grassland vegetation in the former military area Dobrá Voda, the Šumava National Park. Silva Gabreta 5: 103–112. | ||
*Zemek F., Heřman M. 1996. Remote sensing and GIS in the Šumava region research and management. Silva Gabreta 1: 281–284. | *Zemek F., Heřman M. 1996. Remote sensing and GIS in the Šumava region research and management. Silva Gabreta 1: 281–284. | ||
*Zemek F., Heřman M. 1998. Landscape pattern changes in the Šumava Region – a GIS approach. Silva Gabreta 2: 395–410. | *Zemek F., Heřman M. 1998. Landscape pattern changes in the Šumava Region – a GIS approach. Silva Gabreta 2: 395–410. | ||
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