Expansion of Nature Conservation Areas: Problems with Natura 2000 Implementation in Poland?
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- Cite this article as:
- Grodzinska-Jurczak, M. & Cent, J. Environmental Management (2011) 47: 11. doi:10.1007/s00267-010-9583-2
In spite of widespread support from most member countries’ societies for European Union policy, including support for the sustainable development idea, in many EU countries the levels of acceptance of new environmental protection programmes have been and, in particular in new member states, still are considerably low. The experience of the countries which were the first to implement union directives show that they cannot be effectively applied without widespread public participation. The goal of this study was, using the example of Poland, to assess public acceptance of the expansion of nature conservation in the context of sustainable development principles and to discover whether existing nature governance should be modified when establishing new protected areas. The increase in protected areas in Poland has become a hotbed of numerous conflicts. In spite of the generally favourable attitudes to nature which Polish people generally have, Natura 2000 is perceived as an unnecessary additional conservation tool. Both local authorities and communities residing in the Natura areas think that the programme is a hindrance, rather than a help in the economic development of municipalities or regions, as was initially supposed. This lack of acceptance results from many factors, mainly social, historic and economic. The implications of these findings for current approach to the nature governance in Poland are discussed.
KeywordsConflict managementNatura 2000Nature conservationPublic participationSustainable development
European Nature Conservation Policy: Current Trends
Accession to the European Union (EU) offered extensive opportunities for development and changes in policy of individual countries in practically all sectors of the economy. A consequence of membership in the EU was the implementation of standards of Union law including a broad spectrum of principles of sustainable development (Larobina 2001). In the case of nature conservation, the European policy distinctly strengthened the implementation of the sustainable development strategy through the requirement that member countries have to adopt international commitments, chiefly the Convention on Biological Diversity and the resulting expansion of nature conservation areas. Of special importance in this regard are the provisions resulting from EU directives: the Birds and the Habitats Directive. Pursuant to the requirements of the Habitat Directive, a new form of nature conservation—the Natura 2000 European Ecological Network—has been created in the territory of the EU (International Union for Conservation of Nature 2005).
Legal protection of natural resources in majority of the EU Member States is currently provided by legislation protecting individual species and areas. In Poland, for example, they take the form of national parks, nature reserves, nature, landscape parks and areas of landscapes parks. These systems seem to be an effective tool for the protection of natural resources at the national level of each country (Symonides 2008). On a continental scale the nature conservation policy requires the adoption of a wider and operational perspective. Nowadays at the enlarged EU level however, the goals, general principles and the implementation of the nature conservation policy have become more complex and multi-level, eventually resulting in top-down governance. Such an attitude is inherently at risk of being introduced locally with a low level of effectiveness and adaptability (Folke and others 2007). That is why current trends in managing nature (mainly biodiversity) protection in the EU, in addition to recommending the means of implementing actions imposed in a top-down fashion, are increasingly often perceived as needing to be complemented with significantly more effective bottom-up initiatives. The latter appear to be essential, particularly in the new Member States where nature conservation is still often affected by the post-socialistic governance type and thus operates in a rather ineffective way (Kluvánková-Oravská and others 2009).
The key issue, as shown by practices already in use mainly in EU-25 countries which were the first to introduce the new nature conservation policy seems to be to involve the widest possible group of actors (non-governmental organizations, community members, etc.) at various, particularly local levels (Paavola and others 2009; Silva and others 2009). Public participation is explicitly mentioned as a means and goal of sustainable development in EU strategies (Commission of the European Communities 2005). In the case of nature and environmental conservation it is defined in the provisions of the Habitat Directive and the Convention on access to information, public participation in decision-making and access to justice in environmental matters, commonly known as the Conventions of Aarhus (Dz. U. 2003, No 78, item 706; Koester 2007; Stec and others 2000). According to both these documents, public participation should manifest itself in society’s access to information about the natural environment and its involvement in successive stages of the implementation of protective measures: from planning to making decisions in management. Public participation is consistent with the three-dimensional concept of sustainable development as it allows natural capital to be traded off for economic and social capital. That is why the difficulty of involving the public in the execution of nature conservation tasks illustrates the more general problems associated with the implementation of sustainable development principles (Palerm 2006). In addition to increasing acceptance for a new policy itself, public participation in environmental protection has a broader significance, as it leads to the development of multilevel governance, encompassing the wider—interdisciplinary—context, the introduction a number of new structures and financial resources to the civil society of a country (Antoniewicz 2006; McCauley 2008).
Whether the expansion of nature conservation caused by the introduction of Natura 2000 European Ecological Network is a source of potential social conflicts observed at the local level among various actors—government and community? If so, what are the reasons and how do they differ between the two groups involved?
How do residents of newly established protected areas and their surroundings perceive the need for nature conservation in the context of infrastructure development and private business investment in their regions?
Is the effectiveness of Natura 2000 implementation affected by the current nature conservation policy?
Do opinions and problems associated with the establishment of new protected areas vary among municipalities and regions? If so, what factors differentiate them?
The Natura 2000 European Ecological Network: Theory and Practice
The Natura 2000 programme is of great practical importance for the implementation of the sustainable development strategy, mainly due to its firm legal basis (including the possibility of national decisions to be revised by the European Commission), the scale of this undertaking and the principles of the nature conservation system itself (Ostermann 1998). The latter considerably differ from the previous traditional European system, that is, going beyond a direct ban on damaging plants or killing animals. The main effect of the programme’s introduction is to reconcile nature conservation with features of sustainable development, namely a possibility of working out a compromise between economic development and rational use of natural resources. Particularly significant for the functioning of the programme is the introduction of the criterion of the overriding public interest which should also include future generations, as well as levelling the existing economic differences between European Community countries (Oana 2006; Unnerstall 2006).
Generally, European nature conservation policy and the resulting necessity to implement new programmes, e.g., Natura 2000, has led to dissatisfaction and relatively low acceptance levels with regard to the solutions proposed (Beaufoy 1998; European Commission 2004; Julien 2000). In many countries, including Poland, this was due to many factors, the main ones being no tradition of the public participation approach, the ownership structure of the land brought into protected areas and the funding of the programmes (Bland and Thiry 2003; de Piérola and others 2009; Perzanowska and Grzegorczyk 2009; Weber and Christophersen 2002).
Although the methods of implementation of Natura 2000 programme are defined by legislation and there is a possibility of benefiting from the experience of older EU Member States, in many countries the programme’s implementation encountered considerable difficulties. This was caused by both the centralised character of the programme and the public participation requirements being too vaguely defined by the Habitat Directive (Beunen 2006). In central and eastern Europe implementation difficulties were additionally caused by a weak history of participatory governance, including the absence of a collective choice mechanism, lack of a conflict management system, undefined responsibility for the coordination of resources and very limited experience in acquiring EU funding for the programme’s implementation which were simply not available at the national level (International Union for Conservation of Nature 2005). In the almost all EU countries, dissatisfaction was noticed at various stages of the programme’s implementation, particularly designation of the site boundaries and recommendations to be taken into account in preparing management plans (Dimitrakopoulos and others 2004; Visser and others 2007). In the majority of the EU Member States, the sites were designated practically only on the basis of environmental considerations whereas a very limited number of consultations with local governments, decision-makers and land owners were conducted (Małopolski Urząd Wojewódzki 2008; Makomaska-Juchiewicz 2007). This has additionally confirmed local governments in their opinion that the initiative itself is centralised in character—not properly adapted to specific local conditions, and consequently discouraged them from becoming involved in it (Cash and others 2006).
The land use structure in the Natura 2000 areas features a high proportion (varying between the regions and countries) of private land, hence it is managed by their owners—chiefly farmers (Makomaska-Juchiewicz and Tworek 2003; Soma 2009). This, in turn has a definite negative traditional and historical connotation. Many owners of arable land or forests took Natura 2000 to be an initiative infringing their basic property rights (Hiedenpää 2002). The designation of protected areas especially in the case of post-socialist countries such as Poland, is still associated with the post-war incorporating of private land to establish national parks, which involved a loss or the obligation to sell private properties for outlandishly low prices (Królikowska 2007; Partyka and Żółciak 2005). Thus far, within Natura 2000 no attractive compensation programme for the owners of private land that is included in the network has been developed. Only some countries, like France, managed to resolve these issues although late and only when forced by the need to ease conflicts (Alphandery and Fortier 2001; McCauley 2008). Activities developed and completed in the EU are however a far cry from the well prospering system of financial compensation that has been in operation in the USA for a long time (Fischer and others 2009; Wallace and others 2008).
To sum up, it can be assumed that many EU countries already completed two first stages of the Natura 2000 Programme by establishing the list of protected areas and developing the management plans for each of the site. Finally, Natura 2000 sites cover around 20% of the continent surface varying among the countries from 7.1% in the UK, 12.8% in Germany, 20.9% in Portugal, 21% in Poland to as much as 34.9% in Bulgaria or 35.5% in Slovenia (Ministry of the Environment Poland 2009, http://natura2000.mos.gov.pl). In the case of Poland, the sites’ list is currently being assessed and verified by the European Commission. The country enters the next stage of the programme—preparation of the management plans for individual sites. This, as in other EU countries, will probably result in arising various conflicts, particularly at the local level (Young and others 2005).
Materials and Methods
The Study Area
Description of the municipalities studied and the areas of protected nature within their boundaries
Name of the municipality
Babia Góra (PLB120011; PLH120001)
Czarna Orawa (PLH120002)
Orawa and Nowy Targ Peat Bogs (PLB120007; PLH120016)
67.5 km² (49% farm & 48% forest use)
286.89 km², (5% farm & 87% forest use)
455.18 km² (23% farm & 69% forest use)
(60% farm & 34% forest use)
Unemployment rate (%)
Environmental description of the Natura 2000 site
18 types of habitats with forest communities & high mountain grassland; dwarf mountain pine;
924 vascular plants species (rare, threatened or already protected), rich (ca. 2500 species) invertebrate fauna;
very important area for birds;
Threats to the area: transfrontier air pollution, dumping of waste from homesteads
A need to protect rare fish species habitats; one of two in Poland natural sites of the Danube salmon; important vegetation on the streams embankments, riparian forests;
Threats to the area: sewage, collection of stones & gravel from the stream bed
Orawa-Nowy Targ Peat Bog
Valuable peat bogs, marsh forests, meadows & riparian habitats;
The most important habitats: Myricaria & willow thicket on the stony embankments of streams, high peat bogs, marshy coniferous forests & riparian forests; rich fauna: bears, wolves, otters, Yellow-bellied toads, Great Crested Newts & Carpathian Newts.
Threats to the peat: General lack of water, illegal extraction by locals, water pollution & drainage.
Plans to build a sewage treatment plant.
29 protected species & 21 types of habitats; 1100 vascular plant species (many rare, threatened & legally protected);
valuable forest communities, e.i. Carpathian beech, sycamore & unique to Poland mountain pasture communities. 38 bird species named in the Directive & 13 in the Polish Red Book;
Important terrain for nesting (ca. 150 species) & hatching (area occupied by 1% of the national population of many important species, i.e.: the black stork, the White-backed woodpecker, Lesser Spotted Eagle, Golden Eagle, Eagle Owl);
rich forest fauna: bears, wolves, lynxes; strong populations of otters, the Aeskulapian snake.
Other forms of nature protection within the municipality (date of creation)
Babia Góra National Park (1954) and the Babia Góra Biosphere reserve (1977)
Bieszczadzki National Park (1973)
San Valley Landscape Park (1992)
“Bembeńskie” Forest Reserve (2001)
Transborder Part of the Biosphere Reserve Eastern Carpathians (1992)
“Na Policy” Reserve (1972)
Cisna-Wetlina Landscape Park (1992)
The whole municipality is a Protected landscape Area*
Sine Wiry Reserve (1988r.)
Jaśliski Landscape Park (1992);
“Olszyna łęgowa w Kalnicy” Reserve (1971)
“Zwięzło” Reserve- Duszatyn Lakes (1957); “Przełom Osławy pod Duszatynem” Reserve (2000)
Methodology of the Study
Analysis of documents covered remarks made by 233 representatives from local governments of municipalities where Natura 2000 was introduced. Remarks were formulated in the form of answers to the official request from the Minister of the Environment to express their opinion on the submitted proposals for the site boundaries. The contents of the remarks were coded with the QDAMiner software. Two lists with codes were used. The first one pertained to the general character of the opinions expressed, the second list included problem issues. Data concerning local governments’ opinions is presented here in accordance to alpine and continental bioregion.
The surveys were conducted on a random sample of 606 households of four selected municipalities of the alpine region. The municipalities were selected so as to represent to the fullest possible extent the potential conflicts and conditions, resulting from the introduction of the Natura2000 programme. This selection was dictated by the previous analysis of the municipalities’ opinions, press and official information on the planned projects and emerging conflicts. The households were selected using simple random sampling on the basis of address lists obtained from individual municipality offices. Within a household, respondents were selected on a quota basis, so that the sample corresponded to the municipality demographic structure in terms of age and sex. Because of the huge economic emigration from these areas (mainly men), such a method ensured that all groups of municipality residents would be well represented. The questionnaire surveys were conducted from December 2007 to January 2008. In order to inform inhabitants of aims of such an action, it was announced on the municipality office information boards and in the local catholic parishes. The survey response rate obtained was 65%.
The questionnaire used to conduct the survey was developed on the basis of semi-structured interviews conducted earlier with representatives of local governments of the municipalities surveyed, and on the basis of consultations with experts. The answers were evaluated using 5-grade scales concerning (1) the meaning of nature for people living in a given area, (2) the evaluation of potential projects in terms of their harmful effect on nature and how strongly they are desired by the respondent, (3) an evaluation of the burden of the existing forms of environmental protection, and also a part concerning (4) the respondent’s activity and occupation, (5) knowledge of the existence of the Natura 2000 programme.
The results of the questionnaire were analysed using SPSS software. Factor analysis was employed to discover the structure of attitudes to nature protection and the expansion of nature conservation areas. Groups were compared using the Kruskal–Wallis test, and basic descriptions were made using averages and frequencies to questionnaire questions.
Local Governments’ Attitudes Toward the Expansion of Nature Conservation Areas
Local governments’ opinions about the proposed Natura 2000 sites. Assessment of the sites and categories of arguments. Table presents % of the municipalities
Continental local governments (%)
Alpine local governments (%)
Opinions on the proposed areas:
Request to alter borders
Neutral opinion / no comment
No comment possible on the basis of provided materials
Conflicts indicated: (total)
On the basis of ownership of the areas
On the development of infrastructure
On actual and planned businesses
On building extensions
Types of arguments given:
(a) Economic, including:
extension of procedures and rise in costs
restricting the development of tourism
restricting the development of enterprise, encompassing industrial land (e.g. mines)
hindering and restricting the development of agriculture
hindering and restricting the development of fishing
(b) Relating to the development of infrastructure, including: (total)
(c) Conflicts indicated with existing development plans:
(d) Environmental, including: (total)
indicating the non-occurrence of given species and habitats
current protection is sufficient
imposing the sites will cause problems
(e) Procedural, including: (total)
lack of agreement with the local governments
lack of agreement with local naturalists
erroneously mapped out / on incorrect maps and templates
(f) Social (unemployment, migration of young people, impoverishment of society):
(g) Conflicts indicated with existing development plans for the sustainable development of the municipality
Is Nature Conservation an Obstacle to the Economic Development of Municipalities and Regions?
Poland is classified among the group of countries of high-level economic development (Organisation for Economic Co-operation and Development 2009, http://www.hdr.undp.org/en/statistics). In practice, when compared to other EU countries, this status means, among other things, a poorly developed road network, high urbanisation rate and problems with the restructuring of agriculture. Improvement in these areas can lead to conflicts with nature conservation, especially in the cases of EU-financed projects.
In questioning the reasons for establishing Natura 2000 sites in their municipalities, local governments often used arguments referring to the overriding importance of public interest in local infrastructure development as opposed to the need to conserve local nature. These opinions opposed to in the survey studies conducted among residents of individual municipalities.
Possible restrictions associated with the designation of Natura 2000 sites pertain not only to public infrastructure projects or to major companies, but also to small projects undertaken by individuals. That is why it seemed expedient to analyse the residents’ individual investment plans, the more so that, according to local governments the hindering of these investment tasks is and will be a source of dissatisfaction and consequent unpopularity of the Natura 2000 programme.
Assessment of the statistical significance of the differences between municipalities in answering the analysed questions, using the Kruskal–Wallis test
Do they plan to build a house
Do they plan to start a business
Do they plan to run an agrotourism business
Do they plan to farm organically
Do they plan to sell the land
Do they plan to apply for a farming subsidy
Natura 2000 will make it difficult to build a house
Natura 2000 will make it difficult to start a business
Natura 2000 will make it difficult to run an agrotourism business
Natura 2000 will make it difficult to farm organically
Natura 2000 will make it difficult to sell the land
Natura 2000 will make it difficult to apply for a farming subsidy
Does the national park make life difficult for people here
Is it important that the municipality has been included in the European network
Is it worth extending the sites of protected nature in the area
Is it also important to protect nature outside of the national park
Would they vote for a candidate planning to extend the area of protected nature
Should the owners of the land decide themselves about the nature on their land?
Do organisations that protect nature disadvantage the residents
Would the town/village develop faster without the national park
Rotated factor matrix in the factor analysis conducted
1—nature conservation hinders development
2—it is worth extending the protected areas
The national parks makes life difficult for people here
Organisations protecting nature disadvantage residents
Without the national park the town/village would develop faster
It is worth extending the sites of protected nature in this area
It is important that the municipality has been included in the European network
People move here so as to live closer to protected nature
It is also important to protect nature outside of the national parks
National Versus European Forms of Nature Conservation in the Opinion of Local Communities
As in the case of local government members, the opinions of local communities concerning Natura 2000 are mostly based on their attitude to the conservation system currently in use in Poland. All of the municipalities studied that were included in the survey have national parks within their boundaries, or are found in their vicinity.
Local and Regional Connotations of Introducing New Nature Conservation Programmes
The results of this study were affected by the characteristics of the municipalities and regions where it was conducted. Both the general assessment of the Natura 2000 programme, the opinion or the way it was expressed by local governments and residents of the alpine bioregion were clearly different from that of the continental bioregion. In 64% of alpine municipalities and 42% of continental municipalities, opinions about the proposed site boundaries were unequivocally negative (Table 2). Note that the percentage of positive opinions was similar in both regions presented whereas more negative opinions came from the local governments of the alpine region. Both regions also differ in the language they use to justify their opinions. Comments from the continental region are more often moderate, written in official language, whereas in those coming from the alpine region, the proposed designations of the Natura sites were expressed in a more emotional way. In both regions, however, similar arguments were used in support of negative opinions, or in requests for modification to the designated boundaries and in the examples where possible conflicts were identified, which may occur after the Natura sites are established in the planned locations.
The results of the survey also reveal considerable differences, especially in terms of activities currently undertaken by their residents and those planned for the nearest future. Residents’ plans differ between individual municipalities: statistically significant differences were noted in such areas as the intention to establish their own businesses (χ2 = 25.322, P < 0,005) run agrotourism (χ2 = 57.941, P < 0,005) or apply for subsidies for farming (χ2 = 28.545, P < 0,005) (Table 3). The most entrepreneurial plans involving their own businesses are noted for residents of the Cisna municipality (located in a popular tourist area) and of the Jabłonka municipality (with the highest population among municipalities surveyed). More than half of the Cisna residents hope to live on agrotourism and about 20% of those in Orawa region municipalities (Jabłonka and LipnicaWielka). The opposite proportion is noted for plans for farming subsidies, which are declared by every second resident of Jabłonka and LipnicaWielka, every third resident of Cisna and every fourth resident of Komańcza.
Shares of potential conflict groups and beneficiaries among residents of the studied municipalities
Running an agrotourism business
Running an organic farm
Owners of developed land
Owners of cultivated agricultural land
Owners of meadows
Owners of land for development
Owners of forest
The individual categories of both the conflict groups and beneficiaries identified in the study are often interlinked. Often, one person runs more than one type of business because they own several types of land. The Orawa region and the Komańcza municipality in the Bieszczady mountains contain the highest numbers of beneficiaries who can make use of the programmes for farmers and for maintaining meadows (Table 5). The Komańcza municipality also has the highest percentage of people engaged in organic farming. In the Cisna municipality, however, the vast majority of people make their living from running agrotourism businesses. As regards conflict groups, the vast majority in all municipalities were noted amongst those who own plots with developments—they make up over two thirds of the residents in all the studied locations. The greatest share of people who own plots for development is found in the Orawa municipalities. Although this share is significantly lower than in the case of those owning already developed plots, the risk of conflict is potentially greater as a result of potential obstacles in carrying out any building plans. In the Orawa municipalities, the percentage of people who own woodland is also significant—at least three times that of the municipalities studied in the Bieszczady mountains.
The Value of New Protected Areas for Local Communities
New solutions to the nature conservation sector, especially those imposed as top-down decisions, are often reluctantly received by local communities (Lee and Roth 2006). This is most often the case for people living around national parks, but also around other protected areas, included those covered by the Natura 2000 network (Burger 2005, 2007, 2008; Lewis 1996; Stoll-Kleeman 2001). Similar to our present study, the residents of protected areas appreciate the neighbouring natural environment and agree with the necessity of the actions of the institutions managing natural resources. They often appreciate the methods of such actions. But their understanding of the nature conservation principles is seldom complete. Consequently, in spite of their friendly attitude, various conflicts emerges, as in the case of the municipalities we studied. Such misunderstandings most often pertain to the physical development of areas adjacent to those protected, as well as decision-making issues concerning nature conservation on private land (Daniels and Walker 1997; Depoe and others 2004; Simmons 2001). All of the arguments mentioned above could be heard from members of local management that were respondents to this study.
Acceptance/Non-Acceptance of Natura 2000 Governance Policy
In the case of the Natura 2000 programme, the local governments and residents of municipalities located in the protected areas are of the opinion that the lack of the programme’s acceptance primarily stems from the unavailability of information and hence a lack of knowledge and false opinions regarding the beliefs of other groups. Members of local governments also point out bad communication at various decision-making levels: from the national to the local (International Union for Conservation of Nature 2005; Stern 2004). In the case of Poland the communication system between the representatives of the Polish Ministry of the Environment responsible for the Natura 2000 implementation and local governments was most severely criticized. In contrast, the local government’s position was seen as consistent with that of their community.
The opinions of members of Polish local governments and communities do not fundamentally differ from those observed in other EU countries, where the introduction of practically all phases of Natura 2000 has been and still is accompanied by general reluctance and consequent conflicts (Apostolopoulou and Pantis 2009; Hiedenpää 2002). That is why current trends in managing the protection of biodiversity in the EU are increasingly often perceived as needing to be complemented with bottom-up initiatives. The latter seem essential primarily to legitimize conservation programmes that are implemented and result in these programmes’ efficient functioning (Kluvánková-Oravská and others 2009; Winter 2003).
Providing Information About the Programme
It seems thus justified that Poland should participate more widely in European communication programmes firstly due to economic reasons and secondly to the satisfaction of communities. The share of European funding in Natura 2000 implementation in Poland has been very high so far and accounted for as much as 65% of the total expenditure whereas the rest has been completed by the state budget and funds from other institutions (Jaśkiewicz 2008). One of the most promising EU programme Poland has just entered is the EU LIFE-Nature Programme (currently called LIFE+) (Silva and others 2009). Its effectiveness—expressing in an increase in business and activity on the Natura 2000 covered areas—significantly depends on the proper timing of implementation, the scale of the actions, their relevance, as well as the involvement of local communities in the planned actions (Audretsch and Keilbach 2006; Sundseth 2004). Completing such programmes at a national level, which, although very few and much delayed, are well received by society. A good example is the initiative of local authorities of the Malopolska Province, who themselves with assistance of the EU funds, organised a series of information (consultation) meetings for residents, investors and decision-makers of municipalities located in Natura 2000 areas (oral information from employees of the Regional Directorate of Environmental Protection; Cent and others 2010). People planning communication programmes should take into account local social factors. It is especially important in countries in transition, such as Poland, which are primarily oriented at avoiding or resolving existing conflicts connected to the introduction of new forms of nature conservation (Beltran 2000; Peters 1999; Pujadas and Castillo 2007), and not in order to manage the protected sites in a better way as is the case in the richest countries (Borrini-Feyerabend and others 2004; Ludwig and others 2001).
Nature Conservation Governance: Multi-Level Structure
One of the consequences of poor communication between decision-makers is the residents’ lack of participation in the decision-making processes, especially those concerning physical development. This problem seems more complex in Poland, as it depends on many factors. In Poland, the socialist system strongly affected the functioning of public administration and the development of civil society (Gliński 1994, 1996). As compared to Western countries, the nature conservation sector still has less support from the population. Also, such a tradition persists of small participation in social initiatives (Bell and others 2008; Cent and others 2007). Finally there are no clear legal regulations for participatory approaches. For instance, with regard to national parks, this issue has practically been neglected in the national acts of parliament regarding nature protection (Dz.U.2008.201.1237, Dz.U.2004.92.880). On the one hand, the dissatisfaction of local communities associated with not being treated as a party in local decision-making is understandable. On the other hand, even in areas where local communities are encouraged to such participation, (e.g., by national park managements) they often have groundless and false convictions about the harmful consequences of the conservation measures planned. Consequently, the local communities do not support their undertaking and implementation (Terlecka and Górecki 1998).
The effect of the lack of participation in the management of protected areas is additionally aggravated by the fact that people are generally positive about nature conservation activities as long as it does not interfere with their personal or institutional goals and needs (Young and others 2005; Chuenpagde and others 2004). Convincing society and political activists of the need for the programme will depend on, amongst other things, whether nature conservation is perceived as necessary and factually justified (US Environmental Protection Agency 2001). People surveyed in this study were willing to invest in areas that are relatively harmless to the local natural environment, but at the same time they complained about Natura 2000 hindering business activity. Depending on local conditions, the residents’ determination concerning individual or the municipality’s development can be so high that it veils the possible consequences to the natural environment. But if the locals are familiarised in advance with the negative impact on nature of the project, or other business activity, their resistance to the implementation of a harmful undertaking will dwindle (Mendez-Contreras and others 2008).
Interdisciplinary Approach: A Way to an Effective Sustainable Development Policy
Opinions regarding and support for the Natura 2000 programme often vary among places or regions. It seems understandable that there are differences in business activity undertaken now and those planned for the nearest future among residents of individual places and regions, and opinions concerning the expansion of protected areas. Similar dependence can be noted when viewing the opinions of local governments on the territory of almost the whole of Poland. Poland as a new EU member country has become a beneficiary of relatively high union funds intended for investment, including those most controversial in terms of environmental protection (Kiejzik-Głowińska and Samsel 2006). Their implementation was blocked by the work going at the same time to determine Natura 2000 sites. This, in turn, led to local governments and communities growing frustrated, especially in underinvested areas, waiting for years for specific projects on their area to be completed. The practical implementation of principles, including those of sustainable development, which go beyond the traditional forms of conservation, still seems ineffective, in both the conservation and investment sectors (Najwyższa Izba Kontroli 2008).
The anxiety regarding financial matters, often mentioned by local governments, are not associated with the possible hindering of economic development in their place or region due to the introduction of Natura 2000, but also the very “service” of the programme. Local governments from all municipalities studied, in their opinions clearly draw attention to the costs of managing the protected areas as well as the higher costs of other indirectly linked procedures, which they will have to meet. Generally, decision-making in nature conservation in Europe, particularly in connection with the designation of the Natura 2000 network, does not sufficiently make use of cost effective analysis (Maiorano and others 2007). This mistake was also made at least partly in the process of designating the sites in Poland (Makomaska-Juchiewicz and Tworek 2003). A direct consequence of this situation is the underinvestment in individual tasks of the programme, including their staffing. In Poland the number of professional staff trained for Natura 2000 is still insufficient. Instead, the Ministry of the Environment delegated the responsibilities associated with the programme to the current personnel of organisations responsible for its development (i.e., Polish State Forests, National Parks, regional Water Management Authorities, etc.). The resulting shortage of staff and consequently general disinformation only increase the local governments’ reluctance to the programme (Walder and Schnell 2006).
To introduce the Natura 2000 programme in Poland and in consequence the sustainable development strategy, the authorities have to change the management of natural assets system, mainly by encompassing the wider—interdisciplinary—context comprising the social aspects of nature conservation (i.e., public participation), and creating a system allowing those aspects to be taken into consideration in practice (Bath 2005; Harwood 2000; Schwarz 2005). The experience of other countries shows that only such an attitude allows tasks of a sustainability strategy, Natura 2000 included, to be effectively accomplished. It increases the chance of a sustainability strategy to be effectively accomplished, resulting in a proper operation of the sites in the future, especially those that are designated on private land where there is a need to ensure realistic opportunities for nature conservation often dependant on the owners’ willingness to get involved in conservation and on the sympathies of the local authorities (Charbonneau 1997; Giordano 2004; The Gallup Organization 2007; Walder and Schnell 2006). It will be difficult to achieve the aims of Natura 2000 without elements being taken up by local nature conservation plans and policy. Even where a given area is densely covered by the network, its successful conservation depends on the behaviour and management of areas outside of it, which is a challenge not only for managing those areas themselves, but also for broader thinking about the needs of nature and sustainable development (Dimitrakopoulos and others 2004).
revise and modify the current approach to governance, management and physical planning. This primarily stems from the need to reconcile sustainable development tasks (economic development with those of nature conservation) and increase the effectiveness of natural resources management at all ecological and administrative levels (Grodzińska-Jurczak 2008),
encourage local communities to actively participate in the new forms of nature conservation, while at the same time ensuring the introduction of appropriate legal solutions to safeguard their interests,
take other members of society into consideration. They may indirectly reap benefits or incur losses as a result of, for example, changes in the amount of recreational use of the areas (Borrini-Feyerabend and others 2004; Worth 2002). A well introduced programme has the chance to initiate a change in the approach to nature conservation so that it is more participatory,
make use of the experience of Western European countries, as many of the problems Poland is currently struggling with have already been encountered there and successfully resolved. That is, adopt an interdisciplinary approach, namely a combination of the efforts of specialists in the natural and social sciences,
use the resources of the EU programmes in a more effective way, especially by wider and more active participation in communication programmes such as LIFE+ while continuing regional and local initiatives already underway. Communication should be conducted by interdisciplinary qualified staff providing reliable information about the principles of action of new forms of nature conservation and the aid programmes accompanying it. Intense communication should be in particular addressed at the most conflicting-prone groups, including, local governments’ representatives and legal owners of the plots included in the network.
We are grateful to the MSc students at the Jagiellonian University (Krakow) for taking part as interviewers in this project. Thanks also to the representatives of Jabłonka, LipnicaWielka, Komańcza, Cisna governments for their fruitful co-operation and ongoing support. Finally, thanks go to Stanisław Tworek and Małgorzata Makomaska-Juchiewicz (Institute of Nature Protection, Polish Academy of Science, Kraków, Poland) for sharing their experiences, and for their strategic advice during the project’s delivery and evaluation. The study described here was done as part of two research projects “Effectiveness of protection of Natura 2000 sites and social aspects of the programme’s implementation in Poland” funded by the Ministry of Science and Higher Education (grant no. N305 094 32/3185) and “Information, education and communication for the natural environment” sponsored by the Jagiellonian University (grant no. WRBW/DS/INoŚ/760).
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