ArticlePDF Available

Contribution of social science to large scale biodiversity conservation: A review of research about the Natura 2000 network

Authors:

Abstract and Figures

Successful conservation needs to be informed by social science because it is closely linked to socio-economic processes and human behaviour. Limited knowledge about ecosystems' interactions with these processes currently undermines conservation efforts. This review provides a comprehensive synthesis of social science concerning the world's largest multinationally-coordinated conservation infrastructure: the European Ecological Network - ‘Natura 2000’. Based on a review of 149 publications, we analyse and discuss the main findings and outline key social-science research gaps with regard to the Natura 2000 network. The review shows that human dimension of the Natura 2000 network is complex and varies among EU Member States. In general, low level and quality of public participation in implementation of the Natura 2000 network and its management, negative public perceptions of the network, lack of flexibility of responsible authorities and insufficient consideration of the local context pose the greatest challenges to the network's functioning. Important but hitherto little studied research topics include: evaluation of participation; effects of education on potential to raise public awareness; effects of potential financing mechanisms for compensating private land-owners; economic studies on cost-effectiveness; and benefits from conservation and ecosystem services. These knowledge gaps will need to be filled for the Natura 2000 network to reach its goals.
Content may be subject to copyright.
Review
Contribution of social science to large scale biodiversity conservation: A
review of research about the Natura 2000 network
Malgorzata Blicharska
a,b,
, Ewa H. Orlikowska
c
, Jean-Michel Roberge
d,e
, Malgorzata Grodzinska-Jurczak
f
a
Swedish Biodiversity Centre, Box 7016, 750 07 Uppsala, Sweden
b
Department of Earth Sciences, Uppsala University, Villavägen 16, 75 236 Uppsala, Sweden
c
School for Forest Management, Swedish University of Agricultural Sciences (SLU), Box 43, 739 21 Skinnskatteberg, Sweden
d
Department of Wildlife, Fish and Environmental Studies, Swedish University of Agricultural Sciences (SLU), 901 83 Umeå, Sweden
e
Department of Forest Resource Management, Swedish University of Agricultural Sciences (SLU), 901 83 Umeå, Sweden
f
Institute of Environmental Sciences, Jagiellonian University, Gronostajowa 7, 30-387 Kraków, Poland
abstractarticle info
Article history:
Received 24 November 2015
Received in revised form 8 May 2016
Accepted 11 May 2016
Available online xxxx
Successful conservation needsto be informed by social science because it isclosely linked to socio-economic pro-
cesses and human behaviour. Limited knowledge about ecosystems' interactions with these processes currently
undermines conservation efforts. This review provides a comprehensive synthesis of social science concerning
the world's largest multinationally-coordinated conservation infrastructure: the European Ecological Network
-Natura 2000. Based on a review of 149 publications, we analyse and discuss the main ndings and outline
key social-science research gaps with regard to the Natura 2000 network. The review shows that human dimen-
sion of the Natura2000 network is complexand varies among EU MemberStates. In general,low level and quality
of public participation in implementation of the Natura 2000 network and its management, negative public per-
ceptions of the network, lack of exibility of responsible authorities and insufcient consideration of the local
context pose the greatest challenges to the network's functioning.Important but hitherto little studied research
topics include: evaluation of participation; effects of education on potential to raise public awareness; effects of
potential nancing mechanisms for compensating private land-owners; economic studies on cost-effectiveness;
and benets from conservation and ecosystem services. These knowledge gaps will need to be lled for the
Natura 2000 network to reach its goals.
© 2016 The Authors. Published by Elsevier Ltd. Thisis an open access article under the CC BY license
(http://creativecommons.org/licenses/by/4.0/).
Keywords:
Biodiversity conservation
Human dimension
Natura 2000
Research gaps
Review
Social science
Contents
1. Introduction.............................................................. 111
2. Methods................................................................ 111
3. Results................................................................. 113
3.1. Focusofthepublications..................................................... 113
3.2. Synthesis of the main ndings................................................... 113
3.2.1. Conservation conictsandimplementationchallenges/solutions............................... 113
3.2.2. Management ...................................................... 116
3.2.3. Perceptions,attitudesandvalues.............................................. 116
3.2.4. Valuationandeconomics................................................. 116
3.2.5. Legalissues....................................................... 117
3.2.6. Governance....................................................... 117
3.2.7. Policyintegration..................................................... 117
3.2.8. Conservationprioritysetting ............................................... 117
3.2.9. Participationevaluation.................................................. 118
4. Discussion............................................................... 118
4.1. Main ndingsandtheirimplications................................................ 118
Biological Conservation 199 (2016) 110122
Corresponding author at: Department of Earth Sciences, Uppsala University, Villavägen 16, 75 236 Uppsala, Sweden.
E-mail address: malgorzata.blicharska@geo.uu.se (M. Blicharska).
http://dx.doi.org/10.1016/j.biocon.2016.05.007
0006-3207/© 2016 The Authors. Published by Elsevier Ltd. This is an open access article under the CC BY license (http://creativecommons.org/licenses/by/4.0/).
Contents lists available at ScienceDirect
Biological Conservation
journal homepage: www.elsevier.com/locate/bioc
4.2. Researchgaps.......................................................... 119
Acknowledgements............................................................. 120
AppendixA. Supplementarydata...................................................... 120
References................................................................. 120
1. Introduction
Conservation science is characterised by a tight coupling of social
and natural systems(Kareiva and Marvier, 2012). Successful conserva-
tion is not solely contingent on ecological knowledge, but should also
incorporate human behaviour and the resulting social processes which
eventually inuence the status of biodiversity (Ban et al., 2013; Fox et
al., 2006). It is vital for conservation professionals to understand the fac-
tors shaping human-environment interactions, particularly human
choices concerning the use or conservation of natural resources
(Mascia et al., 2003). For example, the human-induced global water cri-
sis endangers not only human societies, but also affects freshwater bio-
diversity (Vörösmarty et al., 2010). Anthropogenic global climate
change is not only posing challenges to humans, but is also perceived
as one of the most serious threats to the planet's biodiversity
(Malcolm et al., 2006). Moreover, it has become obvious that conserva-
tion measures cannot be fully successfulif poverty issues are not tackled
(Adams et al., 2004). Therefore successful conservation requires recog-
nition and understanding of the value of social science research, i.e. re-
search that uses conceptual and theoretical underpinnings of social
sciences, such as sociology, human geography, social policy, social psy-
chology, political sciences, economy, public communication and man-
agement to investigate human behaviour and associated social
processes (Bryman and Teevan, 2005).
However, there is an increasingly recognised gap in understanding
and tradition of co-operation between natural and social scientists,
and particularly a lack of appreciation of social science knowledge in
practical operation of conservation policy (Liu et al., 2007). This prob-
lem needs to be addressed if we want to produce knowledge that
truly contributes to solving today's conservation challenges (Fox et al.,
2006; Nyhus et al., 2002). Comprehensive syntheses of social science re-
search concerning major conservation initiatives may contribute to
building that knowledge.
One key conservation action worldwide is the development of large-
scale networks of protected areas (Rodrigues et al., 2004). In spite of the
fact that over 200,000 protected areas cover ~14% of the world's land
area (Deguignet et al., 2014), there are very few coordinated networks
of protected areas aiming at continental-scale conservation. Examples
of such networks stretching across national borders include the Yellow-
stone-to-Yukon Conservation Initiative in North America and the Euro-
pean Ecological Network –‘Natura 2000. Thelatter is the world's largest
multinationally coordinated conservation infrastructure.
As the centrepiece of the European Union's (EU) biodiversity conser-
vation policy, the Natura 2000 network was created based on the Article
3 of the EU's Habitats Directive (CEC, 1992). It aims at protecting habi-
tats and species of EU interest, listed both in the Habitats Directive
and Birds Directive (CEC, 1979, 1992). The Natura 2000 network plays
a key role in protection of biodiversity in the EU territory by assuring
the long-term survival of Europe's most valuable andthreatened species
and habitats(EC, 2015a). The network consists of Special Protection
Areas SPA (for protecting species included in Birds Directive), Special
Areas of Conservation SAC (species and habitats included in Habitats
Directive), and also includes marine environments (EC, 2015a). Natura
2000 has been implemented gradually, starting in 1992 in the 12 EU
countries, followed by other countries joining the European Union after-
wards. This initiative is considered critical for the implementation of in-
ternational conservation policies such as the Convention on Biological
Diversity (UN, 1992) and the European Strategy for Biological Diversity
(EC, 2011). The Natura 2000 network considerably differs fromprevious
conservation systems in Europe as it goes beyond a direct ban on dam-
aging plants or killing animals and focuses on socially sustainable con-
servation harmonising the maintenance of species and habitats with
economic, social and cultural human needs (Grodzińska-Jurczak,
2008). Because of that the meaningful involvement of affected stake-
holders is seen as necessary for the network's success (EC, 2000).
The entire implementation process, starting from the selection of the
protected sites till development of management plans, met opposition
from various stakeholder groups in almost all EU Member States
(Alphandéry and Fortier, 2001; Hiedanpää, 2002; Krott et al., 2000;
Pietrzyk-Kaszyńska et al., 2012; Visser et al., 2007). The problems in im-
plementation called for a proper assessment and monitoring of the net-
work, and eventually led to the development of more effective
implementation recommendations (Bouwma et al., 2008; Kati et al.,
2015). In 2015, the European Commission initiated a process of tness
check on the implementation of the Birds and Habitats Directives. The
tness check aims at scrutinising the effectiveness, efciency, relevance
and coherence (EC, 2015b) of all stages of the network implementation,
from the designation through inventory and monitoring to the develop-
ment of management plans for particular sites.
Considering its importance for European nature conservation Natura
2000 has also been the subject of an increasing research interest, partic-
ularly from conservation scientists (Popescu et al., 2014). To achieve a
good functionality of the network, there is a need for knowledge not
only on the ecological conservation and management issues relevant
to the Natura 2000 (e.g. status ofspecies and habitats, ways of managing
the sites), but also on key social, economic, political and managerial re-
alities potentially inuencing its effectiveness. In a recent revie w of pub-
lished research on Natura 2000, Popescu et al. (2014) concluded that
ecological research prevails, while social, economic and policy research
on the network is underrepresented. Still, there isa non-negligible body
of research focusingon the social aspects of the Natura 2000. However,
perhaps as a consequence of its broad scope, there have been so far no
attempts to comprehensively review this research. In this paper, we
present a review of thepublished scientic literature focusing on the so-
cial aspects of the Natura 2000 network, expanding Popescu's et al.
(2014) work by analysing in depth the ndings of the existing social sci-
ence studies. The aims are to (1) synthesise the existing social scientic
knowledge on Natura 2000 and identify future research needs, and (2)
inform conservation professionals and other relevant actors about the
broad spectrum of challenges and solutions relevant to the implementa-
tion and functioning of the Natura 2000 network.
2. Methods
We performed an in-depth review and analyses of published En-
glish-language scientic papers applying a social science perspective
in conservation research focused on Natura 2000. We are aware of the
fact that some social aspects of Natura 2000 may be addressed in the
grey literatureor local manuscripts or reports. However, here we fo-
cused on the peer-reviewed literature only because (1) we wanted to
concentrate on scientic knowledge, with a reliable level of scientic
rigour, (2) it would have been logistically impossible to directly cover
the diversity of grey literaturecharacterised by a multiplicity of lan-
guages, and (3) the peer-reviewed literature builds to a large extent
on analyses of various types of non-scientic texts (reports, legal texts,
articles, etc.) published in different languages, and hence our approach
111M. Blicharska et al. / Biological Conservation 199 (2016) 110122
does indirectly capture substantial parts of the information contained in
these publications.
We collected the data through desk research. The main unit of our
analysis was an individual article. We applied a mixed-mode social sci-
ence research methodology (qualitative and quantitative) that allowed
for a broader perspective of gathering and analysing of the data. We
used the Webof ScienceCore Collection database for searching the lit-
erature. We searched for the phrase Natura 2000in the topiceld of
the database for the period 19982014. From the initial set of publica-
tions, we only retained studies that were either primary original re-
search or reviews; thus, we removed publications categorised as
correspondences, letters, responses, commentaries, policy perspectives,
etc. Conference proceedings were only included if published in a peer-
reviewed journal. We also removed publications in other languages
than English, even if they had an English abstract. After this selection
we ended up with 664 publications (as of January 1st, 2015).
We performed an initial scanning of selected publications to retain
only articles that addressed social science or included a social analysis
component (e.g. inter, multi or transdisciplinary studies combining so-
cial sciences with other disciplines). After that preliminarily scanning,
248 publications were classied as belonging to the social sciences or
as having a social-science component. A review of theecological litera-
ture about Natura 2000 will be published elsewhere (Orlikowska et al.
unpublished results). Out of the 248 publications retained for the pres-
ent review, we further removed 46 after in-depth examination, either
because they were not research/review papers or because they did not
address Natura 2000. For example, if a paper had Natura 2000merely
in the abstract but did not focus at all on any aspect of Natura 2000, we
removed it from the analysis. We removed another 39 publications be-
cause in-depth examination revealed that they did not include any so-
cial-science analysis. Finally, we removed 14 publications due to
unavailability of the full-text versions. Thus, 149 publications were left
for in-depth analysis, 112 classied as social science and 37 including
some social-science analysis. The Results section below is based exclu-
sively on these publications. However, in the Discussion section we
also refer to some relevant studies not identied by our search, e.g.
studies published after the closing date of our literature search.
Note that 91 of the 149 publications retained for the present study
were included in the recent review by Popescu et al. (2014).Ourre-
view includes 58 papers not analysed by these authors, while 29 of
the papers they included were not retained for the present study.
These differences are most likely due to the different inclusion
criteria used in the two studies.
The rst step of the analysis consisted in distinguishing eleven core
categories of papers (Table 1) based on their main focus, identied
through reading the title and abstract of each publication. We then
used a qualitative content analysis method (Bryman and Teevan,
2005) for analysing all the papers. We utilised an open coding approach
without pre-dened codes. Thus, the codes emerged in the course of
analysis and involved identication of the most important issues and
the key ndings of the papers. We analysed each of the eleven catego-
ries of papers separately using specic codes for each particular catego-
ry of papers. Because some of the initial categories were of a relatively
broad scope, the analysis led to the identication of a set of sub-catego-
ries within ve of the main categories of papers (see Table 1 for expla-
nation). In the next step of the analysis, we used memos (Glaser and
Strauss, 2008) for summing up information on the identied issues
and key ndings. Using the memos and building on the issues identied
in them, we created summaries of the results by categories and
discussed their determinants in the context of the main socio-economic
ndings for each category (see Results section). At the same time, we
created a short summary of each paper (see online Appendix). We
also recorded the country (or countries) investigated by each of the pa-
pers. Finally, we scrutinised the scope of all papers(based on their cat-
egories and sub-categories) to identify the most commonly addressed
topics and the main research gaps.
Table 1
Categories and sub-categories used to structure the review process.
Category Contents of the papers Sub-categories
Conservation
conicts
Includes studies that analyse
conservation conicts, e.g. actual or
potential conicts between N2000 site
protection and resource use, human
well-being or tourism, potential
problems in industrial/infrastructure
development within or in the vicinity of
N2000 sites, threats to N2000.
Conservation vs.
use
Conservation vs.
development
Threats to N2000
sites
Combining
tourism and
conservation
Policy
Implementation
challenges and
solutions
Includes studies that address different
challenges faced during at least one
stage of the N2000 policy
implementation (including site
designation, development of
management plans, monitoring, etc.),
and/or presents potential solutions to
these challenges.
a
Management Includes assessment of the human
dimension of management practices,
adaptive measures or need for
appropriate management plans to
maintain species in favourable status,
methodological studies on the
development of management plans for
N2000 sites or planning conservation
action, studies proposing tools,
approaches and frameworks for
development of management plans and
conservation strategies, etc.
Tools, methods,
approaches
Management and
CC
Management
evaluation
N2000 impact on
management
Restoration
management
Need for
management
Perceptions,
attitudes and
values
Includes studies that investigates
attitudes towards and perceptions of
various aspects of the N2000 network,
attitudes towards particular N2000
sites or their management, people's
awareness of the N2000, etc.
Local attitudes
Perceptions of
management
Recreation and
tourism
Other (see Online
Appendix)
Valuation and
economics
Includes studies that investigate costs
or benets of the N2000 establishment,
management measures or restrictions,
effectiveness of N2000 conservation
funding, valuation (both use and
non-use values) of the N2000 site,
incentive mechanisms, etc.
Preferences and
WTP
Benets from
N2000
Cost-effectiveness
Costs of N2000
Incentives
Legal issues Includes studies on legal aspects of
N2000, e.g. analysis of legal acts and
their consequences, or of some specic
topic related to N2000 in relation to
legal requirements.
National level
enforcement
Legislation
effectiveness
CC in N2000
legislation
ES in N2000
legislation
Governance Includes studies on different aspects of
governance related to N2000, e.g.
governance shifts due to
implementation of the N2000, changes
in possibilities of different actors to
inuence governance.
n/a
Policy integration Includes studies that analyse N2000
policies that have been formulated and
used during the designation and
management processes, and potential
problems connected with their relation
to policies belonging to other sectors,
e.g. potential overlaps, possibilities or
barriers for integration of different
policies.
n/a
Conservation
priority setting
Includes studies that focus on
determining conservation priorities or
utilise systematic conservation
planning with regard to N2000 which
include socio-economic indices or
criteria.
n/a
Participation
evaluation
Includes studies that focus on
evaluation of participatory processes in
n/a
(continued on next page)
112 M. Blicharska et al. / Biological Conservation 199 (2016) 110122
We are aware that the division into particular categories and sub-cate-
gories is to some extent subjective and arbitrary, as many papers ad-
dress more than one issue and thus one paper could theoretically be
included into two or more categories simultaneously. However, to
allow a structured analysis we needed a clear division into categories.
Thus, in cases where a particular paper tted more than one category,
we assigned the paper to the category which represented the main
focus of the paper.
Even though some of the papers had a wider scope than Natura
2000, in the present review we only consider the information
concerning this network. Thus, if a paper was about different kinds of
protected areas including Natura 2000 sites, we only considered the
contents which specically concerned Natura 2000.
3. Results
3.1. Focus of the publications
Most of the publications belonged to the category of Conservation
conicts(23 publications), Implementation challenges and solutions
(21), Management(20), Perceptions, attitudes and values(17), Valu-
ation and economics(16), Legal issues(11), Governance(8), Policy
integration(5), Conservation priority setting(4), and Participation
evaluation(4). The remaining 20 publications were classied as
Others(Fig. 1).
The Conservation conictscategory focused mainly on local land
use or infrastructure development in potential conict with conserva-
tion in particular locations (Fig. 2). Many papers focused on particular
challenges faced by Natura 2000 and possible solutions (papers from
Implementation challenges and solutionscategory) or tools and
methods for practical work with Natura 2000 (11 out of 20 papers in
the Managementcategory) both groups studying the factors
inuencing the practical implementation of the network. Within the
category Perceptions, attitudes and values, the largest topic was the at-
titudes of local communities (10 out of 17 studies) (Fig. 2). Valuation/
economic studies in most cases investigated preferences and willing-
ness to pay for Natura 2000 conservation or management (5 out of 16
studies) or cost-effectiveness of conservation (5 out of 16 studies).
Twenty-ve publications presented studies encompassing the entire
EU. In terms of particular countries, Greece had the highest level of rep-
resentation in the publications, followed by the Netherlands, UK, Ger-
many, Poland, Romania and Italy (Fig. 3). In general, the EU-15
countries (i.e. countries that had joined the EU prior to 1st May 2004)
had more (altogether 117, mean 11 per country) publications than the
countries that joined the EU in and after 2004 (altogether 40, mean 4).
Important exceptions were Belgium and Sweden, two EU-15 countries
with only one publication each, as well as Poland and Romania, two
late-accession countries with relatively large numbers of publications
(Fig. 3). At the level of the whole EU, most of the publications concerned
either legal issues (4 papers), followed by valuation, governance and
implementation challenges and solution studies (3 papers in each of
these categories). Most publications about management were conduct-
ed in Italy (5papers), followed by Greece andthe Netherlands (4 papers
each), while Romanian studiesfocused on conservation conicts (6 pa-
pers) (Fig. 4).
3.2. Synthesis of the main ndings
In this section, we synthesise the ndings of the reviewed articles for
the different main categories (Table 1). We do not include the category
Otherbecause it represents studies that lack common ndings. A short
summary of all the reviewed publications (including those in category
Others) is included in the online Appendix.
3.2.1. Conservation conicts and implementation challenges/solutions
Conservation conictsand Implementation challenges and solu-
tionscategories are related and therefore we address them together.
The potential conicts in implementation and functioning of thenet-
work were those between conservation under Natura 2000 and differ-
ent kinds of land and water use, such as forestry (Hiedanpää, 2002;
Pecurul-Botines et al., 2014), farming (Gonzales et al., 2009; Oana,
2006; Visser et al., 2007), shing (Pedersen et al., 2009; Zaharia et al.,
2014; Zaharia et al., 2012), ship navigation (Freitag et al., 2008), as
well as industry and infrastructure development (Andrulewicz et al.,
2010; Bielecka and Różyński, 2014; Wszołek et al., 2014). Some studies
Table 1 (continued)
Category Contents of the papers Sub-categories
relation to N2000 implementation and
operation, e.g. participatory aspects of
the designation processes of particular
sites or the whole network, or related to
the N2000 network.
Other Studies that do not t in any of the
categories above.
See Online
Appendix
Note: CC = climate change; ES = ecosystem services; N2000 = Natura 2000; WTP =
willingness to pay.
n/a not applicable; small category including fewpapers, no need to have sub-categories.
a
The category Implementationchallenges and solutionsis a broadcategory including
studies that analyse challenges and solutions from very different perspectives and at dif-
ferent stages of Natura 2000implementation.Because of that inherent diversityat the lev-
el of individual papers, it was not possible to dene distinct sub-categories that would
include meaningful numbers of papers.
Fig. 1. Number of publications belonging to the main categories.
113M. Blicharska et al. / Biological Conservation 199 (2016) 110122
Fig. 2. Numberof articles belonging to the different sub-categories within maincategories. Only ve categories are included, as other categorieswere not divided into sub-categories (for
explanation see Table 1). A: conservation conicts; B: management; C: perceptions attitudes and values; D: valuation and economics; E: legal issues.
Fig. 3. Number of articles presenting research pertaining to individual EU countries. Note that in some articles more than one country was included, and thus one article could be listed
under more than one country. Both social-science articles and articles with a social-science componentare included.
114 M. Blicharska et al. / Biological Conservation 199 (2016) 110122
in the Conservation conictscategory investigated the impacts of dif-
ferent anthropogenic activities on Natura 2000 areas (Muntean et al.,
2013; Pîrvu and Petrovici, 2013), with a particular focus on agro-tour-
ism (Ciapala et al., 2014; de Noronha Vaz et al., 2012). According to
Hiedanpää (2002),the administrative environmental actions disturb
localities in intended good ways, but also in many unintended and sur-
prising wayswhich can be perceived by local people as harmful and
immoral. However, whether the conict will arise depends on the
local institutional context (Pecurul-Botines et al., 2014).
As key approaches for addressing existing conicts, mitigating
threats, and improving implementation and functioning of the network,
differentauthors suggested cooperation and improved communication
with the resource users, as well as development of management plans
for each site using participatory approaches (Pedersen et al., 2009;
Pîrvu and Petrovici, 2013; Visser et al., 2007; Zaharia et al., 2014). In-
deed, increased social support of formal rules was considered a key to
successful implementation (Beunen et al., 2013). Such cooperation can
elicit valuable local knowledge helpful to conservation (Pedersen et
al., 2009), but requires meaningful involvement of a wide spectrum of
stakeholders (Ferranti et al., 2010). Hiedanpää (2005) described such
involvement in terms of a transactive approach,i.e.aparticipatory,
discursive, engagingly organised, sensitively operated, and decisively
powerful approach. Participatory approaches should operate within
and be sensitive to the local and regional economic context
(Hiedanpää, 2002), address conicting issues across different sectors
(Andrulewicz et al., 2010) and enable land users to understand theben-
ets from particular Natura 2000 sites (Oana, 2006). This is particularly
important with regard to farming: to avoid the ongoing in the EU land
abandonment, there is a need to win the minds and hearts of future
farmers(Visser et al., 2007). The latter need to be convinced about
the benets of conservation (Kamal and Grodzinska-Jurczak, 2014;
Prazan et al., 2005) as they may fear potential limitations imposed by
Natura 2000, including compromises linked to their place identity
(Welch-Devine, 2012). This can only be accomplished when both
sides (conservation and food production) acknowledge the impor-
tance of each other's priorities (Visser et al., 2007). Also, as conserva-
tion may imply signicant costs for the landowners, there may be a
need for nancial instruments such as public funding or tax reduc-
tions (Rojas-Briales, 2000). The need for sufcient funding was
underlined in several studies (Ferranti et al., 2010; Hochkirch et al.,
2013; Iojăet al., 2010), for example as regards nancial compensa-
tion schemes for landowners (Stancioiu et al., 2010) and activities
that would increase general conservation awareness (Hochkirch et
al., 2013). Similarly, Ciapala et al. (2014) suggested that tourism
and recreation are inherent element of human inuence on biodi-
verse areas, and that such activities need to be considered when
planning for and managing Natura 2000 sites. To address that,
Parolo et al. (2009) proposed an optimisation model for allocating
tourism infrastructure.
Regarding the key challenges of the Natura 2000 implementation,
the studies identied problems pertaining to legitimacy of the imple-
mentation process (Alphandéry and Fortier, 2001), low capacity of the
state in implementation (Apostolopoulou and Pantis, 2009) or weak-
nesses in the scienticwork(Alphandéry and Fortier, 2001). A lack of
proper participatory approaches implemented at the local level
(Alphandéry and Fortier, 2001; Apostolopoulou and Pantis, 2009; Iojă
et al., 2010) was also frequently mentioned. Even in cases where partic-
ipation took place, emphasis on legal procedures could reduce the qual-
ity of deliberation (Beunen et al., 2013). On the other hand, some
studies underlined that EU accession and associated implementation
of EU policies provided new opportunities for participation of local ac-
tors and better cooperation among governmental institutions rarely
used so far, especially in post communistic countries (Prazan et al.,
2005).
Lack of clearimplementation goals and discrepancy between stated
and actual goals can also compromise the national-level implementa-
tion of the Habitats Directive (Apostolopoulou and Pantis, 2009). In ad-
dition, superimposing the Natura 2000 sites onto existing (e.g. national)
systems of protected areas may lead to duplication of administration
and legislation, as well as overly complex protection systems
(Papageorgiou and Vogiatzakis, 2006). For example, in Romania the
Natura 2000 network overlapped at ~96% with existing protected
areas, with some sites having up to three different protection forms
(Iojăet al., 2010).
Alphandery and Fortier (2010) emphasised thatthe implementation
of the Habitats Directive is a non-linear, at times chaotic process that oc-
curs at different scales from thelocal to the Europeanlevel. In relation to
this complex process, some authors highlighted the crucial role of local
actors (Borrass, 2014). Ferranti et al. (2010) suggested education and
training of local authorities to improve the practical implementation
and Louette et al. (2011) proposed the development of regional conser-
vation objectivesas a means to bridge thegap between localand nation-
al interests. Several authors underlined the needfor better cooperation
among national-level authorities (Prazan et al., 2005) and the impor-
tance of inter-sectoral cooperation (Papageorgiou and Vogiatzakis,
2006; Sarvasova et al., 2013). Alphandery and Fortier (2010) argued
that proliferation of procedures and provisionality in implementation
are natural elements of the Natura 2000 implementation, and that
they do not necessarily imply inefciency of the government. Beunen
et al. (2013) underlined the need to take into account the particular
context and interests in the implementation process. Beunen and van
Assche (2013) cautioned against the blindness of legalismand
Fig. 4. Number of publications in each category for individual countries with 10 papers. Both social-science articles and articles with a social-science component are included.
115M. Blicharska et al. / Biological Conservation 199 (2016) 110122
suggested exible local planning as the best means of enabling space for
deliberation of different interests when implementing Natura 2000.
Once we recognize that formal rules can never be sustained without
public support and we understand that public narrative determines
their success, we can nolonger ignore this dimension of nature conser-
vation in research and practice(Beunen et al., 2013), as the battle for
biodiversity will be won or lost at local levels(Bryan, 2012).
3.2.2. Management
A large proportion of the papers in this category (11 out of 20) pro-
posed or examined different methods to facilitate the planning of man-
agement activities in Natura 2000 sites and support the development of
management plans for these sites. These studies most commonly pro-
posed participatory approaches to knowledge production, scenario de-
velopment and planning of management activities (Bots et al., 2011;
Gil et al., 2011; Graziano et al., 2008; Oikonomouet al., 2011). For exam-
ple, Ernoul et al. (2011) and Teoli and Battisti (2011) proposed the use
of Open Standards for the Practice of Conservation, adapted to the local
specics of each site, that promote participatory processes for adaptive
management. Other approaches took into account the human dimen-
sion by using indices of human activities in management planning
(Cortina and Boggia, 2014) or adopting an ecosystem services perspec-
tive (Scolozzi et al., 2014). The remaining studies were of a very diverse
character. They focused, for example, on evaluating the management
(Ganatsas et al., 2013; Morris et al., 2014; Winter et al., 2014)orimpli-
cations of particular policies for the Natura 2000 network (Fock, 2011).
A number of recommendations have been made for the design of
participatory process in management planning. For example, Bots et
al. (2011) proposed that the process should be set up to favour open-
ness, protection of the actors' core values, use of relevant knowledge
and possibility to acknowledge uncertainties; Oikonomou et al. (2011)
emphasised the necessity of considering the social value judgements
of different actors; and Gil et al. (2011) underlined the need for partic-
ipation and co-responsibility of all relevant stakeholders. Also,
Malatinszky et al. (2014) emphasised the necessity to set a priority
order of conservation aims at an early stage of management planning,
based both on science and the needs and interests of relevant stake-
holders. The issues identied in this set of papers included the lack of
time, resources and qualied facilitators that could serve the participa-
tory process (Ernoul et al., 2011) and lack of exibility of authorities
due to strict regulations (Malatinszky et al., 2014). According to
Malatinszky et al. (2014),management planning should be based on
current, exact, relevant ecological and social circumstances, and histor-
ical land uses. Therefore, this process cannotbe simplied into following
a planning scheme. It was also underlined that, to improve effective-
ness of management schemes, legal provisions concerning manage-
ment need to be matched with local capacity (Morris et al., 2014).
According to Cortina and Boggia (2014), a multi-criteria approach
that incorporates both the ecological and the human dimension is par-
ticularly useful for Natura 2000 management planning, as it enables ad-
dressinga multidimensionaldecision process andthe complex nature of
biodiversity itself. Also Soane et al. (2012) underlined the multidimen-
sional anddynamic nature of many Natura2000 sites. These authors ap-
plied resilience theory to describe the complex socio-ecological systems
of managed alpine grasslands. They proposed that this theory can sup-
port adaptive management of Natura 2000 sites, as it offers useful in-
sights into resource management and in particular for nature
conservation interest sites, by focusing more on dynamics than on an
optimal state of species assemblages.
3.2.3. Perceptions, attitudes and values
Most of the publications in this category (10 out of 17) aimed at in-
vestigating the attitudes of various (predominantly local) stakeholders
towards Natura 2000. They revealed both positive and negative atti-
tudes towards the network. It was generally considered as a good tool
for conservation (Dimitrakopoulos et al., 2010; Grodzinska-Jurczak
and Cent, 2011; Mouro and Castro, 2009; Pietrzyk-Kaszyńska et al.,
2012; Sumares and Fidelis, 2009), but also as an impediment to
economic sustainability, whereby it was often perceived as being asso-
ciated with a ban on development at practically all levels (from local
to regional) (Grodzinska-Jurczak and Cent, 2011; Sumares and Fidelis,
2009). Moreover, in some cases, the perceived dictatorship-style,
top-down implementation contributed to a low level of trust towards
the network and associated authorities (Sumares and Fidelis, 2009).
For example, many landowners in Poland viewed top-down manage-
ment of private land as questioning their capability and rights to man-
age the land. As a consequence, these landowners tended to distrust
the authorities (Kamal and Grodzinska-Jurczak, 2014). A study from
Greece (Andrea et al., 2013) showed low satisfaction of the local people
with the work of local authorities implementing the network. This case
pointed to staff deciencies and irregular funding as main obstacles for
effective management. On the contrary, a study from another Greek re-
gion (Dimitrakopoulos et al., 2010) showed greater acceptance towards
local implementing actors, but high distrust towards higher-level gov-
ernmental actors, indicating that the local perceptions may be context
dependent. In a study from Latvia (Pavasars, 2013) the problem of mis-
trust towards authorities was described in terms of existence of paral-
lel realities,i.e.thatofofcial environmentalismand that of the
everyday life of people in the countryside.
Insufcient communication (Grodzinska-Jurczak and Cent, 2011;
Tonder and Jurvelius, 2004) and weak, if any, traditions of participation
(Grodzinska-Jurczak and Cent, 2011; Sumares and Fidelis, 2009)were
underlined as factors contributing to low trust. Well organised and
more meaningful participation, stronger collaboration with local stake-
holders (Dimitrakopoulos et al., 2010; Kamal and Grodzinska-Jurczak,
2014) and better cooperation between administrative bodies (Andrea
et al., 2013) were proposed as means to improve acceptance towards
Natura 2000. The need to increase awareness towards N2000 through
proper information campaigns was also underlined (Kafyri et al.,
2012; Marmureanu and Geamana, 2012).
Numerous individual-level factors were foundto inuence attitudes
towards conservation in general and Natura 2000 in particular. These
were, for example, education, the fact of moving to the area affected
by Natura 2000 designation in adulthood, ownership of a business
(Pietrzyk-Kaszyńska et al., 2012), vested interests, institutional trust,
place identication (Mouro and Castro, 2009), socio-economic position,
culture and social backgrounds (Tonder and Jurvelius, 2004), as well as
the degree of satisfaction with the recreational experience (Torbidoni,
2011).
3.2.4. Valuation and economics
Most publications in this category encompassed studies about
people's preferences and their willingness to pay (WTP) for particular
protection measures or management plans in Natura 2000 sites
(Grammatikopoulou and Olsen, 2013; Hoyos et al., 2012; Jones et al.,
2011; Li et al., 2004; Rekola et al., 2000; Strange et al., 2007). Moreover,
some studies investigated the costs of particular measures and activities
in the sites (Jacobsen et al., 2013; Lee, 2001), services and benets from
Natura 2000 (Cruz et al., 2011) and cost-effectiveness or efciency of
Natura 2000 (Jantke et al., 2010; Wätzold et al., 2010; Wätzold and
Schwerdtner, 2005), particularly with regard to conservation funding
(Lung et al., 2014; Santana et al., 2014).
Even though people often had positive attitudes towards proposed
conservation measures (Grammatikopoulou and Olsen, 2013; Pouta et
al., 2000), their WTP depended on different factors, such as the ability
of the conservation programme to take into account the rights of land-
owners, the respondents' opinion about the importance of preserving
species and biotopes (Pouta et al., 2000), their level of knowledge
about species to be protected (Strange et al., 2007), and the level of
trust towards particular options (Jones et al., 2011). Also socio-demo-
graphics were important predictors of the WTP, as young, high-income
and urban populations show stronger support for conservation (Pouta
116 M. Blicharska et al. / Biological Conservation 199 (2016) 110122
et al., 2000).Moreover, respondents with lexicographic preferences for
nature rights were willing to pay much more for conservation than
those with preferences for property rights (Rekola et al., 2000).
Relatively few studies (3 out of 16) focused on the benets from
Natura 2000. Cruz et al. (2011) outlined ecosystem services provided
by a Special Protected Area in the Azores Islands, such as those related
to water provision, quality and regulation, and also underlined the
role of Natura 2000 in job provision. Other studies showed that the
non-use values of the protected areas can exceed the use values
(Hoyos et al., 2012; Strange et al., 2007).
Studies that focused on cost-effectiveness of Natura 2000's imple-
mentation and functioning were scarce (Wätzold and Schwerdtner,
2005). Wätzold et al. (2010) pointed to lack of long-term funding,
wrong allocation of funds between different tasks when designing and
implementing management plans, and costly EU requirements on mon-
itoring as key problems. Lung et al. (2014) concluded that the distribu-
tion of EU biodiversity funding was generally well aligned with the
existing Natura 2000 network, but not with the future needs linked to
climate change. Jantke et al. (2010) showed that the current Natura
2000 network does not cover well all endangered wetland vertebrate
species. They estimated that additional 3 million ha of protected areas
would be required to achieve coverage of all important species, at an es-
timated cost of 107 million Euros per year.
We identied only one study on economic incentives supporting
Natura 2000 implementation(Anthon et al., 2010). The paper presented
theoretical justication for using contracts when implementing the net-
work in forest areas and discussed different mechanism of payment
used in Natura 2000 contracts.
3.2.5. Legal issues
Publications about legal issues mostly investigated national-level
enforcement of Natura2000 legislation, particularly with regard to En-
vironmental Impact Assessment (EIA). The general view was that
Natura 2000legislation was still not fully incorporated into national leg-
islations (Vaiškūnaitėet al., 2012) although clear improvements could
be observed (Christensen, 2006). It was proposed that specic socio-
legal conditions must be fullled for a better implementation and func-
tioning of the Natura 2000 legislation, such as e.g. capacity of the public
interest groups and their access to national courts or the way in which
European provisions are interpreted by national courts (Slepcevic,
2009). A study by Marandi et al. (2014) suggested that protection
should be actually commenced as soon as a specic area is proposed
for inclusion in the Natura 2000 network.
Other studies investigated the effectiveness of the Natura 2000 leg-
islation. For example, Leone and Lovreglio (2004) described it as one
of the most important building blocks contributing to conservation,
and Mallard and François (2013) concluded that the Natura 2000 net-
work is the most effective instrument for conservation in relation to
road planning in France. However, they criticised the fact that the road
construction permits can be issuedfor imperative reason of major pub-
lic interest, which limits the power of the Natura 2000 legal require-
ments in practice. Weaknesses of the national Natura 2000 legislation
could be also observed in Lithuanian road planning, where EIA proce-
dures and principles did not comply with EU requirements regarding
the biodiversity impact assessment of roads (Vaiškūnaitėet al., 2012).
Two studies considered legal issues related to marine conservation
within Natura 2000. While Metcalfe et al. (2013) highlighted criticisms
against the Habitats Directive as being ill-suited for marine conserva-
tion, Rees et al. (2013) claimed that site integrityand favourable con-
servation statusare powerful legal terms that can facilitate effective
marine conservation if fully transposed into the legislation of the EU
Member States.
The remaining studies investigated the extent to which legal re-
quirements regarding Natura 2000 incorporate considerations for
some particular issues, such as climate change (Cliquet, 2014; Jackson,
2011) or the provision of ecosystem services (Kistenkas, 2014).
According to Cliquet (2014), although the Natura 2000 legislation
does not explicitly mention climate change, it contain[s] sufcient
tools to deal with the effects of climate change. Still, Cliquet (2014) ar-
gued that these tools have been insufciently implemented so far and
provided recommendations for improvement (see Table in online Ap-
pendix). On the contrary, Jackson (2011) suggested that legislation
linked to Natura 2000 may potentially undermine climate change miti-
gation efforts by challenging many renewable energy projects. The au-
thor proposed to broaden the range of acceptable alternatives, and
saw much potential in combining lower-impact renewable energy pro-
jects with Natura 2000 protection. Kistenkas (2014) advocated incorpo-
ration of the ecosystem services concept into EU's nature conservation
law, emphasising that the present legislation is too rigid to enable prop-
er assessment of these services.
3.2.6. Governance
The main focus of the papers in this category was on the effects of
the implementation of Natura 2000 and, particularly, on the accompa-
nying governance shifts. They described the general shift towards in-
creased inclusion of more relevant stakeholders (Ferranti et al., 2014),
the emergence of multilevel governance and an associated increase in
implementation legitimacy (Niedziałkowski et al., 2012; Rauschmayer,
2009) with important input from environmental non-governmental or-
ganisations (NGOs) (Börzel and Buzogány, 2010; Cent et al., 2013;
Weber and Christophersen, 2002). For example, both in Poland and
Hungary, NGOs contributed strongly to the selection of Natura 2000
sites (Cent et al., 2013). In the course of action, the agendas and actions
may change, which cancontribute to increase in professionalization and
institutionalisation of civil society groups (Börzel and Buzogány, 2010).
However, this does not always result in sustainable cooperative state-
society relations, particularly when both state actors and civil society
are weak (Börzel and Buzogány, 2010). For example, CentralEastern Eu-
ropean countries (CEE) are still characterised bytop-down policy mak-
ing. Here, conict is still the main driver of the implementation of
participatory processes (Rauschmayer, 2009), although there has been
a recent shift to more multilevel governance in decision making
(Niedziałkowskiet al., 2012) and growing importance of NGOs in biodi-
versity conservation (Cent et al., 2013).
In Romania, Stringer and Paavola (2013) observed a lack of NGO in-
volvement in the implementation of Natura 2000 and generally limited
experience in public participation. They suggested that this is due to his-
torical legacies of low participation and government reluctance towards
more inclusive governance. Even in cases where governance shifts can
be observed, there can be a gap between the rhetoric and practice of in-
clusive governance (Rauschmayer, 2009). Nevertheless, Börzel and
Buzogány(2010) argued that an effective implementation of EU policies
requires departure from top-down centralised steering, and that it de-
mands meaningful inclusion of non-state stakeholders. Such shift can
also address the existing problem of low acceptance of EU conservation
policies, particularly among landowners (Weber and Christophersen,
2002).
3.2.7. Policy integration
This relatively small category included ve papers that looked into
integration of nature conservation policies concerning Natura 2000
with policies from other sectors. It was shown that policies and debates
on issues other than conservation, e.g. agricultural land use (Koutseris,
2006), climate change (de Koning et al., 2014; Roggema, 2009), or
noise protection (Votsi et al., 2014b) can affect conservation and man-
agement under Natura 2000 network. Thus better integration of differ-
ent policies and Natura 2000 was advocated (Roggema, 2009; Votsi et
al., 2014b).
3.2.8. Conservation priority setting
Several (4) papers discussed Natura 2000 implementation from the
perspective of prioritization or systematic conservation planning. It was
117M. Blicharska et al. / Biological Conservation 199 (2016) 110122
argued that implementation of the network should make better use of
systematic conservation planning (Gaston et al., 2008) incorporating
socio-economic indices or human related criteria (Giakoumi et al.,
2011; Tsianou et al., 2013) to facilitate the achievement of conservation
goals. Thismay lead to very different outcomes on the ground compared
to less systematic approaches. For example, by using spatial prioritiza-
tion software including innovative socio-economic cost indices in the
eastern Mediterranean Sea, Giakoumi et al. (2011) showed that only a
few of the sites selected through the systematic approach overlapped
with those previously identied in an unsystematic way.
3.2.9. Participation evaluation
Four studies directly evaluated the participation processes related to
Natura 2000 either during the designation of the network
(Apostolopoulouet al., 2012; Cent et al., 2014), or development and im-
plementation of management plans (Enengel et al., 2014; Young et al.,
2013). The general picture was one of relatively low prevalence of par-
ticipatory practices in Natura 2000. These were commonly rather super-
cial, operating mostly on paper (Apostolopoulou et al., 2012), and did
not enable all relevant stakeholders to exert meaningful participation
(Cent et al., 2014). The process of participation was usually steered in
a top-down manner, with highly asymmetric power distribution
among the involved actors. The governmental actors were the ones de-
ciding who may participate and in what form (Apostolopoulou et al.,
2012; Cent et al., 2014), aiming at fullling legal requirements or the
needs of the organisers rather than empowering the participants
(Cent et al., 2014). Even when theparticipation process was in principle
open to everyone, a need for broader involvement of local people was
expressed (Enengel et al., 2014). In addition, in some cases there was
a lack of formal governance structures that would require procedures
ofparticipationindecisionmaking(Apostolopoulou et al., 2012). Over-
lapping responsibilities of management agencies, governance fragmen-
tation and heavy bureaucracy led to many parallel co-decision
procedures for a specic site, causing problems in terms of accountabil-
ity and legitimacy of the process (Apostolopoulou et al., 2012). More-
over, lack of precise information and trust was identied as a barrier
to a more effective participation process (Enengel et al., 2014; Young
et al., 2013).
Notwithstanding the above mentioned shortcomings, in three of the
four studies in this category theparticipation process was deemed pos-
itive at least to some extent by the relevant stakeholders, as it increased
their knowledge about and overall satisfaction with the Natura 2000
network (Cent et al., 2014), contributing to attitude changes towards
the network (Young et al., 2013), and allowed the participants to con-
tribute with their own knowledge and experiences (Enengel et al.,
2014).
4. Discussion
4.1. Main ndings and their implications
The reviewed literature showed a very wide scopeof topics,indicat-
ing that the social dimension of Natura 2000 is complex and multidi-
mensional, and varies among EU countries. The introduction of Natura
2000 met the opposition of various stakeholder groups in almost all
Member States. Thus, an implementation of Natura 2000 policy may re-
quire a denite shift towards recognition of a wide range of social as-
pects relevant to the particular contexts of individual countries. One of
the most conspicuous aspects identied by our review was the question
of public participation or, broadly, stakeholder involvement. There were
relatively few papers that focused mostly on public participation and its
role (included in Participation evaluationcategory). Still, in several cat-
egories of papers such as e.g. Conservation conicts,Managementor
Perceptions, this issue was mentioned. The reviewed papers indicated
a general trend towards more inclusive approaches in implementation
and management of Natura 2000, practically at all stages. However,
stakeholder involvement, especially at the local level, was reported to
be still of relatively small magnitude and low quality, and numerous
challenges were identied.Evenifnewmodesofgovernanceemerged
during the implementation and more power was given to non-state
stakeholders such as NGOs or private landowners (Cent et al., 2013;
Niedziałkowski et al., 2012) the effect was not always enduring.
Sotirov et al. (2015) called such effect symbolic transformation,
where informal institution and practical behaviour did not change in
line with formal domestic policy and institutions. This was particularly
evident for the CEE countries that still bear some legacies of their com-
munist past, characterised by top-down governance and practically no
tradition of a broad stakeholder inclusion, especially those from non-
public sector (Cherp, 2001; Kluvánková-Oravská et al., 2009). Yet,
many studies underlined that meaningful participation is a key to suc-
cessful Natura 2000 implementation and functioning and a necessary
ingredient for efcient management of the sites. This is particularly im-
portant inthe case of private land (e.g. farmland),as private landowners
seem to be the most reluctant group in regard to the implementation of
Natura 2000 requirements, due to potential limitations on land use
(Geitzenauer et al., 2016). On the other hand, local governments seem
to be a crucial group in the network's implementation and functioning,
because Natura 2000 is in practice governed at the municipality level.
Our review revealed that although Natura 2000 was generally per-
ceived as a useful conservation approach, there were also many nega-
tive perceptions of the network. The network was seen by many as an
impediment to economic development. However, recent research
from Poland (including all municipalities with at least one site of Natura
2000) did not support the assertion that the network was a signicant
negative barrier to economic development (Gutowska et al., unpub-
lished). Indeed, a majority of municipalities were able to overcome
the potential economic barriers, in most cases thanks to an operative
local government. Our analysis showed, however, that the overall low
representativeness and quality of stakeholder involvement could have
greatly contributed to negative perceptions of Natura 2000, resulting
in challenges in the network's implementation and functioning.
Another important obstacle reported in several studies was the low
exibility of the Natura 2000 regulations and their implementing au-
thorities. It was emphasised that the local context matters, and hence
that decisions based solely on strict rules and templates may not always
be appropriate. This is particularly important with regard to the devel-
opment of management plans for particular sites. Again, a participatory
approach to management planning, with meaningful involvement of all
relevant stakeholders, was suggested as a key component. A wide range
of socio-cultural, institutional and discursive factors may inuence the
probability of success or failure of policy implementation, and thus tak-
ing them into considerations is essential (Hilding-Rydevik and
Bjarnadottir, 2007; Runhaar, 2009). Implementation and functioning
of Natura 2000 in various Member States is linked to multiple processes
at differentpolicy levels and depends on case-specic interplay (Borrass
et al., 2015). A large diversity of approaches to implementation can be
seen as a strength, as it can enable learning for improved future func-
tioning of Natura 2000 (Winkel et al., 2015). However, to utilise this po-
tential, there is a need for improved platforms and mechanisms of
learning across the Member States (Winkel et al., 2015).
Some studies underlined the temporal aspects of Natura 2000 im-
plementation. As Natura 2000 was implemented very quickly in many
countries, it was not surprising that the process was not ideal (Kati et
al., 2015). However, as Europe currently faces the next step of the
network's implementation, i.e. creation and implementation of man-
agement plans for specic sites, the process could be improved by tak-
ing better consideration of the local context. Guidelines concerning
organisation of the stakeholder involvement process (e.g. Bots et al.,
2011; Hiedanpää, 2002) could be helpful in that respect.
Finally, the reviewhas shown many implementation problems relat-
ed to the low capacity of local actors. This suggests that a better ow of
know-how from the EU to the local level, a larger number of better
118 M. Blicharska et al. / Biological Conservation 199 (2016) 110122
qualied staff and adequate funding are necessary components of suc-
cessful implementation and functioning of the network. Intheir survey
of conservation scientists on the functioning of Natura 2000 implemen-
tation, Kati et al. (2015) also underlined the low political will of both na-
tional and local authorities to full the goals of Natura 2000. They
underlined the need for mechanisms strengthening the linkages be-
tween EU policy and national, regional and local administration levels.
4.2. Research gaps
Our analysis has shown unequal distribution of social-science re-
search about Natura 2000 among the different EU countries. In general,
there were fewer studies addressing the countries that entered the EU
in 2004 or later (i.e. the non-EU-15 countries). Obviously, this could
be a result of a later implementation of Natura 2000 in these countries,
leading to a delay in associated research. However, as discussed by
Popescu et al. (2014), this issue is more complex. According to these au-
thors, the newEU countries only lagged behind EU-15 by a relatively
short time (3 to 5 years) in the designation of Natura 2000 sites. Never-
theless, even this short time lag could have contributed to the observed
differences in research effort. An additional contributing factor could be
the relatively lower levels of research funding in the countries in eco-
nomic transition compared to the EU-15 countries. However, there
were also exceptions, where some of the late-accession countries (e.g.
Poland) were represented in more papers than some of theEU-15 coun-
tries, which possibly could be explained by the higher importance of
particular social issues in these countries (e.g. linked to more conictual
situations), or the presence of particularlyproductive research groups in
some countries. Moreover, it must be keptin mind that our review only
includes peer-reviewed scientic articles in English. This could have led
to some bias, as some issues may have been covered in the grey litera-
ture or in references published in other languages. Particularly, this
could have led to underrepresentation of ndings of practical relevance,
such as e.g. local-specic challenges faced by various stakeholders
groups (e.g. the site managers) or best-practice solutions to particular
cases on the ground. Still, our review presents a reliable overview of
the body of knowledge which is broadly available to the international
scientic community. As such, it could contribute to the EU tness
check and to the recommendations for improving Natura 2000 imple-
mentation and functioning; however, one should keep in mind the lim-
itations of such review, and whenever possible complement our
ndings with existing local recommendations and guidelines.
Several additional gaps could be identied in the body of social-sci-
ence research concerning Natura 2000. First of all, in spite of the widely
recognised importance of the participation of various stakeholders in
the implementation and operation of the network, relatively few stud-
ies have evaluated in detail theparticipation processes linked to Natura
2000. It is possible that such information could be found in grey litera-
ture for the local studies but such literature was not a focus of our re-
view. Particularly, there is a need for more research on the importance
of participation for actual conservation outcomes, i.e. the extent to
which participation affects biodiversity on the ground. Rauschmayer
et al. (2009) suggested that both the process and outcomes of natural
resources governance need tobe investigated if weare to judge its effec-
tiveness. In the case of participation, some studies evaluated the process
itself (e.g. in terms of good or deliberative participation), but its effects
on biodiversity were rarely scrutinised (Reed, 2008). Young et al.
(2013) have investigated the correlation between the quality of stake-
holders' involvement and the future biodiversity outcomes as perceived
by the stakeholders, but they could nd clear relationship between the
process quality andthe perceived outcome only in some cases.Although
it was conrmed that in general a better quality of participation had a
positive impact on social outcomes and particularly trust and justice,
more studies are needed to conrm if the improved participation also
leads to improved ecological outcomes. As public participation is still
rather undeveloped in the majority of the EU countries, insights from
such studies could provide useful knowledge for improving the further
steps of Natura 2000 implementation and functioning. However, one
needs to keep in mind that not only the participation process, but also
different external factors may inuence the ultimate conservation out-
comes. Nevertheless, participatory approaches could beuseful in the de-
velopment of management plans for Natura 2000 (Hochkirch et al.,
2013), as they increase trust among stakeholders and enable better in-
tegration of their differentvalues, potentially allowing for better conser-
vation outcomes (Williams, 2011; Young et al., 2013).
Better participation may practically lead to improved engagement in
conservation and increased awareness of the conservation needs. Also,
participatory process may contribute to Natura 2000 managers' under-
standing of the potential reasons for the resistance towards the net-
work. At the same time, there is a need for studies investigating the
potential effects of education and increasing awareness on people's per-
ceptionsof Natura 2000 and potential attitudechanges. Although cogni-
tive approaches alone proved not to be sufcient in furthering attitude
change (Heberlein, 2012), they are an important component of strate-
gies for dealing with environmental issues (Gardner and Stern, 1996).
The importance of increasing the public awareness on Natura 2000,es-
pecially at the local level, was also underlined in a large survey of con-
servation scientists recently carried out by Kati et al. (2015).Our
review has shown that there is still low acceptance of the Natura 2000
network in society, and a lack of knowledge on the network operation
can be a factor contributing to it. As social acceptance is an important
prerequisite for the implementation of conservation policies, there is a
need for increased efforts, e.g. in terms of education and information,
aiming at raising this acceptance (Kati et al., 2015). Still, although edu-
cation and information are important, they are not sufcient for facili-
tating social acceptance. There is thus a need to also explore what
other factors (in addition to low awareness) contribute to the resistance
against the network in many places.
In addition, the low acceptance of the network by landowners may
suggest that there is a need for compensatory measures, such as reim-
bursement of the conservation costs incurred by the private land
owners (Kamal and Grodzinska-Jurczak, 2014; Schröter-Schlaack et
al., 2014). For example, Stancioiu et al. (2010) suggested the need for
compensatory nancial mechanisms to cover the costs of Natura 2000
for the land owners. Also, conservation scientists surveyed by Kati et
al. (2015) highlighted the need for an independent funding mechanism
entirely devoted to supporting implementation of Natura 2000 goals.
Also Winkel et al. (2015) suggested the need for development of a coher-
ent funding strategy for Natura 2000 based on comprehensive assess-
ment of both current spending and nancial needs for the network. This
may be particularly important for the CEE countries with extensive rural
areas, large coverage of Natura 2000 sites and lower level of economic de-
velopment compared to the EU-15 countries (Pavasars, 2013; Stancioiu et
al., 2010). To design effective nancing mechanisms that support the net-
work, we see a need for more studies analysing the effects of alternative
compensatory approaches in a range of socio-economic settings, on e.g.
acceptance of conservation or biodiversity outcomes; however our re-
view have revealed that such studies are still rare.
The issue of effectiveness has been largely neglected in the social re-
search about Natura 2000. Very few studies looked at the costs or the
benets of the network, and comprehensive economic analyses were
entirely missing in the reviewed publications. Surprisingly, the concept
of ecosystem services was very rarely utilised in social-science research
about Natura 2000, although it may seem particularly well tted to
analysing the complex socio-ecological systems of Natura 2000 sites
(Primmer et al., 2015; Soane et al., 2012). Ecosystem service research
could, for example, aim to identify and quantify potential benets
from the protection of the Natura 2000 sites, which in term could con-
tribute to wider acceptance of the network (Cruz et al., 2011). Research
on the effectiveness of the Natura 2000 network should also involve
studies developing and testing indicators of effectiveness, including
both ecological indicators as well as indicators of the social dimension
119M. Blicharska et al. / Biological Conservation 199 (2016) 110122
encompassing human actions, institutions, organisations and networks
(Salafsky et al., 2002). Such indicators are urgently needed to evaluate
the success (or failure) of the network.
Conservation does not operate in an emptyspace. Rather, it is an in-
tegral part of complex socio-ecological systems. Consequently, insuf-
cient consideration of social aspects risks undermining conservation
effectiveness, while integrating local human context in the protected
areas facilitates achieving biological conservation and socioeconomic
development outcomes (Oldekop et al., 2016). Although Natura 2000
is generally seen as a successful conservation endeavour (Kati et al.,
2015), our review points to different shortcomings affecting practically
all EU Member States. Social science research has a great potential to
contribute to the knowledge basenecessary for improving the situation.
Particularly, the knowledge derived from the social science investiga-
tions could contribute to the ongoing Natura 2000 tness check (EC,
2015b), by pointing to the areas in the network's implementation and
functioning that need to be improved.
Acknowledgements
This work was made possible thanks to nancial support from the
Kempe Foundations (grant number SMK-1339) to JMR. We would like
to thank three anonymous reviewers whose comments greatly contrib-
uted to the improvement of this paper.
Appendix A. Supplementary data
Supplementary data to this article can be found online at http://dx.
doi.org/10.1016/j.biocon.2016.05.007.
References
Adams, W.M.,Aveling, R., Brockington, D., Dickson, B., Elliott, J., Hutton, J., Roe, D., Vira, B.,
Wolmer, W., 2004. Biodiversity conservation and the eradication of poverty. Science
306, 1146.
Alphandery, P., Fortier, A., 2010. Local settings and biodiversity:a sociological approach to
the implementation of the EC Habitats Directive in France. Curr. Sociol. 58, 755776.
Alphandéry, P., Fortier, A., 2001. Can a territorial policy be based on science alone? The
system for creating the Natura 2000 network in France. Soc. Ruralis 41, 311328.
Andrea, V., Tampakis, S., Tsantopoulos, G., Arabatzis, G., 2013. Administration and man-
agement effectiveness of protected areas: stakeholders' views of Dadia National
Park, Greece. J. Protected Mt. Areas Res. 5, 2334.
Andrulewicz, E., Otremba, S., Kaminska, K., 2010. Ongoing technical activities and conser-
vation. Pol. J. Environ. Stud. 19, 553563.
Anthon, S., Garcia, S., Stenger, A., 2010. Incentive contracts for Natura 2000 implementa-
tion in forest areas. Environ. Resour. Econ. 46, 281302.
Apostolopoulou, E., Drakou, E.G., Pediaditi, K., 2012. Participation in the management of
Greek Natura 2000 sites: evidence from a cross-level analysis. J. Environ. Manag.
113, 308318.
Apostolopoulou, E., Pantis, J.D., 2009. Conceptual gaps in the national strategy for the im-
plementation of the European Natura 2000 conservation policy in Greece. Biol.
Conserv. 142, 221237.
Ban, N.C., Mills, M., Tam,J., Hicks, C.C., Klain, S., Stoeckl, N., Bottrill, M.C., Levine, J., Pressey,
R.L., Sattereld, T., Chan, K.M., 2013. A socialecological approach to conservation
planning: embedding social considerations. Front. Ecol. Environ. 11, 194202.
Beunen, R., van Assche, K., 2013. Contested delineations: planning, law, and the gover-
nance of protected areas. Environ. Plan. A 45, 12851301.
Beunen, R.,Van Assche, K., Duineveld, M., 2013. Performing failurein conservation policy:
the implementation of European Uniondirectives in the Netherlands. Land UsePolicy
31, 280288.
Bielecka, M., Różyński, G., 2014. Management conicts in the Vistula lagoon area. Ocean
Coast. Manag. 101, 2434.
Borrass, L.,2014. Varying practices of implementing the Habitats Directive in Germanand
British forests. Forest Policy Econ. 38, 151160.
Borrass, L., Sotirov, M., Winkel, G., 2015. Policy change and Europeanization. Analysing
the implementation of the European Union's Habitats Directive in Germany and the
United Kingdom. Environ. Polit. 24, 788809.
Bots, P.W.G., Bijlsma, R., von Korff, Y., Van der Fluit, N., Wolters, H., 2011. Supporting the
constructive use of existing hydrological models in participatory settings: a set of
rules of the game. Ecol. Soc. 16, 16.
Bouwma, I.M., Kamphorst, D.A., Beunen, R., Apeldoorn, R.C.V., 2008. Natura 2000 bench-
mark. A Comparative Analysis of the Discussion on Natura 2000 Management Issues,
Wageningen.
Bryan, S., 2012. Contested boundaries, contested places: the Natura 2000 network in Ire-
land. J. Rural. Stud. 28, 8094.
Bryman, A., Teevan, J., 2005. Social Research Methods. Oxford University Press, London.
rzel, T., Buzogány, A., 2010. Environmental organisations and the Europeanisation of
public policy in Central and Eastern Europe: the case of biodiversity governance. En-
viron. Polit. 19, 708735.
CEC, 1979. Council Directive 79/409/EC of 2 April 1979 on the conservation of the wild
birds. Off. J. L 103, 00010018 (25/04/1979).
CEC, 1992. Council Directive 92/43/EEC of 21 730 May 1992 on the conservation of natu-
ral habitats and of wildfauna and ora. Council of the European Communities.Ofcial
731 Journal of the European Communities 22.7.92, no L 206/7-50, p. 66.
Cent, J., Grodzińska-Jurczak, M., Pietrzyk-Kaszyńska, A., 2014. Emerging multilevel envi-
ronmental governance a case of public participation in Poland. J. Nat. Conserv. 22,
93102.
Cent, J., Mertens, C.,Niedziałkowski, K., 2013. Roles and impacts of non-governmental or-
ganizations in Natura 2000 implementation in Hungary and Poland. Environ.
Conserv. 40, 119128.
Cherp, A., 2001. Environmental assessment in countries of transition: evolution in a
changing context. J. Environ. Manag. 62, 357374.
Christensen, P., 2006. Danish experiences on EIA of livestock projects. Environ. Impact As-
sess. Rev. 26, 468480.
Ciapala,S., Adamski, P., Mroczka, A., Svajda, J., Witkowski,Z., 2014. Threats related to tour-
ism and recreation in Natura 2000 areas, based on the analysis of the standard data
forms (SDF) from the Alpine Bioregion of Slovakia. Eco Mont-J. Protected Mt. Areas
Res. 6, 5560.
Cliquet, A., 2014. International and European law on protected areas and climate change:
need for adaptation or implementation? Environ. Manag. 54, 720731.
Cortina,C., Boggia, A., 2014.Development of policies for Natura 2000 sites: a multi-criteria
approach to support decision makers. J. Environ. Manag. 141, 138145.
Cruz, A., Benedicto, J., Gil, A., 2011. Socio-economic benets of Natura 2000 in Azores
Islands a case study approach on ecosystem services provided by a special
protected area. J. Coast. Res. 64, 19551959.
de Koning, J., Winkel, G., Sotirov, M., Blondet, M., Borras, L., Ferranti, F., Geitzenauer, M.,
2014. Natura 2000 and climate changepolarisation, uncertainty, and pragmatism
in discourses on forest conservation and management in Europe. Environ. Sci. Pol.
39, 129138.
de Noronha Vaz, E., Walczynska, A., Nijkamp, P., 2012. Regional challenges in tourist wet-
land systems: an integrated approach to the Ria Formosa in the Algarve, Portugal.
Reg. Environ. Chang. 13, 3342.
Deguignet, M., Juffe-Bignoli, D., Harrison, J., MacSharry, B., Burgess, N., Kingston, N., 2014.
2014 United Nations List of Protected Areas. UNEP-WCMC, Cambridge, UK, p. 44.
Dimitrakopoulos, P.G., Jones, N., Iosides, T., Florokapi, I., Lasda, O., Paliouras, F.,
Evangelinos, K.I., 2010. Local attitudes on protected areas: evidence from three
Natura 2000 wetland sites in Greece. J. Environ. Manag. 91, 18471854.
EC, 2000. Managing Natura 2000 Sites, the Provisions of Article 6 of the Habitats Directive
92/43/CEE (ed.) E. Commission.
EC, 2011. Communication from the commission to the European parliament, the council,
the economic and social committee and the committee of the regions. Our Life Insur-
ance, Our Natural Capital: An EU Biodiversity Strategy to 2020, (ed.) E. Commission,
Brussels.
EC, 2015a. Natura 2000. European Commission (http://ec.europa.eu/environment/
nature/natura2000/).
EC, 2015b. Fitness Checkof EU Nature Legislation (Birds and HabitatsDirectives). Europe-
an Commission (http://ec.europa.eu/environment/nature/legislation/tness_check/
index_en.htm.).
Enengel, B., Penker, M., Muhar, A., 2014. Landscape co-management in Austria: the
stakeholder's perspective on efforts, benets and risks. J. Rural. Stud. 34, 223234.
Ernoul, L., Vareltzidou, S., Teoli, C., Gasulla, X.E., Tilders, I., 2011. Adaptive management
of coastal areas: using the open standards approach. In: Ozhan, E. (Ed.)Medcoast 11
Vols 1 and 2. Mediterranean Coastal Foundation-Medcoast Foundation, Akyaka,
pp. 123133.
Ferranti, F., Beunen, R., Speranza, M., 2010. Natura 2000 network: a comparison of the
Italian and Dutch implementation experiences. J. Environ. Policy Plan. 12, 293314.
Ferranti, F., Turnhout, E., Beunen, R., Behagel, J.H., 2014. Shifting nature conservation ap-
proaches inNatura 2000 and the implications for the roles ofstakeholders. J. Environ.
Plan. Manag. 57, 16421657.
Fock, H.O., 2011. Natura 2000 and the European common sheries policy. Mar. Policy 35,
181188.
Fox, H.E., Christian, C., Nordby, J.C., Pergams, O.R., Peterson, G.D., Pyke, C.R., 2006. Per-
ceived barriers to integrating social science and conservation. Conserv. Biol. 20,
18171820.
Freitag, C., Ohle, N., Strotmann,T., Glindemann, H., 2008. Concept of Sustainable Develop-
ment of the Elbe Estuary. pp. 10851092.
Ganatsas, P., Tsakaldimi, M., Katsaros, D., 2013. Natural resource management in national
parks: a management assessment of a Natura 2000wetlands site in Kotychi-Strofylia,
southern Greece. Int. J. Sustain. Dev. WorldEcol. 20, 152165.
Gardner, G.T., Stern, P.C., 1996. Environmental Problems and Human Behavior. Allyn & Bacon.
Gaston, K.J., Jackson, S.F., Nagy, A., Cantu-Salazar, L., Johnson,M., 2008. Protected areas in
Europe: principle and practice. Ann. N. Y. Acad. Sci. 1134, 97119.
Geitzenauer, M., Hogl, K., Weiss, G., 2016. The implementation of Natura 2000 in Austria.
A European policy in a federal system. Land Use Policy 52, 120135.
Giakoumi,S., Grantham, H.S., Kokkoris, G.D., Possingham,H.P., 2011. Designing a network
of marine reserves in the MediterraneanSea with limited socio-economic data. Biol.
Conserv. 144, 753763.
Gil, A., Calado, H., Costa, A.C., Bentz, J., Fonseca, C., Lobo,A., Vergilio, M., Benedicto, J.,2011.
A methodological proposal for the development of Natura 2000 sites management
plans. J. Coast. Res. 64, 13261330.
Glaser, B., Strauss, A., 2008. The Discovery of Grounded Theory: Strategies for Qualitative
Research. Aldine, London.
120 M. Blicharska et al. / Biological Conservation 199 (2016) 110122
Gonzales, C., Clemente, A., Nielsen, K.A., Branquinho, C., Dos Santos, R.F., 2009. Human
nature relationship in Mediterranean streams: integrating different types of knowl-
edge to improve water. Ecol. Soc. 14, 35.
Grammatikopoulou,I., Olsen, S.B., 2013. Accounting protestingand warm glow bidding in
contingent valuation surveys considering the management of environmental goods
an empirical case study assessing the value of protecting a Natura 2000 wetland area
in Greece. J. Environ. Manag. 130, 232241.
Graziano, R., Gilberto, P., Alessandro, F., 2008.A rapid and cost-effective tool for managing
habitats of the European Natura 2000 network: a case study in the Italian Alps.
Biodivers. Conserv. 18, 13751388.
Grodzińska-Jurczak, M., 2008. Rethinking of nature conservation policy in Poland: the
need of human dimensions approach. Hum. Dimens. Wildl. 13, 380381.
Grodzinska-Jurczak, M., Cent, J., 2011. Expansion of nature conservation areas: problems
with Natura 2000 implementation in Poland? Environ. Manag. 47, 1127.
Heberlein, T.A., 2012. Natigating Environmental Attitudes. OxfordUniversity Press, New York.
Hiedanpää, J., 2002. European-wideconservation versuslocal well-being:the reception of
the Natura 2000Reserve Network in Karvia. SW-Finland. LandscapeUrban Plann. 61,
113123.
Hiedanpää, J., 2005. The edges of conict and consensus: a case for creativity in regional
forest policy in Southwest Finland. Ecol. Econ. 55, 485498.
Hilding-Rydevik, T., Bjarnadottir, H., 2007. Context awareness and sensitivity in SEA im-
plementation. Environ. Impact Assess. Rev. 27, 666684.
Hochkirch, A., Schmitt, T., Beninde, J., Hiery,M., Kinitz, T., Kirschey, J., Matenaar, D., Rohde,
K., Stoefen, A., Wagner, N., Zink, A., Lötters, S., Veith, M., Proelss, A., 2013. Europe
needs a new vision for a Natura 2020 network. Conserv. Lett. 6, 462467.
Hoyos, D., Mariel, P., Pascual, U., Etxano, I., 2012. Valuing a Natura 2000 network site to
inform land use options using a discrete choice experiment: an illustration from
the Basque Country. J. For. Econ. 18, 329344.
Iojă,C.I.,Pătroescu, M., Rozylowicz, L.,Popescu,V.D., Vergheleţ, M., Zotta, M.I., Felciuc, M.,
2010. The efcacy of Romania's protected areas network in conserving biodiversity.
Biol. Conserv. 143, 24682476.
Jackson, A.L.R., 2011. Renewable energy vs. biodiversity: policy conicts and the future of
nature conservation. Global environ. Change 21, 11951208.
Jacobsen, J.B., Vedel, S.E., Thorsen, B.J., 2013. Assessing costs of multifunctional Natura
2000 management restrictions in continuous cover beech forest management. For-
estry 86, 575582.
Jantke,K., Schleupner, C.,Schneider, U.A., 2010. Gap analysis of Europeanwetland species:
priority regions for expanding the Natura 2000 network. Biodivers. Conserv. 20,
581605.
Jones, N., Panagiotidou, K., Spilanis, I., Evangelinos, K.I., Dimitrakopoulos, P.G., 2011. Visi-
tors' perceptions on the management of an important nesting site for loggerhead sea
turtle (Caretta caretta L.): the case of Rethymno coastal area in Greece. Ocean coast.
Manage 54, 577584.
Kafyri, A.,Hovardas, T., Poirazidis, K., 2012. Determinants of visitor pro-environmental in-
tentions on two small Greek islands: is ecotourism possible at coastal protected
areas? Environ. Manag. 50, 6476.
Kamal, S., Grodzinska-Jurczak, M., 2014. Should conservation of biodiversity involve pri-
vate land? A Q methodological study in Poland to assess stakeholders' attitude.
Biodivers. Conserv. 23, 26892704.
Kareiva, P., Marvier, M., 2012. What is conservation science? Bioscience 62, 962969.
Kati, V., Hovardas, T., Dieterich,M., Ibisch, P.L., Mihok, B., Selva,N., 2015. The challenge of
implementing the European network of protected areas Natura 2000. Conserv. Biol.
29, 260270.
Kistenkas, F., 2014. Innovating European nature conservation law by introducing ecosys-
tem services. GAIA - Ecol. Perspect. Sci. Soc. 2, 8892.
Kluvánková-Oravská, T., Chobotová, V., Banaszak, I., Slavikova, L., Trifunovova, S., 2009.
From government to governance for biodiversity: the perspective of central and East-
ern European transition countries. Environ. Policy Gov. 19, 186196.
Koutseris, E., 2006. Sustainable Resources Management in the Context of Agro-Environ-
mental EU Policies: Novel Paradigms in Thessaly, Greece (I) pp. 197207.
Krott, M., Julien, B., Lammertz, M., Barbier,J.-M., Jen,S., Ballesteroz, M.,de Bovis, C., 2000.
Voicing interests and concerns: Natura 2000: an ecological network in conict with
people. Forest Policy Econ. 1, 357366.
Lee, M., 2001. Coastal defence and Habitat Directive: predictions of habitat change in En-
gland and Wales. Geogr. J. 167.
Leone, V., Lovreglio, R., 2004. Conservation of Mediterranean pine woodlands: scenarios
and legislative tools. Plant Ecol. 171, 221235.
Li, C.Z., Kuuluvainen, J., Pouta, E., Rekola, M., Tahvonen, O., 2004. Using choice experi-
ments to value the Natura 2000 nature conservation programs in Finland. Environ.
Resour. Econ. 29, 361374.
Liu, J., Dietz, T., Carpenter, S.R., Alberti, M., Folke, C., Moran, E., Pell, A.N., Deadman, P.,
Kratz, T., Lubchenco, J., Ostrom, E., Ouyang, Z., Provencher, W., Redman, C.L.,
Schneider, S.H., Taylor, W.W., 2007. Complexity of coupled human and natural sys-
tems. Science 317, 15131516.
Louette, G., Adriaens, D., Adriaens, P., Anselin, A., Devos, K., Sannen, K., Van Landuyt, W.,
Paelinckx, D., Hoffmann, M., 2011. Bridging the gap between the Natura 2000 region-
al conservation status and local conservation objectives. J. Nat. Conserv. 19, 224235.
Lung, T., Meller, L., van Teeffelen, A.J.A., Thuiller, W., Cabeza, M., 2014. Biodiversity funds
and conservation needs in the EU under climate change. Conserv. Lett. 7, 390400.
Malatinszky, A., Ádám, S., Falusi, E., Saláta, D., Penksza, K., 2014. Suggested management
measures for Natura 2000 habitats in Körös-Maros National Park, Hungary. Adv.
Glob. Chang. Res. 58, 197207.
Malcolm, J.R., Liu, C., Neilson, R.P., Hansen, L., Hannah, L.E.E., 2006. Global warming and
extinctions of endemicspecies from biodiversity hotspots. Conserv.Biol. 20, 538548.
Mallard, F., François, D., 2013. Effectiveness of the legal framework for natural areas pro-
tection relative to French road projects. Land Use Policy 30, 582591.
Marandi, A., Veinla, H., Karro, E., 2014. Legal aspects related to the effect of underground
mining close to the site entered into the list of potential Natura 2000 network areas.
Environ. Sci. Pol. 38, 217224.
Marmureanu, L., Geamana, N.A., 2012. The Need for Education and Public Awareness
Campaign in Natura 2000 Sites Journal of Environmental Protection and Ecology
13, 24232432.
Mascia, M.B., Brosius, J., Dobson, T., Forbes, B., Horowitz, L., McKean, M., Turner, N., 2003.
Conservation and the social sciences. Conserv. Biol. 17, 649650.
Metcalfe, K., Roberts, T., Smith, R.J., Harrop, S.R., 2013. Marine conservation science and
governance in NorthWest Europe: conservation planning and international law
and policy. Mar. Policy 39, 289295.
Morris, R.K.A., Bennett, T., Blyth-Skyrme, R., Barham, P.J., Ball, A., 2014. Managing Natura
2000 in the marine environment an evaluation of the effectiveness of management
schemesin England. Ocean Coast. Manag. 87, 4051.
Mouro, C., Castro, P., 2009. Local communities responding to ecological challengesapsy-
cho-social approachto the natura 2000 network. J. Community Appl. Soc.Psychol. 20,
139155.
Muntean, O.-L., Buzila, L., Mihaiescu, R., Malos, C., Baciu, N., 2013. Assessment of environ-
mental vulnerabilities and constraints in the Vascau Plateau (Natura 2000 Protected
Area, Romania). J. Environ. Prot. Ecol. 14, 18601870.
Niedziałkowski, K., Paavola, J., Jędrzejewska, B., 2012. Governance of biodiversity in Po-
land before and after the accession to the EU: the tale of tworoads. Environ. Conserv.
40, 108118.
Nyhus, P., Westley, F., Lacy, R., Miller, P., 2002. A role for natural resource social science in
biodiversity risk assessment. Soc. Nat. Resour. 15, 923932.
Oana, B., 2006. Natura 2000 network an opportunity for rural space sustainable develop-
ment. Buletin USAMV-CN 62, 179183.
Oikonomou, V., Dimitrakopoulos, P.G., Troumbis, A.Y., 2011. Incorporating ecosystem
function concept in environmental planning and decision making by means of
multi-criteria evaluation: the case-study of Kalloni, Lesbos, Greece. Environ. Manag.
47, 7792.
Oldekop, J.A., Holmes, G., Harris, W.E., Evans, K.L., 2016. A global assessment of the social
and conservation outcomes of protected areas. Conserv. Biol. 30, 133141.
Papageorgiou, K., Vogiatzakis, I.N., 2006. Nature protection in Greece: an appraisal of the
factors shaping integrative conservation and policy effectiveness. Environ. Sci. Pol. 9,
476486.
Parolo, G., Ferrarini, A., Rossi, G., 2009. Optimization of tourism impacts within protected
areas by means of genetic algorithms. Ecol. Model. 220, 11381147.
Pavasars, I., 2013. Environmentalism in Latvia: two realities. J. Baltic Stud. 45, 3955.
Pecurul-Botines, M., Di Gregorio, M., Paavola, J., 2014. Discourses of conict and collabo-
ration and institutional context in the implementation of forestconservation policies
in Soria, Spain. Biodivers. Conserv. 23, 34833499.
Pedersen, S.A., Fock, H., Krause, J., Pusch, C., Sell, A.L., Böttcher, U., Rogers, S.I., Sköld, M.,
Skov, H., Podolska, M.,Piet, G.J., Rice, J.C.,2009. Natura 20 00 sites and sheries in Ger-
man offshore waters. ICES J. Mar. Sci. 66, 155169.
Pietrzyk-Kaszyńska, A., Cent, J., Grodzińska-Jurczak, M., Szymańska, M., 2012. Factors
inuencing perception of protected areasthe case of Natura 2000 in Polish
Carpathian communities. J. Nat. Conserv. 20, 284292.
Pîrvu, M., Petrovici, M., 2013, 11-16. DPSIR conceptual framework role: a case study re-
garding the threats and conservation measures for caddisies (Insecta: Trichoptera)
in Romania. Knowl. Manag. Aquat. Ecosyst. 11, 1116.
Popescu,V.D., Rozylowicz,L., Niculae, I.M., Cucu, A.L., Hartel, T.,2014. Species, habitats, so-
ciety: an evaluation of research supporting EU's Natura 2000 network. PLoS One 9,
e113648.
Pouta, E., Rekola, M., Kuuluvainen, J., Tahvonen, O., Li, C.Z., 2000. Contingent valuation of
the Natura 2000 nature conservation programme in Finland. Forestry 73, 119128.
Prazan, J., Ratinger,T., Krumalova, V., 2005. The evolution of nature conservation policy in
the Czech Republicchallenges of Europeanisation in the White Carpathians
Protected Landscape Area. Land Use Policy 22, 235243.
Primmer, E., Jokinen, P., Blicharska, M., Barton, B.N., Bugter, R., Potschin, M., 2015. Gover-
nance of ecosystem services: a framework for empirical analysis. Ecosystem Serv.
http://dx.doi.org/10.1016/j.ecoser.2015.05.002i.
Rauschmayer, F., 2009.Participation in EU biodiversity governance: how far beyond rhe-
toric. Environ. Plann. C Gov. Policy 27, 4258.
Rauschmayer, F., Berghöfer, A., Omann, I., Zikos, D., 2009. Examining processes or/and
outcomes? Evaluation concepts in European governance of natural resources. Envi-
ron. Policy Gov. 19, 159173.
Reed, M., 2008. Stakeholder participation for environmentalmanagement: a literature re-
view. Biol. Conserv. 141, 24172431.
Rees, S.E., Sheehan, E.V., Jackson, E.L., Gall, S.C., Cousens, S.L., Solandt, J.L., Boyer, M., Attr ill, M.J.,
2013. A legal and ecological perspective of site integrityto inform policy development
and management of Special Areas of Conservation in Europe. Mar. Pollut. Bull. 72, 1421.
Rekola, M., Pouta, E., Kuuluvainen, J., Tahvonen, O., Li, C.Z., 2000. Incommensurable pref-
erencesin contingent valuation: the case of Natura2000 Network in Finland.Environ.
Conserv. 27, 260268.
Rodrigues, A.S.L., Andelman, S.J., Bakarr, M.I., Boitani, L., Brooks, T.M., Cowling, R.M.,
Fishpool, L.D.C., da Fonseca, G.A.B., Gaston, K.J., Hoffmann, M., Long, J.S., Marquet,
P.A., Pilgrim, J.D., Pressey, R.L., Schipper, J., Sechrest, W., Stuart, S.N., Underhill, L.G.,
Waller, R.W., Watts, M.E.J., Yan, X., 2004. Effectiveness of the global protected area
network in representing species diversity. Nature 428, 640643.
Roggema, R., 2009. Ecology. Adaptation to Climate Change: A Spatial Challenge. Springer,
Netherlands, pp. 211251.
Rojas-Briales, E., 2000. Socio-economics of nature protection policies in the perspectiveof
the implementation ofNatura 2000 network: the Spanish case. Forestry 72, 199207.
Runhaar, H., 2009. Putting SEA in context: a discourse perspective on how SEA contrib-
utes to decision-making. Environ. Impact Assess. Rev. 29, 200209.
121M. Blicharska et al. / Biological Conservation 199 (2016) 110122
Salafsky, N., Margoluis, R., Redford, K.H., Robinson, J.G., 2002. Improving the practice of
conservation: a conceptual framework and research agenda for conservation science.
Conserv. Biol. 16, 14691479.
Santana, J., Reino, L., Stoate, C., Borralho, R., Carvalho, C.R., Schindler, S., Moreira, F.,
Bugalho, M.N., Ribeiro, P.F., Santos, J.L., Vaz, A., Morgado, R., Porto, M., Beja, P., 2014.
Mixed effects of long-term conservation investment in Natura 2000 farmland.
Conserv. Lett. 7, 467477.
Sarvasova, Z., Salka, J., Dobsinska, Z., 2013. Mechanism of cross-sectoral coordination be-
tween nature protection and forestry in the Natura 2000 formulation process in Slo-
vakia. J. Environ. Manag. 127 (Suppl), S65S72.
Schröter-Schlaack, C., Ring, T., Koellner, T., Santos,R.,Antunes,P.,Clemente,P.,Mathevet,R.,
Borie, M., Grodzińska-Jurczak, M., 2014. Intergovernmental scal transfers to support
local conservation action in Europe. German J. Econ.Geogr. Z. Wirtschaftsgeographie
23, 98114.
Scolozzi, R., Schirpke, U., Morri, E., D'Amato, D., Santolini, R., 2014. Ecosystem services-
based SWOT analysis of protected areas for conservation strategies. J. Environ.
Manag. 146, 543551.
Slepcevic, R., 2009. The judicial enforcement of EU law through national courts: possibil-
ities and limits. J. Eur. Public Policy 16, 378394.
Soane, I.D., Scolozzi, R., Gretter, A., Hubacek, K., 2012. Exploring panarchy in alpine grass-
lands: an application of adaptive cycle concepts to theconservation ofa cultural land-
scape. Ecol. Soc. 17.
Sotirov, M., Lovric, M., Winkel, G., 2015. Symbolic transformation of environmental gov-
ernance: implementation of EU biodiversity policy in Bulgaria and Croatia between
Europeanization and domestic politics. Environ. Plann. C Gov. Policy 33, 9861004.
Stancioiu,P.T., Abrudan, I.V., Dutca, I., 2010. The Natura 2000 ecological network and for-
ests in Romania: implications on management and administration. Int. For. Rev. 12,
106113.
Strange, N., Jacobsen,J.B., Thorsen, B.J., Tarp, P., 2007. Value for money: protecting endan-
gered species on Danish heathland. Environ. Manag. 40, 761774.
Stringer, L.C., Paavola, J., 2013. Participation in environmental conservation and protected
area management in Romania: a review of three case studies. Environ. Conserv. 40,
138146.
Sumares, D., Fidelis, T., 2009. Local perceptions and postures towards the SPA Ria de
Aveiro. J. Integr. Environ. Sci. 6, 121137.
Teoli, C., Battisti, C., 2011. May the conservation measures partnership open standards
framework improve the effectiveness of the Natura 2000 European network? A com-
parative analysis. J. Integr. Environ. Sci. 8, 721.
Tonder, M., Jurvelius, J., 2004. Attitudes towards shery and conservation of the Saimaa
ringed seal in Lake Pihlajavesi, Finland. Environ. Conserv. 31, 122129.
Torbidoni, F.E.I., 2011. Managing for recreational experience opportunities: the case of
hikers in protected areas in Catalonia, Spain. Environ. Manag. 47, 482496.
Tsianou,M.A., Mazaris, A.D.,Kallimanis, A.S., Deligioridi, P.-S.K.,Apostolopoulou, E., Pantis,
J.D., 2013. Identifying the criteria underlying the political decision for the prioritiza-
tion of the Greek Natura 2000 conservation network. Biol. Conserv. 166, 103110.
UN, 1992. Convention on Biological Diversity. United Nations, Rio de Janeiro.
Vaiškūnaitė, R., Mierauskas, P., Špakauskas, V., 2012. Biodiversity impact assessment in
road development in Lithuania. Transport 27, 187195.
Weber, N., Christophersen, T., 2002. The inuence of non-governmental organisations on
the creation of Natura2000 during the European policy process. Forest PolicyEcon. 4,
112.
Welch-Devine, M., 2012. Searching for success: dening success in co-management.
Hum. Organ. 71, 358368.
Williams, B.K., 2011. Adaptive management of natural resourcesdframework and issues.
J. Environ. Manag. 92, 13461353.
Winkel, G., Blondet, M., Borrass, L., Frei, T., Geitzenauer, M., Gruppe, A., Jump, A., De
Koning, J., Sotirov, M., Weiss, G., S., G.W., Turnhout, E., 2015. The implementation of
Natura 2000 in forests: a trans- and interdisciplinary assessment of challenges and
choices. Environ. Sci. Pol. 52, 2332.
Winter, S., Borrass, L., Geitzenauer, M., Blondet, M., Breibeck, R., Weiss, G., Winkel, G.,
2014. The impact of Natura 2000 on forest management: a socio-ecological analysis
in the continental region of the European Union. Biodivers. Conserv. 23, 34513482.
Visser, M., Moran, J., Regan, E., Gormally, M., Skefngton, M.S., 2007. The Irish agri-envi-
ronment: how turlough users and non-users view converging EU agendas of Natura
2000 and CAP. Land Use Policy 24, 362373.
Votsi, N.E.P., Kallimanis, A.S., Mazaris, A.D., Pantis, J.D., 2014b. Integrating environmental
policies towards a network of protected and quiet areas. Environ. Conserv. 41,
321329.
Wszołek, T., Klaczynski, M., Mleczko, D., Ozga, A., 2014. On certain problems concerning
environmental impact assessment of wind turbines in scope of acoustic effects.
Acta Phys. Pol. A 125, 3944.
Wätzold, F., Mewes, M.,van Apeldoorn, R., Varjopuro, R., Chmielewski, T.J.,Veeneklaas, F.,
Kosola, M.-L., 2010. Cost-effectiveness of managing Natura 2000sites: an exploratory
study for Finland, Germany, the Netherlands and Poland. Biodivers. Conserv. 19,
20532069.
Wätzold, F., Schwerdtner, K., 2005. Why be wasteful when preserving a valuable re-
source? A review article on the cost-effectiveness of European biodiversity conserva-
tion policy. Biol. Conserv. 123, 327338.
Vörösmarty, C.J., McIntyre, P., Gessner,M.O., Dudgeon, D., Prusevich,A., Green, P., Glidden,
S., Bunn, S.E., Sullivan, C.A., Liermann, C.R., 2010. Global threatsto human water secu-
rity and river biodiversity. Nature 467, 555561.
Young, J.C., Jordan,A., Searle, K.R., Butler, A., Chapman, D.S.,Simmons, P., Watt, A.D., 2013.
Does stakeholder involvement really benet biodiversity conservation? Biol. Conserv.
158, 359370.
Zaharia, T., Maximov, V., Radu, G., Anton, E., Spinu, A., Nenciu,M., 2014. Reconciling sh-
eries and habitat protection in Romanian coastal marine protected areas. Sci. Mar.78,
95101.
Zaharia, T., Micu, D., Nedelcu, M., Ganea, G., Ursache, C.M., Golumbeanu, M., Nenciu, M.,
2012. Romanian marine sheries and Natura 2000 network. J. Environ. Prot. Ecol.
13, 17921798.
122 M. Blicharska et al. / Biological Conservation 199 (2016) 110122
... Thus, the conservation of mobile and migratory wildlife species is challenging due to their extensive space use, seasonal resource needs and impact on human land use (Runge et al., 2015). (EC, 2016;Orlikowska et al., 2016) the coordinated implementation of these initiatives is generally lacking. The N2K is the world's largest network of protected areas and covers 18% of the 28 EU member states' land (EC, 2016). ...
... The N2K is not a network of strict protection, but includes human land use, such as sustainable agriculture and forestry (EC, 2016). Conflicts between conservation and other land use are still common due to land use restrictions such as grazing regimes and water rights (Blicharska et al., 2016) and damage caused by protected species in surrounding farmlands (Nilsson et al., 2016). This may risk the intended goals of socio-economic sustain-ability. ...
... This may risk the intended goals of socio-economic sustain-ability. The majority of previous scientific studies of the effectiveness of the N2K network has been limited to regional or national scales and only a few studies have covered several EU member states or the range of migratory species (Orlikowska et al., 2016). The common crane (Grus grus, hereafter crane) is an iconic species of conservation importance and is included in Annex I of the Birds Directive since 1979. ...
Conference Paper
Full-text available
Biodiversity loss is one of the global challenges that we all encounter due to over exploitation of natural resources by human beings. The Black-crowned Crane (Balearica pavonina L.) is one of the six crane species found in Africa with population declining and considered as vulnerable species. Black-crowned Crane habitat especially wetlands are declining in many regions. Because wetlands are declining in extent and areal coverage, we suggest convincing the importance’s of wetlands for the local communities as one of the major ecosystem services is a pre-requisite actions for conservation. To minimize the over-exploitation of wetlands, understanding the knowledge, attitude and practices of local people is important for conservation actions. Human beings drive both threats to biodiversity and its conservation. In order to minimize the threat and loss of the species, the bottom-up and top-down conservation approaches was conducted in Jimma Zone, south-western Ethiopia. Both approaches are complementary and necessary components of conservation. A systematic survey research, field observation, and focused group discussions was conducted from March 2015 to January 2016 in the study area in order to identify the major threats of Black-crowned Crane and the way forward for practical conservation actions. The overall results show that the Black-crowned Crane is under threats because of habitat loss. To overcome the existing situations, various training and workshop was conducted for the communities, students at different levels and multi-stakeholders. Moreover, social media and mass media were frequently used for public awareness at large. Finally, the findings suggests that greater attention is needed to promote public awareness on Black-crowned Crane conservation using both bottom-up and top-down conservation approaches.
... Another explanation could be that the implementation of Natura 2000 was not completely successful. As Blicharska et al. (2016) [68] and Maczka et al. (2019) [69] highlighted, stakeholder involvement is a key factor for success. In CEE countries which joined the EU from 2004, the Natura 2000 implementation was too fast, and they have no tradition of a broad stakeholder inclusion and are still characterized by top-down governance [68]. ...
... Another explanation could be that the implementation of Natura 2000 was not completely successful. As Blicharska et al. (2016) [68] and Maczka et al. (2019) [69] highlighted, stakeholder involvement is a key factor for success. In CEE countries which joined the EU from 2004, the Natura 2000 implementation was too fast, and they have no tradition of a broad stakeholder inclusion and are still characterized by top-down governance [68]. ...
... As Blicharska et al. (2016) [68] and Maczka et al. (2019) [69] highlighted, stakeholder involvement is a key factor for success. In CEE countries which joined the EU from 2004, the Natura 2000 implementation was too fast, and they have no tradition of a broad stakeholder inclusion and are still characterized by top-down governance [68]. In contrast, our findings related to national protected areas showed highly significant positive spatial association (recreational and educational services). ...
Article
Full-text available
Despite the growing quantity of ecosystem-services-related research, there is still a lack of deeper understanding on cultural ecosystem services (CES). This is mainly due to the perception of CES, which can vary by geographic location and population. In this study, we present a Public Participation Geographic Information System (PPGIS) method in a Hungarian microregion. Our goal is to increase understanding on how cultural services are perceived in this geographical context and level, and how this relative importance is related to biophysical landscape features. We also consider the influence of accessibility on the perceived landscape and compare our findings with the results of other studies with different sociocultural backgrounds. The research consists of participatory mapping with 184 persons that were digitized and analyzed with GIS and statistical software. During the analysis, we identified CES hotspots and compared CES with landscape features, as well as CES perception with accessibility. Our results showed positive correlation of CES with land covers related to built-up areas, as well as aesthetic and recreational services with water bodies. Compared to other studies, we found different spatial relationships in the case of spiritual services, and higher importance of agricultural land covers during the CES perception, thanks to the Central-Eastern European (CEE) sociocultural background. Our study highlights the effect of accessibility on CES perception; nevertheless, these relationships varied by different infrastructural elements. We conclude by discussing the implications and limitations of our study and encouraging future landscape research to apply the PPGIS method in this geographical context.
... The Convention on Biological Diversity (Rio de Janeiro 1992) is the epitome of liberal conservation strategy, a compromise between the designation of Protected Areas (PAs henceforth), re-regulation of the environment, and commodification of biotic resources (Secretariat of the Convention on Biological Diversity, 2005). Real-world results in implementing this conservation strategy are relatively weak (e.g., Blicharska et al., 2016;Butchart et al., 2010;Perrings et al., 2010;Tittensor et al., 2014; Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES) 2019; Troumbis, 2021). Research on the so-called biodiversity conservation implementation gap or space (e.g., Maas et al., 2019), i.e., disciplinary and geographical biases and limited communication between scientists, practitioners, and decision-makers, is actively developing. ...
... It should be explicit, allowing for conceptual enrichment in a way that facilitates interdisciplinary collaboration, transnational coordination, and ultimately judge's decision, for it addresses cases that might carry built-in ambiguity in expert terminology and semantics if examined from the perspective of different scientific disciplines. It should also be formal to avoid Courts oscillating for justice between incumbent administrative policies and choices regarding conservation (e.g., Blicharska et al., 2016); theoretical mismatches of general penal and biodiversity crime cases (e.g., Barton & Moran, 2013); insufficient prosecution dossiers; insignificant judicial statistics, similar to those in unregistered crime (e.g., Stroh et al., 2016); and, theoretically unprepared benches and district attorneys (e.g., Rose, 2011). Figure 7 presents such an ontology and a typology of biodiversity crime. ...
Article
Full-text available
This paper examines aspects of the relationship between (1) the recently typified form of biodiversity crime, (2) information made available to the public through the Internet, and (3) cultural dynamics quantified through info-surveillance methods through Culturomics techniques. We propose two conceptual models: (1) the building-up process of a biodiversity crime culturome, in some language, and (2) a multi-stage biodiversity conservation chain and biodiversity-crime activities relating to each stage. We use crowd search volumes on the Internet on biodiversity crime-related terms and topics as proxies for measuring public interest. The main findings are: (1) the concept of biodiversity-crime per se is still immature and presents low penetration to the general public; (2) biodiversity-crime issues, not recognized as such, are amalgamated in conservation-oriented websites and pages; and (3) differences in perceptions and priorities between general vs. niche public with particular interest(s) in environmental issues- are discernable.
... Conservation social science is a recent discipline and uses social science to improve conservation practice, from individual to community, and at local-to-international levels [15,17,18]. This concept combines sociology, psychology, and communication, to provide a human dimension for natural resource management [17]. ...
... If provided with the right conservation message, the community and private sector could become actively involved during the planning, decision making, and evaluation stages, and raise their moral beliefs and values toward pro-conservation behavior [52][53][54]. Voicing opinions for conservation practices in line with social-economic needs, and built on local knowledge, would gain traction for supporting conservation [18,55]. ...
Article
Full-text available
Garnering support from multiple stakeholders to increase the number or size of protected areas remains a key challenge for wildlife conservation efforts in Malaysia. Human–wildlife conflict often arises when local socio-economic development compromises wildlife survival due to negative landscape changes. It is essential to assess both human–wildlife conflict and human–human conflicts about wildlife, in order to promote mutually beneficial human–wildlife coexistence. This paper examines pertinent factors influencing wildlife conservation by integrating ecological and social approaches using a conservation planning framework. The findings demonstrate the importance of appraising social values to address issues such as size limits for protected areas and compensation for wildlife damage to property. It shows that monetary incentives are not the sole determinant in gaining the support of indigenous people in reporting wildlife crimes and their active participation in conservation programs. Therefore, developing effective communication with stakeholders, empowerment of rural communities, and proper appraisal of social values are all urgently needed to promote effective rural wildlife conservation programs.
... It requires a balanced approach between ecological, social, and economic aspects of the landscape. Biodiversity conservation, especially for large carnivores, is affected by the nature of human-wildlife relationships (e.g., traditional values) and socioeconomics of the landscape [112][113][114][115]. These relationships and people's perception toward wildlife and conservation are often driven by factors that vary with scale (e.g., at household and village level) but also across and between landscapes [112,113,116,117]. ...
... These relationships and people's perception toward wildlife and conservation are often driven by factors that vary with scale (e.g., at household and village level) but also across and between landscapes [112,113,116,117]. Therefore, more efforts are required to understand these relationships and integrate them into planning at the local scale [114]. Further, this analysis can benefit from the availability of detailed socioeconomic cost data and ecosystem service supply maps in the landscape, as utilized in other studies [118]. ...
Article
Full-text available
Conservation approaches in tiger landscapes have focused on single species and their habitat. Further, the limited extent of the existing protected area network in India lacks representativeness, habitat connectivity, and integration in the larger landscape. Our objective was to identify sites important for connected tiger habitat and biodiversity potential in the Greater Panna Landscape, central India. Further, we aimed to set targets at the landscape level for conservation and prioritize these sites within each district in the landscape as specific management/conservation zones. We used earth observation data to derive an index of biodiversity potential. Marxan was used to identify sites that met tiger and biodiversity conservation targets with minimum costs. We found that to protect 50% of the tiger habitat with connectivity, 20% of the landscape area must be conserved. To conserve 100% of high biodiversity potential, 50% moderate biodiversity potential, and 25% low biodiversity potential, 55% of the landscape area must be conserved. To represent both tiger habitat and biodiversity, 62% of the total landscape area requires conservation or restoration intervention. The prioritized zones can prove significant for hierarchical decision making, involving multiple stakeholders in the landscape, including other tiger range areas.
... This under-representation of socially focused research and capacity has considerable implications for decision making and a concerted effort to address these imbalances is needed . More particularly, in the absence of relevant social, political, or economic research advice, non-scientific sources of evidence, opinion, political agendas or other views, are more likely to influence the decision-making process (Ban et al., 2013;Blicharska et al., 2016). ...
Thesis
Full-text available
The pervasiveness of threats posed by biological invasions presents significant challenges to human well-being, biodiversity conservation, and natural resource management, which has contributed to the growth of invasion science as a discipline. However, several studies have shown that the social-ecological complexity of invasions, the compartmentalisation of knowledge into disciplines and the lack of integrative research approaches, current invasion research has not informed management decision making effectively. Thus, to maximise the impact of research investments, there is a need to explore and evaluate how research informs management practices and processes linked to biological invasions. Accordingly, this dissertation outlines the state of invasion management-related research in South Africa, using the internationally recognised Working for Water (WfW) programme as a case study. Drawing on insights from science studies and evaluation research, a mixed-method approach is used to assess the processes, conditions and outputs associated with research produced under the programme’s auspices. The research comprised two areas of inquiry 1) the exploration of textual information (journal articles, grey literature, and their content), and 2) the social dimensions of research and decision making linked to invasion science and management, with a specific focus on collaborative relationships amongst scientists and decision makers. It sought to determine the extent to which published research aligned with the programme’s needs, research and management strategies. The research also aimed to identify effective ways for organising and producing knowledge relevant to decision making; and to provide insights into how the social dimensions, the people and organisations, their interactions and impact, have shaped research and decision-making processes. Findings suggest that there are significant gaps in the knowledge base particularly in relation to the social dimensions of biological invasions, which were poorly represented and aligned with the mandate and priorities set by the programme. This research showed significant deficiencies in knowledge management and the uptake of research funded by the programme, despite its potential relevance to decision making as evidenced by the recommendations presented in the research. Moreover, research produced under WfW’s auspices was authored by a handful of key researchers who fulfil a significant role in shaping research collaborations both across disciplines and institutions. The loss of these key individuals, including those involved in management-related decision making, would be detrimental to the stability of collaboration networks and research productivity. Finally, findings show that research productivity, collaborative relationships between scientists within and across research organisations, and between research and decision-making processes are positively influenced by collegiality and cooperation between actors, while increased competition and bureaucratisation in the workplace negatively influence research productivity. To address the shortcomings concerning the invasion research and management identified in this dissertation, efforts towards improving the relationship between researchers and decision-makers and building more resilient collaboration networks need to be implemented. Firstly, institutions must engage in and fund more targeted, long-term transdisciplinary or integrative research that incorporates appropriate structures that foster collaboration, knowledge coproduction and knowledge sharing. Secondly, systems and strategies for monitoring and evaluating research, including the use of bibliometric indicators, social network analyses and qualitative assessments, should be developed to ensure that research relevant to managing biological invasions is not lost to the decision-making process. Such an undertaking would in turn require the development of an integrated research strategy and action plan that accounts for both the knowledge management and the social processes underpinning research and decision making.
... However, for a noticeable number of the workshops' attendees and PA managers, PA designation had had some negative impacts on local wellbeing and depopulation due to restrictions to economic activities. The authors of [25] found similarly negative social perceptions on Natura 2000 sites linked to socioeconomic restrictions and little social engagement in PA designation and management across Europe. These results also align with a previous study using official statistics in Spain where protected municipalities generally performed worse than unprotected ones when facing rural depopulation [17]. ...
Article
Full-text available
Protected areas (PAs) are thought by some to contribute to local wellbeing and socioeconomic development, whereas for others PAs remain a regulatory burden that hampers rural development. Here, we sought to ascertain the perceived causes of rural depopulation and the potential impact of four Natura 2000 sites on the wellbeing and depopulation figures of four protected rural municipalities in Spain that were selected as extreme case studies. We used phone surveys to elicit experts’ views (n = 19) on the topic and convened eight in-person workshops to garner local residents’ insights (n = 40) using structured questionnaires. We complemented perceived wellbeing data from PAs with surveys to residents in neighbouring unprotected municipalities (n = 28). Both experts and workshops’ attendees from protected municipalities overwhelmingly attributed depopulation figures to structural causes linked to transport accessibility, basic service provision and the existence of job opportunities, which they perceived to be unrelated to the PAs’ regulations or management. Local residents did generally not perceive any impact on their collective or individual wellbeing from those PAs, and most who did, expressed a negative impact chiefly due to socioeconomic restrictions. Four-fifths of the experts and half of the workshops’ attendees from protected municipalities, however, expressed that PAs’ administrations could help improve depopulation figures in their towns mainly through promoting tourism and greater compatibility of land uses, including housing and infrastructure development. While the assessed Natura 2000 sites certainly have scope for tourism promotion, their lenient legal regimes make it largely unfeasible to broaden land use compatibility without damaging protected features.
... It has been revealed that protected areas may be insufficient to provide effective conservation of flying insects (Hallman et al., 2017) or to prevent biological invasions (Guerra et al., 2018). Effectiveness of Natura 2000 sites may depend on public perception of the network (Blicharska et al., 2016), human population size, and taxonomic group considered (Trochet and Schmeller, 2013). Despite the increasing interest in ecological studies conducted in Natura 2000 sites, little is known about the actual effectiveness of Natura 2000 sites on the status and population trends of focal species in habitats vulnerable to increasing urbanisation pressure. ...