The European Alps harbour a unique and species-rich biodiversity, which is increasingly impacted by habitat fragmentation through land-use changes, urbanization and expanding transport infrastructure. In this study, we identified the 50 most important questions relating to the maintenance and restoration of an ecological continuum – the connectedness of ecological processes across many scales including trophic relationship and disturbance processes and hydro-ecological flows in the European Alps. We initiated and implemented a trans-national priority setting exercise, inviting 48 institutions including researchers, conservation practitioners, NGOs, policymakers and administrators from the Alpine region. The exercise was composed of an initial call for pertinent questions, a first online evaluation of the received questions and a final discussion and selection process during a joint workshop. The participating institutions generated 484 initial questions, which were condensed to the 50 most important questions by 16 workshop participants. We suggest new approaches in tackling the issue of an ecological continuum in the Alps by analysing and classifying the characteristics of the resulting questions in a non-prioritized form as well as in a visual conceptualisation of the inter-dependencies among these questions. This priority setting exercise will support research and funding institutions in channelling their capacities and resources towards questions that need to be urgently addressed in order to facilitate significant progress in biodiversity conservation in the European Alps.
Citation: Walzer C, Kowalczyk C, Alexander JM, Baur B, Bogliani G, Brun J-J, et al. (2013) The 50 Most Important Questions Relating to the Maintenance and Restoration of an Ecological Continuum in the European Alps. PLoS ONE 8(1): e53139. doi:10.1371/journal.pone.0053139
Editor: Raphaël Arlettaz, University of Bern, Switzerland
Received: August 30, 2012; Accepted: November 23, 2012; Published: January 14, 2013
Copyright: © 2013 Walzer et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Funding: Funding for this project was provided in part by the “Platform Ecological Network” of the Alpine Convention (http://www.alpconv.org/en/organization/groups/WGEcologicalNetwork/default.html) and the ECONNECT project funded by the EU within the framework of the European Territorial Cooperation Alpine Space Programme and co-funded by the European Regional Development Fund (www.econnectproject.eu). RH was supported by the CCES-GENEREACH project of the ETH domain. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors acknowledge that one of the co-authors (AR) is employed by a private company (PiU GmbH). This fact does not, in any way, alter the authors’ adherence to all PLOS ONE policies on sharing data and materials.
The European Alps span eight countries, from the Mediterranean shores of Southern France to Slovenia and link with adjacent mountain ranges such as the Carpathians, Balkans and Apennines. The Alps harbour an extraordinary diversity of habitats, plants and animals including many endemics. They are considered as one of the most important regions for the preservation of biodiversity in Europe . However, the Alps are also the home and workplace of up to 14 million people and a holiday destination for more than 100 million tourists each year. Anthropogenic land-use changes, urbanization and the development of transport infrastructure have fragmented the ecological continuum - the connectedness of ecological processes across many scales including trophic relationship and disturbance processes and hydro-ecological flows of the Alps , . Plant and animal populations become increasingly isolated on ever-smaller remnant habitat patches in a human-dominated landscape. Isolation leads to increased vulnerability in the face of stochastic events and decreased genetic diversity . Enhancing ecological connectivity is an integral part of the European Commission’s ambitious 2020 Biodiversity Strategy (http://ec.europa.eu/environment/nature/ecosystems/index_en.htm). During the past few years, major efforts have been undertaken to maintain and foster pan-alpine biodiversity. The “Platform Ecological Network” of the Alpine Convention (http://www.alpconv.org/en/organization/groups/WGEcologicalNetwork/default.html), the “Ecological Continuum Initiative” (http://www.alpine-ecological-network.org/about-us/ecological-continuum-initiative) and the Alpine Space project “ECONNECT” (www.econnectproject.eu) are three examples of such initiatives that also aim at enhancing ecological connectivity across the Alpine range.
ECONNECT is a project funded by the EU within the framework of the European Territorial Cooperation Alpine Space Programme and co-funded by the European Regional Development Fund. The project envisions an enduringly restored and maintained ecological continuum, consisting of inter-connected landscapes and protected areas, across the Alpine Arc region, where biodiversity will be conserved for future generations and the resilience of ecological processes will be enhanced. Employing an integrated and multidisciplinary approach, the project has provided an Alpine-wide overview on areas important for ecological connectivity by integrating quantitative and qualitative information on selected sites and the level of interconnectivity among them . Additionally, social, legal and economic barriers to connectivity have been identified and proposals made on how to overcome them . However, in the course of the project it became evident that relevant knowledge and information is missing despite being considered essential for on-going and future projects. This knowledge gap includes consistent scientific definitions, evidence-based assessment methods, evaluation of impacts on the ecological continuum in the Alps as well as best practice measures. Similarly, other authors have recently addressed an analogous lack of evidence in respect to the design and implementation of ecological corridors, an important conservation intervention in an ecological continuum . To address and surmount this knowledge deficit, the three initiatives mentioned above formed a small core group comprising both researchers and practitioners in order to start a process identifying these knowledge gaps.
Sutherland et al. 2011  introduced the method of a “priority setting exercise” to identify research needs of practitioners and policy makers. Identifying research needs is essential in furthering evidence-based conservation , . Priority setting exercises have been successfully applied in the UK, USA, Switzerland and even on a global scale tackling such diverse issues as biodiversity, global agriculture and national environmental policy –. A priority setting exercise identifies existing knowledge, supports research and helps funding institutions channel their capacities and resources towards questions that need to be urgently answered in order to facilitate significant progress in a respective field: in our case biodiversity conservation in the European Alps.
In this study, we identified the 50 most important questions relating to the maintenance and restoration of an ecological continuum in the European Alps. We initiated and implemented a trans-national priority setting exercise, inviting researchers, practitioners, NGOs, policy makers and other stakeholders from the Alpine region to participate. The exercise was composed of an initial call for pertinent questions, a first online evaluation of the received questions and a final discussion and selection process during a joint workshop. Furthermore, we suggest new approaches in tackling the issue of an ecological continuum in the Alps by analysing and classifying the characteristics of the resulting questions in a non-prioritized form as well as a visual conceptualisation of the inter-dependencies among these questions.
The non-prioritized list of the 50 most important questions concerning an ecological continuum in the Alps is shown in tables 1 and 2. The resulting questions were individually classified broadly in nature-, people- and management contexts (NC, PC, MC) based on a concept previously introduced by Worboys et al. . Each context area has three sub-topic areas to which the questions are finally attributed. For reasons of clarity, we assign each question to only one context area, but provide the second interrelated context and dependencies in brackets where appropriate.
The largest proportion of questions (46%) was attributed to the nature context. The nature context questions are rather evenly distributed between the three subtopics. This is followed by the management context (44%) where by far the largest proportion of questions relates to the legislation, policy and planning needs subtopic (63%). Finally the people context makes up a mere 10% of the total questions. From the 50 questions, by far the largest fraction (60%) was formulated as “how” questions, followed by “what” (26%) and “which” questions (14%). Consequently, most attention was given to transformation processes aiming at practices to improve the current situation in Alpine connectivity.
Visualization of Interactions, Inter-relations and Dependencies of the 50 Final Questions
We created a graph in the form of a web to illustrate the “location” of each question within the framework of the nine sub-topics in the nature-, people- and management-context (Figure 1). Each context and its assigned questions are shown in the same colour, whereas the sub-topics in each context area are given in varying shades of the same colour (NC: green; PC: red; MC: blue). The sub-topics designate the edges of the web, while the questions from one context area are arranged in a connected cycle in the middle of the web to illustrate their interactions. Questions, which were also assigned to a second sub-topic of another context area, are interlinked with a grey line. Bold arrows indicate that this particular question has to be answered first before a subsequent one (to which the arrow points) can be addressed. In some cases, answers from two previous questions are required for the solution of a third question (e.g. question 8 depends on the answers from questions 1 and 5) whereas in other cases, two or three questions depend on the answer of a single question in advance (e.g. questions 2, 19 and 46 depend on the answer of question 15).
The nine sub-topics of the three context areas (nature: green; people: red; management: blue) mark the edges of the web. The questions of each context area are interlinked and marked in the same colour as the sub-topics they were assigned to. Questions (numbers; see text) which also address another context area are further linked with a second sub-topic, highlighting the interactions. Bold arrows indicate that one or more questions need to be solved before a subsequent question can be answered.
Overall, 27 questions were assigned to a second context area due to their transdisciplinary nature. The sub-topics 6 “economic, social and political needs” (PC) and 9 “tools, incentives, knowledge” (MC) showed the most inter-relations to other context areas (8 and 7 links, respectively).
The aim of this study was to identify and analyse gaps of knowledge with respect to achieving, restoring and maintaining an ecological continuum in the European Alps. In order to identify information gaps, we implemented an alpine wide “priority setting exercise” as previously described by Sutherland et al. . This exercise was a useful and efficient tool to compile inputs from various researchers, practitioners, administrators, stakeholders and policy makers from different countries with a relatively low initial effort. The major part of the process was performed via email communication and was administered part-time by one person. We feel that this resource-saving method is a strong argument in favour of this approach, especially given the generally limited resources for connectivity conservation , .
The output of priority setting exercises depends on a number of factors, such as the selection of participants, the number of individuals effectively involved in formulating the questions and on the voting system –. One selection bias that could arise as a consequence of listing some 400+ questions is that an individual performing the selection process is almost certainly going to become tired as he proceeds down the list. In order to address this possible bias in future exercises, it would be prudent to provide the numbered questions in a individualized random sequence to the participants. Decisions claim to be objective, however, since people’s choices are subjective, the only option is to make them “to the best of one’s knowledge”. Only a constant review-process from the organisational core team, consisting preferably of several people from different fields, and continuous discussion with and feedback from other colleagues can minimize the inherent bias. Recently Braunisch et al.  have reported on a two-step evaluation of a similar priority setting exercise that elegantly addresses bias through a process of rating and speciation of the questions. The composition of the workshop participants exemplifies this problem. Although we invited six policy makers to join the initiative, only two generated initial questions and only one participated in the workshop. The problem of a non-representative group of experts missing valuable issues has been pointed out by previous authors , ). In future efforts of this type, it could be beneficial to provide more information to the potential participants in order to alleviate any concerns as to information from discussions being individually attributed and distributed outside the framework of the actual exercise. Clearly stating, and explaining if necessary, that the Chatham House Rule: “When a meeting, or part thereof, is held under the Chatham House Rule, participants are free to use the information received, but neither the identity nor the affiliation of the speaker(s), nor that of any other participant, may be revealed”. (http://www.chathamhouse.org/about-us/chathamhouserule) will be adhered to is in our view beneficial to encourage openness and the sharing of information. Furthermore, as previously stated by Wuelser et al.  effective transdisciplinary problem framing and research orientation exercises require a careful specification of context and purpose. Possibly, this exercise was unsatisfactorily framed with a generic “identifying knowledge gaps”. Without a clearly defined output context it can be difficult for an individual to select the most important questions from the bulk of initially proposed questions.
A further issue that hindered and complicated the exercise is the fact that the Alps are distributed across eight countries, 28 regions, 98 provinces and 5 spoken languages. Participants originated from five alpine countries (in the collection phase complemented by one participant from the UK) and divergent cultural backgrounds. In contrast to most previous studies that were English-language based, this study involved four different languages (English, German, French and Italian), which made the succinct formulation of questions particularly difficult. We tried to alleviate the fact that English was a foreign language to all of the participants by consulting with a native speaker during the entire process. Similarly, Braunisch et al.  had to deal with multiple languages in their study and in contrast to this study opted to translate questions into the two main local languages (French and German). Moreover, we tried to address uncertainties in the formulation of questions by making direct queries to the main author of a question if needed and encouraged all participants to do the same during the evaluation process and the workshop. It is interesting to note that numerous questions are formulated in very generic terms. While this is possibly a result of language constraints, it can, in these authors’ view also be seen as a consequence of the nonspecific use of the term “connectivity” and the wide-ranging interpretation and understanding of the term. In contrast to a previous study in Switzerland (Braunisch et al.) it is interesting to note the absence of species- specific questions and the significant integration of questions related to ecological theory (14%) in this study. While the significance of this theoretical basis has been recognized in this exercise it is clear that these questions are inherently difficult to address and implement into action  We analysed the interactions, inter-relations and dependencies of the final questions that resulted from the priority setting exercise in order to suggest approaches to answer these questions. Therefore, we classified the questions into a nature-, people- and management context, applying a concept previously introduced by Worboys et al. . The majority of the questions (54%) could be assigned to more than one context area, indicating the transdisciplinary character of the results. It is important to note that the resulting list is neither prioritized in respect to the individual questions nor in respect to the assigned contexts. The nature context though listed first does not necessarily take precedence over the people and management contexts in framing this problem. It is interesting to note that while only 4 questions were attributed to the people context, these were highly inter-linked to other questions clearly demonstrating in this case the pivotal role of economic, social and political needs. Braunisch et al. have previously showed a similar importance of questions reconciling biodiversity conservation with societal and economic goals for Switzerland  though, the goal of this exercise was a non-prioritized list, eleven questions where directly dependent on each other, suggesting that a chronological order must be considered when addressing these problems. This fact inherently creates some prioritization. In order to answer question 8 “Which of the habitat types important for landscape connectivity are most affected by climate change?”, we first need to understand question 1 “Which landscape elements and land use types enhance or moderate the gaps in connectivity?”. Furthermore, the answer to question 5 “Which indicators reflect the changes in connectivity that result from climate or human induced changes in Alpine landscapes?” is also essential to adequately address question 8 above. Hence, question 8 depends on the results of two other questions.
Similarly question 15 “What is an effective set of indicators (for species and habitats) that can be used to evaluate and monitor connectivity at different scales?” is a prerequisite in addressing 3 other questions: namely question 2 “How are corridors best implemented; with clearly spatially defined borders or as functional units integrated in wide ecological continuums?”, question 19 “Are artificially engineered ecological networks a threat or benefit to endemic species?” and question 46 “What methods can be used to record the effectiveness of functional connectivity, or its elements, across different spatial and temporal scales?”. Essential questions like question 15, dealing with indicators and methodological approaches, should be given clear priority, as their answer is a precondition for scientifically sound answers to other, subsequent questions.
Solving certain questions in a consecutive order indicates a potential time lag between putting forward a question and actually answering it. This time lag may lead to a change of the initial situation, which would imply that the results of the preceding question are no longer suitable for solving the initial issue. This time lag in connectivity conservation makes it impossible to “come back” to the initial situation after the extended process of research, decision-making and implementation. This clearly indicates that there is an asymmetric drift of the initial problem and its proposed solution due to the general inertia in decision-making processes dealing with environmental issues. As holds true for numerous environmental problems, most notably global climate change, we suggest that the conservation and restoration of an ecological continuum is a “wicked problem” . The example of question 19 clearly demonstrates several characteristics of a “wicked” and possibly even a “super-wicked problem” .
The gaps of knowledge, in conserving and restoring connectivity emphasized in this exercise make evident that these involve a highly dynamic and interconnected process rather than a simplistic and straightforward approach. It appears essential to reconcile the dynamic and complex nature of the problem with the problem solving approaches. Inadequate simplification of the interdependencies will possibly lead to results that are not relevant in forming policy . Furthermore, our results indicate that maintaining and restoring ecological connectivity in the Alps is most likely a “super-wicked problem”, and this implies the need for novel approaches in addressing this issue. As has been previously suggested by other authors, we also feel strongly that the usual backward looking method of investigating the past and generating selective and singular predictions, is only sufficient for “tame problems” but inadequate for a highly dynamic and interconnected process such as ecological connectivity , .
In order to address the complex issue of an Alpine ecological continuum, it appears necessary to apply a forward reasoning approach which identifies possible future scenarios and integrates uncertainties . It is somewhat surprising that questions concerning how ecological connectivity is affected and can be managed make up the largest percentage (60%) of the generated questions. Authors from the field of transdisciplinary research have termed knowledge related to this type of question “transformation knowledge” , . These questions deal with the genesis and future development of a problem and subsequently with the interpretation and perception of the problem in the “real world”. “What” questions address determining factors of connectivity, and answers to such questions provide “system knowledge”. Finally, “which” questions address desired goals and better practices. This has been termed “target knowledge”. Each of these knowledge forms has specific challenges and notably “system knowledge” must confront uncertainties. It is essential to understand that solutions are only possible when the other postulated forms of knowledge, “target-” and “transformation knowledge”, are integrated into the solution-mix. Another method introduced by Sutherland et al. , , called “horizon scanning”, an exercise that focuses on potential threats and opportunities in the future rather than identifying present knowledge gaps, may supplement and enhance this approach.
The visual “chaos” and multi-structural character of our results, shown in the “web of questions” (Figure 1), reflects the sectoral structure of society, governance and administration with respect to environmental problems in general. To overcome this, an integrative transdisciplinary approach is necessary. What appears to be missing in order to find a starting point to address the problem of the Alpine ecological continuum, is a common strategy or vision , . In the authors’ view, this is also supported by the fact that the largest percentage of the formulated questions questioned the manner, condition or quality of ecological connectivity. This exemplifies the necessity of generating “system knowledge” and confronting uncertainties. Total conformity among all actors in the search for a common denominator is unrealistic and cannot be a realistic goal, as Worboys et al.  have pointed out, but a clear vision that “expresses the joint aspirations of leaders, managers and participants in the initiative, without closing off avenues for constructive debate and disputation” to support and sustain connectivity conservation may be a starting point. Possibly, ecological connectivity can constitute a common “anchor” for trans-sectoral deliberations on biodiversity conservation. However, in order to not become overburdened by the complexity of the issue, it appears essential to address the inherent complexity within a well-reflected investigational framework .
For this type of study to provide guidance and contribute towards conservation-action implementation the results must be disseminated accordingly. As has been pointed out previously, bridging the gap of knowledge between research and conservation practice cannot be achieved with unidirectional platforms , . While other authors have suggested that new platforms of bidirectional knowledge dissemination must be developed these authors believe that it is more efficient to employ and if necessary adapt existing information platforms. The results from this study will be disseminated over existing platforms, most importantly the “Platform of Ecological Networks” of the Alpine Convention. This platform encompasses representatives of the Alpine countries, protected areas, Alpine institutions and experts. It strives to provide a bidirectional link between policy makers, the scientific community and practitioners and encourages more efficient cooperation with other sectors . As has been pointed out by Braunisch et al. , integrating scientifically trained and transdisciplinary-cognizant personnel that can translate science and ease the exchange of information could significantly enhance the effectiveness of such platforms. In these authors view, an initial task of the platform could be to organize and facilitate research and conservation-action activities centred on the inter-dependent questions identified in this study. It is the authors’ opinion that this priority setting exercise and the subsequent dissemination of results will support research and funding institutions in channelling their capacities and resources towards questions that need to be urgently addressed in order to facilitate significant progress in biodiversity conservation in Europe and specifically in the Alps. Furthermore, the definition of 50 most important questions is an important first step towards a common and harmonized approach in maintaining and enhancing ecological connectivity across the heterogeneous Alpine arch.
Priority Setting Exercise to Identify Gaps of Relevant Knowledge and Generating the most Urgent Questions
A core team of five researchers and practitioners initiated and facilitated the entire exercise. The priority setting process was divided into four steps: initiation, assembling and organizing initial questions, pre-workshop voting and workshop voting. The method has been previously described in detail in various publications –. Therefore, we only briefly outline the main steps of the process. Further information on characteristics of the participants and the voting process are given in Table 3.
- Initiation. Based on the individual networks of the core team and striving to depict a representative cross-section of the main players in Alpine biodiversity conservation, we invited 48 institutions including researchers, conservation practitioners, NGOs, policymakers and administrators from the Alpine area to participate in this initiative.
- Collating of initial questions. 25 of the invited 48 institutions (52%) generated 484 initial questions. The core team collated and assigned these questions to twelve main topics for clarity (Table 3).
- Pre-workshop voting. In order to reduce the set of questions, we distributed the initial-questions-list to all participants for a first evaluation. Rephrasing and adding of questions was actively encouraged at this stage. In preparation for the workshop phase, participants were then asked to select a maximum of 55 questions from the total of 484 questions submitted. Participants were also asked to only select questions from areas in which they had sufficient knowledge base. A total of 385 questions received at least one vote and an additional 15 questions were proposed at this stage.
- Workshop. Final discussion and voting took place during a two-day workshop in December 2010 in Switzerland. Unfortunately, only 16 participants were able to attend. The remaining 400 questions assigned to the twelve topic areas (median: 33; range: 24–46/topic area) were discussed in four sessions. In each session, three groups worked simultaneously to reduce and rephrase the questions. In the plenary session the participants decided to reduce the questions to 50 instead of 55 due to overlaps. The final 50 questions were selected in a plenary session by majority vote following discussion.
II) Classification and Analysis of the Questions
The core team ascribed individual questions from the final non-prioritized list of 50 questions, to three interacting context areas according to a slightly modified, previously published, management framework for connectivity conservation: nature-, people- and management contexts. Each context area has 3 interacting sub-topic areas, We subsequently assigned each question to one or more sub-topic area within the individual context areas (Figure 2) . We selected the context area most likely concerned when addressing the question and the context area that would be affected by the outcome. This approach was given preference over linking questions to a context area with respect to the cause of the issue or question. For instance, question 5 “Which indicators reflect the changes in connectivity that result from climate or human induced changes in Alpine landscapes?” was assigned to “Structural and functional connectivity” and linked to “Tools, incentives, knowledge”, since the solution (“indicators” = tool, knowledge) provides answers to a particular problem (“changes in connectivity”). It is not a question concerning the causes of this problem (“climate or human induced changes”).
Every context area consists of three different sub-topics which interact with each other.
All questions were formulated either as (i) what - asking for information about something, (ii) which - asking about choice and (iii) how – questioning manner, condition or quality in order to further breakdown and classify the outcomes.
Finally, we established a simple non-prioritized list that attributes all 50 questions to the three context areas and respective sub-topics (Tables 1 and 2). The majority (54%) of the final 50 questions could be assigned to two context areas due to their transdisciplinary nature. Furthermore, we identified direct dependencies of individual questions on other questions, meaning that a specific question can only be solved if another question is answered beforehand. Finally, we created a graphic conceptualisation showing the interactions, inter-relations and dependencies of the questions.
The authors thank the following persons for the submission of questions and comments: Michaela Kuenzl and Anne-Katrin Heinrichs (Nationalpark Berchtesgaden, Germany); Kerstin Lehmann (Bundesamt für Naturschutz, Federal Ministry for the Environment, Nature Conservation and Nuclear Safety, Germany); Kathrin Renner (European Academy of Bozen - EURAC); Daniela Pauli and Marc Gessner (Swiss Biodiversity Forum); Janine Bolliger (Swiss Federal Institute of Technology/Swiss Federal Institute for Forest, Snow and Landscape Research WSL); Christina Kubalek and Natalia Razumovsky (WWF Austria); Gabor von Bethlenfalvy (Federation of Associations for Hunting and Conservation of the EU (FACE)); Anke Hahn (Transeconect); Anne-Sophie Croyal (Conseil general de L’Isere, France); Michael Proschek Hauptmann (Umweltdachverband, Austria); Riccardo Santolini (Univ. of Urbino, Italy); Karl Buchgraber (LFZ Raumberg-Gumpenstein, Austria); Rebecca Drury (FIWI, Austria), Marianne Badura (BLUE!). Renate Hengsberger for editing support.
Implemented the study: CW C. Kowalczyk YK TS LF. Developed the study design: CW C. Kowalczyk WJS TS. Provided significant editorial inputs: JMA BB C. Kueffer R. Holderegger AR RS. Participated in question generation, question evaluation and workshop discussions: CW C. Kowalczyk JMA BB GB JJB LF MOG R. Haller R. Holderegger YK AR RS AUS SNVB TS. Analyzed the data: C. Kowalczyk CW. Wrote the paper: CW C. Kowalczyk TS.
- 1. Kohler Y, Scheurer T, Ullrich A (2009) Ecological networks in the Alpine Arc. Innovative approaches for safeguarding biodiversity. J Alp Res 97. doi: 10.4000/rga.808.
- 2. Lindenmayer D, Fischer J (2006) Habitat fragmentation and landscape change: an ecological and conservation synthesis. Melbourne: CSIRO Publishing.
- 3. Soulé ME, Mackey BG, Recher HF, Williams JE, Woinarski JC, et al.. (2006) The role of connectivity in Autralian conservation. In: Crooks KR, Sanjayan M, editors. Conservation biology 14: connectivity conservation: Cambridge University Press pp. 649–675.
- 4. Keller LF, Waller DM (2002) Inbreeding effects in wild populations. Trends Ecol Evol 17: 230–241 doi:10.1016/S0169-5347(02)02489-8.
- 5. Walzer C, Angelini P, Füreder L, Plassmann G, Renner K, et al.. (2011) Webs of life - Alpine biodiversity needs ecological connectivity - Results from the ECONNECT project. Milan Grafica Metelliana.
- 6. Füreder L, Waldner T, Ullrich-Schneider A, Renner K, Streifeneder T, et al.. (2011) Econnect - Policy recommendations. Innsbruck: STUDIA Universitätsbuchhandlung und -verlag. 16 p.
- 7. Beier P, Gregory AJ (2012) Desperately Seeking Stable 50-Year-Old Landscapes with Patches and Long, Wide Corridors. PLoS Biol 10: e1001253 doi:10.1371/journal.pbio.1001253.
- 8. Sutherland WJ, Fleishman E, Mascia MB, Pretty J, Rudd MA (2011) Methods for collaboratively identifying research priorities and emerging issues in science and policy. Methods Ecol Evol 2: 238–247 doi:10.1111/j.2041-210X.2010.00083.x.
- 9. Milner-Gulland EJ, Fisher M, Browne S, Redford KH, Spencer M, et al. (2010) Do we need to develop a more relevant conservation literature? Oryx 44: 1–2 doi:10.1017/S0030605309991001.
- 10. Sutherland BJ, Pullin AS, Dolman PM, Knight TM (2004) The need for evidenced-based conservation. Trends Ecol Evol 19: 305–308 doi:10.1016/j.tree.2004.03.018.
- 11. Sutherland WJ, Armstron-Brown S, Armsworth PR, Brereton T, Brickland J, et al. (2006) The identification of 100 ecological questions of high policy relevance in the UK. J Appl Ecol 43: 617–627 doi:10.1111/j.1365-2664.2006.01188.x.
- 12. Sutherland WJ, Adams WM, Aronson RB, Aveling RB, Blackburn TM, et al. (2009) One hundred questions of importance to the conservation of global biological diversity. Conserv Biol 23: 557–567 doi:10.1111/j.1523-1739.2009.01212.x.
- 13. Sutherland WJ, Albon SD, Allison H, Armstrong-Brown S, Bailey MJ, et al. (2010) The identification of priority policy options for UK nature conservation. J Appl Ecol 47: 955–965 doi:10.1111/j.1365-2664.2010.01863.x.
- 14. Braunisch V, Home R, Pellet J, Arlettaz R (2012) Conservation science relevant to action: A research agenda identified and prioritized by practitioners. Biol Conserv 153: 201–210 doi:10.1016/j.biocon.2012.05.007.
- 15. Worboys GL, Francis WL, Lockwood M (2010) Connectivity Conservation Management - A global Guide; Worboys GL, Francis WL, Lockwood M, editors. London, Washington DC: Earthscan. 382 p.
- 16. Bennett G (2004) Linkages in practice, a review of their conservation value. Gland: IUCN Publication Services.
- 17. Morrison S, Reynolds M (2006) Where to draw the line: integrating feasibility into connectivity planning. In: Crooks KR, Sanjayan M, editors. Conservation biology 14: connectivity conservation: Cambridge University Press pp. 536–554.
- 18. Cooke SJ, Danylchuk AJ, Kaiser MJ, Rudd MA (2010) Is there a need for a ‘100 questions exercise’ to enhance fisheries and aquatic conservation, policy, management and research? Lessons from a global 100 questions exercise on conservation of biodiversity. J Fish Biol 76: 2261–2286 doi:10.1111/j.1095-8649.2010.02666.x.
- 19. Wuelser G, Pohl C, Hirsch Hadorn G (2012) Structuring complexity for tailoring research questions to sustainable development: a framework. Sustain Sci 7: 81–93 doi:10.1007/s11625-011-0143-3.
- 20. Fazey I, Fischer J, Lindenmayer DB (2005) What do conservation biologists publish? Biol Conserv 124: 63–73 doi:10.1016/j.biocon.2005.01.013.
- 21. Rittel H, Webber M (1973) Dilemmas in a general theory of planning. Policy Sci 4: 155–169.
- 22. Lazarus RJ (2009) Super Wicked Problems and Climate Change: Restraining the Present to Liberate the Future. Cornell L Rev 94: 77 Available: http://ssrn.com/abstract=1302623.
- 23. Bernstein S, Lebow RN, Stein JG, Weber S (2000) God Gave Physics the Easy Problems. Eur J Int Rel 6: 43–76 doi:10.1177/1354066100006001003.
- 24. Hirsch Hadorn G, Hoffmann-Riem H, Biber-Klemm S, Grossenbacher W, Joye D, et al.. (2008) The emergence of transdisciplinarity as a form of research. In: Hirsch Hadorn G, Hoffmann-Riem H, Biber-Klemm S, Grossenbacher W, Joye D et al.., editors. Handbook of transdisciplinary research. Heidelberg: Springer. pp. 19–39.
- 25. ProClim/CASS (1997) Visions by Swiss researchers. Research on sustainability and global change - visions in science policy by Swiss Researchers. Berne: CASS/SANW. 33 p.
- 26. Sutherland WJ, Clout M, Cote IM, Daszak P, Depledge MH, et al. (2010) A horizon scan of global conservation issues for 2010. Trends Ecol Evol 25: 1–7 doi:10.1016/j.tree.2009.10.003.
- 27. Sutherland WJ, Woodroof HJ (2009) The need for environmental horizon scanning. Trends Ecol Evol 24: 523–527 doi:10.1016/j.tree.2009.04.008.
- 28. Arlettaz R, Mathevet R (2010) Dossier « Le réveil du dodo III » - Biodiversity conservation: from research to action. Natures Sciences Sociétés 18: 452–458 doi:10.1051/nss/2011009.
- 29. Roux DJ, Rogers KH, Biggs HC, Ashton PJ, Sergeant A (2006) Bridging the science-management divide: Moving from unidirectional knowledge transfer to knowledge interfacing and sharing. Ecol Soc 11: 4 online. Available: http://www.ecologyandsociety.org/vol11/iss1/art4/.
- 30. Ecological Networks in the European Alps. Available: http://www.alpine-ecological-network.org/.