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The following is the established format for referencing this article:
Stotten, R., L. Ambrosi, E. Tasser, and G. Leitinger. 2021. Social-ecological resilience in remote mountain communities: toward a novel framework for an interdisciplinary investigation. Ecology and Society 26(3):29.
https://doi.org/10.5751/ES-12580-260329
Research

Social-ecological resilience in remote mountain communities: toward a novel framework for an interdisciplinary investigation

1University of Innsbruck, Department of Sociology, 2University of Innsbruck, Department of Ecology, 3Eurac Research, Institute for Alpine Environment

ABSTRACT

Globally, mountain areas are facing numerous social, economic, and ecological challenges. The interplay of natural and social factors makes them complex social-ecological systems. To investigate a mountain setting in the Austrian Alps, we developed the resilient livelihood framework (RLF), relying on the sustainable livelihood framework and integrating the community resilience and ecosystem services concepts. This novel RLF highlights the basic function of natural capital for economic, social, cultural, and political capital and displays the social valorization and demand of single-ecosystem services. The RLF serves to examine the social-ecological complexities with a set of drivers, capitals, livelihood strategies, and outcomes of two remote mountain villages, Obergurgl and Vent in the Upper Ötztal Valley (Tyrol, Austria). Here, qualitative and quantitative descriptions enable comprehensive insights into the complex interplay of the social and ecological spheres of both communities. Its output has been densified and calculated with a modified Shannon-Wiener Index that revealed a higher social-ecological resilience for the village of Vent than Obergurgl. The study bridges various disciplines and contributes to the theoretical and practical advancement of a resilience framework through the application to a case study site by combining ecological and sociological approaches. The application study can serve as a pilot for similar applications in remote mountain areas to support the decision making of local managers and stakeholders.
Key words: community resilience; ecosystem services; forms of capital; Shannon-Wiener Index; sustainable rural livelihood framework

INTRODUCTION

Background

Although generally rich in natural and cultural resources, the economic development of mountain regions across the world has been lagging behind the development of lowlands for several centuries. Especially remote mountain communities in the developing countries of Asia, Africa, and Central and South America are still among the poorest in the world (Mishra 2002). The communities of the European Alps, however, have experienced rapid economic development, mainly driven by tourism in the 20th century (Barker 1982). Nevertheless, remote mountain communities in the European Alps are facing numerous social, economic, and ecological challenges. They have undergone substantial socioeconomic changes over the past decades, including a decrease in farms and farmland, especially in marginal areas, an overdependence on (winter) tourism as the main form of income, limited opportunities for education and skill development, and the outmigration of young people as well as the associated loss of social memory and cultural changes (Zucca 2006). Mountain areas are further disproportionally affected by natural hazards and climate change (Fuchs 2009, Luthe et al. 2012). Even if farming was the basis for livelihood in those communities for many centuries, it has been replaced by tourism in the 20th century (Wilson et al. 2018). Nevertheless, agriculture provides several functions that are crucial for rural communities, especially regarding tourism. These include the preservation of landscape, the provision of ecosystem services (ES), and the positive impact on social cohesion and other economic activities (van der Ploeg et al. 2000, Flury et al. 2013).

The interplay of natural factors and social drivers makes remote mountain communities complex social-ecological systems (SES) that have multiple characteristics and are challenging to understand: “they are cross- or multiscale, multidisciplinary, dynamic ..., subject to behavioral uncertainty, involve nonlinear relationships and hence thresholds or tipping points, and have emergent and embedded properties” (Dorward 2014). Here, the feedback between social and ecological patterns and processes defines social-ecological systems and vice versa, as bridging natural and social sciences has led to the development of social-ecological system approaches (Plummer and Armitage 2007 and references therein). It is challenging to elaborate hybrid and pluralistic frameworks that integrate social and ecological science aspirations to examine and evaluate the resilience of such SES (Miller et al. 2010). As an example, the social science-oriented sustainable rural livelihood (SRL) framework strives for a holistic approach to investigating less-favored communities and the complexities of poverty (Morse and McNamara 2013). It combines participatory, bottom-up approaches with recognition of the impact of macro-level governance, policies, and institutions (Small 2007). Within this framework, a livelihood can be considered sustainable, if it can cope with and recover from stresses, shocks, and seasonality and maintain or enhance its capabilities and assets both now and in the future (Carney 1998). However, the SRL framework has been criticized for several weaknesses, including a lack of emphasis on ecological elements (Dorward 2014) and a fuzzy integration of concepts like “sustainability” and “resilience” (Small 2007). Others criticize the economic perspective within the SRL approach (Acre 2003, De Haan 2012). Originally, the SRL served to shed light on the complexity of poverty and was mainly applied in the Global South. We are convinced, however, that while addressing the mentioned criticism it is a valuable framework for examining the complexities of remote mountain communities in the Global North in comparatively less globalized areas. Drawing on a field study conducted in two remote villages of the Ötz Valley in the Austrian Alps, we aim to provide insights into the interplay of tourism and farming within the SES and the provision of ecosystem services (ES). Finally, we demonstrate how this interplay affects the social-ecological resilience of remote mountain communities. For this purpose, we introduce a novel conceptual framework based on the SRL framework by integrating the concepts of community resilience and ES. Relying on a normative understanding of resilience that designates resilience as a desirable state, we aim to integrate into this novel conceptual framework positivist (social-ecological) and constructivist (social) resilience approaches (see Wilson 2018). Based on this novel framework, we reveal characteristics that contribute to the resilience of the communities at the case study sites, especially examining tourism and farming activities, and highlight the local provision of ES.

Conceptual framework

The SRL framework organizes the factors that limit or enhance livelihood opportunities and reveals their complex interdependencies. Here, sustainable livelihoods are achieved through access to a range of livelihood resources (capitals) that are combined in the pursuit of various livelihood strategies, e.g., agricultural intensification or marginalization. Consequently, the livelihood strategies lead to different outcomes that feedback on the resources. In homogeneous communities, livelihoods are diverse and dynamic to survive and improve the standards of living (Ellis 1998). The livelihood strategies are “negotiated results of interactions between individuals and households and the world around them” (Small 2007:35). The SRL framework considers multiple available capitals that are faced with the vulnerability context including trends, shocks, and seasonality. Originally, Scoones (1998) distinguished five different capitals: human, natural, financial, physical, and social. The SRL has been widely applied in development projects in the Global South (see Farrington et al. 1999, New Zealand Nature Institute 2006, Scoones 2015), as well as in scientific investigations (Daskon and Binns 2010, Jacobs and Makaudze 2012, Tang et al. 2013). Dorward (2014), however, criticized the lack of emphasis on ecological elements and other socioeconomic issues such as markets, institutions, and politics. Others fault the economic perspective within the SRL approach and consider social and other capitals only with regard to how to mobilize economic capital (Acre 2003, De Haan 2012). Scoones (2009) admitted to missing theoretical ground in the SRL framework, resulting in a fuzzy integration of concepts like “sustainability” and “resilience” (Small 2007). Additionally, the term sustainability today seems to have been superseded by the resilience thinking approach as the essential concept for rural development (Freshwater 2015) because it captures dynamic aspects of a system better than the outcome-focused concept of sustainability (Park et al. 2013). We further rely on the resilience concept, deriving from mathematical sciences to describe dynamic systems, elaborated by ecologists (Davidson 2010), which has also become popular among social scientists (Adger 2000, Magis 2010, Wilson 2012a, Maclean et al. 2014). The broadly accepted definition of resilience “is the capacity of a system to absorb disturbance and reorganize while undergoing change so as to still retain essentially the same function, structure, identity, and feedbacks” (Walker et al. 2004).

MATERIALS AND METHODS

Toward a novel framework for an interdisciplinary investigation

To enable evaluation of an SES, we integrated the social resilience concept of community resilience with ecological aspects within the SRL. Social-ecological resilience explicitly includes adaptability and transformability, implying that a system does not necessarily have one or more equilibrium states. Instead, it adapts and changes continuously (Folke et al. 2010, Davoudi et al. 2012). Also, trends, shocks, and seasonality, which might appear as fast-onset natural disturbances (e.g., weather-related and geological disasters) or as slow-onset anthropogenic disturbances (e.g., human-environmental mismanagement, socio-political disturbances, economic disturbances, or disturbances linked to globalization processes) are considered in the concept of social-ecological resilience (Wilson 2012a).

Regarding the conceptualization of social-ecological resilience on a community scale, we refer mainly to Wilson (2012a, b). The concept of community resilience builds on two previously existing concepts: capital by the French sociologist Bourdieu (2016) and the sustainable development concept (Baker 2007). Sustainable development is based on the three pillars of social, environmental, and economic issues, whereas capital refers to “accumulated labour in its materialized form or its ‘incorporated’, embodied form” (Bourdieu 1986:241). The three forms of capital, namely social, economic, and cultural capital, have been supplemented with political and environmental capital (Bourdieu 1986). Without claiming to be holistic, this set of capitals encompasses a broad range of factors, influencing community resilience. However, other authors follow other capital constellations (Emery and Flora 2006, Magis 2010, Wilson 2012b). In our understanding, economic capital refers to the financial resources of the community and its households as well as the existing built infrastructure (Wilson 2010) and the embeddedness of the economic activities into the global capitalist market (Kelly et al. 2015). Social capital “include[s] levels of interaction between community members such as trust, relationships, conflict resolution processes, engagement of young and old people, learning and communication pathways, cooperation, strength of networks, bonding and bridging capitals as well as community ‘cohesiveness’” (Kelly et al. 2015:13). Furthermore, cultural capital reflects rites, traditions, language, taboos, norms, and convention; it represents “the way people ‘know the world’ and how they act within it” (Emery and Flora 2006:21). Also, the socio-cultural identity of community members, shaped by the self-conception and self-perception as part of social groups that have their own distinct culture (Warren et al. 2016), is reflected in the cultural capital. Furthermore, political capital refers to the political context, such as governance structures, leadership, power, institutional rigidity, transparency of decision making, political participation, the role of media, and corruption. Finally, natural capital covers aspects such as climate, topography, land cover, biodiversity, and natural beauty (Emery and Flora 2006). To demonstrate resilience at the community level it is crucial to understand the complex interplay of economic, social, cultural, political, and natural capitals (Emery and Flora 2006, Kelly et al. 2015). Building on this, communities are resilient when the five capitals are well developed (Kelly et al. 2015). However, one or more weakly developed capitals raise the vulnerability of the community, which is understood here as the antithesis of resilience (Wilson 2012a). Cumming et al. (2005:978) further argue that “if system identity is maintained over the time horizon of interest under specified conditions and perturbations, we can term the system resilient” (see also Carpenter et al. 2001). Thus, an SES is resilient when the single factors (capitals, livelihood strategies, livelihood outcomes, ES) remain relatively stable so that the SES can maintain the same identity shaped by the five capitals. However, drawing the line between an identity remaining stable and changing identities can be fuzzy and is based on a subjective interpretation (Walker et al. 2004).

In addition to the combination of the SRL and the concept of community resilience, the natural and ecological aspects were given a greater role in the framework. As suggested by Costanza et al. (2014), all capitals were embedded in the natural capital because it provides the environment in which the other capitals sit. Furthermore, we also integrated the ES concept (de Groot et al. 2002, Millennium Ecosystem Assessment 2005). Here, we follow the differentiation between supply, demand, and flow as described by Burkhard and Maes (2017) and Villamagna et al. (2013) and we distinguish between (1) the capacity of ecosystems to provide ES (ES provision or supply), (2) the demand for ES (ES demand), and (3) their actual use (ES flow). This is a special prerequisite for evaluating the resilience of SES by considering each chain link in the ES delivery process within the SES.

The newly developed resilient livelihood framework (see Fig. 1) integrates the SRL framework with the concepts of community resilience and ES to better understand the interlinkages of farming and tourism as well as their impacts on the SES. It conceptually illustrates the state of an SES and demonstrates its influencing dynamics. Within the framework, the social, economic, political, cultural, and natural capitals characterize stocks of assets. The external and internal drivers represent everything influencing these capitals. External drivers forwarded by agents represent broader conditions on the global and regional scale and shape the external context for vulnerabilities and resilience. Economic and political drivers, including governance and institutions, encompass markets (Dorward et al. 2003). A cultural driver is the current approach of UNESCO to protect tangible and intangible cultural heritage (Vecco 2010); the EU LEADER program fosters social capital building (Rivera et al. 2018) and is a social driver. Political drivers, or transformative structures and processes, as originally named in the SRL framework, represent various levels of government as well as laws, policies, incentives, and institutions (Scoones 1998). Natural drivers are an integral part of human-environment interactions that have a direct impact on society or are perceived as such by society (Forbes et al. 2009), such as climate change or ongoing biodiversity loss. The agent-based internal drivers are dynamic capabilities influenced by external drivers and rely on the capitals to react. They shape the internal context for resilience and vulnerabilities and thus facilitate or hinder community capital building (Fischer and McKee 2017). Through the interaction with the economic, social, cultural, and political capital, the natural capital can provide ES (potential ES supply; Costanza et al. 2014). Influenced by the status of the capitals and by internal and external drivers, residents decide on various livelihood strategies, i.e., they decide how to use their capitals to generate specific ES flow and income. These livelihood strategies are expressed as desires for certain ES (ES demand) that lead to specific actions or activities to enhance the supply or to “harvest” the desired ES. The resulting livelihood outcome includes ES flow or income. ES flows and incomes in turn influence the capital; this can trigger changes in the livelihood strategy and livelihood outcomes in a subsequent period.

Study sites

This framework served to empirically investigate the case study sites of two remote mountain communities, namely Obergurgl and Vent (Fig. 2). Obergurgl and Vent are two Alpine villages in the municipality of Sölden in the Upper Ötz Valley (Tyrol, Austria) with a population of 509 and 138, respectively (Statistik Austria 2017). At the end of the 18th century, the economy in both villages was based on animal husbandry and residents were mainly subsistence farmers. However, the population decreased as food shortages forced migration. A modernization process, brought about by tourism development in the Alps, initiated economic recovery, especially in the village of Obergurgl (Meleghy et al. 1985). Although Obergurgl has developed as a center for mass winter tourism in the Alps, the neighboring village of Vent positioned itself as a classified mountaineering village for “soft tourism” that strives to reduce the destructive character of mass tourism (Fischer 2014). Both communities have faced substantial socioeconomic change over the past decades, such as the decline in farming to a recent dependency on tourism as the main source of livelihood, which makes them suitable case studies for an investigation of their social-ecological resilience.

Practical implementation and data collection methods

We applied various methods of qualitative and quantitative social research as well as ecological approaches. Finally, all the results are condensed in an evaluation of the social-ecological resilience of the selected communities.

Qualitative data collection

To draw an image of economic, social, cultural, political, and natural capital as well as its drivers in each village, semi-structured expert interviews were conducted. Such interviews are open structured to gain a broad range of information and knowledge as well as to acquire access to the expert’s tacit knowledge. For our purposes, an expert is a person with specific knowledge in a certain field of activity and who functions as a representative of a group (Bogner et al. 2014). Between October 2017 and June 2018 we conducted 20 interviews (Table 1) with local actors from both villages as well as with regional stakeholders. Each interview lasted 30–100 minutes. The local interviewees were selected with a view to gender, age group, immigrant status, and role in the community. Issues like farming, tourism, village development, social cohesion, and local disturbances were addressed during the interviews, but also additional aspects were mentioned by the interviewees. A verbatim transcript of the expert interviews served to transform spoken material into written form. For data evaluation, we applied qualitative content analysis (Mayring 2007). This systematic, rule-guided, and theoretically grounded step-by-step approach to qualitative text analysis is based on the inductive development of categories close to the given text material and the application of deductive verification of those categories regarding the research questions and theory. For development of the categories, the software ATLAS.ti was used to organize and code the text material (Konopásek 2011). Finally, 52 inductively developed categories were deductively grouped into the five domains of the community resilience concept. The acquired knowledge has been enriched with additional documented analyses of development concepts and laws (Hoffmann 2018).

Quantitative data collection

The perception of the actual contribution of the local landscape to certain ES and their importance for the communities were investigated among the inhabitants. From March to August 2018, questionnaires with closed questions for self-completion (Paier 2010) were distributed personally in Vent and Obergurgl. In total, 40 persons (27% of all local inhabitants) took part in the survey in Vent, and 66 persons (13% of the inhabitants) in Obergurgl (see Gruber 2019). These results were tested with the Mann-Whitney U test in the present study. The Mann-Whitney U tests were conducted with SPSS statistics, version 26 (IBM Corporation).

Habitat mapping and settlement activities

Because many of the ES models are based on land use/land cover maps, we first mapped habitats for the case study site for several historical dates: 1860, 1950, 1970, 2000, and 2015. For each time period, historical maps and orthophotos were analyzed following a methodical approach for standardized landscape studies in small dimensions (Tasser et al. 2009). The Francisco-Josephinian Cartographical Register from 1860 marks the start of spatially explicit historical land use/cover. With it, various land use/cover types (e.g., forest, meadows, pastures, and settlements), as well as specific landscape features (e.g., rivers and rocks), were mapped. For 1950 and 1970, we used georectified aerial photographs, and for 2000 and 2015, we consulted the orthophotos. All data were mapped and referenced in a geographic information system, whereby only areas greater than four hectares were considered. To evaluate settlement activities, the habitat type “settlement area” was classified and individual buildings were evaluated. For this purpose, all buildings (e.g., houses, stables, huts) with a roof area of more than 16 m² were counted for each historical time step.

Beef production

In a first step, fodder production was calculated based on a biophysical model and the mapped area of used grassland from the five historical years (see habitat mapping above). Quantification of the potential yields was calculated via yield functions based on the length of the growing season. Yields were refined according to site parameters such as precipitation during the growing season and solar radiation (for more details, see Jäger et al. 2020). In the second step, the grassland yield was derived from the production by considering feed quality in the form of metabolic energy content (megajoules MJ ME) and yield losses (for extensively used pastures and meadows: -53%; for intensively used meadows: -43%). We estimated the potential number of bovines that can be kept based on the harvested forage energy (energy demand per bovine: 35,251.9 MJ ME/a). In the third step, we estimated the potential quantity of beef produced as the ES flow. The quantity was calculated considering herd composition, average live weight, average slaughter age, and the resulting quantity of meat (boneless) per year (see Table 2).

Land management

To evaluate the share of protected areas in the case study sites, the extent of the protected areas according to the European Environment Agency (2015) was analyzed in ArcGIS. The extent of the sealed area was estimated based on the habitat type “settlement area” and the number of individual buildings was provided by Sulzer (2018). Furthermore, the extent of the paved road network was provided by Schirpke et al. (2019). For the individual buildings, a mean extent of 600 m² of sealed soil per building was assumed, based on the visual inspection of 20 random samples from Obergurgl and Vent in the orthophotos of 2015. For the asphalted roads, a mean width of 7 m was assumed.

Water supply

We approximated naturally available water from the runoff in the main creeks “Venter Ache” in Vent and “Gurgler Ache” in Obergurgl. Gauge measurements of runoff were available for Venter Ache and Gurgler Ache from 1966 and 1976 until 31 December 2015. We calculated the total runoff for every year and estimated an average runoff for 1970 (by taking the mean for 1968–1972), for 2000 (mean 1998–2002), and for 2015 (mean 2011–2015).

Statistical methods of resilience evaluation

Based on the livelihood strategies, the livelihood outcome feeds back on the individual capitals (Fig. 1). To illustratively evaluate the resilience of the investigated SES (see Table 3), the impact of given livelihood strategies and outcomes on the capitals was assessed based on a subjective résumé of our gained knowledge. As a common simplification, a weakly developed capital weakens the resilience (see Cumming et al. 2005). A strongly developed capital is considered positive for resilience. Consequently, we considered a system to be strongly resilient if all capitals are at a relatively high level and more or less balanced (see Adger 2000) and if the prevailing livelihood strategies contribute to a further strengthening of the capital (livelihood outcome). To measure the diversity of items (i.e., capitals) and their proportional abundances (pi), the Shannon-Wiener index (H’) was used (Spellerberg and Fedor 2003):

Equation 1(1)

Here, pi is calculated by multiplying the capitals with the effects of the strategies and standardizing them in comparison to a “best case situation,” i.e., a highly positive capital multiplied with a highly positive strategy (0.9 × 0.9). More precisely, for a final evaluation of the social-ecological resilience of both villages, we assigned mean class values from 0.1 to 0.9 to the status of the capitals and the influence of the livelihood strategies on the capitals. Using this modification of the calculation method for pi we ensure that the index takes the value 1 when all capitals are equally at a high level and are equally further increased by the livelihood strategies. The H’ index (min = 0) is lower when the capitals are less equal and becomes lower when the livelihood strategies (1) lower all capitals or/and (2) lead to less balanced capitals. Therefore, also trade-offs between the livelihood outcomes are indicated.

RESULTS OF APPLICATION OF THE FRAMEWORK

With application of our resilient livelihood framework (RLF), we investigated the social-ecological systems of Vent and Obergurgl. The results are presented below according to the novel framework (see Fig. 1).

External and internal drivers influencing the capital

During the expert interviews, the local and regional stakeholders mentioned only a few external drivers within the resilience-vulnerability context that influence the internal drivers as well as capitals; they presented themselves as detached from the phenomenon of external trends, shocks, and seasonality. Therefore, economic, social, cultural, political, and natural external drivers are presented for both villages.

Economically, neither Obergurgl nor Vent has been concerned by external drivers such as the bovine spongiform encephalopathy (BSE) crisis in the 1990s, the global financial crisis in 2008, or the drop in the European milk price in 2015. Also, stakeholders did not mention any effect of Brexit on the local economy, even though British tourists make up a large share of Obergurgl’s clientele. Farmers in both villages have multiple incomes, so they see themselves as negligibly affected by the EU’s Common Agricultural Policy. However, the industrialization of gastronomy in the 1970s reduced the traditional exchange relations between farms and hotels because of regulations (e.g., hygiene), low production volumes, and high production costs.

The social cohesion of both local communities is affected by immigration; however, it affects Obergurgl more than Vent. Most of the seasonal workers in both villages come from countries with diverse cultural backgrounds, e.g., southeastern Europe, and bring their values. Because foreign seasonal workers constitute more than half of the residents during the season, they affect the local communities. Additionally, some years ago foreign investors took over family-owned hotels in Obergurgl, where succession within the family was not given. Also, these stakeholders bring new attitudes and values to their hotels and the local community. Furthermore, it is difficult for immigrants (as well as Austrians from other parts of Austria) to become integrated in the community. This has negatively affected social cohesion in Obergurgl and Vent. Furthermore, cultural capital is threatened by the rising mobility that allows residents to join clubs and organizations outside the village, for example. Consequently, local clubs and organizations suffer a lack of members and therefore risk losing traditional knowledge and capacities. Further external drivers include rules made by the Tyrolean state government, for example, those concerning awarding water concessions and strict rules on the amount of residual water in each tributary (Amt der Tiroler Landesregierung 2017). Moreover, with the scope of implementation of the Austrian Spatial Development Concept (ÖREK), Tyrol has developed regional spatial programs and strategies that affect, inter alia, the development of tourist facilities, and the preservation of agricultural and green areas (Gruber et al. 2018). In Obergurgl and Vent, a protected area (“Ruhegebiet Ötztaler Alpen” since 1981, additionally classified as a Natura 2000 site in 1995 and as a nature park in 2006) exists adjacent to a ski resort. The Tyrolean Nature Conservation Act explicitly prohibits the construction of roads for public use and lifts (§11 TNSchG 2005), and the additional classification as a Natura 2000 site according to the Habitats Directive (Art 6.2) and the Birds Directive (Art 4.4.) specifically calls for refraining from any actions that have any, direct or indirect, negative impact on the ecological structure and functions of the protected habitats. Hence, touristic use of protected areas is limited to activities that require only low infrastructure, such as hiking, ski touring, or snowshoe hiking.

The internal drivers influencing the economic, social, cultural, political, and natural capital strongly affect the capitals and are thus related to them. In order to not be repetitive, they are presented in detail for both villages in Appendix 1.

Capitals of the social-ecological system

Here we extrapolate the influence of the drivers on the respective forms of capital and thereby evaluate the strength of the capital. Obergurgl focuses primarily on winter tourism, which demands financial capital for investments in infrastructure. Farming has lost its economic importance and is not integrated in tourism activities. However, as one regional expert stated “Those farmers, who were lucky to inherit properties in favorable locations have high monthly incomes, especially in Obergurgl,” which results in a tendency for the socio-cultural identity to shift from being farmers to being landowners. Obergurgl has strong economic capital (see Table 3), because tourism brings multiple and high incomes and has hardly been affected by external drivers. The economy in Vent is also largely unaffected by external drivers, but in contrast to Obergurgl the financial investments in tourism infrastructure are small, as the following statement highlights: “Higher up we have a very long drag lift and it will be an important step for the coming years to replace it with a second-hand chairlift“ (local expert). Vent has a balanced tourist season, which creates relatively stable use of infrastructure and the need for labor. Farming has also lost its economic importance. However, it is integrated in tourism activities. In sum, Vent’s economic capital is evaluated as being only moderate (see Table 3). Considering the social domain, Obergurgl suffers from seasonal outmigration of residents that weakens social cohesion and has an impact on daily village life, which is underlined by the following statement made by a local expert: “I think that people in long phases of prosperity, as in Obergurgl, tend to this egotistic, greedy behavior.” In Vent, it is the population size that endangers social cohesion, because it influences the maintenance of infrastructure and clubs and organizations. However, cohesion among the new generation of hotel owners is strong, as the following comment underlines: “I recognize a positive attitude among the young people and most of them are motivated to work together“ (local expert). Therefore, the social capital in Vent and Obergurgl is assessed to be only moderately developed (see Table 3). With reference to cultural aspects, in Obergurgl the inhabitants’ socio-cultural identity risks taking on a service provider habitus that is becoming increasingly alienated from farming. Cultural festivities are important for the residents and are not marketed for tourism purposes. Vent demonstrates lively cultural traditions from sheep breeding and the transhumance of sheep from South Tyrol that play a major role here in the socio-cultural farming identity, as pointed out by a regional expert: “The close connection to the South Tyrolean valleys, especially to the Schnals Valley, is part of the identity in Vent.” Therefore, the cultural capital is assessed as being stronger in Vent than in Obergurgl (see Table 3). Politically, individual residents of Obergurgl belonging to one extended family clan are well-integrated in and well-connected to several state institutions and hold political power. Also, Obergurgl is well represented at the municipal level, as is Vent. However, Vent is less well represented at the regional level. This suggests that Obergurgl’s political capital is stronger than is Vent’s (see Table 3). Considering environmental issues, in Obergurgl economic goals have so far enjoyed higher priority than have ecological goals, and expansion of the human living and economic space is given priority. Vent strives for more sustainable development in line with environmental issues. Therefore, Vent’s natural capital is stronger than is that of Obergurgl (see Table 3).

Although the questionnaire survey revealed similarities among residents of Obergurgl and Vent in the perceived supply of ES (Fig. 3), significant differences in the assessment between the two villages were demonstrated for the ES “Protection from hazards” (p = 0.045), “Providing habitats for pollinators” (p = 0.009), and “Maintaining biodiversity” (p = 0.023); the perceived ES supply in Vent is higher for each service, which underlines the stronger natural capital in Vent.

Livelihood strategies (human activity) and outcome

Relying on the external and internal drivers and the resulting shapes of capital, the populations of Obergurgl and Vent construct their livelihood strategies by considering certain strengths and weaknesses of their community. We investigated four of the main livelihood strategies (see Fig. 1) in Vent and Obergurgl: agricultural strategy, touristic strategy, land management strategy, water use strategy (Table 4).

Agricultural strategy and outcome

Agricultural activities have declined in both Obergurgl and Vent, because they have lost economic significance in comparison to tourism activities. This can be seen in the number of farms that dropped from full-time to part-time operation: in the whole municipality of Sölden, 106 full-time and 86 part-time farms were counted in 1970, but only 14 full-time and 157 part-time farms were counted in 2010 (Tasser et al. 2013). Obergurgl had 20 farms in 1990, which decreased to 14 in 2016. In contrast, the number of farms in Vent increased from seven in 1990 to eight in 2016 (Data for 1990: Statistics Austria; Agricultural Structural Census; Data for 2016: Federal Ministry for Agriculture, Regions, and Tourism; Integrated Administration and Control System). Farmers have enmeshed agriculture with tourism through different forms of integration, e.g., the provision of accommodation, off-farm employment in tourism, compensation payments for touristic use of the land, or the provision of high-quality food products for tourism. Currently, especially in Vent, the produce of many farms is sold directly, either to consumers, restaurants, or within their tourism facilities. These direct marketing strategies often depend on personal contacts with customers, e.g., in the Ötz Valley, and with professional providers, e.g., local restaurants (for details, see Stotten 2020a). However, the results of the survey (Fig. 3) show that the provision of food is considered to be of little importance to the residents of both Obergurgl and Vent. Although the consumption of agricultural products increased with the growth of the local population and of tourism (as seen for the example of beef, Table 5), no strategies were developed in either of the two villages to promote agriculture as a producer of local food products. Thus, meat production declined from 1860 to 2015 (Table 5).

In the 19th century, overproduction of meat was achieved in both villages (Fig. 4). Nevertheless, the applied agricultural strategy resulted in an outcome, where the supply of meat declined significantly: in Vent, the amount of meat needed to cover consumption at the local tourism structures, e.g., the mountain huts, can still be produced today, and farmers maintaining mountain huts often offer their produce in the menu there. In contrast, Obergurgl now imports 96.5% of its beef. This shows a lack of strategies to improve meat production in accordance with rising consumption, especially in Obergurgl. Also, local catering services do not encourage local meat production. The region showed a net export of beef (mostly calves) until the 19th century (Leiter 2016), but Obergurgl in particular and Vent to a lesser extent have become net importers of beef. Nevertheless, the additional income generated by tourism enables the inhabitants to continue costly and time-consuming agricultural activities, such as mowing steep slopes to maintain farming. Thus, the prevalent socio-cultural farming identity, mainly in Obergurgl, is detached from producing food, but instead is related to working the land and being a landowner. In contrast, the socio-cultural identity in Vent still relies on the production of food.

Touristic strategy and outcome

Tourism activities in Obergurgl and Vent have always been dominated by a few powerful actors (Stotten 2020b). Despite the touristic use of the local landscape, the inhabitants have long recognized the relevance of high aesthetic and recreation values to attract visitors and tourists. To make the areas of highest values accessible they expanded infrastructure, but the two villages set different priorities. In Obergurgl, a stronger focus is set on winter tourism. Local shareholders of the lift companies increased lift facilities to 25 in 2015. The density of hiking trails and roads increased from 0.15 km/km² in 1860 to 1.55 km/km² in 2015 (Schirpke et al. 2019). The lift shareholders are also the owners of large upper-class hotels, whose goal is to increase ski resort capacity in winter to ensure the occupancy of their hotel beds. In contrast, there are also several small- and middle-sized bed and breakfast operations, whose owners have less power within the community. Efforts to strengthen the summer season are informally discussed, but no distinctive strategy is apparent for Obergurgl. Vent, however, positioned itself as a “mountaineering village” (ÖAV 2018) for “soft tourism” with a smaller number of guest beds and a more pronounced focus on summer tourism. The skiing infrastructure has not been expanded for a long time, and only a drag lift was recently replaced with a second-hand chairlift. In total, only four lifts existed in 2015. The inhabitants of Vent invested mainly in enhancement of the road and expansion of the hiking trail network (increased from 0.14 km/km² in 1860 to 0.81 km/km² in 2015 (Schirpke et al. 2019). Yet, hiking trail density in Vent is still significantly lower than in Obergurgl. Also, the ownership structure differs from that in Obergurgl. In Vent, the stakeholders of the lift company are farmers and thus also landowners. Furthermore, Vent has very few large hotels, and local tourism is based more on lower- and middle-class small- and medium-sized accommodation structures. Additionally, farm produce is often directly incorporated in accommodation services, which creates local food supply chains. The focus away from economic investments corresponds to Vent’s soft tourism strategy.

As an outcome of the extreme focus on tourism in Obergurgl and Vent, both case study sites are economically dominated by tourism income. Detailed numbers for Obergurgl and Vent are not available, but the turnover of the five main tourism service providers (accommodation, gastronomy, ski lifts, ski schools, and sports article retailers) throughout the entire Ötz Valley (consisting of the six municipalities Sölden, Längenfeld, Umhausen, Ötz, Sautens, and Haiming) was nearly € 500 million in 2015. From 2005 to 2010, the valley showed 36.1% growth in turnover (inflation-adjusted; Haselwanter et al. 2019), which underlines the valley’s general focus on the tourism industry. However, this monostructural orientation of its economy also makes Vent and Obergurgl vulnerable. The focus on the winter season in Obergurgl results in seasonal outmigration to second homes that negatively influences social cohesion. Moreover, this phenomenon fosters possible future weakening of clubs and organizations and social services, which negatively affects social capital. The loss of social capital affects further cultural issues, e.g., declines in the importance of the church or traditional festivities. All this reinforces the shift in the socio-cultural identity from a former farming community to a modern service-oriented community. In contrast to Obergurgl, the tourism strategy in Vent aligns with environmental issues (natural capital) and is less capital-intensive. Furthermore, the balance between the summer and the winter season permits active village life for approximately 9 to 10 months a year, which contributes positively to social cohesion. Here, the small number of residents is the limiting factor in building social capital. Additionally, the local food supply chains in Vent support the local economic circle. Expansion of touristic infrastructure in Vent and Obergurgl has affected the aesthetic and recreation value, with accessibility especially increasing at higher elevations, such as alpine pastures that are characterized by high aesthetic values. The recreation value shows a steady increase until 2015 (Table 4). With regard to the aesthetic value, however, the opposite of the intended effect was reached beginning in the 1970s; the increase in settlement area and the abandonment of pastures (natural capital) negatively affected the aesthetic value.

Land management strategy and outcome

Obergurgl has largely expanded its settlement area, road infrastructure, and the number of individual buildings (“rural sprawl”; Andexlinger 2015). Under Austrian law, the municipality of Sölden is the central planning authority and thus responsible for local spatial planning. Land development, however, has also been managed by designating protected areas. In 1977, a UNESCO biosphere reserve was designated in Obergurgl. However, because this reserve was established under pre-Seville conditions, the requirements were relatively low and skiing infrastructure was able to be established in the protected area. Faced with the impeding re-constitution of the UNESCO biosphere reserve (Seville Strategy of 2005), Obergurgl changed its strategy in 2014 and no longer supported the designation of larger areas with stricter conditions, but instead terminated the UNESCO biosphere reserve. The extent of the Ruhegebiet Ötztaler Alpen, however, has not changed since its establishment in 1981. Instead, stricter requirements have been added with the establishment of the Natura 2000 site in 1995. Although the inhabitants of Vent also expanded the settlement area, road infrastructure, and individual buildings, the built-up/sealed area remained smaller than in Obergurgl (Table 4). Vent also played an active role in conserving a traditional landscape by refusing to expand a ski resort (Hochjochferner) and connect it to a ski resort in South Tyrol (Schnalstaler Gletscher) in the 1990s (Scharr 2013). Since 1981, a large portion of the landscape has been continuously protected as a nature conservation area (it has also been a Natura 2000 site since 1995 and a Nature Park since 2006).

As tourism strategy outcomes, the built-up/sealed area has increased in both Obergurgl and Vent (in Obergurgl to a greater degree). The agricultural area (used and potential) has thereby been reduced, and habitats have been lost and fragmented. Moreover, the inhabitants of Obergurgl decreased the share of the protected landscape to 83.2% of the total area (in Vent, it is still 97.2% of the total area, see Table 4) and ensured the continuation or new construction of skiing infrastructure (including roads, hotels, and lifts). Thus, they favored economic aspects at the expense of nature conservation and agricultural production.

Water use strategy and outcome

Considering the numbers of inhabitants and overnight stays, facilities for tourist accommodation and gastronomy have since the 1970s consumed more water than have the households (Table 6). Additionally, artificial snowmaking consumes huge amounts of water, especially in Obergurgl (Table 6). In Vent, water for artificial snowmaking is taken directly from one creek during the snowmaking season between November and March. The significantly greater water demand for snowmaking purposes in Obergurgl requires more infrastructure and regulations, e.g., in the form of water concessions granted by the state government. To cope with the water use regulations, lift operators in Obergurgl built artificial reservoirs that can be filled year-round and used for snowmaking in the winter months. Since 2015, two big reservoirs are operated in Obergurgl: the Wurmkogel reservoir has a usable storage volume of 82,800 m³ and the Schönwieshütte reservoir 49,500 m³. In 2021, the Festkogel reservoir with a usable storage volume of 39,900 m³ will go into operation. The volume of water naturally available in Obergurgl (1970: N.A., 2000: 134,170,646 m³, and 2015: 111,361,824 m³) and in Vent (1970: 97,452,288 m³, 2000: 159,776,064 m³, and 2015: 142,218,029 m³) is significantly larger than water demand; the absence of water use strategies is legitimate and no negative outcomes can be noted (Table 6).

Evaluation of resilience

Based on the livelihood strategies, the livelihood outcome feeds back on the individual capitals (Fig. 1). To illustratively evaluate the resilience of the investigated SES, the impact of given livelihood strategies and outcomes on the capitals was assessed. The status of the capitals in Obergurgl and Vent is quantified according to the evaluation of capitals (Table 3) and the influence of the four strategies is evaluated as follows:

Farming in Obergurgl (Table 3, agricultural strategy) significantly declined in economic importance; the traditional function of farming and the production of food also disappeared. The high demand for beef in Obergurgl, for example, is not covered by the local production possibilities. Meat needs to be imported, making the village more sensitive to external factors and decreasing its resilience. This local consumption of meat in tourism infrastructures could support local agriculture by providing a demand for local meat. In any case, farm household income relies on additional sources, such as land ownership and/or accommodation services. This additional income creates leeway for the farms so that adaptation strategies become possible and financially affordable. In this way, farms can respond to any disturbance and, more importantly, proactively strategize to keep the farms resilient (for details, see Stotten, 2020a). In Vent, farming (Table 3, agricultural strategy) also depends on public transfer and local payments for the touristic use of land. Moreover, the provision of accommodation services generates an important share of farm income. However, the synergies between farming and tourism are more intense than in Obergurgl as the touristic value of the cultural landscape seems to be more visible for summer tourism, and local food chains are intertwined with tourism. The farming identity is still strong in Vent (for details, see Stotten, 2020b); farming plays an important role in the prevailing type of soft tourism, even if Vent is far from being a farming village.

Although the touristic strategies (Table 3, touristic strategy) bring considerable income (especially in Obergurgl, Table 5), the touristic activities depend on the external labor force in both villages, a phenomenon that is more pronounced in Obergurgl than in Vent. The municipality of Sölden records a massive turnover generated by tourism, the high share of external labor leads to capital flow from the community to other regions or countries. Obergurgl’s economic goals restrain the drive for natural capital. Furthermore, the wealth that many individuals in Obergurgl acquire from touristic incomes enables them to have a second home, which in effect weakens social cohesion and thus social and cultural capitals. However, the strengthening of economic capital, mainly by the tourism strategy, facilitates a gain in political power. Tourism further enabled the increase in aesthetic values at higher elevations because of expansion of the hiking trails and thus accessibility. However, the aesthetic and recreational outcomes overall decreased with time because of greater urban sprawl, abandonment of agricultural areas, and the loss of a biosphere reserve, thereby negatively influencing natural capital. In contrast, the moderate strengthening of economic capital by the tourism strategy in Vent leads to overall stronger resilience. Social cohesion functions better because residents are not wealthy enough to maintain a second home; the conflicting relationship between landowners (usually farmers) and the lift company is also far less pronounced than in Obergurgl. All of this also contributes to shared values among the villagers, which strengthens the cultural capital. However, the small number of residents limits the resilience of social and cultural capital.

A resilient SES has to maintain land for valuable ecosystem service provision (habitat, food, fodder, and recreation), but soil sealing increased in both Obergurgl and Vent (Table 3, land management strategy). The former rural character of Obergurgl has been obliterated, and potential farmland, as well as habitats for wild plants and animals, has decreased. The valley floor in Obergurgl is already densely built up, and consequently little potential remains for the construction of new tourist facilities. Therefore, the resilience of natural capital has been further lowered. In Vent, the sealed area is smaller and the share of protected areas is higher. Overall, human interference with the landscape and nature is kept to a minimum and in terms of the natural capital, resilience increases more than in Obergurgl. Regarding water use (Table 3, water use strategy), both villages are resilient. The high water demand for artificial snowmaking, however, makes the building of artificial reservoirs necessary in Obergurgl and changes the hydrological cycle from its natural condition, which weakens the resilience of the natural capital.

In summary, the H’ indices (Table 3) in Vent are very balanced between 0.57 and 0.64 and are significantly higher than those in Obergurgl, especially in the case of agriculture and land management (2-tailed One-Sample Test: p = 0.001 based on 1000 bootstrap samples). In summary, the H’ indices (Table 3) in Vent are very balanced between 0.57 and 0.64 and are significantly higher than those in Obergurgl, especially in the case of agriculture and land management. Thus, a higher overall social-ecological resilience is evident in Vent. At the same time, this result also supports the fact that there are fewer trade-offs between the individual livelihood strategies in Vent.

DISCUSSION

Social-ecological resilience of Obergurgl and Vent

Evaluation of the social-ecological resilience as well as the differences between both communities has been illustrated above, where we revealed and described economic, social, cultural, political, and natural drivers and capitals. The evolution of resilience capitals differs greatly between Obergurgl and Vent and highlights the fact that the resilience of both communities is jeopardized more by several slow-onset disturbances, such as outmigration and social change, than by fast-onset disturbances such as natural hazards or global shocks. Our evaluation of the resilience finds Vent to be more resilient than Obergurgl, but possibly also more than other Alpine, tourism-based communities. Here, Vent has positioned itself as a winter and summer destination based on small-scale structures, which might be helpful in the long term when ski tourism decreases, and Vent has proved to cope better with the COVID-19 crisis in 2020 (observation by the authors in summer 2020).

In the qualitative data collection, both local communities considered themselves disconnected from macro-level (external) influences. This might be a phenomenon of lacking awareness rather than a real autonomy from externalities. Furthermore, respondents could hardly imagine any shocks because they were abstract at the time. However, the current COVID-19 crisis demonstrates that a disturbance can appear suddenly; the pandemic affected tourism in Tyrol especially hard (Bachtrögler et al. 2020). The perception of possible risks and shocks including causes, possible coping strategies, and the resulting consequences (Jurt Vicuña Muñoz 2009) are in both Obergurgl and Vent more focused on fast-onset disturbances such as avalanches, which especially for Vent have been harmful in the past. In contrast, slow-onset disturbances such as consequences of socioeconomic or climate change, are not actively addressed. Although climate change is considered a major issue jeopardizing resilience (Fuchs 2009, Luthe et al. 2012) and also Obergurgl and Vent are affected by it (see Tompkins and Adger 2004), the elevation of the two villages ensures temperatures that guarantee snow cover, either through precipitation or artificial snow. Therefore, no reactivity is needed immediately to keep the tourism industry running (see Steiger and Scott 2020). However, this missing consideration might cause problems in the long term.

Strength and weaknesses of the novel framework and its application

For application, the RLF integrates qualitative and quantitative social data as well as data from natural sciences. To address the concerns about the economic focus of the SRL framework (Acre 2003, De Haan 2012), the integrated concept of social-ecological resilience on a community scale applies the forms of capital from Bourdieu (1986). It gives crucial value to every capital and also considers interdependencies. It reflects the social embeddedness of economic action (see Granovetter 1985) as well as the cultural setting (Zelizer 2011). This improved the conceptualization of the resilience concept within the framework and contributes to its theoretical ground. However, the emphasis of individual capitals and thus their balance differs not only among different communities, but also within a community. In Obergurgl, major stakeholders strive for activities that favor economic capital, whereas in Vent, they highlight activities that respect natural capital. However, in each village there are also some inhabitants who do not support these activities.

Originally, the community resilience concept and the SRL framework considered all capitals as equal. In the novel RLF, we differentiated the natural capital from the economic, social, cultural, and political capital, thereby enhancing the consideration of ecological elements. From a human point of view, the environment is not only important in natural capital, but also contributes to human welfare through all capitals. Hence, we integrated the ES concept in the RLF. On the one hand, natural capital includes a set of critical and non-substitutable natural items satisfying basic needs (“critical natural capital”), which makes it fundamental to all other capitals. On the other hand, natural capital also supports “amenity services” that contribute but are not crucial to human well-being and could largely be substituted by manufactured services (Ekins et al. 2003). In both cases, natural capital is strongly influenced by its social valorization, e.g., recognition of climate change needed to launch measures, and is linked to and co-dependent with the other capitals (Potschin and Haines-Young 2011). Only through interaction with the other capitals can the natural capital in the RLF provide ES; in combination with the various livelihood strategies, the natural capital enables specific ES flows. These livelihood strategies are, inter alia, driven by ES demands. Our case study in Obergurgl highlights, for example, the fact that based on the natural capital a higher provision of beef (ES) would be possible and could at least partly cover the high consumption, but this is not demanded by the community because they prefer to import beef products. Hence, the agricultural livelihood strategy does not integrate the provision of beef. Contrastingly, in Vent the production volume of beef meets the consumption volume. Food self-sufficiency is often a component of resilient food systems, thereby contributing to a resilient SES (Wittmann 2011). The goal should not be to produce 100% of the food locally, but rather to increase the capacity to produce food, even if the region engages in food imports and exports (FAO 2015). In contrast, the aesthetic value of the landscape is another example of ES that is important for the tourism strategy (Pechlaner et al. 2007) and is recognized by the communities of both Obergurgl and Vent. Here, livelihood strategies were developed to maintain or even enhance the flow of “Aesthetic value.” Therefore, the RLF shows the social valorization, the demand for certain ES, and the effects of the livelihood strategies arising therefrom.

Although we applied a modified Shannon-Wiener index to objectively evaluate social-ecological resilience based on capitals and livelihood strategies, the decision on how to integrate and rate the data rested with the researchers. Therefore, it is still partly subjective. Moreover, the four discussed livelihood strategies that determine the outcome were chosen by the authors on the basis of the issues that appeared to be important from the data and from the authors’ expertise. The integration of other or further livelihood strategies could change the overall evaluation of social-ecological resilience. This subjectivity has to be considered. However, the application of any framework demands a subjective decision (Kalu 2019). Finally, to evaluate the social-ecological resilience, we broke down the resilience of the two case study sites to a densified numerical value in order to bring all considered aspects into a final résumé. Certainly, not all information can be considered in this step. However, it serves to illustrate a densified outcome. We think the densified outcome and the background should serve as an information basis for further decisions regarding the livelihood strategies of both communities. For example, the intertwined complexities of the SES in Obergurgl and Vent result in similar consequences regarding the moderately social capital. There are, however, various underlying causes. In Obergurgl, wealth (strong economic capital) enables seasonal outmigration of the population, which weakens social capital. In Vent, the small number of residents endangers the social capital. So far, however, the economic activity in Vent is more strongly embedded in social (e.g., family networks) and cultural (e.g., farming traditions) aspects (see Granovetter 1985, Zelizer 2011) than in Obergurgl. This further explains the strong socio-cultural farming identity in Vent (see Stotten 2020b). Overall, Vent shows a stronger social-ecological resilience regarding the four investigated strategies than does Obergurgl.

The RLF is based on the elaborated framework integrating the concepts of community resilience and ES and provides a richly textured frame for understanding the subtleties of the resilience of an SES. The novel framework has the potential to reveal the social valorization and the social demand of a single ES. Here, we agree with Adger (2000) that social resilience, including economic, social, cultural, and political capital, depends on the ecological system and thus on the natural capital. Even if the original SRL framework was developed with a view to understanding the complexities of poverty in the Global South, the novel RLF enriched the framework and made it suitable for application in remote mountain areas. With emphasis on the natural capital and integration of the ES concept, we reveal complex interdependencies of social and ecological resilience.

CONCLUSIONS

By applying the RLF to case study sites in the Austrian Alps with combined sociological and ecological research approaches, we demonstrate how a detailed image can be drawn of the complex interplays of several drivers and capitals shaping the SES. Our case study area reveals that the complexities of an SES make it impossible to grasp all aspects in a schematization. Thus, the RLF strives to be holistic without claiming to be so. In the case studies, Vent showed stronger social-ecological resilience regarding the four investigated strategies than did Obergurgl. However, these results are subjective because of the methodological procedures and do not cover the full background information. Hence, to support management decisions and individual livelihood decisions within the community, we recommend transferring the full information about all external and internal drivers, the capitals, the livelihood strategies, and their resulting outcome, rather than only the densified outcome. The RLF might be a useful tool for investigation in other communities in the Alps because they have mostly experienced a substantial socioeconomic change in the last century and are furthermore affected by the impacts of climate change. The RLF provides a richly textured framework for understanding the subtleties of social, economic, and ecological challenges influencing the resilience and vulnerability of SES. We consider the RLF especially applicable in areas that are less globalized, more closely embedded in their physical environment, and thus strongly related to their natural capital. Moreover, the RLF is seen to also be able to capture gradual slow-onset disturbances that jeopardize resilience in many communities more than fast-onset disturbances.

RESPONSES TO THIS ARTICLE

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ACKNOWLEDGMENTS

The authors wish to thank all our respondents in the Ötztal valley for their time and effort in participating in our research. They also wish to acknowledge very useful and constructive comments by the reviewers of this article. Further, the authors would like to thank Ika Darnhofer, Magnar Forbord, Johannes Rüdisser, Markus Schermer, and Geoff Wilson for valuable comments on earlier drafts of this paper. The Austrian Academy of Sciences (ÖAW) within the Earth System Science call project “RESilience through synergies between agricULTure and tourism: a comparison of two contrasting trajectories in the Tyrolean Alps” financially supported this work.

DATA AVAILABILITY

The data that support the findings of this study are available on request from the corresponding author. None of the data are publicly available because of their containing information that could compromise the privacy of research participants.

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Correspondent author:
Rike Stotten
rike.stotten@uibk.ac.at
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