Next Article in Journal
“Some Angles Are Gonna Be Weird”: Tinkering with Math and Weaving
Previous Article in Journal
Application of Luminescent Bacteria Bioassay in the Detection of Pollutants in Soil
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

An Exploration of Drivers for Abandonment or Continuation of Summer Pasture Grazing in South Tyrol, Italy

1
Institute for Regional Development, Eurac Research, Drususstrasse 1, 39100 Bozen, Italy
2
Institute of Integrative Nature Conservation Research, Department of Integrative Biology and Biodiversity Research, University of Natural Resources and Life Sciences, Gregor-Mendel-Strasse 33, 1180 Vienna, Austria
*
Author to whom correspondence should be addressed.
Sustainability 2023, 15(9), 7355; https://doi.org/10.3390/su15097355
Submission received: 15 March 2023 / Revised: 29 March 2023 / Accepted: 12 April 2023 / Published: 28 April 2023

Abstract

:
Summer pasture grazing is perceived as being under pressure from renewed wolf presence in the Italian Alpine province of South Tyrol. To investigate this, we combined a literature review with expert interviews to (1) get an overview of the situation of small ruminant farming and (2) identify drivers with an influence on summer pasture use, including wolf presence. Firstly, the results show an increase in small ruminant farms and stock numbers in the valley and on summer pastures during the last years. Secondly, subsidy programs, off-farm employment, lack of personnel and tourism are some of the main drivers for summer pasture development in the past and future. Thirdly, this analysis detects the potential pressure of wolf presence on small ruminant summer farming. Nevertheless, this impact should still be considered modest compared to other driving processes that have started before the return of the wolves. Based on this, the study finally discusses the importance of focusing on targeted funding, the revalorization of the shepherd profession and the balance between tourism and livestock farming to support summer pasture farming in the future.

1. Introduction

The term mountain summer pasture (hereinafter summer pasture) is defined as the semi-natural grassland above the permanent settlement boundary used for livestock grazing during the summer months [1,2]. These pastures, also called alpine pasture farming areas [3,4], are examples of habitats created by the interactions of environmental factors, such as climate and topography, and human activities. On one hand, these pastures guarantee the provision of forage to livestock and lead to work relief in the valley; on the other hand, their traditional agricultural use provides an important contribution to site-specific biodiversity and keeping the landscape open, with high recreational and cultural value [1,5,6]. This site-specific biodiversity is the result of small-scale changes in site conditions and the associated mosaic of vegetation types, and it relies on extensive grazing. For these reasons, the European Commission promotes the extensive management of livestock on pastures with low yield as a promising possibility to counter biodiversity decline, and defines it as high nature value farming [7,8].
Summer pasture grazing is widespread in the Alps in different geographic and natural contexts with different livestock breeds, mainly cattle, sheep and goats [9]. Unfortunately, the intensification of agricultural practices at valley bottoms and the abandonment of high elevation agricultural areas and traditional land use types have caused a deterioration of many of these summer pastures during the last decades, including a loss of biodiversity and landscape attractivity [10,11].
Since the return of the wolf, the predator has increasingly been labeled as a threat to a species-rich alpine cultural landscape in public debates, but also in reference books [12,13]. In these discussions, the wolf is often assigned the main blame for the abandonment of summer pastures and the loss of biodiversity. Other influencing factors, such as socio-cultural, agro-political, technological, economic and operational driving forces, which have led to agro-structural changes, are often ignored in these discussions [14,15], and only few scientific studies have investigated the socioeconomic impact of the wolves’ return and the necessity to use herd protection measures on summer pastures [16,17,18,19,20].

1.1. The Situation in South Tyrol

As in other alpine areas, in the Italian province of South Tyrol (hereinafter ST), agriculture is confronted with fundamental agro-structural changes, which mainly started in the 1960s. The livestock sector has shifted towards intensification with fewer but larger dairy farms with intensified land use and the economic marginalization of sheep and goat farming [21]. Additionally, the agricultural focus in the valley floors (up to 1000 m.a.s.l.) has changed from arable and livestock farms towards more profitable permanent crops, mostly apples and grape. This development has led to a decrease in livestock farms with around 35% abandonment between 1982 and 2020 [22].
Changes in livestock farms in the valley are closely connected with changes on summer pastures, which cover around 33% of ST and play an important role for the local economy as a highly frequented tourism destination [23,24]. Many summer pastures are managed from the valley; therefore, staff are not on site permanently and livestock are mostly unattended. Especially in central and eastern parts of the province with predominantly private pastures, the majority have no or only one person responsible for the management of livestock and terrain [11]. Heated discussions on wolf impact also emerged in this region after the predator returned in 2010, following more than 120 years of absence. In 2021, a minimum number of 30 individuals can be assumed [25]. Several demonstrations and petitions to remove wolves from ST to protect traditional summer pasture activities, especially concerning sheep and goats, took place in the last five years [26,27]. Livestock farmers experience wolf predation on their animals, with sheep on summer pastures being most affected, causing more than 130,000€ of damages in 2022 [28]. While the responsible provincial authority offers funding for herd protection, most livestock farmers still doubt the compatibility of fences, shepherds and guardian dogs with the present local circumstances. Besides the conflict with direct predation losses, the main arguments against livestock protection measures are prohibitively high additional costs and workload, especially in steep areas, leading to the abandonment of summer pastures [27,29]. Until now, however, no systematic data analysis on the development and status of summer pastures and the impact of wolves compared to other drivers was conducted in ST. This information could be crucial to objectivizing the polarized discussions during the last thirteen years.

1.2. Aim

The aim of this study is to explore the relationships between social, economic and natural drivers that determine the development of summer pasture use in ST. The focus lies on small ruminants, especially sheep, as it represents the sector most vulnerable to the wolf’s return and stands at the center of the related discussion on the future of summer grazing [28].
The authors set the hypothesis that there are different drivers to influence summer pasturing in ST and that the wolf is only one among several. This leads to the following research questions:
  • What is the recent state of small ruminant farming and summer pasture grazing in ST?
  • What are the main drivers to influence the development of summer pasture grazing in ST?
Finally, the study attempts to highlight the most pressing problems and implementable solutions to tackle in order to preserve summer pasturing in the province. The discussion will dedicate a separate chapter to the impact of the wolves’ return as the impetus for this study.

2. Materials and Methods

2.1. The Study Area of South Tyrol

The study area of ST lies in the north-eastern part of the Italian Alps (Figure 1). The province covers 7400 km2 and counts around 533,000 inhabitants, of which approximately 38% live in the five largest cities. Most people work in the tertiary (69.9%) and secondary sector (23.9%), while the number of persons employed in the agricultural sector decreased from 14% in 1986 to 6.2% in 2020 [30,31]. The provincial territory ranges from 230 to 3900 m above sea level, with about 40% above 2000 m above sea level.
Following the Council Regulation (EC) No.1698/2005, 94% of the total area of ST belongs to mountain territory [32]. Based on this, the local agriculture is divided into two areas: favored valley regions with intensive fruit and wine horticulture and mountain farming regions, also named alpine agriculture [33], focusing on grassland and dairy farming combined with tourism income. With an average of 11.9 ha of cultivated land per farm, the local agriculture is small-structured, almost exclusively done by family smallholders and clearly below the European average of 16 ha. Livestock farms usually manage larger areas, but a considerable part of their land consists of less productive grazing areas or summer pastures which cannot be cultivated by machinery [21].

2.2. Data Collection and Analysis

This study followed an explanatory two-phase mixed method design with a sequential data analysis process to record the past and present situation of small ruminant farming and summer pastures in ST [34]. In the first stage, the study collected and reviewed administrative data published by the national and provincial statistic institute and other provincial administrative offices (especially the Office of Mountain Economy and the Office for Hunting and Fishing). Additionally, a literature review was performed by reviewing the bibliography by Bätzing [2] and by using Google Scholar and local libraries’ search engines under the keywords “mountain summer pasture”, “driver”, “livestock farming” and “small ruminant” in the geographic context of the study area in German, English and Italian language. The study included the key literature related to those keywords in the context of the study area (see Table 1 for the references included).
In the second stage, six qualitative, systematic interviews were conducted with purposively selected local experts (Table 2) to amplify and address quantitative data results that needed more in-depth explanation or clarification [34,35]. The semi-structured interviews were conducted between January 2022 and February 2022 and were recorded. Afterwards, an explorative expert interview analysis of the transcribed responses was completed using NVivo software (Release 1.6.1; © 1999–2022 QSR International). Based on the literature review and the expert interviews, the main drivers were defined and discussed. The results section of this study is structured by the themes identified in the analysis.
Table 1. Overview of the drivers identified that influence the development of summer pasture farming in South Tyrol. − = negative impact; + = positive impact; / = no impact.
Table 1. Overview of the drivers identified that influence the development of summer pasture farming in South Tyrol. − = negative impact; + = positive impact; / = no impact.
Identified DriverDirectionExplanationSource
Agricultural subsidiesInappropriate use of subsidies[36]
Experts (5/6)
Accessibility provokes pasture management neglectionExperts (3/6)
+Accessibility favors continuation of farming activities[21,37]
Experts (3/6)
+Diverse and extensive income support[38,39,40,41,42]
Experts (4/6)
Off-farm
employment
Primary employment in more profitable sectors[33,40,43,44,45]
Experts (4/6)
Part-time farming neglects work intensive
activities
Experts (3/6)
+Part-time farming supports farm continuation[41,42,46]
Experts (3/6)
PersonnelLack of personnel impacts pasture management[25,44,47,48,49,50]
Experts (5/6)
TourismPrioritization of tourism over livestock[37,44,46]
Experts (5/6)
+Additional income[21,40,41,44,48]
Experts (4/6)
Other
drivers
Natural conditions+Fodder source and work release during summer[40,50,51]
Experts (5/6)
Steepness, low productivity, harsh working conditions[39,43,46]
Experts (3/6)
Market orientationIntensive fruit cultivation in the valley bottoms[21,37,39,46,50]
Fewer but larger farms in the valley[52]
Experts (5/6)
Mountain pasture products niche market[44]
Experts (4/6)
+Revalorization of high-quality local products[41]
Experts (2/6)
Farmers’
commitment
Narrow-mindedness prevents adaptationExperts (4/6)
+Strong connection to tradition and culture[33,40,42,53]
Experts (6/6)
The return of
wolves
Predation by wolves[45]
Experts (3/6)
+Wolves chance for pasture revalorization
Wolves have no impact
Experts (3/6)

3. Results

The research has revealed a lack of reliable data series related to summer pastures in ST over longer periods. For example, continuous data on the development of summer pasture areas and associated livestock numbers are only available with the start of the digital recordings in 2008 and 2016, respectively (A. Kasal, personal communication, 21 February 2021; Provincial Veterinary Service, personal communication, 16 March 2021). Therefore, the study relied on the total number of livestock retrieved from the national agricultural census data and expert interviews to estimate trends in this context. Data before the 1980s refer to sources evidenced in the literature review. The latter provided very few, and often relatively old references with a direct connection to the situation in the study area. In total, 22 reports and scientific publications coped with the keywords selected and were considered in this analysis (see Table 1). Considering this, the qualitative interviews provided crucial insights to fill the knowledge gaps and minimize the errors in the dataset.

3.1. The State of Small Ruminant Farming and Summer Pasture Grazing

The number of farms holding goat or sheep increased by more than 10% from 1982 to 2020 [22,54], as did the overall number of small ruminants: the goat stock grew considerably by 64% and the sheep stock by 37% within these 40 years (Figure 2) [54,55].
Nevertheless, 5/6 experts confirm the hobby and non-revenue related character of the local small ruminants’ husbandry, although some local companies sell wool products or work with sheep manure [38]. After a clear decrease of slaughtered sheep and goat for meat consumption in the 1970s and 1980s, the number kept increasing in the 1990s, surpassing that recorded in the 1960s, and arrived to the maximum number of 25,000 heads slaughtered in 2020. A similar development can be observed for sheep wool with around 900,000 kg produced in the 1960s, followed by a clear decrease in the 1970–80s and then an increase until 2017 (most recent data source), when 1.1 million kilograms of wool was produced [30,56].
By now, South Tyrol has 1598 active summer pastures that mostly lie on high elevation areas above the tree line (Table 3). Although 5/6 experts classify the number of pastures as stable with only a slight decline during the last decades, they expect numbers to decrease further in the future. In fact, only 55% of the agricultural areas in the subalpine level and less than 30% of the areas in the alpine level are still cultivated today [39].
Today, young cattle spend the summer on mountain pastures alongside most sheep and goats in the province. The high milk prices in the summer and the acid soil on many pastures, which is not so suitable for dairy farming, are the main reason for low adult cattle numbers, as confirmed by the literature [25,57] and 4/6 experts. Small ruminant numbers experience an increasing trend, starting from the systematic registration of livestock taken to summer pastures in 2016, with a 4.6% increase for sheep and 24% for goats until 2021 (Provincial Veterinary Service, personal communication, 9 August 2022). The largest and most numerous sheep or goat pastures can be found in the west, on large farming community areas with 55% of all small ruminants roaming in the forestry districts of Schlanders and Meran (see Figure 1). Nevertheless, the literature [58] and 5/6 experts expect an ongoing trend towards fewer but larger farms, intensification with generation turnover and an increase in the abandonment of small-scale farms in the future. According to 4/6 experts, summer pastures are influenced by this development, as some areas lack livestock and are confronted with scrub encroachment and forest expansion while others, especially in touristic areas, are overused.
Table 3. Summary of summer pastures characteristics in South Tyrol. Data sources: Gross grazing area [38]; Ownership [59]; Livestock numbers: Provincial Veterinary Service, [25]. Percentages based on own calculations. * Numbers include animals from South Tyrolean farms on pastures in South Tyrol and other provinces. Number of animals in other provinces is statistically not relevant (Provincial Veterinary Service, personal communication, 9 August 2022). ** Proportion of animals taken to summer pastures from total stock registered in the province.
Table 3. Summary of summer pastures characteristics in South Tyrol. Data sources: Gross grazing area [38]; Ownership [59]; Livestock numbers: Provincial Veterinary Service, [25]. Percentages based on own calculations. * Numbers include animals from South Tyrolean farms on pastures in South Tyrol and other provinces. Number of animals in other provinces is statistically not relevant (Provincial Veterinary Service, personal communication, 9 August 2022). ** Proportion of animals taken to summer pastures from total stock registered in the province.
CategoryMeasurement UnitPercentage
Gross Grazing Area<10 ha45
10–50 ha26
50–100 ha12
>100 ha17
OwnershipPrivate71
Farming community13
Co-owned7
Public body5
Others4
Livestock numbers (status: 2021) *Cattle40 **
Sheep81 **
Goat55 **

3.2. Drivers Affecting the Use of Summer Pastures in ST

Based on the literature review and expert interviews, this explorative study highlights four main drivers which seem to have a particularly strong influence on summer pasture use in ST, and some other drivers that have an influence, but they seem to be less in relation to others (Table 1). The drivers, often with both hindering and supporting aspects, are presented as follows.

3.2.1. Agricultural Subsidies

The extensive and diverse subsidy opportunities for agricultural farms, including summer pastures, play a key role in the preservation and competitiveness of mountain agriculture in ST [25]. The agricultural policy focuses on preserving as many farms as possible and part-time farming is strongly encouraged. One example is the large public investments in infrastructure developments in rural areas. In 1983, 42% of the summer pastures were not accessible by road [40]. By 2017, the percentage dropped to 11%, with 4% of the summer pastures located in protected areas [60]. Three experts explicitly name these investments in accessibility as a massive work relief, which has favored the continuation of summer pasture activities. At the same time, it also means that personnel and farmers spend less time in the area as they can drive up and down every day. Even if accessibility has improved, the same experts underline the risk of neglected pasture management and reduced attention towards the animals.
All experts agree that summer pasture management would hardly be feasible without agricultural subsidies and 4/6 state that the amount of income support is sufficiently high. Pasture owners or managers are eligible for monetary support from the European Common Agricultural Policy (CAP), namely the rural development program between 1978 and 2019 and the direct payments per hectare since 2015 [25,61]. However, 5/6 experts criticize these direct payments without conditions for their lack of targeted use. In their opinion, targeted subsidies are strongly needed to foster the investment in well-trained shepherds and proper pasture management, as already stated by Streifeneder et al. [41] and Hilpold [36]. Additionally, besides the European subsidy schemes, the provincial contribution supports investments in shepherds’ housing and livestock shelters on pastures, and on accessibility and pasture management improvements, such as livestock watering and gathering areas [25].

3.2.2. Off-Farm Employment

The general development in the employment sector exerts a decisive influence; until the middle of the nineteenth century, around 70% of people in ST worked in the primary sector. The situation shifted until 2000, with more than 93% of people working in the secondary and tertiary sector today [30,46]. Streifeneder [42] and 4/6 experts report the attraction of better paid jobs in other sectors which often provoke the decision of the young generation to abandon the family farming activity. The working decision is also based on economic considerations, with more than 60% of the self-managed farms running as an additional or secondary source of income [43,56]. This leads to a balancing act: on one hand, part-time farming reduces the number of farm abandonments in ST; on the other hand, labor-intensive activities, such as dairy farming or the cultivation of marginal areas, are reduced as much as possible due to time constraints [21]. Here, the opinion of the experts differs significantly; while one half underlines the importance of part-time farming against farm and pasture abandonment, the other half doubt the long-term success, as young farmers reject this double burden.

3.2.3. Personnel

The lack of well paid, experienced shepherds is classified by 5/6 experts as a major challenge for summer pastures in ST. The related challenges and consequences are, firstly, that maintenance measures are often neglected, and that these areas suffer from afforestation in the medium term which consequently causes biodiversity losses and over- or underuse of grazing areas [37,52]. Secondly, the daily presence of a shepherd improves animal welfare and is a necessary component of herd protection against large predators [25].
ST counted more than 1300 shepherds for around 101,000 animals on summer pastures in 1881. Between 1881 and 1975, the milk and dairy industry grew and pure sheep pastures, formally available in high numbers, became very rare [40,47]. Since the 1970s, it has become increasingly difficult to find shepherds for multiple seasons, and the employment costs are often too high, especially for small private pastures. Consequently, the number of shepherds diminished, and were often substituted with inexperienced and unpaid family members or old people, or employed with low pay rates [46,48,49]. Today, no official statistics exist, but the number of all day present shepherds is estimated to be very low [25].

3.2.4. Tourism

In the 1970s, the additional pasture income from small tourism businesses made it possible to pay wages above the provincial average and had a positive impact on the continuation of pasture grazing [48].
Today, 5/6 experts highlight a progressing imbalance between income from tourism and livestock husbandry as one of the main aspects influencing summer pasture grazing: firstly, pasture management, including shepherding and shrub clearance, is often neglected because more time is invested in the catering of tourists. Secondly, there is a general trend to invest more time and resources in the more profitable tourism sector than in livestock farming at home farms [46]. Although 4/6 experts agree that additional income from tourism can be crucial, especially for part-time farms, 5/6 experts name this shift from livestock farming to tourism as the primary challenge to preserve traditional summer pasture farming in the future.

3.2.5. Other Drivers

Natural, Market Related and Social Aspects

A positive driver is the crucial work relief and fodder source during the summer months for local livestock farmers [40,46]. Especially in previous decades, many small farms only achieved their arable food sources and the possibility to work as full-time farmers by bringing all their animals to summer pastures [50]. Depending on the location and weather conditions, the animals spend up to seven months away from the home farm, allowing the farmer to focus on other activities, such as haymaking, in this work-intensive period of the year. On the other side, the harsh natural circumstances and low financial viability have a negative effect on the use of summer pasture, interlinked with the general shift in society and labor market [21]. Market orientation towards larger, intensively run farms in the valley must be considered a negative driver as summer pasture products cannot compete with an open market. Today, apple and wine production account for a significantly larger share of added value than the livestock sector, with 60% compared to 36%, respectively [62]. In the last decades, wool has been replaced by other materials and the meat and dairy sector has been increasingly sourced from industrial large-scale livestock farming [44]. The market for summer pasture products is niche with limited financial viability, confirmed by 4/6 experts. Today, steep and small areas are often neglected as the effort to bring livestock there is not compensated by the financial return. Additionally, the number of people interested and capable of working under these harsh conditions over a longer period is limited.
Another twofold driver is the farmers’ commitment: on the one hand, the share of farm succession in ST is higher than in many other areas of the Alps. The local mountain farmers show a strong connection to tradition and thus a desire to preserve local culture. Often the economic income is rated lower than the emotional and cultural values [21,53]. All six interviewed experts underlined the reluctancy with which current farmers often give up their farms and the associated preservation of local cultures, which also includes summer pasturing traditions. Interested newcomers without an agricultural background could struggle with the harsh working conditions and low financial viability, and half of the experts underlined the importance of supporting existing livestock farmers on mountain farms and shepherds on pastures in any way possible to avoid abandonment. On the other hand, however, 4/6 experts point out that thinking in terms of traditions often impedes changes in the mindset, which consequently hinders necessary adaptation processes to new developments, such as the return of large carnivores.

The Return of Wolves

The literature review detected only one study that so far investigated the attitude towards wolf return in ST among society [63] and one among the agricultural sector [45], with a clear negative attitude among farmers and a perception of threat for summer pasture activities. The expert interviews conducted here reveal diverging opinions. Most experts name the renewed presence of wolves and the necessity to use livestock protection measures as one of many challenges that summer pasturing is confronted with. The interviewees see the farmers’ emotional attachment to their animals and the forced management changes with protection measures as the central aspects to be considered—which also bring the problem to the forefront in comparison to others. In detail then, three experts consider the wolf as a negative impact, especially for small ruminant farming, and two consider it to have no impact at all. One expert suggests that the wolves’ return is both a challenge and a chance to properly adapt pasture management through the return of shepherds and guided grazing, with benefits for biodiversity and landscape attractiveness.

4. Discussion

The results of this study highlight some interesting findings, including the increasing number of sheep and goat farms and stock numbers. One explanation may be linked with a steady decrease in cattle farms, which decreased by 42% between 1982 and 2020 from 12,792 to 7400 [22]. Here, interviewed experts noted that farmers may give up cattle, but in order not to quit farming altogether, keep sheep or goats, which are less labor-intensive and costly. Goat husbandry especially is currently experiencing an upswing, mostly among hobby farmers. This result contradicts trends in other areas of Europe and Italy [55,64] and shows that the local sector may be more resilient than expected or that other drivers, not detected in this study, must have an impact. Secondly, subsidy programs, off-farm employment and tourism are some main drivers for summer pasture development. This result is in line with Streifeneder et al. [41], who name the same drivers as crucial for safeguarding the livelihood of alpine pasture farms. Additionally, to the authors’ best knowledge, this is the first study to highlight the key function of personnel in ST, especially shepherds, to preserve summer pasture in the future.

4.1. The Guiding Power of Agricultural Subsidies

Agricultural subsidies, especially on the European level, are a considerable driver to influence the preservation of summer pastures and seem to be the only way to compensate for the low rentability and high workload [25,65,66]. Projections from Renwick et al. [67] clearly showed that extensive farming, such as summer pasture grazing, faces a higher level of risk of being abandoned without CAP support. Nevertheless, unconditional income support is being questioned in other contexts [41,68,69] as well as here as unjustified income by mere proof of ownership. These studies highlight the need to target subsides for pasture management and personnel, as also underlined by 5/6 experts in this study. The previous European agri-environmental measures, established to support environmentally friendly farming such as pasture-based farming, have often been criticized for their low impact rates due to their voluntary nature [70]. In this context, O’Rourke et al. [71] and Marini et al. [72] talked about ‘paying by results’ or ‘payment for ecosystem services’ to support High Nature Value farming. For example, in Switzerland, staggered payments supporting permanent shepherds’ presence and guided grazing are already installed [73]. The newly introduced CAP eco-schemes, including “Shepherding on open spaces and between permanent crops, transhumance and common grazing”, could support summer pasture grazing [74]. At the time of this publication, no official document on the future distribution of these subsidies or on targeted payments were available for ST. Another aspect is that tourism profits from the cultural landscape with high aesthetic and recreational value, formed also through the continuous grazing activities on summer pastures. More than half of the yearly tourist numbers visit ST during the summer period and name hiking activities and the attractiveness of the traditional landscape as the main reasons for a holiday in this province [24,30]. A form of tourism taxes could be introduced to support the preservation of this landscape and biodiversity, as already successfully put into practice in the Southern Black Forest Nature Park [75]. The willingness to also pay for the nonmarket function of agriculture is growing [76,77,78] as summer pasture farming forms a variety of regulating, provisioning and cultural ecosystem services [79]. This would allow us to move away from conservative payment structures and develop new communication and marketing strategies to connect with the general public and increase the market value of the products [68]. This strategy must, however, consider the fact that expectations from the landscape and its offers may vary between locals and tourists [78].

4.2. The Impact of Side Farming

The impact of part-time farming on agricultural activities in general is considered controversial in the literature, with some studies arguing it could increase the chance for farm abandonment [80,81] and others viewing it as a factor of stability [41,82]. A recent study on part-time farming in Europe showed a decrease in secondary income farming and a slight increase in additional farming and expects an increase in larger, more professional farms [83]. For summer pasture use, part-time farming is often problematic as proper pasture management would need manual labor and time, which is often lacking [66]. Politics, associations and administration support part-time farming in ST as a factor of stability, however a representative study measuring its impact on livestock farming is not available at this time [25].

4.3. The Rediscovery of the Personnel’s Role

The lack of professional personnel to control the animals and manage the pasture in a positive way is a key challenge for local summer pasture use, but notable also in other areas of Europe [15,84]. The role of the shepherd to prevent forest regrowth and keep the open landscape through guided grazing, especially in the face of decreasing livestock numbers, as stated by Lombardi [85] and 4/6 experts, is evident. Additionally, today the shepherd profession experiences a revival, linked with the return of wolves and the necessity to implement herd protection measures [86]. However, the costs for shepherds often seem too high, especially for small herds, and the social recognition of the shepherd profession is still too low to pay an appropriate salary [66]. In ST, the first initiatives to revalorize this profession started in 2020 with the launch of the European LIFE project LIFEstockProtect and the introduction of a shepherd training course with an official profession recognition by the provincial administration. Nevertheless, the number of experienced shepherds is still very low [25] and no salary benchmarks are set.

4.4. The Ambivalent Relationship to Tourism

Tourism is another driver to impact summer pasture use in the study area. Farms offering rooms for tourists have more than doubled in the last 25 years [87], with a 10% share of all overnight stays in the province in 2021 [88]. The direct and indirect impacts could be positive by generating additional income on the summer pasture or the home farm, or negative by shifting the attention towards hospitality and away from livestock. The results from this study indicate a negative impact, but further research is needed to make general valid statements. Research from other areas is twofold: on the positive side, tourism may offer a complementary income, which may reduce or prevent farm and summer pasture abandonment [10,41,89], it requires the preservation of the semi-natural landscape as a desired destination [65,72] and it offers multifunctional use and fosters the innovation potential of farms [90]. On the negative side, better income opportunities in tourism may lead to the marginalization or abandonment of livestock related activities [91], provoke a neglection or loss of knowledge of the optimal use of pasture [66,92], or may overload personnel [93]. For sure, an integrative concept is needed to combine agriculture, tourism and rural development in a fruitful way, such as mentioned in the form of tourism taxes before [89,94].

4.5. Natural, Market Related and Social Considerations

The impact of natural circumstances as a driver of summer pasture use must be classified as two-sided. On the negative side, the high cultivation costs combined with low yield provoke the abandonment of marginal areas in steep slopes as no longer being economically or timely rentable [95,96]. Additionally, the harsh working conditions which involve working long hours during extreme weather may be difficult to endure for a longer period [97]. On the positive side, firstly, the use of summer pastures was and still is an essential fodder source and an important work relief for the farms in the valley. Secondly, the land in the valley is more fertile and can also be used for crop cultivation [3]. Thirdly, the benefits for the animals’ health, resistance and fitness are undoubted [65,95]. Additionally, the natural constraints could be turned into an added value with the ability of providing environmental, historical and cultural insights. The recent demand for high quality products, animal welfare and traceability of food sources favors this opportunity [41,94,98] and could open new perspectives in the face of difficult competitiveness with intensive agriculture in the valley [80]. Nevertheless, a clear strategy is necessary to open the market to the marginal sheep sector and guarantee a coverage of production costs [66,99].
From a social viewpoint, passion, tradition and place attachment are relevant and fundamentally contribute to continuing high mountain farming and summer pasturing in spite of fewer economic gains in ST and in other mountainous areas [100,101]. Schmitt (1997), quoted by Strijker [102] and named again by Terres et al. [82], noted in general a high willingness to be a farmer where the income must be very low to leave the primary sector. On the other side, long-established habits may impede innovation and provoke conflict between modern and traditional values, such as a change in animal husbandry systems on pasture due to the return of wolves [15].

4.6. The Impact of Wolves

The return of wolves can be considered one of many drivers to impact summer pasture farming in the study area. The additional costs and efforts related to herd protection measures discourage livestock farmers and cause doubt on the future of summer grazing, as also reported in other studies [2,100,103]. In this context, Gervasi et al. [104] emphasized the higher difficulties with reinstalling traditional grazing practices with necessary protection measures in an area where they have been forgotten, compared to maintaining them in areas with continuous historic use. Especially “hobby” farmers with small herds are under pressure with wolf presence, and herd protection measures are a limited option due to financial and time restrictions [17]. These difficulties in husbandry adaptations and small herds largely reflect the situation in ST and may explain the low willingness to reduce the impact of wolves on summer pasturing through livestock protection measures [25]. In Switzerland, with longer wolf presence and similar conditions on pastures as in ST, the process of adaptation has been ongoing for more than 25 years. Firstly, it has led to a general increase in goat numbers and a decrease in sheep numbers, which seem to be more difficult to protect, and secondly to a positive increase in guided grazing and permanent shepherding on pastures [103]. This is a development that could be transferred to ST, if trends in livestock number and initiatives to revalorize the shepherd profession continue in the upcoming years. On one side, the financial burden and workload linked to this change in animal husbandry must be considered [94,105]. Additionally, the stress that livestock farmers experience with wolves can trigger negative reactions, such as pasture abandonment or small-scale fencing, with negative consequences for species richness and abundance [106]. On the other side, the necessity to adopt guided grazing could also result in an added benefit for landscape preservation, biodiversity and animal welfare, with the constant presence of shepherds and the cultivation of marginal areas [107]. Forest regrowth linked to the abandonment of marginal areas on summer pastures has been documented since the 1950s in ST and is an ongoing process [21]. Additional nutrient inputs and changing climatic conditions enhance fodder growth, and livestock only consume around half of the fodder resources produced on summer pastures [21]. Taking this into account, the open, species-rich cultural landscape and the image of the alpine pastures will change fundamentally [10,72]. Future discussions on the value of summer pastures for biodiversity must therefore also reflect on another conservation perspective, as from a process-oriented, dynamic point of view, the abandonment of pasture areas and passive rewilding can also have positive impacts on ecosystems [108,109].
To sum up, until now the impact of wolves on small ruminant farming and the abandonment of summer pastures should still be considered modest compared to other driving forces discussed here and in other studies [15,51,110]. As for ST, these processes go back to before the return of the wolf, and within this explorative study, no long-term cause and effect relationship could yet be determined. Nevertheless, a holistic approach will be necessary to counteract the ongoing abandonment of pastoralism due to economic and social drivers, which could be fortified with damages caused by an inappropriate management related to the wolf presence [14,104].

4.7. Limitations

A limitation of this study concerns the lack of reliable data series. Since no continuous data on the development of summer pasture areas and associated livestock numbers were available for a longer period of time, a quantitative data analysis was not possible. Additionally, concerning the impact drivers, data monitoring and previous research were too sparse or missing, so we could not talk about cause-effect relations. Therefore, caution should be exercised when extending these results to other regions and trying to prioritize drivers of impact quantitatively.

5. Conclusions

This study provides a first overview on the status of small livestock farming and summer pasture use in ST and should serve as a starting point for future research on this topic. One conclusion of this study is the lack of a comprehensive, long-term dataset for summer pastures and the related livestock movement in the study area. This fact makes it difficult to describe the development, current situation and likely future scenarios in a reliable way, not only for strict scientific use, but also in a more general way for dissemination and educational purposes. A second insight is that impact drivers are interrelated with the wider economic, social and natural development and a one-to-one relation is blurred. Their number is manifold but based on the current experts’ experiences, and the major challenges to consider in the near future seem to be the re-evaluation of subsidies, the unclear impact of side farming, the lack of personnel and the balance between tourism and agriculture. Based on results of our research, the following suggestions are presented:
1.
Efforts to improve long-term datasets should further be intensified to be able to work in a more targeted way. Related to this, more research is needed to give a balanced overall picture of drivers or even allow for a quantitative weighting of impacts.
2.
The high dependence of farmers on public subsidies could make them vulnerable to political and societal changes in subsidy distribution. A new form of support must be introduced, such as compensation for environmental services or landscape tourism taxes.
3.
As shown, shepherds will play a key role in the preservation of high nature value areas, especially in steep zones, and contribute to landscape preservation, biodiversity and animal welfare. The first initiatives to revalorize this profession have been launched, but there is still a considerable need for improvement of working conditions, such as appropriate housing, regulation of working hours and payment.
4.
As long as tourism serves to maintain summer pasturing, it should be recognized as a good opportunity to increase income. However, when there is a growing imbalance between agriculture and hospitality, tourism may cause more harm in the long term. Careful management and monitoring should prevent such a development.
5.
The issue of the wolf return is relatively new compared to the other drivers, but due to its emotional value, it will be important to tackle in a proactive way.

Author Contributions

Conceptualization, J.S. and M.K.; Methodology, J.S.; Validation, J.S.; Investigation, J.S.; Writing—original draft, J.S.; Writing—review & editing, H.M. and M.K.; Visualization, J.S.; Supervision, H.M. and M.K.; Project administration, J.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Informed Consent Statement

Informed consent was obtained from all subjects involved in the study.

Data Availability Statement

The data presented in this study are available on request from the corresponding author. The data are not publicly available due to privacy restrictions.

Acknowledgments

The authors thank the Department of Innovation, Research and University of the Autonomous Province of Bozen/Bolzano for covering the Open Access publication costs.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Deléglise, C.; Dodier, H.; Garde, L.; François, H.; Arpin, I.; Nettier, B. A Method for Diagnosing Summer Mountain Pastures’ Vulnerability to Climate Change, Developed in the French Alps. Mt. Res. Dev. 2019, 39, D27–D41. [Google Scholar] [CrossRef]
  2. Bätzinger, W. Alm-Und Alpwirtschaft Im Alpenraum; Context Verlag: Augsburg, Germany, 2021. [Google Scholar]
  3. Gilck, F.; Poschlod, P. The Origin of Alpine Farming: A Review of Archaeological, Linguistic and Archaeobotanical Studies in the Alps. Holocene 2019, 29, 1503–1511. [Google Scholar] [CrossRef]
  4. Nettier, B.; Dobremez, L.; Brunschwig, G. Alpine Pasture-Farms System: A Concept to Analyse the Management of Alpine Pastures. In Forage Resources and Ecosystemservices Provided by Mountainand Mediterranean Grasslandsand Rangelands, Proceedings of the Joint Meeting of the ”Mountain Pastures, Mediterranean Forage Resources (FAO/ESCORENA-CIHEAM) and Mountain Cheese” Network, Clermont-Ferrand, France, June 2014; Baumont, R., Carrere, P., Jouven, M., Lombardi, G., Lòpez-Francos, A., Martin, B., Peeters, A., Porqueddu, C., Eds.; pp. 717–721. Available online: https://hal.science/hal-01140667/ (accessed on 14 July 2022).
  5. Bätzinger, W. Die Alpen: Geschichte Und Zukunft Einer Europäischen Kulturlandschaft; Verlag C.H.Beck: München, Germany, 2005. [Google Scholar]
  6. Nettier, B.; Dobremez, L.; Lavorel, S.; Brunschwig, G. Resilience as a Framework for Analyzing the Adaptation of Mountain Summer Pasture Systems to Climate Change. Ecol. Soc. 2017, 22, 4. [Google Scholar] [CrossRef]
  7. Kerven, C.; Behnke, R. Policies and Practices of Pastoralism in Europe. Pastor. Res. Policy Pract. 2011, 1, 28. [Google Scholar] [CrossRef]
  8. Lesschen, J.P.; Elbersen, B.; Hazeu, G.; van Doorn, A.; Mucher, S.; Velthof, G. Defining and Classifying Grasslands in Europe; Alterra, part of Wageningen UR: Wageningen, The Netherlands, 2014. [Google Scholar]
  9. Guitton, M.; Levret, C.; Delefortrie, R. Challenges of Pastoralism: Exchange of Innovative Experiences for a Sustainable Development in Mountain Areas; Euromontana: Brussels, Belgium, 2008. [Google Scholar]
  10. Cocca, G.; Sturaro, E.; Gallo, L.; Ramanzin, M. Is the Abandonment of Traditional Livestock Farming Systems the Main Driver of Mountain Landscape Change in Alpine Areas? Land Use Policy 2012, 29, 878–886. [Google Scholar] [CrossRef]
  11. Flury, C.; Huber, R.; Tasser, E. Future of Mountain Agriculture in the Alps. In The Future of Mountain Agriculture; Mann, S., Ed.; Springer: Berlin/Heidelberg, Germany, 2013; pp. 105–126. [Google Scholar]
  12. Hackländer, K. Der Wolf: Im Spannungsfeld von Land- & Forstwirtschaft, Jagd, Tourismus und Artenschutz, 1st ed.; Leopold Stocker Verlag: Graz, Austria, 2019. [Google Scholar]
  13. Züger, M. Welchen Einfluss Hat Der Wolf Auf Die Biodiversität Der Alpen? In Der Wolf Im Visier. Konflikte und Lösungsansätze. Im Fokus: Der Wolf in den Alpen; Aukenthaler, H., Ed.; Athesia Verlag: Bozen, Italy, 2022; pp. 136–139. [Google Scholar]
  14. Khorozyan, I.; Heurich, M. Large-Scale Sheep Losses to Wolves (Canis lupus) in Germany Are Related to the Expansion of the Wolf Population but Not to Increasing Wolf Numbers. Front. Ecol. Evol. 2022, 10, 778917. [Google Scholar] [CrossRef]
  15. Linnell, J.; Cretois, B. Research for AGRI Committee–The Revival of Wolves and Other Large Predators and Its Impact on Farmers and Their Livelihood in Rural Regions of Europe; European Parliament, Policy Department for Structural and Cohesion Policies: Brussels, Belgium, 2018. [Google Scholar]
  16. Martin, J.-L.; Chamaillé-Jammes, S.; Waller, D.M. Deer, Wolves, and People: Costs, Benefits and Challenges of Living Together. Biol. Rev. 2020, 95, 782–801. [Google Scholar] [CrossRef] [PubMed]
  17. Mink, S.; Mann, S. The Effect of Wolves on the Exit and Voicing Exit of Swiss Mountain Farmers. J. Rural Stud. 2022, 96, 167–179. [Google Scholar] [CrossRef]
  18. Rode, J.; Flinzberger, L.; Karutz, R.; Berghöfer, A.; Schröter-Schlaack, C. Why so Negative? Exploring the Socio-Economic Impacts of Large Carnivores from a European Perspective. Biol. Conserv. 2021, 255, 108918. [Google Scholar] [CrossRef]
  19. Chapron, G.; Kaczensky, P.; Linnell, J.; von Arx, M.; Huber, D.; Andrén, H.; López-Bao, J.V.; Adamec, M.; Álvares, F.; Anders, O.; et al. Recovery of Large Carnivores in Europe’s Modern Human-Dominated Landscapes. Science 2014, 346, 1517–1519. [Google Scholar] [CrossRef]
  20. Kovařík, P.; Kutal, M.; Machar, I. Sheep and Wolves: Is the Occurrence of Large Predators a Limiting Factor for Sheep Grazing in the Czech Carpathians? J. Nat. Conserv. 2014, 22, 479–486. [Google Scholar] [CrossRef]
  21. Tasser, E. Landschaft. In Landwirtschaftsreport zur Nachhaltigkeit Südtirol; Tappeiner, U., Marsoner, T., Niedrist, G., Eds.; Eurac Research: Bozen, Italy, 2020; pp. 35–43. [Google Scholar]
  22. ISTAT. 7° Censimento Generale Dell’agricoltura: Integrazione dei Primi Risultati. Available online: https://www.istat.it/it/archivio/273753 (accessed on 15 October 2022).
  23. Autonomous Province of Bolzano. Almen in Südtirol. Available online: https://www.provinz.bz.it/land-forstwirtschaft/wald-holz-almen/almen-suedtirol.asp (accessed on 21 February 2022).
  24. Pechlaner, H.; Volgger, M.; Demetz, M.; Scuttari, A.; Innerhofer, E.; Lun, L.-M.; Erschbamer, G.; Bassani, R.; Ravazzoli, E.; Maier, R.; et al. Zukunft Tourismus Südtirol 2030; Eurac Research: Bozen, Italy, 2017. [Google Scholar]
  25. Autonomous Province of Bolzano. Agrar- und Forstbericht. 2021. Available online: https://www.provinz.bz.it/land-forstwirtschaft/landwirtschaft/agrar-forstbericht.asp (accessed on 5 May 2022).
  26. Falkensteiner, C. Mahnfeuer Gegen Den Wolf. Available online: https://www.sbb.it/home/news-detail/index/2018/09/13/mahnfeuer-gegen-den-wolf (accessed on 13 July 2022).
  27. Südtiroler Bauernbund. Großdemo in München Gegen den Wolf. Available online: https://www.sbb.it/Home/News (accessed on 10 February 2022).
  28. Autonomous Province of Bolzano. Wolfsschäden und Vergütung. Available online: https://www.provinz.bz.it/land-forstwirtschaft/fauna-jagd-fischerei/fauna/wolf-suedtirol/wolfsschaeden-verguetung.asp (accessed on 14 March 2023).
  29. Südtiroler Bauernbund. Der Wolf in Südtirol Und Trentino; Sonderbeilage: Dolomiten, Italy, 2019. [Google Scholar]
  30. ASTAT. Statistisches Jahrbuch für Südtirol. 2021. Available online: https://astat.provinz.bz.it/downloads/JB2021.pdf (accessed on 3 May 2022).
  31. ASTAT. Statistisches Jahrbuch für Südtirol. 1997. Available online: https://astat.provinz.bz.it/downloads/Statistisches_Jahrbuch_1998.pdf (accessed on 7 March 2022).
  32. Autonomous Province of Bolzano. Erschwernispunkte in der Berglandwirtschaft. Available online: https://www.provinz.bz.it/land-forstwirtschaft/landwirtschaft/publikationen.asp (accessed on 28 June 2020).
  33. Massot-Marti, A. Agriculture in the Alpine Areas of Austria and Italy; European Parliament: Brussels, Belgium, 2007. [Google Scholar]
  34. Creswell, J.W.; Plano Clark, V.L. Designing and Conducting Mixed Methods Research, 3rd ed.; SAGE Publications: Thousand Oaks, CA, USA, 2018. [Google Scholar]
  35. Bogner, A.; Menz, W. Das Theoriegenerierende Experteninterview-Erkenntnisinteresse, Wissensformen, Interaktion. In Experteninterviews-Theorien, Methoden, Anwendungsfelder; Bogner, A., Littig, B., Menz, W., Eds.; VS Verlag für Sozialwissenschaften: Wiesbaden, Germany, 2009; pp. 61–97. [Google Scholar]
  36. Hilpold, A. Biodiversität. In Landwirtschaftsreport zur Nachhaltigkeit Südtirol; Tappeiner, U., Marsoner, T., Niedrist, G., Eds.; Eurac Research: Bozen, Italy, 2020; pp. 61–75. [Google Scholar]
  37. Tasser, E.; Schermer, M.; Siegl, G.; Tappeiner, U. Wir Landschaftsmacher: Vom Sein Und Werden der Kulturlandschaft in Nord-, Ost- Und Südtirol; Athesia: Bolzano, Italy, 2012. [Google Scholar]
  38. Autonomous Province of Bolzano. Agrar-Und Forstbericht 2020. 2021. Available online: https://issuu.com/landsuedtirol-provinciabolzano/docs/forst-_agrar-katalog_deutsch_internet_2020?fr=sYjhiODczMDk3Nw (accessed on 14 July 2022).
  39. Grüber, M.; Tasser, E. Südtirols Kulturlandschaft: Gestern-Heute-Morgen. In Südtirol. Eine Landschaft auf dem Prüfstand; Kreisel, W., Ruffini, F.V., Reeh, T., Pörtge, K.-H., Eds.; Tappeiner AG: Lana, Italy, 2010; p. 360. [Google Scholar]
  40. Plank, J. Stand und Entwicklung der Almwirtschaft in Südtirol; Leopold-Franzens-Universität: Innsbruck, Austria, 1983. [Google Scholar]
  41. Streifeneder, T.P.; Giuliani, C.; Hoffmann, C. A Cross-Border Analysis of the Policies for Alpine Pasture Farming. In Cross-Border Spatial Development in Bavaria: Dynamics in Cooperation–Potentials of Integration; Chilla, T., Sielker, F., Eds.; Verlag der ARL-Akademie für Raumentwicklung in der Leibniz-Gemeinschaft: Hannover, Germany, 2022; pp. 44–71. [Google Scholar]
  42. Streifeneder, T.P. Die Agrarstrukturen in Den Alpen Und Ihre Entwicklung Unter Berücksichtigung Ihrer Bestimmungsgründe–Eine Alpenweite Untersuchung Anhand von Gemeindedaten. Ph.D. Thesis, Universität München, Munich, Germany, 2009. [Google Scholar]
  43. Tasser, E.; Tappeiner, U.; Cernusca, A. Südtirols Almen Im Wandel. Ökologische Folgen von Landnutzungsänderungen; Eurac Research: Bozen, Italy, 2001. [Google Scholar]
  44. Müller, B. Die Almwirtschaft in Südtirol. In Historische Und Aktuelle Entwicklung; GRIN Verlag: Munich, Germany, 2010. [Google Scholar]
  45. Stauder, J.; Omizzolo, A.; Streifeneder, T.P.; Favilli, F. Erhebung der Einstellung von Einheimischen und Touristen zur Rückkehr des Wolfes Nach Südtirol; Eurac Research: Bozen, Italy, 2019. [Google Scholar]
  46. Tasser, E.; Aigner, S.; Egger, G.; Tappeiner, U. Almatlas, Alpatlas = Atlante delle Malghe; Arbeitsgemeinschaft Alpenländer ARGE ALP: Innsbruck, Austria, 2013. [Google Scholar]
  47. Pazeller, M. Die Entwicklung der Alpwirtschaft in Südtirol im Laufe Eines Jahrhunderts, Insbesondere Im Planeiltal, Sowie die Grenzüberschreitende Alpung Zwischen Südtirol, Österreich und der Schweiz; University of Natural Resources and Life Sciences: Vienna, Austria, 1987. [Google Scholar]
  48. Tscholl, H. Der Tschögglberg. Eine Bevölkerungs- und Wirtschaftsgeographische Untersuchung; Geographisches Institut der Universität Innsbruck: Innsbruck, Austria, 1978. [Google Scholar]
  49. Jentsch, C. Jüngere Wandlungen in der Almwirtschaft des Östlichen Südtirol am Beispiel des Oberen Ahrntales. In Studien zur Landeskunde Tirols und Angrenzender Gebiete: Festschrift des Instituts für Landeskunde zum 60. Geburtstag von Adolf Leidlmair; Selbstverl des Instituts für Geographie der Univ Innsbruck: Innsbruck, Austria, 1979; pp. 319–326. [Google Scholar]
  50. Fischer, K. Agrargeographie des Westlichen Südtirols; Braumüller: Vienna, Austria; Stuttgart, Germany, 1974. [Google Scholar]
  51. Niedrist, G.; Hilpold, A. Naturräumliche und Geographische Voraussetzungen. In Landwirtschaftsreport zur Nachhaltigkeit Südtirol; Tappeiner, U., Marsoner, T., Niedrist, G., Eds.; Eurac Research: Bozen, Italy, 2020; pp. 35–43. [Google Scholar]
  52. Autonomous Province of Bolzano. Kulturlandschaft Südtirol. der Wandel Seit. 1950. Available online: https://digital.zlb.de/viewer/metadata/15358906/1/ (accessed on 30 June 2022).
  53. Vogel, S.; Maurer, O.; Wytrzens, H.K.; Larcher, M. Perceptions of Mountain Farming in South Tyrol: Cultural Differences in a Border Region. In Man in the Landscape across Frontiers: Landscape and Land Use Change in Central European Border Regions, Proceedings of the IGU/LUCC Central European Conference 2007, Charles University, Prague, Czech Republic, 28 August–4 September 2007; Kabrda, J., Bicik, I., Eds.; 2007; pp. 209–220. [Google Scholar]
  54. ASTAT. Landwirtschaftszählung. 1982. Available online: https://astat.provinz.bz.it/downloads/LZ_1982_dt.pdf (accessed on 10 April 2022).
  55. ISTAT. Agricoltura. Available online: https://www.istat.it/it/agricoltura (accessed on 20 October 2022).
  56. ASTAT. Zeitreihe der Landwirtschaft 1929–2016. Available online: https://astat.provinz.bz.it/de/aktuelles-publikationen-info.asp?news_action=4&news_article_id=617592 (accessed on 2 February 2020).
  57. Prugger, I. Südtiroler Almgeschichten, 4th ed.; Löwenzahn: Innsbruck, Austria, 2015. [Google Scholar]
  58. Autonomous Province of Bolzano. Agrar- und Forstbericht. 2009. Available online: http://www.provinz.bz.it/land-forstwirtschaft/landwirtschaft/agrar-forstbericht.asp?publ_page=1 (accessed on 10 March 2022).
  59. Autonomous Province of Bolzano. Agrar- und Forstbericht. 2019. Available online: https://issuu.com/landsuedtirol-provinciabolzano/docs/535096_agrar-forstbericht_2019_web?fr=sZjkzMzczMDk3Nw (accessed on 10 March 2022).
  60. Schuler, A.; Theiner, R. Almerschließungen. Available online: https://redas.services.siag.it/redasArticlesAttachment?attachId=903489 (accessed on 17 November 2021).
  61. Schuler, A. Beantwortung der Landtagsanfrage Nr. 1062-2020: Aufstellung über Beiträge und die Alpungsprämien. Available online: http://www2.landtag-bz.org/documenti_pdf/idap_613751.pdf (accessed on 26 July 2022).
  62. Handels- Industrie-, H.L.B. Economy in Figures. Die Südtiroler Wirtschaft-aktuelle Daten, Indikatoren und Entwicklungen. Available online: https://www.wifo.bz.it/media/c54652fc-e7bd-4e27-a2ce-b3c5bf63f8ab/2021-wifo-economyinfigures-de.pdf (accessed on 23 July 2022).
  63. Stauder, J.; Favilli, F.; Stawinoga, A.; Omizzolo, A.; Streifeneder, T. The Attitude of Society to the Return of the Wolf in South Tyrol (Italy). Eur. J. Wildl. Res. 2020, 66, 40. [Google Scholar] [CrossRef]
  64. Eurostat. Livestock Population in Numbers. Available online: https://ec.europa.eu/eurostat/web/products-eurostat-news/-/ddn-20200923-1 (accessed on 10 March 2022).
  65. Wanner, A.; Pröbstl-Haider, U.; Feilhammer, M. The Future of Alpine Pastures–Agricultural or Tourism Development? Experiences from the German Alps. J. Outdoor Recreat. Tour. 2021, 35, 100405. [Google Scholar] [CrossRef]
  66. Obweger, A. Analyse des Rückgangs der Almauftriebszahlen in Österreich. Master’s Thesis, University of Natural Ressources and Life Science, Vienna, Austria, 2018. [Google Scholar]
  67. Renwick, A.; Jansson, T.; Verburg, P.H.; Revoredo-Giha, C.; Britz, W.; Gocht, A.; McCracken, D. Policy Reform and Agricultural Land Abandonment in the EU. Land Use Policy 2013, 30, 446–457. [Google Scholar] [CrossRef]
  68. Faccioni, G.; Sturaro, E.; Ramanzina, M.; Bernués, A. Socio-Economic Valuation of Abandonment and Intensification of Alpine Agroecosystems and Associated Ecosystem Services. Land Use Policy 2019, 81, 453–462. [Google Scholar] [CrossRef]
  69. Salhofer, K.; Feichtinger, P. Regional Differences in the Capitalisation of First and Second Pillar Payments of the CAP into Land Rental Prices. Eur. Rev. Agric. Econ. 2021, 48, 8–41. [Google Scholar] [CrossRef]
  70. Rodríguez-Ortega, T.; Olaizola, A.M.; Bernués, A. A Novel Management-Based System of Payments for Ecosystem Services for Targeted Agri-Environmental Policy. Ecosyst. Serv. 2018, 34, 74–84. [Google Scholar] [CrossRef]
  71. O’Rourke, E.; Charbonneau, M.; Poinsot, Y. High Nature Value Mountain Farming Systems in Europe: Case Studies from the Atlantic Pyrenees, France and the Kerry Uplands, Ireland. J. Rural Stud. 2016, 46, 47–59. [Google Scholar]
  72. Marini, L.; Klimek, S.; Battisti, A. Mitigating the Impacts of the Decline of Traditional Farming on Mountain Landscapes and Biodiversity: A Case Study in the European Alps. Environ. Sci. Policy 2011, 14, 258–267. [Google Scholar] [CrossRef]
  73. Bundesamt für Landwirtschaft BLW. Überblick: Direktzahlungen an Sömmerungs- und Gemeinschaftsweidebetriebe. Available online: https://www.blw.admin.ch/dam/blw/de/dokumente/Instrumente/Direktzahlungen/VoraussetzungenBegriffe/WeitereInformationen/ueberblick-dz-soemmerungsbetriebe.pdf.download.pdf/Überblick_DZ_Sömmerungsbetriebe_DE.pdf (accessed on 10 May 2022).
  74. European Commission. List of Potential Agricultural Practices that Eco-Schemes Could Support. Available online: https://agriculture.ec.europa.eu/news/commission-publishes-list-potential-eco-schemes-2021-01-14_en (accessed on 17 October 2022).
  75. Liesen, J.; Coch, T. Finanzielle Unterstützung Des Landschaftserhalts Durch Die Kurtaxe–Erfahrungen Aus Der Ferienregion Münstertal-Staufen (Naturpark Südschwarzwald). Nat. Landsch. 2015, 47, 69–76. [Google Scholar]
  76. Bernués, A.; Rodríguez-Ortega, T.; Alfnes, F.; Clemetsen, M.; Eik, L.O. Quantifying the Multifunctionality of Fjord and Mountain Agriculture by Means of Sociocultural and Economic Valuation of Ecosystem Services. Land Use Policy 2015, 48, 170–178. [Google Scholar] [CrossRef]
  77. Pachoud, C.; Da Re, R.; Ramanzin, M.; Bovolenta, S.; Gianelle, D.; Sturaro, E. Tourists and Local Stakeholders’ Perception of Ecosystem Services Provided by Summer Farms in the Eastern Italian Alps. Sustainability 2020, 12, 1095. [Google Scholar] [CrossRef]
  78. Schermer, M.; Bacher, M.; Tappeiner, U. Wer Will Welche Landschaft ?–Zur Konzeption von Kulturlandschaft in Nord-Und Südtirol. Agrarwirtsch. Agrarsoziol. 2011, 2011, 85–110. [Google Scholar]
  79. Schirpke, U.; Timmermann, F.; Tappeiner, U.; Tasser, E. Cultural Ecosystem Services of Mountain Regions: Modelling the Aesthetic Value. Ecol. Indic. 2016, 69, 78–90. [Google Scholar] [CrossRef]
  80. Lasanta, T.; Arnáez, J.; Pascual, N.; Ruiz-Flaño, P.; Errea, M.P.; Lana-Renault, N. Space–Time Process and Drivers of Land Abandonment in Europe. Catena 2017, 149, 810–823. [Google Scholar] [CrossRef]
  81. Rickebusch, S.; Gellrich, M.; Lischke, H.; Guisan, A.; Zimmermann, N.E. Combining Probabilistic Land-Use Change and Tree Population Dynamics Modelling to Simulate Responses in Mountain Forests. Ecol. Modell. 2007, 209, 157–168. [Google Scholar] [CrossRef]
  82. Terres, J.M.; Scacchiafichi, L.N.; Wania, A.; Ambar, M.; Anguiano, E.; Buckwell, A.; Coppola, A.; Gocht, A.; Källström, H.N.; Pointereau, P.; et al. Farmland Abandonment in Europe: Identification of Drivers and Indicators, and Development of a Composite Indicator of Risk. Land Use Policy 2015, 49, 20–34. [Google Scholar] [CrossRef]
  83. Abid Shahzad, M.; Fischer, C. The Decline of Part-Time Farming in Europe: An Empirical Analysis of Trends and Determinants Based on Eurostat Panel Data. Appl. Econ. 2022, 54, 4812–4824. [Google Scholar] [CrossRef]
  84. Sendyka, P.; Makovicky, N. Transhumant Pastoralism in Poland: Contemporary Challenges. Pastor. Res. Policy Pract. 2018, 8, 5. [Google Scholar] [CrossRef]
  85. Lombardi, G. Optimum Management and Quality Pastures for Sheep and Goat in Mountain Areas. In Sustainable Grazing, Nutritional Utilization and Quality of Sheep and Goat Products; Molina Alcaide, E., Ben Salem, H., Biala, K., Morand-Fehr, P., Eds.; Options Méditerranéennes: Série A. Séminaires Méditerranéens; n. 67; CIHEAM: Zaragoza, Spain, 2005; pp. 19–29. [Google Scholar]
  86. CIPRA International. Knowledge Transfer on the Co-Adaptation of Humans and Wolves in the Alpine Region. 2021. Available online: https://www.cipra.org/en/cipra/international/projects/completed/knowledge-transfer-on-the-co-adaptation-of-man-and-wolf-in-the-alpine-region/dateien/FinalReportCoadaptationHumans_Wolfs_Alps_CIPRA_en.pdf/@@download/file/210518_FinalReportCoadaptation (accessed on 12 October 2022).
  87. ASTAT. Beherbergungsbetriebe und Betten nach Kategorie. 2022. Available online: https://qlikview.services.siag.it/QvAJAXZfc/opendoc.htm?document=Tourismus.qvw&host=QVS@titan-a&anonymous=true (accessed on 15 October 2022).
  88. ASTAT. Zeitreihe zum Tourismus. 1950–2021. Available online: https://astat.provincia.bz.it/it/news-pubblicazioni-info.asp?news_action=4&news_article_id=667485 (accessed on 15 October 2022).
  89. Muñoz-Ulecia, E.; Bernués, A.; Casasús, I.; Olaizola, A.; Lobón, S. Drivers of Change in Mountain Agriculture: A Thirty-Year Analysis of Trajectories of Evolution of Cattle Farming Systems in the Spanish Pyrenees. Agric. Syst. 2021, 186, 102983. [Google Scholar] [CrossRef]
  90. Mazzocchi, C.; Sali, G. Assessing the Value of Pastoral Farming in the Alps Using Choice Experiments: Evidence for Public Policies and Management. J. Environ. Plan. Manag. 2019, 62, 552–567. [Google Scholar] [CrossRef]
  91. Mayer, M.; Kraus, F.; Job, H. Tourism-Driver of Change or Preserver of Alpine Culture and Landscape? Mitt. Osterr. Geogr. Ges. 2011, 153, 31–74. [Google Scholar]
  92. Holzner, W. Almen. Almwirtschaft Und Biodiversität; Böhlau Verlag: Vienna, Austria; Köln, Germany, 2007. [Google Scholar]
  93. Arnberger, A.; Muhar, A.; Sterl, P. Auswirkungen des Tourismus (ALP Austria Programm zur Sicherung und Entwicklung der alpinen Kulturlandschaft. Endbericht zum Teilprojekt 17). Available online: https://www.almwirtschaft.com/images/stories/fotos/alpaustria/pdf/ArnbergerMuharSterl_Tourimus.pdf (accessed on 23 October 2022).
  94. Bätzinger, W. Die Alpen. Das Verschwinden Einer Kulturlandschaft, 1st ed.; Wissenschaftliche Buchgesellschaft (wbg): Darmstadt, Germany, 2018. [Google Scholar]
  95. Herzog, F.; Seidl, I. Swiss Alpine Summer Farming: Current Status and Future Development under Climate Change. Rangel. J. 2018, 40, 501–511. [Google Scholar] [CrossRef]
  96. Tasser, E.; Walde, J.; Tappeiner, U.; Teutsch, A.; Noggler, W. Land-Use Changes and Natural Reforestation in the Eastern Central Alps. Agric. Ecosyst. Environ. 2007, 118, 115–129. [Google Scholar] [CrossRef]
  97. Lauber, S.; Erzog, F.; Seidl, I.; Böni, R.; Bürgi, M.; Gmür, P.; Hofer, G.; Mann, S.; Raaflaub, M.; Schick, M.; et al. Zukunft der Schweizer Alpwirtschaft. Fakten, Analysen und Denkanstösse aus dem Forschungsprogramm AlpFUTUR. Available online: https://www.dora.lib4ri.ch/wsl/islandora/object/wsl%3A10511/datastream/PDF/view (accessed on 11 October 2022).
  98. Battaglini, L.; Bovolenta, S.; Gusmeroli, F.; Salvador, S.; Sturaro, E. Environmental Sustainability of Alpine Livestock Farms. Ital. J. Anim. Sci. 2014, 13, 431–443. [Google Scholar] [CrossRef]
  99. Teston, M.; Orsi, M.; Bittante, G.; Cecchinato, A.; Gallo, L.; Gatto, P.; Mota, L.F.M.; Ramanzin, M.; Raniolo, S.; Tormen, A.; et al. Added Value of Local Sheep Breeds in Alpine Agroecosystems. Sustainability 2022, 14, 4698. [Google Scholar] [CrossRef]
  100. Garde, L.; Dimanche, M.; Lasseur, J. Permanence and Changes in Pastoral Farming in the Southern Alps. Rev. Géogr. Alp. 2014, 102-2, 13. [Google Scholar] [CrossRef]
  101. Hinojosa, L.; Lambin, E.F.; Mzoughi, N.; Napoléone, C. Place Attachment as a Factor of Mountain Farming Permanence: A Survey in the French Southern Alps. Ecol. Econ. 2016, 130, 308–315. [Google Scholar] [CrossRef]
  102. Strijker, D. Marginal Lands in Europe—Causes of Decline. Basic Appl. Ecol. 2005, 6, 99–106. [Google Scholar] [CrossRef]
  103. Bundesamt für Landwirtschaft BLW. Agrarbericht 2021. Available online: https://www.agrarbericht.ch/de/service/dokumentation/publikationen (accessed on 23 November 2022).
  104. Gervasi, V.; Linnell, J.D.C.; Berce, T.; Boitani, L.; Cerne, R.; Ciucci, P.; Cretois, B.; Derron-Hilfiker, D.; Duchamp, C.; Gastineau, A.; et al. Ecological Correlates of Large Carnivore Depredation on Sheep in Europe. Glob. Ecol. Conserv. 2021, 30, e01789. [Google Scholar] [CrossRef]
  105. Bautista, C.; Revilla, E.; Naves, J.; Albrecht, J.; Fernández, N.; Olszańska, A.; Adamec, M.; Berezowska-cnota, T.; Ciucci, P.; Groff, C.; et al. Large Carnivore Damage in Europe: Analysis of Compensation and Prevention Programs. Biol. Conserv. 2019, 235, 308–316. [Google Scholar] [CrossRef]
  106. Flykt, A.; Eklund, A.; Frank, J.; Johansson, M. “Landscape of Stress” for Sheep Owners in the Swedish Wolf Region. Front. Ecol. Evol. 2022, 10, 783035. [Google Scholar] [CrossRef]
  107. Bollmann, R.; Schneider, M.; Flury, C. Minimalnutzungsverfahren zur Offenhaltung der Kulturlandschaft. Agroscope Sci. 2014, 7, 1–57. [Google Scholar]
  108. Perino, A.; Pereira, H.M.; Navarro, L.M.; Fernández, N.; Bullock, J.M.; Ceauşu, S.; Cortés-Avizanda, A.; Van Klink, R.; Kuemmerle, T.; Lomba, A.; et al. Rewilding Complex Ecosystems. Science 2019, 364, 351. [Google Scholar] [CrossRef]
  109. Broughton, R.K.; Bullock, J.M.; George, C.; Gerard, F.; Maziarz, M.; Payne, W.E.; Scholefield, P.A.; Wade, D.; Pywell, R.F. Slow Development of Woodland Vegetation and Bird Communities during 33 Years of Passive Rewilding in Open Farmland. PLoS ONE 2022, 17, 1–19. [Google Scholar] [CrossRef]
  110. Kriechbaum, M.; Splechtna, B.; Pennerstorfer, J.; Pröbstl, F.; Seiberl, M. Biodiversität Und Alpwirtschaft. In Gutachterliche Stellungnahme zu den Auswirkungen von Rückkehrenden Wölfen auf Landwirtschaft und Traditionelle Weidehaltung, Freizeit- und Erholungswirtschaft, Jagd-Und Forstwirtschaft Sowie; Hackländer, K., Daim, A., Bayer, K., Kantelhardt, J., Hinterseer, A., Niedermayr, A., Kapfer, M., Pröbstl-Haider, U., Mostegl, N., Schlegel, A., Eds.; BOKU-Berichte zur Wildtierforschung und Wildbewirtschaftung 23; Universität für Bodenkultur: Vienna, Austria, 2019; pp. 353–386. [Google Scholar]
Figure 1. Upper left: Location of South Tyrol in the Alps. FR = France; CH = Switzerland; DE = Germany; AT = Austria; SI = Slovenia; IT = Italy Large figure: Distribution of summer pastures and proportional distribution of sheep stock on these pastures. Potential area = 2.2% of total.
Figure 1. Upper left: Location of South Tyrol in the Alps. FR = France; CH = Switzerland; DE = Germany; AT = Austria; SI = Slovenia; IT = Italy Large figure: Distribution of summer pastures and proportional distribution of sheep stock on these pastures. Potential area = 2.2% of total.
Sustainability 15 07355 g001
Figure 2. Development of small ruminant farms and stock number over the last 40 years in South Tyrol.
Figure 2. Development of small ruminant farms and stock number over the last 40 years in South Tyrol.
Sustainability 15 07355 g002
Table 2. Overview of the expert interviews conducted between January 2022 and February 2022.
Table 2. Overview of the expert interviews conducted between January 2022 and February 2022.
ExpertProfessional ExpertiseFunctionYears of Expertise
1mountain economy, agricultural subsidy schemes, agricultural politicsCollaborator Provincial Office for Mountain Economy35
2livestock husbandry, agricultural subsidy schemesManagement Position Provincial Office for Livestock Breeding25
3natural resource management, alpine ecologyProfessor for Alpine Ecology and Landscape>30
4small ruminant breeding, markets and trendsManagement Position Small Ruminant Breeders’ Association31
5mountain farming, livestock husbandry, agricultural subsidy schemes, agricultural politicsManagement Position Mountain Farming Advisory Council>40
6rural development, socio-economy in mountain areas, agritourismProfessor for Economic Geography21
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Stauder, J.; Meimberg, H.; Kriechbaum, M. An Exploration of Drivers for Abandonment or Continuation of Summer Pasture Grazing in South Tyrol, Italy. Sustainability 2023, 15, 7355. https://doi.org/10.3390/su15097355

AMA Style

Stauder J, Meimberg H, Kriechbaum M. An Exploration of Drivers for Abandonment or Continuation of Summer Pasture Grazing in South Tyrol, Italy. Sustainability. 2023; 15(9):7355. https://doi.org/10.3390/su15097355

Chicago/Turabian Style

Stauder, Julia, Harald Meimberg, and Monika Kriechbaum. 2023. "An Exploration of Drivers for Abandonment or Continuation of Summer Pasture Grazing in South Tyrol, Italy" Sustainability 15, no. 9: 7355. https://doi.org/10.3390/su15097355

APA Style

Stauder, J., Meimberg, H., & Kriechbaum, M. (2023). An Exploration of Drivers for Abandonment or Continuation of Summer Pasture Grazing in South Tyrol, Italy. Sustainability, 15(9), 7355. https://doi.org/10.3390/su15097355

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop