Scenarios of bioenergy provision: technological developments in a landscape context and their social...
Transcript of Scenarios of bioenergy provision: technological developments in a landscape context and their social...
Scenarios of bioenergy provision: technologicaldevelopments in a landscape context and theirsocial effects
Anja Starick • Ralf-Uwe Syrbe • Reimund Steinhaußer •
Gerd Lupp • Bettina Matzdorf • Peter Zander
Received: 11 March 2013 / Accepted: 14 October 2013� Springer Science+Business Media Dordrecht 2013
Abstract While it is developing rapidly throughout Germany, bioenergy provision is open
to different development opportunities. To understand the cause–effect relationships that
drive bioenergy development and explore different development options and their effects on
regional development, qualitative scenarios have been drafted using the Gorlitz district as an
example. The paper introduces the scenario method, with scenarios that are expressed in
storylines. Driving forces and their relationships are thereupon reflected. The results show
that the relation of the Common Agricultural Policy and Renewable Energy Act is of par-
ticular importance for future development in general. For the specific type of development in
particular in rural regions, technologies are equally important, as they allow for both strongly
central and highly decentralised developments. Due to an increasing diversity of options, the
decision between central and decentral developments is, however, less technologically
determined, but rather dependent on stakeholders’ decisions. Such stakeholders not only
include stakeholders from the production sector, but also include consumers and affected
parties, particularly the inhabitants whose living environment is changing rapidly. Both the
landscape and society are subject to change. As a major driving force and an impacted system
under change itself, social constellations must be taken into account to ensure a sustainable
development under the signs of renewable energy expansion. Management tools should
consider the interlinkage between landscape, energy, and social systems.
Keywords Renewable energies � Social impact � Stakeholder �Regional development � Impact assessment � Germany
A. Starick (&) � B. Matzdorf � P. ZanderInstitute of Socio-Economics, Leibniz-Centre for Agricultural Landscape Research (ZALF),Eberswalder Str. 84, 15374 Muncheberg, Germanye-mail: [email protected]
R.-U. Syrbe � R. SteinhaußerLandscape Change and Management, Leibniz Institute of Ecological Urban and Regional Development(IOR), Weberplatz 1, 01217 Dresden, Germany
G. LuppSchlossstrasse 8, 79211 Denzlingen, Germany
123
Environ Dev SustainDOI 10.1007/s10668-013-9495-4
1 Introduction
Increasing renewable energy supplies is a main social objective in Germany that is
politically encouraged and financially supported (cp. e.g. BWT and BMU 2007; BMELV
and BMU 2009; BRD 2010; Renewable Energy Act (REA)). In this framework, bioenergy
as storable energy plays an essential role, but its role is not undisputed (Kaphengst 2009). It
is not known how further expansion of bioenergy will take place and how it will affect
regional development. Recent subsidy policy is related not only to technical facilities but
also affects land use around power plants. The total amount of German cropland devoted to
growing energy plants has quintupled within the last decade. Currently, approximately two
million hectares of farmland are used to grow energy crops (FNR 2012). Both the future
construction of biopower plants and the increased cultivation of energy crops will inevi-
tably have serious spatial consequences and either positive or negative effect on regional
ecosystem services (Lupp et al. 2011; Starick et al. 2011; Rowe et al. 2009; Wiehe et al.
2009; Ammermann 2008).
In the face of spatial and environmental challenges and uncertainties concerning further
development, responsible authorities at the state, regional, and local levels seek deeper
insight into expected regional developments and direction about how they can guide
bioenergy development to maintain their regional characteristics and enhance their eco-
nomic competitiveness and social balance. Attention to these issues is an interesting
starting point for discussion of future planning and regional development in general (cp.
Leibenath and Otto 2012).
In a current research project, these issues are approached through exploratory qualitative
scenarios for the future development of bioenergy supply in a spatial context and on a regional
scale. The scenarios make it possible to examine potential developments and investigate the
possible future consequences of various development options. The scenarios and the scenario
process behind them also permit a deeper understanding of the cause-and-effect relationships
involved. On this basis, key control mechanisms can be identified that consider uncertainty in
land use decisions for sustainable regional development. The scenario process can initiate a
social learning process among stakeholders and inhabitants in general (cp. Alcamo 2008) and
facilitate the decision-making of stakeholders (Soliva 2009; Sohl et al. 2010). Specifically, in
the current study, scenario construction and a comprehensive view of the future as repre-
sented by the scenarios are used for the following purposes:
1. To gain knowledge about upcoming developments in bioenergy provision and the
mechanisms behind these developments,
2. To understand the effects of these developments on a region and discuss development
options,
3. To assess the impacts on ecosystem services in greater detail, and
4. To identify control and management mechanisms.
For these purposes, a scenario is not understood as a future forecast but rather as a
description of ‘‘how the future may unfold based on ‘if–then’ propositions and typically
consists of a representation of an initial situation and … the key-driving forces and
changes that lead to the particular future state’’ (Alcamo 2008). The scenarios represent
possible outcomes under specific settings and with specific interdependencies (cp. Starick
et al. 2011). ‘‘Scenarios show what potentially could happen in the future as a result of
policy or environmental change’’ (Sohl et al. 2010).
The application of the scenario technique to environmental concerns became quite popular
in the last decade (MA 2005). There are well-elaborated methods for environmental scenarios
A. Starick et al.
123
based on land use models (e.g. Sohl et al. 2010), expert assessments (e.g. MA 2005; Artner
et al. 2006), and participation (e.g. Walz et al. 2007). In the context of new technologies that
quickly change our landscapes and conflicting climate change and nature conservation
concerns, a more complex scenario framework is recommended (Alcamo 2008).
Bioenergy provision has been intensively analysed in scenario studies at the interna-
tional (e.g. IEA 2009), national (e.g. Thran et al. 2011; SRU 2011), and regional levels
(e.g. DREBERIS 2012; Scheuermann et al. 2012). However, all these scenarios work
primarily with quantitative forecast methods. For public discussion at the regional level,
we need qualitative descriptions that are focused on the social and spatial implications of
increased bioenergy production. Starick et al. (2011) developed qualitative scenarios using
the example of Western Saxony. These scenarios focus on the interaction between tech-
nologies and landscape conditions alone and do not analyse the interaction of different
driving forces. These scenarios do allow the analysis of environmental impacts but restrict
the explanation of developments, particularly in terms of social implications.
To address the shortcomings of existing scenario methodologies, Syrbe et al. (2013)
developed a combined methodological framework for scenario construction at the interface
of technological requirements and environmental concerns. This framework combines
participatory scenario construction with expert assessments. To include the broad set of
factors that influence regional development, we tested Syrbe et al.’s (2013) scenario
framework in this study and applied it to the topic of regional bioenergy use. We advanced
it to include the social dimension of spatial developments (cp. van Drunen et al. 2011).
In this paper, we introduce the scenarios. We discuss what we have learnt about the role
of the conditions identified and their interactions in future regional development. We
reflect upon the upcoming developments suggested by the scenario process, and we
investigate the effects for a region and for its society in particular. We thereby address the
first and second purposes of the scenarios. In addition, we draw conclusions concerning the
transferability of the scenario method and the results obtained. Future challenges for
shaping bioenergy in a sustainable way are identified.
2 Methods
Using Syrbe et al.’s (2013) framework, scenarios were developed through interaction with
external experts and regional stakeholders (Table 1). The basic qualitative approach
consists of seven steps (Fig. 1) and is implemented using an argumentative methodology
based on the identification of cause-and-effect relationships. The qualitative approach is
complemented by a quantitative analysis of existing data. The quantitative analysis plays a
supporting role in answering questions that arose during the qualitative process and thereby
supported the discussions with and between the stakeholders. Therefore, successive
translations of the results between quantitative and qualitative terms were necessary
(Carpenter et al. 2006; Houet et al. 2010). These translations included representing the
existing land use distribution, climate predictions, and forecasts of demographic devel-
opment by descriptions, illustrations, and maps. In addition, the areal requirements for
supplying bioenergy plants with raw materials were calculated based on the amount of raw
material needed by a certain type of plant, the possible crop yield, and crop rotation
according to the code of good practice.
The following describes the implementation of the seven steps in this study.
The first step was deciding the main issues to be addressed, i.e. how increased bioenergy
provision can develop in a rural region and what social and ecological effects it might cause.
Scenarios of bioenergy provision
123
The factors that determine the development of bioenergy provision were selected in the
second step. A literature review was conducted, geographic data for the study area were
analysed, and experts and stakeholders were identified and invited to workshops or visited for
interviews. (cp. Table 1). The driving forces identified (and their underlying trends) were
then classified as exogenous or endogenous factors (cp. Starick et al. 2011) and were also
classified according to the degree of abstraction. Based on this classification scheme, the
factors that informed the scenarios were selected by an expert panel in a two-step voting
process, followed by a workshop discussion among members of the project team, stake-
holders, and experts. The factors selected were differentiated into three groups: fixed factors,
dynamic factors, and key driving forces. Fixed factors and dynamic factors, such as climate
predictions and demographic development, are assumed to be the same for all scenarios. Key
Table 1 Participation working steps for the development of energy plant scenarios in the Gorlitz district (ifnot mentioned otherwise, participation included experts and stakeholders)
Year Participation/working step Results
2010 World Cafe Aims of scenario development, main drivers
Expert work (literature review) Driving forces, trends, technological options
2011 Expert workshop Selection of drivers, trends, scenario directions
2011 Interviews and surveys Technological lines, stakeholders’ motivations
Expert work (text elaboration, G.I.S., models) Storylines, areal demand of biogas plants
2011 Expert workshop Review of the trajectories and the storylines
2011 Scenario mapping workshop Maps of the three scenarios
2012 Milestone workshop Discussion of scenario results
2012 Off-the-record talks Inclusion of agricultural expertise
2013 Guideline workshop Conclusions for the future
4 State and trajectories
Spatial, policy and literature analysis; interviews
3 Scenario logic Literature and expert based collection, classification, prioritisation and selection
2 Driving forces Literature and expert based collection, classification, prioritisation and selection
1 Main question Policy and literature analysis
Step Task Methods
5 Synthesis Analysis of causal relationships, network analysis, storylines, spatialisation
6 b Impact assessment
Risk analysis, interviews
6 a Interpretation Hermeneutic approach
7 Communication Interviews, workshops, newspaper articles, action guidelines
Fig. 1 Scenario framework adapted from Syrbe et al. (2013) and methods applied to each step
A. Starick et al.
123
driving forces shape the future in several ways, depending on their specific expression, and
are key to distinguishing among different scenarios (the third step). Key driving forces
include the Common Agricultural Policy (CAP), the REA, technologies, and actors.
Based on the results of an initial literature review, the possible future developments of
all factors were identified and driving forces were roughly defined. For the sake of logical
consistency, these future developments were combined into three different scenarios that
represent hypothetical but realistic developments. By means of in-depth policy, document,
and stakeholder analyses conducted using existing scenarios, trend analysis, and inter-
views, the future appearance of the factors and possible expressions of the key driving
forces were determined and described in greater detail (the fourth step). The time horizon
for the projections extends to the year 2020. The resulting profiles for the future expec-
tations for all factors were presented both in pamphlet form and in an opening lecture in the
scenario workshops.
In the fifth step, the scenarios were synthesised on the basis of the anticipated inter-
action of the driving forces up to the year 2030. The synthesis was conducted by means of
storylines (cp. Stocker et al. 2012). Storylines outline the plausible interaction between
driving forces und interpret them in the form of a comprehensive narrative. The narrative
describes a state. The final consistency of the storylines was tested and advanced in a
workshop that focused on the spatial consequences.
The last two steps in the scenario development consisted of evaluation and communi-
cation. The evaluation (sixth step) was divided into two subtasks. The first subtask was an
evaluation of the effects of interactions among the factors on the scenarios and their
implications for regional development and society. The second subtask was an evaluation
of the environmental impacts on ecosystem services. Communication was a process
throughout the study rather than a single step and included interviews, workshops, and
discussion of guidelines.
The following describes in more detail how the key driving forces were projected into
future.
Technological lines of development were investigated through a literature review (i.e.
Starick et al. 2011; Thran et al. 2010; Wietschel et al. 2010), expert lectures (i.e. Billig
et al. 2011; Grundmann 2010), and semi-structured interviews with seven bioenergy plant
operators, representing a spectrum of plant sizes,1 ownership and land use connectivity,2
and types.3 The interviews were recorded and transcribed. The contents were categorised
and subjected to a content analysis using MaxQDA, a software package for qualitative and
mixed methods’ data analysis (cp. VERBI 2013).
A stakeholder analysis was carried out as ongoing part of the participative process. We
used the expertise of our practice partners and snowball sampling to identify groups of
stakeholders who affect the future development of bioenergy provision and who are
affected by the landscape changes it causes (cp. Reed et al. 2009). Following Chevalier and
Buckles’s (2008) rainbow diagram, we formed three focus groups: farmers and plant
operators; land use, planning, and development authorities; and authorities and non-gov-
ernmental organisations engaged in environmental protection and landscape management.
Their interaction and their knowledge, attitudes, and activities were investigated in 23
1 including small facilities with a capacity of 150–500 kW, medium facilities with capacities up to 2 MW,and large facilities with capacities up to 20 MW.2 companies with international, national, and regional markets, municipal operators, and agriculturalenterprises.3 heating plants, biogas and biogas injection facilities.
Scenarios of bioenergy provision
123
additional semi-structured interviews with representatives of these groups. Trends that
emerged from the interviews were aligned with prospective studies (i.e. Opaschowski
2008) and studies on environmental awareness (i.e. BMU 2008).
On 12 October 2011, the European Commission presented a CAP reform proposal for
the period 2014–2020 to support food security, sustainable management of natural
resources, and rural territorial balance in the EU (EC 2011). This reform proposal served as
the baseline for our projections. Some caveats of the proposed reform were formulated by
Bureau (2012), who denounced the budget remaining high, while fundamental inconsis-
tencies in the current CAP remain in effect. In particular, the issue of reorienting the CAP
budget towards the provision of public goods remains unresolved. According to Bureau
(2012), ‘‘as explained by Mahe (2012), conditioning large payments to good practices … is
a high-cost policy compared to payments directly targeting public goods. Some other
criticisms could be made of the proposal. For example, maintaining two pillars, one
requiring cofinancing and the other not, will also maintain the bias against environmental
payments, which need to be matched with domestic funds’’. Therefore, local stakeholders
were asked whether the objectives of free trade, a highly competitive European agricultural
sector, and a high priority on public goods might not be better and more cheaply achieved
in a different policy setting.
Similarly, the Renewable Energies Act and the associated sublegal regulations were
analysed with a focus on bioenergy. The time frame was perfect for that analysis because
an amendment process was ongoing during the project period. Thus, it was possible to gain
insights into the parliament’s legislative process and follow the debate in parliamentary
transcripts (i.e. DB 2011a), white papers (i.e. DB 2011b), and conferences (i.e. Dreher
2011). This process also included interviewing stakeholders, such as researchers and
representatives of environmental NGOs. Furthermore, REA-monitoring papers (i.e. BMU
2011) were used in the analysis, as were papers containing requests from environmental
organisations concerning the use of renewable energies.
The development options identified in these investigations were intensively discussed in
various stakeholder fora, and ultimately, three alternatives for each driving force
crystallised.
3 Description of the case study
The scenarios were developed using the example of the Gorlitz district in Saxony. The
district is a rural area in the south-eastern part of Germany, neighbouring Poland and the
Czech Republic. It is home to a Slavic minority (the Sorbs). The northern part of the
district is sparsely populated; the largest town is Gorlitz, with approximately 55,000
inhabitants. Larger towns outside the Gorlitz district whose potential catchment areas for
biomass reach the district are Dresden and Berlin. The southern part of the district is
formed by rolling hills with moderately fertile soils that are used agriculturally. The
landscape is open, with woodlands in wide areas restricted to mountain tops, thus forming
recognisable landmarks. The northern part of the district is less hilly and features soils of
low fertility. In addition to farmland and forests, fish ponds and brown coal mining areas
are important land use structures. Approximately half of the agricultural land is used by
independent farmers, and half is used by a wide variety of farmers’ cooperatives and larger
agricultural enterprises. On average, the size of a farm is 1000 hectares. Overall, the
economy of the district is built on small- and medium-sized businesses.
A. Starick et al.
123
4 Results
4.1 Scenario frame conditions
The key driving forces distinguish the scenarios as described below:
• The promotion of renewable energy (by the REA) provides a guaranteed feed-in tariff
for power that is generated from renewable resources. For the future, we made the
following assumptions: first, that the REA will continue with declining financial
support, the utilisation of manure will be supported, and the utilisation of maize will be
limited; second, that the policy will improve the degree of support for its directives in
the spirit of sustainability, promoting, for instance, a positive greenhouse gas balance,
new energy crops, crop rotation, and substantial use of self-produced raw materials,
waste materials, and landscape conservation materials; and third, that the objectives
will shift away from bioenergy (cp. Leopoldina 2012) and away from financial support.
• The trend projection of the CAP is based on the CAP proposal for the EC.
Alternatively, two more extreme development paths were developed: payments only
for ecosystem services with a complete shift in funding resources from the first to the
second pillar of the CAP (‘‘greening’’) and the total cessation of any support.
• With respect to technologies, the projections were separated according to the
dominant bioenergy plant size. For the first projection, it was assumed that
development would be driven by process innovation and improvements in efficiency
and that this development would be accompanied by an increase in plant size. For the
second projection, it was assumed that small bioenergy plants would be profitable, as
mass production will lead to decreasing prices and technological innovations will lead
to a diversification of facility types. For the third projection, it was assumed that,
above all, large solutions will remain profitable and demand large-scale industrial
facilities.
• The engagement of regional actors is the final driving force. For the projection, three
existing trends were considered: first, the majority of actors will remain passive, and
stakeholders in the field of bioenergy provision are not numerous and act in a diffuse
and sporadic manner; second, a sense of homeland (‘‘Heimat’’), awareness of the
opportunities a regional economy offers, and a desire for steady energy prices will
motivate actors to cooperate and create local networks to provide and distribute
bioenergy on local and regional scales. Third, an international energy provider will
enter the region to extract biomass; this provider will offer incentives for farmers to
cooperate.
4.2 Storylines
The four key driving forces and their three alternatives can be combined in 81 (34) ways.
Within the scenario process, it proved to be impracticable to discuss such a large number of
cases. In addition, not all the combinations are logically consistent, and some were seen to
be politically implausible. Therefore, the expert panel chose three scenario trajectories that
represented the extremes of possible developments and encompass all 12 alternatives for
the driving forces (Fig. 2):
• The ‘‘Trend’’ scenario represents the four business-as-usual conditions. This scenario is
considered an extension of all key driving forces. However, this scenario does not
Scenarios of bioenergy provision
123
express a linear trend. Newly arising modifications must be considered, namely the
CAP 2014-2020 draw. Other factors are assumed to change only slightly.
• The ‘‘Decentral’’ scenario combines sufficient support and political conditions directed
at environmental protection and sustainability with a motivated population making use
of a variety of small-scale bioenergy plants.
• The ‘‘Central’’ scenario assumes that a decreasing political influence mainly benefits
the strongest economic parties, which can survive without subsidies and which will set
the agenda.
As a result of the interaction between the selected drivers, the final storylines of the
scenarios describe the following developments of bioenergy provision in the social and
spatial context of the Gorlitz district.
4.2.1 ‘‘Trend’’ scenario
The ‘‘Trend’’ scenario anticipates habitual behaviour by the stakeholders. Although various
stakeholder groups appear around the bioenergy value chain, there is little local or regional
cooperation. Residents remain partly unaffected by questions of bioenergy provision,
although more than half of population expresses environmental concerns. However, the
key players’ interest in using biomass for energy provision grows. The key players are, first
and foremost, farmers, particularly members of farmers’ cooperatives with livestock.
Municipalities and local power companies also play important roles in bioenergy provi-
sion. Overall, the stakeholders’ activities are rather selective; however, their commitment
increases. Large-scale investors from outside the region are faced with scepticism.
Driven by the technological options and the policy on subsidies, a further expansion of
established technologies takes place. Although growth slows down, approximately 30
additional agricultural bioenergy plants with capacities of up to 750 kWel are built and
operated. These new plants are located closer to villages and industrial sites. In addition, up
to 20 new combined heat and power plants (CHPP) are favoured, primarily small muni-
cipal facilities that are erected in the northern part of the district. Through local grids, both
types of technologies contribute to the provision of heat, for which there is strong demand.
Scenario “Trend” Scenario “Decentral” Scenario “Central”
C AP updating without major changes
advancement with greening
no funding
R E A updating without major changes
funding with increased sustainability requirements
no funding
Techno-l og i e s
establishment of approved techno-logies, process innovation
enhancement and diversification of small plants
ascendance of large facilities
A c t or s no particular regional commitment
establishment of regional actor networks
appearance of a major investor, development of supraregional networks
Fig. 2 The alternative expressions of the key-driving forces shaping the scenarios
A. Starick et al.
123
Similarly, the flexible provision of energy is increasingly demanded. The production and
feeding of biomethane into the natural gas network thus plays an important role and is
accomplished by two additional large plants.
Overall, bioenergy provision requires more substrate and a greater share of forest and
cropland, as more than the entire forest area is needed to generate the necessary firewood,
leaving stem wood for construction purposes. Thus, public forests are used more inten-
sively, and the forest area increases. Approximately two-fifths of the arable fields are
planted with energy crops in alternating rotations. Maize remains the most abundant biogas
crop; however, future legislation will require planting of alternative crops such as legumes,
grass, and other perennials. The overall structural diversity is reduced by larger and more
intensively cultivated fields with more fast-growing crops that resemble plantations during
the summer months. This development dominates the appearance of the landscape in prime
locations, where several farmers leave the CAP system and cultivate energy plants in
monocultures. In contrast, structural diversity is enriched by a slightly higher diversity of
crops and more landscape elements, such as groves and hedgerows. Moreover, farmland
strongly features technical facilities such as silos, bioenergy plants, energy networks, and
stables.
4.2.2 ‘‘Decentral’’ scenario
Major changes in the conditions set by the reform of the CAP and REA require social and
economic adjustments. In the context of a peripheral rural region with a low population
density, these changes lead to an initial setback in development of bioenergy provision.
The multitude of small-scale technologies and utilisable raw materials will thereafter be
increasingly used by a population that seeks alternative ways of life and sources of income
and is ready to take action. The inhabitants are increasingly involved in bioenergy pro-
vision. This involvement is supported by the establishment of service relationships, energy
cooperatives, and, consequently, networks. The combination of remnant collection, raw
material provision, and energy processing and use forms the backbone of regional
development of provision of power, particularly heat. Farmers, foresters, and municipal
power providers are the heart of this process, with farmers and foresters operating busi-
nesses and providing services such as harvesting and processing. They become an integral
part of rural society and culture.
As a result, the scenario involves approximately the same number of new bioenergy
plants as the ‘‘Trend’’ scenario. Overall capacity, however, is lower. Altered decentralised
technologies, including fuel cells, power–heat cogeneration, biomethane injection and
gasification plants, and ORC technologies, are applied. Networks extend to the storage and
distribution of energy, regional energy exchanges, and establishment of smart grids.
A few agrarian companies in prime locations leave the CAP system as the payments for
ecosystem services do not compensate them for the effort and the losses associated with the
related environmental measures at highly profitable sites. In contrast, the majority of
farmland is dedicated to a combination of agricultural production and landscape preser-
vation. Often, agri-environmental measures are combined with biomass production. A
praxis innovation regarding cultivation methods is promoted. In addition, traditional cul-
tivation systems, such as agroforestry systems following the historic hoof-shaped clearings
(‘‘Waldhufenflur’’), are reactivated. Both systems permit multiple uses of farmland. On the
other hand, due to extensification and a wider range of crops, such as flowering plants,
permanent crops, legumes, girasol, and clover, more land is required for biomass
production.
Scenarios of bioenergy provision
123
Consequently, land is used in a differentiated manner, providing space for richer and
more numerous structural elements. The portion of groves within the landscape increases.
Wood is particularly mobilised in private forests, where marginal wood products are also
extracted. Part of the system is landscape utilisation for recreational and tourist activities.
Because the system absorbs biomass from the whole region, there are few resources
available for large plants.
4.2.3 ‘‘Central’’ scenario
The ‘‘Central’’ scenario describes a development within which the willingness to sell land
increases. Several farmers and farmers’ cooperatives do not survive the increased com-
petition. A few farmers’ cooperatives expand in the southern part of the region. A bi-
omethane feed-in plant of industrial size (20 MW) is erected and operated by a syndicate.
The northern part is affected by supraregional interests. Large-scale investors are attracted,
including agricultural enterprises and an international energy provider, whose activities are
targeted at supplying the heating plants in the Berlin–Brandenburg region with woody
biomass. Agricultural and forestry enterprises and the wood-processing industry gradually
become important partners of this energy provider. Additionally, new enterprises are
founded, which provide cultivation techniques and offer cultivation services. The energy
provider establishes business relationships with these enterprises. For example, the pro-
vider leases land from insolvent farmers’ cooperatives, which, in return, cultivate the land
for the provider. The energy provider contracts agricultural enterprises for the plantation
and maintenance of short-rotation coppices, to which 30–50 per cent of the farmland is
allocated. The energy provider also cultivates land on reclamation sites.
The consequence of these developments is a strong demand for wood and maize. As a
result, wood is grown in short-rotation coppices on a large scale, particularly in the
northern part of the region. Infertile and reclamation sites are partly reforested. Forests are
partly managed as energy wood plantations and thus are progressively segregated into
forests that are devoted to productive, conservational, or recreational purposes. The pro-
portion of open-country landscape area decreases. In the southern part of the region,
sorghum and cup plant are grown alongside maize. Site conditions are optimised for large-
scale production. Only large nature reserves are unaffected by these intensification trends.
Overall, development that segregates agricultural landscapes marked by industrial-style
intensive production and traditional cultural landscapes is fostered.
5 Discussion
The scenarios describe the broad range of future development options at the interface of
bioenergy provision, regional, and landscape development, and society. In this section, we
discuss what we have learnt from the scenario process and the results. In particular, for
insights into the technologies, we draw on the findings from the projection of this driving
force. We discuss the effects of an increased bioenergy supply on regional development
and society. Generalisable challenges for shaping future development are noted.
5.1 Effects of the key drivers
Reflecting on the scenario process and the storylines, the landscape is observed to undergo
dramatic transitions in all cases (cp. Nadai van der Horst 2010).
A. Starick et al.
123
The four key driving forces were shown to have an intense interaction. At the same
time, all the driving forces function independently (cp. Lambin and Meyfroidt 2010).
Combinations other than those chosen are possible. The driving forces have strong,
although different, effects. The CAP and the REA have the most notable effects on the type
and intensity of agricultural production and the intensity of the renewable energy supply.
The relationship between CAP and REA subsidies and the corresponding requirements are
particularly important for future development. In certain cases, farmers may leave the CAP
support scheme due to unfavourable environmental demands and rely solely on REA
subsidies. Nonetheless, technologies have the stronger effect on the type of regional and
landscape development. In particular, technologies drive either more centralised devel-
opment or decentralised development.
5.2 Technological trends and the implications for regional development
As the investigation of the driving forces reveals, the differentiation effect of the tech-
nologies is due to a broad range of technological opportunities that continues to develop.
This broad range permits the following (cp. Szarka et al. 2013):
• provision of various types of energy or energy carriers, including electric power, heat,
gas, and petrol
• processing of various primary products from annual crops and wood products to
residues and waste
• various types of transformation (e.g. pyrolysis, gasification, fermentation, and
combustion)
• small facilities with capacities of several kilowatts (e.g. to supply heat for individual
houses) to large facilities with capacities of several hundred megawatt (e.g. to supply
heat for entire towns)
The type of development differs for large and small facilities. A few selected trends and
their implications for regional development, which have informed the projections of the
technologies and their interaction with other driving forces, are discussed below.
With respect to small facilities, the development of technologies themselves and thus
technological differentiation are particularly noticeable. Therefore, (creative) solutions
appropriate to the type of demand and independent of supraregional market prices are
possible and are particularly worthwhile in rural areas with low population densities.
Typically, small facilities can be installed on the basis of the existing infrastructure.
However, such facilities often require and support new cooperative structures at the local
and regional levels. Above a certain number of facilities, they also require the additional
installation of district heating networks, conversions to the power grid, and amendments
for energy trading. These requirements entail the allocation of an equivalent number of
sites for facilities and may have a concentrating effect on the local landscape, as typical
catchment areas range from 10 to 35 kilometres distance.
The development of larger facilities is supported by improvements in the processing of
primary and intermediate products, such as the processing of biogas for the feeding into the
natural gas grid. In addition, high-energy-density pellets are available and can be trans-
ported profitably over long distances, so they can be offered on supraregional markets.
Consequently, larger facilities are frequently biogas injection plants, biomass heating
plants, and coal heating plants that are partly fuelled by woodchips and pellets. The
existing infrastructure and logistics and the know-how and realisation potential of the
present large energy suppliers are used. On the other hand, an expansion of infrastructure
Scenarios of bioenergy provision
123
networks may be required. The technologies allow for energy storage and, theoretically, for
an energy supply based on demand. These technologies are comparatively efficient.
Because they rely on large catchment areas for the supply of primary products, they have
far-reaching effects on land use and the landscape. Trends towards contracting farmers and
towards environmental or sustainability standards and agreements are observed with
medium- and large-sized facility operators.
As a result, both large and small facilities offer reasonable solutions for future. In rural
areas in particular, both solutions are feasible. From a technical point of view, how they
play against each other is an open question. Over time however, one solution precludes the
other in a particular region, due to limited resources and infrastructure requirements.
Beyond the competition between food production and bioenergy supply, the realisation
of the broad range of technological opportunities on a supraregional scale can, for instance,
mean increasing competition for raw materials and land in a particular region. This might
happen when the number of facilities increases and more stakeholders assert claims. It
moreover might happen in places where catchment areas of different sizes overlap. Not
least, competition arises when the regional catchment areas of small facilities interfere with
the supraregional catchment areas of large facilities within the same region (cp. Figure 3).
As an operator of a large biogas plant explains:
‘‘As far as I know, such a plant will not be built any more [by our company; inference
by the author]. Because […] the disadvantage is that […] you have to bring together
this amount of primary products, that is obvious. This is, however, not so easy
everywhere. As I said, we are lucky because here is the land, here is Poland–here it
POLAND
CZECH REPUBLIC
Berlin
GÖRLITZ
DISTRICT
Dresden
catchment area of different bioenergy plants
POLAND
Berlin
GÖRRLLIITTZZ
DISTRICTT
Dresdennn
CT
legend: motorway border major city
Fig. 3 The Gorlitz district in asupraregional context andexamples of overlappingcatchment areas (here those of anestablished small agriculturalbiogas plant, a future medium-sized biomethane injection plant,and a possible large-sized heatingplant)
A. Starick et al.
123
does still work. Elsewhere, things appear to be worse. And as I said, [small agri-
cultural; inference by the author] biogas plants currently spring up like mushrooms.
So there is, of course, a certain competition for saving the raw materials. And then it
is, of course, not so easy, to build up such a park again and to ensure all of this. That
is pretty clear.’’
Once resources are allocated and infrastructure is partially enhanced either way, the
resulting spatial conditions predetermine further development.
5.3 Social effects of the technologies
5.3.1 Diversification and increasing complexity
In either case, technological development causes a diversification of value chains. The
logistics become more complex. With the construction of larger facilities, the cultivation
and processing of primary products leaves in-house production and is outsourced. Almost
in parallel, the differentiation and maturing of technologies results in a specialisation of the
production and service sectors. Figure 4 shows the logistical model of an older large biogas
plant that is similar to the in-house model of a small agricultural biogas plant. Figure 5
shows a rather complex model of a new medium-sized biomethane injection plant. This
model includes cross-border relationships such as contracting and consulting with Polish
farmers by an operation syndicate, harvesting and transportation of biomass by a logistics
company, ensilage in leased silos, processing and distribution of the biomethane, provision
of power and heat via block heat and power plants, and, ultimately, the application of the
digestate in the fields. Diversity is further increased by the entry of international energy
suppliers into the renewable energies’ market.
Consequently, technological development results in increases in the number and diversity
of stakeholders (cp. Bagliani et al. 2010). This is particularly evident with respect to plant
operators, who are no longer solely stakeholders primarily from the agricultural sector.
This makes the constellation of actors more complex, in the area under investigation in
particular, as land owners are seldom the land users. The relation between owners and
users covers a wide range, from neighbourhood relationships and owners’ attachment to
land uses to regional absence and a lack of attachment to land uses.
Due to its broadness, diversity, and complexity, technological development also rep-
resents additional new options for stakeholders. This is particularly obvious with respect to
farmers, who must choose among various economic options and partnerships with various
interested parties. Thus, they must reconsider their original self-concepts and readjust their
100 km
cultivation
Vertrag über die Lieferung von Mais
Der Vertragsnehmer, AgrarSoonne GmbH,
vertreten durch Herrn Werner Müller verpflichtet sich , an den Vertragsgeber, die SiamStrom AG zur Lieferung von 10 Tonnen
Mais (Erntegewicht) bis zum 15. Oktober 2012. Der Vertragsnehmer liefert frei Haus zum Preis von 10 000
. Er verpflichtet sich weiter,
maize
digestate
annual contract
transformer substation
pellet factorypress cake
biogas plant
Fig. 4 Logistic model of an in-house agricultural biogas plant
Scenarios of bioenergy provision
123
social perceptions. Furthermore, as a small stakeholder group (s. Fasterdimg 1997) with a
major influence on landscapes under transformation, they are placed in a new spotlight of
society and are becoming the focus of the broad majority of people whose main interests
pertain to non-commodity outputs, such as a landscape’s contribution to the formation of
identity and recreation in a natural setting (cp. van der Horst 2007; Madureira et al. 2007).
5.3.2 Stakeholder options and decision behaviour
Decisions that farmers make in this rather open situation are, as indicated, not solely
explained by profit maximisation. As the interviews with plant operators revealed, they
largely depend on attitudes that affect, for example, the willingness to enter into contractual
relationships. Despite the widespread idea of total flexibility, the interviews also revealed a
strong willingness, if not a necessity, of non-agrarian plant operators to enter into contracts
with farmers who secure the supply of raw materials. Farmers did not display the same
readiness to enter into contracts, as two selected quotations indicate. ‘‘When we started’’,
stated one plant operator, ‘‘the farmers here in the region have of course been a bit sceptical.
If this would work here, and closing contracts–who knows what this is going to become
[…]’’. ‘‘We have found our partners in Poland’’, explained a second plant operator. ‘‘And
one cannot say this is cheaper. However, what there was, and what has rebounded to our
advantage, was the willingness to enter fairly long-term contracts. And this is where we, after
all, have considerable problems of acceptance among German farmers’’.
Apparently, soft reasons play an important role in decision-making. The interviews
revealed a wide variety of such reasons, including the margin between scepticism towards
investors from the non-agrarian sector or about upcoming developments and contentment
with contractual relationships in operation, between progressiveness and a pioneering spirit
on the one hand and a well-rehearsed role perception on the other, between activity and
passivity, and between one’s own ideas and the experiences of other regional stakeholders.
Soft reasons also include confidence and responsibility. The interviews also demonstrated
the roles of openness and prejudices among stakeholder groups that are not strongly related
to each other and thus demonstrated the importance of communication. In addition, legal
certainty is an important issue that was addressed by four interview partners. The variety of
35 km
cultivation digestate
transport
Vertrag über die Lieferung von Mais
Der Vertragsnehmer, AgrarSoonne GmbH,
vertreten durch Herrn Werner Müller verpflichtet sich , an den Vertragsgeber, die SiamStrom AG zur Lieferung von 10 Tonnen
Mais (Erntegewicht) bis zum 15. Oktober 2012. Der Vertragsnehmer liefert frei Haus zum Preis von 10 000
. Er verpflichtet sich weiter,
ten-year contractannual land designation
logistican
harvest
Poland Germany
logistican
CHPP
norms, advise
silos
lease
CHPP
Fig. 5 Logistic model of a medium-sized biomethane injection plant (CHPP = combined heat and powerplant)
A. Starick et al.
123
soft reasons involved leads to ambivalent decision-making behaviour under contradicting
demands, such as the desire for security and autonomy at the same time.
Given the growing diversity of stakeholders and their complex linkages, the diversity of
options similarly applies to other stakeholder groups. They too find themselves in a new
and open decision situation that requires the reconsideration of self-concepts and social
perceptions.
This applies not least to the heat and power consumers, who are faced with increasing
energy prices,4 who must reconsider the amounts and types of energy they consume,5 and
who are increasingly becoming producers and service providers themselves.6 Furthermore,
they are increasingly faced with the consequences of their energy consumption. Energy
production was previously concentrated in selected areas, most of which were far out of
sight; however, renewable energy production now takes place everywhere in the immediate
environment. Among the various forms of energy production, bioenergy utilises the most
space and is most associated with the infiltration of technical facilities into the open
landscape. As the scenarios illustrate, it also transforms agriculture (and possibly forestry),
leading to intensification of land uses, homogenisation (uniformisation), and monostruc-
turing of landscapes, with large-scale maize and canola cultures. Thus, landscapes are
taking on increasingly industrialised forms and are changing rapidly. Consumers are thus
faced with the results of their energy consumption in new ways.
The groups that are affected by the transformation of their landscapes and their
homeland, particularly the inhabitants of rural areas, are thus also involved. Their reception
of the transformation of landscape and energy systems and their resulting actions should
not be underestimated. Their ability and their willingness to take their destinies into their
own hands and participate in or oppose supraregional developments, as well as their
societal commitment to support or oppose either bioenergy or landscape development, will
strongly influence both types of development.
5.3.3 Stakeholders’ constellation
The linkages demonstrated by the descriptions of the different stakeholder groups illustrate
that with technological changes and spatial transformation comes a shift in the social
situation as a whole. The boundaries between the different stakeholder groups blur or shift
and are newly drawn (Fig. 6). This is a challenge to each party that requires a reorientation
of individuals and stakeholder groups as part of an active social discourse about complex
development contexts. This discourse should include questions concerning land use
activities in which society as a whole is becoming increasingly involved, although indi-
rectly and after years of declining direct involvement (cp. Plieninger et al. 2006). It should
also include reflection on the concept of landscape, the envisaged spatial development, and
the relationships between town and country.
Because each stakeholder group has a considerable variety of options, the decisions
made under this shifting constellation—and the pace at which and resolution with which
they are made—will determine the direction in which bioenergy supply and the landscape
will develop within a region.
4 One reason is that the costs of the transformation of the energy system to renewable energies are allocatedto the consumer by means of the REA.5 This is possible due to the diversity of providers that offer energy from different resources.6 Involvement in the service sector represents, for instance, participation in smart grids and regional energymarkets.
Scenarios of bioenergy provision
123
6 Conclusions
Throughout Germany, the provision of energy using renewable resources is developing
rapidly and is particularly affecting the development of rural regions. To better understand
the cause-and-effect relationships involved and anticipate the directions that future
developments may take and the impacts that they may have, regional scenarios have been
drafted, using bioenergy provision in the Gorlitz district as an example.
The framework developed by Syrbe et al. (2013) served as the basis for the development
of the scenarios. The framework allows the use of different methods and directional
decisions during the process. It thus facilitates a gradual refinement of the approach based
on the progress of knowledge and discourse.
We divided the evaluation step into two subtasks, thereby allowing a later technical
assessment of the scenario effects (in this case, on ecosystem services) as a major con-
tribution to decisions about objectives (cp. Bastian et al. 2013), while permitting a direct
interpretation for regional development and society. The division was also a methodo-
logically useful step because in the course of the scenario process, the projections of the
key driving forces and the storylines themselves increasingly became the object of political
will and normative discussions. Although this became a challenge for ensuring an
explorative process, it provided an opportunity for an intense discussion of the cause-and-
effect relationships and thereby led to an early discussion of the parameters that ought to be
adjusted to achieve the type of development envisaged.
In our case, decentralised development was clearly preferred. A more sophisticated
discussion could have been achieved by adding a scenario that combines expressions of
key driving forces that do not initially appear to be supportive of each other. Based on
the situation in the Gorlitz district, the action of a few major investors under a greened
CAP and REA might have been a combination worth investigating. Another combi-
nation might have been the establishment of a few large plants by regional actor
networks.
For the purpose of distinguishing among the scenarios, four key driving forces (CAP,
REA, technologies, and actors) were identified. In general, the relationship between CAP
and REA will be of particular importance to the future development of agriculture. For the
type of development upon which rural regions embark, technologies are even more
important, because they allow for either highly centralised or highly decentralised devel-
opment. Over time, due to limited resources and system requirements, one type of solution
tends to preclude the other. Time is an important factor, as the decisions that are made now
predetermine further developments. Even more so than the technologies however, the
Landscape
Landscape
Producers
Affectedgroups
Consumers
Con
sum
ers
Producers
Affectedgroups
Fig. 6 Shift in stakeholders’constellations
A. Starick et al.
123
attitudes, capacities, decisions, and actions of the actors are decisive for either type of
development.
The scenario interpretation demonstrates the strong effects of bioenergy provision on
land uses and landscapes. Furthermore, we observed strong social effects of bioenergy and
renewable energy growth in general. These social effects include a growing number of
stakeholders being involved in energy development on the production side and the growing
importance of consumers and non-productive land users, particularly the inhabitants whose
environments are affected. Because each stakeholder group’s options for action increase
and the boundaries between these stakeholder groups blur, stakeholders’ constellations as a
whole shift, leading to changes in the society. Society is thus both a driving force and an
affected system.
The reaction of societies to renewable energy growth, particularly in terms of resistance,
has been widely investigated (cp. e.g. van der Horst 2007; Jenssen 2010; Pasqualetti 2011).
Less investigation has been undertaken regarding the wider effects and the proactive role
of society in renewable energy growth (cp. Bagliani et al. 2010). The results of this study
constitute a contribution to the field in this respect. The results show the influence of a
region’s actors on the technological development in a region. Under shifting social con-
stellations, it is still open into which direction the technological development drives.
We see high creative potential in the situation described. The situation is, however, also
disposed to developments that could overwhelm a region’s capacity to anticipate and
regulate development.
To manage the interlinked developments of an energy system, the landscape, and
society in sustainable ways and ensure that development is socially stable, technical
support for regional target setting, with discursive processes that combine exogenous and
endogenous knowledge, is reasonable. The process of qualitative scenario construction
has proven to be an appropriate tool for facilitating the learning process on both the
researchers’ and the stakeholders’ sides and consequently an appropriate tool for sup-
porting this management (cp. van der Horst 2007; Albert et al. 2012). The ability of this
tool to demonstrate the magnitudes of possible future development challenges should not
be underestimated. Based on this ability alone, the scenarios considered can serve to
support decisions. We echo the plea by Howard et al. (2013) for a system approach to
energy planning that considers the interconnections of energy, landscape, and society (cp.
also van der Horst 2007; Bagliani et al. 2010; Nadai van der Horst 2010; Pasqualetti
2011).
The strengthening of the counter-current principle regarding the development of the
energy system could be another management tool. In particular, such strengthening could
provide an additional means of revising national objectives and exploring regionally
adapted solutions. Furthermore, questions of social and environmental justice must be
discussed on a supraregional scale. Offers of involvement in structuring regional devel-
opment and participation in its benefits might be concrete approaches, as the poles between
an increasing number of citizens’ initiatives against renewable energy developments and
citizens’ cooperatives for the establishment of renewable energy facilities in their imme-
diate environments indicate.
Acknowledgments The authors are grateful to the plant operators interviewed for insights into theiroperations and to the stakeholders in the Gorlitz district who contributed to the scenario process. The authorsthank the anonymous reviewers whose comments significantly improved the clarity of the paper. This studywas supported by the funding scheme ‘‘Sustainable Land Management–Module B’’ of the German FederalMinistry for Education and Research (FKZ 033L028A-E).
Scenarios of bioenergy provision
123
References
Albert, C., Zimmermann, T., Knieling, J., & von Haaren, C. (2012). Social learning can benefit decision-making in landscape planning: Gartow case study on climate change adaptation, Elbe valley biospherereserve. Landscape and Urban Planning, 105(4), 347–360.
Alcamo, J. (Ed.). (2008). Environmental futures: The practice of environmental scenario analysis. Devel-opments in Integrated Environmental Assessment. Amsterdam u. a.: Elsevier.
Ammermann, K. (2008). Energetische Nutzung nachwachsender Rohstoffe. Auswirkungen auf die Bio-diversitat und Kulturlandschaft. Natur und Landschaft, 83(3), 108–110.
Artner, A., Frohnmeyer, U., Matzdorf, B., Rudolph, I., Rother, J., & Stark, G. (2006). Future landscapes.Berlin, Bonn: Perspektiven der Kulturlandschaft.
Bagliani, M., Dansero, E., & Puttilli, M. (2010). Territory and energy sustainability: The challenge ofrenewable energy sources. Journal of Environmental Planning and Management, 53(4), 457–472.
Bastian, O., Lupp, G., Syrbe, R.-U., & Steinhaußer, R. (2013). Ecosystem services and energy crops—spatial differentiation of risks. Ekologia, 32(1), 13–29.
Billig, E., Thran, D., Bunzel, K. (2011). Bioenergie. Stand der Technik und Entwicklungsperspektiven.Lecture, Scenario Workshop of the research project Loebestein, 01/03/11, St. Marienthal.
BMELV Bundesministerium fur Ernahrung, Landwirtschaft und Verbraucherschutz, & BMU Bundesmin-isterium fur Umwelt, Naturschutz und Reaktorsicherheit (Eds.). (2009). Nationaler Biomasseaktions-plan fur Deutschland. Beitrag der Biomasse fur eine nachhaltige Energieversorgung. Berlin.
DB Deutscher Bundestag (Ed.) (2011a). Beschlussempfehlung und Bericht des Ausschusses fur Umwelt,Naturschutz und Reaktorsicherheit (16. Ausschuss). 17/6363. Berlin.
DB Deutscher Bundestag (Ed.) (2011b). Beschlussempfehlung und Bericht des Ausschusses fur Umwelt,Naturschutz und Reaktorsicherheit (16. Ausschuss). Drucksache 17/6247. Berlin.
Bureau, J. C. (2012). Where is the common agricultural policy heading? In D. Viaggi, J. C. Bureau, S.Tangermann, A. Matthews, C. Crombez, L. Knops, J. Swinnen (Eds) The common agricultural policyafter 2013. Intereconomics, Review of European Economic Policy 47(6), 316–342.
Carpenter, S. R., Bennett, E. M., & Peterson, G. D. (2006). Scenarios for ecosystem services: An overview.Ecology and Society, 11(1), art. no. 29. http://www.ecologyandsociety.org/vol11/iss1/art29/.
Chevalier, J. M., & Buckles, D. J. (2008). SAS2 social analysis systems: A guide to collaborative inquiry andsocial engagement. New Delhi: Sage Publications.
BRD Bundesrepublik Deutschland (Ed.) (2010). Nationaler Aktionsplan fur erneuerbare Energie gemaß derRichtlinie 2009/28/EG zur Forderung der Nutzung von Energie aus erneuerbaren Quellen. www.erneuerbare-energien.de/. Accessed 14 June 2012.
DREBERIS (Ed.) (2012). Analyse der Potentiale zur energetischen Biomassenutzung sowie einer Akteurs-und Netzwerkanalyse im Bereich der Biomasseerzeugung und –nutzung in der Region Dresden imRahmen des Modellvorhabens der uberregionalen Partnerschaft der Metropolregion Mitteldeutschland‘‘Partnerschaft der Stadtregionen’’; Teilbericht 1. Biomassepotentiale in der Region Dresden. http://region.dresden.de/media/pdf/region/ErsterTeilbericht.pdf. Accessed 18 December 2012.
Dreher, B. (2011): Aktuelle Entwicklungen im EEG. Lecture at the conference Energetische Nutzung vonLandschaftspflegematerial‘‘, 01/03–02/03/11, Berlin.
EC European Commission (2011). Establishing rules for direct payments to farmers under support schemeswithin the framework of the common agricultural policy. Proposal for a regulation of the Europeanparliament and of the council (ed EC), COM(2011) 625 final/2. http://ec.europa.eu/agriculture/cap-post-2013/legal-proposals/com625/625_en.pdf. Accessed 03 March 2013.
Fasterdimg, F. (1997). Projection of the structure of labour input in German’s agriculture. Landbaufors-chung Volkenrode, 47(3), 135–145.
Grundmann, J. (2010): Konzepte zur Sicherung von Biomassebrennstoffen fur die Heizkraftwerke derVattenfall Gruppe. Lecture at the Kick-off-Meeting of the BMBF research project AgroForNet at the19 November 2010 in Tharandt.
Houet, T., Loveland, T., Hubert-Moy, L., Gaucherel, C., Napton, D., Barnes, C., et al. (2010). Exploringsubtle land use and land cover changes: A framework for future landscape studies. Landscape Ecology,25(2), 249–266.
Howard, D. C., Burgess, P. J., Butler, S. J., Carver, S. J., Cockerill, T., Coleby, A. M., et al. (2013).Energyscapes: Linking the energy system and ecosystem services in real landscapes. Biomass andBioenergy, 55, 17–26.
IEA International Energy Agency (Ed.) (2009). World energy outlook 2009. Paris: IEA.Jenssen, T. (2010). The good, the bad, and the ugly: Acceptance and opposition as keys to bioenergy
technologies. Journal of Urban Technology, 17(2), 99–115.Kaphengst, T. (2009). Nachhaltige Biomassenutzung in Europa. GAiA, 16(2), 93–97.
A. Starick et al.
123
Lambin, E. F., & Meyfroidt, P. (2010). Land use transitions: Socio-ecological feedback versus socio-economic change. Land Use Policy, 27(2), 108–118.
Leibenath, M., & Otto, A. (2012). Diskursive Konstituierung von Kulturlandschaft am Beispiel politischerWindenergiediskurse in Deutschland. Raumforschung und Raumordnung, 70(2), 119–131.
Leopoldina German National Academy of Sciences Leopoldina (Ed.) (2012). Statement bioenergy—chances and limits. Halle (Saale).
Lupp, G., Albrecht, J., Darbi, M., & Bastian, O. (2011). Ecosystem services in energy crop production—Aconcept for regulatory measures in spatial planning? Journal of Landscape Ecology, 4(3), 49–66.
MA: Millennium Ecosystem Assessment. (2005). Ecosystems and human well-being: Synthesis. Washing-ton, DC: Island Press.
Madureira, L., Rambonilaza, T., & Karpinski, I. (2007). Review of methods and evidence for economicvaluation of agricultural non-commodity outputs and suggestions to facilitate its application to broaderdecisional contexts. Agriculture, Ecosystems & Environment, 120(1), 5–20.
Mahe, L.-P. (2012). Do the proposals for the CAP after 2013 herald a ‘major’ reform? Policy paper 53.Paris: Notre Europe.
Nadai, A., & van der Horst, D. (2010). Introduction: Landscapes of energies. Landscape Research, 35(2),143–155.
Opaschowski, H. W. (2008). Deutschland 2030. Gutersloh, Munchen: Wie wir in Zukunft leben.Pasqualetti, M. J. (2011). Social barriers to renewable energy landscapes. Geographical Review, 101(2),
201–223.Plieninger, T., Bens, O., & Huttl, R. F. (2006). Landwirtschaft und Entwicklung landlicher Raume. APuZ
Aus Politik und Zeitgeschichte, 37(2006), 23–30.Reed, M. S., Graves, A., Dandy, N., Posthumus, H., Hubacek, K., Morris, J., et al. (2009). Who’s in and
why? A typology of stakeholder analysis methods for natural resource management. Journal ofEnvironmental Management, 90(5), 1933–1949.
FNR Fachagentur Nachwachsende Rohstoffe (Ed.) (2012). Biogas. 8. Ed. Rostock.Rowe, R. L., Street, N. R., & Taylor, G. (2009). Identifying potential environmental impacts of large-scale
deployment of dedicated bioenergy crops in the UK. Renewable and Sustainable Energy Reviews,13(1), 271–290.
Scheuermann, A., Erfurt, I., Peters, W., Schicketanz, S. et al. (2012). Regionales Energie- und Klimas-chutzkonzept fur die Region Oberlausitz-Niederschlesien. Kurzfassung des Endberichts. Leipzig.www.rpv-oberlausitz-niederschlesien.de/projekte/regionales-energie-und-klimaschutzkonzept-klimaanpassungsstrategie/regionales-energie-und-klimaschutzkonzept/ergebnisse.html. Acces-sed 20 Dec 2012.
Sohl, T. L., Loveland, T. R., Sleeter, B. M., Sayler, K. L., & Barnes, C. A. (2010). Addressing foundationalelements of regional land-use change forecasting. Landscape Ecology, 25(2), 233–247.
Soliva, R. (2009). Die Zukunft des Schweizer Berggebiets: Eine partizipative Nachhaltigkeitsprufung vonLandwirtschafts- und Landschaftsszenarios. GAiA, 16(2), 122–129.
Starick, A., Klockner, K., Moller, I., Gaasch, N., & Muller, K. (2011). Entscheidungshilfen fur einenachhaltige raumliche Entwicklung der Bioenergiebereitstellung: Methoden und ihre instrumentelleAnwendung. Raumforschung und Raumordnung, 69(6), 367–382.
Stocker, A., Omann, I., Jager, J. (2012). The socio-economic modelling of the ALARM scenarios withGINFORS: Results and analysis for selected European countries. Global Ecology and Biogeography21 (Special Issue), 36–49.
Syrbe, R.-U., Rosenberg, M., & Vowinckel, J. (2013). Kap. 4.3 Szenarioentwicklung und partizipativeVerfahren. In K. Grunewald & O. Bastian (Eds.), Okosystem-Dienstleistungen. Methoden und Fall-beispiele (pp. 110–119). Berlin, Heidelberg: Konzepte.
Szarka, N., Scholwin, F., Trommler, M., Fabian Jacobi, H., Eichhorn, M., Ortwein, A., et al. (2013). A novelrole for bioenergy: A flexible, demand-oriented power supply. Energy, 61(1), 18–26.
BWT Bundesministerium fur Wirtschaft und Technologie, & BMU Bundesministerium fur Umwelt, Na-turschutz und Reaktorsicherheit (Eds.). (2007). Bericht zur Umsetzung der in der Kabinettsklausur am23./24.08.2007 in Meseberg beschlossenen Eckpunkte fur ein Integriertes Energie- und Klimapro-gramm. Berlin. www.bmu.de/klimaschutz/downloads/doc/40514.php. Accessed 18 Nov 2009.
Thran, D., Bunzel, K., Seyfert, U., Zeller, V., Buchhorn, M., Muller, K., et al. (2011). Global and regionalspatial distribution of biomass potential: status quo and options for specification; final report; projectnumber DBFZ 3330001. DBFZ Report Nr. 7. Leipzig.
Thran, D., Bunzel, K., Viehmann, C., et al. (2010). Bioenergie heute und morgen—11 Bereitstellungs-konzepte. Leipzig: Sonderheft zum DBFZ-Report.
Scenarios of bioenergy provision
123
BMU Bundesministerium fur Umwelt, Naturschutz und Reaktorsicherheit (Ed.). (2008). Umweltbewusstseinin Deutschland 2008—Ergebnisse einer reprasentativen Bevolkerungsumfrage. Reihe Umweltpolitik.Niestetal.
BMU Bundesministerium fur Umwelt, Naturschutz und Reaktorsicherheit (Ed.). (2011). Erfahrungsbericht2011 zum Erneuerbare-Energien-Gesetz (EEG-Erfahrungsbericht) (Entwurf mit Stand vom 03/05/11).Berlin.
SRU Sachverstandigenrat fur Umweltfragen (Ed.). (2011). Wege zur 100 % erneuerbaren Stromversorgung.Sondergutachten: Berlin.
van der Horst, D. (2007). NIMBY or not? Exploring the relevance of location and the politics of voicedopinions in renewable energy siting controversies. Energy Policy, 35(5), 2705–2714.
van Drunen, M. A., van’t Klooster, S. A., & Berkhout, F. (2011). Bounding the future: The use of scenariosin assessing climate change impacts. Futures, 43(4), 488–496.
VERBI GmbH (Ed.). (2013). MaxQDA—Qualitative data analysis software. www.maxqda.com. Accessed23 Sept 2013.
Walz, A., Lardelli, C., Behrendt, H., Gret-Regamey, A., Lundstrom, C., Kytzia, S., et al. (2007). Partici-patory scenario analysis for integrated regional modelling. Landscape and Urban Planning, 81(1–2),114–131.
Wiehe, J., Ruschkowski, Ev, Rode, M., Kanning, H., & Haaren, Cv. (2009). Effects of the cultivation ofenergy plants on the landscape—the example of maize production for biomethanation in LowerSaxony. Naturschutz und Landschaftsplanung, 41(4), 107–113.
Wietschel, M., Arens, M., Dotsch, C., Herkel, S., Krewitt, W., Markewitz, P., et al. (2010). Energietech-nologien 2050—Schwerpunkte fur Forschung und Entwicklung. Stuttgart, Fraunhofer Verlag:Technologienbericht.
A. Starick et al.
123