Energy Policy 39 (2011) 2550–2559 Contents lists available at ScienceDirect Energy Policy journal homepage: www.elsevier.com/locate/enpol A participatory approach to sustainable energy strategy development in a carbon-intensive jurisdiction: The case of Nova Scotia Michelle Adams a,n, David Wheeler b, Genna Woolston a a b School for Resource and Environmental Studies, Dalhousie University, 6100 University Avenue, Suite 5010, Halifax, NS, Canada B3H 3J5 Plymouth Business School, University of Plymouth, Cookworthy Building, Drake Circus, Plymouth, Devon PL4 8AA, UK a r t i c l e i n f o a b s t r a c t Article history: Received 14 July 2010 Accepted 4 February 2011 Available online 1 March 2011 The need for governments to reduce the exposure of energy consumers to future increases in fossil fuel prices places urgent pressure on policy-makers to deliver fundamental transformations in energy strategies, particularly in jurisdictions with high dependency on fossil fuel sources (Dorian et al., 2006). This transformation is unlikely without a high level of stakeholder engagement in the policy development process. This paper describes two policy development processes recently undertaken in Nova Scotia in which the inclusion of stakeholder views was central to the approach. The first delivered a new institutional framework for electricity energy efficiency involving the inception of an independent performance-based administrator. The second required the delivery of a strategy to significantly increase renewable energy generation in the Province. It involved recommendations for changes in institutional arrangements, financial incentives and technological options. This process was followed by new commitments to renewable energy developments, new infrastructure for the importation of hydro-electricity, and the announcement of FITs for ocean energy. In both cases, recommendations were made by an independent academic institution, and the Government responded directly to a majority of recommendations. The paper concludes with a discussion of lessons learned and the implications for future energy policy making in carbon-intensive jurisdictions. & 2011 Elsevier Ltd. All rights reserved. Keywords: Sustainable energy policy Stakeholder engagement Participatory approach 1. Introduction In the 1990s renewable energy policy was largely motivated by environmental considerations (Lipp, 2007). Today, energy security, which first showed up as a policy driver in the 1970s (Lipp, 2007) seems to have once again emerged as an additional important factor (Chatham House, 2010). Particularly where a jurisdiction’s energy resource base is dependent on imported, non-renewable fuels, the sense of urgency to promote indigenous renewable energy has increased (Jacobsson and Lauber, 2006; Lipp, 2007). The number and diversity of stakeholders who are interested in pursuing alternatives to fossil fuel energy generation – or who are impacted by the adoption of related strategies such as energy efficiency or renewable energy development – can be daunting for policy-makers to address. And yet public pressure for meaningful responses to climate change and the need for governments to reduce the exposure of energy consumers to potentially very significant rises in future fossil fuel prices puts urgent pressure on policy-makers in fossil fuel dependent jurisdictions n Corresponding author. Tel.: +1 902 494 4588; fax: + 1 902 494 3827. E-mail address: [email protected] (M. Adams). 0301-4215/$ - see front matter & 2011 Elsevier Ltd. All rights reserved. doi:10.1016/j.enpol.2011.02.022 to deliver radical transformation in energy strategies in the shortest time possible (Dorian et al., 2006). However, fundamental transformation is unlikely to occur in the absence of a high level of stakeholder engagement in the policy development process (Dorian et al., 2006; Ricci et al., 2010). In this paper we describe two public policy development processes undertaken in Nova Scotia in 2008 and 2009 in which the inclusion of stakeholder views and aspirations were central to the approach. The first process was the delivery of a new institutional framework for electricity energy efficiency involving the inception of an independent performance-based administrator. The second process was more complex and required the delivery of a strategy to significantly increase the level of renewable energy generation in the Province. The intention was to develop recommendations for changes in institutional arrangements, financial incentives and technological options that arose directly out of the input of all relevant stakeholders. Thus, the Government could respond directly to the concerns and input of stakeholders, embedding this contribution into the policy development process. In both cases recommendations were synthesized and delivered by an independent academic institution and in both cases the Government received and responded directly to a majority of policy recommendations. The paper concludes with a discussion of what was learned from these processes and the implications for future energy policy making in M. Adams et al. / Energy Policy 39 (2011) 2550–2559 carbon-intensive jurisdictions that face significant transformational challenges. 2. Emerging approaches to policy development—the importance of independence and accountability As energy prices rise and the importance of successful implementation of energy conservation and renewable energy strategies increases, the need for accountability and transparency in policymaking will be paramount (Ricci et al., 2010). Stakeholders will insist that the policies are reflective of the broader public interest and that any institution involved in the delivery of such strategies will need to demonstrate the validity and objectivity of their role. The increasing complexity of contemporary energy policy issues, which combine economic, ecological, cultural, political and technical dimensions, invokes the needs for expanded analyses of policy implications (Vigar and Healey, 2002; Holmes and Scoones, 2000; Munda, 2004). There is a growing recognition that including broader interests in the policy development process is essential for effective outcomes (De Marchi and Ravetz, 2001; Vigar and Healey, 2002). Stirling (2008) goes further to suggest that accountability is enhanced when stakeholder can recognize their contributions embodied within the outcome as well as the process, rather than their involvement simply being a required element of a deliberative process. Specific to achieving success within a renewable energy agenda, it has been suggested that to overcome the fossil fuel dependencies that some believe influence current political, economic and technical assumptions – and are thereby built into the current energy markets – entirely new policy measures will be required which build on these emerging realities (Mendonc- a et al., 2009). It has been argued that where broader stakeholder interests are sidelined, it is likely that sustainable energy markets will remain largely centralized, inefficient, increasingly costly and exclusive (Mendonc- a et al., 2009; Mitchell and Woodman, 2010). This phenomenon is argued to be counterproductive when the aim is meaningful penetration of renewables (Juhl, 2010). Therefore, new measures must include new actors, as it is their input that could provide balance to the historical vested interests that have been seen to influence energy policy development until now. In the past, policy development has typically developed subject to political factors and the needs and views of these powerful interest groups, often those groups that stood to benefit most from the status quo of ongoing fossil fuel dependence (Van Rooijen and van Wees, 2006; Zoellner et al., 2008). Thus, as policy makers design strategies to meet sustainable energy goals, they are faced with growing pressure to ensure that decisions are taken with transparency and accountability that satisfies diverse constituencies (Rayner, 2010). As Zoellner et al. (2008) noted, if people feel left out of the planning process and decision making, they will be more likely to oppose the process outcome. Mitchell and Woodman (2010), for example, found that heightened concern about the level of effectiveness and appropriateness of renewable energy policies in the UK resulted in a lack of trust about the policy development process. Such situations could have implications for policy makers to generate support around decisions that require buy-in at a societal level to be successful. In should also be noted that stakeholder participation and accountability is often very important for the successful development of renewable energy industries—particularly in jurisdictions where it is key to secure long-term stakeholder (particularly community) support (Lipp, 2007). Successful jurisdictions, for example those in continental Europe (Meyer, 2003; Gan et al., 2007; Lipp, 2007), have sought to ensure that such energy strategies were 2551 developed with maximum stakeholder engagement and minimal political uncertainty and interference. Recent research conducted in Ontario revealed that one of the most important factors influencing the unsuccessful development of renewable energy technology and the associated skill capacities was the instability of the policy and fiscal environment (Holburn, 2009). Clearly, the ‘rules of the game’ in policy making for sustainable energy strategies are changing (Van Rooijen and van Wees, 2006). However, it is important to note that participatory methods are not an alternative to scientific expertise and more technical assessments, but, they are a necessary complement to the process by broadening the number of dimensions that are considered (Holmes and Scoones, 2000). Policy development that actively promotes the inclusion of a multiplicity of stakeholders can succeed in improving transparency, accountability and understanding—conditions for improved sustainable energy policy outcomes (Zoellner et al., 2008; Agterbosch et al., 2009; Mendonc- a et al., 2009). 3. Implications for participatory processes for sustainable energy policy What emerges from the practice-based observations described above is that policy making as a traditional ‘top down’ bureaucratic process where policy makers heed only the input of a select few actors is insufficient to address the policy requirements needed to address the complex issues of today. It is necessary to improve the quality of the information involved by actively integrating insight and expertise from a broader set of sources than is typically available to the bureaucratic process. As such, the inclusion of stakeholders in the process – right from the ‘problem definition’ – through to the development of the policy that will guide the ‘solutions’ will aid in addressing potential emergent properties and conditions (and thereby creating a more resilient framework) that would otherwise be overlooked. Decision makers who recognize the complexity of contemporary policy processes will need to think and act differently than they have in the past. Decision makers will need to employ novel methodological approaches to address the various factors at play and meet higher stakeholder expectations. This suggests a more creative and innovative approach that is responsive to emerging patterns and can respond to shifts in social and other systems as required. Successful strategy-development that can address emergent properties will necessarily involve stakeholder input. Using participatory approaches, particularly in situations of high stakeholder expectations and/or low trust/social capital (Nahapiet and Ghoshal, 1998; Adler and Kwon, 2002), policy-makers can demonstrate openness to diverse, multi-disciplinary opinions and expertise, and therefore co-create successful policy development processes directly with stakeholders. Mendonc- a et al. (2009) reiterated the importance that this innovative democracy could play in creating a decision making process that formally integrates all relevant stakeholders, thereby garnering improved social capital within the stakeholder ranks and simultaneously accelerating renewable energy project development. The adoption of a policy strategy informed by this kind of open approach, i.e. one of being adaptive to stakeholder expectations and the policy-induced behaviours, can help overcome the issue of mistrust between the various actors (Thompson, 2006; Rayner, 2010; Ricci et al., 2010). Proponents of an approach that involves policy makers being responsive to emergent information describe an increasing number of cases with successful outcomes (Buchholz and Rosenthal, 2004; Thompson, 2006). Specifically, some of the numerous proposed benefits of participatory approaches to sustainable energy policy development (Holmes and Scoones, 2000; 2552 M. Adams et al. / Energy Policy 39 (2011) 2550–2559 De Marchi and Ravetz, 2001; Vigar and Healey, 2002; Khan, 2004; Munda, 2004) include the following: better appraisal of proposed policies; framing of policy issues in broad terms, including all sectors of society and the environment; generating novel policy solutions; reducing opportunism by committing participants into a range of interdependent decisions; addressing the growing distrust in the policy process and towards related institutions; promoting consensus building; promoting higher public acceptance and legitimacy of policies; generating shared ownership of policy outcomes, which assists in subsequent policy implementation; promoting citizen empowerment; and increasing the knowledge and democratic capabilities of citizens. However, care is also required with such approaches. The quality of the participatory process depends on a number of factors such as the accuracy of information provided to the participants, the degree to which the dialogue includes expertise from a range of institutional actors, and the diversity of views represented. The degree to which participants weigh issues on merit versus the way they relate to the participants’ specific selfinterest is also important (Fishkin, 2002a, b). As De Marchi and Ravetz (2001) note, frustration can arise when participants fear that participatory approaches are used as a means of deflecting protest, inhibiting actions or controlling outcomes. Within the sustainable energy policy development process, the most frequent call for public participation has been at the planning stage when new generation facilities are being sited. This has been in part due to fears of local opposition that often emerge at this stage, and hence many researchers encourage participatory approaches during this phase (Upreti, 2004; Upreti and van der Hors, 2004). In particular, researchers have promoted local stakeholder inclusion during the siting of wind farms, largely as a means of bridging the divide between national environmental objectives and local concerns (Blázquez Garcı́a et al., 2003; Khan, 2004; Jobert et al., 2007; Söderholm et al., 2007; Wolsink, 2007; Wüstenhagen et al., 2007; Agterbosch et al., 2009). Some have suggested that it would be appropriate to institutionalize participation in energy development policy frameworks in order to enhance the likelihood of acceptance at the local level (Breukers and Wolsink, 2007; Wüstenhagen et al., 2007; Agterbosch and Breukers, 2008; Agterbosch et al., 2009). There is rather less discussion in the literature about public participation related issues focused on demand-side management and energy efficiency processes. However, numerous recent publications have focused on the importance of developing trust amongst the various stakeholders to effect positive transitions to more sustainable energy systems, including the policies that underpin those transitions (Bellaby, 2010; Kydd, 2010; Ricci et al., 2010) Many methods have been used to engage stakeholders in the formation of policy, including mediation, citizen juries, consensus conferences and referendums (Smith, 2001; Fishkin, 2002a, b). Enzensberger et al. (2002) offer an approach that begins with the formation of a precise political target based on an analysis of the techno-economic characteristics of the energy supply system and existing market mechanisms. Following the creation of this target, an iterative and participatory evaluation of policy options is suggested. Other research into the development of sustainable energy policy by Greening and Bernow (2004) suggested that a diversity of stakeholder preferences can be incorporated into energy policy analyses, for example through multi-criteria decision-making (MCDM) methods used in an integrated assessment (IA) framework. However, while these and other examples demonstrate that public participation during the formation of sustainable energy policies has been discussed (and in select cases implemented), a detailed literature search has revealed that the actual approach to stakeholder inclusion in these processes has rarely been fully described in an operational sense. Therefore, the policy-making approach to guide progress on energy efficiency and renewable energy in Nova Scotia – a jurisdiction with especially high dependency on fossil fuels – offers a potentially unique lens into the issue. In our approach we drew on the experience of the principal facilitator in corporate strategic management settings (Wheeler and Sillanpää, 1998), combined with an absolute commitment to academic objectivity as ‘honest broker’ between the various parties. Trust and goodwill (social capital) was built intentionally through both processes, consistent with the theories of Adler and Kwon (2002) and Freeman (1984), and adapted to the needs of innovative democracy in energy policy-making (Mendonc- a et al., 2009) in the presence of a clear political target (Enzensberger et al., 2002). Using the constructs of social capital and stakeholder theory it was hoped that sufficient goodwill might be created through the processes to allow the Provincial Government to act both ethically and effectively whilst being insulated from charges of bias or self-interest in what had previously been a problematic domain based on a history of misunderstanding and mistrust. 4. Methodology Two stakeholder-led strategy processes were designed and executed in the period January–April 2008 (Energy Efficiency Strategy for the Province of Nova Scotia—EES) and September–December 2009 (Renewable Energy Strategy for the Province of Nova Scotia—RES). In both cases the independent facilitator was the Faculty of Management, Dalhousie University and the client was the Government of Nova Scotia Department of Energy (DoE). In the first case (EES) the agent of the Government was the provincial energy efficiency agency Conserve Nova Scotia. The lead facilitator was unpaid, and only the direct costs of the process were charged to the Government. In both cases a key stakeholder was the energy utility itself: Nova Scotia Power Inc (NSPI), regulated monopoly electricity utility privatized in 1992. In 2008 NSPI had a mixed reputation for stakeholder responsiveness, in part because of the adversarial nature of the regulatory and electricity rate-setting process that the company was forced to undergo. Other key stakeholders in the processes were environmental and social justice groups, domestic electricity ratepayers, industrial and commercial electricity ratepayers, municipalities and (in the case of the RES), renewable energy developers. The Energy Efficiency Strategy (EES) process was moderately complex, exhibiting early agreement amongst the stakeholders (40 in total) regarding the general direction of the likely outcome, but greater divisiveness when addressing programmatic details. In contrast, the Renewable Energy Strategy (RES) process was highly complex and somewhat contested (involving more than 300 stakeholders). In both cases a ten stage dialogic methodology was pursued by the independent facilitators that adopted the following sequence: 1) Identification and inclusion of stakeholders. 2) Establishment of cognitive baseline with stakeholders (agreement of principles, goals and objectives). 3) Development of plausible scenarios. 4) Elaboration of scenarios through expert presentations and commissioned papers. M. Adams et al. / Energy Policy 39 (2011) 2550–2559 5) Iterative discussion of all of the above through a number of formal dialogue sessions (to be discussed in greater detail further on). 6) Independent assessment of stakeholder trust in process and developing recommendations (opinion surveys conducted after each formal dialogue session). 7) Continuous solicitation of written and other submissions. 8) Presentation of draft policy recommendations back to stakeholders. 9) Presentation of policy recommendations to government. 10) Enactment of policy recommendations by government. The principal difference between the two processes was the need to establish a Project Advisory Steering Committee for the RES—essentially a quasi-representative expert panel under an independent chairperson. This body was established to help address some of the deeper complexities and tensions inherent in the renewable energy stakeholder mix and to provide a source of expert feedback on recommendations. In both cases the independent facilitators were given full responsibility for moving the processes forward swiftly and for making recommendations that would be reasonable and had demonstrated support from by the majority of stakeholders (elucidated through the feedback surveys to be described below) and therefore more likely to be actionable by the Provincial Government. In doing this the facilitators had to absorb pressure in public that in a more conventional process might have led to paralysis of decision-making or a descent into private political lobbying. In both processes stakeholders were coached to commit to a process with an absolute deadline and an absolute commitment to transparency but where no particular outcome or solution was assumed. Below are set out the observations for some of the key steps outlined above. 2553 representatives attended on each occasion. The first meeting established the ‘rules of the game’ for the process together with key ‘principles for success’ in making recommendations for the administration of electricity demand-side management in Nova Scotia. The meeting also received and debated the commissioned expert paper which described four principle administrative options based on a scan of international best practice (Lipp and Baston, 2008). The objectives of the first meeting were to: discuss and try to achieve consensus on the existence of four principle options and their potential advantages and disadvantages; discuss and prioritise the key principles that will drive recommendations for a preferred administrative option for Nova Scotia; and discuss the process and timescale which will allow consensus to be achieved on a preferred option for Nova Scotia. At the initial meeting, four ‘Principles for Success’ and fifteen associated objectives were identified by stakeholders. The Principles for Success were: Accountability and oversight: there need to be ‘crisp and clear’ delineation of authority and responsibility between the delivery agents and the administrator. Administrator effectiveness: fast and market responsive decision-making. Compatibility with public policy goals: avoidance of unhelpful politics—e.g. pressure to deliver funding to constituencies, rather than to acquire cost-effective energy savings. Secure funding allocation: avoidance of misuse of funds for other budgetary purposes. 5. Discussion and observations 5.1. Energy efficiency strategy (2008) 5.1.1. Development and elaboration of plausible scenarios Prior to the first formal meeting of stakeholders a paper entitled Overview of Administrative Models for Electricity DSM was commissioned and circulated to all stakeholders in order to try and clarify definitions and characteristics of the available administrative models based on an international scan of options. The paper was drafted by independent expert consultants and was subsequently updated according to input from stakeholders during the process (Lipp and Baston, 2008). 5.1.2. Inclusion of stakeholders through formal dialogue sessions Potential stakeholders for the Energy Efficiency Strategy process were identified through discussions with readily identified actors followed by telephone and email outreach to those stakeholders and the further identification of names of potential stakeholders through a snowball sampling process.1 In addition, mid-way through the process an advertisement was placed in the local newspaper to further identify individuals and organizations that might wish to participate in the consultations and the proceeded to the recommendations stage. Three formal dialogue meetings were held with stakeholders over a six week period and up to 40 stakeholders and their 1 A number of stakeholders with an interest in energy efficiency, including environmental and social justice groups, municipalities, industrial users and smaller scale electricity consumers had already self-organized into an interest group focused on regulatory and rate-setting processes. The second meeting received five expert presentations on the four main potential administrative models which were: Utility Administration (a) with Regulatory Oversight (presented by a representative of National Grid USA), and (b) with a stakeholder Advisory Board (presented by a representative of Environment Northeast); Government Administration (presented by a representative of the Efficiency New Brunswick); Efficiency Utility Administration (presented by a representative of the Vermont Energy Investment Corp); Third Party Administration (presented by a representative of the Energy Trust of Oregon). The third meeting received the preliminary recommendations of the facilitators based on the logic of the process to that point and the likelihood of acceptance by stakeholders. The decision criteria applied in making the recommendation were: Consistency with Principles for Success Maximize Speed–Minimize Risk Maximize Stakeholder Consensus–Minimize Divisiveness Accountability to Funders (ratepayer versus taxpayer) The facilitators did not meet with stakeholders outside these processes in order to avoid generating side conversations and possible perceptions of non-transparency between stakeholder groups. 2554 M. Adams et al. / Energy Policy 39 (2011) 2550–2559 expected action and their answers to this question allowed them to send such a signal. Finally, between the first and third meetings stakeholders were asked: Fig. 1. Stakeholder scoring of administrative options. 5.1.3. Inclusion of stakeholders through regular confidential surveys of opinion In addition to the three formal meetings, four rounds of telephone and email outreach were conducted (one before each meeting) in order to ascertain views that stakeholders might prefer to express privately. Finally, some stakeholder groups sent in letters and other communications that summarised their perspectives. Broadly speaking, stakeholders engaged with the process in good spirit, although trust in the process did come under strain towards the end when certain stakeholder positions were being advanced with more vigour and persistence. This was perhaps understandable as the potential implications of the models became clearer for stakeholders and decision-time drew closer. This was reflected in a slight softening of trust in Dalhousie University’s facilitation and the Government of Nova Scotia’s ability to respond effectively to final recommendations. At the beginning of the process it was very important for stakeholders to agree that the range of administrative options open to the Province was a fair and comprehensive list, and that the advantages and disadvantages of the various options were well understood. A strong majority of stakeholders who responded (12 of 13) to the first survey of stakeholder opinion believed the Administrative Models paper ‘‘captured the main options for electricity demand-side management’’. Nearly as strong a majority (11 of 13) believed ‘‘fairly captured the potential advantages and disadvantages identified for each identified option’’. The broad consensus established on the available administrative options, together with the co-creation of criteria for success, allowed the process to move forward with some momentum based on sense of common purpose, shared knowledge and a growing level of cognitive alignment. It was vital then to establish the level of trust and support for the process itself. From before the first stakeholder meeting through to the runup to the final stakeholder meeting stakeholders were asked the following question: Based on what happened at the meeting on [date], on a scale of 1–5 where 1¼ no trust and 5¼ total trust, can you please tell me how much trust you place in Dalhousie University now to run a fair and objective consultation process? Over the six weeks trust in Dalhousie University’s process went from a score of 5.0, to 4.4, to 3.9. Care should be taken when interpreting the data; sample sizes were relatively low (typically less than 15) and respondents were not identical each time. Stakeholders were also asked: Based on what happened at the meeting on [date] on a scale of 1–5 where 1¼no trust and 5¼ total trust, can you please tell me how much trust you are willing to place now in the Government of Nova Scotia responding effectively to the recommendations of the consultation process? Over the six weeks trust in the Government’s ability to respond effectively went from a score of 3.5, to 3.3, to 2.7. Again, care should be taken in interpreting these data. Clearly stakeholders were keen to send a signal to the Government that they Based on what happened at the meeting on [date], where 1 ¼Much Less Optimistic and 5¼Much More Optimistic, are you now more or less optimistic that we will be able to make clear recommendations to the Province in a timely and consensus-based way? Stakeholder opinion on this question went from 3.2 to 3.3, demonstrating perhaps that despite the signals being sent to the facilitators and to the Government, stakeholders were not discouraged by the unfolding of the process, although the level of optimism remained moderate. 5.1.4. Stakeholder attitudes to the administrative options as the process unfolded Before each stakeholder meeting stakeholders were asked: Based on what you learned at the meeting [date], on a scale of 1–5 where 1 ¼highly undesirable and 5¼highly desirable can you please comment on what you now think will work for Nova Scotia. Again, we must note the care with which these data must be interpreted given the relatively low number of respondents and the likely variability in the respondents over the course of the process. Nevertheless, as we can see below, the popularity of the different options remained remarkably stable throughout the process. Scores should be read from right to left with the first score on the right and the final score on the left (Fig. 1). The data can be summarised as follows: (i) the Utility Administrator option was generally not favoured by stakeholders; (ii) the Government Administrator option was generally not favoured by stakeholders although it was supported strongly by some of the industrial stakeholders; (iii) the Efficiency Utility Administrator option merited both strong support and strong (if more minor) opposition and (iv) the Third Party Administrator option merited strongest and most consistent support among stakeholders, including among some of the industrial stakeholders. The outcome of the process was the recommendation of a hypothecated charge on electricity consumers equivalent to 5% of electricity costs and the establishment of a ‘performance-based’ independent agency to maximize the impact of energy conservation measures. The newly elected Government of Nova Scotia legislated to establish these measures in the fall of 2009. 5.2. Renewable energy strategy (2009) In the summer of 2009 the new Government of Nova Scotia issued a challenge for the Province to reach 25% renewable electricity generation by 2015, with greatest benefits for the social, environmental and economic health of the Province. To achieve this, a ‘Renewable Energy Stakeholder Consultation Process’ was commissioned by the Government, convened by the Faculty of Management of Dalhousie University. Stakeholders from across the Province expressed a desire to achieve the short-term objective, at the same time laying the ground for more ambitious targets to 2020 and beyond. There was also an expressed desire for the Province to achieve competitive advantage through minimizing electricity costs to consumers (large and small) and maximizing industrial technology leadership possibilities for the long term—particularly in renewable energy sectors for which Nova Scotia is particularly well endowed, such as tidal energy. M. Adams et al. / Energy Policy 39 (2011) 2550–2559 Although more complex than the EES process, the RES process broadly had a similar series of steps. Again the key observations for some of these steps are set out. 5.2.1. Development and elaboration of plausible scenarios In September 2009 a group of invited knowledgeable persons came together to construct a series of scenarios. These scenarios were developed to represent a spectrum of ‘‘possible’’ renewable energy futures that could meet the 25% target in 2015 and potentially also meet a 40% target by 2020. The session was facilitated a former Shell International executive familiar with scenario planning work. It was attended by around 80 individuals representing environmental organizations, social justice organizations, provincial and municipal governments, academic institutions, renewable energy developers, and power generators. The participants were asked: to discuss the context for the process, including highlighting the attitudes of Nova Scotians regarding the development of renewable energy capacity within the Province; to explore individual energy and technology options and the current enabling conditions found within the Province to bring these options to bear on meeting the targets of 2015 (and beyond); and to develop a series of scenarios designed to expand the thinking of what could be possible for Nova Scotia – building upon the earlier technology/enabler discussions – that would then be further examined from a specific economic, environmental and social context through the commissioning of three subsequent expert papers It was assumed that Nova Scotia’s energy demand would be 12,000 GWh in 2015 (if energy conservation measures implemented through the provincial EES was to prove effective). Thus the production of roughly 3000 GWh of renewable energy by 2015 would be required to reach the target. The intent of the scenario-building process was to provide stakeholders with a comprehensive, high-level overview of the implications of the various options, keeping in mind the illustrative nature of specific percentages for energy generation from various sources in the four scenarios. The constants for each scenario were: attaining the target of 25% electrical energy coming from renewable sources by 2015; and ensuring flexibility to allow for increasingly stringent targets to be set in the future. The four scenarios developed for further elaboration were: large-scale, centralized developments using only wind; large-scale, centralized developments capitalizing on wind and biomass (thermal generation); multi-scale, geographically diverse technologies with a primary focus on innovative, nascent technologies with the aim of creating a renewable energy development sector; and multi-scale, geographically diverse technologies with a primary focus on known technologies with a gradual integration of nascent technology as it has demonstrated cost-effectiveness 5.2.2. Inclusion of stakeholders through formal dialogue sessions Prior to the first formal meeting of stakeholders a paper entitled Nova Scotia Renewable Energy Strategy—Scenarios and Policy Options was commissioned and circulated to all stakeholders in order to ensure that (a) the information captured during the scenario 2555 planning day was accurately documented and (b) to provide clarifications to newly participating stakeholders not present at the scenario planning session of the mandate of the process and the stepping off point for the day. The paper was drafted by an independent consultant and was updated according to input from stakeholders prior to its final submission to all participants. In addition three papers were commissioned from authors who were independently nominated by the stakeholders to evaluate the impacts of the four scenarios developed at the scenario planning session from environmental, social and economic perspectives. Having established and described the scenarios, the writers were asked to assess the environmental, social and economic impacts of these initial scenarios. The three papers were intended to be a preliminarily contribution to the process that would provide a foundation for input and commentary surrounding the initial scenarios, as well as to illuminate considerations that would need to be included in any final recommendations. All material submitted to the project team by external stakeholders was provided to the writers and was reviewed to ensure that applicable information from contributing expertise and past expert sessions was assessed as part of this process and included where appropriate. In the first public session, approximately 115 stakeholders attended. The main points of the three commissioned papers were delivered. The intentions of this day were: (i) to obtain from stakeholders their insights with respect to the primary gaps and concerns that need further consideration and (ii) to build consensus around key success factors from economic, social and environmental perspectives. This session was another opportunity to ensure the mobilization of wisdom and knowledge from stakeholders into the process. All the information generated from discussions was consolidated and returned to the writers for their consideration, along with submissions offered in the days following the session. Their revised draft papers were then posted for further public comment. This iterative process of review was used throughout the process to ensure the comprehensiveness of the discussion documents. Prior to the second public session a synthesis paper (Gagnon, 2009) was prepared to: receive and absorb outputs of the process thus far, most especially the outputs of stakeholder consultations and the three commissioned papers; refine the initial scenario work and suggest candidate scenarios for Nova Scotia to meet short term and long term renewable energy targets, taking special note of economic, social, technological and environmental factors; describe the candidate scenarios in terms of relative likely costs, benefits and risks based on international experience and the particular local circumstances of Nova Scotia and Atlantic Canada; and identify enablers and barriers for options and the timescales involved. Similar to the process preceding the commissioning of the three expert papers, nominations were accepted from stakeholders and evaluated against a set of terms of reference developed in advance by the project team. In the second session, approximately 120 stakeholders attended. The main points of the synthesis paper were presented (Gagnon, 2009). The intentions of this day were: (i) to obtain from stakeholders their insights with respect to the gaps and concerns that still needed to be addressed and/or given further consideration; (ii) to secure stakeholder feedback on the paper and (iii) to identify factors that could provide the basis of recommendations to Government. Again, all information generated from discussions was consolidated 2556 M. Adams et al. / Energy Policy 39 (2011) 2550–2559 and returned to the author for consideration, along with submissions offered following the session. The revised paper was then posted for further public comment. At the final stakeholder session an interim report to stakeholders outlining draft recommendations was developed and presented (Adams and Wheeler, 2009a). The objective of the interim report was to: Table 1 Response to question ‘‘how well were the objectives of the session met?’’. Response Sep (%) Oct (%) Nov (%) Dec (%) Completely met Partially met Somewhat met Not met 32.5 50 17.5 0 15 54 24 7 8 60 25 8 45 35 14 6 absorb the outputs of the process, most especially the outputs of stakeholder consultations and the various papers; describe the recommended candidate scenarios in terms of applicable timeframes (i.e. when would they come on-stream), and the relative likely costs, benefits and risks; describe the recommended administrative frameworks and program requirements necessary to optimize the success of the various candidate scenarios; and describe the policy/regulatory implications based on the experiences within other jurisdictions and the particular local circumstances of Nova Scotia and Atlantic Canada. The project team reviewed all materials accumulated to date, including submitted reference materials, the three commissioned papers, the draft synthesis paper, stakeholder commentary, and the outcomes and notes taken from the stakeholder consultation sessions. Inputs gathered from a series of expert, content-driven meetings (held on key themes such as biomass sustainability, cost implications and policy implications) were also included. This interim report was circulated to stakeholders and also posted publicly for review on the project website. At the final public session, approximately 125 stakeholders attended and the main points of the Interim Report to stakeholders were presented. The intentions of this day were: (i) to effectively present the Interim Report to stakeholders; (ii) to secure stakeholder feedback on the Interim Report and (iii) to discuss any remaining concerns and address any outstanding issues. Ultimately the objective was to crystallize recommendations where significant consensus was identified and to provide an opportunity for stakeholders to respond to draft recommendations related to issues where only modest consensus was possible. The consolidation of the information and input through this process resulted in the final report that was submitted to the Government of Nova Scotia in late December 2009 (Adams and Wheeler, 2009b). Similar to the previous DSM process, the principal facilitator did not meet with stakeholders outside these processes in order to avoid generating side conversations and possible perceptions of non-transparency between stakeholder groups. 5.2.3. Inclusion of stakeholders through regular confidential surveys of opinion In order to gauge the level of stakeholder support for the outcomes of each session, shortly after each of the four stakeholder meetings an on-line survey was issued to all registrants to capture their thoughts and attitudes towards the process. The intention was to use this information to determine: (i) how well stakeholders felt their input was being captured; (ii) what aspects of the sessions could be improved; (iii) how well the stakeholders felt their concerns were being addressed; (iv) how well each session met the expressed objectives of the day; (v) how confident stakeholders were in the Dalhousie team to run a fair and objective process and (vi) the level of stakeholder confidence that the Government would respond effectively to the process recommendations. There was also a general comment section where stakeholders could offer their input in a free form. The results of Fig. 2. Key outputs from stakeholder surveys. each survey were then presented at the following session, unedited. While there were minor fluctuations in the level of satisfaction with the process over time, the final survey reflecting the stakeholder attitudes about the whole process and their satisfaction with the direction of the final recommendations were positive. Table 1 provides an overview of stakeholder satisfaction with session objectives being met throughout the process. Given the very significant amount of material that needed to be presented and discussed, it was particularly pleasing to see the level of confidence in objectives being met at least partially throughout the process, and particularly at the final session. Fig. 2 demonstrates the average output for each of the sessions for two other key questions with the bold text representing the output from the culminating session. 5.2.4. Stakeholder attitudes towards the legitimacy of the process While the primary intention was to develop policy recommendations created from a consensual stakeholder inclusive process, a secondary objective was to deliver the social/political license that would provide the Government a measure of confidence to act. To this end, it was necessary to monitor stakeholder opinion regarding the perceived legitimacy of the process and the level of expectation stakeholders had that the Government would act. Fig. 3 provides the output of this survey. The results from the final session are in bold. As can be seen, there was a reasonably high level of confidence in the facilitation team as well as trust in the government to respond effectively to recommendations—both ending on upward trends. As noted above, the final policy recommendations were developed through dialogue involving several hundred stakeholders, many of whom had a direct financial stake in the outcome. Consensus was not absolute, but it was predicated on the premise that the policy recommendations represented the best value for money for consumers and also contributed to the growth and competitiveness of the provincial economy. A key element of the policy recommendations was the development of policy that would safeguard and enhance the natural environment, as well as contribute to social justice, with particular consideration for mitigating ‘energy poverty’. In order to meet or exceed the 2015 Provincial target and achieve compliance with climate change and other goals, a pragmatic, low risk, low cost strategy was advocated whereby: the power utility and independent power producers are responsible for lowest cost delivery of the bulk of the target, M. Adams et al. / Energy Policy 39 (2011) 2550–2559 2557 Government’s willingness in both situations to use the process outputs as the basis for their new public policies on these two issues. Fig. 3. Key outputs from stakeholder surveys. overseen by a new renewable energy procurement body and (potentially) a new system operator; community-based renewable energy projects receive a guaranteed price for electricity with an initial goal of 100 MW installed capacity (with a secondary aim of promoting community economic development); and ordinary citizens and small and medium sized enterprises (SMEs) would be encouraged to become engaged in renewable energy generation and use. In the case of the demand-side management process, new legislation based on those recommendations was passed in the fall of 2009 (Government of Nova Scotia, 2009). And in the case of renewable electricity generation, the new ‘Renewable Electricity Plan’ was announced on April 23, 2010, by Darrell Dexter, the Premier of the Province of Nova Scotia. Most major recommendations put forth were embraced; key items included: enacting legislation committing to a 2015 target of 25% renewable electricity; a new commitment of 40% Renewable Electricity by 2020; the announcement of a plan to establish a community-based The Government of Nova Scotia announced its response to these recommendations in April 2010. 6. Outcomes In 2007 the Nova Scotia government enacted the Environmental Goals and Sustainable Prosperity Act (Government of Nova Scotia, 2007). While this legislation included a range of targets and specific goals, the overarching theme was one of creating an economy that was based on the concept of ‘sustainable prosperity’. Key elements in the Act related to energy security and GHG emission reductions; a particularly challenging task given that 88% of the province’s electricity generation was at that time based on fossil fuels, 75% of which was imported coal. The transition to a more secure energy future required an equitable focus on demand-side management to reduce the overall energy needs of the region, and the integration of renewable energy. Both strategies endeavoured to impact the key drivers of energy sustainability; long-term energy security (and ultimately future costs) and GHG emission reductions. As noted previously, the number and diversity of stakeholders impacted by the adoption of energy efficiency or renewable energy strategies can be daunting for policy-makers to address. However, for Nova Scotia to deliver the radical transformation needed to achieve ‘sustainable prosperity’, new public policy related to energy demand and energy generation had to be developed. These reforms also had to be developed in the shortest time possible and with the greatest degree of social license in order for this transformation to be effective on the scale required. Policy makers expressed that a novel strategy for creating policy was likely required. Therefore, in both cases (energy efficiency policy and renewable energy generation policy) the government sought to maximize the inclusivity and accountability of the policy development process. Any success of this innovative approach was contingent on four key elements: use of an independent third party facilitator to ensure the objective development of recommendations that were free from influence of special interests and lobbying (in this case the Dalhousie University Faculty of Management); use of transparent and iterative approaches to ensure clarity for all stakeholders on how their contributions were being integrated into the policy development process; concurrent ‘check ins’ with stakeholders to gauge their level of confidence in the process and the resulting outputs; and feed-in tariff for renewable energy developments by municipalities, First Nations, co-operatives and non-profit groups; the assurance that a portion of the large- and medium-scale renewable energy projects will be set aside for Independent Power Producers (IPP), with a bidding process that would be overseen by a new authority, the Renewable Electricity Administrator (in the stead of the local monopoly electrical utility); and the establishment of a feed-in tariff for tidal energy in the Bay of Fundy. It should also be noted that since April 2010, new announcements regarding major investments into to renewable energy research and development have been announced—including: a $20M investment into FORCE (Fundy Ocean Research Centre for Energy) by the Government of Canada, and the award of a $11M contract to FORCE for the production and installation of four subsea cables at the test site in the Bay of Fundy; the approval of a 60 MW biomass-fired cogeneration facility to be operated in Northern Nova Scotia by NewPage Pulp and Paper; and an MOU between the Province of Nova Scotia and Newfoundland to build a subsea cable to allow for the transition of a portion of the 3000 MW of hydro-electric power that is currently under development in the Lower Churchill region of Newfoundland. This will contribute to Nova Scotia’s renewable energy targets, but will also provide key stability to the transmission and distribution (T&D) system in Nova Scotia [ideally] permitting increased capacity from ‘variable’ sources, such as wind and tidal, than would otherwise be possible with the current T&D system. The willingness on the part of policy-makers to accept the majority of recommendations that arose out of these participatory mechanisms should reinforce the level of trust between stakeholders and policy makers. Although there will inevitably be ‘special pleading’ from specific groups seeking to maximize their advantage from the overall changes announced by the Government of Nova Scotia, it is believed that the policy frameworks now in place are internally consistent and resilient, precisely because of the process that took place to design them. 7. Conclusions While the ultimate success of these particular policies cannot be assessed at this time, by incorporating multiple viewpoints and perspectives into the development process, these results should be both resilient and adaptive to future conditions, 2558 M. Adams et al. / Energy Policy 39 (2011) 2550–2559 including changes in political priorities. It should be noted that the processes described in this paper spanned several years when a significant change in political leadership occurred in Nova Scotia – from a conservative to a social democratic government – and yet cross-party consensus prevailed throughout. At times during both processes, significant negative opinion was expressed by particular parties, often aimed at the monopoly energy supplier or the Government of Nova Scotia and its agencies. However, the fact that the principal facilitator was both unpaid and his employer objective, that the Government of Nova Scotia and the monopoly utility were committed to embrace the outcomes without trying to influence them, and that all voices were included, made it very difficult for the process itself to be undermined. Thus, the occasional strident voices seeking media attention and external influence outside the process appeared self-serving whether they came from industry, environmental organizations, or developers. Irritation was certainly expressed with the facilitators for not being amenable to conventional lobbying or making special provision in large meetings for dominant voices, but this served only to reinforce the perceived integrity of the process. Of course, any process can be captured by political, institutional or individual forces through the explicit or tacit exercise of power through control of knowledge, technical expertise or language. This may happen in international policy-making (Haas, 1992), organizational settings (DiMaggio and Powell, 1983), and everyday social interactions (Foucault, 1980), as well as in the field of energy policymaking. However, as we believe has been demonstrated here, stakeholders and policy-makers can build on a clear political target (Enzensberger et al., 2002), and address problems and deliver outcomes that are built on inclusivity, transparency and trust. By employing novel methodological approaches to address the various factors at play and meet stakeholder expectations, policy makers can adopt more creative and innovative approaches such as those suggested by Thompson (2006), Mendonc- a et al., (2009), Rayner (2010) and Ricci et al. (2010) provided they are prepared to relinquish control to an independent process and accept the emergent nature of the outcomes. Given the difficulty of establishing national and international consensus on effective responses to climate change, as evidenced by the failure of the Copenhagen process (Wheeler et al., 2010), it is now worthwhile to consider the advantages for Canada on extending the processes described in this paper to other provincial jurisdictions. Provinces such as Alberta and Saskatchewan with high dependencies on fossil fuel provision need to radically improve their administrative arrangements for delivering energy efficiency. Provinces such as British Columbia and Quebec, with traditionally very high levels of hydro-electricity provision, may need new processes to enable more effective export of their endowments, both to other provinces and to the United States. Provinces such as Ontario and Newfoundland, with aggressive plans for development of new renewable resources, will require processes to that legitimately engage their own citizens, including First Nations, in how those resources will be developed and exploited. Whilst there is no attempt here to broaden the public policy implications of the Nova Scotia case beyond Canada, there may be especially relevant insights from this work for jurisdictions with high levels of fossil fuel dependency and/or low trust environments elsewhere in the world. Acknowledgements We would like to acknowledge the support and hard work of Penny Slight, Zoe Caron (both Dalhousie University’s Eco-Efficiency Centre) and Corrine Cash (University of Waterloo) – as well as the eleven graduate students from the School of Resource and Environmental Studies (Dalhousie University) – who were instrumental in the successful delivery of the two stakeholder participation processes referred to in this work. In addition we would like to note that two anonymous referees made very useful and objective comments that helped improve the final manuscript; their input is appreciated. References Adams, M., Wheeler, D., 2009a. Interim Report for Stakeholders: Stakeholder Consultation Process for a New Renewable Energy Strategy for Nova Scotia. Dalhousie University Faculty of Management, Halifax, Canada. Adams, M., Wheeler, D., 2009b. Stakeholder Consultation Process for: A New Renewable Energy Strategy for Nova Scotia. Nova Scotia Department of Energy, Halifax, Canada. Adler, P., Kwon, S., 2002. Social capital: prospects for a new concept. The Academy of Management Review 27 (1), 17–40. Agterbosch, S., Breukers, S., 2008. Socio-political embedding of onshore wind power in the Netherlands and North Rhine–Westphalia. Technology Analysis and Strategic Management 20 (5), 633–648. Agterbosch, S., Meertens, R.M., Vermeulen, W.J.V., 2009. The relative importance of social and institutional conditions in the planning of wind power projects. Renewable and Sustainable Energy Reviews 13 (2), 393–405. Bellaby, P., 2010. Uncertainties and risks in transitions to sustainable energy, and the part ‘trust’ might play in managing them: a comparison with the current pension crisis. Energy Policy 38 (6), 2624–2630. Blázquez Garcı́a, G., Calero de Hoces, M., Lehtine, T., 2003. Policy networks of wind energy: the story of the first commercial wind farm in Spain. Wind Engineering 27 (6), 461–472. Breukers, S., Wolsink, M., 2007. Wind power implementation in changing institutional landscapes: an international comparison. Energy Policy 35 (5), 2737–2750. Buchholz, R., Rosenthal, S., 2004. Stakeholder theory and public policy: how governments matter. Journal of Business Ethics 51, 143–153. Chatham House, 2010. Sustainable Energy Security: Strategic Risks and Opportunities for Business. Chatham House, London, UK. De Marchi, B., Ravetz, J., 2001. Participatory approaches to environmental policy. Concerted Action EVE, Policy Research Brief, No. 10. DiMaggio, P., Powell, W.W., 1983. The iron cage revisited: institutional isomorphism and collective rationality in organizational fields. American Sociological Review 48, 147–160. Dorian, J., Franssen, H., Simbeck, D., 2006. Global challenges in energy. Energy Policy 34 (15), 1984–1991. Enzensberger, N., Wietschel, M., Rentz, O., 2002. Policy instruments fostering wind energy projects—a multi-perspective evaluation approach. Energy Policy 30 (9), 793–801. Fishkin, J.S., 2002a. Deliberative Democracy. In: Simon, R.L. (Ed.), The Blackwell guide to social and political philosophy. Blackwell Publishers Ltd., Malden, pp. 221–291. Fishkin, J.S., 2002b. Deliberative polling and public consultation. Retrieved from /http://www.essex.ac.uk/ecpr/events/jointsessions/paperarchive/turin/ws24/ Fishkin.pdfS. Freeman, R.E., 1984. Strategic Management: A stakeholder approach. Pitman, Boston. Foucault, M., 1980. Power/Knowledge: Selected Interviews and Other Writings, 1972–1977. Random House, Toronto. Gagnon, Y., 2009. Synthesis Paper: A Renewable Energy Strategy for Nova Scotia. Dalhousie University Faculty of Management, Halifax, Canada. Gan, L., Eskeland, G.S., Kolshus, H.H., 2007. Green electricity market development: lessons from Europe and the US. Energy Policy 35 (1), 144–155. Government of Nova Scotia, 2007. Environmental Goals and Sustainable Prosperity Act. Government of Nova Scotia, Halifax, Canada. Government of Nova Scotia, 2009. Efficiency Nova Scotia Corporation Act. Government of Nova Scotia, Halifax, Canada. Greening, L.A., Bernow, S., 2004. Design of coordinated energy and environmental policies: use of multi-criteria decision-making. Energy Policy 32 (6), 721–735. Haas, P.M., 1992. Introduction: epistemic communities and international policy coordination. International Organization 46, 1–35. Holburn, G., 2009. Attracting private investment in renewable energy. Presentation to National Forum on Management, HEC Montreal, October. Holmes, T., Scoones, I., 2000. Participatory environmental policy processes: experiences from North and South. IDS Working Paper 113. Jacobsson, S., Lauber, V., 2006. The politics and policy of energy system transformation-explaining the German diffusion of renewable energy technology. Energy Policy 34 (3), 256–276. Jobert, A., Laborgne, P., Mimler, S., 2007. Local acceptance of wind energy: factors of success identified in French and German case studies. Energy Policy 35 (5), 2751–2760. Juhl, D., 2010. The Interview: Dan Juhl. Renewable Energy World North America Magazine, 2(1). Retrieved from /http://www.renewableenergyworld.com/rea/ news/article/2010/02/the-interview-dan-juhlS. Khan, J., 2004. Doctoral Thesis: Local politics of renewable energy: project planning, siting conflicts and citizen participation. Retrieved from /http://www. tdcat.cesca.es/TESIS_UAB/AVAILABLE/TDX-0925109-123324/ggj1de1.pdfS. M. Adams et al. / Energy Policy 39 (2011) 2550–2559 Kydd, A., 2010. Learning together, growing apart: global warming, energy policy and international trust. Energy Policy 38 (6), 2675–2680. Lipp, J., Baston, D., 2008. Electricity Conservation in Nova Scotia: administration of demand side management approaches. Overview of administrative models for electricity DSM. Dalhousie University Faculty of Management, Halifax, Canada. Lipp, J., 2007. Lessons for effective renewable electricity policy from Denmark, Germany and the United Kingdom. Energy Policy 35 (11), 5481–5495. Mendonc- a, M., Lacey, S., Hvelplund, F., 2009. Stability, participation and transparency in renewable energy policy: lessons from Denmark and the United States. Policy and Society 27 (4), 379–398. Meyer, N.I., 2003. European schemes for promoting renewables in liberalized markets. Energy Policy 31 (7), 665–676. Mitchell, C., Woodman, B., 2010. Toward trust in regulation—moving to a public value regulation. Energy Policy 38 (6), 2644–2651. Munda, G., 2004. Social multi-criteria evaluation: methodological foundations and operational consequences. European Journal of Operational Research 158 (3), 662–677. Nahapiet, J., Ghoshal, S., 1998. Social capital, intellectual capital, and the organizational advantage. The Academy of Management Review 23 (2), 242–266. Rayner, S., 2010. Trust and the transformation of energy systems. Energy Policy 38 (6), 2617–2623. Ricci, M., Bellaby, P., Flynn, R., 2010. Engaging the public on paths to sustainable energy: who has to trust whom? Energy Policy 38 (6), 2633–2640. Smith, G., 2001. Taking deliberation seriously: institutional design and green politics. Environmental Politics 10 (3), 72–93. Söderholm, P., Ek, K., Pettersson, M., 2007. Wind power development in Sweden: global policies and local obstacles. Renewable and Sustainable Energy Reviews 11 (3), 365–400. Stirling, A., 2008. Science Technology and Human Values 33, 262–294. 2559 Thompson, A., 2006. Management under anarchy: the international politics of climate change. Climatic Change 78, 7–29. Upreti, B.R., 2004. Conflict over biomass energy development in the United Kingdom: some observations and lessons from England and Wales. Energy Policy 32 (6), 785–800. Upreti, B.R., van der Hors, D., 2004. National renewable energy policy and local opposition in the UK: the failed development of a biomass electricity plant. Biomass and Bioenergy 26 (1), 61–69. Van Rooijen, S., van Wees, M., 2006. Green electricity policies in the Netherlands: an analysis of policy decisions. Energy Policy 36 (1), 60–71. Vigar, G., Healey, P., 2002. Developing environmentally respectful policy programmes: five key principles. Journal of Environmental Planning and Management 45 (4), 517–532. Wheeler, D., Sillanpää, M., 1998. Including the stakeholders: the business case. Long Range Planning 31 (2), 201–210. Wheeler, D., Medalye, J., Adams, M., 2010. Creating sustainable value through entrepreneurial and stakeholder inclusive responses to climate change: an historical-institutional perspective. In: Proceedings of the Politeia Forum on Business Ethics and Corporate Social Responsibility in a Global Economy. Milan, February 2010. Wolsink, M., 2007. Planning of renewables schemes: deliberative and fair decision-making on landscape issues instead of reproachful accusations of non-cooperation. Energy Policy 35 (5), 2692–2704. Wüstenhagen, R., Wolsink, M., Bürer, M.J., 2007. Social acceptance of renewable energy innovation: an introduction to the concept. Energy Policy 35 (5), 2683–2691. Zoellner, J., Schweizer-Ries, P., Wemheuer, C., 2008. Public acceptance of renewable energies: results from case studies in Germany. Energy Policy 36 (11), 4136–4141.
© Copyright 2026 Paperzz