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Article

Applying a Practice Lens to Local Government Climate Change Governance: Rethinking Community Engagement Practices

School of Global Urban and Social Studies and the Centre for Urban Research, RMIT University, Melbourne, VIC 3001, Australia
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Author to whom correspondence should be addressed.
Sustainability 2021, 13(2), 995; https://doi.org/10.3390/su13020995
Submission received: 19 December 2020 / Revised: 12 January 2021 / Accepted: 14 January 2021 / Published: 19 January 2021
(This article belongs to the Section Air, Climate Change and Sustainability)

Abstract

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Governments commit substantial time and resources engaging individuals and households to reduce their greenhouse gas emissions. These approaches, based largely upon behaviour change theories, have been criticised for their limited reach and effectiveness by practice theorists who have offered an alternative approach, broadening the focus beyond individuals. While practice theory has provided valuable insights into the energy consuming activities of households it has gained limited traction as a way to analyse and inform government practices and policy making. We address this by applying a practice lens to climate change community engagement practices performed by Australian local governments. Drawing on 29 interviews with practitioners and analysis of 37 Australian local government climate strategies, we examine the bundle of practices that constitute climate change community engagement: recruitment, engagement and evaluation. We consider how these practices are situated vis-a-vis other climate governance practices (regulation, service delivery, infrastructure provision and advocacy) as well as internal local government processes. Using a practice lens reveals the weaknesses in current engagement approaches which we contend are limiting efficacy. We draw upon Spurling et al.’s conceptualisation of re-crafting, re-integrating and substituting practices to consider how climate change community engagement practices might be reconfigured to improve their effectiveness.

1. Introduction

The super wicked nature of climate change as a policy problem requires solutions that can be immediately acceptable to a population, can embed themselves within the everyday activities of that population and have the capacity spread rapidly throughout society and drive down emissions [1]. Achieving this requires a theoretical framework capable of identifying and understanding the complexities of these everyday activities undertaken by individuals, organisations and governments [2,3]. It must also be capable of zooming in and out in focus between specific activities and broader systemic structures and influences [4].
Practice theory meets these requirements by offering a nuanced understanding of everyday activities undertaken by individuals, households, businesses, organisations and governments [5]. Drawing on Giddens [6], practice theory rejects the notion that the actions of individuals are solely guided by the structures within which they exist or that those actions are shaped solely through human agency. Instead, it transcends the structure/agency dualism creating a more dynamic view of practices as entities contributing to their own reproduction within society, simultaneously shaping and being shaped by the social context [7].
As a unit of analysis, the defined concept of a practice reflects the diversity of thought within theories of practice, focusing on elements, relationships between elements and positioning within broader socio-technical frameworks [8]. Reckwitz [9] sought to summarise key features through the construction of an “ideal type” of a practice: “A practice is, thus, a routinized way in which bodies are moved, objects are handled, subjects are treated, things are described and the world is understood” [9].
In this paper, we employ Shove et al.’s [7] model of the primary elements of competencies, materials and meanings that constitute a practice and which aligns to Reckwitz’s [9] definition. The competencies required to perform a practice corresponds with how “bodies are moved” and things are “handled”, the materials required with “objects” and “subjects” and meanings with how “things are described and the world is understood” [7,9]. Shove et al. [7] recognise that their construction compresses additional complexity afforded by other approaches [8], but argue that doing so allows for focus not just on the individual elements that constitute a practice but also how they relate to one another and how these relationships can change over time.
Because practices are “alive” they exist both as a commonly defined understanding (e.g., cooking, cycling, walking, lighting etc.) as well as in a multitude of variations, reflecting how they are enacted. This tension between the static unit of analysis and how it lives is addressed through Schatzki’s [10] framing of practice-as-entity and practice-as-performance. A practice-as-entity exists across time and space as a concept that can be understood in terms of its component elements and its relationships to other practices; it exists even when the practice itself is not being actively carried out [11].
In addition to the intra-relationships between the constituent elements of a practice, practice theory pays equal attention to the interactions between different practices. These include loose configurations of practices that are brought together in bundles by being physically, thematically or temporally co-located [7]. For example, within households, bundles may include separate practices that are dependent on the same materials (e.g., water for cooking, washing and laundry). Other practices are more closely interwoven in a complex of practices, in which each practice is co-dependent upon another for its successful performance (e.g., meal-related practices, such as shopping, food preparation, cooking, eating and disposal of waste) [12].
For governments, practice theory offers a deeper understanding of the complexities associated with the everyday household practices that produce greenhouse gas emissions, but also an opportunity to reflect upon their own governance practices. This includes a shift away from the dualism of interventions focusing on individual agency (e.g., “do your bit”) [13,14] or structural changes enacted through policy [15] when responding to climate change.
While practice theory has proved valuable in analysing and understanding everyday activities that contribute to the causes of climate change [13], it has struggled to gain acceptance within governments as a working approach to develop policy and interventions to reduce greenhouse gas emissions [16]. By contrast to the widespread adoption of behaviour change theories within government circles [17,18], the deliberate use of practice theory has primarily been limited to the experimental scale [19,20,21]. Positing an alternative to behaviour change-based governance requires more than simply swapping out one theoretical approach for another. Practice theory’s focus on the complexity of individual practices as well as the relationship between them has presented problems for policymakers seeking to understand their role in designing effective interventions (17). We contend that a necessary first step is to understand how current climate governance is structured, which has been historically under-examined by practice theory [22].
Applying practice theory offers a deeper understanding of how climate governance activities are constructed, what sustains them, how they interact with one another and how they relate to the household practices they seek to influence [23]. By doing so, we not only gain a rounded picture of how policy and interventions work but also how practice theory might shape them to improve their efficacy in reducing household emissions [21]. To test how this analysis might be developed and applied and what it might tell us about the value of applying a practice lens to government activities, we examine the practices of climate change community engagement, as performed by Australian local governments.
Lacking the regulatory, service or financial powers available to many of their international counterparts, Australian local governments seeking to reduce community-based greenhouse gas emissions are more reliant on voluntary action being taken by others, such as households [24,25,26]. This is achieved through community engagement programs that seek to convince individuals of the need to act on climate change and empower them with the resources and capacity to do so [27,28,29,30]. These programs are underpinned by an assumption that individuals can, through altering their behaviours and choices, reduce their personal emissions [31] and form part of a global appreciation and use of behaviour change theories to tackle policy problems by governments [32,33].
This reliance upon behaviour change theories has already been the subject of practice-based critiques [13,34]. Primarily, practice theory is critical of a behaviour change focus on the role of the individual while neglecting broader systemic influences [13]; by contrast, practice theory—with its positioning of the individual as a performer of practices—broadens the view of policymakers and practitioners to the practice (e.g., washing, heating, driving etc.) and the relationships between individuals and systems that sustain it [7]. Despite this, behaviour change-based approaches remain a key component of Australian local government climate change community engagement [35]. Our contention is that while practice theory has explained what needs to change in thinking about what households do (i.e., a broader focus on practices rather than individuals), it has less successfully explained how that is to be achieved and the implications for what governments do [22].
In this vein, here, we combine an analysis of a set of climate governance practices performed by Australian local governments and Spurling et al.’s [19] methodology of how practices can be altered through re-crafting or substituting practices or changing how they interlock with one another. Recrafting refers to changing the practice enough that it recognisably remains the same practice but is performed in a manner that has a reduced environmental impact (e.g., switching from drying clothes in a dryer to hanging them on a washing line). Practices may be substituted to achieve similar but more sustainable outcomes, such as changing from driving to catching public transport, walking or cycling, to get to work. Finally, it is possible to identify elements in the relationships between different practices (and between different bundles and complexes) and reconfigure these (e.g., shifting eating routines to integrate with other daily practices and thus, reducing opportunities for unhealthy forms of eating) [19].
We begin by examining the elements that constitute practices (competencies, materials and meanings) drawing on the work of Shove and others [7,9,36]. We consider an intervention methodology based upon re-crafting or substituting practices or through reconfiguring relationships between different practices [19]. We then define the governance framework within which community engagement practices sit, including other climate governance practices, such as the use of regulations, the provision of supportive infrastructure, the delivery of services and advocacy to other stakeholders on behalf of their communities, as well as the influences of internal process practices, such as local government strategy management, governance and political cultures. We then define and examine the three distinct practices performed by Australian local governments that form what we call community engagement: recruitment to a program, engagement to change a specific practice and evaluation of the impact of these programs. We consider the relationship between these three practices within a bundle of community engagement practices.
This analysis identifies weaknesses in current forms of local government climate change community engagement, including limited resourcing resulting in short-term interventions; a reliance on concern for climate change as a motivation for action and assumptions about the ability of the individual to change their behaviours. We explore opportunities to reconfigure or shift these practices, drawing on the work of Spurling et al. [19]. They talk about reconfiguring practices in three different ways: re-crafting (changing the composition of an individual practice), substituting (replacing one practice with another) or re-integrating (changing the relationships between different practices) [19]. We apply this approach, identifying examples where local governments have already undertaken forms of re-crafting, substituting or re-integrating, and consider how these approaches might be applied more broadly to improve the effectiveness of interventions.

2. Materials and Methods

The research for this paper is based upon a mixed-methods approach comprised of interviews with local government community engagement practitioners and document analysis of local government sustainability and climate change strategies. Semi-structured interviews were conducted with 29 local government officers and managers responsible for the delivery of climate change community engagement programs from across Australia. An initial set of interviewees was selected based upon their participation in local government networks, such as the greenhouse alliances in Victoria [37]. Additional interviewees were selected based upon the recommendation of this first batch of local government officers.
Interviews were conducted between July and September 2015, either face-to-face in the offices of the interviewees or by phone. The interviews sought to establish the professional capacities of staff and how these influenced their understandings of community engagement methodologies, including the recruitment, engagement and evaluation methods employed. Practitioners were also asked about the role of community engagement within their local governments in relation to other governance practices. Finally, the interviews sought information about specific community engagement programs managed by the interviewees, including target audiences, methods employed and the resources available to perform these practices.
The interviews were supplemented by an analysis of 37 local government climate change and sustainability strategies, again drawn from local governments across Australia. This sought to understand the strategic motivations of local governments responding to climate change and the perceived role of households participating in that response through community engagement practices. The local government strategies were selected through a desktop analysis of local government websites with an emphasis on local governments that specified a clear role for community engagement in their climate change and sustainability strategies. The selection of interviews and strategies is not intended to be representative of all Australian local governments, and is intentionally biased towards better resourced local governments, often in metropolitan areas.
Data from a textual analysis of the strategies and the interviews was entered into qualitative data analysis software (Nvivo) and coded thematically.

3. Analysing Local Government Climate Governance and Community Engagement Practices

Local government climate change community engagement practices are situated within a broader governance framework which influences how these practices are structured and performed. These include other climate governance practices that mitigate against the production of greenhouse gas emissions or adapt to the projected impacts of climate change, including regulation, infrastructure provision, service delivery and advocacy. In addition, what might be termed internal process practices central to the general operation of local governments, such as strategy development, management and political cultures, are also influential in both hindering and supporting the effectiveness of community engagement practices [2,38,39,40].
In this section, we draw upon the analysis of local government climate change and community engagement strategies as well as interviews with local government practitioners to explore these related practices to understand the implications of their structures, performances and relationships for climate change community engagement. We then apply a practice lens to each of the community engagement practices (recruitment, engagement and evaluation).

3.1. Local Government Climate Governance and Internal Process Practices

In addition to community engagement, climate governance practices performed by local governments include regulation, infrastructure provision, service delivery and advocacy. Regulatory practices include land use planning provisions and guidance, local traffic laws and ecologically sustainable design requirements for new building approvals [41]. Infrastructure provision may include local sustainability centres that provide direct demonstrations of low or zero carbon forms of household practices, as well as supportive built forms, such as walking and cycling paths [42]. Service delivery includes domestic waste collection and recycling that directly addresses the production of household greenhouse gas emissions arising from consumption practices [43]. Advocacy practices, such as engaging in formal consultations with state and Federal governments, seek supportive policy frameworks and resourcing [44,45,46,47].
Internal process practices within local governments include strategic management in which climate change governance practices are planned and resourced through multi-year strategies to meet climate change mitigation and adaptation objectives [48,49,50,51,52]. The form of these strategies is broadly consistent throughout the sector, including measurement of baseline emissions, establishing emissions reduction targets, developing and implementing a plan of action and evaluating its effectiveness, both in terms of the efficacy of governance processes, as well as outcomes in the form of reduced emissions for the municipality [53]. This consistency reflects the influence of the Cities for Climate Protection program, which created a structured process for local governments to tackle climate change in the early 2000s [54,55]. Initially focused on local government corporate emissions, this process subsequently expanded in scope to account for community emissions, including those from households [45,56,57]. Strategies have more recently included adaptation measures that seek to protect council assets and services and improve community resilience to projected climatic impacts [58,59].
Finally, climate change governance practices, including community engagement, are influenced by management and political culture practices that may actively weaken support for, or undermine the effectiveness of climate governance [60]. These include narrow perspectives of professional practices that resist change [61,62]: “I feel like there’s a high proportion of people in councils who are … rusted on. They’re kind of hanging out for retirement. They don’t want anything to get more difficult or more complex” (Interviewee E).
While local governments possess creative individuals responding to climate change [10], these individuals may be constrained by internal structures and cultures within local government that emphasise risk and the limited role of councils [63]. Practitioners note that this often results in a contest between a conservative risk management culture, as expressed by senior managers and directors, and progressive councillors wishing to act on climate change:
“Our executive is very fiscally conservative. They’ve almost kind of been recruited to play that role because we were in this very financially constrained situation, so it’s their role to tighten the screws. The irony is that, at the moment, we have this super progressive council, so it will be very interesting to see how that plays out, whether that has an influence on what gets done, whether things continue to be constrained through that bottleneck of the executive”
(Interviewee E)

3.2. Climate Change Community Engagement Practices

Local government climate change community engagement seeks to influence the performance of everyday practices carried out within households, such as heating and cooling, lighting, cooking, washing and entertaining, that contribute to the production of greenhouse gas emissions [64]. Our analysis of local government strategies and interviews with officers have identified three primary community engagement practices, recruitment, engagement and evaluation, that create a step-process bundle we call community engagement. The first step, recruitment, refers to the communications strategies and techniques employed to identify and target individuals and households, promote initiatives and encourage households to participate in programs. The second step, engagement, refers to the actual process the individual or household is encouraged to undertake in order to enact a shift in the performance of their everyday practices. Finally, the third step, evaluation, records whether climate change community engagement interventions are effective in meeting their objectives. In this section, we apply Shove et al.’s [7] formulation of practices (materials, meanings and competencies) to examine community engagement practices, reveal weaknesses in current performance and identify opportunities to improve their effectiveness.

3.3. Recruitment Practices

How Australian local governments recruit households to climate change community engagement programs is heavily influenced by the available communication channels (materials) and the limited financial capacity of local governments (competencies). This results in the use of more affordable avenues such as local newspapers and council publications [65,66,67], supplemented by public outreach opportunities, such as festivals:
“That is actually a very good platform to reach out to the people that aren’t currently already interested or that minded, just because, you know ‘oh a festival, you can come along, you can look at markets, there’s music, there’s also free workshops and activities’ that sounds fun and interesting, we think”
(Interviewee I)
Practitioners will also seek to recruit within audiences that have already been engaged, using cross-promotional opportunities in engagement practices to highlight other topics that may be of interest:
“We cross-promote all our different activities at each workshop, people are like ‘oh, I might go to this sustainable gardening one on the weekend or I’d love to go to that cooking workshop to learn how to use food scraps’, so, yeah, we do get a fair bit of crossover in that respect”
(Interviewee C)
The primary meaning informing recruitment practices is that individuals are part of a collective response to climate change with council filling in gaps in information or improving the skills of individuals to help them change their behaviours. These meanings are set out in local government strategies: “the pursuit towards a sustainable future also requires a shift in values and behaviour by the community” [52], “success depends on the support and involvement of community stakeholders” [68] and “positive environmental change in the future can only be achieved through influencing and altering our current lifestyle and behaviours which are unsustainable” [69].
The use of climate change as the primary motivation to engage individuals raises two potential issues that limit the effectiveness of this type of recruitment practice. Firstly, it confronts well understood psychological barriers specifically associated with climate change [70,71]. Secondly, it places “doing something about climate change” in competition with other meanings associated with everyday household practices [64].
Psychological barriers include fatalistic beliefs about the efficacy of acting, contested political influences, negative social norms that reinforce existing forms of practice and financial barriers to changing household practices [70,71,72,73,74]. From a practice perspective, the use of climate change as a motivation for action clashes with other meanings associated with the performance of everyday household practices, few of which have to do with the consideration of the environmental impacts of these practices [7]. By contrast, the need to act on climate change can appear less immediate and attractive only to a limited audience, a weakness recognised by local government practitioners:
“How do you get the people who should be doing all of this instead of the group that’s already invested?”
(Interviewee I)
The conflict with psychological barriers associated with acting on climate change often leads to limited success in recruitment, where a like-minded group engages, leaving the wider population much more challenging for local governments to reach. The conflict with meanings associated with everyday practices not only blunts the potential to recruit households, but also results in missed opportunities that would arise from a better understanding of such practices.

3.4. Engagement Practices

The meanings associated with recruitment practices (namely, that there is a need to respond to climate change and that this is achieved through building the capacities of individuals) also flow through engagement practices. The constrained financial resources that affect recruitment practices also influence forms of engagement. The most common engagement practices are face-to-face workshops (materials and competencies), often hosted at local government facilities, such as libraries and community centres, to pass on information or improve the skills of individuals [25,29,75,76]. Interested individuals are brought together to learn about specific subjects, such as energy efficiency, solar power, rainwater harvesting, chicken rearing, composting, worm farming, recycling, reusing goods, healthy and frugal cooking as well as discussions about climate change [27]. Practitioners note that the popularity of workshops varies by topic:
“I think the solar panel ones, because the room was absolutely packed, it had a real energy of ‘wow, lots of people are doing this’ so it was kind of exciting”
(Interviewee M)
Recognising that face-to-face workshops are limited in their ability to reach larger audiences, local government seek to build the capacity of leaders within the community to not only act themselves, but to also educate and inspire others. Participants in such leadership programs may already have an interest in climate change and sustainability issues or the local government may identify them as leaders within existing social networks, such as culturally and linguistically diverse communities [48,77]. This “train the trainer” approach requires deeper engagement:
“Training touches on some key sustainability issues but it’s also leadership training and project planning training. Then the idea is that some people bring project ideas, and those project ideas are formed up into projects and other champions might join in with one of those project ideas or create a new group and deliver the project”
(Interviewee F)
Funding limitations and uncertainty also hamper the ability of local governments to develop longer-terms forms of engagement that would build relationships with households over time:
“We might have strategic plans going ten years into the future but that doesn’t mean that we can allocate money that far. So, if you want to do something, even if you know that it’s a longer-term thing, the way that you pitch it to us is as a pilot, as a one-off project which ideally will lead to other things, but it still leaves us open to saying yes or no in the future”
(Interviewee B)
This results in a need to deliver projects within a limited time period that favour short-term interventions. This, in turn, influences the third community engagement practice within the bundle: evaluation.

3.5. Evaluation Practices

Evaluation practices vary in their performance depending upon whether their focus is process measures, such as the number of individuals engaged in a program, or outcomes, such as tonnes of emissions saved [30]. For practitioners, focusing on process measures is influenced by a need to better understand what works in their recruitment and engagement practices:
“It’s questions around ‘Are the topics suitable? Is the time suitable? How can we get more people there? What do the people want out of it?’. So, it’s more evaluation of our own stuff rather than what outcomes have the people got from it”
(Interviewee R)
The most common materials used in this form of evaluation are post-event surveys, whether conducted immediately following a workshop or later, especially if practitioners want to record any changes in household practices following the engagement. Once again, constrained financial and time resources limit the ability of practitioners (competencies) to evaluate their interventions effectively:
“Our intention is to send out emails three months later or something like that or a survey and see if people are doing it but to be honest, at this stage I’ve only managed to get one out”
(Interviewee D)
This recognised difficulty in evaluating programs combined with an emphasis on emissions reductions, as stressed in local government strategies, can favour some forms of intervention over others. In particular, technological improvements to a household, such as the installation of rooftop solar, can be measured in a straightforward manner (has the technology been adopted or not?). Reasonable assumptions can be made about emissions reductions, based on the known performance of the technology although these need to be treated with a degree of caution [78]. What is less clear, and is recognised as such by practitioners, is how much credit a program can claim and how much is a decision that may have been taken by the household regardless:
“Someone might have come up to a street stall and we’ve had a five-minute chat about solar and they’ve gone off and done some Googling and ended up getting solar. So, we’re definitely part of that process but it’s really difficult to measure”
(Interviewee S)
From a practice perspective, the difficulty in evaluation relying upon outcomes based solely on emissions reductions is that it tells practitioners very little about how particular interventions engaged with and changed (or failed to change) everyday practices within the household. Lacking a deep understanding of why practices change due to climate change community engagement presents future challenges for local government practitioners seeking to deliver effective solutions: why is one form of engagement sticky with an audience and another not? What makes a particular technology capable of embedding itself within the lives of a target audience while another fails to do so? Are some forms of practice suitable for spreading rapidly amongst new audiences, and if so, why? None of these issues are addressed in the narrow approach to evaluation commonly used by local governments.
To conclude this analysis of local government climate change community engagement practices, three primary limitations have been identified, as set out in Table 1:
The first, which is common to all three community engagement practices, is limited resourcing. This is produced by a range of factors beyond the control of practitioners, including conservative management cultures within local government. This results in low impact forms of recruitment, such as local media, engagement practices based upon face-to-face interventions and evaluation that can favour easier-to-measure approaches, such as encouraging the adoption of emissions reduction technology. Additionally, such numbers-based outcome measurement misses the complexities of what is occurring within households.
The second is the focus on the individual as a rational actor capable of changing behaviour and contributing to a collective response within the community to climate change. This alignment with behaviour change theories results in engagement practices that stress the development of skills and provision of information to address perceived shortfalls in capacities or understandings of participants. In doing so, it fails to understand the complexity of the household practices it seeks to influence. As a result, the integration of community engagement with other climate governance practices is neglected.
Finally, the third is the use of climate change as a motivation for individuals to act. Spelled out in the strategies that frame community engagement and other climate governance practices is the assumption that the threat of climate change will encourage individuals to act. As has been noted, this not only faces known psychological barriers but also conflicts with meanings associated with the performance of everyday practices within the household.
Identifying these weaknesses offers opportunity. We regard them as pressure points within existing practices and relationships that can be used to reconfigure these practices to improve their effectiveness. The motivation to change how climate change community engagement practices are performed and interact is not about “doing community engagement better” but rather should seek to improve the opportunity for local governments to attain broader strategic objectives. In the next section, we draw upon an existing practice-based intervention methodology to test what is possible [19].

4. Re-Crafting, Substituting and Re-Integrating Local Government Practices

Having identified shortcomings in the existing performance of community engagement and climate governance practices, we now consider how these practices might be altered to improve their effectiveness. To achieve this, we turn to Spurling et al.’s [19] approach to consider how existing community engagement practices might be re-crafted, re-integrated or substituted to address these weaknesses. In exploring the possible avenues for shaping local government practices through this approach, we identify a need for practitioners and policymakers to establish clear objectives to be sought through climate governance, to understand the relationship between community engagement and other climate governance practices and to understand the dynamic relationship between community engagement and household practices.
We develop a framework that addresses each of the identified weaknesses in current forms of community engagement (lack of resources, using climate change as a motivation for action and a reliance on behaviour change theories that focus on the role of changing individual behaviours). As set out in Table 2, addressing each of these weaknesses with Spurling et al.’s [19] suggested approach reveals that as we consider each form of practice change (moving left to right in terms of least to more radical change) in relation to the level of ambition associated with climate governance.
Selecting interventions from this set of possible practice changes is guided by objectives set out in climate change strategies. Deciding which approach to take will reflect those objectives and the political will of the local government. We now examine each of the potential approaches in detail, drawing on the existing experience of local governments and considering how these might be used to improve community engagement.

4.1. Re-Crafting

Re-crafting existing community engagement practices (recruitment, engagement, evaluation) can range from minor tweaks to existing forms of community engagement, to a fundamental re-consideration of the role of households in responding to climate change. In the case of the former, recruitment can be re-crafted to include new communication channels, such as social media, that can reach a larger and more targeted audience in a manner that reflects the financial constraints of local government [79,80]. In the case of the latter, recruitment can take better advantage of existing networks within the community based upon practices rather than identifiable demographic groups. Analysis of how everyday practices are performed can identify networks of practice based on commonalities in performance between households [81]. These networks may then suggest new interventions based around practice household types. Recruitment could also be re-crafted through the use of alternative sectors of local government that have existing governance relationships with households. For example, practitioners at Hume City Council (in Melbourne’s outer northern suburbs) have developed interventions to improve the energy efficiency of low-income, elderly households using Home and Community Care services already delivered by council, drawing on existing trusted relationships between the council and the target audience [82].
Local governments wishing to maintain a framing based upon a collective response to climate change, in which the community is viewed as working together to reduce emissions or adapt to projected impacts, may consider other forms of engagement. Engagement practices based around climate adaptation responses, such as public tree planting and citizen science projects, meet this need by introducing new practices to be performed by households. Alternatively, climate change may be positioned as a secondary meaning associated with everyday practices; for example, community engagement to encourage the uptake of rooftop solar has, more recently, shifted its emphasis to stress the financial and health benefits of solar while climate change as a motivation sits in the background [83].
Should practitioners seek to dramatically expand the scale of their impact upon household emissions, engagement practices can be re-crafted through more ambitious interventions. For example, local governments could increase their support for community energy projects that accelerate the uptake of renewable energy in a collective manner [84]. Such an approach consolidates a collective approach but also draws attention to the construct of the energy provision system and its contribution to climate change [85].
Finally, evaluation practices may be re-crafted to reflect an understanding that different forms of evaluation are required to meet different needs. Instead of relying solely on quantitative approaches to measure outcomes (e.g., numbers of workshop participants or numbers of solar units installed as reported by interviewees), practitioners could employ more qualitative approaches, such as targeted surveys and interviews, to better understand what is going on within household practices as they interact with climate governance practices [86]. Instead of conducting their own quantitative evaluation, local governments could rely more on evaluation practices performed by other agencies to capture broader, municipal-wide shifts in energy use and emissions production [87].

4.2. Re-Integrating

Re-integrating requires consideration of the relationship between community engagement and other climate governance practices, with the household practices they seek to influence and with actors and forces driving broader changes in the socio-technical system. It offers local governments an opportunity to overcome a constraint of limited resources by combining community engagement with other forms of climate governance, potentially increasing the effectiveness of policies and programs with little or no additional expenditure.
For example, the City of Darebin’s Solar Savers program brought together community engagement and regulatory practices to increase the uptake of rooftop solar amongst a previously untapped audience, thereby addressing energy poverty issues amongst the elderly and renters and reducing greenhouse gas emissions [88]. Pre-intervention research informing this project identified a target audience that was likely to benefit financially from the adoption of rooftop solar but was excluded from the market: low-income pensioners owning their properties [89]. This audience reported to the council that they were unable to afford the upfront costs of solar and were less likely to use air conditioning during heat waves because they were concerned about the associated energy costs [90]. The council employed a provision in the Victorian Local Government Act [91] to provide solar units to participating households and recoup the funds through a special rates charge, at a rate which guaranteed savings from reduced energy bills [89].
This intervention demonstrates an ability to re-integrate the relationship between targeted community engagement practices and regulatory practices, by drawing on available legislative powers [84]. In addition, community engagement practice meanings associated with the promotion of rooftop solar were re-crafted, shifting away from a focus on needing to act on climate change, to health messaging associated with staying safe during heatwaves [89,90]. The first round of the council’s Solar Savers program installed solar on the roofs of 294 low-income pensioner households in 2014, and has been repeated and expanded in subsequent years, adding another 2000 households per year in 2017 and continuing to be a central plank of council’s climate change response [92,93].
The City of Moonee Valley (in Melbourne’s north east suburbs) re-integrated community engagement with infrastructure provision to encourage higher rates of walking and cycling for children travelling to school [94]. While Australian local governments perform a range of engagement, regulatory and infrastructure practices to encourage and support children to walk or cycle to school, including parking and speed restrictions for vehicles, footpaths and cycling lanes and interventions such as walking school buses [44,56,95,96], the integration of these with community engagement has been haphazard [97,98]. The City of Moonee Valley’s re-integration rewarded those schools active in supporting walking and cycling through community engagement by prioritising infrastructure installation where it was most needed. This approach not only incentivised school communities to act, but also provided council traffic engineers with stronger justification for the selection of projects [94].
While both examples highlight the power of re-integration, other forms of practices could have broader implications for local government. For example, local governments could consider re-integration between climate governance practices to directly address the identified weakness of conservative management cultures by tying performance of the managers and directors to successful climate governance practices, such as executive staff key performance indicators relevant to local government climate change responses [99].

4.3. Substituting

Local governments may also consider whether to replace community engagement practices altogether in favour of other climate governance practices that may drive a greater decrease in community-based emissions [100]. In terms of meeting the requirements of addressing climate change as a super wicked problem—developing solutions that are immediately popular, can embed themselves in people’s lives and have the capacity to spread rapidly—community engagement may be less effective than other practices. Regulatory practices, such as building requirements to encourage sustainable building design and land use planning to increase urban density and tree cover have the capacity to drive material improvements that are embedded for the long term [51,101,102,103]. Local governments may also consider delivering services that will achieve the same objective. For example, councils may take on new roles, such as energy retailers, that ensure the delivery of renewable energy to their communities [104] or they may focus more on supportive infrastructure, such as walking and cycling routes [105]. Alternatively, they may decide to devote their resources to advocating to higher tiers of government with greater capacity to act [106]. In practice, it is rare for local governments to abandon community engagement in favour of other climate governance practices. Engaging communities is still a key role for local governments as it provides social license for regulatory practices and advocacy [107].

5. Discussion

In this paper, we set out to correct the historical under-examination of governance practices within the practice theory literature [22]. By gaining a better appreciation of how governance practices work, we have advanced practice theory as a useful lens for policymakers and practitioners, replacing current methodologies based upon behaviour-change theories. We focused on climate change community engagement practices which we characterised as a bundle of three practices—recruitment, engagement and evaluation—as performed by Australian local governments. Drawing on a sample of 37 local government strategies and 29 interviews with local government practitioners from across Australia, we examined the relationship between each of these practices as well as between these and other climate governance practices (regulation, infrastructure provision, service delivery and advocacy). It should be noted that in the time since the interviews were conducted, there has been little change in the content and form of community engagement programs delivered by Australian local governments. We also reflected on local government strategic management and working cultures and how this can influence local government approaches to engaging with the everyday household practices they seek to influence. We identified three primary constraints influencing the performance of community engagement practices.
The first is that Australian local governments operate within constrained financial circumstances, resulting in low-cost forms of recruitment, engagement and evaluation. This includes recruitment practices that use local and free media, such as newspapers and council publications, engagement practices such as face-to-face workshops held in council premises and relatively simplistic evaluation of process measures (e.g., numbers of program participants) or outcome measures (e.g., numbers of solar installations in municipality). In each instance, there is little opportunity to explore or understand the nuance and complexity that informs how household practices are performed.
The second is an adherence to behaviour change methodologies in which individuals are encouraged to adopt more sustainable forms of household practices, through the provision of information and resources. This is allied with the third shortcoming of climate change community engagement: a reliance upon climate change as a motivation for individuals to change how they perform practices such as heating and cooling, washing, cooking and travelling to work or school. We note that this approach not only faces obstacles within the behavioural framing common to community engagement, but also conflicts with meanings associated with everyday household practices (e.g., notions of comfort associated with air conditioning versus reducing energy usage to cut emissions).
We then drew upon Spurling et al. [1] to examine how current local government climate engagement practices might be re-crafted, re-integrated or substituted to improve their efficacy. This includes examples of local government initiatives that have already sought to shift how community engagement practices are performed, including re-integration of community engagement with regulation and infrastructure. As part of this, we developed a framework for re-crafting, re-configuring and substituting local government community engagement practices with a view to addressing the three identified weaknesses in current forms.
While applying a practice lens to community engagement practices has proved valuable in showing how practices can be altered (and, in turn, can change household practices), developing a practice-based approach to local government climate governance requires further investigation at both the practice-specific and the systemic level. For practices, there is still more work to be done on understanding the dynamic relationship between climate governance practices and the household practices they seek to shape. For the emissions over which local governments have control or strong influence, climate governance practices are framed as tools to be used to influence household practices [45,51,93,108,109], but the relationship between governance and household practices runs both ways. For example, the rapid and widespread adoption of rooftop solar has disrupted meanings associated with community engagement, most notably through a shift away from using a collective social response to climate change as a motivation to personal financial gains [83]. The implications of this dynamic relationship need to be considered when crafting more effective forms of community engagement.
While some changes in household practices, such as the adoption of rooftop solar, can be anticipated, others are less predictable, though just as consequential for community engagement practices. For example, the shift to working from home during the COVID-19 pandemic for a significant proportion of the population, has driven significant changes in residential energy consumption patterns [110]. Such a rapid change in household energy consumption practices may create new opportunities for community engagement but only if policymakers and practitioners have a clear understanding of what is going on within the home, how everyday practices have shifted and what this means for energy use. This new understanding might inform effective governance practices to enable a reduction in energy use and greenhouse gas emissions.
In addition, practitioners need to understand how their governance practices might be influenced by new political movements and resulting cultural changes within councils. Just as existing community engagement practices have been shaped by the past participation of local governments in programs such as the International Council for Local Environmental Initiatives’ Cities for Climate Protection program, the recent emergence of the climate emergency movement is likely to change cultures and practices within the local government sector. In particular, the climate emergency movement’s emphasis on the need to advocate to other tiers of government rather than focus on encouraging households to change their practices envisages new forms of community engagement with a stronger emphasis on advocacy and working across sectors [111]. These wider social change movements are likely to influence meanings and competencies within local government climate governance practices, which increases pressure on councils to address the complexities associated with responding to climate change.
Finally, while Spurling et al.’s [19] approach proves valuable in thinking about how climate governance practices can be re-shaped or reconfigured, there is more work to be done to apply this practice-based framework so that it can provide clearer direction for policymakers and practitioners. Translating conceptual frameworks into practice change and ways of doing things is necessarily an active and engaged process. Action research with engaged local governments will be an important way to demonstrate the value and impact of a practice-based approach.
In this paper, we have commenced that process with a rethink of assumptions underpinning many climate change strategies in local government, such as an over-reliance on climate change as a motivating factor to change household practices. A climate change strategy based on a practice-based understanding of how both household and local government practices are constituted and performed (as well as the influence of other actors and movements) may look significantly different. If the impetus driving local government goals and objectives is the need to do all it can to reduce emissions, then there is a need to re-think what is possible to inform where their limited resources are best directed. Addressing the super wicked problem of climate change requires that local governments recognise the complexity not only in the practices that it is seeking to shape, such as household practices, but also in its own governance practices. Practice theory can offer a useful framework to address both.

Author Contributions

The three authors (D.M., S.M. and S.B.) co-designed the research, D.M. carried out the research and analysed the data and all co-wrote the paper. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

The study was conducted according to the guidelines of the Declaration of Helsinki, and approved by the Institutional Review Board (or Ethics Committee) of RMIT University (CHEAN B 0000019375-05/15, 9 June 2015).

Informed Consent Statement

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

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Levin, K.; Cashore, B.; Bernstein, S.; Auld, G. Overcoming the Tragedy of Super Wicked Problems: Constraining Our Future Selves to Ameliorate Global Climate Change. Policy Sci. 2012, 45, 123–152. [Google Scholar] [CrossRef]
  2. Betsill, M.; Bulkeley, H. Cities and the Multilevel Governance of Climate Change. Glob. Gov. 2006, 12, 141–159. [Google Scholar] [CrossRef] [Green Version]
  3. Chan, S.; Brandi, C.; Bauer, S. Aligning Transnational Climate Action with International Climate Governance: The Road from Paris. Rev. Eur. Comp. Int. Environmental. Law 2016, 25, 238–247. [Google Scholar] [CrossRef] [Green Version]
  4. Nicolini, D. Practice Theory, Work, and Organization: An Introduction; OUP Oxford: Oxford, UK, 2012. [Google Scholar]
  5. Watson, M. How Theories of Practice Can Inform Transition to a Decarbonised Transport System. J. Transp. Geography. 2012, 24, 488–496. [Google Scholar] [CrossRef] [Green Version]
  6. Giddens, A. The Constitution of Society: Outline of the Theory of Structuration; University of California Press: Berkeley, CA, USA, 1984. [Google Scholar]
  7. Shove, E.; Pantzar, M.; Watson, M. The Dynamics of Social Practice Everyday Life and How It Changes; SAGE Publications: London, UK, 2012. [Google Scholar]
  8. Schatzki, T.; Cetina, K.K.; von Savigny, E. The Practice Turn in Contemporary Theory; Routledge: London, UK, 2001. [Google Scholar]
  9. Reckwitz, A. Toward a Theory of Social Practices: A Development in Culturalist Theorizing. Eur. J. Soc. Theory 2002, 5, 243–263. [Google Scholar] [CrossRef]
  10. Schatzki, T.R. Practices and Actions A Wittgensteinian Critique of Bourdieu and Giddens. Philos. Soc. Sci. 1997, 27, 283–308. [Google Scholar] [CrossRef]
  11. Schatzki, T. Keeping Track of Large Phenomena. Geographische Zeitschrift. 2016. Available online: http://www.academia.edu/download/51415631/Tracking_Large_Phenomena_Published.pdf (accessed on 9 August 2020).
  12. Oberascher, C.; Stamminger, R.; Pakula, C. Energy Efficiency in Daily Food Preparation. Int. J. Consum. Studies. 2011, 35, 201–211. [Google Scholar] [CrossRef]
  13. Shove, E. Beyond the ABC: Climate Change Policy and Theories of Social Change. Environ. Plan. A 2010, 42, 1273–1285. [Google Scholar] [CrossRef] [Green Version]
  14. Hargreaves, T. “Practice-Ing Behaviour Change: Applying Social Practice Theory to pro-Environmental Behaviour Change.” Edited by Bente Halkier, Tally Katz-Gerro, and Lydia Martens. J. Consum. Culture. 2011, 11, 79–99. [Google Scholar] [CrossRef]
  15. O’Gorman, M.; Jotzo, F. Impact of the Carbon Price on Australia’s Electricity Demand, Supply and Emissions; CCEP Working Paper No. 1411; Crawford School of Public Policy: Canberra, Australia, 2014. [Google Scholar]
  16. Watson, M.; Browne, A.; Evans, D.; Foden, M.; Hoolohan, C.; Sharp, L. Challenges and Opportunities for Re-Framing Resource Use Policy with Practice Theories: The Change Points Approach. Glob. Environ. Chang. Hum. Policy Dimens. 2020, 62, 102072. [Google Scholar] [CrossRef]
  17. John, P.; Smith, G.; Stoker, G. Nudge Nudge, Think Think: Two Strategies for Changing Civic Behaviour. Political Q. 2009, 80, 361–370. [Google Scholar] [CrossRef]
  18. Halpern, D. Inside the Nudge Unit: How Small Changes Can Make a Big Difference; Random House: New York, NY, USA, 2015. [Google Scholar]
  19. Spurling, N.; McMeekin, A.; Shove, E.; Southerton, D.; Welch, D. Interventions in Practice: Re-Framing Policy Approaches to Consumer Behaviour; Sustainable Practices Research Group: Lancaster, UK, 2013. [Google Scholar]
  20. Hoolohan, C.; Browne, A.; Evans, D.; Foden, M.; Sharp, L.; Watson, M. Change Points: A Toolkit for Designing Interventions That Unlock Unsustainable Practices; University of Manchester: Manchester, UK, 2018. [Google Scholar]
  21. Strengers, Y.; Maller, C. Social Practices, Intervention and Sustainability; Routledge: Abingdon, UK, 2014. [Google Scholar]
  22. Macrorie, R.; Foulds, C.; Hargreaves, T. Governing and Governed by Practice. In Social Practices, Intervention and Sustainability; Strengers, Y., Maller, C., Eds.; Routledge: Abingdon, UK, 2015. [Google Scholar]
  23. Keller, M.; Halkier, B.; Wilska, T.-A. Policy and Governance for Sustainable Consumption at the Crossroads of Theories and Concepts. Environ. Policy Gov. 2016, 26, 75–88. [Google Scholar] [CrossRef]
  24. Pillora, S. Australian Local Government and Climate Change; Australian Centre for Excellence for Local Government: Sydney, Australia, 2011.
  25. Coenen, F.; Menkveld, M. The Role of Local Authorities in a Transition towards a Climate-Neutral Society. In Global Warming and Social Innovation; Routledge: London, UK, 2013; pp. 120–138. [Google Scholar]
  26. Van Staden, M.; Musco, F. Local Governments and Climate Change; Springer: Dordrecht, The Netherlands, 2010. [Google Scholar]
  27. Fritze, J.; Williamson, L.; Wiseman, J. Community Engagement and Climate Change: Benefits, Challenges and Strategies; Department of Planning and Community Development: Melbourne, Australia, 2009.
  28. Moloney, S.; Horne, R.E.; Fien, J. Transitioning to Low Carbon Communities—From Behaviour Change to Systemic Change: Lessons from Australia. Energy Policy 2010, 38, 7614–7623. [Google Scholar] [CrossRef] [Green Version]
  29. Tilbury, D.; Coleman, V.; Jones, A.; MacMaster, K. A National Review of Environmental Education and Its Contribution to Sustainability in Australia: Community Education; Australian Government: Canberra, Australia, 2005.
  30. UrbanTrans. Stocktake and Analysis of Household Behaviour Change Programs in Victoria; Department of Sustainability and Environment: Melbourne, Australia, 2008.
  31. Southerton, D.; McMeekin, A.; Evans, D. International Review of Behaviour Change Initiatives: Climate Change Behaviours Research Programme; Scottish Government: Edinburgh, UK, 2011.
  32. Science and Technology Select Committee. Behaviour Change; House of Lords: London, UK, 2011. [Google Scholar]
  33. Ly, K.; Soman, D. Nudging around the World. Rotman School of Management, University of Toronto. 2013. Available online: https://rotman.utoronto.ca/-/media/Files/Programs-and-Areas/behavioural-economics/Nudging%20Around%20The%20World_Sep2013.pdf (accessed on 12 July 2018).
  34. Moloney, S.; Strengers, Y. “Going Green”?: The Limitations of Behaviour Change Programmes as a Policy Response to Escalating Resource Consumption. Environ. Policy Gov. 2014. [Google Scholar] [CrossRef] [Green Version]
  35. Moloney, S.; Horne, R. Low Carbon Urban Transitioning: From Local Experimentation to Urban Transformation? Sustainability 2015, 7, 2437–2453. [Google Scholar] [CrossRef] [Green Version]
  36. Strengers, Y. Conceptualising Everyday Practices: Composition, Reproduction and Change. Carbon Neutral Communities Centre for Design, RMIT University, Melbourne, Australia. Working Papers, no. 6. 2010. Available online: https://www.academia.edu/download/29830597/6p1hikrdei2rz.pdf (accessed on 11 May 2018).
  37. Moloney, S.; Horne, R. Reconfiguring Spatial Boundaries and Institutional Practices: Mobilizing and Sustaining Urban Low Carbon Transitions in Victoria, Australia. 2018. Available online: https://researchbank.rmit.edu.au/view/rmit:51135 (accessed on 15 January 2019).
  38. Fallon, D.; Sullivan, C. Are We There Yet? NSW Local Governments’ Progress on Climate Change. Autralian Geogr. 2014, 2, 221–238. [Google Scholar] [CrossRef]
  39. McGuirk, P.; Dowling, R.; Brennan, C.; Bulkeley, H. Urban Carbon Governance Experiments: The Role of Australian Local Governments. Geogr. Res. 2015, 53, 39–52. [Google Scholar] [CrossRef] [Green Version]
  40. Storey, H. Local Action for a Low Carbon Future; Australian Centre of Excellence for Local Government: Sydney, Australia, 2012.
  41. Maddocks. Planning Policy and Practice: The Right Mechanism to Tackle Climate Change? Maddocks: Melbourne, Australia, 2010. [Google Scholar]
  42. Inglis, J.; Whittaker, S.; Dimitiadis, A.; Pillora, S. Climate Adaptation Manual for Local Government—Embedding Resilience to Climate Change; Australian Centre of Excellence for Local Government: Sydney, Australia, 2014.
  43. Xu, X.; Rudolph, V.; Greenfield, P.F. Australian Urban Landfills: Management and Economics. Waste Manag. Res. 1999, 17, 171–180. [Google Scholar] [CrossRef]
  44. City of Boroondara. Our Low Carbon Future; City of Boroondara: Camberwell, Australia, 2009. [Google Scholar]
  45. Gold Coast City Council. Climate Change Strategy 2009-2014; Gold Coast City Council: Nerang, Australia, 2009. [Google Scholar]
  46. Hobsons Bay City Council. Hobsons Bay City Council Environmental Strategies; Hobsons Bay City Council: Altona, Australia, 2015. [Google Scholar]
  47. City of Moreland. Zero Carbon Evolution; City of Moreland: Coburg, Australia, 2014. [Google Scholar]
  48. City of Darebin. Darebin Community Climate Change Action Plan; City of Darebin: Melbourne, Australia, 2009. [Google Scholar]
  49. City of Fremantle. One Planet Fremantle Strategy; City of Fremantle: Fremantle, Australia, 2014. [Google Scholar]
  50. City of Newcastle. Newcastle 2020 Carbon and Water Management Action Plan; City of Newcastle: Newcastle, Australia, 2011. [Google Scholar]
  51. City of Sydney. Sustainable Sydney 2030 Community Strategic Plan; City of Sydney: Sydney, Australia, 2013. [Google Scholar]
  52. City of Yarra. Yarra Environment Strategy 2013–2017; City of Yarra: Melbourne, Australia, 2013. [Google Scholar]
  53. Lindseth, G. The Cities for Climate Protection Campaign (CCPC) and the Framing of Local Climate Policy. Local Environ. 2004, 9, 325–336. [Google Scholar] [CrossRef]
  54. ICLEI. Local Government Action on Climate Change 2007; Department of Environment, Water, Heritage and the Arts: Canberra, Australia, 2007.
  55. ICLEI. Local Government Action on Climate Change 2008; Department of Environment, Water, Heritage and the Arts: Canberra, Australia, 2008.
  56. Brisbane City Council. Brisbane’s Plan for Action on Climate Change and Energy 2007; Brisbane City Council: Brisbane, Australia, 2007. [Google Scholar]
  57. City of Moonee Valley. City of Moonee Valley Greenhouse Strategy 2010; City of Moonee Valley: Moonee Ponds, Australia, 2010. [Google Scholar]
  58. City of Melbourne. Climate Change Adaptation Strategy; City of Melbourne: Melbourne, Australia, 2009. [Google Scholar]
  59. Hume City Council. Climate Change Adaptation Plan; Hume City Council: Broadmeadows, Australia, 2013. [Google Scholar]
  60. Zeppel, H. Climate Change Governance by Local Councils: Carbon Mitigation by Greater Adelaide Councils. In Local Government Researchers Forum: Local Governance in Transition; ACELG: Sydney, Australia, 2011. [Google Scholar]
  61. Binder, G.; Boldero, J. Planning for Change: The Roles of Habitual Practice and Habitus in Planning Practice. Urban Policy Res. 2012, 30, 175–188. [Google Scholar] [CrossRef]
  62. Rickards, L.; Wiseman, J.; Kashima, Y. Barriers to Effective Climate Change Mitigation: The Case of Senior Government and Business Decision Makers. Wiley Interdiscip. Rev. Clim. Chang. 2014, 5, 753–773. [Google Scholar] [CrossRef]
  63. Considine, M.; Lewis, J. Innovation and Innovators Inside Government: From Institutions to Networks. Governance 2007, 20, 581–607. [Google Scholar] [CrossRef]
  64. Shove, E.; Spurling, N. Sustainable Practices: Social Theory and Climate Change; Routledge: Abingdon, UK, 2013. [Google Scholar]
  65. Jenner, D.; Roberts, E. Moreland City Council: Household Survey 2013; Market Solutions: Coburg, Australia, 2014. [Google Scholar]
  66. Metropolis Research. Yarra City Council 2015 Annual Customer Satisfaction Survey; City of Yarra: Richmond, Australia, 2015. [Google Scholar]
  67. Hoff, J. Local Climate Protection Programmes in Australia and New Zealand; CIDEA: Copenhagen, Denmark, 2010. [Google Scholar]
  68. Sunshine Coast Council. Sunshine Coast Climate Change and Peak Oil Strategy 2010–2020; Sunshine Coast Council: Caloundra, Australia, 2010. [Google Scholar]
  69. City of Canada Bay. Canada Bay Futures Plan 2012; City of Canada Bay: Canada Bay, Australia, 2012. [Google Scholar]
  70. Lorenzoni, I.; Nicholson-Cole, S.; Whitmarsh, L. Barriers Perceived to Engaging with Climate Change among the UK Public and Their Policy Implications. Glob. Environ. Chang. Hum. Policy Dimens. 2007, 17, 445–459. [Google Scholar] [CrossRef]
  71. Gifford, R. The Dragons of Inaction: Psychological Barriers That Limit Climate Change Mitigation and Adaptation. Am. Psychologist. 2011, 66, 290–302. [Google Scholar] [CrossRef] [PubMed]
  72. Pike, C.; Eaves, S.; Herr, M.; Huva, A. The Preparation Frame; Climate Access: Eugene, OR, USA, 2015. [Google Scholar]
  73. Oliver, A. The Lowy Institute Poll 2017; The Lowy Institute: Sydney, Australia, 2017. [Google Scholar]
  74. Axsen, J.; Kurani, K. Social Influence, Consumer Behavior, and Low-Carbon Energy Transitions. Annu. Rev. Environ. Resour. 2012, 37, 311–340. [Google Scholar] [CrossRef] [Green Version]
  75. Department of Transport. LivingSmart Households (Sustainability Program)—Monitoring and Evaluation (January 2012); Government of Western Australia: Perth, Australia, 2012.
  76. Ingle, A.; Moezzi, M.; Lutzenhiser, L.; Diamond, R. Better Home Energy Audit Modelling: Incorporating Inhabitant Behaviours. Build.Ing Res. Inf. 2014, 42, 1–13. [Google Scholar] [CrossRef]
  77. Sustainability Fund. Talking My Language Final Project Report; Victorian Local Sustainability Accord: Melbourne, Australia, 2012. [Google Scholar]
  78. Aydin, E.; Kok, N.; Brounen, D. Energy Efficiency and Household Behavior: The Rebound Effect in the Residential Sector. Rand J. Econ. 2017, 48, 749–782. [Google Scholar] [CrossRef]
  79. Ross, C.; Warwick, C.; Terras, M.; Nyhan, J. Social Media for Digital Humanities and Community Engagement. Digit. Humanit. Pract. 2012, 1, 23–46. [Google Scholar]
  80. Heldman, A.B.; Schindelar, J.; Weaver, J.B. Social Media Engagement and Public Health Communication: Implications for Public Health Organizations Being Truly ‘Social’. Public Health Rev. 2013, 35, 13. [Google Scholar] [CrossRef] [Green Version]
  81. Higginson, S.; McKenna, E.; Hargreaves, T.; Chilvers, J.; Thomson, M. Diagramming Social Practice Theory: An Interdisciplinary Experiment Exploring Practices as Networks. Indoor Built Environ. 2015, 24, 950–969. [Google Scholar] [CrossRef] [Green Version]
  82. Northern Alliance for Greenhouse Action. Hume Energy Savers; NAGA: Broadmeadows, Australia, 2016. [Google Scholar]
  83. Meiklejohn, D.; Bekessy, S.; Moloney, S. Shifting Practices: How the Rise of Rooftop Solar PV Has Changed Local Government Community Engagement. Cogent Environ. Sci. 2018, 4, 1481584. [Google Scholar] [CrossRef]
  84. Mey, F.; Diesendorf, M.; MacGill, I. Can Local Government Play a Greater Role for Community Renewable Energy? A Case Study from Australia. Energy Res. Soc. Sci. 2016, 21, 33–43. [Google Scholar] [CrossRef]
  85. Pears, A.K. Imagining Australia’s Energy Services Futures. Futures 2007, 39, 253–271. [Google Scholar] [CrossRef]
  86. Pullinger, M.; Browne, A.; Anderson, B.; Medd, W. Patterns of Water; Lancaster University: Lancaster, UK, 2013. [Google Scholar]
  87. Ironbark Sustainability. CO2 Emissions Snapshots for Municipalities in Australia. Snapshot. 2020. Available online: https://snapshotclimate.com.au (accessed on 27 September 2020).
  88. EAGA. Solar Savers; Eastern Alliance for Greenhouse Action: Melbourne, Australia, 2017. [Google Scholar]
  89. City of Darebin. Solar Saver Program 2017–2019; City of Darebin: Preston, Australia, 2017. [Google Scholar]
  90. Robertson, A. Understanding the Impacts of Residential Solar on Everyday Practices: A Case Study of Darebin Solar Savers. Master’s Thesis, University of Melbourne, Melbourne, Australia, 2016. [Google Scholar]
  91. State of Victoria. Local Government Act 1989; State of Victoria: Melbourne, Australia, 1989. [Google Scholar]
  92. Irwin, J. Darebin Council Approves Special Rate for Australian First Solar Saver Scheme for Pensioners. Herald Sun, 12 September 2014. [Google Scholar]
  93. City of Darebin. Darebin Climate Emergency Plan 2017–2022; City of Darebin: Preston, Australia, 2017. [Google Scholar]
  94. Bagnati, L.; Meiklejohn, D. School Travel Planning an Engineer Will Love: Using Audits and Surveys to Identify Capital Works Priorities. In Proceedings of the Australasian Transport Research Forum, Brisbane, Australia, 2–4 October 2013. [Google Scholar]
  95. City of Manningham. Climate 2020; City of Manningham: Doncaster, Australia, 2009. [Google Scholar]
  96. City of Port Phillip. Greenhouse Plan; City of Port Phillip: St. Kilda, Australia, 2011. [Google Scholar]
  97. Morris, J.; Wang, F.; Lilja, L. School Children’s Travel Patterns: A Look Back and a Way Forward. Transp. Eng. In Aust. 2001, 7, 15. [Google Scholar]
  98. Peddie, B.; Somerville, C. School Travel Planning: Travel Behaviour Change and Community Engagement—Results from Victoria. Road Transp. Res. J. 2006, 15, 82–93. [Google Scholar]
  99. Inner West Council. CEO KPIs. 2019. Available online: https://www.innerwest.nsw.gov.au/about/the-council/ceo-and-senior-staff/ceos-diary-and-expenses-disclosure (accessed on 18 August 2020).
  100. Beyond Zero Emissions; ICLEI; Ironbark Sustainability. Australian Local Government Climate Review; Beyond Zero Emissions; ICLEI; Ironbark Sustainability: Melbourne, Australia, 2018. [Google Scholar]
  101. Allender, S.; Gleeson, E.; Crammond, B.; Sacks, G.; Lawrence, M.; Peeters, A.; Loff, B.; Swinburn, B. Moving beyond ‘Rates, Roads and Rubbish’: How Do Local Governments Make Choices about Healthy Public Policy to Prevent Obesity? Aust. New Zealand Health Policy 2009, 6, 20. [Google Scholar] [CrossRef] [Green Version]
  102. City of Yarra. Yarra Climate Emergency Plan 2020–2024; City of Yarra: Melbourne, Australia, 2020. [Google Scholar]
  103. City of Melbourne. Overshadowing Impacts on Solar Panels: Planning Guidance Note; City of Melbourne: Melbourne, Australia, 2017. [Google Scholar]
  104. Dunn, K. Electricity Retailing in Victoria: Is There a Role for Local Government? Northern Alliance for Greenhouse Action: Brunswick, Australia, 2018. [Google Scholar]
  105. Pucher, J.; Garrard, J.; Greaves, S. Cycling down under: A Comparative Analysis of Bicycling Trends and Policies in Sydney and Melbourne. J. Transp. Geogr. 2011, 19, 332–345. [Google Scholar] [CrossRef]
  106. Council Action in the Climate Emergency. A Guide For Councils. CACE. 2018. Available online: http://www.caceonline.org/a-guide-for-councils.html (accessed on 5 May 2020).
  107. Wiseman, J.; Williamson, L.; Fritze, J. Community Engagement and Climate Change: Learning from Recent Australian Experience. Int. J. Clim. Chang. Strateg. Manag. 2010, 2, 134–147. [Google Scholar] [CrossRef]
  108. Adelaide City Council. Carbon Neutral Strategy; Adelaide City Council: Adelaide, Australia, 2015. [Google Scholar]
  109. City of Melbourne. Climate Change Mitigation Strategy to 2050; City of Melbourne: Melbourne, Australia, 2019. [Google Scholar]
  110. EA. Covid-19 Impact on Electricity; International Energy Agency: Paris, France, 2020. [Google Scholar]
  111. Sutton, P. Local-First Implementation; RSTI: Melbourne, Australia, 2017. [Google Scholar]
Table 1. Limitations of existing forms of local government climate change community engagement.
Table 1. Limitations of existing forms of local government climate change community engagement.
Weaknesses/PracticeRecruitmentEngagementEvaluation
Limited resourcesSmall-scale, local recruitment.Face-to-face interventions.Favours easy to measure outcomes.
Climate change as motivation for actionLimited to those already engaged.Psychological barriers.Misses other motivations.
Focus on individualsRestricted to behaviour change approaches.Restricted to behaviour change approaches.Misses systemic changes.
Table 2. Re-crafting, re-integrating and substituting to address weaknesses in current community engagement practices.
Table 2. Re-crafting, re-integrating and substituting to address weaknesses in current community engagement practices.
Weaknesses/ResponsesRe-CraftingRe-IntegratingSubstituting
Limited ResourcesNew forms of recruitment, engagement and evaluation.Deliver community engagement along with other climate governance practices.Replace community engagement with other forms of climate governance.
Climate change as motivation for actionCommunity engagement on climate specific actions.Integrate with other meanings associated with household practices.Replace with more effective meanings.
Focus on individualsFocus on household practice.Integrate with other household practices.Address systemic issues that enable or disable household practices.
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Meiklejohn, D.; Moloney, S.; Bekessy, S. Applying a Practice Lens to Local Government Climate Change Governance: Rethinking Community Engagement Practices. Sustainability 2021, 13, 995. https://doi.org/10.3390/su13020995

AMA Style

Meiklejohn D, Moloney S, Bekessy S. Applying a Practice Lens to Local Government Climate Change Governance: Rethinking Community Engagement Practices. Sustainability. 2021; 13(2):995. https://doi.org/10.3390/su13020995

Chicago/Turabian Style

Meiklejohn, David, Susie Moloney, and Sarah Bekessy. 2021. "Applying a Practice Lens to Local Government Climate Change Governance: Rethinking Community Engagement Practices" Sustainability 13, no. 2: 995. https://doi.org/10.3390/su13020995

APA Style

Meiklejohn, D., Moloney, S., & Bekessy, S. (2021). Applying a Practice Lens to Local Government Climate Change Governance: Rethinking Community Engagement Practices. Sustainability, 13(2), 995. https://doi.org/10.3390/su13020995

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