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Annual Lectures

Climate change politics and the urban contexts of messy governmentalities

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Pages 241-258 | Received 14 Sep 2018, Published online: 12 Jul 2019

ABSTRACT

The purpose of this paper is two-fold. The first part diagnoses three limitations of current thought on the urban governance of climate change. First, current action emerges within a wave of urban optimism with limited historical sensitivity to previous climate change action. Second, the mobile nature of climate change policies is overlooked in studies that emphasize cities as the unit of analysis for climate action. Third, the focus on global cities or alternative locations that are constructed as exemplary sites takes attention away from the ordinary contexts of action where climate action is most needed. The second part of the paper uses this analysis as the main motivation for a call for studies of climate change governance to engage with the messiness of urban knowledge and action. Three theories of messiness are put forward. The first relates the idea of governance as messiness to postcolonial analyses of radical environmental action. The second emphasizes the messiness embedded in current methods of knowing the city, and the logic of situated knowledge. The third emphasizes messiness in the relations between the body, society and the emotions characterizing the interactions of everyday life.

This article is part of the following collections:
Celebrating ten years of Territory, Politics, Governance

INTRODUCTION

Addressing climate change in cities is more urgent than ever. An international policy consensus exists regarding the need in cities and urban regions to enable action for climate change. Some have referred to this as part of a ‘rapid consolidation of urban optimism’ in sustainable development agendas (Barnett & Parnell, Citation2016, p. 88). Achieving the emission reductions needed to avoid dangerous climate change will require aligning subnational and national-level action for a coordinated global response (Chan et al., Citation2015, p. 134). Global environmental politics have increasingly focused on city-based initiatives that support the development and harmonization of a global, multilevel partnership to tackle climate change. The sustainable city is now more than ever intrinsically linked to the low-carbon city.

Climate change action should address the actual material requirements of low-carbon transitions in cities. The infrastructures that will emit the majority of emissions in the next century have not yet been built (Davis & Socolow, Citation2014). Meeting current growth rates will require an annual investment of approximately US$3.3 trillion until 2030 (4% of the global gross domestic product (GDP) in nominal terms, each year) (Woetzel, Garemo, Michke, Hjerpe, & Palter, Citation2016). The key question is as follows: Where will such infrastructure needs emerge? United Nations (UN) data suggest that over 60% of the population growth in urban areas between 2010 and 2030 will occur in cities that had fewer than 1 million inhabitants in 2010 (UN, Citation2014). The urban transformation depends on routine decisions on infrastructure made in thousands of smaller cities, particularly in rapidly urbanizing areas in South Asia, Southeast Asia and Africa. Crucially, these are the cities we know less about.

These cities have been ignored in debates on urban governance and climate action. Academic interest in documenting forerunner actions and leading networks with global impacts has tended to prioritize visible actions in global and strongly branded cities. Also, low-carbon urban development has not been seen as a priority for less developed areas, notwithstanding the infrastructure imperatives explained above and the wider sustainability benefits associated with low-carbon urban development. However, delivering a low-carbon urban future requires engaging with the contexts of ‘ordinary cities, following’. Robinson's (Citation2013) argument against urban theory’s focus on the experiences of global, wealthy cities that are perceived to be leading innovators, in contrast to an indistinct mass of ordinary, less developed cities. The construction of a discourse of global cities has dominated climate politics, even though many cities find themselves struggling between modernity and development, regardless of their location. An emphasis on famous examples and transformative potential has directed attention to cases which are deemed to have global relevance (Castán Broto & Bulkeley, Citation2013; Hodson & Marvin, Citation2010). Even when there is a deliberate intention to highlight action in unusual places, an understanding of the findings is hindered by a focus on city-based case studies (e.g., Hughes, Chu, & Mason, Citation2018).

How can we theorize low-carbon action in ‘ordinary cities’? Decentralizing the knowledge hegemonies that characterize contemporary thought in climate change governance requires alternative theorizations of urban governance. This paper first characterizes the current moment of urban optimism about the possibilities of delivering the sustainable, low-carbon city in the climate change governance literature. This is done by identifying three limitations in this literature: the limited historical sensitivity of climate change action; the emphasis on cities as the unit of analysis; and the focus on global cities or alternative locations that are constructed as exemplary. The paper then discusses these limitations and explores possible responses. Ideas of messy governance emerge as an alternative to the current assumptions shaping the climate change debate.

LIMITATIONS OF CURRENT CLIMATE CHANGE GOVERNANCE RESEARCH

The first decades of climate change and cities research evolved through a detailed analysis of the history and conditions of climate change action in urban areas (Betsill & Bulkeley, Citation2007). However, global assessments of climate change action at the local level are currently fragmented because they emphasize the comparison of a small number of case studies of examples of best practices in specific cities (e.g., Bartlett & Satterthwaite, Citation2016; Carmin, Anguelovski, & Roberts, Citation2012; Hsu, Weinfurter, & Xu, Citation2017). The combination of large-n data methodologies and case studies to study global trends in climate change action in cities has helped to navigate a multilevel context (Castán Broto, Citation2017b; Castán Broto & Bulkeley, Citation2013; Castán Broto & Westman, Citation2017). However, there are three limitations that impede a global understanding of urban climate action. The first limitation of this body of literature is the interpretation of the current wave of urban optimism as a moment of ‘discovery’ of cities as new sites for climate change action (Hughes et al., Citation2018). This assumption downplays the historical development of the relationship between local action and global environmental policy. Consequently, research in this area tends to overlook crucial historical lessons, especially, the lessons of the local action experiences of sustainability that followed the 1992 Rio Declaration on Environment and Development. For example, the insight that climate change action will be more effective if it reflects environmental and social co-benefits (Bain et al., Citation2016; Harlan & Ruddell, Citation2011) has a long pedigree in environmental thought. Moreover, previous experiences of sustainability action should foster learning regarding key institutional aspects of climate change action, including aspects of sectoral integration, participatory planning, or multi-institutional coordination, to mention a few examples.

The second limitation is the emphasis on cities as the unit of analysis for climate change action. The definition of cities in relation to local government jurisdictions and administrative boundaries reduces the terms of the debate because it circumscribes policies to single contexts of action. This generates two forms of analysis: one being focused on the strategic level and the types of plans and commitments made by key institutional actors (Kern & Alber, Citation2009; Reckien et al., Citation2014; Seto et al., Citation2014), and the other focused on individual initiatives and experiments, both time and place bound, whose aggregate results are uncertain (Bulkeley & Castán Broto, Citation2013; Hoffmann, Citation2011). These analyses overlook the fact that climate change policies are rarely generated in one single site. Social, technological and institutional innovations travel across locations and mutate to adapt to the conditions of implementation in different urban contexts. Such ‘urban policy mobilities’ (McCann, Citation2011) are observable in the course of climate change policy across locations. One strategy is to move the unit of analysis away from the city to policy to reveal the key factors that enable policy development and implementation.

The third limitation is a focus on global cities and exemplary action. A few large-n studies of low-carbon action in cities have built upon the comparative analysis of commitments and self-reported action (e.g., Castán Broto & Bulkeley, Citation2013). Policy platforms such as Non-State Actor Zone for Climate Action (NAZCA) (the Global Climate Action portal of the United Nations Framework Convention on Climate Change – UNFCCC) have adopted a similar approach to track commitments (e.g., Ven, Bernstein, & Hoffmann, Citation2017). Another strategy is to compare plans for climate action in a circumscribed area (Reckien et al., Citation2014). However, we lack an assessment of the extent to which those commitments translate into actual transformations. Assessment of impacts has mostly taken place in single case studies or in the comparison of a few case studies from which it is difficult to extract lessons about the global trends of climate action (as shown in Frantzeskaki, Castán Broto, Coenen, & Loorbach, Citation2017; and Hughes et al., Citation2018).

The implications of each of these limitations are explored in the following sections, attending particularly to responses already emerging within the current scholarly literature on low-carbon governance.

The post-2015 wave of urban optimism and the discovery of cities as sites of action

The 2015 Paris Agreement for Climate Action (henceforth PA) represented a radical change in global environmental policy. What began with a concern for the role of urban areas in producing carbon emissions in the 2000s soon turned into a wave of optimism about how climate change action in urban areas could reduce carbon emissions and facilitate climate change adaptation (Bulkeley, Castán Broto, Hodson, & Marvin, Citation2010; Frantzeskaki et al., Citation2017). Solecki and Leichenko (Citation2006) already predicted that climate change action in urban areas could transform global environmental politics. At the Conference of Parties (COP) in Copenhagen in 2009, the failure within the international climate regime to negotiate the replacement of the Kyoto Protocol marked a shift away from regulatory approaches to climate governance and towards voluntary commitments for climate action. The possibility to address climate change at subnational levels (outside the COP framework) became increasingly relevant in the context of the failure of the international climate regime (Hoffmann, Citation2011; Jones, Citation2012). International attention ensued as multilateral organizations coordinated a series of high-profile reports that underscored the urgency of climate change action in urban areas (IPCC, Citation2014; UN-Habitat, Citation2011; World Bank, Citation2011). Since the debacle at the 2009 COP in Copenhagen, subnational actors have responded to gridlocks and delays in international negotiations with voluntary interventions and innovation (Hale, Citation2016).

As voluntary approaches to climate change policy have gained ground over regulatory ones, models of governance have also diversified (Newell, Pattberg, & Schroeder, Citation2012). Such diversification of governance entails the coordination of multiple forms of state and non-state action (Rosenau, Citation2000) and thus, a recognition that a climate resilient society depends on the interventions of multiple actors (Newell et al., Citation2012; Okereke, Bulkeley, & Schroeder, Citation2009). Local governments are particularly important because they can shape urban trajectories towards low-carbon resilient futures, delivering climate change strategies whether this is on their own, or through partnerships with the business sector, civil society organizations, or community groups.

Following this, the PA recognized the need to engage with subnational level institutions to deliver climate action. The PA provides the enabling conditions to foster a simultaneous national and subnational transformation. It provides tools to record and promote subnational action as a means to bridge the gap between the aggregate national intended contributions agreed in Paris and the actual requirements of emissions reductions needed to maintain the increase in global temperature to under 1.5°C. Initiatives such as NAZCA have emerged to capture the actors’ expanding role beyond that played in the traditional international climate regime. In this context, the UNFCCC has adopted a role as an orchestrator of a range of state and non-state actors, to steer action in the right direction (Bäckstrand & Kuyper, Citation2017).

Simultaneously, the view of cities as strategic arenas for climate change action is spreading into other domains of international policy. The 2015 Sustainable Development Goals reflect a pro-urban policy consensus in international sustainable development policies (Barnett & Parnell, Citation2016). The UN adopted a New Urban Agenda (NUA) at the III United Nations Conference on Housing and Sustainable Urban Development (Habitat III Secretariat, Citation2016) in Quito, Ecuador, in October 2016. The NUA, a generic document full of good intentions but limited in practical recommendations for practitioners, makes a case for harnessing the potential of urban areas to deliver sustainable futures (Parnell, Citation2016). The NUA foregrounds the value of urbanization as a means to deliver solutions for sustainability and resilience (Bureau of the Preparatory Committee, Citation2016) However, the technological focus on smart solutions reveals a tension between the need to integrate proposals for sustainable development within specific contexts and the quest for innovations and technologies to revolutionize the urban agenda. There is a risk in the ‘rapid consolidation of urban optimism’ (Barnett & Parnell, Citation2016, p. 88) that views the city as a site of opportunity and action but advances technologies whose potential impacts are not fully examined. Barnett and Parnell (Citation2016) recommend approaches that engage with both global policy networks and specific locations, focusing on the needs of the urban areas and regions where sustainability action occurs.

These international agendas are characterized by a lack of engagement with the history of environmental thought and project implementation in cities. Debra Roberts, a leading voice in the climate change and cities debates (and now co-chair of Working Group 2 of the current round of the Intergovernmental Panel on Climate Change (IPCC) assessment) has stated publicly that one limitation of agreements, such as the NUA, is that they provide little guidance to urban managers who are actually operating on the ground. Since the publication of the Brundtland Report in 1987, we have lived through three decades of a global environmental consensus on the need for sustainable cities (Hodson & Marvin, Citation2017). However, there is a sense of rediscovery within the climate change governance literature (Hughes et al., Citation2018). This problem has historical roots. In the decades that followed the formation of the international climate regime with the adoption of the UNFCCC in 1992, climate change was framed as a global problem requiring global solutions (Bulkeley, Citation2013; Bulkeley & Newell, Citation2015). Climate change was largely delinked from the emphasis on local action that followed the sustainability agendas from the 1992 Rio Declaration on Sustainable Development to Local Agenda 21, despite international efforts to coordinate what was often perceived as two separate realms of action (e.g., Gebre-Egziabher, Citation2004). Now, with the newfound interest in urban areas as engines of climate change action, it is time to revisit those historical roots and examine how past experiences might shape future possibilities of action.

Mobile nature of climate change policy

The literature on urban climate change governance has focused on cities as the unit of analysis, establishing an equivalence between the city and its government or between the city and the constellation of actors that operate within a bounded site (often characterized in relation to administrative boundaries). This type of approach has generated debates about the institutional conditions that enable effective climate action. A recent review attempted to summarize this body of literature, to reflect upon discussions regarding normative ideas of governance and the complexity of establishing multilevel governance across different levels of government and domains of action, which have remained stagnant (Castán Broto, Citation2017b).

Climate change challenges have to be addressed in the context of enormous gaps in urban infrastructure and service delivery in rapidly urbanizing areas, particularly in informal settlements with deficient urban equipment (Baker, Citation2012; Dodman, Bicknell, & Satterthwaite, Citation2012; Satterthwaite, Citation2007). Scholarly debates have also examined at length the institutional factors that enable effective climate change action; however, they have chiefly relied on experiences in global cities and networks based in the Global North. One important question has been what motivates local government to deliver climate change action, an how different exogenous and endogenous drivers facilitate or condition local capacities to respond to climate change imperatives (Anguelovski & Carmin, Citation2011; Carmin et al., Citation2012).

This body of work points to the need to engage with the rapidly changing, mobile and messy context of climate change action in urban areas. For example, empirical analyses have consistently demonstrated that climate change strategies need to be adapted to the context of action, when not developed within those specific conditions. There are not ready-made recipes for action that will be effective in every situation. For example, the persistent interest on traditional notions of political leadership as a driver of effective action (e.g., Burch, Citation2010; Janjua, Thomas, & McEvoy, Citation2010; Sanchez-Rodriguez, Citation2009; Shey & Belis, Citation2013) contrasts with an increasing realization that horizontal collaboration and self-organization are often central to deliver climate resilient pathways of urban development (Djalante, Holley, & Thomalla, Citation2011; Sovacool, Citation2011). Both styles of governing are relevant to deliver climate change action, in messy processes that require the combination of multiple strategies. A vision of climate change governance as a process of ‘muddling through’ has progressively gained ground in institutional analyses of how climate change policy is actually delivered on the ground (Marsden, Ferreira, Bache, Flinders, & Bartle, Citation2014).

These debates suggest that for any action to bring about a radical change in cities, spurring a low-carbon transition requires messy interactions across different realms of operation. Studies of multilevel governance highlight the multitude of actors that lead and deliver climate change action alongside local governments (Bulkeley & Betsill, Citation2005, Citation2013; Betsill & Bulkeley, Citation2006). Effective action depends on the alignment of state and non-state actors (Biermann & Pattberg, Citation2012; Okereke et al., Citation2009). For example, local governments often depend on the resources and support of state actors at the national level to deliver local-level actions (Dodman & Mitlin, Citation2015; Fidelman, Leitch, & Nelson, Citation2013; Hughes, Citation2013; Jones, Citation2013; van Stigt, Driessen, & Spit, Citation2013). The role of international organizations in providing information and facilitating innovation has long been documented (Monni & Raes, Citation2008). Finally, a range of other non-state actors, including business, networks, and communities intervene in urban governance, particularly adding capacities where these may be lacking (Amundsen, Berglund, & Westskog, Citation2010; Burch, Shaw, Dale, & Robinson, Citation2014; Dodman & Satterthwaite, Citation2008; Leck & Simon, Citation2013). Normative ideas of multilevel governance have gained currency as a response to the perceived complexity of a governance landscape populated by many actors (e.g., Jones, Citation2012; Sperling, Hvelplund, & Mathiesen, Citation2011). However, the organizational impulse of multilevel governance theory fails to overcome the messy character of the processes of governance on the ground (Smith, Citation2007). While multilevel governance theory is now an indispensable element of the conceptual toolbox for articulating debates on climate change policies, it falls short of explaining the global dynamics of policy innovation, and in particular, the translation of social, technological and institutional innovation across different contexts.

The literature on urban policy mobilities proposes a view of policy transfer as a process in which different components of the policy are reassembled to fit the context rather than as a rational process of adoption conducted by leading actors. An analysis of policy mobilities engages with both the specificity of the context in which policy is assembled and the aspects of policy that remain consistent regardless of the context where it is implemented (Temenos & McCann, Citation2013).

Processes usually described simply as linear policy transfers consist of complex and overlapping interactions during which tools of policy calculation are appropriated and reimagined. The analytical focus is not only on how policies move but also on how policies are disassembled and rearranged to suit the characteristics of particular contexts (McCann & Ward, Citation2012). This is something that directly matches the insights gained from empirical analyses of climate change governance in cities that attend to, among other things, the processes whereby climate change interventions are rendered feasible and made compelling to a wide range of actors (Bulkeley, Castán Broto, & Edwards, Citation2014). Policy mobilities are central to the construction of visions of green cities (McCann, Citation2013), although, within this literature, less attention has been paid to climate change governance in urban areas.

Methodologically, approaches for policy mobilities propose ‘following policy’, for example, by looking at the manifestations of an idea in different contexts and its materialization in specific events (Peck & Theodore, Citation2012). Thus, policies are no longer implemented in a bounded space (i.e., a city within a set of administrative boundaries) but rather they manifest across the multiple and mobile situations whereby cities are produced (McCann & Ward, Citation2012). Another key implication is that policies become the result of a social process of assemblage in particular locations (Peck & Theodore, Citation2012).

One methodological strategy is to follow the carriers of policies or the actors who embody certain principles and ideas and who transfer them across locations. However, it should not be assumed that thinking about mobile policies requires looking only at mobile actors, as policies can be adopted and appropriated through other mechanisms. Roy and Ong (Citation2011), for example, provide examples of the active role played by middling bureaucrats in negotiating an intervention space between global discourses of competitiveness and sustainability and the specific local demands of the contexts in which they operate. In climate change policy, for example, local policy-makers can translate environmental sustainability discourses into programmes of action that advance elite agendas without addressing urban inequality and the challenges of delivering health and services (Boyd, Ensor, Castán Broto, & Juhola, Citation2014). Meanwhile, the identification of mobile policies requires understanding those aspects of action that remain immobile – that is, not relatable across contexts (McCann & Ward, Citation2015). A focus on the movement of low-carbon policies beyond the context of the exemplary city is a strategy to rethink low-carbon action in the context of ‘ordinary cities’.

Decarbonization challenges call for engagement with messy, unusual sites of action

The third limitation of contemporary scholarship is its fixation with global cities as key sites of governance, emphasizing exemplars and best practice examples. Often, the examples available are unattainable for medium-sized cities (Hodson & Marvin, Citation2010). Alternatively, there is a suspicion that most cities outside global circuits of promotion and exposure will move towards addressing the lowest common denominator, sometimes limiting themselves to low-hanging fruit, even when this opportunity can be an avenue to initiate more meaningful climate action (Aylett, Citation2014). Moreover, there is a need to understand how such action in ordinary cities affects the lives of urban citizens.

Urban infrastructure landscapes represent the co-constitution of societies, ecologies and technological worlds in particular places (in the field of energy, see Bridge, Bouzarovski, Bradshaw, & Eyre, Citation2013; and Calvert, Citation2015). Landscapes are constituted through the interaction of material flows, ideological representations and the actual experiences of the world in specific locales. Simultaneously, landscapes have been explored through a rich tradition of empirical studies which take experience as an analytical point of departure to examine socio-natural relations (Wylie, Citation2006).

The author’s previous work has engaged with the concept of urban infrastructure landscapes to understand energy-related transformations occurring in contemporary cities (Castán Broto, Citation2017a, Citation2019). Initially, the author was inspired by Owens’ (Citation1986) classic work on the relationship between energy systems and spatial structure. First, Owens explains that the development of spatial structure depends on the nature, location and availability of energy sources. Second, Owens argues that spatial factors also shape energy requirements. Finally, Owens explains that energy sources, spatial structure, and energy requirements impose constraints on innovation and the possibility to introduce deliberate changes in energy systems. Sustainable urbanism scholarship has focused on improving energy efficiency through interventions in urban morphology and urban form (e.g., Howard et al., Citation2012; Rode, Keim, Robazza, Viejo, & Schofield, Citation2013; Salat, Citation2009; Wong et al., Citation2011; Zanon & Verones, Citation2013; Zhou, Lin, Cui, Qiu, & Zhao, Citation2013). A key concern has been the uncritical application of one-size-fits-all approaches to deliver sustainable urbanism models that fail to recognize the diversity of human settlements, such as with the imposition of compact city standards (for a seminal critique, see Jenks, Burton, & Williams, Citation1996). Attention to the urban context is essential for the creative development of multiple, parallel models of sustainable urbanism that address the challenges of specific locales (Williams, Jenks, & Burton, Citation2000).

Following this, urban energy landscapes can be understood as a means to capture the mutual constitution of urban energy infrastructures, energy governance processes, and spatially embedded practices of energy use (Castán Broto, Citation2019). Urban energy landscapes result from diverse and overlapping activities that involve energy use (lighting, communication, thermal comfort, cooking) and the means of provision of energy services (infrastructure and governance systems). The concept of landscape makes it explicit that all energy-dependent activities are contingent to socioecological relations and have a territorial expression. In practice, urban energy landscapes are no more than assemblages of socioecological and sociotechnical artefacts that acquire coherence and retain specificity as they are deployed in specific contexts:

For example, buying street food for dinner may require a lighting system, cooking devices, and perhaps a system of communications to pay for the meal with a credit card. Even when using similar technologies, the experience will be completely different in each city, from Munich to Marrakesh. From the structures of the built environment that support both cooking and selling to the lived experience of the city and how cooking is shaped by a specific culture, urban space shapes energy use and the means that support its provision. (Castán Broto, Citation2017a, p. 756)

Analyses of urban energy landscapes do not show a deliberate engagement with purposive attempts to claim authority over the contested fields of climate change governance in urban areas. From the perspective of urban energy landscapes, low-carbon innovations constitute new modifications in historical, situated trajectories of change. It is from this perspective that this paper proposes to reimagine current governance theory through an engagement with the concept of messiness as a strategy that embraces the methodologies of policy mobilities and urban energy landscapes and responds to global debates on climate governance.

GOVERNANCE AND MESSINESS: REIMAGINING CLIMATE CHANGE GOVERNMENTALITIES

Governmentality theory supports a critical perspective on governance that emphasizes how governing actions unfold in practice. Governing is presented as a process of ‘orchestration’, that is, as attempts at conducting and coordinating actions that involve surreptitious machinations to facilitate the alignment of interests, the persuasion of a variety of actors, and the overall integration of policy ideals with the material and practical conditions of action (Bäckstrand & Kuyper, Citation2017; Bulkeley, Citation2015). Michel Foucault’s governmentality theory has inspired the adoption of the idea of ‘governing as an art’ in climate change governance. For Bulkeley (Citation2015), governmentality theory highlights power as relational, that is, as emerging from the interactions between the actors and things that need govern and are governed. Governing requires, as well, enrolling people and things in the process of governing.

Certain tools or rationalities – governmentalities – are essential to facilitate a form of governing that requires an alignment between actors and things (Bulkeley et al., Citation2014). Governmentalities are developed to define interventions and strategies. Persuasion is the essential tool that enables the creation of subjects to be governed, subjects who regulate their own conduct and both adapt to and adopt appropriate dispositions that make governing possible (Bulkeley, Citation2015).

Climate change governmentalities include a series of calculus that relate material actions with rationales of intervention (While, Jonas, & Gibbs, Citation2010). For example, measuring carbon has been central to carbon governance as mitigation efforts are defined in relation to reductions in greenhouse gas emissions (e.g., Bulkeley, Citation2015; Rice, Citation2010; Pearce & Cooper, Citation2011). Linking material, spatial and social contexts of action to actual intervention possibilities is a means to demonstrate effectiveness and to persuade and enrol multiple climate publics (Knuth, Citation2010). In this sense, urban areas constitute arenas for climate politics within broader institutional and economic networks (Rutherford & Coutard, Citation2014). Multiple forms of knowledge are integrated into institutions alongside material artefacts in urban infrastructure networks (Monstadt, Citation2009). Governing climate change requires not only organizing existing materials and spaces but also providing new imaginations of urban futures and implementing new forms of urban service provision that can be validated at the global scale (Bulkeley et al., Citation2014). As explained above, orchestration platforms such as NAZCA are examples of mechanisms that aim to compute and value the new landscape of climate governance (Ven et al., Citation2017).

Self-governing is also central to the delivery of climate change governmentalities, as individuals regulate their behaviours and those of others. Self-governing entails a deeper process of cultural change, whereby bodies are integrated into newly imagined futures. Urban areas provide the grounds for different attempts to govern climate change through processes of behaviour change (Revell, Citation2013; Rice, Citation2014). Local authorities may emerge as intermediaries who facilitate broader cultural change for pro-environmental behaviour that focuses on controlling carbon and structural vulnerabilities to climate change (Dowling, McGuirk, & Bulkeley, Citation2014; While et al., Citation2010). Self-governing is also a key form of governance for municipal governments that have attempted to lead by example through greening their operations (Bulkeley & Kern, Citation2006). These kind of orchestrating governmentalities explain the configuration of the international climate regime in the post-Copenhagen context (Bäckstrand & Lövbrand, Citation2016).

However, within governmentality theory, there is a weaker sense of the relationship between the deployment of climate change rationalities of material and personal control, and the material changes that transform urban areas over time. The specific ways in which urban socioecological systems are known and lived without recourse to strategic projects are less visible in a theory that emphasizes deliberate mechanism for orchestration and control. Is there an opportunity for the development of alternative theorizations of governance and messiness that emerge from within the particular debates and concerns in specific cities and how cities change? Following Haraway’s understanding of knowledge (see below), can we engage with the politics of situated governmentalities?

Conceptually, we can imagine governance as a messy process that depends on multiple random connections between technologies, discourses and actions. While governance is conventionally thought as a means for ordering the world, effective governance depends on navigating disorder and engaging with the confusion that emerges from having multiple points of view about what is possible or desirable. Rather than seeking success, policy-makers often talk of governance as a process of ‘muddling through’ (cf. Marsden et al., Citation2014).

The present paper ends with a call for the development of a conceptual framework that reflects messiness in governance, as this messiness is noticeable in particular locations and moments of action. While governmentality theory is often associated with efforts to establish order and control, it argued here that messiness is central to any attempts to govern. A modest proposal is made here to look at governmentality theory through the lens of messiness in governance. Governmentality theory links three aspects of governance (Bulkeley et al., Citation2014; Li, Citation2007): a will to improve associated with strategic intent, a repertoire of rationalities of government grounded on the production of knowledge and calculations, and an emphasis on the conduct of conduct through the regulation of bodies. Strategy, knowledge, and bodies are the three legs of analysis to engage with a theory of messiness. In this vein, climate change action is explained as the result of three different elements: the strategic ideas that motivate it, the calculations and technologies that make it possible, and the fit of action to a particular context.

Theories of messiness and urban change

The three aspects of the practice of governing explained above have been documented in climate change arenas (Bulkeley, Citation2015; Bulkeley et al., Citation2014; Dowling et al., Citation2014). First, the deployment of governmentalities is associated with an interest to build forms of authority over a given space. In other words, governmentalities emerge associated with purpose and intention, particularly in the sense of mobilizing the future through a plan for something to be done. For Li (Citation2007), in the context of international development in Indonesia, such purposes or intentions are intrinsically linked to ideas of improvement that relate both to value enhancement and to the purposeful use of resources of development.

Second, governmentalities imply some form of calculation. While et al. (Citation2010) explain that controlling carbon depends on the deployment of strategic calculations, crafted through the deployment of environmental policy.

Third, environmental governmentalities are not only linked to a particular will to gain power and authority over the world and the territory but also to the ability to control the self (Paterson & Stripple, Citation2010; Stripple & Bulkeley, Citation2013). The exercise of power in the environmental field depends on the multiple abilities to reach the sites of governing: strategy, knowledge, body.

On this basis, hypothesize the importance of messiness in the deployment of climate change governmentalities. The most immediate reaction is that in a messy and uncertain world, governmentalities are directed towards creating forms of order that enable intervention: identifying purposes, creating calculations, pointing at the individuals who would deploy those calculative rationalities over themselves and the world. In other words, it is the encounter with the world’s messiness that moves policy-makers, activists and organizations to establish forms of control and intervention. What if we could turn that approach on its head and put forward the idea that the art of government depends on messy experiences to enable governing and that in the encounter with the world (messy or not), the ability to harness mess ultimately determines which strategies, calculations and bodies become important in the act of governing climate change? If we start from the perspective of the classical anthropologist Mary Douglas, who looked at messiness as ‘matter out of place’, we immediately engage with messiness as something that incites revelation (Douglas, Citation2003). The placing of one’s shoes on the table, Douglas argues, is an act of quotidian transgression that reveals the cultural basis of human organization. The most fundamental of human fictions are those that help us to conceive of the orderly world through the establishment of boundaries between what is ‘in’ and ‘out’ of place.

Returning to a reflection on messiness and its interaction with strategies/knowledges/bodies, first consider the deployment of strategic projects. An encounter with a city’s ungovernability opens up ideas of messiness. In some cases, low-carbon action is related to the possibility of mobilizing heterogeneous infrastructure configurations (Lawhon, Nilsson, Silver, Ernstson, & Lwasa, Citation2018). Silver (Citation2014, p. 79), for example, defends a focus on incremental infrastructures as one that examines infrastructures ‘in-the-making, under constant adjustment, and shifting technological and material configurations’. In his experiences in Accra and other African cities, Silver highlights how citizens themselves configure how infrastructures work, and in so doing, they also reveal what strategic futures are possible. Messiness in conceptualizations of infrastructure can open up alternatives to dominant mechanisms of making urban strategies in a postcolonial context. This becomes particularly important in low-carbon action because of the need to move away from triumphal analyses of initiatives in global wealthy cities and to examine instead the mundane spaces of spatial transformation in the city: strategic projects become distributed and relatable, something never entirely apprehended in high modernist projects à la Scott. In a postcolonial context, hegemonic projects often appear to be ridiculous in their intent to govern, resembling fantasies of urban domination that nevertheless do not compromise the landscape of intervention but rather await their opportunity to jump from the corners into the spotlight of governance discourses.

Second, consider calculations. In an article about the governing impulses of environmental programmes in US universities, Luke (Citation1996, p. 1) described his environmental concerns as concerns of knowledge:

In and of itself, Nature is meaningless unless or until particular human beings assign significance to it by interpreting some of its many ambivalent signs as meaningful to them. The outcomes of this activity, however, are inescapably indeterminate, or at least, they are a culturally contingent function of who decodes which signs when and how they find decisive meaning there. Because human beings will observe natural patterns differently, choose to accentuate some, while deciding to ignore others, Nature’s meanings always will be multiple and unfixed.  …  And, once Nature is rendered intelligible through these discursive processes, it can be used to legitimize many political projects.

That act of rendering nature intelligible reveals a utilitarian approach to bound, identify and fill in ‘resources’, Luke highlights the meaningless, disordered character of Nature before humans, in the ultimate act of making nature intelligible, decide to ascribe meaning to it, in a process that is fraught with lack of understanding, multiple meanings and different interpretations. However, what is the act of creating intelligibility, if not one, strictly, of ordering? How do things become known? The philosopher of science Paul Feyerabend stood against contemporaries by refusing to accept the idea of science based on methods that follow from clearly delimited principles (Feyerabend, Citation1993). He did so on the grounds of two unacceptable assumptions: first, the idea that there was a certain autonomy between facts and theory that would enable humans to identify discontinuities and inadequacies in theory by simply bringing those facts to light; and second, the idea that in science, there is a clear uniformity in which scientists tend towards conformity rather than towards distinguishing themselves. For Feyerabend, such a conceptualization of an ordering science in which facts help to perfect theory (as a reaction to his own enchantment with Karl Popper’s ideas) and organize social–scientific life not only is inadequate to explain how science ‘should be’ but also how it actually is – for example, how it is embodied in passions and an anarchic drive that helped scientists such as Galileo Galilei to make believe what was unbelievable by the standards of his time.

The challenge for governmentality scholars who share Luke’s concerns is the critical examination of any putative straightforward relationship between intelligibility and purpose. Nature commodification is preceded, Luke says, by an inherent understanding of nature as a resource, ready for human manipulation and use. However, the forms of knowledge that make manipulation and use purpose are not predetermined. The present paper follows Feyerabend’s objection to the autonomy of facts and theory: the process of observing nature itself is chaotic and led by commitments and passions. Knowledge cannot solely be a means for ordering, even though ordering itself may need of certain knowledges to make it possible. Similar intent inspires Law’s (Citation2004) claim that attempts to transform science into a hegemonic, unified (ordering) project limits what science is and how it happens.

Fast forward to Haraway’s (Citation1988) critique of objectivity, and we find ourselves liberated by the idea that knowledge is produced within a given relational, situated setting, and hence, free from constraints that attempt to reduce science to instances of mutually agreed universal knowledge. Later in Haraway’s work, this realization would translate into recognizing knowledge production as a committed rather than an objectivist and cynical enterprise (not that far from Galileo’s commitment to his intellectual project, as per Feyerabend’s analysis). Aside from the descriptive claim, the idea of situated knowledge put at the core of knowledge, making activities ‘a view from the margins’, and the question of the lack autonomy between facts and theory becomes a question of lack of autonomy between understanding and experiencing in the contingent contexts in which knowledge is produced (Widerberg, Citation2005). In practice, messiness for researchers means (1) engaging with the material, contingent contexts of knowledge production; (2) recognizing the lack of boundaries between understanding and experiencing; and (3) recognizing the contingency of knowledge-making encounters, where it is impossible to separate between subjective accounts and objective facts (Askins & Pain, Citation2011). In climate change governance, there has been a growing interest in the dynamics of experimentation as a means to build alternative actions in the context of uncertainty. However, there has been a continuous production and re-enactment of the rationalities that underpin the experimentation processes. Making an experiment requires assembling narratives of intervention, but experiments themselves remake those narratives. Both processes of engaging with and making messiness are central to knowledge-making and, therefore, enable governing.

Third, consider the body. If the body is the central site of both disciplining and knowing, how do we confront the ever-increasing realization that the body itself is not amenable to clear ordering patterns? A biopolitical project will depend on the identification of bodies whose conduct is understood and regulated and that can be disciplined but in specific contexts. However, if bodies are messy and leaky (Longhurst, Citation2004), then governing requires engaging with such messiness. For example, carbon control policies have drawn strongly on ideas of individual carbon budgets and other devices to help individuals make a rational choice about the carbon emissions they produce (Paterson & Stripple, Citation2010; Stripple & Bulkeley, Citation2013). This has had some effects: for example, it may create visible areas of action. However, accepting that there is a linkage between such visibility and the inclination of people to do something about low carbon, let alone bring about a societal transformation, is grossly exaggerated. Such changes depend on multiple forms of attachment to spaces and the generation of emotional linkages that make different actions possible. Some carbon activists are already moving in that direction by seeking to activate societal transformations through creative means, including theatre, creative writing, or storytelling. The body and its relations are highly unstable sites of action that can hardly be disciplined.

Thus, if we think of ‘mess’ as a point of access to deliver change, then we find an action that emerges at the intersection of messy interactions between strategy, knowledge, and bodies (). In terms of urban governance and climate change, those intersections raise three starting points for analysis:

Figure 1. Perspectives on messiness and governance.

Figure 1. Perspectives on messiness and governance.
  • Mess draws attention to the semiotic–material interlinkages between bodies and the worlds they inhabit as a key to understand the possibilities for intervention in a particular context, as exemplified in the ideas of bodies as infrastructures of everyday life.

  • Mess, with respect to knowledge production processes, relates to a situated, experiential notion, which emphasizes the contingent character of social innovation.

  • Mess requires an open approach to understand the relationship between the observer and the observed in the process of making sense of the processes of governing, as they are intrinsically linked in the mobilization of actions.

CONCLUSIONS

Bhabha (Citation2004, p. 134) wrote that ‘the political moment of cultural difference emerges within the problematic of colonial governmentality and eclipses the transparency between legibility and legitimate rule’ (p. 94). Scholarship on policy mobilities and urban energy landscapes has generated methodologies to study situated trajectories of change but there is a need to translate those analyses into concrete insights to deliver global assessments of climate change governance in cities. Messiness reimagines alternatives to hegemonic governmentalities by opening the climate change sphere as a governing arena that can also be appropriated to contest the structures of power and forms of domination that emerge in a postcolonial context. Mess challenges that thing that Bhabha beautifully calls ‘the transparency between legibility and legitimate rule’ (p. 134). It challenges not only strategies, knowledges and bodies but also how the three are brought together in attempts to build authority.

The academic debate within the climate change governance literature has focused on the low-carbon experiences of wealthy, globally connected cities that are perceived to be leading innovators rather than focusing on a mass of undifferentiated cities whose urban experiences are thought of as ordinary. All that which is ordinary in climate change governance becomes unremarkable. However, if we are to witness the kind of transformational change that will bring new cultures, societies, and economies, we need a new politics of change that is built upon the efforts of such ordinary actions not only because climate change action must be on a scale that engages with the multiplicities and the repetition in ordinary lives but also because ordinary actions point towards the political potential of messiness: while such messiness is constantly appropriated in the re-adaptation of high modernity strategies to changing environments, it continues to offer opportunities for what Bhabha calls ‘the political moment of cultural difference’ in specific contexts of climate action.

ACKNOWLEDGEMENTS

This paper was originally presented as the 2018 Territory, Politics, Governance Annual Lecture at the Regional Studies Association Global Conference in Beijing, China. The theme of the conference was Regional Governance, Industrial Restructuring and Sustainable Development. Thanks to Sally Hardy and Daniela Carl for their support and encouragement during the event. A short version of this paper was presented at the session Theorizing the Just City in the Era of Climate Change, organized by Joshua Long, Jennifer Rice and Anthony Levenda, at the 2019 Annual Meeting of the American Association of Geographers. Thanks to Professor John Agnew for his help and patience, as well as to three anonymous reviewers for their insights.

DISCLOSURE STATEMENT

No potential conflict of interest was reported by the author.

ORCID

Vanesa Castán Broto http://orcid.org/0000-0002-3175-9859

Additional information

Funding

The findings reported in this paper are part of a project that has received funding from the European Research Council (ERC) under the European Union’s Horizon 2020 research and innovation programme Grant Agreement No 804051 — LO-ACT — ERC-2018-STG.

REFERENCES

  • Amundsen, H., Berglund, F., & Westskog, H. (2010). Overcoming barriers to climate change adaptation a question of multilevel governance? Environment and Planning C – Government and Policy, 28(2), 276–289.
  • Anguelovski, I., & Carmin, J. (2011). Something borrowed, everything new: Innovation and institutionalization in urban climate governance. Current Opinion in Environmental Sustainability, 3(3), 169–175.
  • Askins, K., & Pain, R. (2011). Contact zones: Participation, materiality, and the messiness of interaction. Environment and Planning D: Society and Space, 29(5), 803–821.
  • Aylett, A. (2014). Progress and challenges in the urban governance of climate change: Results of a global survey. Cambridge, MA: MIT.
  • Bäckstrand, K., & Kuyper, J. W. (2017). The democratic legitimacy of orchestration: The UNFCCC, non-state actors, and transnational climate governance. Environmental Politics, 26, 764–788.
  • Bäckstrand, K., & Lövbrand, E. (2016). The road to Paris: Contending climate governance discourses in the post-Copenhagen era. Journal of Environmental Policy & Planning, 1–19.
  • Bain, P. G., Milfont, T. L., Kashima, Y., Bilewicz, M., Doron, G., Garðarsdóttir, R. B., … Pasquali, C. (2016). Co-benefits of addressing climate change can motivate action around the world. Nature Climate Change, 6(2), 154–157.
  • Baker, J. L. (2012). Climate change, disaster risk, and the urban poor: Cities building resilience for a changing world. Washington, DC: World Bank Publications.
  • Barnett, C., & Parnell, S. (2016). Ideas, implementation and indicators: Epistemologies of the post-2015 urban agenda. Environment and Urbanization, 28(1), 87–98.
  • Bartlett, S., & Satterthwaite, D. (2016). Cities on a Finite Planet: Towards transformative responses to climate change. Abingdon, Oxon: Routledge.
  • Betsill, M., & Bulkeley, H. (2007). Looking back and thinking ahead: A decade of cities and climate change research. Local Environment, 12(5), 447–456.
  • Betsill, M. M., & Bulkeley, H. (2006). Cities and the multilevel governance of global climate change. Global Governance: A Review of Multilateralism and International Organizations, 12(2), 141–160.
  • Bhabha, H. K. (2004). The location of culture. Abigndon: Routledge Classics.
  • Biermann, F., & Pattberg, P. H. (2012). Global environmental governance reconsidered. Cambridge, MA: MIT Press.
  • Boyd, E., Ensor, J., Castán Broto, V., & Juhola, S. (2014). Environmentalities of urban climate governance in Maputo, Mozambique. Global Environmental Change – Human and Policy Dimensions, 26, 140–151.
  • Bridge, G., Bouzarovski, S., Bradshaw, M., & Eyre, N. (2013). Geographies of energy transition: Space, place and the low-carbon economy. Energy Policy, 53(0), 331–340.
  • Bulkeley, H. (2013). Cities and climate change. Abingdon, Oxon: Routledge.
  • Bulkeley, H. (2015). Accomplishing climate governance. Cambridge: Cambridge University Press.
  • Bulkeley, H., & Betsill, M. M. (2005). Rethinking sustainable cities: Multilevel governance and the ‘urban’ politics of climate change. Environmental Politics, 14(1), 42–63.
  • Bulkeley, H., & Betsill, M. M. (2013). Revisiting the urban politics of climate change. Environmental Politics, 22(1), 136–154.
  • Bulkeley, H., & Castán Broto, V. (2013). Government by experiment? Global cities and the governing of climate change. Transactions of the Institute of British Geographers, 38(3), 361–375.
  • Bulkeley, H., Castán Broto, V., Hodson, M., & Marvin, S. (2010). Cities and low carbon transitions. London: Routledge.
  • Bulkeley, H., & Kern, K. (2006). Local government and the governing of climate change in Germany and the UK. Urban Studies, 43(12), 2237–2259.
  • Bulkeley, H., & Newell, P. (2015). Governing climate change. Abingdon, Oxon: Routledge.
  • Bulkeley, H. A., Castán Broto, V., & Edwards, G. A. (2014). An urban politics of climate change: Experimentation and the governing of socio-technical transitions. Abingdon, Oxon: Routledge.
  • Burch, S. (2010). Transforming barriers into enablers of action on climate change: Insights from three municipal case studies in British Columbia, Canada. Global Environmental Change – Human and Policy Dimensions, 20(2), 287–297.
  • Burch, S., Shaw, A., Dale, A., & Robinson, J. (2014). Triggering transformative change: A development path approach to climate change response in communities. Climate Policy, 14(4), 467–487.
  • Bureau of the Preparatory Committee. (2016). Zero draft of the New Urban Agenda. Nairobi: UN-Habitat.
  • Calvert, K. (2015). From ‘energy geography’ to ‘energy geographies’ Perspectives on a fertile academic borderland. Progress in Human Geography: 0309132514566343.
  • Carmin, J., Anguelovski, I., & Roberts, D. (2012). Urban climate adaptation in the global South: Planning in an emerging policy domain. Journal of Planning Education and Research, 32(1), 18–32.
  • Castán Broto, V. (2017a). Energy landscapes and urban trajectories towards sustainability. Energy Policy, 108, 755–764.
  • Castán Broto, V. (2017b). Urban governance and the politics of climate change. World Development, 93, 1–15.
  • Castán Broto, V. (2019). Urban energy landscapes. Cambridge: Cambridge University Press.
  • Castán Broto, V., & Bulkeley, H. (2013). A survey of urban climate change experiments in 100 cities. Global Environmental Change, 23(1), 92–102.
  • Castán Broto, V., & Westman, L. (2017). Just sustainabilities and local action: Evidence from 400 flagship initiatives. Local Environment, 22(5), 635–650.
  • Chan, S., van Asselt, H., Hale, T., Abbott, K. W., Beisheim, M., Hoffmann, M., … Widerberg, O. (2015). Reinvigorating international climate policy: A comprehensive framework for effective nonstate action. Global Policy, 6(4), 466–473.
  • Davis, S. J., & Socolow, R. H. (2014). Commitment accounting of CO2 emissions. Environmental Research Letters, 9(8), 084018.
  • Djalante, R., Holley, C., & Thomalla, F. (2011). Adaptive governance and managing resilience to natural hazards. International Journal of Disaster Risk Science, 2(4), 1–14.
  • Dodman, D., Bicknell, J., & Satterthwaite, D. (2012). Adapting cities to climate change: Understanding and addressing the development challenges. London: Routledge.
  • Dodman, D., & Mitlin, D. (2015). The national and local politics of climate change adaptation in Zimbabwe. Climate and Development, 7(3), 223–234.
  • Dodman, D., & Satterthwaite, D. (2008). Institutional capacity, climate change adaptation and the urban poor. Ids Bulletin – Institute of Development Studies, 39(4), 67–74.
  • Douglas, M. (2003). Purity and danger: An analysis of concepts of pollution and taboo. London: Routledge.
  • Dowling, R., McGuirk, P., & Bulkeley, H. (2014). Retrofitting cities: Local governance in Sydney, Australia. Cities (London, England), 38, 18–24.
  • Feyerabend, P. (1993). Against method. London: Verso.
  • Fidelman, P. I. J., Leitch, A. M., & Nelson, D. R. (2013). Unpacking multilevel adaptation to climate change in the Great Barrier Reef, Australia. Global Environmental Change – Human and Policy Dimensions, 23(4), 800–812.
  • Frantzeskaki, N., Castán Broto, V., Coenen, L., & Loorbach, D. (2017). Urban sustainability transitions. London: Routledge.
  • Gebre-Egziabher, A. (2004). Sustainable cities programme: A joint UN-HABITAT–UNEP facility on the urban environment with participation of the Dutch government. Urban Biosphere and society: Partnership of Cities, 1023, 62–79.
  • Habitat III Secretariat. (2016). New urban agenda (English). Quito: United Nations. Retrieved from http://habitat3.org/the-new-urban-agenda/
  • Hale, T. (2016). ‘All hands on deck’: The Paris agreement and nonstate climate action. Global Environmental Politics, 16(3), 12–22.
  • Haraway, D. (1988). Situated knowledges: The science question in feminism and the privilege of partial perspective. Feminist Studies, 14(3), 575–599.
  • Harlan, S. L., & Ruddell, D. M. (2011). Climate change and health in cities: Impacts of heat and air pollution and potential co-benefits from mitigation and adaptation. Current Opinion in Environmental Sustainability, 3(3), 126–134.
  • Hodson, M., & Marvin, S. (2010). World cities and climate change: Producing urban ecological security. Maidenhead, UK: McGraw-Hill Education.
  • Hodson, M., & Marvin, S. (2017). Intensifying or transforming sustainable cities? Fragmented logics of urban environmentalism. Local Environment, 22, 8–22.
  • Hoffmann, M. J. (2011). Climate governance at the crossroads: Experimenting with a global response after Kyoto. Oxford: Oxford University Press.
  • Howard, B., Parshall, L., Thompson, J., Hammer, S., Dickinson, J., & Modi, V. (2012). Spatial distribution of urban building energy consumption by end use. Energy and Buildings, 45, 141–151.
  • Hsu, A., Weinfurter, A. J., & Xu, K. (2017). Aligning subnational climate actions for the new post-Paris climate regime. Climatic Change, 142(3), 419–432.
  • Hughes, S. (2013). Authority structures and service reform in multilevel urban governance: The case of wastewater recycling in California and Australia. Urban Affairs Review, 49(3), 381–407.
  • Hughes, S., Chu, E. K., & Mason, S. G. (2018). Climate change in cities: Innovations in multi-level governance. Amsterdam: Springer.
  • IPCC. (2014). Climate change 2014, synthesis report. Contribution of working groups I, II and III to the fifth assessment report of the intergovernmental panel on climate change. Geneva: Author.
  • Janjua, S., Thomas, I., & McEvoy, D. (2010). Framing climate change adaptation learning and action: The case of Lahore, Pakistan. International Journal of Climate Change Strategies and Management, 2(3), 281–296.
  • Jenks, M., Burton, E., & Williams, K. (1996). The compact city: A sustainable urban form? London: Spon Press.
  • Jones, S. (2012). A tale of two cities: Climate change policies in Vancouver and Melbourne – Barometers of cooperative federalism? International Journal of Urban and Regional Research, 36(6), 1242–1267.
  • Jones, S. (2013). Climate change policies of city governments in federal systems: An analysis of Vancouver, Melbourne and New York city. Regional Studies, 47(6), 974–992.
  • Kern, K., & Alber, G. (2009). Governing climate change in cities: Modes of urban climate governance in multi-level systems. The international conference on competitive cities and climate change, Milan, Italy, 9–10 October, 2009.
  • Knuth, S. E. (2010). Addressing place in climate change mitigation: Reducing emissions in a suburban landscape. Applied Geography, 30(4), 518–531.
  • Law, J. (2004). After method: Mess in social science research. London: Routledge.
  • Lawhon, M., Nilsson, D., Silver, J., Ernstson, H., & Lwasa, S. (2018). Thinking through heterogeneous infrastructure configurations. Urban Studies, 55(4), 720–732.
  • Leck, H., & Simon, D. (2013). Fostering multiscalar collaboration and co-operation for effective governance of climate change adaptation. Urban Studies, 50(6), 1221–1238.
  • Li, T. M. (2007). The will to improve. Durham and London: Duke University Press.
  • Longhurst, R. (2004). Bodies: Exploring fluid boundaries. London, New York: Routledge.
  • Luke, T. W. (1996). Generating green governmentality: A cultural critique of environmental studies as a power/knowledge formation. Unpublished manuscript. Retrieved from www.cddc.vt.edu/tim/tims/Tim514a.PDF
  • Marsden, G., Ferreira, A., Bache, I., Flinders, M., & Bartle, I. (2014). Muddling through with climate change targets: A multi-level governance perspective on the transport sector. Climate Policy, 14(5), 617–636.
  • McCann, E. (2011). Urban policy mobilities and global circuits of knowledge: Toward a research agenda. Annals of the Association of American Geographers, 101(1), 107–130.
  • McCann, E. (2013). Policy boosterism, policy mobilities, and the extrospective city. Urban Geography, 34(1), 5–29.
  • McCann, E., & Ward, K. (2012). Assembling urbanism: Following policies and ‘studying through’ the sites and situations of policy making. Environment and Planning A, 44(1), 42–51.
  • McCann, E., & Ward, K. (2015). Thinking through dualisms in urban policy mobilities. International Journal of Urban and Regional Research, 39(4), 828–830.
  • Monni, S., & Raes, F. (2008). Multilevel climate policy: The case of the European Union, Finland and Helsinki. Environmental Science & Policy, 11(8), 743–755.
  • Monstadt, J. (2009). Conceptualizing the political ecology of urban infrastructures: Insights from technology and urban studies. Environment and Planning A, 41(8), 1924–1942.
  • Newell, P., Pattberg, P., & Schroeder, H. (2012). Multiactor governance and the environment. Annual Review of Environment and Resources, 37(37), 365–387.
  • Okereke, C., Bulkeley, H., & Schroeder, H. (2009). Conceptualizing climate governance beyond the international regime. Global Environmental Politics, 9(1), 58–78.
  • Owens, S. E. (1986). Energy, planning and urban form. London: Taylor & Francis.
  • Parnell, S. (2016). Defining a global urban development agenda. World Development, 78, 529–540.
  • Paterson, M., & Stripple, J. (2010). My space: Governing individuals’ carbon emissions. Environment and Planning D: Society and Space, 28(2), 341–362.
  • Pearce, G., & Cooper, S. (2011). Sub-national responses to climate change in England: Evidence from local area agreements. Local Government Studies, 37(2), 199–217.
  • Peck, J., & Theodore, N. (2012). Follow the policy: A distended case approach. Environment and Planning A, 44(1), 21–30.
  • Reckien, D., Flacke, J., Dawson, R. J., Heidrich, O., Olazabal, M., Foley, A., … Pietrapertosa, F. (2014). Climate change response in Europe: What’s the reality? Analysis of adaptation and mitigation plans from 200 urban areas in 11 countries. Climatic Change, 122(1), 331–340.
  • Revell, K. (2013). Promoting sustainability and pro-environmental behaviour through local government programmes: Examples from London, UK. Journal of Integrative Environmental Sciences, 10(3–4), 199–218.
  • Rice, J. L. (2010). Climate, carbon, and territory: Greenhouse gas mitigation in Seattle, Washington. Annals of the Association of American Geographers, 100(4), 929–937.
  • Rice, J. L. (2014). Public targets, private choices: Urban climate governance in the pacific Northwest. Professional Geographer, 66(2), 333–344.
  • Robinson, J. (2013). Ordinary cities: Between modernity and development. London: Routledge.
  • Rode, P., Keim, C., Robazza, G., Viejo, P., & Schofield, J. (2013). Cities and energy: Urban morphology and residential heat-energy demand. Environment and Planning B: Planning and Design, 41(1), 138–162.
  • Rosenau, J. N. (2000). Change, complexity, and governance in globalizing space. In: J. Pierre (Ed.), Debating governance (pp. 167–200). Oxford: Oxford University Press.
  • Roy, A., & Ong, A. (Eds.). (2011). Worlding cities: Asian experiments and the art of being global (Vol. 42). Malden: John Wiley & Sons.
  • Rutherford, J., & Coutard, O. (2014). Urban energy transitions: Places, processes and politics of socio-technical change. Urban Studies, 51(7), 1353–1377.
  • Salat, S. (2009). Energy loads, CO2 emissions and building stocks: Morphologies, typologies, energy systems and behaviour. Building Research & Information, 37(5–6), 598–609.
  • Sanchez-Rodriguez, R. (2009). Learning to adapt to climate change in urban areas. A review of recent contributions. Current Opinion in Environmental Sustainability, 1(2), 201–206.
  • Satterthwaite, D. (2007). Adapting to climate change in urban areas: The possibilities and constraints in low- and middle-income nations. London: IIED.
  • Seto, K. C., Dhakal, S., Bigio, A., Blanco, H., Delgado, G. C., Dewar, D., … Ramaswami, A. (2014). Human settlements, infrastructure and spatial planning. Climate change 2014: Mitigation of climate change. Contribution of Working Group III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change, O. Edenhofer, R. Pichs-Madruga, Y. Sokona, E. Farahani, S. Kadner, K. Seyboth, A. Adler, I. Baum, S. Brunner, P. Eickemeier, B. Kriemann, J. Savolainen, S. Schlömer, C. Von Stechow, T. Zwickel and J.C. Minx. Cambridge: Cambridge University Press.
  • Shey, J. E., & Belis, D. (2013). Building a municipal food policy regime in Minneapolis: Implications for urban climate governance. Environment and Planning C – Government and Policy, 31(5), 893–910.
  • Silver, J. (2014). Incremental infrastructures: Material improvisation and social collaboration across post-colonial Accra. Urban Geography, 35(6), 788–804.
  • Smith, A. (2007). Emerging in between: The multi-level governance of renewable energy in the English regions. Energy Policy, 35(12), 6266–6280.
  • Solecki, W. D., & Leichenko, R. M. (2006). Urbanization and the metropolitan environment – lessons from New York and Shanghai. Environment, 48(4), 8–23.
  • Sovacool, B. K. (2011). An international comparison of four polycentric approaches to climate and energy governance. Energy Policy, 39(6), 3832–3844.
  • Sperling, K., Hvelplund, F., & Mathiesen, B. V. (2011). Centralisation and decentralisation in strategic municipal energy planning in Denmark. Energy Policy, 39(3), 1338–1351.
  • Stripple, J., & Bulkeley, H. (2013). Governing the climate: New approaches to rationality, power and politics. Cambridge: Cambridge University Press.
  • Temenos, C., & McCann, E. (2013). Geographies of policy mobilities. Geography Compass, 7(5), 344–357.
  • UN. (2014). World urbanization prospects: The 2014 revision. New York, NY: United Nations Population Division.
  • UN-Habitat. (2011). Global report on human settlements: Cities and climate change. Nairobi: Author.
  • van Stigt, R., Driessen, P. P. J., & Spit, T. J. M. (2013). Compact city development and the challenge of environmental policy integration: A multi-level governance perspective. Environmental Policy and Governance, 23(4), 221–233.
  • Ven, H. v. d., Bernstein, S., & Hoffmann, M. (2017). Valuing the contributions of nonstate and subnational actors to climate governance. Global Environmental Politics, 17(1), 1–20.
  • While, A., Jonas, A. E. G., & Gibbs, D. (2010). From sustainable development to carbon control: Eco-state restructuring and the politics of urban and regional development. Transactions of the Institute of British Geographers, 35(1), 76–93.
  • Widerberg, K. (2005). ‘Situating knowledge-liberating or oppressive.’ Challenging situatedness: Gender, culture and the production of knowledge. Delft: Eburon, pp. 259–267.
  • Williams, K., Jenks, M., & Burton, E. (2000). Achieving sustainable urban form. London: Spon Press.
  • Woetzel, J., Garemo, N., Michke, J., Hjerpe, M., & Palter, T. (2016). Bridging global infrastructure gaps. McKinsey Global Institute.
  • Wong, N. H., Jusuf, S. K., Syafii, N. I., Chen, Y., Hajadi, N., Sathyanarayanan, H., & Manickavasagam, Y. V. (2011). Evaluation of the impact of the surrounding urban morphology on building energy consumption. Solar Energy, 85(1), 57–71.
  • World Bank. (2011). Climate change and cities: Responding to an urgent agenda. Washington DC: Author.
  • Wylie, J. (2006). Depths and folds: On landscape and the gazing subject. Environment and Planning D, 24(4), 519–535.
  • Zanon, B., & Verones, S. (2013). Climate change, urban energy and planning practices: Italian experiences of innovation in land management tools. Land Use Policy, 32, 343–355.
  • Zhou, J., Lin, J., Cui, S., Qiu, Q., & Zhao, Q. (2013). Exploring the relationship between urban transportation energy consumption and transition of settlement morphology: A case study on Xiamen Island, China. Habitat International, 37, 70–79.