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      Policy experimentation: core concepts, political dynamics, governance and impacts

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          Abstract

          The experimentalist ‘turn’ in science In the last two decades, many areas of the social sciences have embraced an ‘experimentalist turn’. It is well known for instance that experiments are a key ingredient in the emergence of behavioral economics, but they are also increasingly popular in sociology, political science, planning, and in architecture (see McDermott 2002). It seems that the potential advantages of experiments are better appreciated today than they were in the past. But the turn towards experimentalism is not without its critics. In her passionate plea for more experimentation in political science for instance, McDermott (2002: 42) observes how many political scientists are hesitant: they are more interested in large-scale multiple regression work, lack training in experimentation, do not see how experiments could fit into a broader research strategy, and alternative movements in political science (such as constructivists and postmodernists) consider that experimental work is not able to capture complexities and nuances. Representing some of these criticisms, Howe (2004) suggests that experimentation is being oversold and highlights various complications, especially the trade-offs that exist between internal and external validity, the fact that causal inferences can be generated using many other research methods, and the difficulty of comparing governance interventions to new medications in medicine. Even if McDermott (2002) and Howe completely disagree on the potential of experiments, they do agree that experiments should mainly be seen as a research method. But this is clearly not the only way in which experiments are viewed in practice; indeed there are many signs that the experimentalist turn is restricted to issues of methodology. Far from it. In an influential overview of the experimentalist turn in a range of disciplines, Ansell and Bartenberger (2016) suggest that the term experiment denotes a range of forms and activities. It is, for example, being used to refer to the design and evaluation of institutional arrangements, to the encouragement of social and political learning, and to the triggering of innovations and transitions (ibid.: 64). In other words, experimentalism is being actively equated with a distinct approach to governing, including but not limited to public policy. This change in conceptualization is one reason why it could be interesting, also for policy scientists, to engage with the experimentalist turn, and this is exactly the purpose of this special issue. Our main goal is to identify the scope for mutual learning, between this turn and the policy sciences. What new insights, for example, does the new work on experimentation offer to those in the policy sciences who have been wrestling with experimentation for many years, even decades? And just as importantly, what can policy scientists add to the new experimentalist literature with respect to core concepts, methods, theoretical insights and empirical findings? In this introductory paper, we seek to address these questions by exploring experimentation in relation to climate governance. This provides a good opportunity to showcase new experimentalist turn in action, in its various shapes and forms. Why this particular case? There is probably no field where the impact of the experimentalist turn has been greater than that of sustainability studies, of which the discussion on climate governance is but one part. At least two leading current approaches—transitions management (see for instance Voß et al. 2009; Berkhout et al. 2010) and adaptive co-management (see for instance Huitema et al. 2009)—regard experimentation as being foundational. Both treat experiments as the starting point (or seed) for desirable societal transformations (for an overview, see Den Uyl 2014). And in more specific discussions on how to govern climate change, experimentation is increasingly mentioned as a critical part of the way forward (see for instance Hildén et al. 2017). The past decade has seen a steep increase in the adoption and implementation of measures—in the public and private realms, nationally and internationally (Bulkeley et al. 2012; Dubash et al. 2013). Since agreement at the global level has often proven to be elusive, hopes are increasingly pinned on initiatives at lower jurisdictional levels, on public–private partnerships, on NGOs and other societal actors, and on business-to-business initiatives. Such initiatives are widely seen as experiments (see for instance Hoffmann 2011; Bulkeley et al. 2014; Evans and Karvonen 2014; McGuirk et al. 2015) in a broader governance system that is considerably more polycentric (Jordan et al. 2018). It is said that these experiments are mainly about achieving practical results, but that they nevertheless also “generate moments in which [past] logics are laid bare for contestation and thus, constitute opportunities for the construction of more progressive outcomes” (Bulkeley et al. 2014: 1484). Indeed, some suggest that they may have even wider “catalytic” impacts (Hoffmann 2011), as it is hoped that under certain circumstances they create a bandwagon effect. We identify four topics around which a new, more cross disciplinary debate about experimentation could be organized. The first is crucial and in many ways foundational: the meaning of core concepts. At the moment, there is a marked lack of conceptual clarity in the various debates about experimentation. In fact, the term experiment is sometimes used so loosely that anything that deviates from normality—however defined—is assumed to qualify as ‘an experiment’. But, to paraphrase Wildavsky (1979), if everything is an experiment, then maybe nothing is an experiment. To avoid concept stretching, the term should be bounded, and consequences for a more collaborative, interdisciplinary forms of research should be thought through. The second topic is to do with the political dynamics surrounding experimentation. In theory, a wide array of ideas can be tested in policy experiments, but in reality this does not always occur (see Hoffmann 2011). Experiments are not necessarily born equal; they may affect target groups in different ways. Some actors may reap considerable benefits, but others may bear considerable costs (see for instance Castán Broto and Bulkeley 2013). There is a realization that experimentation is not a neutral activity, but since the overall emphasis is on (any) action outside the domain of the state (where any action in relation to governing climate change is sometimes perceived as better than international gridlock), the political dynamics of experiments are all too easily assumed away (as already observed by Hoffmann 2011: 156). Paying attention to the objectives behind experiments and/or levels of agreement on the subject of experimentation is thus necessary. The third topic is the way experiments are governed to produce policy-relevant evidence. Experiments are obviously an embodiment of a new idea, but it is worthwhile analyzing who gets to formulate the ideas, who is involved in producing the evidence on their efficacy, which kinds of information should be collected, and which rules of evidence are used. Many politically consequential matters lurk below the surface, for instance, whether one can speak of credible experimental outcomes only when independent scientists are present to evaluate the experiment or not, or whether one can enhance the legitimacy of experiments and their outcomes when their boundary rules are open and many parties can co-experiment. The fourth and final topic relates to what experiments produce by way of policy-relevant learning and ultimately policy change. Ansell and Bartenberger (2016: 70) suggest that the desire to learn is what unites all understandings of experimentation. They suggest that two types of learning dominate: epistemic learning, which is about the scientific understanding of the world, and political learning, which is about changes in the preferences, goals, and commitments of stakeholders. But in the current debates on experiments in sustainability studies at least, learning from experiments is often taken for granted (McFadgen and Huitema 2017), when in reality experimental evidence may only be one consideration for decision makers. Understanding such effects would probably require a better understanding of the way in which experiments are (strategically) used in the diffusion and evaluation of policy inventions (Jordan and Huitema 2014), although the policy entrepreneurship literature does contain some pointers to the role of “success stories” (see, e.g., Huitema and Meijerink 2009). Our exploration of these four topics starts in “Experimentation in the social sciences, with a special consideration of the policy sciences”, where we explore the concept of experimentation in the social sciences in general and the policy sciences in particular. We show that it is still a niche topic in the policy sciences, but one that nevertheless has considerable lineage. We confirm that several policy-relevant interpretations exist, ranging from those that are quite exclusive (essentially a research method) to those that are much inclusive, touching on much broader issues of governance. We think that the policy sciences have a great deal to add to and take from debating this topic. Then, we run through the other three topics—political dynamics, governance and effects—and subject them to similar scrutiny, our aim was to identify the main zones of agreement and disagreement and related to that the scope for bringing in the policy sciences. In “Experimentation: new and emerging perspectives”, we discuss what the papers contribute to our understanding of the four topics. We conclude with a number of suggestions on how to develop a new, more coherent and hopefully more cumulative program of work which draws more fully on policy science insights, and which advances our collective understanding of experimentation in social systems. Experimentation in the social sciences, with a special consideration of the policy sciences Core concepts The social sciences have a long tradition of reflecting on experimentation, much of it going back to early 20th century thinking on pragmatism. Ansell and Bartenberger (2016: 65) suggest that pragmatist thought considers means and ends to be interrelated. A key concept in pragmatism is “experimentalism”, which is the: process of iterative adaption to new circumstances and experiences that entails a certain idea of progress and improvement but no teleological endpoint. This perspective leads to an appreciation for historicity and to a conception of growth as a continuous reconstruction of experience. They subsequently discuss how both Charles Peirce and John Dewey did much to elaborate on the notion of experimentation, albeit from different angles. Residues of their thinking persist in current debates. Peirce elaborated on experimentation as a method for scientific research and was one of the first to discuss the role of randomization in experiments (ibid.: 65). This approach includes active interventions or treatments, randomization and statistical analysis aiming at producing valid evidence about cause and effect, moving closer to the Baconian ideal of experimentation (Weiland et al. 2017). By contrast, Dewey sought to make experimentation a central phenomenon in democracy and ethics, thus emphasizing the need for probing, and trial and error in solving private and public problems. Thus for him, experimentation is seen as an approach to governance; in fact, the very essence of experimentation is to try out new approaches in practice. Ansell and Bartenberger (ibid.: 66–67) suggest that two variants of this perspective exist. The first they call “Darwinian experimentalism”, which focuses on systems or ecologies of innovation and emphasizes high levels of diversity so that many diverging approaches are tried out. The second they refer to as “generative experimentation”, which is essentially about trying out one specific innovation and constantly improving upon it on the basis of experience. Although he obviously affected quite a few other disciplines, Donald T. Campbell is probably the most well-known exponent of experimentation in the policy sciences (see Campbell 1997; Dunn 1997). He considered experiments to be the gold standard for scientific research and saw randomization as the defining feature of experimentation. However, Campbell also developed a broader vision of how experimentation could contribute to better governance. Campbell formulated the Utopian ideal (in his words) of an experimenting society. He surmised that it would be characterized by a preference for decentralization and diversity, an inclination towards action rather than inaction, a premium on honest assessment based on transparent data produced in an accountable manner, and a willingness to change theories and values in the face of disconfirming evidence. Subsequently, much of his work was devoted to the methods through which experiments could help advance learning, which for him had to be contrasted with non-reflective and overly ideological approaches to governing. Campbell’s influence can still be felt today. His thinking still influences those who wish to use experiments as a research method (see for instance McDermott 2002). Howe (2004: 42) offers a good summary of relevant discussions amongst them, which focus for instance on the question whether experimentation should be seen as a standalone research method or part of an ensemble of methods, whether to accept deviations from a strict experimental designs or not, and whether to allow for qualitative (instead of quantitative) data collection. Campbell’s work has also informed more recent work, for instance on forms of experimentalist governance (see for instance Dorf and Sabel 1998 & Sabel and Zeitlin 2008). Despite Campbell’s influence, it is fair to say that experimentation has not been the center of attention in the policy sciences. Very few textbooks even index the concept (Anderson 2006; Parsons 1995). The recent edited volume by James et al. (2017) is probably one of the first seek to renew interest in experimentation, in line with what Howe (2004) dubbed mixed-methods experimentalism (seeing experiments as one research method, part of a suite of methods). They focus on experiments as a research method and apply relatively strict definitions when it comes to what counts as an experiment (randomization is considered key), but experimentation is also placed alongside a range of other research methods. As part of their volume, Li and Van Ryzin (ibid.) reviewed the number of experimental studies in “public management journals”1 and found that the number of articles describing experimental studies hovered at only 2–4 per annum in the early 1990s, climbing quite slowly to around to reach a peak at 18 per annum in 2015 (see Li and Van Ryzin 2017). Furthermore, it is remarkable how studies in the policy sciences tradition that do refer to experimentation have mostly focused on a limited number of policy fields, notably social policy and education (see for instance Greenberg et al. 2003, who studied 143 experiments in social policy). In almost all such studies, experimentation is approached as a research method and quite a strict (neoclassical) definition of what constitutes an experiment is applied. It is fair to say that this is the dominant conception in the policy sciences. Key political dynamics2 Policy scientists have pointed out that experimentation—also when applied as a research method—is not a neutral activity; far from it. This does not only concern the situation surrounding experiments; politics are also abundant within them. This is because the choice of measures to study and the interpretation and presentation of the results often depends on the values and influence of the persons and institutions involved (see, e.g., Guba and Lincoln 1989). Indeed, the work of Brodkin and Kaufman (2000), on experiments in social policy, shows how experiments are infused with political ideas and they suggest that in practice experiments often confirm existing ideas rather than challenge them. Sanderson (2002: 13–17) studied the British experience with experiments under the New Labour governments in the UK, which were keen to emphasize evidence-based policy making—a context that is in theory was relatively conducive to experimentation. Experiments were meant to provide an evidence basis for policy, but Sanderson found that the ruling party was mostly interested in showcasing their preferred approaches by means of pilots, rather than openly testing lots of ideas. As a correlate of that, experimental settings were often not very representative for ordinary policy making contexts, as extra resources were provided to increase the chances of a successful experiment. To that, Brodkin and Kaufman (2000) add that the ever changing political context provides challenges and opportunities for those advocating certain new ideas. The ideas guiding particular experiments may or may not stay in vogue for long. This means that by the time experiments start to produce evidence, the political landscape around them may have changed. Thus, experiments may serve as time capsules from a previous era. Interpreting experiments—irrespective of their ideological pedigree—is also an inescapably political process, with various opponents using the experiment as an instrument of advocacy. Governing experimentation Because the dominant conception of experiments in the policy sciences is that they are mainly a research method, proponents of experimentation have paid limited attention to issues of governance, viewing them mostly in quite narrow, methodological terms (e.g., how necessary is a control group, how important is randomization, how relevant is the category of quasi-experiments?) (see for instance Howe 2004). But in the period between the Second World War and the 1970s, there was a fair bit of development in the thinking about the right scale of experiments. This was an era in which the role of government in many societies expanded rapidly and the rational planning model was in vogue (Huitema et al. 2009). At the heart of this thinking was rationalistic policy analysis: decisions should be based on a scientific analysis of the various issues at stake. It was assumed that government led planning should guide societal development and that utilitarian logic (as expressed in cost–benefit analysis) should guide decision making. In the post-war period, the assumption was that governments could and should intervene, where necessary with large-scale experiments in societal systems (see, Van Gunsteren 1976). But in the current era of smaller and leaner government, a pronounced aversion to large-scale experimentation has taken hold (see Bobrow and Dryzek 1987: 142). Instead, notions such as “piecemeal engineering” (Popper 1985 [1944]: 309) and “trial and error learning” (Collingridge 1992) came to be seen as more appropriate guides for policy making. The notion of evidence-based decision making was another symptom of this trend; the onus nowadays is on the government to demonstrate that an intervention is warranted. When such evidence is lacking, the starting assumption is that the government should refrain from action. In other words, experiments become the means to demonstrate the need for policy change, as opposed to the means for effecting change. Finally, Greenberg et al. (2003: 46) add that the notion of experimentation works best for a situation in which there is a single decision maker with clear goals, a limited set of well-known policy alternatives, and sufficient time to await the outcomes of research. Because we live in times of doubt about the power of big ideas (and solutions) and a world arguably characterized by more “institutional voids” and less ‘big government’ (Hajer 2003), it is not surprising that there has been a turn back to experimentation, only smaller, more exploratory and much more modest in its aspirations. The impacts: learning and change In the 1960s, Harold Lasswell suggested that experiments serve three purposes: improve policy making practices, generate scientific knowledge, and build capacity to implement novel ways of doing policy. For Parsons (1995: 552), all three purposes presume a certain level of learning and a subsequent translation into policy practices. Bobrow and Dryzek (1987) suggested that learning from experimentation needs to be seen in light of a Popperian philosophy of science in which all knowledge is seen as temporary and open to falsification. In this vein, policies are to be regarded as tentative hypotheses—they should be based on the best available theory and should be critically assessed by building up from small scale experiments (hence the aforementioned piecemeal social engineering). The discussion about the outcomes of such tests should be open to anyone who wanted to participate in the debate so that a free interplay of proposals and criticisms can ensue (something that Donald Campbell referred to as a “dialectic of experimental arguments”) (see Bobrow and Dryzek 1987: 140). Knowledge about the outcomes of experiments should certainly not be monopolized by technocrats. Bobrow and Dryzek (ibid.) suggest, however, that these ideals have since lost their appeal, because organizers of experiments are generally less interested in talking to the general public than “in establishing the client–analyst relationships that yield the resources that field experiments require” (ibid.: 140). This is quite a sweeping statement to make, but if correct, the ideal of democratic experimentalism (as opposed to small scale, technocratic experimentalism) will probably remain forever unrealized. There are also several skeptics in the policy sciences when it comes to the learning potential of experiments, understood as a research method. For example, Frank Fischer (1995) has suggested that experiments potentially stifle intellectual progress. This is because, unlike the pragmatists, Fischer beliefs they focus exclusively on means and not goals. Moreover, experimentation can test only one idea at the time, and in any case always absorbs significant time and resources. This echoes Bobrow and Dryzek (1987: 148) who claimed that the class of problems for which experimentation is suitable is probably so small that it is bordering on the non-existent. They say experimentation is appropriate when there “is a well-structured, reasonably static, and highly decomposable problem at hand, with consensus on the criteria to be applied to it”. One does not go as far as labeling climate change a wicked problem to acknowledge that it fails to pass this test. The policy sciences offer few insights into the way experimental results translate into policy change, although a broader literature of course exists on how policy evaluation influences policy. This literature was surveyed by Mark and Henry (2004), but they made no mention of experiments as a factor explaining policy influence. There is some mention made of the use of experiments by policy entrepreneurs, however. Roberts (1992) claims entrepreneurs use experiments to test the survivability of their innovations. Conversely, John (2017) has suggested that anyone who instigates an experiment qualifies as a policy entrepreneur. Experimentation: new and emerging perspectives The roots of the social science debate on experimentation can be traced back to the pragmatists, some of whom advocated experimentation as a research method, others as an approach to governing. In the policy sciences, the debate about experimentation is largely preoccupied with experimentation as a research method, and quite a few authors have suggested there are many limitations and potential complications. This stands in sharp contrast with the high expectations in the debate on climate governance. Do these challenges simply not exist in these two realms? If not, should we as policy scientists amend our expectations about policy experiments? Or perhaps should those writing about experiments in climate governance heed the many warnings issued policy scientists? In this section, we reflect on these questions by drawing on the main findings of the papers in the rest of this issue. We arrange them under the four topics identified in the first section. So first we focus on conceptual discussions and advances, then on insights regarding the political dynamics surrounding experiments. Then, we move to insights in the way experiments are governed and finally we focus on the impacts of policy experiments. Interestingly, none of the contributions to this special issue is concerned with understanding experiments as a research method; all focus on experimentation as an approach to governance. As we will see, this has implications for the analyses and conclusions that follow. Conceptual perspectives In their contribution on the role of experimentation in the way Dutch water managers handle climate change issue, McFadgen and Huitema (2018: X) define a policy experiment as “a temporary, controlled field-trial of a policy-relevant innovation that produces evidence for subsequent policy decisions”. This definition highlights the deductive nature of experimentation, in the sense that the underlying assumption is that experiments should by definition have an underlying (action) theory, which can be proven correct or incorrect. This criterion eliminated most of the experiments on the long list of projects they assembled from self-reporting exercises conducted by Dutch water authorities. In fact, of the 180 projects that policy makers regarded as experiments, only 14 contained an intervention theory. One possible implication of this finding is that the word experiment is used differently in practice, i.e., denoting an intention to do something novel, which follows an inductive logic. In their study of the way experiments can contribute to radical societal transformations, Bernstein and Hoffmann (2018) also embrace this more inductive logic. They conclude that various conceptualizations of experiments exist, but that all “share the notion that something new is being tried out—there is a conscious intervention that differs from the status quo” (Ibid. X). They cite Abbott (2017) who suggests that experiments can be formal or informal depending on the level of conscious experimentation and control over the process. Formal experiments denote analogs of controlled laboratory experiments and informal experiments refer to “a more metaphorical understanding that views climate governance experiments as novel attempts at governing climate by non-traditional global actors […]” (Bernstein and Hoffmann 2018: X). They place themselves at the informal end of the spectrum, by focusing on the activities of subnational actors (states, provinces, cities, but also civil society and company initiatives) in the context of global discussions about climate change. They suggest that when the global discussion gridlocked, subnational actors took over. Bernstein and Hoffmann (2018) present a potentially very interesting conceptual innovation when they try to develop a simple model of the way experiments alter reality. The dependent variable in their model is the effect that experiments have on lock-ins in the way that economies operate, principally those increasing their dependence on fossil fuels. Sharing an insistence on the political character of experiments they are particularly interested in: (1) the politics that experiments produce; and (2) the subsequent pathways for change that they create, hopefully in the direction of “decarbonization”. Regarding topic (1), they propose that experiments affect what is considered normal (“normalization” which is about the framing and reframing of what is appropriate action), how capacities are directed (in a material, institutional and cognitive sense), and which coalitions develop (compare some of the forms of learning, mentioned by McFadgen and Huitema (2017)). They explicitly indicate that each act to affect framing, capacities, or coalitions is bound to result in counter action. Regarding Topic 2, they suggest that, depending on the nature of the politics that emerge, experiments can reinforce existing lock-ins, help improve such lock-ins, or they can lead to a breaking up of the lock-in and help decarbonize the economy. One tantalizing theoretical advantage of thinking about lock-ins is that an experimental intervention in one element of an interlocking system may create disturbance (and thereby potentially effects) in other parts. To describe these effects, Bernstein and Hoffmann (2018) introduce the terms scaling and entrenchment. Scaling has to do with the way in which a successful experiment leads to more experiments, larger-scale experiments, or experiments on other jurisdictions. Entrenchment relates to the stickiness of innovations introduced by experiments—some new policies may immediately get locked-in (as if they had always been there), some policies have rising benefits over time, and new populations may join the new policy. Voß and Simons (2018), in their study of the way emissions trading become a credible and legitimate policy option, make an important conceptual claim about experiments. They go beyond Lasswell’s notion that experiments affect reality in part by capacity building. They explore the reality shaping nature of experiments; if and when an intervention is deemed successful, the manipulation in question will form the basis of further attempts to model and reshape reality. They suggest experiments can perform two important roles, which they refer to as scientific reality making and political reality making. Both forms involve similar acts, such as demonstrating a condition, justifying claims, and establishing order. But there are strong differences in what is at stake in the lab and in the field, i.e., epistemic versus political authority. The type of evidence considered is different too, as are the obligations considered. The political dynamics of experimentation Voß and Simons (2018) side with policy scientists when they contend that experiments are intrinsically political in nature. This is because neutral observation is impossible and because the starting premises of an experiment are often highly consequential. They conceptualize experiments as entities operating at the interface between science and policy. They contend that these two fields are more interwoven than is usually acknowledged. One of their most significant contributions is to show how experiments play a role, which is not so much by means of a one-off attempt to produce evidence, but rather in a longer and convoluted process which may actually involve multiple experiments (but also other ways of gathering evidence). By dissecting the long and arduous path that the instrument of emissions trading had to accomplish, Voß and Simons show how it involved no less than five experiments. Lab experiments contributed to the epistemic authority of the idea and field experiments contributed to the formation of political support. They also underline the importance of time: experimentation with emissions trading evolved over many decades, thus aligning with the idea that experiments may serve an indirect (or enlightenment) function over the very long term (Weiss 1977). The contribution by Rocle and Salles (2017) also demonstrates the political sensitivities surrounding experiments. In their analysis of what was essentially a thought experiment with planned retreat from the eroding coastline in the Aquitaine region of Southwest France, they show how much the initial framing of the experiments mattered. The French national government was considering planned retreat, but encountered much local resistance to the idea. Volunteer communities were asked to come forward and receive money for a participatory process that would actively consider retreat through a scenario based approach combined with back casting. Leading politicians in one of the few municipalities to come forward and join the experiment emphasized that the choice to retreat should be a local one. It would not be forced upon them—hence the request for “pioneers, not Guinea pigs” (ibid.: X). The central government in turn was keen to emphasize the fact that the experiment was a shared responsibility, with the national government working with local governments to experiment with new ideas about coastal management. The governance of experiments McFadgen and Huitema‘s contribution focuses on the way experiments can be governed. They suggest that the institutional design choices that initiator of experiments must take go beyond the choice for an intervention, randomization and presence of a control group. Based on Ostrom’s (2005) Institutional Analysis and Development framework, they suggest that initiators of experiments need to make several choices concerning the type of information that is regarded or ignored, the authority to make decisions on the experiment, the costs and benefits associated with the experiment, etc. They present a set of ideal type experiments, which can serve as a tool for the interpretation of real life experiments. Leaning on Pielke (2007), they suggest that design of experiments can rely mainly on technocracy, on advocacy, or on brokerage at the boundary between science and politics (the key point being that experiments are not intrinsically technocratic as is often assumed). Their typology is able to detect subtle differences between 14 experiments in Dutch climate adaptation, which suggests that it may have analytical value elsewhere too. What changes? Experiments, learning and change Bernstein and Hoffmann (2018), in their quest to understand the disruptive force of experiments, provide a test run of their model on a few real world examples. To that end, they apply it to three case studies, one that reinforced existing lock-ins (Colorado’s New Energy Economy initiative), one that unlocked carbon lock-ins (the UK government-sponsored Carbon Trust), and one that has the potential to decarbonize (Copenhagen’s climate policy). They find that in Copenhagen it was normalization that contributed to the scaling and entrenchment of the notion of carbon neutrality. This occurred by consistently framing climate action as contributing to the improvement of life in the city—through the slogan the Good Life = Sustainable Life and a Green City = Economic Growth. They warn, however, that the “potential or trajectory [of experiments] generally cannot be calculated a priori” (Bernstein and Hoffmann 2018: X). But they do suggest that their framework sheds light on the political dimension, as it “provides a way to identify and track the political forces and mechanisms through which experiments impact targets of intervention and make (or fail to make) broader connections” (Bernstein and Hoffmann 2018: X). Rocle and Salles (2018) confirm some of the bold predictions made by Voß and Simons (2018) about the reality creating effect of experiments. They show that simply discussing planned retreat made the notion more acceptable and at least changed the local political discourse. They also show how policy entrepreneurs—in their case, a collaboration of local authorities—played an active role in setting up the experiment, in gaining local acceptance by framing it in a positive light, by navigating political dynamics emanating from local elections and in connecting across jurisdictional levels. The fact that the committee monitoring the experiment included two national parliamentarians was not a coincidence; in fact it actively facilitated the transfer of lessons—namely adapting national legislation to make planned retreat a viable option. Because this was always the aim of the national government, Rocle and Salles hesitate to speak of social learning beyond the very local level. In effect they side with Castán Broto and Bulkeley (2013) who have suggested that experiments are one way through which visions of the future are rendered practical and hence governable (compare Voß and Simons 2018). It the typology of McFadgen and Huitema (2017, 2018), the French coastal experiment was very much an advocacy experiment, with relatively high degrees of openness in terms of which kind of actors could participate. But there was less openness in terms of the expected outcomes: the experiment was much more a means to gauge and ultimately govern local responses to rising sea levels. McFadgen and Huitema (2018) are interested in the conceptual utilization of experimental results; that is, how the experiments influence the mindsets of policy makers (and especially elected politicians). Following Weiss (1977) they suggest that experiments are likely to play a role in the gradual sedimentation of ideas in policy making, yet they also suggest that measuring such effects over years or even decades is very difficult. Instead they propose three proxy indicators that gauge the short-term reaction of policy makers to experiments by assessing the degree to which policy makers considered the results salient, credible and legitimate (see Cash et al. 2003). In addition, McFadgen and Huitema hypothesize that the way an experiment scores on the three criteria vary under the influence of the institutional design. On the basis of data from 164 online surveys targeting policy makers who know about experiments (many of them did not), they tested several explicit hypotheses, for instance that “technocratic experiments” score higher on credibility than the other two types (“advocacy” and “boundary” experiments, respectively). Statistical analysis revealed that institutional design had a significant effect, but surprisingly some intuitively plausible hypotheses were rejected. For example, technocratic experiments, despite their emphasis on science and scientific impartiality, did not score higher for credibility than the other two types. In addition, advocacy experiments scored higher for legitimacy; this was surprising because of the one-sided and somewhat closed nature of their institutional setting. They assume this is to do with the relatively low level of conflict over policy goals in the Dutch water management community, and speculate the scores might have been lower in more conflictual settings. Conclusions and new directions The expectations surrounding the experimentalist turn are sky high, but we have suggested that four topics deserve much more attention. To obtain more insight, we took proceeded via two steps: we gave a short overview of the discussion about experimentation in different literatures including the policy sciences and then we discussed the various novel contributions contained in this special issue. In this final section, we draw conclusions on the possibilities for mutual learning across the disciplines and identify directions for further research. Towards common concepts? In terms of core concepts (our first topic), we have shown how experimentation has long been debated across the social sciences. In pragmatist thought, two different ways of looking at experiments can be discerned: experiments as a research method and experiments as an approach to governing. In the discussion on experimentation in the policy sciences, the emphasis has overwhelmingly been on experiments as a research method (i.e., specifically one that requires randomization, control groups, etc.). By contrast, most authors writing about sustainability and in particular climate governance, see experimentation as an approach to governance. On reflection, some of the confusion that has arisen is probably down to the fact that scholars are talking past one another, with some prominent policy scientists claiming that the term experiment has been “somewhat inaccurately” defined in the climate governance literature (see Dryzek 2017: 789). It is probably not that helpful to count every form of policy making and/or governance as ‘an experiment’. In this debate, McFadgen and Huitema (2018) helpfully identify a middle ground which a shared understanding could be achieved at the intersection between fields. They suggest that at minimum two basic conditions should be satisfied before something is labeled as an experiment: there should be an intervention theory with explicit assumptions (or hypotheses) which are tested and there should be some novelty. Hence, they write: “the act of experimentation should be explicit: without appraisal of the intervention’s effects, there is only demonstration of a new initiative, and without innovation, only established ideas are being evaluated” (McFadgen and Huitema 2018: X). Admittedly, their suggestion rules out many aspects of experimentation that are quite common in the climate governance literature (e.g., the assumption that an experiment is any initiative that occurs outside the international regime for instance). But it is inclusive enough to include experiments as a research method and experiments as a means of governance. Applying such a definition could have important implications for the policy sciences. These go beyond the obvious observation that a shared understanding would allow us to study a number of specific cases and thus more rapidly enhance our empirical understanding of experimentation. Beyond the obvious, there may also be other consequences. Regarding the very practical ones, Voß and Simons (2018) demonstrate that the inclusion of both types can have added value since practitioners would be able to apply both types in one decision process—something they would have missed if they had applied a very strict definition. On a more profound level, taking a broader definition of experiments could create a means to connect to the pragmatist philosophy of Dewey and others. What are the key political dynamics? This leads logically to our next conclusion, which relates to the political dynamics surrounding experiments (our second topic). We have argued that in the debate on climate governance experiments political issues have largely been downplayed because experiments are seen as a way to evade the politics bedevilling inter-state diplomacy. Policy scientists have repeatedly sought to play up this aspect. For instance, many discussions of Campbell’s ideas have revolved around the compatibility between taking risks in an experimenting society and basic democratic values (see Dunn 1997). Would the role of ideology not be diminished in an experimenting society? Do scientists crowd out elected politicians in the decision making process? How does society avoid the selective use of scientific evidence? How will ordinary citizens be involved in decision making? Note here that speaking of the politics surrounding experiments (as we did ourselves at the outset of this article) is constraining, because such language may imply that the experiment itself is free from politics, whereas for many policy scientists politics are an intrinsic part of experiments. Unlike many publications on experimentation in climate governance so far, the contributions to this special issue directly address the political nature of experiments. The notion that experiments create new realities and affect discourses comes out very strongly in all the contributions. This special issue also advances our understanding of the interaction between science and policy. In many literatures, this is largely seen as a cognitive process of enlightenment—of unsettling and breaking up existing power arrangements. The model that Bernstein and Hoffmann (2018) offer is potentially innovative and could be considered for wider use. They suggest that experiments can change expectations about what is normal, build capacities, and affect coalition formation. They also suggest that experiments should be analyzed over time, asking whether they have actually broken up existing situations, have actually unwittingly perfected them, or have left them as they originally were. The governance of experiments: understanding the stakes We propose that the current stringent way of studying experiments in the policy sciences (i.e., seeing them as a research method) has limited the ability of policy sciences to offer reflections on the governance of experiments (our third topic). Indeed, when experiments are viewed purely as a research method, the whole issue of governance becomes narrowly framed: e.g., the hypotheses to be tested; the characterization of the control situation (or group); the comparison of treatment vs non-treatment options, etc. However, under a broader understanding, the way the governance of experiments is set up, does become an issue as suggested by McFadgen and Huitema (2018). We think that their idea that experiments could be designed in various ways (e.g., in a technocratic way, but also as a boundary object, or as a tool for advocacy) potentially has important implications. At a conceptual level, it means that experiments need no longer be exclusively associated with technocracy. This is significant because possible tensions between the proper functioning of democracy and experimentation surface in almost every publication on experimentalism or experimentalist governance. Such tensions will not completely disappear if experiments are understood as boundary objects or advocacy tools. In fact new tensions could well appear—for instance when the capacity to experiment, or access to experimental results, is distributed unequally in societies. However, the impression that experimentalist governance essentially means rule by experts would be taken away. The fact that experiments can also be undertaken in a non-technocratic way would actually embolden those who argue that experimentalist governance should operate as a (democratic form of) “directly deliberate polyarchy” (Sabel and Zeitlin 2008: 276). At the empirical level, this insight offers the potential to acquire a more detailed picture of what it is that experimenters do in practice—the stock in trade of many policy scientists. In fact, accepting the idea that an experiment can sometimes be a tool of advocacy or a boundary object would allow us to bring the politics back into experimentation. It would also help us form us a better understanding of the potential impacts. Here, we draw on the insights proffered by Voß and Simons (2018), who emphasize the performative aspects of experiments and the craft that goes along with this. As noted, they suggest that sometimes experiments are intended for political reality making, sometimes for scientific reality making. What actually changes? The impacts of experiments This brings us to the matter of impacts that experiments have, whether through learning or policy change (our fourth topic). Here too, the idea that experiments can be governed in multiple ways has implications for the way we study them, because it draws attention to their internal dynamics. If not all experiments have (by definition) to be technocratic, then it becomes important to study the possibilities for learning from experiments that go beyond simple scientific conclusion drawing. Indeed, if experiments are treated as boundary objects (see McFadgen and Huitema 2018), then it encourages analysts to study their effects on the norms that their organizers bring to the problem—something that has so far largely escaped the attention of policy scientists. The question of what happens to the findings of experiments in the broader policy setting has obviously not escaped attention. In fact it is well known that politicians can ignore the results that they cherry pick from the conclusions, etc. Interestingly, insights into how experiments affect learning and policy change have yet to be included in most of the leading models of the policy process. This feels like an omission after that more policy scientists should start to address. Several papers in this special issue also underline the importance of the time dimension. McFadgen and Huitema (2018) propose that the three criteria of salience, credibility and legitimacy may serve as short-term indicators for the impact that experiments may eventually have in policy circles. They do so on the basis of an assumption that the outcomes of experiments with higher scores for these criteria have a higher chance of being taken on-board by policy makers. However, they do not test this assumption, but rather flag it as a matter deserving further research. Voß and Simons (2018) also take a very long perspective on emissions trading. They show the added value of paying attention to both experiments as research method (what they call lab experiments) and experiments as an approach to governance (which they refer to as field experiments). Applying the thinking of Bernstein and Hoffmann, one can easily see how the experiments with emissions trading indeed led to capacity building, to normalization, to coalition building, and eventually to anchoring of this instrument. In summary, conceptual precision is needed, especially in the realm of what counts as an experiment. The political dynamics surrounding and within experiments should also receive more attention because experiments are not neutral endeavors and their use potentially invokes difficult questions about the proper relation between science and policy. In addition, experiments can be governed in multiple ways: many important decisions have to be made about the types of information that count, which participants can become involved; and the way evidence is established, etc. The consequences of such “design questions” need to be understood if, as seems to be the case, more governors wish to experiment. Finally, it remains unclear which factors determine whether certain experiments lead to learning and policy change. The contributions to this special issue offer important suggestions for taking forward the debate on these topics. Whether or not we need an experimentalist turn in the policy sciences is very much an open question. The prospects seem tantalizing as insights on the way experiments function is potentially very relevant (for instance) for an update of our theories on the policy process, on policy learning, for insights on the interactions between formal and more informal forms of policy making, and for theories on the functioning of the science-policy interface. But our argument is that such a turn will probably not add up to as much if we keep treating experiments as a research method, as opposed to a broader approach to governing.

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          A survey of urban climate change experiments in 100 cities

          1 Introduction Addressing climate change requires an “unprecedented level of cooperation, not only between countries, but also between different levels of Governments and the private sector” (De Boer, 2009, p. 1). The city is an increasingly important site for climate response. While there remains much dispute about the exact contribution that cities make to GHG emissions (Dodman, 2009), and about who and what is most vulnerable to the effects of climate change (De Sherbinin et al., 2007), urban centres are now regarded as a vital part of the global response to climate change (UN-Habitat, 2011; World-Bank, 2010). While recognition of urban responses to climate change at the international policy level has been relatively recent, a burgeoning research community has studied the relationships between cities and climate change. Since the mid-1990s, research has focused on municipal strategies, policies and measures, and the challenges that municipal authorities face in terms of policy implementation and effectiveness. This body of work, mainly developed with case-study methods, has yielded numerous insights including: the multiple modes of governing through which municipalities seek to govern climate change; the importance of institutional capacity, including resources, knowledge and organisational structures; the critical role of individuals, political champions and policy entrepreneurs; and how multi-level governance structures opportunities and limits for municipal action (see Betsill and Bulkeley, 2007; Bulkeley, 2010; Schreurs, 2008 for recent reviews). However, this work also has limitations to understand how, why and with what implications urban responses to climate change are taking place. The first issue concerns the type of studies and cities studied. Research has mainly focused on generating rich data about either individual case studies or small sets of cities. Such approaches, combined with a focus on early city pioneers and members of specific transnational municipal networks, have created a geographical bias towards cities in more economically developed countries, predominantly the US, Canada, Europe and Australia (e.g. Allman et al., 2004; Bulkeley and Betsill, 2003; Bulkeley and Kern, 2006; Davies, 2005; Kousky and Schneider, 2003; Lindseth, 2004), although there are now an increasing number of cases in Asia and Latin America (Bai, 2007; Dhakal, 2006; Holgate, 2007; Ranger et al., 2011; Romero Lankao, 2007). Moreover, research has primarily focused on mitigation, rather than adaptation (see recent exceptions Hallegatte and Corfee-Morlot, 2011; Hunt and Watkiss, 2011; Romero-Lankao and Dodman, 2011; Romero Lankao, 2007; Satterthwaite et al., 2009). Fewer studies have sought to undertake systematic comparison between cases, or have employed quantitative methodologies. Where these exist, analysis has focused on whether particular urban characteristics explain the emergence of particular kinds of policy response within cities in more developed economies (e.g. Krause, 2011; Pitt and Randolph, 2009; Zahran et al., 2008). Overall, our understanding of urban responses to climate change is largely derived from case-study work, focused on cities in more developed economies and mitigation responses. A second limitation has been the predominant concern with understanding the role of local authorities in shaping urban responses. The literature on global environmental governance now makes clear that non-state actors (corporations, NGOs, international foundations, community groups) are increasingly involved in responding to climate change (Bulkeley and Newell, 2010). Moreover, the boundaries between the public and private actors are increasingly blurred, as private organisations take on roles traditionally regarded as the province of the state, while public authorities are engaged in forms of activity often regarded as a private domain, such as intervening in carbon markets or promoting the energy economy. These coupled issues – the growing roles of private actors in responding to climate change and the blurring of the public/private boundary – mean that it is no longer sufficient to regard urban responses to climate change as a matter for municipalities alone. A third limitation to our current understanding of urban responses to climate change is the analytical focus on the processes of agenda setting and policy-making, the development of plans and strategies and the selection of specific measures in different contexts. Less attention has been paid to responses to climate change taking place outside of formalised policy channels, constraining our knowledge of these interventions. A fuller understanding of urban responses to climate change will require new forms of case-study and comparative research that consider a more geographically diverse range of cities together with the range of urban actors involved in such responses, and capture initiatives and interventions falling outside of formal processes of planning and policy. In this paper, we discuss the results from one methodological approach – a survey of the climate change initiatives or experiments taking place in 100 cities – designed to further this agenda. Despite the acknowledgement that there remains a ‘stubborn gap’ between the rhetoric and reality of local climate policy and its implementation (Betsill and Bulkeley, 2007), urban landscapes are littered with examples of actions being taken under the banner of climate change. Our approach examines these initiatives, which we term ‘climate change experiments’. The concept ‘climate change experiment’ (Bulkeley and Castán Broto, 2012) is based on insights from literatures on governance experiments (Hoffman, 2011), the role of niches and grassroots innovations in socio-technical regimes (Geels et al., 2011), and the notion of ‘urban laboratories’ (Evans, 2011) that point to the ways in which experimentation forms part of the governance and contestation of socio-technical systems. We define urban climate change experiments according to three criteria which build upon these perspectives: first, an intervention is experimental when it is purposive and strategic but explicitly seeks to capture new forms of learning or experience; second, an intervention is a climate change experiment where the purpose is to reduce emissions of greenhouse gases (mitigation) and/or vulnerabilities to climate change impacts (adaptation); third, a climate change experiment is urban when it is delivered by or in the name of an existing or imagined urban community. Climate change experiments are presented here as interventions to try out new ideas and methods in the context of future uncertainties. They serve to understand how interventions work in practice, in new contexts where they are thought of as innovative. The objective of the research was to understand the extent and diversity of climate change experimentation both in the global north and the global south adopting a comparative approach to capture the extent and diversity of urban climate change experiments. The analysis considered: when and where urban climate change experiments emerge; what types of urban climate change experiments we find and what are their characteristics; and who leads these experiments and what mechanisms make them possible. Results suggest that experimentation is a feature of urban responses to climate change across different world regions and multiple sectors but it does not appear to be related to particular kinds of urban economic and social condition. Some core features of experimentation are visible. Experimentation, like other forms of urban climate change response, tends to focus on energy. Both social and technical forms of experimentation are emerging, though the latter is most common and dominates the urban infrastructure systems within which experimentation is most common. Municipalities have a critical role in experimentation, though analysis also reveals the wide variety of forms of partnership through which experimentation is taking place and that are arguably opening up new political spaces for governing climate change in the city. 2 Methodology The construction of the database involved surveying 100 cities using secondary materials, and the systematic storage of information to facilitate the analysis. The construction of the database involved a selection of cities, database design, data collection and analysis. 2.1 Selection of cities In academic discourse, ‘global city’ refers to cities that are important nodes within the global economic system (Sassen, 1991), but colloquially it also refers to cities that have significance because of their size and concentration of population, or political significance. The sample in this research was designed to represent a sample of a heterogeneous group of cities in all parts of the world with clear significance in terms of contributions to greenhouse gases and concentration of vulnerabilities to climate change, using six indicators: Total Population and Density indicate the extent to which exposure to climate vulnerabilities may be concentrated in the urban arena and the potential total GHG emissions from any one city or urban area. Indicators of economic activity were used as a proxy to reflect the overall contribution to GHG emissions, including gross domestic product and a ‘world city’ indicator to characterise cities that have an established role in international economic networks providing global service centres and graded for accountancy, advertising, banking/finance and law (Beaverstock et al., 1999). Two other indicators were introduced, one to select all cities which actively participate in the C40 Climate Leadership Group, and another to highlight cities with specific vulnerabilities to climate change, including, port cities, cities vulnerable to sea level rise (Nicholls et al., 2008; UN-HABITAT, 2008) and cities vulnerable to glacier changes (Stern et al., 2006). Data was obtained from the City Mayors website (City Mayors, 2012). Six hundred and fifty cities were ranked according to the indicators, and all ranks were added to establish a compound measure for each city. The final sample included the top one hundred cities, which scored relatively high in all indicators, but with clear variation among the cities for all indicators (Tables 1 and 2). 2.2 Database design Each record in the database corresponds to a discrete urban climate change experiment. Following previous comparative research about municipal responses to climate change in eight cities (Bulkeley et al., 2009; World-Bank, 2010) the database was divided in six sheets, one for each of five key sectors of climate change mitigation (urban infrastructure, built environment, transport, carbon sequestration and urban form) and one for adaptation experiments (see Table 3). Analytical categories recorded in each record cover: (1) where and when urban climate change experiments occur; (2) what are these experiments how are they developed and (3) who leads initiatives and how they are governed (Table 4). Indicators of where and when urban climate change experimentation occurs provide a sense of the context in which these initiatives occur. Each initiative was dated in relation to the approval of the Kyoto protocol in 1997 and its ratification in 2005. Recording specific types of innovation was a means to check that the initiative met the definition of experiment and provided a ground for comparison, as experiments reflected attempts to develop technological innovations (designs, technologies, materials), social innovations (policy tools, financial mechanisms, changes to cultural norms) or both. The form of innovation was a better indicator than the factors which made the experiment possible, because while the form of innovation was always reported, the factors leading to the experiment were not always explicit or were only found in secondary sources. For each sector the database included specific aspects of the system of provision in which the experiment intervened (see Table 3) and the specific service which was met. The design follows an understanding of governance as a multi-level and multi-actor process. The database captured the experiment leading actors, but also recorded separately the partnerships that made the experiment possible. The information regarding funding mechanisms and costs was very fragmentary. Modes of governance were also recorded. A mode of governance is a set of tools and technologies deployed through particular institutional relations through which agents seek to reconfigure the specific social and technical relations with a specific governing purpose (Bulkeley and Kern, 2006), in this case, to address climate change. Municipalities can deploy four modes of governance including: (1) self-governing, intervening in the management of local authority operations to “lead by example”; (2) provision, greening infrastructure and consumer services provided by different authorities; (3) regulations, enforcing new laws, planning regulations, building codes, etc.; and (4) enabling, supporting initiatives led by other actors through information and resource provision and partnerships (Bulkeley and Kern, 2006). Given that climate change action requires coordination of mutually dependent actions beyond public institutions (Bulkeley et al., 2009; Kern and Alber, 2008), this concept was extended to non-governmental actors leading climate change experiments. 2.3 Data collection methods Information on experiments was collected through three main means: review of key literature; consultation with climate change experts; and Internet searches. Interviews with individuals at the International Institute of Environmental Development, the Building and Social Housing Foundation (including access to their large database of innovation projects in housing worldwide) and urban experts at the World Bank provided examples of experimental initiatives which are considered to be leading worldwide. Internet searches looked systematically through the websites of local, regional and national governments and private and civil society organisations, news items and reports for each city in turn. Additional data was obtained from the Clean Development Mechanism database (UNFCCC, 2012). The search looked beyond recognised examples of best-practice and recorded as many instances of experimentation as possible in an allotted amount of time. The archival system included a folder per city with a city-specific summary of the main climate change activities, a list of experiments recorded in the database and a collection of data sources backing the information provided in the database records. The data was compiled from June 2009 to June 2010, with a revision and update of data in December 2010. The predominant use of Internet data sources had some limitations because it relied in self-reported data. Self-reported data may focus on making the experiment rather than its implementation in practice and it is more likely to report successes than difficulties and failures. Moreover, many interesting experiments may not be reported on the Internet or may be inaccessible to standard search engines. Overall, there were practical limitations in terms of the time dedicated to each city (we dedicated in average 2 days per city but included additional time for cities where less information was available) and the languages covered (the database included initiatives reported in Portuguese, Spanish, English, French, Italian and German but crucially, not those in key languages such as Chinese and Russian). Thus, the database should not be regarded as comprehensive, but rather, as providing an indicative account of the emergence of climate change experimentation in these cities. 2.4 Analysis of database results To facilitate the statistical analysis, we re-coded numeric dates in reference to the approval and ratification of the Kyoto protocol; the type of innovation to register whether the experiment included technological innovation, social innovation or both; the schemes used, focusing on the interventions on energy systems and whether the experiment was directed at producers (energy generation and transmission measures) or at consumers (demand side measures); and the type of actors as public, including local government, regional government, national government, international organisation, private and civil society organisations, including non-governmental organisations (or charities) and community-based organisations. Variables for which information was incomplete or unconfirmed were excluded. We also used the city-based variables (see Table 2) and a variable registering cities’ membership to the following transnational municipal networks: • ICLEI, Local Governments for Sustainability, an association of over 1200 local governments working for sustainability which work together since 1990. • Cities for Climate Protection, an affiliate programme of ICLEI in which cities commit to concrete actions for carbon reduction. • C40 Cities Climate Leadership Group (C40), a network of cities created in 2005 by the London Mayor and the Clinton Foundation's climate change initiative. The analysis examined: (1) where and when urban climate change experiments occur; (2) what are these experiments how are they developed and (3) who leads initiatives and how they are governed. Variable comparison used either linear regression or correlation statistics in the case of categorical variables. This approach advances and complements existing studies because it develops a large-n sample, in contrast to case-study work; it works with a variety of urban contexts, north and south, unlike previous survey-based analyses focused on one national context; and it focuses on climate change experiments, rather than plans and policies. The limitations of the study are in terms of sacrificing breadth for depth, both in understanding each experiment and exploring richer data that emerge from research in specific locations. 3 Results and discussion The results concern three main questions: (1) where and when these experiments occur; (2) what types of interventions are emerging as climate change experiments and the extent to which we can identify some common trends and characteristics; and (3) who leads the experiments and what governance mechanisms make them possible. 3.1 Where and when do these experiments emerge? Most experiments in the database, that is 79% of them (495 experiments) started after 2005, that is, after Kyoto was ratified. Only 5% of initiatives started before its initial adoption in 1997. This is not necessarily an indication that international agreements have direct impact in fostering climate change experimentation, but rather, that international climate change governance efforts correspond with an increasing interest on climate change in the collective imaginations of urban actors. Climate change has gained more visibility in the city at the same time as the agreements took place (Hoffman, 2011). The observed frequency of experiments in all world regions is a function of the distribution of cities in the sample (Fig. 1), an observation confirmed by the statistical correlation test. This suggests that urban climate change experiments are not necessarily confined to certain world regions, such as, Europe and North America. We also examined the association between urban climate change experiments in “more developed”, “less developed” and “least developed” nations (UN, 2010). The distribution of experiments is similar to the distribution of cities in world regions, with 8 experiments in cities in least developed regions (2%), 291 (46%) in less developed ones and 328 (52%) in more developed regions. The statistical correlation test confirms that the distribution of the sample of experiments is a function of the selection of cities, supporting the conclusion that urban climate change experimentation is not confined to any regions of the world. The analysis also looked into what urban characteristics predict the emergence of experiments. The total number of experiments found in each city was taken as the dependent variable, and independent variables included those whose data was compiled during the selection of cities (Total Population, Total GDP, World City Rank and Density and adding Total Land Area, GDP per capita and Annual Population Growth). We applied a linear regression model using different combinations of variables, from one up to seven. The best goodness of fit model was a model that included the seven variables, but the statistics for the model suggest that the predictive value of the model is limited. Whether a city is richer, or more populated or denser does not predict accurately whether we are more likely to find more experiments in such a city. An alternative hypothesis is that experiments as more likely in cities involved in transnational municipal networks, an important institutional arrangement through which climate change is governed (Kern and Bulkeley, 2009). Belonging to a network often requires taking certain forms of action, from plans to direct commitments, to reduce emissions or improve adaptation. The test evaluated to what extent the number of experiments in a city (dependent variable) could be explained by whether or not a city belonged to any of these networks. An independent variable was defined by whether or not a city belonged to transnational municipal networks. When we considered this variable together with the seven variables described above it improved the goodness of fit of the overall model, suggesting that this influences whether urban climate change experimentation is likely to occur and/or be more visible (although this comment should be taken with caution, considering that the model only explains 63% of observed values). The analysis of correlation between variables shows that the variable of whether or not the city belongs to a city network has a stronger association with the number of experiments in each city than any of the other variables described above. The importance of transnational municipal networks confirms the findings of case studies of urban climate governance. For example, London's prominent role as a site of experimentation (Hodson and Marvin, 2007; Bulkeley et al., 2012) has been supported by its active role in the C40 network. Yet, urban climate change experimentation goes beyond international policy initiatives, size and concentration of resources or population. Understanding the drivers and nature of urban climate change experimentation requires a more fine grained analysis, including looking into the kind of experimentation that occurs and how it is governed, the two issues that are analysed in turn in the following two sections. 3.2 What types of climate change experiments can we find and what are their characteristics? Most experiments are in the sectors urban infrastructure (31.1%), built environment (24.7%), and transport (18.8%). Adaptation experiments only account for 12.1% of the initiatives (Fig. 2). Adaptation initiatives may be less represented in the database because they have less visibility as experiments than those concerned with mitigation. Adaptation initiatives focus on taking anticipatory action to deal with future climate risks. Different areas of intervention for climate change adaption include protection (e.g. vulnerability assessment, capacity building and risk reduction measures); pre-disaster damage limitation (e.g. early-warning systems and community-based disaster preparedness and response plans); immediate post-disaster responses (rapid infrastructure restoration); and rebuilding (Moser and Satterthwaite, 2008). However, adaptation is often regarded as a transversal issue to be considered in most operations and not always differentiated from on-going development efforts or disaster management programmes (Satterthwaite et al., 2009). Because many adaptation initiatives are not necessarily taken purposively in the name of climate change, they are therefore missing from our definition of climate change experiments. Urban climate change experiments concentrate in urban infrastructure despite the difficulties inherent to manage infrastructures at the local level. Built environment and transport experiments are frequent in cities in the South were rapid population growth in peri-urban areas has led to raising demands for housing and transport (Allen, 2003). Less frequent are urban form and carbon sequestration experiments. In the case of urban form, one possible explanation is that there are still few practical examples of how to address mitigation through planning (but see Davoudi et al., 2009). The absence of carbon sequestration experiments highlights that either cities lack land resources to implement large carbon sequestration programmes or urban greening programmes are developed with independence of concerns with climate change mitigation. Fig. 3 provides an overview of the relative frequency of experiments in each sector in the different world regions considered above. The graph shows that although experiments in all sectors were found in every region, certain sectors appear to predominate in some areas. For example, in Asia, the data suggest that urban infrastructure experiments are more frequent. Transport projects are more popular in Central and South America, reflecting the regional impact of flagship transport experiences in Curitiba (Brazil) and Bogotá (Colombia) (Arup, 2011). Table 5 presents demonstrates the association between sectors, time periods and regions. As experiments concentrate in the last period since the ratification of the Kyoto protocol, the subsequent hypothesis is whether this is reflected in the growth of experimentation across sectors. The statistical test of independence suggests that there is no association between the sector and the time of occurrence. The second half of the table shows the total number of experiments in each sector in either less or more developed regions, to explore the association between the sector of urban climate change experimentation and different levels of development. Because of the distribution of the data, least developed and less developed regions were grouped together (least developed regions are defined as a subset of less developed ones, see UN, 2010). The test shows a weak association between the sectors and the regional distribution of experiments. Tests of association between specific regions and specific sectors suggest that while in most regions experiments are likely to emerge in any sector, in Asia, particularly, there is a predominance of urban infrastructure experiments. While it may be tentatively argued that the rapid processes of urbanization taking place in this region provide some degree of explanation for these findings, further research is needed to understand the broader drive in Asia towards this sector, and in particular, examining the flows of capital invested in large scale low carbon infrastructure. Urban climate change experiments are socio-technical because they purposively attempt to change the material arrangements and the cultures, norms and conventions that determine collective GHGs emissions and climate-related vulnerabilities in the city (Bulkeley et al., 2011). For example, a survey of climate change plans in 30 cities worldwide identified the most common mitigation measures in transport (Wagner, 2009) including examples of experiments such as the congestion charge in London or the experimentation with new ideas about the provision of transport in the city or the use of alternative fuels in other European cities (see e.g. Bertaud et al., 2009; Leape, 2006; Prud’homme and Bocarejo, 2005). Experiments challenge the technical basis of GHGs emissions, the social practices that produce them or both. Technical forms of innovation were more prevalent in the database, in 76% of all experiments (Table 6). Technical innovation was frequent in all sectors, especially in urban infrastructure, where 88% of interventions had a technical innovation component, but less frequent in carbon sequestration (40% of initiatives) and adaptation (60%). Social innovation was present in half of all the initiatives (50%). It was most frequent in carbon sequestration (60%) and urban form (64%) and most rare in urban infrastructure (39%). Is the type of innovation independent of the sector of intervention? The test of independence between variables suggests that although social and technical innovations emerge in all sectors, technical innovation is more likely in urban infrastructure experiments, while social innovation is more likely in adaptation, carbon sequestration and urban form experiments. Built environment experiments favour interventions that combine both social and technical innovation. In transport experiments neither type is more prevalent. Because of the strong links between energy use and GHGs emissions, urban climate change action has mostly focused in measures to optimise energy production, distribution and consumption. A study for the World Bank of climate change action in eight cities found that energy efficiency issues dominate the local agenda in climate change mitigation (Bulkeley et al., 2009). Improving the efficiency of appliances and designs is often coupled with behavioural measures to reduce energy demand (Betsill and Bulkeley, 2007). The extent to which initiatives in these sectors focus on reconfiguring energy systems is reflected in Table 7. The majority of interventions in the built environment and urban infrastructure systems were explicitly concerned with intervening in the energy system (74.8% of initiatives in the built environment and 77.6% of initiatives in urban infrastructure). Energy related initiatives were less frequent in urban form interventions (only 9 initiatives). This confirms a common observation among local policy-makers (for example those involved in the well-known Climate Change Action Plan in Mexico City), about the lack of means to put into practice low carbon planning principles to address issues of density and urban form and the resulting emphasis on punctual projects in infrastructure and the built environment (Castán Broto, 2011). Analyses of energy systems often tend to focus in the consumption or demand side, looking at energy end uses, and a production or supply side, looking at the generation and distribution of energy (RaEng, 2010). Table 7, an analysis of a sub-set of 281 experiments whose major objective is to intervene in energy systems, shows that most experiments in the database seek to intervene in energy consumption processes, although there is a trend towards new systems of energy production and generation in urban infrastructure, confirmed by the independence test. Since perceived size of investment and restructuring needed to develop a systemic change is a barrier to production-oriented interventions (RaEng, 2010), the emphasis on demand-side interventions may reflect greater possibilities to intervene in a distributed manner. Overall, experiments constitute strategies to open up new forms of intervention in different urban spaces. Who has capacity and authority to intervene leading and participating in urban climate change experiments is the broader question of governance to which the following section turns. 3.3 Who leads these experiments and what mechanisms made them possible? The analysis explored three aspects of urban climate change governance: the actors who lead action; the increased relevance of partnerships as a form of governance; the deployment of specific governance mechanisms, or modes of governance; and the extent to which environmental justice was a facet of experiments. Fig. 4 shows that, in line with previously gathered evidence through case-study research, local governments have a prominent role in leading 66% of urban climate change experiments. However, the data also reveal that, alongside city governments, other actors may be playing a key role in climate change experimentation such as private and civil society actors. Table 8 shows that actors are not confined to certain regions and there is variation in how actors operate. Using independence tests for each pair of values we established that, while in most cases the presence of an actor leading the experiment is independent from the region of operation, the tests of independence support the observation than private actors predominate in Asia, while other actors, especially civil society actors, lead fewer experiments than expected in that region. The predominance of private actors in Asia may be related to the rapid growth that has made capital available for climate change experiments, especially in infrastructure (see above). Private actors emerge as more likely to operate in capital-intensive sectors such as urban infrastructure while other actors do not have strong associations with any specific sector. Partnerships are important for local governments because they extend the operation of the state through facilitating further action by other actors (Kern and Bulkeley, 2009). Beyond the local government, partnerships are generally considered a key tool for capacity building (Eakin and Lemos, 2006) and building consensus (Newman et al., 2009). In the database, 296 experiments (47%) involved some form of formally recognised partnership between actors at different governance levels, whether this is in terms of vertical governance (e.g. partnerships between local, regional and national governments) or horizontal (e.g. partnerships between governments, civil society organisations and private actors). When considering participation, rather than leadership, multiple actors gain prominence (Fig. 5). Table 9 shows that the most common forms of partnership are those in which the local government leads with either private actors (112 experiments) or civil society actors (44 experiments). Local governments operate outside partnership more often than expected (in 239 experiments) whereas for other actors the frequency of operating in partnership is higher than expected. Civil society organisations often lead initiatives enrolling local governments as partners. This highlights that government support may be important in achieving projects led by civil society organisations, both in terms of providing resources and institutional support. Another significant trend is that private actors are able to draw partnerships with other private actors, for example, in partnerships between service delivery and financial organisations to make low carbon infrastructure projects possible. Analysis of modes of governance throws further light in terms of how the governance of climate change is being performed. This theory was originally developed with reference to municipal organisations (Bulkeley and Kern, 2006; Bulkeley et al., 2009). So far, our results suggest that the realm of authority is being blurred both because of the prominence of partnerships and the increasing importance of non-governmental actors in areas traditionally considered as governed by governmental actors (Table 10). Tests of independence show strong association of the modes of governance with the leading actors and the emergence of partnerships. Partnership makes enabling initiatives more likely and regulation initiatives less likely (Table 10). Thus, enabling may be a tool for different actors to built explicit forms of support from other actors as a means for establishing authority beyond their own realm. As the social and economic costs of climate change increase, attention is turned towards the equity implications of collective responses to climate change (Giddens, 2009). Climate justice debates are often framed in terms of nation-wide inequalities, and the responsibilities of industrialised countries in producing climate change. However, when examining the fabric of the city, it appears that the distribution of climate change responsibilities and vulnerabilities is often parallel to existing patterns of urban inequality (Satterthwaite, 2008). This raises questions about to what extent urban climate change experiments are concerned with justice and equity implications. Environmental justice concerns were found in 154 climate change experiments (24.6%) and they were more common in urban form, built environment and adaptation. A second concern is whether certain actors play a key role in advancing justice-related arguments. The contingency table (Table 11) shows that while both private actors and civil society organisations considered justice explicitly in their experiments, public actors were less likely to do so, which is confirmed by the strong association between the two variables. One explanation for the absence of justice claims in publicly led experiments is that government actors already operate under the belief of having the mandate to govern, which includes considerations of legitimacy and social justice, whereas private and civil society actors may make explicit environmental justice claims to justify their operations. Broader explanations pointing at the dominance of elites or the utilitarian approaches embedded in planning cultures should be tested within specific urban contexts. 4 Conclusion This paper tracks the rise of urban climate change experimentation as a new means through which climate governance is conducted. The survey shows that experimentation has been a growing trend after the Kyoto ratification in 2005 and it is not confined to specific regions. Its emergence cannot simply be predicted by the general characteristics of the city (whether this is size, density or wealth) or the city's commitments to climate change action. Among all the factors considered, the internationalisation of urban environmental governance through city networks will need closer attention in further research. Experimentation involves multiple forms of technical and social innovation. Despite the diversity of experiments, these do not always challenge established ideas about the management of resources in the city. For example, in the case of interventions on energy system there is still a separation between interventions seeking to reconfigure consumption patterns, mostly in the built environment, and interventions seeking to transform the systems of energy production. Experiments in energy decentralisation and in energy production within the household question this divide, but the survey data suggest that such radical experiments – capable to foster systemic change – coexist with forms of experimentation that do not fundamentally challenge mainstream ideas about the production and consumption of energy in the city. Further research is needed to examine the potential to move from incremental interventions (like the majority included in this survey) to interventions leading towards systemic change. While local governments lead the majority of experiments, many other actors intervene either leading experiments or in partnerships. Partnership emerges as a key feature in climate change governance. Linked to enabling modes of governance it emphasises the extension of local forms of authority through the support of initiatives conducted by non-state actors. Another interesting feature is the inclusion of justice claims in climate change experiments, especially among private and civil society actors (rather than local governments), who may need to construct explicitly justifications for their attempts to govern climate change. Finally, the analysis throws interesting questions regarding the emergence of a characteristic form of urban climate change experimentation in Asia. In particular, the analysis suggests that experiments where private actors intervene in urban infrastructure predominate in Asia, in contrast to other regions where neither a particular sector nor particular actors appear to predominate. This new trend of purposive experimentation in climate change governance in cities in Asia, could be associated with new private-led forms of urbanism in emerging economies or with different cultural approaches to managing climate change. This methodology has allowed, for the first time, a systematic comparison of urban climate change experiments across 100 cities. The long-term effectiveness of experiments and their interaction across scales are issues beyond the scope of this analysis to be addressed with further research. However, alongside case-study based research, this methodology provides a fruitful avenue to understand urban climate change experimentation in context. Revealing the underlying drivers in climate change experimentation, factors hindering action, effectiveness on the ground and impact could be further developed through additional survey work, focused on specific regions or metropolitan areas. Overall, the methodology reveals the heterogeneity and ubiquity of climate change experimentation and traces the opening up of new spaces for climate change governance in the city.
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                Author and article information

                Contributors
                dave.huitema@ivm.vu.nl
                A.Jordan@uea.ac.uk
                stefania.munaretto@ivm.vu.nl
                mikael.hilden@ymparisto.fi
                Journal
                Policy Sci
                Policy Sci
                Policy Sciences
                Springer US (New York )
                0032-2687
                24 May 2018
                24 May 2018
                2018
                : 51
                : 2
                : 143-159
                Affiliations
                [1 ]ISNI 0000 0004 1754 9227, GRID grid.12380.38, Institute for Environmental Studies (IVM), , Vrije Universiteit Amsterdam, ; De Boelelaan 1087, 1081 HV Amsterdam, The Netherlands
                [2 ]ISNI 0000 0004 0501 5439, GRID grid.36120.36, Faculty of Management, Science, and Technology, , Netherlands Open University, ; Valkenburgerweg 177, 6419 AT Heerlen, The Netherlands
                [3 ]ISNI 0000 0001 1092 7967, GRID grid.8273.e, Tyndall Centre for Climate Change Research, School of Environmental Sciences, , University of East Anglia, ; Norwich, NR4 7TJ UK
                [4 ]ISNI 0000 0001 1019 1419, GRID grid.410381.f, Climate Change Program, , Finnish Environment Institute, ; P.O. Box 140, 00260 Helsinki, Finland
                Author information
                http://orcid.org/0000-0001-8565-3200
                Article
                9321
                10.1007/s11077-018-9321-9
                6438633
                1cba8283-7421-4455-9608-e4f01e43b30b
                © The Author(s) 2018

                Open AccessThis article is distributed under the terms of the Creative Commons Attribution 4.0 International License ( http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.

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