Abstract
The recent shift to individualisation of flood risk calls for a stronger involvement of private actors. Bottom‐up citizen initiatives (BUIs) may bring together governmental bodies with people at risk. Drawing on a screening of existing BUIs in Europe, North America, and Australia and an in‐depth analysis of three study sites, this paper maps BUI activities to stages in the risk management cycle and discusses the institutional, relational and social proximity between BUIs and other stakeholders. Flood BUIs often take over roles that the authorities are not willing or able to fulfil. BUIs emerge out of frustration with current risk policies, after a catastrophic flood event, government‐initiated engagement projects or targeted funding opportunities. BUIs can take different forms, ranging from oppositional pressure groups, self‐help movements for disaster response and recovery, to initiatives formally installed by law. While self‐organised BUIs benefit from high proximity to their home communities, formalised BUIs are deeper embedded in existing institutional structures. In order to gain a stronger voice in the risk debate, BUIs need to expand from the local level to catchment areas and exchange expertise and resources in nationwide or cross‐border networks. However, BUIs may create parallel political structures that are not democratically legitimised.
Keywords: citizen participation, civic protest, disaster risk management, flood action group, grassroots movement, risk governance
1. INTRODUCTION
Increasing flood risks under climate and societal change (IPCC, 2014) significantly transform the roles held by different actors in flood risk management. Government authorities struggle to carry the full load of protecting and recovering from extreme hydrological events (Pfurtscheller & Thieken, 2013). Thus, the forthcoming policy agenda strives to delegate responsibilities and costs from the civil authorities to private citizens (Adger, Quinn, Lorenzoni, & Murphy, 2016; Thaler & Priest, 2014). As international strategies such as the Local Agenda 21 (UN Conference on Environment and Development, 1992), the EU Floods Directive (EU, 2007), or the Sendai Framework for Disaster Risk Reduction (UNISDR, 2015) are implemented in national jurisdictions, centralised policy directions are increasingly combined with local strategies for managing local risks with local stakeholders (van Aalst, Cannon, & Burton, 2008; Veraart, van Nieuwaal, Driessen, & Kabat, 2014). Among those local stakeholders, concerned citizens are meant to take centre stage (Thaler & Levin‐Keitel, 2016).
1.1. Citizen initiatives in risk governance
Giving citizens at risk a stronger role in flood risk management has already been on the agenda for many decades (e.g., Arnstein, 1969). Against this background, the recent concept of risk governance emphasises stronger citizen engagement (Renn, 2008). Involving citizens is seen as essential for leveraging local risk expertise, legitimising policy decisions, or establishing compliance with emergency procedures (Dilling & Lemos, 2011; Moser & Ekstrom, 2010). To this end, power, responsibility and policy outcomes need to be balanced and co‐produced between professionals and involved citizens (Albrechts, 2013; Boyle & Harris, 2009; Innes & Booher, 2004).
However, citizens rarely enter the risk discourse as individuals, but pool their influence and resources (Kruse & Seidl, 2013; Kuhlicke et al., 2011). The present paper aims to shed light on the emerging role of bottom‐up citizen initiatives (BUIs), understood here as community‐based, participatory groups, in which private households at risk band together for local preventive action, flood response, recovery, or lobbying governmental bodies. Self‐organised BUIs, on the one hand, emerge as local grassroots groups founded by committed activists as a response to the inadequacy and ineffectiveness of mere top‐down policy (van Aalst et al., 2008; Veraart et al., 2014). Formalised BUIs, on the other hand, are initiated by government authorities seeking cooperation or transfer of responsibility from public to private actors (Edelenbos, Van Buuren, Roth, & Winnubst, 2017; Mees, 2013).
In light of the upcoming risk governance agenda, BUIs may bridge the gap between mainstream, centralised institutions and individual citizens (Djordjevic, Butler, Gourbesville, Mark, & Pasche, 2011; Termeer et al., 2011). As intermediaries and facilitators, BUIs may help to align the views of individuals and institutions (Reed et al., 2009; Stanghellini, 2010). BUIs may act as dialogue partners that civil servants are more willing to accept as counterpart than they would free‐floating individuals (Driessen, Dieperink, Laerhoven, Runhaar, & Vermeulen, 2012; Levin‐Keitel, 2014). Nevertheless, government agencies are sometimes reluctant to embrace BUI activity, as open civic dialogue easily turns into protest and media attention that impede rather than support deliberative decision processes (Blackstock et al., 2015; Buchecker, Ogasa, & Maidl, 2016; Newig, Kochskämper, Challies, & Jager, 2016).
1.2. Objectives
The aim of this paper is to illustrate how bottom‐up initiatives emerge and establish themselves in local flood risk management. To this end, we seek to answer the following research questions:
Which activities are undertaken by BUIs, and how did those activities develop against the background of citizen needs and governmental practice?
How do BUIs relate to other actors in the risk governance arena, in particular to governmental institutions, local communities, and other citizens at risk of flooding?
This paper begins by presenting the analytical frameworks and methods in Sections 2 and 3: the risk management cycle and a screening of the BUI landscape for answering the first, and the proximity concept and an in‐depth analysis of three study sites for answering the second research question. The results in Section 4 first map the current scope of flood BUIs in Europe, North America, and Australia and then spotlight the three study sites, assessing how BUIs tie in with other activities and actors. Therein, we illustrate the spectrum of self‐organised to formalised BUIs, that is, BUIs independent from or supervised by governmental authorities. Section 5 provides a conclusion on future roles of BUIs in regards to existing institutions.
2. ANALYTICAL FRAMEWORKS
We employ two analytical frameworks to describe and classify BUIs: first, we map BUIs' activities to the prevention, protection, preparedness, response, and recovery stages of the classic risk management cycle (EU, 2004; see Table 2). BUI activities in lobbying to governmental bodies are mapped to the stages specific for the contested policy; for example, a BUI that negotiates the designation of flood risk zones with the local authorities is mapped to the prevention stage. Using the risk management cycle framework, we illustrate typical activities of BUIs, and how these activities complement existing institutions in flood risk management.
As second analytical framework, the concept of proximity allows us to better understand how stakeholders operate in a collaborative setting such as flood risk management (Boschma, 2005; Huber, 2012; Lundquist & Trippl, 2013). Proximity encompasses geographical distance as well as involvement in a shared network (Torre & Rallet, 2005). The proximity lens enables analysis of the partnership arrangements that BUIs establish with local stakeholders. Here, we differentiate between the institutional, relational, and social dimension of proximity, which are common distinctions in proximity theory, as they describe the stakeholder interrelations emphasised in risk governance (Thaler, Priest, & Fuchs, 2016). Table 1 lists indicators of how each proximity dimension can be evaluated in a particular BUI (higher levels of proximity imply that a BUI is more likely to achieve its objectives).
Table 1.
Proximity dimension | Indicators |
---|---|
Institutional proximity (between the BUI and the public administration) | The BUI's agenda and arguments enter and shape formal decision processes and lead to consensus building instead of unilateral decision‐making |
The BUI receives support from authorities (e.g., funding, resources, sharing of knowledge) | |
The BUI's area of influence overlaps with the boundaries set out by the rule of law or political practice | |
Roles and responsibilities of the BUI are defined in relation to the roles of other formal actors | |
Relational proximity (between the BUI and its local community or adjacent regions) | The BUI has access to material and non‐material support from local networks |
The BUI shares coherent aims with other actors | |
The BUI coordinates with and complements parallel community processes | |
The BUI exchanges developments, objectives and concepts with other actors (social learning) | |
Social proximity (among BUI members) | BUI members share coherent aims |
BUI members trust each other | |
Low variation and high interaction between BUI members | |
BUI includes everyone who is affected and wishes to participate | |
Key personnel hold defined roles and act in a transparent and accountable way |
Institutional proximity refers to the relationship between a BUI and governmental institutions in flood risk management. Institutional proximity describes the political influence a BUI exerts, and to what extent the issues advocated by a BUI are taken up by those formally in power. Institutions set the “rules of the game” within society; these rules govern individual behaviour and structure social interactions towards joint decisions (North, 1990; Raschky, 2008). A BUI that performs well within the institutional ruleset may achieve a position in the risk debate that goes beyond petitioning governmental decision makers (Albrechts, 2013).
Relational proximity describes how deeply a BUI is embedded in its home community as well as its relations to adjacent regions, such as those located in the same river catchment. Relational proximity also reflects social capital as well as language, experiences and worldviews shared with other citizens (Bourdieu, 1986; Coleman, 1990); these informal threads of the social fabric may give a BUI additional leverage in the risk debate.
Social proximity relates to the size and quality of the network among BUI members. Citizens who engage in a BUI form interpersonal linkages based on friendship and trust (Huber, 2012). The lifetime of a BUI critically depends on the personal relationships between its members (Balland, 2012). Local leaders or social entrepreneurs, such as flood wardens or chairmen, are regarded as crucial to build up and maintain expertise and commitment in a BUI (Mintrom & Vergari, 1996).
In both analytical frameworks, stages or dimensions may overlap to some degree. For example, if a BUI sets up a depot for emergency materials (protection stage) and conducts training in how to use them (preparedness stage), BUI members will probably also apply these procedures together when a flood strikes (response stage). Supra‐regional administrative bodies may affect both institutional and relational proximity; or social and relational proximity may overlap, if BUI members hold multiple community roles.
3. METHODS
We apply a four‐step approach to investigating BUIs in flood risk management (Figure 1): first, an extensive screening based on scientific literature, online sources (including media reports and social media platforms) and expert networks was conducted to identify the current diversity of BUIs. This screening was compiled with the objective of achieving maximum variation within the sample, a common approach in qualitative research (Anderson, 2010). The initial online search used predetermined keywords to capture the citizen‐driven nature of initiatives, including “bottom‐up flood mitigation,” “flood action group,” and “Bürgerinitiative Hochwasserschutz.” Subsequently, search terms were added, refined and translated to improve coverage. A content analysis structured the characteristics and activities of each identified BUI. Because of language barriers with the authors, the screening was limited to information in English and German. The screening adopted a scoping approach (Arksey & O'Malley, 2005), which does not amount to a systematic review. This was due to difficulties in developing universally valid criteria for BUIs and in retrieving an exhaustive set of BUIs, which are often short‐lived, sparsely documented and appear only sporadically in public communication channels. The screening sample, however, is neither comprehensive nor representative and thus may not reflect the actual distribution of BUIs and their activities. Therefore, we may not report any numerical estimates on the prevalence of BUI characteristics or activities. Nevertheless, the screening provides valuable insights on the general activities and orientation of the BUI field.
In the second step, three study sites were selected from the screening to assess the activities of each BUI in depth as well as its relationship with governmental authorities, its local community, and among its members. As a third step, a document analysis for each study site compiled legal documents, flood risk management plans, information available on BUI websites, and media reports. In the final step, semi‐structured qualitative interviews with three to five experts per study site validated and contextualised the findings, and captured aspects not covered by written sources. Interview participants were recruited from among local key actors in administration, academia and the BUIs themselves (see Table A1 in Appendix).
4. RESULTS
4.1. Landscape of flood BUIs
Our screening resulted in 70 BUIs across eight countries, among which we found BUIs to be most prevalent in Germany and the United Kingdom (Table A2 in Appendix; the italicised terms and IDs given below refer to BUIs and headings in this table). Although the BUI landscape appears to be highly fragmented, any particular BUI can be characterised by whether or not it is a pressure group, its triggers for formation, its activities within the risk management cycle, and its geographical scope.
4.1.1. Pressure groups
The key objective of BUI pressure groups is to oppose plans or actions taken by governmental authorities. The existence of pressure groups may point to a failure in flood risk governance, particularly if citizens feel excluded from the policy debate or if they think that their fundamentally different, possibly even incompatible, views do not receive due consideration. Usually, BUI pressure groups seek media attention, publish much of their information online and mobilise local residents for protest activities. One archetypical example is the Initiative Hochwasserschutz Eferdinger Becken (ID4), which publishes counterstatements online, and organises protest marches or joint opposition at risk information events held by the authorities. Overall, our screening indicates that pressure groups seem to be more widespread in Germany and Austria, but less common in the United Kingdom and the United States. This might be due to more integrative governance processes in the latter countries, or a less prevalent attitude of entitlement to public flood protection.
4.1.2. Triggers of formation
Flood BUIs typically emerge out of frustration with current flood risk policies, the occurrence of a specific flood event, or an opportunity offered by civic engagement projects or availability of funding. Frustration often arises from an unsatisfactory status quo, from a perceived lack of urgency in the authorities, or from planned public protection schemes that substantially impact the livelihoods of residents. The Bürgerinitiative Hochwasser Würschnitztal (ID24), for instance, has been frustrated by the slow progress of the planning and approval of local flood protection. Other frustration‐related triggers are nontransparent planning processes (e.g., Interessensgemeinschaft Inntal, ID3) or ongoing conflicts about the location of planned flood defence systems (Bürgerinitiative Landschaftsverträglicher Hochwasserschutz Hexental, ID18). Specific, often catastrophic, flood events are another common trigger. The Sedgeberrow Flood Group (ID43), for example, was founded in the aftermath of the 2007 flood event, when existing management strategies proved insufficient. Other BUIs seized opportunities offered by local authorities, such as the Purley Flood Defence Group (ID48), which was set up after the council contacted interested individuals. Opportunities can also arise through governmental funding, as it happened with the Bodenham Flood Protection Group (ID55), which received money from the Parish Council in its first year to buy flood defence tools and later transitioned into a self‐sustaining group.
4.1.3. Activities within the risk management cycle
The activities of BUIs vary widely across the five stages of the risk management cycle. With respect to the prevention stage, BUIs push for revisions of hazard maps (e.g., Interessensgemeinschaft Inntal, ID3), oppose further surface sealing caused by real estate development (e.g., BürgerInnen‐Initiative Hochwasserschutz Laakirchen, ID8), identify potential retention areas (e.g., Initiative Hochwasserschutz Buldern, ID21) or carry out petitions against building on flood plains (e.g., Glastonbury Northload Bridge Residents Flood Risk Action Group, ID59). BUIs also engage intensively in the protection stage. The Brompton Flood Prevention Group (ID57) for instance, has implemented a series of natural defences against flash floods, paid for by villagers. The Hands on Nashville: Waterway Cleanup, Restoration and Emergency Response initiative (ID68) helped to remove debris from local streams and creeks. The Tadcaster Flood Action Group (ID51) is particularly active in the preparedness stage; it has invested in an early warning and monitoring system, and trains volunteers in the use of equipment like radios and flood pumps. Other BUI preparedness activities include raising awareness of what residents should do before, during and after a flood event (e.g., Bürgerinitiative Andritz, ID6), developing community flood plans (e.g., Purley Flood Defence Group, ID48) and setting up flood stores (e.g., Todmorden Flood Group, ID50). Typically, flood stores are situated in key areas and provide emergency equipment such as shovels, axes, flashlights, walkie‐talkies, first aid kits, tents, or generators. A common BUI activity spanning across the preparedness and response stages is the introduction of flood wardens (e.g., Mytholmroyd Flood Group, ID46). Flood wardens are community volunteers who are trained to watch a section of a river and report critical conditions to early warning systems. They also educate locals about flood risks and establish lines of communication to emergency and rescue services. BUI activities related to the response phase include setting up databases of people who would need or could provide help (e.g., West Virginia Flood Relief Community Connection, ID64), sandbagging and supporting evacuation of residents (Tadcaster Flood Action Group, ID51), and providing food and cleaning materials (arche noVa Fluthilfe, ID12). Other flood BUIs focus on the recovery stage: the Lancashire Flood Recovery Fund (ID40) distributes charitable donations and grants to flood victims. The Community Emergency Response Team (ID42) helps with cleaning out affected homes, supplies cleaning products and replacement furniture, and offers moral support. Many BUIs engage in several stages of the risk management cycle. The Todmorden Flood Group (ID50), for instance, promotes risk awareness among households, maintains flood stores, assists with insurance queries and stays in touch with relevant agencies to develop and implement local flood plans.
4.1.4. Geographical scope
Most BUIs address issues at the local level, where the consequences of flood hazards are mainly experienced. However, it seems that BUIs increasingly realise that cross‐regional collaboration allows them to tackle flood hazards more effectively and to create additional political leverage. The Zusammenschluss der Interessengemeinschaften—Kontra Polder an der Oberen Donau (ID19) is such an example of regional cooperation seeking to align interests along the Danube River. Expanding beyond catchment‐wide cooperation, the National Flood Forum (ID60) is dedicated both to establishing a country‐wide network of community groups who share information and experience, and to channelling political influence. We only identified one single BUI that extends its activities beyond national borders: arche noVa Fluthilfe (ID12) supports communities in Germany and the Czech Republic in reducing future flood risks and recovering from catastrophic floods.
Our screening also reveals specific interrelations between BUI characteristics. Frustration, in particular, appears to fuel the formation of pressure groups. Pressure groups usually only address prevention and protection stages and limit their geographical scope to local issues. Numerous BUIs that are active in the recovery stage seem to have been triggered by previous flood events, probably because the recovery issue is more salient in communities with direct flood experience. BUIs concerned with protective measures often extend their geographical scope to the regional level, presumably because they recognise that successful risk reduction also depends on actions taken in up‐ and downstream communities. The screening further shows that BUIs from Germany and Austria mainly focus on the prevention and protection stage and try to shape flood mitigation plans by the government. Most British and American BUIs, on the other hand, follow a hands‐on approach, trying to improve community resilience by means of low‐cost, improvised and easy‐to‐deploy measures.
4.2. Study sites context
Based on the screening, we zoom in on three BUI study sites to illustrate the full scope of missions and origins of a BUI: the Cockermouth Flood Action Group, born out of the need for self‐reliance, as local risk management institutions are absent; the Bürgerinitiative Hochwasserschutz Übigauer Insel, established to co‐design flood protection at eye‐level with the authorities; and the Flutschutzgemeinschaften Hamburg, obligated by law to fulfil former state roles in flood preparedness and response at the building level. The study sites were purposefully selected as contrasting cases to span BUIs that are (1) active in various stages of the risk management cycle; (2) recently established or grown over a long time; and (3) self‐organised grassroots movements triggered by civic frustration or formalised groups initiated by the government.
4.2.1. Cockermouth flood action group (United Kingdom)
The civil parish of Cockermouth is located in the highly frequented Lake District tourism area. The two rivers Cocker and Derwent merge close to the town centre. Cockermouth has been flooded three times in rapid succession—in 2005, 2008, and 2009. The 2009 event affected the whole community and flooded more than 693 residential houses and 225 businesses (Cumbria Resilience, 2011).
The first community engagement emerged as a small self‐help group of local residents after the 2005 flood. The initiative did not spread to the whole town, though. The 2008 flood event re‐stimulated citizen action to resolve surface runoff in the Gote Road. Nevertheless, the Cockermouth Flood Action Group was only created after the devastating 2009 flood event. Local stakeholders began to exercise considerable pressure in the local flood policy discussion. The community worried about excessive insurance premiums for private households or businesses, or being denied a bank loan if no longer able to secure insurance. In addition, citizens perceived a lack of support and interest from political representatives after the flood event. Consequently, frustration and mistrust towards the civil authorities built up. The formation of the Cockermouth Flood Action Group was assisted by the British National Flood Forum, a UK‐wide BUI, established in 2002, that supports local BUIs, both in disaster recovery and implementing local preventive measures. Furthermore, the National Flood Forum lobbies local and national governmental bodies, giving people at risk a stronger voice in policy decisions (Thaler & Levin‐Keitel, 2016).
4.2.2. Bürgerinitiative Hochwasserschutz Übigauer Insel (Germany)
Übigau is an urban district of Dresden located directly at the River Elbe. The Bürgerinitiative Hochwasserschutz Übigauer Insel was launched one year after Übigau was heavily hit during the Elbe flood in June 2013. After this flood, residents recognised the need to prepare for future floods, especially regarding first responder reaction times, as many resources were wasted and sandbags inefficiently deployed because of coordination problems.
The BUI aims to enhance cooperation with responsible government agencies, which will point out potential improvements to existing dams and emergency plans. The action group is funded by private sponsors and receives no public money. Its activities primarily target the district of Übigau; all citizens with personal ties to this district can join the effort.
The arche noVa association has contributed external expertise to the development of emergency plans for Übigau. Arche noVa—Initiative for People in Distress—is an international aid organisation specialising in water, sanitation, and hygiene education. Dresden's city government actively seeks non‐bureaucratic collaboration with residents on future flood protection. This cooperative effort started in a joint risk analysis and awareness‐raising session in 2016 with all emergency services, the action group and representatives from the local administration.
4.2.3. Flutschutzgemeinschaften Hamburg (Germany)
The urban area HafenCity in Hamburg faces severe risks from tidal floods when storm surges from the North Sea travel up the estuary of the River Elbe. Protecting this area with conventional floodwalls would have incurred substantial costs and delays in real estate development. Instead, and complementary to strict building codes, the City of Hamburg passed a regulation in 2002 requiring building owners in this area to put into effect a partnership for flood protection for each residential building (called Flutschutzgemeinschaft, FSG; LSBG, 2012; Senat Hamburg, 2002). By law, FSGs have to document, maintain, exercise and execute flood protection at their respective buildings. The members of an FSG nominate a Flutschutzbeauftragter out of their circle as speaker and overseer. This person's position is unsalaried; however, the actual workload is rather small (Fellmer, 2014a; Mees, 2013). The majority of FSGs subcontract their duties to security agencies or property managers, though.
The introduction of FSGs by law is in line with the strongly regulated and hierarchical governance approach in Hamburg (Fellmer, 2014b; Mees, 2013). Residents take part in decision making only indirectly, through elected representatives; still, according to Mees, Driessen, and Runhaar (2014), they are satisfied with the division of responsibility and the level of safety. The introduction of FSGs amounts to shifting duties formerly carried out by the government to the affected citizens. An FSG is subsidiary to the flood management authorities and subject to their inspection. FSGs have to take self‐reliant action when a flood strikes and cannot rely on any governmental backup apart from emergency rescue services.
4.3. Activities of the study sites within the risk management cycle
The Cockermouth Flood Action Group influenced the decision process in the design of the local flood alleviation scheme (protection stage; Table 2). Currently, the BUI is playing a central role in the formation of the Cockermouth Emergency Response Group; therein, local citizens are involved and supported in the preparedness, response and recovery stages. However, the BUI is headed by a small circle of individuals and hardly reaches out to engage the larger community. The BUI has had to acquire technical knowledge from external consultants, an option which is only open to initiatives that command adequate financial resources. The BUI encouraged the Environment Agency, a national authority, to revise its original planning for flood protection despite higher costs. The revised scheme caters to the needs and interests of the town, providing economic benefits, and to individual households by means of a self‐raising barrier which offers the aesthetic benefit of an unimpaired view of the river. The BUI is also active in lobbying at the national level. However, these lobbying activities focus on promoting local Cockermouth interests, which implies a lack of solidarity and potential conflicts with neighbouring communities.
Table 2.
Stage | Cockermouth | Übigauer Insel | Hamburg |
---|---|---|---|
Prevention | None | None | None |
Protection | Developing a local flood risk management plan (in cooperation with the national government) | Identification of potential improvements to existing protective measures | Documentation of structural facilities in the building |
Yearly inspection of flood doors and evacuation routes | |||
Preparedness | Encouraging residents, to adapt their households, through face‐to‐face communication, organising round tables and discussions forums, leaflets, web‐site etc. | Development of an emergency plan | Setting up and updating an emergency plan detailing technical operations, communication and evacuation |
Risk analysis and risk awareness workshops with the emergency services, for example, site visits, communication training | Yearly flood emergency training with residents | ||
Building risk awareness among residents, for example, with flood bulletins in the hallway | |||
Response | Improved flood alert within the community | Reducing the reaction time of first responders | Timely alert during a flood event |
Support of evacuation centres | Closing flood doors and activating pumps | ||
Recovery | Support in filling insurance claims | None | None |
The principal activities of the Bürgerinitiative Hochwasserschutz Übigauer Insel focus on the protection and preparedness stages—namely, improving communication with the relevant governmental departments for flood protection. Under the guidance of arche noVa and the City of Dresden, the BUI has co‐produced an emergency plan which includes a detailed documentation of staff and materials that can be mobilised in a flood crisis. During the response to the 2002 and 2013 floods, poor cooperation with the authorities became apparent. To avoid similar problems in the future, the BUI has established contact persons for direct communication with city officials. These contact persons serve as intermediaries during a flood emergency, but also promote risk awareness among residents. Furthermore, the BUI works on branching out communication with other action groups in Dresden.
While nominally an independent group, in practice the Bürgerinitiative Hochwasserschutz Übigauer Insel undertakes its activities as an auxiliary under the leadership of the governmental authorities. In order to maintain the BUI's operational capacities as a full‐fledged emergency unit, especially over long periods without flood events, city officials train BUI members and provide specific guidance on the implementation of protective measures. During an actual flood response, the BUI is put under governmental command.
The main activities of the Flutschutzgemeinschaften Hamburg (FSG) revolve around maintaining and operating flood doors that seal off the ground floors of buildings (protection and preparedness stages). In addition, FSGs ensure that residents will comply with evacuation procedures (response stage). Each FSG has to submit yearly reports to the authorities; the authorities review these reports and, if deemed necessary, verify the practical implementation in site visits. This assignment of the operational role to the FSG and of the oversight role to the authorities is fully accepted among all involved actors. FSG duties can be considered a well‐defined, integral part of the overall flood management scheme in the HafenCity area.
However, in two respects, the actual role of FSGs falls short of the expectations put forward in the underlying legislation. First, the law which originally installed the FSG concept intends those groups to also raise flood awareness among residents as a side benefit (Mees, 2013). In those cases where residents disengage from their FSG role by subcontracting it to external companies, this side benefit is presumably diluted due to diminished citizen involvement. However, in the current view of the authorities, it would be unrealistic to expect this side benefit in an anonymous urban setting that hardly lends itself to promoting risk awareness among a highly fluctuating populace. Second, although the obligations of the operative personnel in FSGs are clearly set out, they are not empowered with the necessary know‐how to fulfil these obligations. The FSGs have to acquire their practical knowledge from learning‐by‐doing, from occasional instructions by flood door manufacturers, or by approaching pertinent experts. The flood management authorities criticise the wide variation in FSG qualifications but do not yet offer a dedicated training program.
4.4. Proximity of the study sites to other stakeholders
Institutional proximity reflects the relationship between a BUI and flood management authorities. The Cockermouth Flood Action Group features the highest institutional proximity of the three study sites. The turning point in the BUI's relationship with the Environment Agency as responsible authority occurred when the BUI changed its own self‐concept from a pressure group to an organisation with professional competences and with the aim of collaborating with the national authorities. The BUI even subcontracted the first flood risk management plan for the town to an external consultant company at their own expense. For its part, the Environment Agency shifted from solely carrying out flood engineering towards a project management role, focusing on negotiating and networking. This change of roles endowed the Cockermouth BUI with legitimacy and respectability, and consequently opened up a conversation about the design of flood alleviation Schemes. A similar agreement is underway in the case of the Bürgerinitiative Hochwasserschutz Übigauer Insel. Here, the authorities are aware and appreciative of the BUI, reflecting the level of trust in the group and its political voice. However, the BUI's actions do not manifest as co‐production among equals, but are subordinated governmental leadership and the expert support of arche noVa. Contrastingly, the Flutschutzgemeinschaften case amounts to a highly formalised civic duty imposed by law. Civil servants and the FSGs communicate only through standardised processes such as updating address information, filing reports, and inspecting selected buildings. Now, though, more than a decade after the original FSG regulation was passed, the authorities have developed informal procedures for quality assurance which go beyond a narrow supervisory role. City officials are sensitive towards minor lapses in FSG activities (such as poor technical competence or delayed notification if a flood door was closed); if they detect signs of negligence, they seek a clarifying discussion.
Relational proximity refers to how a BUI interacts with other stakeholders within the local community. In the Cockermouth case, the BUI channels community needs and facilitates local decisions that reflect these needs. In the flood defence scheme along the Rubby Banks Road, residents were adamant about retaining an open view of the river. The BUI organised local engagement and subsequently encouraged the Environment Agency to adapt their plans. The strong feeling of solidarity after severe flood events, already present in the Übigau district, has been intensified by the BUI's establishment. Local businesses in the district also became involved and promised assistance during future events. The Übigau BUI's community relations are closely connected to the role of arche noVa, who used Übigau as a showcase for a new handbook for facilitating community processes. Besides supporting the development of an emergency plan, arche noVa provided negotiating power and advice in the debate with civil servants and emergency service commanders. While the specific geographical layout of the Übigau district prohibits direct cooperation with neighbouring regions during catastrophic events, cross‐district collaboration is encouraged through an exchange of information. Flutschutzgemeinschaften, on the other hand, are largely disconnected from their local communities. Knowledge sharing between FSGs only occurs if one and the same person or company leads the FSGs of several buildings. FSGs have no discernible ties to other community initiatives; however, to some extent this can be attributed to the anonymous setting of a recently‐founded urban quarter, where close neighbourly networks and risk awareness, which could sustain an FSG, have not (yet) emerged.
Social proximity describes the relationships between BUI members themselves. Interactive arrangements within the Cockermouth BUI ensure sufficient access to information and decision‐making processes for all members. The BUI has recruited members with different backgrounds and knowledge, partly resulting from its origin as a self‐help group after previous flood events, and partly from continuous community interaction over the years. However, the BUI depends heavily on its organisation committee of local leaders, who manage all interactions with the local community and national authorities. The leadership of the Übigauer Insel BUI also consists of a core team. This requires considerable effort in reporting periodically to all concerned residents; however, in line with the BUI's objectives, this organisational structure ensures that external actors have direct access to a contact person at any time, even in times of crisis. The social proximity of the Flutschutzgemeinschaften is less pronounced and further weakened by the tendency to subcontract FSG duties to external companies. This contractual circumventing of actual citizen engagement may have been predisposed (or at least facilitated) by the original law that made FSGs mandatory: describing the FSG duties exactly but leaving open who may execute them made this function transferable to third parties. Thus, many FSGs are not maintained by interpersonal trust among their members, but by monetary transactions for the provision of flood protection services. Conducting FSG duties is currently evolving into a dedicated business model for building management services in Hamburg. If this tendency continues, FSGs might fully lose their BUI character and turn into a vehicle for the privatisation of flood risks.
5. DISCUSSION AND CONCLUSIONS
BUIs are rapidly evolving in the flood policy arena, and the present study can only provide a snapshot of their current scope in Europe, North America and Australia. The recent emergence of flood BUIs coincides with a general trend of citizen initiatives challenging state governmentality, such as urban greening initiatives or community photovoltaic power plants (Cloutier, Papin, & Bizier, 2018; Hatzl, Seebauer, Fleiß, & Posch, 2016). BUIs offer a promising avenue to putting into practice the risk governance objective of co‐producing natural hazard management with affected citizens (Nye, Tapsell, & Twigger‐Ross, 2011; Scolobig & Pelling, 2016). As bridging organisations, BUIs may bundle individual views into a joint agenda, thereby allowing the citizenry to enter partnerships with state institutions. Ideally, BUIs channel workforces and expertise into localised, effective and accepted plans to manage current and future flood risks (Thaler & Levin‐Keitel, 2016).
BUIs are active throughout all stages of the risk management cycle, often taking over roles that the authorities are not (or no longer) willing or able to fulfil (see Table 2). The wide range of BUI activities, as outlined in the screening, may be a stimulus to flood risk managers who seek innovative ways to involve citizens. However, as is evident in the Cockermouth and Übigauer Insel study sites, for BUIs to effectively enter existing management structures, both BUI members and relevant authorities need to rethink their traditional roles: while citizens need to leave behind protest motivations and build specialist expertise, authorities have to abandon paternalistic mindsets and widen their policy toolbox from technical fixes to social and organisational innovations. If both sides revise their traditional positions, reciprocal respect and shared language may set the stage for mutually beneficial collaboration (Nye et al., 2011).
Our results show that BUI constellations cover a spectrum, from self‐organised grassroots movements (e.g.,the Cockermouth study site), to initiatives that grow out of formal citizen hearings (e.g., opportunity as a trigger for formation, see Section 4.1.2), to legal arrangements where the authorities outsource their former protective tasks to the residents at risk (e.g., the Hamburg site). Self‐organised movements may benefit from their core circle of committed members with high relational and social proximity. By merit of their cohesion as a group and embedding in their community, they can keep up their efforts over a long time and adapt to changing political, social or hazard environments. However, some friction can be expected until the movement clarifies its role in the policy arena. In contrast, the strength of BUIs enacted by law lies in their institutional proximity: the legal grounds clearly define their role in relation to established institutions. On the other hand, as soon as the legal obligation or the monetary incentive for subcontractors is discontinued, those BUIs might swiftly break down, since they cannot draw on interpersonal trust as a foundation for their continued existence (see Table 3). Still, the Flutschutzgemeinschaften example underlines that even legally forcing citizens to band together can relieve responsibilities of the state, although it does not follow the higher (and sometimes romanticised) call for participatory, non‐hierarchical risk governance.
Table 3.
Dimension of proximity | Cockermouth | Übigauer Insel | Hamburg |
---|---|---|---|
Institutional proximity | Strong engagement and impact in decision‐making, based on incorporation of internal and external knowledge, such as recruitment of specialists, collaboration with private consultant groups, or informal contacts with the national government | Support from authorities was intensified after the last event | Responsibilities are clearly defined by law |
The BUI's role shifted from a lobby group to a professional dialogue partner | Routines are established for working together with local emergency services in the case of a flood event | Top‐down relationship: Authorities act as supervisors, FSGs act as operational subsidiaries | |
Environment agency remains a key player as supervising authority | Strong engagement from authorities for a long‐term cooperation with the BUI | Authorities do not offer dedicated support to FSGs, aside from water level warnings and flood information leaflets available to all residents | |
Relational proximity | Local actors contributed more than £ 1.1 million to the scheme | The BUI receives construction machinery and sand for filling sandbags from local networks | FSGs are not active beyond their legal mandate |
Temporary increase of the local council tax showed strong approval from the community | The BUI's influence is focused on its city district | No FSG umbrella organisation exists | |
The BUI was strongly supported by the National Flood Forum, in terms of transfer of knowledge and technical expertise | No involvement in other community processes | Build‐up of knowledge and operational synergies only if the same subcontractor works for several buildings or FSGs | |
Future joint activities with action groups in neighbouring city districts are planned | If the FSG consists of a sole building owner, then he may draw on an extended network of property management | ||
Core support role by arche noVa | |||
Social proximity | Low variation among the BUI speakers | The BUI speakers also act as opinion leaders within the group | Members have a contractual, not a personal relationship |
Personal relationship to the BUI | High solidarity and mutual help among members in the case of a flood event | High variation among residents hinders the formation of a social network underpinning the FSG | |
High degree of common goals and vision within the members of the BUI, as well as within the community | Everybody is invited to join the action group |
The diversity of activities and constellations observed in our screening speaks to the flexibility of BUIs as an additional instrument of flood risk governance. BUIs seem remarkably agile in terms of their duration and scope, particularly if they are self‐organised groups active in the preparedness, response and recovery stages: they can be established quickly, maintained for a limited period, and disbanded as soon as their mission is accomplished. They can easily reorient their agenda if local needs shift or previously silent population segments raise their voices. They are unconstrained by the legal and administrative rulesets with which governmental authorities have to comply. The Cockermouth BUI demonstrates this flexibility, as it iteratively changed its mission three times after experiencing a flood event. Therefore, state actors may consider BUIs a highly adaptable, albeit at times unpredictable, tool for change that may cover jurisdictional blind spots or underfinanced areas in all stages of the risk management cycle.
Extending its reach beyond the home community seems important for realising the interests of a BUI. The screening shows that many BUIs have a narrow, local geographical scope. Those BUIs may find it difficult to compete against institutional players drawing on wider expertise and circles of influence. Most BUIs lack external support in terms of technical knowledge transfer or legal backing. Presumably, none of the three study sites would have established itself successfully in the risk policy arena, had it not received a formalised legal status (regulation by the City of Hamburg) or been linked to national NGOs (Cockermouth with National Flood Forum, Übigauer Insel with arche noVa). Therefore, BUIs can be advised to seek collaboration with other civic actors in their catchment area, in order to have a stronger public voice and to obtain additional resources and ideas. National governments wishing to promote the development of BUIs should avoid scattering seed financing over small BUIs. Instead, supporting umbrella organisations may yield leverage and access to the agenda setting of numerous BUIs nationwide. However, umbrella organisations should navigate their role carefully: If they focus to heavily on political lobbying, they may lack the grassroots appeal for emergent pressure groups. If they provide too detailed practical expertise, they may undermine the self‐reliance of local BUIs, as citizens overwhelmed by the legal and engineering complexity of the flood topic may quickly hand over responsibility to the external experts (e.g., as indicated in the relation between the Übigauer Insel BUI and arche noVa).
Regardless of their value in bringing collaborative risk governance into practice, BUIs may create parallel political structures that are not democratically legitimised (Allmendinger & Haughton, 2009; Cloutier et al., 2018). A few outspoken community members might become BUI chairmen; local elite groups, especially, are likely to have the skills necessary to take a position of leadership (Begg, 2018; see Table 3). Civil servants might be tempted to build a personal relationship with a BUI contact without being aware whether this person actually represents the silent majority of all concerned citizens. If the BUI as a non‐state actor dominates the risk debate, it may undermine the standing of state actors that are directed, controlled and held responsible by elected representatives. However, in our three study sites we did not find any indications that BUI spokespeople had overstepped their mandate. The Übigauer Insel BUI even considers inclusiveness a central objective of the initiative. Nevertheless, all risk governance actors should be sensitive to the question of whether BUIs and their representatives have the full backing of the communities they claim or intend to represent.
Another caveat arises from the descriptive character of this study. At present, the BUI landscape seems too diverse and too fragmented to allow for more than mapping the overall directions taken; however, as soon as BUIs have consolidated their roles in the risk governance arena, we would welcome future studies to conduct a comprehensive review and provide a quantitative assessment on the prevalence of certain BUI characteristics and activities. Until then, state funding for citizen participation could be directed towards quasi‐experimental field studies comparing which BUI format works best in which local context.
Finally, the capability of BUIs to tackle environmental problems should not be overestimated. BUIs are not necessarily more efficient than centralised institutions if they merely act as lobbying organisations to influence decision makers instead of contributing new ideas; if they promote only their local agenda without partnership over communal borders; or if they predominantly advance the interests of the more affluent and fail to support deprived communities. It remains a key challenge for risk governance to weigh, in each particular case, whether transferring responsibilities to local communities or enacting top‐down procedures results in a better ratio between costs, inclusiveness, accountability and effective risk reduction.
ACKNOWLEDGEMENTS
We gratefully thank Brigitte Eder for preparing the Übigauer Insel study site, and to Mareike Fellmer for providing interview data on the Hamburg study site. The research project BottomUp:Floods received financial support from the Austrian Climate and Energy Fund and was carried out within the ACRP program (Funding No. B567146). Publication fees were covered by the Austrian Science Fund (FWF) under research grant W1256‐G15 (Doctoral Program Climate Change—Uncertainties, Thresholds and Coping Strategies).
Table A1.
Study site | Organisations of interviewed experts |
---|---|
Cockermouth |
National Flood Forum Cockermouth Flood Action Group Environment Agency Department for Environment, Food & Rural Affairs Cumbria County Council |
Übigauer Insel |
Bürgerinitiative Hochwasserschutz Übigauer Insel Arche noVa – Initiative for People in Distress City of Dresden, Environment Services |
Hamburg |
Hamburg State Company for Roads, Bridges and Waterways, Department of Dike Defence and Monitoring City of Hamburg, Internal Services, Disaster Control and Civil Protection HafenCity University Hamburg, Resource Efficiency in Architecture and Planning Research Group Flutschutzbeauftragte of selected Flutschutzgemeinschaften (provided by courtesy of Mareike Fellmer) |
Table A2.
Triggers of formation | Activities within the risk management cycle | Geographical scope | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Bottom‐up initiative (BUI) | Country | Pressure group | Frust‐ration | Flood event | Oppor‐tunity | Pre‐vention | Pro‐tection | Pre‐paredness | Response | Recovery | Local | Regional | National | Inter‐national | Reference ID |
Ulupna to Barmah Floodwatch | AUS | No | x | x | x | 1 | |||||||||
Numurkah flood action group | AUS | No | x | x | x | 2 | |||||||||
Interessensgemeinschaft Inntal | AUT | Yes | x | x | x | x | 3 | ||||||||
Initiative Hochwasserschutz Eferdinger Becken (OÖ) | AUT | Yes | x | x | x | 4 | |||||||||
Initiative für ökologischen und nachhaltigen Hochwasserschutz ‐ Aist | AUT | Yes | x | x | x | 5 | |||||||||
Bürgerinitiative Andritz | AUT | Yes | x | x | x | x | 6 | ||||||||
DV‐Donau Verein für nachhaltigen Natur‐ und Hochwasserschutz an Donau und Zubringern e.V. | AUT | No | x | x | x | x | 7 | ||||||||
BürgerInnen‐Initiative Hochwasserschutz Laakirchen | AUT | Yes | x | x | x | x | 8 | ||||||||
Team Österreich | AUT | No | x | x | x | x | 9 | ||||||||
Team Weissenkirchen | AUT | No | x | x | x | 10 | |||||||||
Interessengemeinschaft Reuss für einen vernünftigen Hochwasserschutz | CHE | Yes | x | x | x | 11 | |||||||||
Arche noVa Fluthilfe | DEU | No | x | x | x | x | x | 12 | |||||||
Hochwasserschutz Elbe‐Mulde | DEU | No | x | x | x | 13 | |||||||||
Hochwassernotgemeinschaft Rhein | DEU | No | x | x | x | x | x | 14 | |||||||
Hochwasserschutz‐Initiative Elbe‐Havel‐Winkel | DEU | No | x | x | x | x | x | 15 | |||||||
Bürgerinitiative Naturnaher Hochwasserschutz Selke | DEU | Yes | x | x | x | x | 16 | ||||||||
HWS ‐ Hochwasserschutz‐Initiative am Niederrhein | DEU | Yes | x | x | x | x | 17 | ||||||||
Bürgerinitiative landschaftsverträglicher Hochwasserschutz Hexental | DEU | No | x | x | x | 18 | |||||||||
Zusammenschluss der Interessengemeinschaften ‐ Kontra Polder an der Oberen Donau | DEU | Yes | x | x | x | 19 | |||||||||
Bürgerinitiative Hochwasserschutz Übigauer Insel | DEU | No | x | x | x | x | x | x | 20 | ||||||
Initiative Hochwasserschutz Buldern | DEU | No | x | x | x | x | 21 | ||||||||
Bürgerinitiative Hochwasser Aken (Elbe) | DEU | No | x | x | x | 22 | |||||||||
Bürgerinitiative für eine verträgliche Retention Breisach/Burkheim | DEU | Yes | x | x | x | 23 | |||||||||
Bürgerinitiative Hochwasser Würschnitztal | DEU | Yes | x | x | x | 24 | |||||||||
Bürgerinitiative für Hochwasserschutz Kobern‐Gondorf | DEU | Yes | x | x | x | x | 25 | ||||||||
Bürgerinitiative Hochwasser Nünchritz 2013 | DEU | Yes | x | x | x | x | 26 | ||||||||
Bürgeriniiative der Ortsteile im Osten von Erfurt | DEU | No | x | x | x | x | x | 27 | |||||||
Bürgerinitiative Hochwasserschutz für die Isarsiedlung | DEU | Yes | x | x | x | 28 | |||||||||
Buergerinitiative Hochwasser‐ und Naturschutz Altrip | DEU | Yes | x | x | x | 29 | |||||||||
Bürgerinitiative Rückhaltebecken Dietingen | DEU | Yes | x | x | x | 30 | |||||||||
Interessengemeinschaft Hochwasserschutz Ja‐ Polder nein | DEU | Yes | x | x | x | 31 | |||||||||
Bürgerinitiative Rettet das Donauried | DEU | Yes | x | x | x | 32 | |||||||||
Flutschutzgemeinschaften Hamburg | DEU | No | x | x | x | x | x | 33 | |||||||
Bürgerinitiative Grimma | DEU | Yes | x | x | x | x | 34 | ||||||||
Bürgerinitiative Hochwasser ‐ Altgemeinde Rodenkirchen | DEU | No | x | x | x | x | x | 35 | |||||||
Ungebundene Helfer während der Flut Dresden 2013 | DEU | No | x | x | x | 36 | |||||||||
Freuchie flood action group | GBR | No | x | x | x | x | 37 | ||||||||
Isbourne catchment group | GBR | No | x | x | x | x | 38 | ||||||||
Flooding on the levels action group | GBR | Yes | x | x | x | x | 39 | ||||||||
Lancashire flood recovery fund | GBR | No | x | x | x | x | 40 | ||||||||
Pang Valley flood forum | GBR | No | x | x | x | x | 41 | ||||||||
Community emergency response team | GBR | No | x | x | x | 42 | |||||||||
Sedgeberrow flood group | GBR | No | x | x | x | x | x | x | 43 | ||||||
Cockermouth emergency response group | GBR | No | x | x | x | x | 44 | ||||||||
Stonehaven flood action group | GBR | No | x | x | x | x | x | 45 | |||||||
Mytholmroyd flood group | GBR | No | x | x | x | x | x | 46 | |||||||
Hebden Royd flood action group | GBR | No | x | x | x | x | x | x | x | 47 | |||||
Purley flood Defence group | GBR | No | x | x | x | x | 48 | ||||||||
Cockermouth flood action group | GBR | Yes | x | x | x | x | x | x | x | 49 | |||||
Todmorden flood group | GBR | No | x | x | x | x | x | 50 | |||||||
Tadcaster flood action group | GBR | No | x | x | x | x | 51 | ||||||||
Eye on Calderdale | GBR | No | x | x | x | x | 52 | ||||||||
Hebden Royd flood action group | GBR | No | x | x | x | x | x | 53 | |||||||
Whalley & Billington ‐ flood action group | GBR | No | x | x | x | x | x | 54 | |||||||
Bodenham flood protection group | GBR | No | x | x | x | x | 55 | ||||||||
Charlton flood group | GBR | No | x | x | x | x | 56 | ||||||||
Brompton flood prevention group | GBR | No | x | x | x | x | 57 | ||||||||
Carlisle flood action group | GBR | Yes | x | x | x | 58 | |||||||||
Glastonbury Northload Bridge residents flood risk action group | GBR | Yes | x | x | x | 59 | |||||||||
National Flood Forum | GBR | No | x | x | x | x | x | x | 60 | ||||||
Morpeth flood action group | GBR | No | x | x | x | 61 | |||||||||
Skibbereen flood committee (SFC) | IRL | Yes | x | x | x | 62 | |||||||||
Clontarf resident's association | IRL | Yes | x | x | x | 63 | |||||||||
West Virginia flood relief community connection | USA | No | x | x | x | 64 | |||||||||
RainReady | USA | No | x | x | x | x | x | x | x | 65 | |||||
2016 flood of cedar rapids | USA | No | x | x | x | x | 66 | ||||||||
The gross gatherings | USA | No | x | x | x | x | x | 67 | |||||||
Hands on Nashville: Waterway cleanup, restoration and emergency response | USA | No | x | x | x | x | x | 68 | |||||||
Rain ready Floodlothian Midlothian | USA | No | x | x | x | x | x | x | 69 | ||||||
Flood forum for Connellsville City | USA | No | x | x | x | 70 |
x, criteria satisfied; Int.,international. Country codes refer to ISO 3166‐1 Alpha‐3 standard; Selected study sites are highlighted in bold.
Table A3.
Online sources accessed in March 2017.
Seebauer S, Ortner S, Babcicky P, Thaler T. Bottom‐up citizen initiatives as emergent actors in flood risk management: Mapping roles, relations and limitations. J Flood Risk Management. 2019;12:e12468. 10.1111/jfr3.12468
Funding information Austrian Climate and Energy Fund, Grant/Award Number: B567146; Austrian Science Fund (FWF), Grant/Award Number: W1256‐G15
REFERENCES
- Adger, W. N. , Quinn, T. , Lorenzoni, I. , & Murphy, C. (2016). Sharing the pain: Perceptions of fairness affect private and public response to hazards. Annals of the American Association of Geographers, 106(5), 1079–1096. 10.1080/24694452.2016.1182005 [DOI] [Google Scholar]
- Albrechts, L. (2013). Reframing strategic spatial planning by using a coproduction perspective. Planning Theory, 12(1), 46–63. 10.1177/1473095212452722 [DOI] [Google Scholar]
- Allmendinger, P. , & Haughton, G. (2009). Soft spaces, fuzzy boundaries, and metagovernance: The new spatial planning in the Thames gateway. Environment and Planning A, 41(3), 617–633. 10.1068/a40208 [DOI] [Google Scholar]
- Anderson, C. (2010). Presenting and evaluating qualitative research. American Journal of Pharmaceutical Education, 74(8), 141 10.5688/aj7408141 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Arksey, H. , & O'Malley, L. (2005). Scoping studies: Towards a methodological framework. International Journal of Social Research Methodology, 8(1), 19–32. 10.1080/1364557032000119616 [DOI] [Google Scholar]
- Arnstein, S. R. (1969). A ladder of citizen participation. Journal of the American Institute of Planners, 35(4), 216–224. 10.1080/01944366908977225 [DOI] [Google Scholar]
- Balland, P. A. (2012). Proximity and the evolution of collaboration networks: Evidence from research and development projects within the global navigation satellite system (GNSS) industry. Regional Studies, 46(6), 741–756. 10.1080/00343404.2010.529121 [DOI] [Google Scholar]
- Begg, C. (2018). Power, responsibility and justice: A review of local stakeholder participation in European flood risk management. Local Environment, 23(4), 383–397. 10.1080/13549839.2017.1422119 [DOI] [Google Scholar]
- Blackstock, K. , Dinnie, L. , Dilley, R. , Marshall, K. , Dunglinson, J. , Trench, H. , … Griffin, A. (2015). Participatory research to influence participatory governance: Managing relationships with planners. Area, 47(3), 254–260. 10.1111/area.12129 [DOI] [Google Scholar]
- Boschma, R. (2005). Proximity and innovation: A critical assessment. Regional Studies, 39(1), 61–74. 10.1080/0034340052000320887 [DOI] [Google Scholar]
- Bourdieu, P. (1986). The forms of capital In Richardson J. (Ed.), Handbook of theory and research for the sociology of education (pp. 241–258). New York, NY: Greenwood. [Google Scholar]
- Boyle, D. , & Harris, M. (2009). The challenge of co‐production. How equals partnerships between professionals and the public are crucial to improving public services. London, England: New Economics Foundation. [Google Scholar]
- Buchecker, M. , Ogasa, D. M. , & Maidl, E. (2016). How well do the wider public accept integrated flood risk management? An empirical study in two Swiss Alpine valleys. Environmental Science & Policy, 55(2), 309–317. 10.1016/j.envsci.2015.07.021 [DOI] [Google Scholar]
- Cloutier, G. , Papin, M. , & Bizier, C. (2018). Do‐it‐yourself (DIY) adaptation: Civic initiatives as drivers to address climate change at the urban scale. Cities, 74, 284–291. 10.1016/j.cities.2017.12.018 [DOI] [Google Scholar]
- Coleman, J. (1990). Foundations of social theory. Cambridge: Harvard University Press. [Google Scholar]
- Cumbria Resilience . (2011). Cumbria Floods November 2009. Learning from experience recovery phase debrief report. Carlisle: Cumbria Resilience Forum
- Dilling, L. , & Lemos, M. C. (2011). Creating usable science: Opportunities and constraints for climate knowledge use and their implications for science policy. Global Environmental Change, 21, 680–689. 10.1016/j.gloenvcha.2010.11.006 [DOI] [Google Scholar]
- Djordjevic, S. , Butler, D. , Gourbesville, P. , Mark, O. , & Pasche, E. (2011). New policies to deal with climate change and other drivers impacting on resilience to flooding in urban areas: The CORFU approach. Environmental Science & Policy, 14, 864–873. 10.1016/j.envsci.2011.05.008 [DOI] [Google Scholar]
- Driessen, P. P. J. , Dieperink, C. , Laerhoven, F. , Runhaar, H. A. C. , & Vermeulen, W. J. V. (2012). Towards a conceptual framework for the study of shifts in modes of environmental governance – Experiences from the Netherlands. Environmental Policy and Governance, 22(3), 143–160. 10.1002/eet.1580 [DOI] [Google Scholar]
- Edelenbos, J. , Van Buuren, A. , Roth, D. , & Winnubst, M. (2017). Stakeholder initiatives in flood risk management: Exploring the role and impact of bottom‐up initiatives in three ‘room for the river’ projects in the Netherlands. Journal of Environmental Planning and Management, 60(1), 47–66. 10.1080/09640568.2016.1140025 [DOI] [Google Scholar]
- EU . (2004). Flood risk management. Flood prevention, protection and mitigation. Communication from the Commission to the Council, the European Parliament, the European Economic and Social Committee and the Committee of the Regions. COM(2004)472 final, Brussels.
- EU . (2007). Directive 2007/60/EC of the European Parliament and of the Council of 23 October 2007 on the assessment and management of flood risks. Official Journal of the European Union, L 288, 27–34. [Google Scholar]
- Fellmer, M. (2014a). Die Sturmflut im Vorgarten. Das Beispiel zivilgesellschaftlicher Verantwortung in den Flutschutz‐ und Poldergemeinschaften in Hamburg. [The storm flood in the front garden. Civic responsibility on the example of alliances for flood protection and polders in Hamburg] In Knieling J. & Roßnagel A. (Eds.), Governance der Klimaanpassung. Akteure, Organisation und Instrumente für Stadt und Region (pp. 125–140). Munich: oekom Verlag. [Google Scholar]
- Fellmer, M. (2014b). Bürgerschaftliches Engagement und Sturmfluten: Ausprägungen und Einflussfaktoren am Beispiel des Flussgebiets der Tideelbe [Civic engagement and storm floods: Characteristics and drivers on the example of the Tideelbe catchment]. Detmold: Verlag Dorothea Rohn. [Google Scholar]
- Hatzl, S. , Seebauer, S. , Fleiß, E. , & Posch, A. (2016). Market‐based vs. grassroots citizen participation initiatives in photovoltaics: A qualitative comparison of niche development. Futures, 78–79, 57–70. 10.1016/j.futures.2016.03.022 [DOI] [Google Scholar]
- Huber, F. (2012). On the role and interrelationship of spatial, social and cognitive proximity: Personal knowledge relationships of R&D workers in the Cambridge information technology cluster. Regional Studies, 46(9), 1169–1182. 10.1080/00343404.2011.569539 [DOI] [Google Scholar]
- Innes, J. E. , & Booher, D. E. (2004). Reframing public participation: Strategies for the 21st century. Planning Theory & Practice, 5(4), 419–436. 10.1080/1464935042000293170 [DOI] [Google Scholar]
- Intergovernmental Panel on Climate Change (IPCC) . (2014). Climate Change 2014: Impacts, adaptation, and vulnerability. Part A: Global and sectoral aspects. Contribution of Working Group II to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge: Cambridge University Press.
- Kruse, S. , & Seidl, I. (2013). Social capacities for drought risk management in Switzerland. Natural Hazards and Earth System Sciences, 13(12), 3429–3441. 10.5194/nhess-13-3429-2013 [DOI] [Google Scholar]
- Kuhlicke, C. , Steinführer, A. , Begg, C. , Bianchizza, C. , Bründl, M. , Buchecker, M. , … Faulkner, H. (2011). Perspectives on social capacity building for natural hazards: Outlining an emerging field of research and practice in Europe. Environmental Science & Policy, 14(7), 804–814. 10.1016/j.envsci.2011.05.001 [DOI] [Google Scholar]
- Landesbetrieb Straßen, Brücken und Gewässer Hamburg (LSBG) . (2012). Sturmflutschutz in Hamburg. Gestern‐heute‐morgen [Strom flood protection in Hamburg. Past‐present‐future]. Berichte des Landesbetriebes Straßen, Brücken und Gewässer Nr. 10/2012. ISSN 1867‐7959.
- Levin‐Keitel, M. (2014). Managing urban riverscapes: Towards a cultural perspective of land and water governance. Water International, 39(6), 842–857. 10.1080/02508060.2014.957797 [DOI] [Google Scholar]
- Lundquist, K. J. , & Trippl, M. (2013). Distance, proximity and types of cross‐border innovation systems. A conceptual analysis. Regional Studies, 47(3), 450–460. 10.1080/00343404.2011.560933 [DOI] [Google Scholar]
- Mees, H. L. P. (2013). In‐depth report on case studies, belonging to article adaptive flood risk governance beyond the dikes. Retrieved from https://www.researchgate.net/publication/309740608_In‐depth_report_of_case_studies_belonging_to_article_Adaptive_Flood_Risk_Governance_beyond_the_dikes.
- Mees, H. L. P. , Driessen, P. P. J. , & Runhaar, H. A. C. (2014). Legitimate adaptive flood risk governance beyond the dikes: The cases of Hamburg, Helsinki and Rotterdam. Regional Environmental Change, 14(2), 671–682. 10.1007/s10113-013-0527-2 [DOI] [Google Scholar]
- Mintrom, M. , & Vergari, S. (1996). Advocacy coalitions, policy entrepreneurs, and policy change. Policy Studies Journal, 24(3), 420–434. 10.1111/j.1541-0072.1996.tb01638.x [DOI] [Google Scholar]
- Moser, S. C. , & Ekstrom, J. A. (2010). A framework to diagnose barriers to climate change adaptation. Proceedings of the National Academy of Sciences, 107, 22026–22031. 10.1073/pnas.1007887107 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Newig, J. , Kochskämper, E. , Challies, E. , & Jager, N. W. (2016). Exploring governance learning: How policymakers draw on evidence, experience and intuition in designing participatory flood risk planning. Environmental Science & Policy, 55(2), 353–360. 10.1016/j.envsci.2015.07.020 [DOI] [PMC free article] [PubMed] [Google Scholar]
- North, D. (1990). Institutions, institutional change and economic performance. Cambridge: Cambridge University Press. [Google Scholar]
- Nye, M. , Tapsell, S. , & Twigger‐Ross, C. (2011). New social directions in UK flood risk management: Moving towards flood risk citizenship? Journal of Flood Risk Management, 4, 288–297. 10.1111/j.1753-318X.2011.01114.x [DOI] [Google Scholar]
- Pfurtscheller, C. , & Thieken, A. H. (2013). The price of safety: Costs for mitigating and coping with Alpine hazards. Natural Hazards and Earth System Sciences, 13(10), 2619–2637. 10.5194/nhess-13-2619-2013 [DOI] [Google Scholar]
- Raschky, P. A. (2008). Institutions and the losses from natural disasters. Natural Hazards and Earth System Sciences, 8(4), 627–634. 10.5194/nhess-8-627-2008 [DOI] [Google Scholar]
- Reed, M. S. , Graves, A. , Dandy, N. , Posthumus, H. , Hubacek, K. , Morris, J. , … Stringer, L. C. (2009). Who's in and why? A typology of stakeholder analysis methods for natural resource management. Journal of Environmental Management, 90(5), 1933–1949. 10.1016/j.jenvman.2009.01.001 [DOI] [PubMed] [Google Scholar]
- Renn, O. (2008). Risk governance: Coping with uncertainty in a complex world. London, England: Earthscan. [Google Scholar]
- Scolobig, A. , & Pelling, M. (2016). The co‐production of risk from a natural hazards perspective: Science and policy interaction for landslide risk management in Italy. Natural Hazards, 81(S1), 7–25. 10.1007/s11069-015-1702-1 [DOI] [Google Scholar]
- Senat Hamburg . (2002). Verordnung zum Schutz vor Sturmfluten im Gebiet der HafenCity (Flutschutzverordnung‐HafenCity). [Regulation on the protection from storm floods in the HafenCity area]. HmbGVBl. Nr. 19, 107–111.
- Stanghellini, P. S. L. (2010). Stakeholder involvement in water management: The role of the stakeholder analysis within participatory processes. Water Policy, 12(5), 675–694. 10.2166/wp.2010.004 [DOI] [Google Scholar]
- Termeer, C. , Dewulf, A. , Van Rijswick, H. , Van Buuren, A. , Huitema, D. , Meijerink, S. , … Wiering, M. (2011). The regional governance of climate adaptation: A framework for developing legitimate, effective, and resilient governance arrangements. Climate Law, 2(2), 159–179. 10.3233/CL-2011-032 [DOI] [Google Scholar]
- Thaler, T. , & Levin‐Keitel, M. (2016). Multi‐level stakeholder engagement in flood risk management—A question of roles and power: Lessons from England. Environmental Science & Policy, 55(2), 292–301. 10.1016/j.envsci.2015.04.007 [DOI] [Google Scholar]
- Thaler, T. , & Priest, S. (2014). Partnership funding in flood risk management: New localism debate and policy in England. Area, 46(4), 418–425. 10.1111/area.12135 [DOI] [Google Scholar]
- Thaler, T. A. , Priest, S. J. , & Fuchs, S. (2016). Evolving inter‐regional co‐operation in flood risk management: Distances and types of partnership approaches in Austria. Regional Environmental Change, 16(3), 841–853. 10.1007/s10113-015-0796-z [DOI] [Google Scholar]
- Torre, A. , & Rallet, A. (2005). Proximity and localization. Regional Studies, 39(1), 47–59. 10.1080/0034340052000320842 [DOI] [Google Scholar]
- UN Conference on Environment and Development . (1992). Agenda 21 – Action plan for the next century (Rio de Janeiro, UNCED).
- UN Office for Disaster Risk Reduction (UNISDR) . (2015). Sendai framework for disaster risk reduction, 2015–2030. Geneva: UNISDR. [Google Scholar]
- van Aalst, M. K. , Cannon, T. , & Burton, I. (2008). Community level adaptation to climate change: The potential role of participatory community risk assessment. Global Environmental Change, 18, 165–179. 10.1016/j.gloenvcha.2007.06.002 [DOI] [Google Scholar]
- Veraart, J. A. , van Nieuwaal, K. , Driessen, P. P. J. , & Kabat, P. (2014). From climate research to climate compatible development: Experiences and progress in the Netherlands. Regional Environmental Change, 14(3), 1–13. 10.1007/s10113-013-0567-7 [DOI] [Google Scholar]