Abstract
Nature-based Solutions (NbS) are currently promoted as a panacea for improving human-nature relations. Yet the way of amplifying and mainstreaming NbS beyond scientific demonstrator projects into policy contexts is still bearing shortcomings, in particular in the uncertain futures of a post-COVID-19 world. Successful NbS amplification may be achieved by (1) using multi-scalar action to balance differing interests and reconcile governance levels, (2) providing financial and other institutionalized incentives and strategies for integrated participation processes, (3) using appropriate governance and management scales effectively integrating mediators, (4) using opportunities for transformative change offered by crisis, and (5) learning from worldwide amplification experiences.
Current practice of amplifying nature-based solutions
In face of the twin crises of climate and COVID-191, people-nature relations have to be rethought in cooperation with science and policy to secure the continued existence of humans and nature on our planet. Nature-based Solutions (NbS)—understood as actions which are inspired by, supported by, or copied from nature and which address ecological, social, and economic challenges in sustainable ways2—can lead a way forward. NbS arguably provide a promising approach to help achieve many of the United Nations’ Sustainable Development Goals (SDGs), such as good health and well-being (SDG 3), sustainable cities and communities (SDG 11), and sustainable land use (SDG 15)3:169. Examples of NbS include coastal management to mitigate the effects of climate change impacts, reestablishing green spaces to reduce the impact of urbanization, restoring floodplains and wetlands to reduce the risk of downstream flooding, transforming arable land into grasslands, and cooperation among land users to enhance ecosystem services delivery4,5. The term is used as an umbrella term for existing concepts such as e.g., Ecological Restoration, Ecological Engineering, Green and Blue Infrastructure6, Ecosystem Services7,8, Ecosystem-based Management, Ecosystem-based Adaptation, Ecosystem-based Disaster Risk Reduction, or Building with Nature9.
Currently, there are several initiatives to amplify NbS (for a typology of amplification processes see10). At a global policy level, 131 nations—66% of all signatories to the Paris Agreement—include NbS for climate change mitigation and adaptation in their Nationally Determined Contributions (NDCs)11. At a regional scientific level, the European Commission currently supports numerous research and innovation projects, such as Connecting Nature, BlueGreenCities, UrbanGreenUp, RECONECT, NATURVATION, and PHUSICOS, that engage in establishing demonstrator cases for designing and implementing NbS mainly in urban, suburban, and rural areas and assessing their impacts and co-benefits for people and nature12. As requested by the Commission, the projects focus on NbS testing in demonstration sites or frontrunner regions and cities and envision subsequent knowledge transfer to other areas as a form of amplifying out NbS (Fig. 1). The intended transfer of NbS knowledge thereby often follows, not necessarily explicitly but by content, the concept of experimentalist governance which allows the testing of different governance arrangements in a “process of provisional goal-setting and revision based on learning from the comparison of alternative approaches to advancing them in different contexts.”13:3. The aim is, that by comparing and learning from different approaches, policy ends and means can be further developed, evidence-based policy making can be supported, and broader transformative change be initiated14,15.
From shortcomings of NbS demonstrator case studies to recommendations for institutional change. Green tiles refer to the content derived from first wave NbS demonstration studies, blue tiles refer to the content derived from second wave implementation studies, SEE-URBAN-WATER and RECONECT are project examples referred to in this article that address the shortcomings of the first wave of NbS demonstration studies.
We agree that the experimentalist approach to amplifying NbS is advantageous. Most importantly, it enables early testing of novel and flexible solutions to the complex, context-specific, and ambiguous challenges and delivers empirical evidence on NbS effectiveness in approximated real-world situations. This includes the testing of implementation options despite significant barriers, such as existing infrastructures, inhibiting social practices as well as hindering governance systems, and economic instruments in place. It provides opportunities to study unconventional, non-regulated, and untested interventions which otherwise would not materialize because of economic reasons (funding of innovative solutions is usually not provided by public budgets), practical reasons (working routines do not include time for experimentation) or lacking knowledge (innovative ideas are simply not on the table). In this light, the experimentalist approach may allow changing “material arrangements, cultures, norms, and conventions, and in the process, create a new political space”16:5.
While the COVID-19 pandemic reveals the importance of NbS and current opportunities enabled by the public attention to people-nature relations, we identify three shortcomings of the current practice of amplifying NbS. Although science is on its way to address these shortcomings, it needs support from policy to succeed. That is why the recent experiences gained in policy experimentation and initiatives for green recovery emerging from the COVID-19 pandemic should be harnessed. Science and policy can implement key strategies for amplifying NbS if both are effectively working together.
We argue that due to the pressing global challenges, NbS need to contribute to transformative change that can no longer be reached by amplifying planning approaches, but requires a more radical re-thinking of key driving factors17 and combinations of structural, systematic, and enabling approaches18.
Our objective is to reflect on the barriers and opportunities of NbS amplification in a post-COVID-19 world. Our argumentation is based on an iterative reflection of our experience on investigating amplification processes of NbS in Europe and Central America and supported by the experience reported in recent studies of NbS planning and implementation efforts19,20. Starting from highlighting amplification opportunities arising from the COVID-19 pandemic, we argue that ´first wave´ NbS demonstration studies had been set up in non-representative context conditions. Although providing valuable case study insights, they neither allow to demonstrate their full potential (too small, too diverse) nor how to overcome some key challenges (e.g., path dependency, financing, non-supportive actors, legislation etc.21). As an implication, their amplification potential beyond their particular contexts is at least limited and certainly still needs to be demonstrated. However, to really demonstrate the full potential of NbS and to show ways of how to overcome key challenges, demonstration sites need to both unravel their full potential (large-scale) and be representative of key barriers (context conditions). Based upon lessons learned from the first wave and stressed by examples of how to address the shortcomings, ‘second wave´ demonstration studies do not only have to be representative in physical terms, but also in terms of key amplification challenges. They need to go beyond individual demonstration studies and be more systematically coordinated and organized in a complementary way to each other. We conclude with five recommendations on how science and practice can further enhance successful NbS amplification in the current turbulent times of crises and beyond (Fig. 1).
Revealed opportunities arising from the COVID-19 pandemic
The implications of the COVID-19 pandemic relate to the NbS implementation context in different ways. Firstly, lockdown policies decreased environmental pollution and let many people realize the benefits of a healthy natural environment. Those impacts are e.g., cleaner air - the reduced economic activity and traveling as a consequence of the COVID-19 situation temporarily reduced China’s CO2 emissions by a quarter in only a relatively short time22, cleaner water—Venice’s canal water looks clearer as Corona virus keeps visitors away, and less noise which leads to a (increased) perception of silence and sounds of nature (e.g., bird singing). Secondly, the pandemic can be understood as another societal challenge which, similar to climate change, can be tackled by NbS, e.g., by providing more green spaces for outside activities to secure peoples’ health during the crises. NbS therefore offer resilience for maintaining well-being especially in cities23. Finally, the pandemic can also be seen as a window of opportunity or critical juncture that can break the path dependence of hitherto science-policy efforts and allow for a truly greener recovery, harnessing the chances of substantially amplified NbS uptake24,25.
The raise of opportunities for climate adaptation, more sustainability and degrowth due to the pandemic has been recently discussed, e.g., for energy26, electricity and mobility27 or sustainable consumption and supply chains28, biodiversity29,30,31, and nutrition32,33.
In case of breaking the traditional path in favor of NbS, the underlying mechanisms of change can be direct and indirect. Direct changes in the sense that measures that include NbS become more functional through the pandemic, and indirect changes as human behavior and possibly even values transform as a result of pandemic effects. An example combining these three ways of pandemic impact are green spaces in cities. On the one hand, green spaces became more functional as available space for recreation during lockdown restrictions. On the other hand, people noticed the impact of physical outdoor activities on their health and valued green spaces more than before. This may support decisions in favor of setting up or renovating green spaces in the future as the demand increased and the functionality became more visible34.
The pandemic also presents opportunities for ad-hoc experiments that are visible right now and seize the crises as a chance. For example, because of less vehicular traffic, some cities like Berlin, Bogota, and Brussels established so-called pop-up infrastructure to allow for increased physical distancing, safe walking and cycling during the pandemic. More innovations of these types using NbS are imaginable (Box 1).
In comparison to the outlined current experimental practice for amplifying NbS, these initiatives are “real time experiments”28: they result from ad-hoc political decisions, as governance structures have changed faster than before27 and the political will is suddenly there, applying ideas already approved by science. The COVID-19 window of opportunity can be actively used by testing ideas and scenarios independently from scientific funding and usual policy issues.
Shortcomings of the current practice of amplifying NbS
While we consider ‘experimentalist upscaling´ an important step forward towards a broader implementation of NbS, we argue that the current application of the approach bears some fundamental shortcomings.
First, NbS interventions proposed in ongoing research and innovations projects are often too small, frequently due to sheer practical reasons, as they need to be realized during a project duration of maximum 5 years, or too dispersed in space to substantially yield ecological effects and address the societal challenges we face35. The interventions thus provide only limited learning opportunities when not linked to wider contexts of policies and planning strategies for establishing NbS at larger areas that could actually yield relevant ecological changes and improvements36. Furthermore, the focus on smaller scale interventions misses opportunities to explore options for planning, implementing, and governing larger-scale NbS at the landscape scale beyond single cities, which require the tackling of much more complex polycentric and multilevel governance structures. Apart from that, smaller interventions usually require less coordination among diverse actors37,38,39.
Second, the economic context conditions within which ongoing projects are implemented are often not representative of real-world situations. Demonstrator projects are usually equipped with sufficient resources from the funding agencies, are mainly supported by public investment40 and rarely need to explore innovative financing options or develop appropriate business models. However, NbS interventions initiated through research projects still experience challenges to secure funding needed for post-implementation efforts beyond project lifetime (i.e., maintenance and monitoring)41. Therefore, not every city or community might have the potential and necessary conditions to become a demonstrator or follower (for a detailed analysis see42).
Third, and most importantly, the governance contexts in which existing projects implement NbS do not fully reflect or even consider the substantial decision-making and implementation barriers faced by efforts to establish NbS in real world situations43. The policy and decision-making contexts of frontrunner cities and regions are—by design—very supportive for NbS implementation and thus do not represent the complicated governance contexts of practice. For example, project regions are selected which provide supportive governance conditions, decision-makers, and policy instruments. The opportunity to study unconventional NbS is usually provided by the selection of a ´willing´ partner contributing the required setting for the desired NbS. Diverging interests of stakeholders have usually been negotiated before the start of the funding or are homogeneous in favor of the NbS implementation. While such supportive governance conditions where collaboration is a precondition to set up the project are helpful to smooth the technical implementation process, their analysis provides only limited insights regarding the situations in real-world policy settings. In fact, the implementation of NbS in real world cases is often much less aligned, and sometimes even in conflict with prevailing stakeholder interests, ways of thinking, legacies of governance, and funding schemes44,45.
Although project calls usually require the analysis of the political context, questions of governance are often not systematically investigated in research46 or the results are not published. Case studies based on demonstrators can reveal that NbS work in terms of technology, stakeholder involvement, and management. Concerning the institutional arrangements, the analysis rather leads to insights into which framework conditions were supportive or at least not hindering in a certain location. But the request of a “recursive review of implementation experience in different local contexts”13:3 is hardly done by science. In the Urban Nature Atlas from the NATURVATION project, e.g., governance and financial shortcomings of case studies are collected and documented in detail but not scientifically compared.
Some research and innovation projects currently try to tackle the outlined problems in amplifying NbS. Shortcomings related to scale issues are exemplarily tackled by the SEE-URBAN-WATER project by connecting smaller-scale NbS interventions across a larger landscape context. Here, NbS are being implemented in an urban real world lab in a co-designed manner to address waterborne challenges47,48, such as water contamination and flooding, resulting from urbanization in the Great Metropolitan Area of San José, Costa Rica49. The lab is a representative neighborhood within a larger metropolitan area. Besides its socio-economic representativeness for similar areas in the river catchment in terms of building density, population structure, drainage and sewage systems, it is also naturally defined by its hydrological boundaries which are representative for the larger river basin it is part of. The connection to these socio-economic and hydrological landscape levels is achieved with the concepts of ecological connectivity and socio-economic accessibility (see Fig. 2). The experimental NbS demonstrators improve ecological connectivity within the larger river basin and socio-economic accessibility for the larger metropolitan area. Thus, the lab delivers empirical evidence of the potential to amplify experimental NbS for a representative socio-ecological subsystem that is nested within a larger system49. The project is engaged in amplifying out through transferring processes, that is doing a similar initiative in a similar context, and amplifying beyond, that is trying to change rules through the process of scaling up10.
The RECONECT project tries to address all three shortcomings by explicitly analyzing the financial and governance frameworks and by a within-project-upscaling strategy. RECONECT integrates more than two dozen demonstrators and collaborators worldwide through a co-creation methodology as part of a social-innovation concept. The collaborators want to implement in a non-supportive environment (governance and finance) and on a large scale. Therefore, they try to learn from the demonstrators which have implemented NbS more or less successfully so far. Governance, financial, and scalar potentials or barriers for amplifying NbS are assessed by the social scientific partners. In addition, demonstrators are integrated who have already successfully implemented relatively large NbS in the past in European countries like Austria, Switzerland, France, the Netherlands and Denmark. The Austrian demonstrator for instance, represents a case that allows for a better understanding of how NbS have become a mainstream measure in the management of Alpine hazards in torrential catchments. Already during the 1950s and 1960s major advancements were made in the Alpine area with respect to changing the paradigm of reducing torrential risks by the rapid and intensive application of NbS. Accordingly, other RECONECT cases are in the phase of NbS implementation but have proofed a specific amplification potential, e.g., for the Italian demonstrator it is expected to also be high as hundreds of small catchments along the Mediterranean coast face similar challenges. Governance analysis in RECONECT will also conduct surveys/interviews with relevant decision makers identified, discussing how to improve the legal and political framework to ensure the amplification of experiences from these demonstrators.
Besides the current activities promoted by the EU, there are also other programs that try to amplify NbS, e.g., the Working with Nature Approach in the USA, the Sponge City concept in China, the Room-for-the-River program in the Netherlands or the Renaturation of Rivers in Switzerland (Table 1). They face similar (USA, Netherlands) or different shortcomings (China, Switzerland) than NbS demonstrator case studies, nevertheless NbS implementation case studies can learn from them.
Recommendations for amplifying nature-based solutions
Amplifying NbS by replicating or transferring demonstrator projects disregards political realities and takes a long time that we, due to pressing climate scenarios, do not have.
To overcome the shortcomings we identified so far and based on the initial attempts described to overcome the scalar, financial, and governance misfits as well as reflecting on chances the COVID-19 pandemic offers, we have five recommendations for the second wave of NbS implementation studies, to foster NbS amplification with noteworthy environmental-political influence beyond demonstrators and for a post-COVID-19 world (Fig. 1).
Use multi-scalar action to balance differing interests and reconcile governance levels
Enhance the consideration of power constellations and actors’ interests, discourses, resources and perceptions, and develop a mainstreaming concept, e.g., based on multi-scalar action50. The often vested, persistent, and frequently also diverging interests of different stakeholders at different levels of governance need to be studied and ways need to be found of how to balance these interests. By this analysis, veto-players and main legal or financial obstacles are identified as well as actor’s strategies to successfully transform gray to more nature-based solutions. Future research and innovation projects need to study linkages to larger governance scales to better connect bottom-up (grass-root movements) with top-down approaches. Power issues and contestations have to be addressed with a pro-active, conflict resolution approach to deal with inherent conflicts and contestations often involved in implementing Nature-based Solutions18.
Provide financial and other institutionalized incentives and strategies for integrated participation processes
Investigate specific solutions for NbS funding in non-supportive contexts. If possible, examine different approaches that provide financial and other institutionalized incentives, e.g., payments for ecosystem services, public-private partnerships or water or forest funds51 which support actors at many different scales and places to favor NbS over gray infrastructures or to increasingly combine them. Participation in NbS design is welcome, but will be widely ineffective if no strategy is developed beforehand and implemented regarding how the participation process can be linked up with the required formal decision-making processes and instruments in order to lead to actual implementation. Approaches to co-design NbS in a participatory multi-actor action should be encouraged to the degree possible by facilitating a continuous expectation management52, clarifying opportunities for individual contributions, and transparently communicating the way formal decisions will finally be made36. The design of locally-led business models, together with suitable governance models, could be a step towards this goal but knowledge co-creation in this respect is still in its early stages53.
Use appropriate governance and management scales and look for mediators or multiplicators
Develop sustainable solutions for governing environmentally effective NbS at different governance levels. Joined-up planning and implementation at the landscape scale will be needed to introduce this change, thus requiring much cross-sectoral and multi-level coordination and cooperation36. NbS projects and initiatives have to be linked much better to existing governance and planning instruments. Possibly, different actions, i.e., different governance and management instruments, will be needed for different governance levels and/or to explicitly connect these different levels to prevent scale mismatches54,55,56. Efforts to identify and define appropriate governance and management scales to effectively achieve NbS amplification may as well be necessary since existing jurisdictions could not represent the required cross-sectoral and multi-level characteristics. It seems that mediators or multiplicators are needed to bring the different levels together.
Use opportunities for transformative change offered by crisis for real-time experiments and immediate effects
Use the opportunities for transformative change offered by crises like the COVID-19 pandemic widely. These can include the establishment of more flexible governance structures that allow the implementation of pop-up nature-based recoveries as real-time experiments that make immediate effects obvious and in consequence larger scale NbS more acceptable. This can also include the use of COVID-19 recovery programs as additional financing option for NbS1.
Learn from amplification strategies and experiences from other regions
Examine the shortcomings of other international programs for amplifying NbS and learn from their experiences. For instance, make meaningful use of stakeholder engagement to identify possible win-win opportunities at all project phases—derived as an experience from Working with Nature. Try to take advantage of possibilities of simultaneous change in the cognitive, normative, and regulative conditions—derived from experiences of the Sponge City program. Or change the national law and set up a long-term investment program as in Switzerland (see Table 1).
We argue that due to the pressing global challenges—and current negative news on the impact of the pandemic on the fulfillment of SDGs57 and climate change58—NbS need to contribute to transformative change. This can no longer be reached by amplifying planning approaches and requires institutional change to enhance cooperation. Beyond demonstrator projects there is an ´accountability trap´: cooperation for NbS needed across different sectors and governance levels, but no one feels responsible and puts aside own institutional interests. Therefore, we need institutional change to foster cooperation and we need more instruments than demonstrator projects. Structural, systematic, and engaging approaches18 are necessary as well as coordinated, well planned policy-mixes20 in concert with a wide range of other processes such as cultural, technological, social, and environmental to foster transformations59.
In summary, we plea for more social science research and support for the amplification of NbS planning and implementation across levels and scales, as well as for real time cooperation with policy to improve financial and governance structures suitable for NbS. The COVID-19 pandemic presents the chance for NbS to truly integrate solutions true as overlapping societal challenges become transparent. The crises have converged, so have the solutions (Christiana Figueres in Financial Times Interview: https://www.ft.com/video/c28e5efb-a8f4-45ed-b26b-18e87a38c94c). Better understanding and creativity is needed on how NbS innovation can be amplified across sites and levels, and how it can be best supported to address societal challenges and advance as many of the SDGs as possible—in urban areas and beyond.
Data availability
Data sharing not applicable to this article as no datasets were generated or analyzed during the current study.
References
Rosenbloom, D. & Markard, J. A COVID-19 recovery for climate. Science 368, 447 (2020).
European Commission. Towards an EU Research and Innovation policy agenda for nature-based solutions and renaturing cities. Final Report of the Horizon 2020 expert group on nature-based solutions and re-naturing cities, (European Commission, Brussels, 2015).
Cohen-Shacham, E. et al. Core principles for successfully implementing and upscaling nature-based solutions. Environ. Sci. Policy 98, 20–29 (2019).
Seddon, N., Turner, B., Berry, P., Chausson, A. & Girardin, C. A. J. Grounding nature-based climate solutions in sound biodiversity science. Nat. Clim. Change 9, 84–87 (2019).
Keeler, B. L. et al. Social-ecological and technological factors moderate the value of urban nature. Nat. Sustain 2, 29–38 (2019).
Escobedo, F. J., Giannico, V., Jim, C. Y., Sanesi, G. & Lafortezza, R. Urban forests, ecosystem services, green infrastructure and nature-based solutions: Nexus or evolving metaphors? Urban For. Urban Greening 37, 3–12 (2019).
Pan, H., Page, J., Cong, C., Barthel, S. & Kalantari, Z. How ecosystems services drive urban growth: Integrating nature-based solutions. Anthropocene 35, 100297 (2021).
Keesstra, S. et al. The superior effect of nature based solutions in land management for enhancing ecosystem services. Sci. Total Environ. 610-611, 997–1009 (2018).
Hack, J. & Schröter, B. Nature-based solutions for river restoration in metropolitan areas. Brears, R. The Palgrave Encyclopedia of Urban and Regional Futures. 1–10 (Springer International Publishing, Cham, 2021).
Lam, D. P. M. et al. Scaling the impact of sustainability initiatives: a typology of amplification processes. Urban Transform 2, 3 (2020).
Seddon, N. et al. Global recognition of the importance of nature-based solutions to the impacts of climate change. Glob. Sustain 3, e15 (2020).
Faivre, N., Fritz, M., Freitas, T., de Boissezon, B. & Vandewoestijne, S. Nature-based solutions in the EU: innovating with nature to address social, economic and environmental challenges. Environ. Res. 159, 509–518 (2017).
Sabel, C. F. & Zeitlin, J. Experimentalist Governance. Levi-Faur, D. The Oxford Handbook of Governance. 169–183 (Oxford Univ. Press, Oxford, 2012).
Kern, K. Cities as leaders in EU multilevel climate governance: embedded upscaling of local experiments in Europe. Environ. Polit. 28, 125–145 (2019).
Díaz, S. et al. Pervasive human-driven decline of life on Earth points to the need for transformative change. Science 366, eaax3100 (2019).
Chini, C. M., Canning, J. F., Schreiber, K. L., Peschel, J. M. & Stillwell, A. S. The green experiment: cities, green stormwater infrastructure, and sustainability. Sustainability 9 (2017).
McPhearson, T. et al. Radical changes are needed for transformations to a good Anthropocene. npj Urban Sustain. 1, 5 (2021).
Scoones, I. et al. Transformations to sustainability: combining structural, systemic and enabling approaches. Curr. Opin. Environ. Sustain. 42, 65–75 (2020).
Han, S. & Kuhlicke, C. Reducing hydro-meteorological risk by nature-based solutions: what do we know about people’s perceptions? Water 11, 2599 (2019).
Albert, C. et al. Planning nature-based solutions: principles, steps, and insights. Ambio, 1446–1461 (2020).
Matthews, T., Lo, A. Y. & Byrne, J. A. Reconceptualizing green infrastructure for climate change adaptation: barriers to adoption and drivers for uptake by spatial planners. Landsc. Urban Planning 138, 155–163 (2015).
Myllyvirta, L. China’s CO2 emissions have surged back from the coronavirus lockdown, rising by 4-5% year-on-year in May, analysis of new government data shows. https://www.carbonbrief.org/analysis-chinas-co2-emissions-surged-past-pre-coronavirus-levels-in-may (2020).
Samuelsson, K., Barthel, S., Colding, J., Macassa, G. & Giusti, M. Urban nature as a source of resilience during social distancing amidst the coronavirus pandemic. Preprint at https://doi.org/10.31219/osf.io/3wx5a (2020).
Mahoney, J. Path dependence in historical sociology. Theory Soc. 29, 507–548 (2000).
Davies, C. & Lafortezza, R. Transitional path to the adoption of nature-based solutions. Land Use Policy 80, 406–409 (2019).
Kuzemko, C. et al. Covid-19 and the politics of sustainable energy transitions. Energy Res. Soc. Sci. 68, 101685 (2020).
Kanda, W. & Kivimaa, P. What opportunities could the COVID-19 outbreak offer for sustainability transitions research on electricity and mobility? Energy Res. Soc. Sci. 68, 101666 (2020).
Cohen, M. J. Does the COVID-19 outbreak mark the onset of a sustainable consumption transition? Sustain.: Sci. Pract. Policy 16, 1–3 (2020).
Pearson, R. M., Sievers, M., McClure, E. C., Turschwell, M. P. & Connolly, R. M. COVID-19 recovery can benefit biodiversity. Science 368, 838 (2020).
Everard, M., Johnston, P., Santillo, D. & Staddon, C. The role of ecosystems in mitigation and management of Covid-19 and other zoonoses. Environ. Sci. Policy 111, 7–17 (2020).
Kavousi, J., Goudarzi, F., Izadi, M. & Gardner, C. J. Conservation needs to evolve to survive in the post-pandemic world. Glob. Change Biol. 26, 4651–4653 (2020).
Lal, R. Home gardening and urban agriculture for advancing food and nutritional security in response to the COVID-19 pandemic. Food Sec., 1–6 (2020).
Khetan, A. K. COVID-19: why declining biodiversity puts us at greater risk for emerging infectious diseases, and what we can do. J. Gen. Intern. Med. 35, 2746–2747 (2020).
Sugiyama, T. et al. Four Recommendations for Greener, Healthier Cities in the Post-Pandemic. https://www.thenatureofcities.com/2020/06/30/four-recommendations-for-greener-healthier-cities-in-the-post-pandemic/ (2020).
Thorslund, J. et al. Wetlands as large-scale nature-based solutions: status and challenges for research, engineering and management. Ecol. Eng. 108, 489–497 (2017).
Albert, C. et al. Addressing societal challenges through nature-based solutions: how can landscape planning and governance research contribute? Landsc.Urban Plan. 182, 12–21 (2019).
Albert, C., Von Haaren, C., Othengrafen, F., Krätzig, S. & Saathoff, W. Scaling policy conflicts in ecosystem services governance: a framework for spatial. Analysis. J. Environ. Policy Plan. 19, 574–592 (2017).
Hutchins, M. G. et al. Why scale is vital to plan optimal nature-based solutions for resilient cities. Environ. Res. Lett. 16, 044008 (2021).
Raška, P., Slavíková, L. & Sheehan, J. in Nature-Based Flood Risk Management on Private Land: Disciplinary Perspectives on a Multidisciplinary Challenge 9–20 (Springer International Publishing, 2019).
Frantzeskaki, N. et al. Nature-based solutions for urban climate change adaptation: linking science, policy, and practice communities for evidence-based decision-making. BioScience 69, 455–466 (2019).
Watkin, L. J., Ruangpan, L., Vojinovic, Z., Weesakul, S. & Torres, A. S. A framework for assessing benefits of implemented nature-based solutions. Sustainability 11, 6788 (2019).
Wurzel, R. K. W., Liefferink, D. & Torney, D. Pioneers, leaders and followers in multilevel and polycentric climate governance. Environ. Polit. 28, 1–21 (2019).
Frantzeskaki, N. et al. Examining the policy needs for implementing nature-based solutions in cities: findings from city-wide transdisciplinary experiences in Glasgow (UK), Genk (Belgium) and Poznań (Poland). Land Use Policy 96, 104688 (2020).
Zingraff-Hamed, A. et al. Governance models for nature-based solutions: cases from Germany. Ambio 50, 1610–1627 (2020).
Toxopeus, H. et al. How ‘just’ is hybrid governance of urban nature-based solutions? Cities 105, 102839 (2020).
Wamsler, C. et al. Environmental and climate policy integration: targeted strategies for overcoming barriers to nature-based solutions and climate change adaptation. J. Clean. Prod. 247, 119154 (2020).
Pérez Rubi, M. & Hack, J. Co-design of experimental nature-based solutions for decentralized dry-weather runoff treatment retrofitted in a densely urbanized area in Central America. Ambio 50, 1498–1513 (2021).
Chapa, F., Pérez, M. & Hack, J. Experimenting transition to sustainable urban drainage systems—identifying constraints and unintended processes in a tropical highly urbanized. Watershed. Water 12, 3554 (2020).
Chen, V., Bonilla Brenes, J. R., Chapa, F. & Hack, J. Development and modelling of realistic retrofitted Nature-based Solution scenarios to reduce flood occurrence at the catchment scale. Ambio 50, 1462–1476 (2021).
Hüesker, F. & Moss, T. The politics of multi-scalar action in river basin management: Implementing the EU Water Framework Directive (WFD). Land Use Policy 42, 38–47 (2015).
WBCSD. Incentives for Natural Infrastructure: review of existing policies, incentives and barriers related to permitting, finance and insurance of natural infrastructure. (World Business Council for Sustainable Development, Geneva, 2017).
Nesshöver, C. et al. The science, policy and practice of nature-based solutions: an interdisciplinary perspective. Sci. Total Environ. 579, 1215–1227 (2017).
Toxopeus, H. S. Taking Action for Urban Nature: Business Model Catalogue, NATURVATION Guide (2019).
Duraiappah, A. K. et al. Managing the mismatches to provide ecosystem services for human well-being: a conceptual framework for understanding the New Commons. Curr. Opin.Environ. Sustain 7, 94–100 (2014).
Young, O. R. Vertical interplay among scale-dependent environmental and resource regimes. Ecol. Soc. 11, 27 (2006).
Cumming, G. S., Cumming, D. H. M. & Redman, C. L. Scale mismatches in social-ecological systems: causes, consequences, and solutions. Ecol. Soc. 11, 14 (2006).
Naidoo, R. & Fisher, B. Sustainable development goals: pandemic reset. Nature 583, 198–201 (2020).
Fyfe, J. C. et al. Quantifying the influence of short-term emission reductions on climate. Sci. Adv. 7, eabf7133 (2021).
Linnér, B.-O. & Wibeck, V. Conceptualising variations in societal transformations towards sustainability. Environ. Sci.Pol. 106, 221–227 (2020).
Harrabin, R. Coronavirus: Lockdown ‘could boost wild flowers’. https://www.bbc.com/news/science-environment-52215273 (2020).
Bratman, G. N. et al. Nature and mental health: an ecosystem service perspective. Sci. Adv. 5, eaax0903 (2019).
Honey-Rosés, J. et al. The impact of COVID-19 on public space: an early review of the emerging questions—design, perceptions and inequities. Cities & Health, 1-17(2020).
Sanyé-Mengual, E., Anguelovski, I., Oliver-Solà, J., Montero, J. I. & Rieradevall, J. Resolving differing stakeholder perceptions of urban rooftop farming in Mediterranean cities: promoting food production as a driver for innovative forms of urban agriculture. Agric. Human Values 33, 101–120 (2016).
PIANC. Guide for applying Working with Nature to navigation infrastructure projects. (Brussels, Belgium, 2018).
Rijke, J., van Herk, S., Zevenbergen, C. & Ashley, R. Room for the River: delivering integrated river basin management in the Netherlands. Int. J. River Basin Manage. 10, 369–382 (2012). https://doi.org/10.1080/15715124.2012.739173.
Li, H., Ding, L., Ren, M., Li, C. & Wang, H. Sponge City Construction in China: A Survey of the Challenges and Opportunities. Water (Australia) 9, 594 (2017).
Kurth, A.-M. & Schirmer, M. Thirty years of river restoration in Switzerland: implemented measures and lessons learned. Environ. Earth Sci. 72, 2065–2079 (2014). https://doi.org/10.1007/s12665-014-3115-y.
Petty, K. Wildflowers on road verges: an uplifting sight during the coronavirus lockdown. (2020). https://www.plantlife.org.uk/uk/blog/wildflowers-on-road-verges-an-uplifting-sight-during-the-coronavirus-lockdown.
Acknowledgements
Funding was provided by the German Federal Ministry for Education and Research (Bundesministerium für Bildung und Forschung-BMBF) through a grant for the PlanSmart research group (Grant no: 01UU1601A and B) and for the SEE-URBAN-WATER research group (Grant no. 01UU1704) and RECONECT project from the European Union’s Horizon 2020 research and innovation programme under grant agreement no. 776866. We thank Prof. Dr. Dagmar Haase, Prof. Dr. Stephan Pauleit, and Dr. Claudia Sattler who provided feedback on an earlier version of this manuscript. We further would like to thank all anonymous reviewers for their time spent on reviewing our manuscript and their thoughtful comments helping us to substantially improve the article. Last but not least we thank Thea Eleahnora Maria Kelly for language editing the final version of the manuscript.
Funding
Open Access funding enabled and organized by Projekt DEAL.
Author information
Authors and Affiliations
Contributions
This paper is based on a workshop organized by B.S. and F.H. B.S., J.H., F.H., C.K., and C.A. contributed equally and substantially to the manuscript and created the concept, drafted and discussed the manuscript and edited the text in an iterative feedback process. B.S., J.H., F.H., C.K., and C.A. are accountable for all aspects of the work in ensuring that questions related to the accuracy or integrity of any part of the work are appropriately investigated and resolved. B.S., J.H., F.H., C.K., and C.A. approved the final version of this paper.
Corresponding author
Ethics declarations
Competing interests
The authors declare no competing interests.
Additional information
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Rights and permissions
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as 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. The images or other third party material in this article are included in the article’s Creative Commons license, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons license and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this license, visit http://creativecommons.org/licenses/by/4.0/.
About this article
Cite this article
Schröter, B., Hack, J., Hüesker, F. et al. Beyond Demonstrators—tackling fundamental problems in amplifying nature-based solutions for the post-COVID-19 world. npj Urban Sustain 2, 4 (2022). https://doi.org/10.1038/s42949-022-00047-z
Received:
Accepted:
Published:
DOI: https://doi.org/10.1038/s42949-022-00047-z
This article is cited by
-
How path dependency manifests in flood risk management: observations from four decades in the Ennstal and Aist catchments in Austria
Regional Environmental Change (2023)