Skip to main content
Ambio logoLink to Ambio
. 2022 Mar 29;51(6):1433–1445. doi: 10.1007/s13280-022-01725-z

A transformative mission for prioritising nature in Australian cities

Niki Frantzeskaki 1,2,, Cathy Oke 3, Guy Barnett 4, Sarah Bekessy 5, Judy Bush 6, James Fitzsimons 7,8, Maria Ignatieva 9, Dave Kendal 10, Jonathan Kingsley 2,11, Laura Mumaw 12,13, Alessandro Ossola 14,15,16
PMCID: PMC8963402  PMID: 35352304

Abstract

Australia is experiencing mounting pressures related to processes of urbanisation, biodiversity loss and climate change felt at large in cities. At the same time, it is cities that can take the leading role in pioneering approaches and solutions to respond to those coupling emergencies. In this perspective piece we respond to the following question: What are the required transformations for prioritising, valuing, maintaining and embracing nature in cities in Australia? We adopt the mission framework as an organising framework to present proposed pathways to transform Australian cities as nature-positive places of the future. We propose three interconnected pathways as starting actions to steer urban planning, policy and governance in Australian cities: First, cities need to establish evidence-based planning for nature in cities and mainstream new planning tools that safeguard and foreground urban nature. Second, collaborative planning needs to become a standard practice in cities and inclusive governance for nature in cities needs to prioritise Aboriginal knowledge systems and practices as well as look beyond what local governments can do. Third, for progressing to nature-positive cities, it is paramount to empower communities to innovate with nature across Australian cities. Whilst we focus on Australian cities, the lessons and pathways are broadly applicably globally and can inspire science-policy debates for the post COP15 biodiversity and COP26 climate change implementation processes.

Keywords: Indigenous knowledge, Metropolitan, Nature-based solutions, Planning, Policy, Urban

Introduction

Cities are interlinked systems of systems; they consist of ecosystems, economies, cultures, politics manifesting through different visions of the future but ultimately, they are places for people and nature (Gehl 2010). Over recent years knowledge is gathered—theoretical and experiential—on the importance of safeguarding nature in cities to strengthen the resilience of people and the planet to climate change, biodiversity extinction and environmental degradation (UNEP 2021). Cities have the governance capacities to respond to these crises (Oke et al. 2021). A variety of voices and institutions shepherd public (and private) green spaces and urban ecosystems through policies, strategic plans and programmes, in systems of constant flux, where the role of, or, location for nature in cities is contested (Dorst et al. 2019). Leaving nature in place, or creating new spaces for nature in cities demands the transformation of planning approaches, policy mechanisms and community practices to put nature at the forefront (Shade et al. 2020; Ossola and Lin 2021). A social, ecological and economic case can be made for prioritising nature-based solutions in Australian cities (Lin et al. 2021). Examples of nature-based solutions include water sensitive and biodiversity sensitive urban design (Garrrand et al. 2018; Kirk et al. 2021) rather than traditional built infrastructure and engineering solutions (Allan et al. 2020; Coutts et al. 2013; Kabisch et al. 2017; Ignatieva et al. 2018, 2020; Frantzeskaki et al. 2019; Keeler et al. 2019).

A macro-driver affecting urban landscapes in Australia is the pace of urbanisation. Australia is a nation of cities and towns. We use the term Australian ‘cities’ to indicate metropolitan areas rather than jurisdictional boundaries, as most Australian cities are governed by multiple local governments as well as state governments. We would like to respectfully acknowledge that Australia’s cities are built on the lands of Aboriginal First Nations peoples whose relationship with both lands and waters through connection to and caring for Country is ongoing and has existed for tens of thousands of years (Miller 2021). In 2016, almost 80% of Australia’s Aboriginal peoples lived in urban areas. Australian cities continue to grow rapidly, having one of the fastest urbanisation rates in (what it is considered) the western world—89% of the population living in a handful of urban areas. Urban development has been preferenced over nature, with economic pressures and imperatives competing with the need to protect natural landscapes (Champness et al. 2019).

Another macro-level driver of change is climate change. Australia as a continent faces pressures such as more frequent droughts, bushfires and extreme heat events that are affecting the resilience of city infrastructures and city dwellers alike now and in the future (Boer et al. 2020). Many climate change pressures are magnified for Australian cities, (Norman et al. 2021), for example most of Australian cities are coastal and face increasing pressures from sea-level rise (Threlfall et al. 2021). The liveability and character of Australian cities is in jeopardy if “climate-ready” interventions and policies are not promptly implemented (Ossola and Lin, 2021).

Against this context, it is recognised that if Australian cities are to contribute in achieving the global Sustainable Development Goals (SDGs) and strive for livability and resilience, transformations in ways of planning, governing and relating with nature are required (Australian Academy of Science 2021). The exploratory research question that guides us in this perspective piece is: What are the required transformations for prioritising, valuing, maintaining and embracing nature in cities in Australia? We adopt the mission framework of Mazzucato (2018) as an organising framework to present proposed pathways to transform Australian cities as nature-positive places of the future. The mission-oriented framework has its origin in innovation economics and proposes linking policy and strategy formulation for transformative actions to mission statements that fundamentally and radically progress sustainability challenges (Heikkinen et al. 2019; Sachs et al. 2019). The mission-oriented framework can help to mobilise ideas and develop proposals for prioritising planning of urban nature to enact sustainability transitions in cities.

The paper is organised as follows: In Sect. 2 we present a concept of a transformative mission for prioritising, valuing, maintaining and embracing nature in Australian cities. We present three transition pathways that are interconnected and collectively can enable the required transformations. We elaborate on the challenges, the existing good practices as well as the knowledge bases that can support and activate these pathways in Australian cities. We conclude with Sect. 3 by linking our proposed mission-oriented approach for nature in Australian cities to a globally relevant agenda by highlighting key messages and implications aligned with COP15 of the Convention on Biological Diversity in Kumming, China, the United Nations Convention Climate Change (UNFCCC) COP 26 meeting in Glasgow, UK and Intergovernmental Panel on Climate Change review cycles (AR6-AR7).

A transformative mission for nature in Australian cities

A transformative vision for nature-positive cities

The visions and narratives on urban nature in Australian cities need decisive shifting (Australian Academy of Science 2021) to put nature front and centre in all new efforts related to urbanisation, renewal and densification. Whilst often relegated to a lesser urban land use, urban nature needs its urban locus—the physical and metaphysical place where it can grow and thrive. Existing ‘urban futures’ paradigms remain human-centric, employing greening strategies at the margins of urban planning and doing little to confront the drivers of urban development (Daniels et al. 2020). Alternative visions for securing social wellbeing benefits through fostering sustainable human-nature relationships are rarely considered (Ison and Straw 2020) due to short-term governance approaches with limited civil society participation (Mercon et al. 2019; Clark and Harley 2020). Recent scholarship points to the notion of nature-positive economy and futures as an attainable and desirable state for the planet in order to restore planetary boundaries and live in a safe and equitable operating space (Raworth 2017). The focus of nature-positive economies and futures is specifically advocated by World Economic Forum (WEF), stating that a nature-positive future is a goal to work for the coming decade and “a nature positive approaches enhances the resilience of our planet and our societies) (WEF 2020). According to WEF (2020, p. 59) “a nature-positive built environment shares space with nature, putting whole ecosystems rather than humans alone at the centre of design. (…)”. Stemming from this proposal of nature-positive urban environment, we propose to look closer to how nature-positive cities (or even broader, a nature-positive urbanism) can be realised. Specifically, we propose that nature-positive development /future needs to be the aim for our urban systems as well.

By shifting to a narrative of ‘nature-positive cities’, nature can be valued and governed as a formal urban asset with equal scope, worth and importance as traditional capital and infrastructural assets (Buse et al. 2018; Matsler 2019). Urban planning and design need to allow nature to permeate urban landscapes by removing physical and planning barriers that hamper or limit nature integration, to encourage a nature-positive urbanism in Australian cities. In doing so, cities can ensure that urban nature is not only retained but that positive outcomes can boost its performance, resilience and adaptability to old and new global and climate challenges (Davidson and Gleeson 2018; Daniels et al. 2020; Hobbie and Grimm 2020; Ossola and Lin 2021), and the plethora of its benefits for cities, (McPhearson et al. 2016; Kabisch et al. 2017; Dumitru et al. 2020; Padma et al. 2020; Almenaar et al. 2021), noting an acknowledged bias of research into larger cities, and the need for more knowledge of benefits of urban nature, and associated environmental justice issues, for smaller to medium cities (Kendal et al. 2020).

Whilst cities are diverse and complex, they offer plentiful opportunities to plan, retrofit, enhance, design urban nature at different scales, from city masterplan to urban neighbourhood, private yard, public park or verge garden (Ignatieva 2010; Frantzeskaki et al. 2020; Kingsley et al. 2021a). Many facets of urban nature are adaptable, scalable and portable. That will require a shift of knowledge paradigm and practice of landscape architecture, to a biodiversity driven and benefiting landscape architecture approach as an alternative to the existing global homogenised picturesque-gardenesque approach (Ignatieva 2018; Alexandra and Norman 2020).

Nature-positive cities will be planned and managed differently to reflect and support the character and species of nature that belongs to them. The cultivated ‘beautified’ nature of exotic flower gardens, uniform avenues of street trees and carefully managed turf grass may still be favoured, but indigenous wildlife (plants and animals), complex native habitat structure, large trees with hollows and broken limbs, would all be valued and integrated into the landscape. Critically endangered remnant native grasslands would not be destroyed but would be an inspiration for public parks and gardens (DELWP 2016), nor, for example, would grey-headed flying fox camps be dispersed (Currey et al. 2018). Decisions on managing wildlife, or reintegrating nature into cities, need to go beyond human-centric concerns and consider environmental and biodiversity harms and benefits (Maller 2021). Truly nature-positive cities would allow all forms of nature in, to be experienced by urban dwellers (Robertson 2018; Kolokotsa et al. 2020; Mata et al. 2020). This has the potential to benefit humans and nature by mobilising an integrated ethic and practice of caring for human and ecological communities, progressing the possibility of taking on board Indigenous knowledge systems and practices like outlined in Caring for Country (Woodward et al. 2020).

We propose three interconnected pathways as starting actions to steer urban planning and urban policy and governance in Australian cities towards nature-positive urban futures:

  • Establish evidence-based planning for nature in cities;

  • Strengthen collaborative planning and inclusive governance for nature in cities; and,

  • Empower communities to innovate with nature.

Pathway 1: Establish evidence-based planning for nature in cities

A first pathway to drive urban agendas and actions towards nature-positive cities is to establish evidence-based metropolitan and urban planning for valuing, prioritising and maintaining nature in cities. Urban planning has the potential to bridge the gap between aspirations and real-life transformations in urban spaces and infrastructures, especially when informed and guided by evidence through data, accounting for lived experiences of people and a new appreciation of people-nature relationships in cities (Bush 2020; Potter 2020; Voskamp et al. 2021). Urban planning as an institutional platform to enable and accelerate the transition to nature-positive urbanism can elicit this by transforming planning instruments and approaches, including how urban parks are managed and regenerated, how offsetting is regulated, how zoning and urban development is managed and how new planning tools are integrated in existing urban planning processes.

Urban parks and open space are often important places for nature and for residents to experience nature. These spaces have been significant for city residents during COVID-19 lockdowns in many parts of the world, as places of exercise and contact with nature (Hockings et al. 2020; Ugolini et al. 2020). However, their governance and management are often fragmented, creating challenges for planning connectivity between parks and permeability of a city for nature (Ignatieva et al. 2008; Maron et al. 2016; Tzoulas et al. 2021). Greater inventory and coordinated management between councils, parks agencies, water authorities, planners, designers and developers is required to ensure these areas are managed as a network for people and nature (Sharifi et al. 2021a, b). Metropolitan-wide visioning, strategies and planning are important since they enable more holistic consideration of needs across the landscape-scale at which many species function (such as Living Melbourne: Our Metropolitan Urban Forest; The Nature Conservancy and Resilient Melbourne 2019; Hartigan et al. 2021).

Urban development is a major threatening process for nature within and on the fringes of cities. Whilst there may be legislation to protect threatened or vulnerable species and ecosystems within cities, biodiversity offsetting schemes (where biodiversity losses in one place are ‘offset’ in another place) often result in questionable ecological outcomes (Bull et al. 2013; Maron et al. 2016). Reforming offsetting metrics and assessments in the urban landscape is important given that offsetting often does not account for the ‘place-based’ value of nature and results in a localised loss of biodiversity in the places where people live (Garrard et al. 2018; Kalliolevo et al. 2021).

Remnant natural areas in cities are often critical for flora and fauna alike. Both large and small patches can be significant locations for biodiversity conservation with large remnants shown to contain a greater variety of species for some fauna groups (Palmer et al. 2008; Fitzsimons et al. 2011) and small patches often containing the last representatives of the most heavily impacted species and ecosystems (Wintle et al. 2018). Maximising retention of remnant areas when planning newly developing suburbs as well as restoration of natural areas on unused open space or sites decommissioned from other uses have significant positive impacts for nature and needs to be incentivised (Allison 2018). For these processes, it is important for urban planning to consider ecological and biodiversity evidence, research and monitoring, as well as to tap into interdisciplinary knowledge of planners and ecologists (White et al. 2005; Bohnet 2010; Williams et al. 2021). This is specifically relevant for small and medium size cities in Australia located in proximity to remnant natural areas and ecosystem reserves that post-pandemic may seem as desirable areas for peri-urban development. Another aspect to consider in small and medium size cities planning for urban nature is how urban form and biodiversity in urban green spaces relate and in result affect human and ecosystem health (Kendal et al. 2020, p. 6).

Planning schemes and instruments need to better protect features important to nature in cities (e.g. large trees, hollows), with many trees on private land lacking any mechanisms to ensure or promote their retention (Ordóñez-Barona et al. 2021; Wolf et al. 2020; Clark et al. 2020). Urban planning needs to consider lessons and mechanisms from efforts to protect nature on private land in rural landscapes, whilst accommodating the different social and ecological features of cities (Fitzsimons and Wescott 2001; Prado et al. 2018). New urban planning tools need to be integrated into existing planning practices and processes, for example, to connect data on tree canopy cover and other environmental indicators and outcomes to future planning decisions such as the Green Factor Tool (see Box 1).

BOX 1: Green factor tool, city of Melbourne.

We need to foreground and require green in new developments with tools such as City of Melbourne’s Green Factor which specifies minimum amounts of greening—in-ground, green roofs, walls or facades, in new developments—whether in residential, commercial or industrial settings (Bush et al. 2021). Drawing on experience and research from global examples of integrating greening into urban planning processes, such as Berlin’s Biotope Area Factor, and Seattle’s, Helsinki’s and Malmo’s Green Factor Tools (Bush et al. 2021), City of Melbourne developed the Green Factor Tool to quantify the ratio of greening to built form in new developments. The tool, the first of its kind in Australia, brings together City of Melbourne’s environmental policy objectives (including urban heat mitigation and biodiversity habitat provision), with research on how different forms of vegetation (trees, shrubs, ground cover) can deliver a range of ecosystem services (Bush et al. 2021). The tool allocates weighted points to different forms of greening, and importantly, assigns additional points for inclusion of a maintenance plan, in an attempt to influence the post-development establishment success for greening. Indeed, a key critique of development-based green factor ratings is the lack of integrated monitoring and enforcement efforts (Juhola, 2018). Just as we have a building code, we need a greening code that sets minimum standards, is enforceable and enforced. We also need incentives to reward going beyond minimum standards and demonstrating best practice, including voluntary certification approaches (such as developed by the Green Building Council of Australia) (Bush 2020).

Pathway 2: Strengthen collaborative planning and inclusive governance for nature in cities

The need for strong environmental policy at state and federal levels needs to go hand in hand with good governance and good planning by local government to support the prioritisation, design, implementation and maintenance of nature in cities. Australian cities operate under policy and planning cycles of state and federal governance levels that are not always synchronised with the needs and pressure at the local level. Despite this, there have been some bold metropolitan and local governance experiments, with Melbourne’s Living Melbourne Urban Forest strategy leading the way (Fasternrath and Coenen 2021; Moloney and Doyon 2021). To progress mainstreaming of nature-based solutions in Australian cities, Melbourne’s experience and recently City of Sydney’s Urban Forest Strategy point to the importance of collaborative planning approaches and cross sectoral partnerships from formulation to implementation. New forms of collaboration need not only to be experimented with as ways to innovate urban planning (Bush 2020) but also as ways to adapt urban planning institutions and processes to co-create and co-produce strategy formulation and science-to-policy translation (Coenen et al. 2020). In this it is critical to adopt a cross-sectoral approach that bridges interests and brings together different forms of knowledge (Malekpour et al. 2021), that specifically prioritise Indigenous knowledges and knowledge systems, alongside input from groups often shut out of access to nature due to a range of accessibility issues (Levinger et al. 2021).

Aboriginal communities living in urban areas can be supported to maintain nature-based cultural practices. A critically important practice is cultural burning, and fire is needed to maintain the ecological of many Australian ecosystems such as grasslands and heathlands—the absence of fire can lead to significant ecosystem decline. Reintroducing cultural burning to natural ecosystems in urban landscapes (where it can be done safely) can support culture and ecosystem health (Darug Ngurra et al. 2019). Overall, a more comprehensive recognition and representation of Aboriginal perspectives and knowledge (e.g. Caring for Country principles, Woodward et al. 2020) could benefit urban policies by informing sustainable practices in shaping the environment, reducing disadvantage and strengthening the cultural heritage of Australia’s cities (Kingsley et al. 2013, 2021b; Markevych et al. 2017; Porter 2020; Terare et al. 2020; Egerer et al. 2021; Mumaw and Mata 2021). Building from recent developments on how to approach decolonisation of knowledge and planning systems (Nagendra et al. 2018; Wright 2018; Ludwig and Macnaghten 2020; Trisos et al. 2021), and embracing the Caring for Country principles, Australian cities can find ways to decolonise nature-positive cities.

When it comes to nature, what happens on private or public land affects whole ecosystems and communities. Inclusive governance approaches need to also consider and designed to empower communities, particularly civil actors, to be decision makers and carers for nature (Ison and Straw 2020), including private citizens fostering nature on their property to complement government activities (Mumaw and Mata in press). Planning and governing in an equitable, open and therefore inclusive way ensures that all interests, perceptions, expectations and needs are heard and considered (Cohen-Strachan et al. 2019; Fors et al. 2021). At the same time, inclusive governance need to consider ways to be inclusive to ‘more-than-humans’ and give voice and agency to nature (Apfelbeck et al. 2020; Maller 2021; Pineda Pinto et al. 2021). New forms of inclusive governance can build upon and extend existing good practices such as the Yarra River Protection (Wilip-gin Birrarung murron) Act 2017 and Birrarung Council in Melbourne (see Box 2) as well as the Managing with Fire programme in the city of Adelaide or the Chain of Ponds Initiative for Moonee Ponds Creek in Melbourne.

BOX 2: Giving a voice to the river: the Yarra River Protection (Wilip-gin Birrarung murron) Act 2017 and Birrarung Council.

Nature’s multifunctionality is widely recognised and celebrated, from biodiversity habitat, to cooling cities, treating water and air and providing space for social connections and mental and physical health and wellbeing. We need to shift our current monofunctional governance and management arrangements, to develop new approaches that can both accommodate nature’s multifunctionality as well as actually make the most of this multifunctionality (Bush 2020). Participatory approaches are one of these mechanisms. An example is the Victorian Yarra River Protection (Wilip-gin Birrarung murron) Act 2017, which aims to give a voice to nature through the establishment of the Birrarung Council statutory body, with representatives from Traditional Owners, environmental and agricultural industry groups, local community groups (O’Bryan 2019).

Pathway 3: Empower communities to innovate with nature

Urban communities are diverse, and supporting different communities’ innovative practices with nature is an important pathway to inclusive and diverse nature-positive cities that have broad public support and engagement. Importantly, nature is place-based and so are people’s relationships to those places within cities and the biodiversity that constitutes them (Fish et al. 2016; Mattijssen et al. 2020). It is important to ensure that communities of practice that act on protecting, valuing, stewarding nature are not only recognised but further empowered to innovate with nature (Frantzeskaki et al. 2019). Increasingly, professional urban nature-based communities of practice such as arborists, horticulturalists and landscape architects, as well as ecological restoration practitioners, conservationists and residents are innovating to create nature-positive cities. Urban areas allow techniques such as green roofs (Fleck et al. 2022; Wooster et al. 2022), wildlife gardening (Mumaw and Mata in press), chainsaw tree-hollows, ‘planting’ native mistletoe on non-native Plane Trees and detailed modelling of expanded or under-threat habitat areas in cities to be used to support a myriad of urban natures (Griffiths et al. 2018) and renature spaces in the cities.

One advantage of the historically low-density of many Australian cities is that it provides the opportunities for embracing nature and the possibilities of its stewardship across private and public land, such as urban gardening and urban agriculture (Kingsley et al. 2021a). Gardening has traditionally been one of the most popular leisure time activities in Australia, and renewed interest in different forms of gardening (indoor plants, balcony gardening, a renaissance in vegetable gardening) is creating new opportunities for all urban Australians to directly participate in nature-positive activities. Additionally, wildlife gardening has furthered the connection of urban residents with nature: it can function as communities of practice in which residents wildlife garden to support nature stewardship work on public land in partnership with their local governments (Mumaw and Raymond 2021). Learning by doing, involvement of council and community and communication hubs for reminders, motivation and celebration sustain these communities of practice (Mumaw 2017). Wildlife gardening done in partnership between local government and community can provide benefits for biodiversity, personal wellbeing and community capacity building, offering a model for other urban biodiversity conservation initiatives (Mumaw et al. 2019). Such approaches however need to be tailored to the city-specific context taking into account the diversity of small to big cities since people-nature connections are mediated and understood differently across Australian cities (Kendal et al. 2020).

Overall, these diverse communities can be supported by removing regulations that prevent innovation, e.g. on nature-strip (or verge) gardening (Marshall et al. 2020), as well as encourage and province explicit support for culturally and socioeconomically diverse communities to participate in nature-positive practices, such as community gardens, gardening for wildlife programmes and foraging (Oke et al. 2021) (see Box 3).

BOX 3: Gardens for Wildlife Victoria.

In 2016, Gardens for Wildlife Victoria was launched to develop a network of champions from community and government to mentor and learn from each other to codesign and deliver wildlife gardening programmes (Gardens for Wildlife Victoria 2021). The network showcases and promotes principles shown to foster success in wildlife gardening programmes (Mumaw and Bekessy 2017). A core principle is forming community-council partnerships in each local government area—community partners may be volunteer groups or individuals—to develop and run locally sited programs, designed by locals and suited to local aspirations, strengths and species. Another is to target social alongside environmental goals, for example to involve recent immigrants or assist in bushfire recovery. From 2016, the network has spread from 1 to 41 of the state’s 79 local government areas, from inner city to semi-rural townships and from one program to 16 operational, 14 developing and 11 programs in early exploration. The network has over 300 members. Program developers and leaders recount four key themes for what empowers them to persist in their program development activities, themes claimed to underpin empowerment in work-related scenarios (Thomas and Velthouse 1990): having impact, doing something meaningful to you, having the capability to do it and having a choice (Mumaw and Raymond 2021). Examples of working models, trusted relationships, a safe space to think differently and sharing of successes and challenges were key resources provided by the network that stimulated sustained innovation in program development and delivery (Mumaw and Raymond 2021). Importantly, this research found that a vision of wildlife gardening as caring for nature and community, a practice that is feasible and meaningful for residents and connected to their everyday lives and the places they live in, underpinned program development and multiplication (Mumaw and Mata, in press).

The way forward: Lessons from and implications for Australian cities

The COVID-19 pandemic has shone a spotlight on human-nature interactions, inequities of access and other issues of environmental justice (Morse et al. 2020; Diffenbaugh et al. 2020) in cities of all sizes. The pandemic has led to citizens in cities across the world increasing their usage of parks and re-assessing their connection to nature, prioritising access as part of limited freedoms in city lockdowns. Spending time in nature has contributed to stress relief during the social and individual disruptions of the pandemic (Egerer et al. 2022). As the recent Regen Melbourne (2021) report concludes: “it’s not just about building green compromises to existing city areas, but to shift what development looks like in a city, where we put nature back into the heart of how we plan for tomorrow’s urban environment”. Inequity of access to green space has been particularly highlighted during the pandemic, when limitations on travel have restricted urban residents to their local areas; residents without access to local green spaces have reported increased feelings of deprivation (Ugolini et al. 2021). The studies drawing data and observations during the pandemic on how important urban green spaces are as places for human health improvement and sustainability amplify the messages (and key insights from numerous studies before the pandemic) about the multiple benefits deriving from urban nature: for nature/biodiversity, for climate resilience and overall for human and planetary health and pointing to the urban inequalities that manifest via unequal access, uneven or non-intersectional urban design of urban green and blue spaces in cities (Jasinski 2022; Yap et al. 2022). Focussing on provision of access to urban green spaces and opportunities for gardening can be part of a ‘public health strategy, readily accessible to boost societal resilience to disturbances’ (Egerer et al. 2022, p. 1), but a consistent focus on providing opportunities for older citizens and those in lower socioeconomic areas is needed (Levinger et al. 2021). The Covid19 pandemic also revealed the importance of both private green spaces and publicly managed and owned urban ecosystems for dealing with mental distress and improving general well-being of urban citizens (Basu et al. 2021; Wortzel et al. 2021; Noszczyk et al. 2022). Likewise, presenting green infrastructure projects as part of economic stimulus projects, as seen in early responses Covid-19—as seen in an assessment of 100 city response in the first half of 2020, such as the City of Melbourne’s biodiversity planting. The lesson here is prioritising green infrastructure as a job creation exercise, with multiple other social and environmental benefits (Hadfield et al. 2021). Holistic responses, in planning equitable networks of urban green spaces, must also further integrate Aboriginal environmental philosophy and knowledge into mainstream sustainable development practices. We know that the current generation is more likely to live in cities, and will need to connect with nature and with the world’s oldest continuous culture (Miller 2021).

It has been almost 10 years since cities were placed front and centre by the Secretariat on the Convention of Biological Diversity (2012). Since then, nature-based solutions have entered the New Urban Agenda and there have been growing calls to use cities as learning spaces and agents of change to spearhead a transformative agenda in the global biodiversity framework. We add our calls to theirs and here have outlined three key pathways: establish evidence-based planning for nature in cities; strengthen collaborative planning and inclusive governance for nature-based solutions and empower communities to innovate with nature. We have illustrated these with practical, innovative examples. Whilst we focus on Australian cities, the lessons and pathways are broadly applicably globally. Meetings of the Convention on Biological Diversity and UN Convention on Climate Change in 2021 will shape the global responses to biodiversity loss and climate change for the current decade. Cities and residents of cities play a critical role in the response but transformations in the way cities and their residents consider and embrace nature, such as outlined in this article, are urgently needed.

Acknowledgements

NF wants to acknowledge that this work was supported by the US National Science Foundation (NSF) project NATURA. SB was supported by ARC Linkage Grant LP160100324 and an Ian Potter Foundation grant.

Biographies

Niki Frantzeskaki

is a chair professor in regional and metropolitan governance and planning at the Department of Human Geography and Spatial Planning, Faculty of Geosciences, Utrecht University in the Netherlands. Her research interests focus on urban sustainability transitions and transformations with nature-based solutions, urban experimentation and knowledge co-production for better governance and planning of inclusive, livable and resilient cities. She is an adjunct professor at the Centre for Urban Transitions, Swinburne University of Technology, Australia where she was a Research Professor and Director from 2019 to 2021.

Cathy Oke

is a Melbourne Enterprise Principal Fellow in Informed Cities in the Faculty of Architecture Building and Planning and Associate Director (Enterprise and Impact) for Melbourne Centre for Cities. Cathy’s research interests focus on the interaction between urban nature and climate—research, policy and practice—for greater impact in cities. Her research interests focus on the interaction between urban research, policy and practice for greater impact in cities. Cathy is the First Vice President of Local Government’s for Sustainability (ICLEI), and, was a Councillor at the City of Melbourne 2008–2020.

Guy Barnett

is a Principal Research Consultant at the Commonwealth Scientific and Industrial Research Organisation (CSIRO). He has 20 years’ of experience collaborating with community, industry and government on the sustainability, liveability and resilience of cities. His current interests are climate change adaptation and the role of ‘urban living labs’ as place-based, multi-sectoral partnerships for de-risking and accelerating urban innovation and experimentation.

Sarah Bekessy

is a professor and leads the ICON Science research group at RMIT University which uses interdisciplinary approaches to solve complex biodiversity conservation problems. She is particularly interested in understanding the role of human behaviour in conservation and in designing cities to encourage ‘everyday nature’ experiences. She co-developed the Biodiversity Sensitive Urban Design protocol that has now been used by numerous developers, governments and non-government organisations to design innovative urban biodiversity strategies.

Judy Bush

is a Lecturer in Urban Planning at the University of Melbourne. Her research focuses on urban environmental policy and governance, including governance and policy approaches for nature-based solutions, biodiversity, urban ecology and climate change perspectives.

James Fitzsimons

is Director of Conservation and Science with The Nature Conservancy Australia, where he oversees the organisation’s conservation planning, policy, science and implementation functions. He has previously worked for government agencies and non-government organisations in protected area policy and establishment. He is an Adjunct Professor at the School of Life and Environmental Sciences, Deakin University and has a research background in conservation policy, protected area network establishment, private land conservation and ecology.

Maria Ignatieva

is a Professor in Landscape Architecture (the University of Western Australia). For almost thirty years, she has been dedicated to working in academia in five countries (Sweden, New Zealand, USA and Russia and now in Australia), teaching and researching as a full-time tenured academic in landscape architecture programmes. Dr. Ignatieva’s research is in urban ecology (urban biodiversity and design), history of landscape architecture and historical gardens restoration. She is the President of URBIO (Urban Biodiversity and Design international network). Maria has several realised landscape architecture projects in Russia, Sweden, New Zealand and Australia.

Dave Kendal

is a lecturer in environmental management in the school of geography, planning and spatial sciences in the University of Tasmania. Before joining The University of Tasmania, Dave was a postdoc at the University of Melbourne, and before that a researcher at the Australian Centre for Urban Ecology, a division of the Royal Botanic Gardens Victoria.

Jonathan Kingsley

is a Senior Lecturer in Health Promotion (Swinburne University of Technology). Dr. Kingsley has nearly two decades of experience of working in Aboriginal Community Controlled Health Organisations, government bodies, academic institutes and NGO’s across Australia in the public health and community development field. Jonathan sees our natural environment as central to health and having the capacity to bridge health inequalities (the basis of his Honours, Masters, Ph.D. and previous Visiting Academic position at Cambridge University).

Laura Mumaw

is a research associate in the Centre for Urban Research at RMIT University. Dr. Mumaw’s research focuses on biodiversity stewardship, urban nature and wellbeing, and how cities can improve their social and ecological wellbeing through new human-nature relationships and understanding. To this she brings over 30 years industry experience in nature conservation and community engagement. She is a current board member of Gardens for Wildlife Victoria.

Alessandro Ossola

is a Research Coordinator and Research Fellow at Macquarie University in Sydney, Australia. He is also an Honorary Research Fellow within the School of Ecosystem and Forest Science at the University of Melbourne, Australia. Dr. Ossola is a former National Academy of Sciences, Engineering and Medicine NRC Associate within the National Risk Management Research Laboratory of US-EPA in Cincinnati, Ohio, USA. He has worked in numerous projects funded by the Australian Research Council, the US National Science Foundation and numerous industry partners, expanding his professional network throughout four continents.

Footnotes

Publisher's Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Contributor Information

Niki Frantzeskaki, Email: n.frantzeskaki@uu.nl.

Cathy Oke, Email: cathy.oke@unimelb.edu.au.

Guy Barnett, Email: guy.barnett@csiro.au.

Sarah Bekessy, Email: sarah.bekessy@rmit.edu.au.

Judy Bush, Email: judy.bush@unimelb.edu.au.

James Fitzsimons, Email: jfitzsimons@tnc.org.

Maria Ignatieva, Email: maria.ignatieva@uwa.edu.au.

Dave Kendal, Email: dave.kendal@utas.edu.au.

Jonathan Kingsley, Email: jkingsley@swin.edu.au.

Laura Mumaw, Email: laura.mumaw@rmit.edu.au.

Alessandro Ossola, Email: aossola@ucdavis.edu, Email: alessandro.ossola@mq.edu.au, Email: alessandro.ossola@unimelb.edu.au.

References

  1. Alexandra J, Norman B. The city as forest—Integrating living infrastructure, climate conditioning and urban forestry in Canberra. Australia. Sustainable Earth. 2020 doi: 10.1186/s42055-020-00032-3. [DOI] [Google Scholar]
  2. Allan C, Ison RL, Colliver R, Mumaw L, Mackay M, Perez-mujica L, Wallis P. Jumping off the treadmill: Transforming NRM to systemic governing with systemic co-inquiry. Policy Studies. 2020;41:350–371. doi: 10.1080/01442872.2020.1726312. [DOI] [Google Scholar]
  3. Allison L. The history and future of Westgate Park. Planning News. 2018;44:22–23. doi: 10.3316/informit.787310325113784. [DOI] [Google Scholar]
  4. Almenar JB, Elliot T, Rugani B, Philippe B, Gutierrez TN, Sonnemann G, Geneletti D. Nexus between nature-based solutions, ecosystem services and urban challenges. Land Use Policy. 2021 doi: 10.1016/j.landusepol.2020.104898. [DOI] [Google Scholar]
  5. Apfelbeck B, Snep RPH, Hauck TE, Ferguson J, Holy M, Jakoby C, Scott MacIvor J, Schär L, et al. Designing wildlife-inclusive cities that support human-animal co-existence. Landscape and Urban Planning. 2020;200:103817. doi: 10.1016/j.landurbplan.2020.103817. [DOI] [Google Scholar]
  6. Australian Academy of Science. 2021. The risks to Australia of a 3 °C warmer world. Retrieved 13 August, 2021, from http://www.science.org.au/warmerworld.
  7. Basu M, Dasgupta R, Kumar P, Dhyani S. Home gardens moderate the relationship between covid-19-induced stay-at-home orders and mental distress: A case study with urban residents of India. Environmental Research Communications. 2021 doi: 10.1088/2515-7620/ac2ab2. [DOI] [Google Scholar]
  8. Boer MM, Resco de Dios V, Bradstock RA. Unprecedented burn area of Australian mega forest fires. 2020. Nature Climate Change. 2020;10:171–172. doi: 10.1038/s41558-020-0716-1. [DOI] [Google Scholar]
  9. Bohnet I. Integrating social and ecological knowledge for planning sustainable land- and sea-scapes: Experiences from the Great Barrier Reef region, Australia. Landscape Ecology. 2010;25:1201–1218. doi: 10.1007/s10980-010-9504-z. [DOI] [Google Scholar]
  10. Bull JW, Suttle KB, Gordon A, Singh NJ, Milner-Gulland EJ. Biodiversity offsets in theory and practice. Oryx. 2013;47:369–380. doi: 10.1017/S003060531200172X. [DOI] [Google Scholar]
  11. Buse CG, Oestreicher JS, Ellis NR, Patrick R, Brisbois B, Jenkins AP, McKellar K, Kingsley J, et al. Public health guide to field developments linking ecosystems, environments and health in the Anthropocene. Journal of Epidemiology and Community Health. 2018;72:420–425. doi: 10.1136/jech-2017-210082. [DOI] [PubMed] [Google Scholar]
  12. Bush J. The role of local government greening policies in the transition towards nature-based cities. Environmental Innovation and Societal Transitions. 2020;35:35–44. doi: 10.1016/j.eist.2020.01.015. [DOI] [Google Scholar]
  13. Bush J, Ashley G, Foster B, Hall G. Integrating green infrastructure into urban planning: Developing Melbourne’s Green Factor Tool. Urban Planning. 2021 doi: 10.17645/up.v6i1.3515. [DOI] [Google Scholar]
  14. Champness BS, Palmer GC, Fitzsimons JA. Bringing the city to the country: Relationships between streetscape vegetation type and bird assemblages in a major regional centre. Journal of Urban Ecology. 2019;5:juz018. doi: 10.1093/jue/juz018. [DOI] [Google Scholar]
  15. Clark C, Ordóñez C, Livesley SJ. Private tree removal, public loss: Valuing and enforcing existing tree protection mechanisms is the key to retaining urban trees on private land. Landscape and Urban Planning. 2020 doi: 10.1016/j.landurbplan.2020.103899. [DOI] [Google Scholar]
  16. Clark WC, Harley AG. Sustainability science: Toward a synthesis. Annual Review of Environment and Resources. 2020;45:331–386. doi: 10.1146/annurev-environ-012420-043621. [DOI] [Google Scholar]
  17. Coenen L, Davidson K, Frantzeskaki N, Grenfell M, Hakansson I, Hartigan M. Metropolitan governance in action? Learning from metropolitan Melbourne’s Urban Forest Strategy. Australian Planner. 2020;56:144–148. doi: 10.1080/07293682.2020.1740286. [DOI] [Google Scholar]
  18. Cohen-Shacham E, Andrade A, Dalton J, Dudley N, Jones M, Kumar C, Maginnis S, Maynard S, et al. Core principles for successfully implementing and upscaling Nature-based Solutions. Environmental Science and Policy. 2019;98:20–29. doi: 10.1016/j.envsci.2019.04.014. [DOI] [Google Scholar]
  19. Coutts AM, Tapper NJ, Beringer J, Loughnan M, Demuzere M. Watering our cities: The capacity for Water Sensitive Urban Design to support urban cooling and improve human thermal comfort in the Australian context. Progress in Physical Geography. 2013;37:2–28. doi: 10.1177/0309133312461032. [DOI] [Google Scholar]
  20. Currey K, Kendal D, van der Ree R, Lentini PE. Land manager perspectives on conflict mitigation strategies for urban flying-fox camps. Diversity. 2018;10:1–15. doi: 10.3390/D10020039. [DOI] [Google Scholar]
  21. Daniels P, ElBaghdadi O, Desha C, Matthews T. Evaluating net community benefits of integrating nature within cities. Sustainable Earth. 2020 doi: 10.1186/s42055-020-00025-2. [DOI] [Google Scholar]
  22. Davidson K, Gleeson B. New socio-ecological imperatives for cities: Possibilities and dilemmas for Australian Metropolitan Governance. Urban Policy and Research. 2018;36:230–241. doi: 10.1080/08111146.2017.1354848. [DOI] [Google Scholar]
  23. DELWP. 2016. Melbourne Strategic Assessment. The State of Victoria Department of Environment, Land Water and Planning, Melbourne, Australia.
  24. Diffenbaugh NS, Field CB, Appel EA, Azevedo IL, Baldocchi DD, Burke M, Burney JA, Ciais P, et al. The COVID-19 lockdowns: A window into the Earth System. Nature Reviews Earth & Environment. 2020;1:470–481. doi: 10.1038/s43017-020-0079-1. [DOI] [Google Scholar]
  25. Dorst H, van der Jagt A, Raven R, Runhaar H. Urban greening through nature-based solutions—Key characteristics of an emerging concept. Sustainable Cities and Society. 2019 doi: 10.1016/j.scs.2019.101620. [DOI] [Google Scholar]
  26. Dumitru A, Frantzeskaki N, Collier M. Identifying principles for the design of robust impact evaluation frameworks for nature-based solutions in cities. Environmental Science and Policy. 2020;112:107–116. doi: 10.1016/j.envsci.2020.05.024. [DOI] [Google Scholar]
  27. Egerer M, Haase D, McPhearson T, Frantzeskaki N, Nagendra H, Andersson E, Nagendra H, Ossola A. Urban change as an untapped opportunity for climate adaptation. Npj Urban Sustainability. 2021 doi: 10.1038/s42949-021-00024-y. [DOI] [Google Scholar]
  28. Egerer M, Lin B, Kingsley J, Marsh P, Diekmann L, Ossola A. Gardening can relieve human stress and boost nature connection during the COVID-19 pandemic. Urban Forestry & Urban Greening. 2022;68:127483. doi: 10.1016/j.ufug.2022.127483. [DOI] [PMC free article] [PubMed] [Google Scholar]
  29. Fasternrath S, Coenen L. Future-proof cities through governance experiments? Insights from the Resilient Melbourne Strategy. Regional Studies. 2021;55:138–149. doi: 10.1080/00343404.2020.1744551. [DOI] [Google Scholar]
  30. Fish R, Church A, Winter M. Conceptualising cultural ecosystem services: A novel framework for research and critical engagement. Ecosystem Services. 2016;21:208–217. doi: 10.1016/j.ecoser.2016.09.002. [DOI] [Google Scholar]
  31. Fitzsimons JA, Antos MJ, Palmer GC. When more is less: Urban remnants support high bird abundance but diversity varies. Pacific Conservation Biology. 2011;17:97–109. doi: 10.1071/PC110097. [DOI] [Google Scholar]
  32. Fitzsimons J, Wescott G. The role and contribution of private land in Victoria to biodiversity conservation and the protected area system. Australian Journal of Environmental Management. 2001;8:142–157. doi: 10.1080/14486563.2001.10648524. [DOI] [Google Scholar]
  33. Fleck R, Gill RL, Saadeh S, Pettit T, Wooster E, Torpy F, Irga P. Urban green roofs to manage rooftop microclimates: A case study from Sydney, Australia. Building and Environment. 2022 doi: 10.1016/j.buildenv.2021.108673. [DOI] [Google Scholar]
  34. Fors H, Hagemann FA, Sang ÅO, Randrup TB. Striving for inclusion—A systematic review of long-term participation in strategic management of urban green spaces. Frontiers in Sustainable Cities. 2021 doi: 10.3389/frsc.2021.572423. [DOI] [Google Scholar]
  35. Frantzeskaki N, McPhearson T, Collier M, Kendal D, Bulkeley H, Dumitru A, Walsh C, Noble K, van Wyk E, Pinter L, Ordonez C, Oke C, Elmqvist T. Nature-based solutions for urban climate change adaptation: linking the science, policy and practice communities for evidence-based decision-making. Bioscience. 2019;69:455–566. doi: 10.1093/biosci/biz042. [DOI] [Google Scholar]
  36. Frantzeskaki, N., P. Vandergert, S. Connop, K. Schipper, I. Zwierzchowska, M. Collier, and M. Lodder. 2020. Examining the policy needs for implementing nature-based solutions: Findings for citywide transdisciplinary experiences in Glasgow, Genk and Poznan. Land Use Policy 96: 104688. 10.1016/j.landusepol.2020.104688.
  37. Gardens for Wildlife Victoria. 2021. Our Work. Retrieved 7 October, 2021, from https://gardensforwildlifevictoria.com/our-work/ (Web Material)
  38. Garrard GE, Williams NSG, Mata L, Thomas J, Bekessy SA. Biodiversity sensitive urban design. Conservation Letters. 2018;11:e12411. doi: 10.1111/conl.12411. [DOI] [Google Scholar]
  39. Gehl J. Cities for People. Washington: Island Press; 2010. [Google Scholar]
  40. Griffiths SR, Lentini PE, Semmens K, Watson SJ, Lumsden LF, Robert KA. Chainsaw-carved cavities better mimic the thermal properties of natural tree hollows than nest boxes and log hollows. Forests. 2018;9:235. doi: 10.3390/f9050235. [DOI] [Google Scholar]
  41. Hadfield P, Oke C, Verbeeck J. Regional research and innovation for city climate action: Global synthesis report. Connected Cities Lab, the University of Melbourne. 2021 doi: 10.26188/14743125. [DOI] [Google Scholar]
  42. Hartigan M, Fitzsimons J, Grenfell M, Kent T. Developing a metropolitan-wide urban forest strategy for a large, expanding and densifying capital city: Lessons from Melbourne, Australia. Land. 2021;10:809. doi: 10.3390/land10080809. [DOI] [Google Scholar]
  43. Heikkinen M, Ylä-Anttila T, Juhola S. Incremental, reformistic or transformational: What kind of change do C40 cities advocate to deal with climate change? Journal of Environmental Policy and Planning. 2019;21:90–103. doi: 10.1080/1523908X.2018.1473151. [DOI] [Google Scholar]
  44. Hobbie SE, Grimm NB. Nature-based approaches to managing climate change impacts in cities. Philosophical Transactions of the Royal Society b: Biological Sciences. 2020;375:20190124. doi: 10.1098/rstb.2019.0124. [DOI] [PMC free article] [PubMed] [Google Scholar]
  45. Hockings M, Dudley N, Elliot W, Ferreira NM, MacKinnon K, Pasha MKS, Phillips A, Stolton S, et al. COVID-19 and protected and conserved areas. Parks. 2020;26:7–24. doi: 10.2305/IUCN.CH.2020.PARKS-26-1MH.en. [DOI] [Google Scholar]
  46. Ignatieva M. Design and future of urban biodiversity. In: Müller N, Werner P, Kelcey J, editors. Urban Biodiversity and Design. London: Blackwells Publishing Ltd.; 2010. pp. 118–144. [Google Scholar]
  47. Ignatieva M. Biodiversity-friendly designs in cities and towns: Towards a global biodiversinesque style. In: Ossola A, Niemelä J, editors. Urban Biodiversity: From Research to Practice. London: Francis and Taylor; 2018. pp. 216–235. [Google Scholar]
  48. Ignatieva, M., C. Meurk, M. van Roon, R. Simcock, and G. Stewart. 2008. Urban Greening Manual. How to put nature in our neighbourhoods: application of Low Impact Urban Design and Development (LIUDD) principles, with a biodiversity focus, for New Zealand developers and homeowners. Landcare Research Sciences series no.35. Lincoln, N.Z.: Manaaki Whenua Press.
  49. Ignatieva M, Haase D, Dushkova D, Haase A. Lawns in cities: From a globalised urban green space phenomenon to sustainable nature-based solutions. Land. 2020 doi: 10.3390/land9030073. [DOI] [Google Scholar]
  50. Ison R, Straw E. The hidden power of systems thinking—Governance in a climate change emergency. Routledge. 2020 doi: 10.4324/9781351026901. [DOI] [Google Scholar]
  51. Jasinski A. COVID-19 pandemic is challenging some dogmas of modern urbanism. Cities. 2022 doi: 10.1016/j.cities.2021.103498. [DOI] [PMC free article] [PubMed] [Google Scholar]
  52. Juhola S. Planning for a green city: The Green Factor tool. Urban Forestry and Urban Greening. 2018;34:254–258. doi: 10.1016/j.ufug.2018.07.019. [DOI] [Google Scholar]
  53. Kabisch N, van den Bosch M, Lafortezza R. The health benefits of nature-based solutions to urbanization challenges for children and the elderly—A systematic review. Environmental Research. 2017;159:362–373. doi: 10.1016/j.envres.2017.08.004. [DOI] [PubMed] [Google Scholar]
  54. Kalliolevo H, Gordon A, Sharma R, Bull JW. Biodiversity offsetting can relocate nature away from people: An empirical case study in Western Australia. Conservation Science and Practice. 2021;3:e512. doi: 10.1111/csp2.512. [DOI] [Google Scholar]
  55. Keeler BL, Hamel P, McPhearson T, Hamann MH, Donahue ML, Meza Prado KA, Arkema KK, Bratman GN, et al. Social-ecological and technological factors moderate the value of urban nature. Nature Sustainability. 2019;2:29–38. doi: 10.1038/s41893-018-0202-1. [DOI] [Google Scholar]
  56. Kendal D, Egerer M, Byrne JA, Jones J, Marsh P, Threlfall CG, Allegretto G, Kaplan H, Nguyen HD, Pearson S, Wright A, Flies EJ. City-size bias in knowledge on the effects of urban nature on people and biodiversity. Environmental Research Letters. 2020;15:124035. doi: 10.1088/1748-9326/abc5e4. [DOI] [Google Scholar]
  57. Kingsley J, Townsend M, Henderson-Wilson C, Bolam B. Developing an exploratory framework linking Australian Aboriginal peoples' connection to country and concepts of wellbeing. International Journal of Environmental Research and Public Health. 2013;10:678–698. doi: 10.3390/ijerph10020678. [DOI] [PMC free article] [PubMed] [Google Scholar]
  58. Kingsley J, Monika E, Sonia N, Keniger L, Pettitt P, Frantzeskaki N, Gray T, Ossola A, et al. Urban agriculture as a nature-based solution to address socio-ecological challenges in Australian Cities. Urban Forestry & Urban Greening. 2021;60:127059. doi: 10.1016/j.ufug.2021.127059. [DOI] [Google Scholar]
  59. Kingsley J, Munro-Harrison E, Jenkins A, Thorpe A. Developing a framework identifying the outcomes, principles and enablers of ‘gathering places’: Perspectives from Aboriginal people in Victoria. Australia. Social Science & Medicine. 2021;283:114217. doi: 10.1016/j.socscimed.2021.114217. [DOI] [PubMed] [Google Scholar]
  60. Kirk H, Garrand GE, Croeser T, Backstrom A, Berthon K, Furlong C, Hurley J, Thomas F, Webb A, Bekessy SA. Building biodiversity into the urban fabric: A case study in applying Biodiversity Sensitive Urban Design (BSUD) Urban Forestry and Urban Greening. 2021 doi: 10.1016/j.ufug.2021.127176. [DOI] [Google Scholar]
  61. Kolokotsa D, Lilli AA, Lilli M, Nikolaidis NP. On the impact of nature-based solutions on citizens’ health and well-being. Energy and Buildings. 2020;229:110527. doi: 10.1016/j.enbuild.2020.110527. [DOI] [Google Scholar]
  62. Levinger PE, Cerin CM, Hill KD. Older people and nature: The benefits of outdoors, parks and nature in light of COVID-19 and beyond– where to from here? International Journal of Environmental Health Research. 2021 doi: 10.1080/09603123.2021.1879739. [DOI] [PubMed] [Google Scholar]
  63. Lin BB, Ossola A, Ripple WJ, Alberti M, Andersson E, Bai X, Dobbs C, Elmqvist T, et al. Integrating solutions to transform cities for climate change. The Lancet Planetary Health. 2021;5:e479–486. doi: 10.1016/S2542-5196(21)00135-2. [DOI] [PubMed] [Google Scholar]
  64. Ludwig D, Macnaghten P. Traditional ecological knowledge in innovation governance: A framework for responsible and just innovation. Journal of Responsible Innovation. 2020;7:26–44. doi: 10.1080/23299460.2019.1676686. [DOI] [Google Scholar]
  65. Malekpour S, Tawfik S, Chesterfield C. Designing collaborative governance for nature-based solutions. Urban Forestry & Urban Greening. 2021;62:127177. doi: 10.1016/j.ufug.2021.127177. [DOI] [Google Scholar]
  66. Maller C. Re-orienting nature-based solutions with more-than-human thinking. Cities. 2021;113:103155. doi: 10.1016/j.cities.2021.103155. [DOI] [Google Scholar]
  67. Maron, M., C.D. Ives, H. Kujala, J.W. Bull, F.J. Maseyk, S. Bekessy, A. Gordon, J.E. Watson, et al. 2016. Taming a wicked problem: Resolving controversies in biodiversity offsetting. BioScience 66: 489–498. 10.1093/biosci/biw038. [DOI]
  68. Markevych I, Schoierer J, Hartig T, Chudnovsky A, Hystad P, Dzhambov AM, De Vries S, Triguero-Mas M, et al. Exploring pathways linking greenspace to health: Theoretical and methodological guidance. Environmental Research. 2017;158:301–317. doi: 10.1016/j.envres.2017.06.028. [DOI] [PubMed] [Google Scholar]
  69. Maron M, Ives CD, Kujala H, Bull JW, Maseyk FJ, Bekessy S, Gordon A, Watson JE, et al. Taming a wicked problem: Resolving controversies in biodiversity offsetting. BioScience. 2016;66:489–498. doi: 10.1093/biosci/biw038. [DOI] [Google Scholar]
  70. Marshall AJ, Grose MJ, Williams NS. Of Mowers and Growers: Perceived social norms strongly influence verge gardening, a distinctive civic greening practice. Landscape and Urban Planning. 2020;198:103795. doi: 10.1016/j.landurbplan.2020.103795. [DOI] [Google Scholar]
  71. Mata L, Ramalho CE, Kennedy J, Parris KM, Valentine L, Miller M, Bekessy S, Hurley S, et al. Bringing nature back into cities. People and Nature. 2020;2:350–368. doi: 10.1002/pan3.10088. [DOI] [Google Scholar]
  72. Mattijssen TJM, Ganzevoort W, van den Born RJG, Arts BJM, Breman BC, Buijs AE, van Dam RI, Elands BHM, de Groot WT, Knippenberg LWJ. Relational values of nature: Leverage points for nature policy in Europe. Ecosystems and People. 2020;16(1):402–410. doi: 10.1080/26395916.2020.1848926. [DOI] [Google Scholar]
  73. Matsler MA. Making ‘green’ fit in a ‘grey’ accounting system: The institutional knowledge system challenges of valuing urban nature as infrastructural assets. Environmental Science & Policy. 2019;99:160–168. doi: 10.1016/j.envsci.2019.05.023. [DOI] [Google Scholar]
  74. Mazzucato M. Mission-oriented innovation policies: Challenges and opportunities. Industrial and Corporate Change. 2018;27:803–815. doi: 10.1093/icc/dty034. [DOI] [Google Scholar]
  75. McPhearson T, Pickett ST, Grimm NB, Niemelä J, Alberti M, Elmqvist T, Weber C, Haase D, et al. Advancing Urban Ecology toward a Science of Cities. BioScience. 2016;66:198–212. doi: 10.1093/biosci/biw002. [DOI] [Google Scholar]
  76. Melourne, R. 2021. Towards a regenerative Melbourne: Embracing Doughnut Economics to create a new compass for Melbourne. Retrieved 8 October, 2021, from https://static1.squarespace.com/static/5f684d39e08c862107326d43/t/60881373cec2c10c704f7b82/1619530661887/Towards+a+Regenerative+Melbourne+Report+April+2021.pdf
  77. Merçon J, Vetter S, Tengö M, Cocks M, Balvanera P, Rosell JA, Ayala-Orozco B. From local landscapes to international policy: Contributions of the biocultural paradigm to global sustainability. Global Sustainability. 2019 doi: 10.1017/sus.2019.4. [DOI] [Google Scholar]
  78. Miller, M. 2021. The future of our cities is Indigenous. https://pursuit.unimelb.edu.au/articles/the-future-of-our-cities-is-indigenous
  79. Moloney S, Doyon A. The Resilient Melbourne experiment: Analyzing the conditions for transformative urban resilience implementation. Cities. 2021;110:103017. doi: 10.1016/j.cities.2020.103017. [DOI] [Google Scholar]
  80. Morse JW, Gladkikh TM, Hackenburg DM, Gould RK. COVID-19 and human-nature relationships: Vermonters’ activities in nature and associated nonmaterial values during the pandemic. PLoS ONE. 2020;15:e0243697. doi: 10.1371/journal.pone.0243697. [DOI] [PMC free article] [PubMed] [Google Scholar]
  81. Mumaw L. Transforming urban gardeners into land stewards. Journal of Environmental Psychology. 2017;52:92–103. doi: 10.1016/j.jenvp.2017.05.003. [DOI] [Google Scholar]
  82. Mumaw L, Mata L. Wildlife gardening: An urban nexus of social and ecological relationships. EcoEvoRxiv. 2021 doi: 10.32942/osf.io/9rkhm. [DOI] [Google Scholar]
  83. Mumaw, L., and L. Mata. (in press). Wildlife gardening: An urban nexus of social and ecological relationships. Frontiers in Ecology and the Environment.
  84. Mumaw L, Bekessy S. Wildlife gardening for collaborative public–private biodiversity conservation. Australasian Journal of Environmental Management. 2017;24(3):242–260. doi: 10.1080/14486563.2017.1309695. [DOI] [Google Scholar]
  85. Mumaw LM, Raymond CM. A framework for catalysing the rapid scaling of urban biodiversity stewardship programs. Journal of Environmental Management. 2021;292:112745. doi: 10.1016/j.jenvman.2021.112745. [DOI] [PubMed] [Google Scholar]
  86. Mumaw LM, Maller C, Bekessy S. Assessing and strengthening community capacity building in urban biodiversity conservation programs. Cities and the Environment. 2019;12:4. [Google Scholar]
  87. Nagendra H, Bai X, Brondizio ES, Lwasa S. The urban south and the predicament of global sustainability. Nature Sustainability. 2018;1:341–349. doi: 10.1038/s41893-018-0101-5. [DOI] [Google Scholar]
  88. Ngurra D, Dadd L, Glass P, Scott R, Graham M, Judge S, Hodge P, Suchet-Pearson S. Yanama Budyari Gumada: Reframing the urban to care as Darug Country in Western Sydney. Australian Geographer. 2019;50:279–293. doi: 10.1080/00049182.2019.1601150. [DOI] [Google Scholar]
  89. Norman B, Newman P, Steffen W. Apocalypse now: Australian bushfires and the future of urban settlements. Npj Urban Sustainability. 2021 doi: 10.1038/s42949-020-00013-7. [DOI] [Google Scholar]
  90. Noszczyk T, Gorzelany J, Kukulska-Koziet A, Hernik J. The impact of COVID-19 pandemic on the importance of urban green spaces to the public. Land Use Policy. 2022 doi: 10.1016/j.landusepol.2021.105925. [DOI] [PMC free article] [PubMed] [Google Scholar]
  91. Oke C, Bekessy S, Frantzeskaki N, Bush J, Fitzsimons J, Garrard GE, Grenfell M, Harrison L, et al. Cities should respond to the biodiversity extinction crisis. Urban Sustainability. 2021;1:1–4. doi: 10.1038/s42949-020-00010-w. [DOI] [Google Scholar]
  92. O’Bryan K. The changing face of river management in Victoria: The Yarra River Protection (Wilip-gin Birrarung murron) Act 2017 (Vic) Water International. 2019;44:769–785. doi: 10.1080/02508060.2019.1616370. [DOI] [Google Scholar]
  93. Ordóñez-Barona C, Bush J, Hurley J, Amati M, Juhola S, Frank S, Ritchie M, Clark C, et al. International approaches to protecting and retaining trees on private urban land. Journal of Environmental Management. 2021;285:112081. doi: 10.1016/j.jenvman.2021.112081. [DOI] [PubMed] [Google Scholar]
  94. Ossola A, Lin BB. Making nature-based solutions climate-ready for the 50 °C world. 2021. Environmental Science and Policy. 2021;123:151–159. doi: 10.1016/j.envsci.2021.05.026. [DOI] [Google Scholar]
  95. Padma P, Ramakrishna S, Rasoolimanesh SM. Nature-based solutions in tourism: A review of the literature and conceptualization. Journal of Hospitality & Tourism Research. 2020 doi: 10.1177/1096348019890052. [DOI] [Google Scholar]
  96. Palmer GC, Fitzsimons JA, Antos MJ, White JG. Determinants of native avian richness in suburban remnant vegetation: Implications for conservation planning. Biological Conservation. 2008;141:2329–2341. doi: 10.1016/j.biocon.2008.06.025. [DOI] [Google Scholar]
  97. Pineda Pinto M, Frantzeskaki N, Nygaard CA. The potential of nature-based solutions to deliver ecologically just cities: Lessons for research and urban planning from a systematic literature review. Ambio. 2021 doi: 10.1007/s13280-021-01553-7. [DOI] [PMC free article] [PubMed] [Google Scholar]
  98. Potter E. Contesting imaginaries in the Australian city: Urban planning, public storytelling and the implications for climate change. Urban Studies. 2020;57:1536–1552. doi: 10.1177/0042098018821304. [DOI] [Google Scholar]
  99. Prado JA, Puszka H, Forman A, Cooke B, Fitzsimons JA. Trends and values of ‘Land for Wildlife’ programs for private land conservation. Ecological Management & Restoration. 2018;19:136–146. doi: 10.1111/emr.12308. [DOI] [Google Scholar]
  100. Raworth K. A Doughnut for the Anthropocene: Humanity's compass in the 21st century. The Lancet Planetary Health. 2017;1:e48–e49. doi: 10.1016/S2542-5196(17)30028-1. [DOI] [PubMed] [Google Scholar]
  101. Robertson SA. Rethinking relational ideas of place in more-than-human cities. Geography Compass. 2018 doi: 10.1111/gec3.12367. [DOI] [Google Scholar]
  102. Sachs JD, Schmidt-Traub G, Mazzucato M, Messner D, Nakicenovic N, Rockström J. Six Transformations to achieve the Sustainable Development Goals. Nature Sustainability. 2019;2:805–814. doi: 10.1038/s41893-019-0352-9. [DOI] [Google Scholar]
  103. Secretariat of the Convention on Biological Diversity. 2012. Cities and Biodiversity Outlook. http://www.cbd.int/en/subnational/partners-and-initiatives/cbo
  104. Shade C, Kremer P, Rockwell JS, Henderson KG. The effects of urban development and current green infrastructure policy on future climate change resilience. Ecology and Society. 2020;25:37. doi: 10.5751/ES-12076-250437. [DOI] [Google Scholar]
  105. Sharifi F, Nygaard A, Stone WM, Levin I. Accessing green space in Melbourne: Measuring inequality and household mobility. Landscape and Urban Planning. 2021;207:104004. doi: 10.1016/j.landurbplan.2020.104004. [DOI] [Google Scholar]
  106. Sharifi F, Levin I, Stone WM, Nygaard A. Green space and subjective well-being in the Just City: A scoping review. Environmental Science & Policy. 2021;120:118–126. doi: 10.1016/j.envsci.2021.03.008. [DOI] [Google Scholar]
  107. Terare M, Rawsthorne M. Country is yarning to me: Worldview, health and well-being amongst Australian first nations people. The British Journal of Social Work. 2020;50:944–960. doi: 10.1093/bjsw/bcz072. [DOI] [Google Scholar]
  108. The Nature Conservancy and Resilient Melbourne. 2019. Living Melbourne: Our Metropolitan Urban Forest. The Nature Conservancy and Resilient Melbourne, Melbourne. Retrieved 7 October, 2021 from https://resilientmelbourne.com.au/living-melbourne/
  109. Thomas KW, Velthouse BA. Cognitive elements of empowerment: An “interpretive” model of intrinsic task motivation. Academy of Management Review. 1990;15:666–681. doi: 10.5465/amr.1990.4310926. [DOI] [Google Scholar]
  110. Threlfall C, Marzinelli EM, Ossola A, Bugnot A, Bishop M, Lowe L, Imberger S, Myers S, et al. Towards cross-realm management of coastal urban ecosystems. Frontiers in Ecology and the Environment. 2021;19:225–233. doi: 10.1002/fee.2323. [DOI] [Google Scholar]
  111. Trisos CH, Auerbach J, Katti M. Decoloniality and anti-oppressive practices for a more ethical ecology. Nature Ecology and Evolution. 2021;5:1205–1212. doi: 10.1038/s41559-021-01460-w. [DOI] [PubMed] [Google Scholar]
  112. Tzoulas K, Galan J, Venn S, Dennis M, Pedroli B, Mishra H, Haase D, Pauleit S, et al. A conceptual model of the social-ecological system of nature-based solutions in urban environments. Ambio. 2021;50:335–345. doi: 10.1007/s13280-020-01380-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
  113. Ugolini F, Massetti L, Calaza-Martínez P, Cariñanos P, Dobbs C, Ostoic SK, Marin AM, Pearlmutter D, et al. Effects of the COVID-19 pandemic on the use and perceptions of urban green space: An international exploratory study. Urban Forestry and Urban Greening. 2020;56:126888. doi: 10.1016/j.ufug.2020.126888. [DOI] [PMC free article] [PubMed] [Google Scholar]
  114. Ugolini F, Massetti L, Pearlmutter D, Sanesi G. Usage of urban green space and related feelings of deprivation during the COVID-19 lockdown: Lessons learned from an Italian case study. Land Use Policy. 2021;105:105437. doi: 10.1016/j.landusepol.2021.105437. [DOI] [PMC free article] [PubMed] [Google Scholar]
  115. United Nations Environment Programme (UNEP) 2021. Making Peace with Nature: A scientific blueprint to tackle the climate, biodiversity and pollution emergencies. Nairobi. Retrieved 13 August, 2021, from https://www.unep.org/resources/making-peace-nature.
  116. Voskamp IM, de Luca C, Polo-Ballinas MB, Hulsman H, Brolsma R. Nature-based solutions tools for planning urban climate adaptation: State of the art. Sustainability. 2021;13:6381. doi: 10.3390/su13116381. [DOI] [Google Scholar]
  117. White JG, Antos MJ, Fitzsimons JA, Palmer GC. Non-uniform bird assemblages in urban environments: The influence of streetscape vegetation. Landscape and Urban Planning. 2005;71:123–135. doi: 10.1016/j.landurbplan.2004.02.006. [DOI] [Google Scholar]
  118. Williams NSG, Bathgate R, Farrell C, Lee KE, Szota C, Bush J, Johnson KA, Miller RE, et al. Ten years of greening a wide brown land: A synthesis of Australian green roof research and roadmap forward. Urban Forestry and Urban Greening. 2021;62:127179. doi: 10.1016/j.ufug.2021.127179. [DOI] [Google Scholar]
  119. Wintle BA, Kujala H, Whitehead A, Cameron A, Veloz S, Kukkala A, Moilanen A, Gordon A, et al. Global synthesis of conservation studies reveals the importance of small habitat patches for biodiversity. Proceedings of the National Academy of Sciences. 2018;116:13051. doi: 10.1073/pnas.1813051115. [DOI] [PMC free article] [PubMed] [Google Scholar]
  120. Wolf KL, Lam ST, McKeen JK, Richardson GRA, Bosch MD, Bardekjian AC. Urban trees and human health: A scoping review. International Journal of Environmental Research and Public Health. 2020;17:1–30. doi: 10.3390/ijerph17124371. [DOI] [PMC free article] [PubMed] [Google Scholar]
  121. Woodward, E., Hill., R., Harkness, P. and R. Archer (Eds). 2020. Our Knowledge Our Way in caring for Country: Indigenous-led approaches to strengthening and sharing our knowledge for land and sea management. Best Practice Guidelines from Australian experiences. NAILSMA and CSIRO. on-line report an d links: https://www.csiro.au/en/research/indigenous-science/indigenous-knowledge/our-knowledge-our-way Accessed 16 Oct 2021
  122. Wooster EIF, Fleck R, Torpy F, Ramp D, Irga PJ. Urban green roofs promote metropolitan biodiversity: A comparative case study. Building and Environment. 2022 doi: 10.1016/j.buildenv.2021.108458. [DOI] [Google Scholar]
  123. World Economic Forum. 2020. The future of nature and business. New Nature Economy Report II. Switzerland.
  124. Wortze JD, Wiebe DJ, DiDomenico GE, Visoki E, South E, Tam V, Greenberg DM, Brown LA, Gur RC, Gur RE, Barzilay R. Association between urban greenspace and mental wellbeing during the COVID-19 pandemic in a U.S. Cohort. Frontiers in Sustainable Cities. 2021 doi: 10.3389/frsc.2021.686159. [DOI] [Google Scholar]
  125. Wright K. In the shadow of a willow tree: A community garden experiment in decolonising, multispecies research. Cultural Studies Review. 2018;24:74–101. doi: 10.5130/csr.v24i1.4700. [DOI] [Google Scholar]
  126. Yap KL, Soh MCK, Sia A, Chin WJ, Araib S, Ang WP, Tan PY, Er KBH. The influence of the COVID-19 pandemic on the demand for different shades of green. People and Nature. 2022 doi: 10.1002/pan3.10304. [DOI] [PMC free article] [PubMed] [Google Scholar]

Additional URL Links

  1. City of Sydney—Urban Forest Strategy: https://www.cityofsydney.nsw.gov.au/strategies-action-plans/urban-forest-strategy
  2. Green Building Council of Australia: https://new.gbca.org.au/green-star/green-star-strategy/building-nature/
  3. Managing with Fire Program, City of Adelaide: https://www.cityofadelaide.com.au/media-centre/kaurna-cultural-practise-returns-to-the-park-lands/

Articles from Ambio are provided here courtesy of Springer

RESOURCES