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Social Sustainability

Area: Community participation

From the three pillars of sustainable development, economic, environmental and social, the latter  involving social equity and the sustainability of communities, has  been especially neglected. Ongoing problems caused by conflicting economic, environmental and social goals with regard to the processes of urbanisation continue. underpinning economic growth that contradict principles of environmental and social justice (Boström, 2012; Cuthill, 2010; Winston, 2009). Research on sustainable development highlights the need for further investigation of social sustainability (Murphy, 2012; Vallance et al., 2011). Social sustainability has been interpreted as an umbrella term encompassing many other related concepts; “social equity and justice, social capital, social cohesion, social exclusion, environmental justice, quality of life, and urban liveability” (Shirazi & Keivani, 2019, p. 4). A vast number of studies have been dedicated to defining social sustainability by developing theoretical frameworks and indicators particularly relevant to urban development and housing discourse (Cuthill, 2010; Dempsey et al., 2011; Murphy, 2012; Woodcraft, 2012). However, with a lack of consensus on the way of utilising these frameworks in a practical way, especially when applied to planning, social sustainability has remained difficult to evaluate or measure. Consequently, planning experts, housing providers and inhabitants alike understand social sustainability as a normative concept, according to established social norms, and less as an opportunity to critically examine existing institutions.

Vallance et al (2011) provide three categories to analyse social sustainability, development, bridge and maintenance sustainability: (a) social development improves conditions of poverty and inequity, from the provision of basic needs to the redistribution of power to influence existing development paradigms; (b) the conditions necessary to bridge social with ecological sustainability, overcoming currently disconnected social and ecological concerns; and (c) the social practices, cultural preferences as well as the environments which are maintained over time. Maintenance social sustainability particularly deals with how people interpret what is to be maintained and includes “new housing developments, the layout of streets, open spaces, residential densities, the location of services, an awareness of habitual movements in place, and how they connect with housing cultures, preferences, practices and values, particularly those for low-density, suburban lifestyles” (Vallance et al., 2011, p. 345). Therefore, the notion of maintenance is especially important in defining social sustainability by directly investigating the established institutions, or “sets of norms” that constitute the social practices and rules, that in turn, affect responsibilities for planning urban spaces.

A conceptual framework that appears frequently in social sustainability literature is that of Dempsey et al. (2011)⁠ following Bramley et al. (2009), defining social sustainability according to the variables of social equity and sustainability of community and their relationship to urban form, significantly at the local scale of the neighbourhood. In terms of the built environment, social equity (used interchangeably with social justice) is understood as the accessibility and equal opportunities to frequently used services, facilities, decent and affordable housing, and good public transport. In this description of local, as opposed to regional services, proximity and accessibility are important. Equitable access to such local services effectively connects housing to key aspects of everyday life and to the wider urban infrastructures that support it.

Sustainability of community is associated with the abilities of society to develop networks of collective organisation and action and is dependent on social interaction. The associated term social capital has also been used extensively to describe social norms and networks that can be witnessed particularly at the community level to facilitate collective action (Woolcock, 2001, p. 70). They might include a diversity of issues such as resident interaction, reciprocity, cooperation and trust expressed by common exchanges between residents, civic engagement, lower crime rates and other positive neighbourhood qualities that are dependent on sharing a commitment to place (Foster, 2006; Putnam, 1995; Temkin & Rohe, 1998). In fact, “the heightened sense of ownership and belonging to a locale” is considered to encourage the development of social relations (Hamiduddin & Adelfio, 2019, p. 188).

However, the gap between theoretical discussions about social sustainability and their practical application has continued. For example, the emphasis of social sustainability as a target outcome rather than as a process has been prioritised in technocratic approaches to planning new housing developments and to measuring their success by factors which are tangible and easier to count and audit. Private housing developers that deal with urban regeneration make bold claims to social sustainability yet profound questions are raised regarding the effects of gentrification (Dixon, 2019). Accordingly, the attempted methods of public participation as planning tools for integrating the ‘social’ have been found to be less effective - their potential being undercut due to the reality that decision-making power has remained at the top (Eizenberg & Jabareen, 2017).

Therefore, social sustainability is not a fixed concept, it is contingent on the interdependence of the procedural aspects (how to achieve social sustainability) and substantive aspects (what are the outcomes of social sustainability goals) (Boström, 2012). From this point of view, social sustainability reveals its process-oriented nature and the need to establish processes of practicing social sustainability that begin with the participation of citizens in decision-making processes in producing equitable (i.e. socially sustainable) development. As a dimension of sustainable development that is harder to quantify than the economic or environmental aspects, the operationalisation of social sustainability goals into spatial, actionable principles has remained a burgeoning area of research. In such research, methods for enhancing citizen participation are a particularly important concern in order to engage and empower people with “non-expert” knowledge to collaborate with academic researchers.

References

Boström, M. (2012). A missing pillar? Challenges in theorizing and practicing social sustainability: Introduction to the special issue. Sustainability: Science, Practice, and Policy, 8(1), 3–14. https://doi.org/10.1080/15487733.2012.11908080

Bramley, G., Dempsey, N., Power, S., Brown, C., & Watkins, D. (2009). Social sustainability and urban form: Evidence from five British cities. Environment and Planning A, 41(9), 2125–2142. https://doi.org/10.1068/a4184

Cuthill, M. (2010). Strengthening the “social” in sustainable development: Developing a conceptual framework for social sustainability in a rapid urban growth region in Australia. Sustainable Development, 18(6), 362–373. https://doi.org/10.1002/sd.397

Dempsey, N., Bramley, G., Power, S., & Brown, C. (2011). The social dimension of sustainable development: Defining urban social sustainability. Sustainable Development, 19(5), 289–300. https://doi.org/10.1002/sd.417

Dixon, T. (2019). Measuring the social sustainability of new housing development: A critical review of assessment methods. Journal of Sustainable Real Estate, 11(1), 16–39. https://doi.org/10.22300/1949-8276.11.1.16

Eizenberg, E., & Jabareen, Y. (2017). Social Sustainability: A New Conceptual Framework. Sustainability, 9(1), 68. https://doi.org/10.3390/su9010068

Erdiaw-Kwasie, M. O., & Basson, M. (2018). Reimaging socio-spatial planning: Towards a synthesis between sense of place and social sustainability approaches. Planning Theory, 17(4), 514–532. https://doi.org/10.1177/1473095217736793

Foster, S. R. (2006). The city as an ecological space: Social capital and urban land use. Notre Dame Law Review, 82(2), 527–582.

Hamiduddin, I., & Adelfio, M. (2019). Social sustainability and new neighbourhoods: Case studies from Spain and Germany. In Urban Social Sustainability (pp. 171–192). Routledge.

Murphy, K. (2012). The social pillar of sustainable development: A literature review and framework for policy analysis. Sustainability: Science, Practice, and Policy, 8(1), 15–29. https://doi.org/10.1080/15487733.2012.11908081

Putnam, R. D. (1995). Bowling Alone: America’s Declining Social Capital. Journal of Democracy, 6(1), 65–78. https://doi.org/10.4324/9780429261732-19

Shirazi, M. R., & Keivani, R. (2019). Urban social sustainability: Theory, policy and practice. Routledge. https://doi.org/10.4324/9781315115740

Temkin, K., & Rohe, W. M. (1998). Social Capital and Neighborhood Stability: An Empirical Investigation. Housing Policy Debate, 9(1).

Vallance, S., Perkins, H. C., & Dixon, J. E. (2011). What is social sustainability? A clarification of concepts. Geoforum, 42(3), 342–348. https://doi.org/10.1016/j.geoforum.2011.01.002

Winston, N. (2009). Urban regeneration for sustainable development: The role of sustainable housing? European Planning Studies, 17(12), 1781–1796. https://doi.org/10.1080/09654310903322306

Woodcraft, S. (2012). Social Sustainability and New Communities: Moving from Concept to Practice in the UK. Procedia - Social and Behavioral Sciences, 68, 29–42. https://doi.org/10.1016/j.sbspro.2012.12.204

Woolcock, M. (2001). The place of social capital in understanding social and economic outcomes. Canadian Journal of Policy Research, 2(1), 1–35.

Created on 03-06-2022 | Update on 08-06-2022

Related definitions

Housing Governance

Author: T.Croon (ESR11), M.Horvat (ESR6)

Area: Policy and financing

The shift from ‘government’ to ‘governance’ has been debated since the early 1970s. Whilst state interventionism had been widely embraced within western societies during the post-war decades, governments gradually moved from exercising constitutional powers to acting as facilitators and cooperative partners (Rhodes, 1997). Over the course of a few decades, this resulted in governance as ‘interactive social-political forms of governing’ (Nag, 2018, p. 124).  Hira and Cohn (2003, p. 12), influenced by Keohane (2002), define governance as “the processes and institutions, both formal and informal, that guide and restrain the collective activities of a group”. Its decentralised and flexible nature could still include public actors but would also leave space for private and third-sector parties to provide services in hybrid and temporary institutional arrangements. To formulate one single definition of ‘housing governance’ as a particular mode of governance is however difficult due to its multilevel character. Housing could relate to either a family home, a housing association, or a complete local/national housing governance framework. On a household level, Wotschack (2005, p. 2) defines governance as managing “the daily time allocation of spouses by household rules and conflict handling strategies”. The work of Wijburg (2021) indicates that local/municipal governance entails a set of public interventions, strategies, policies and provisions used to provide local needs (e.g. housing supply). On the national level, Yan et al. (2021) define public rental housing (PRH) governance as “a structure of a wide range of government and non-governmental actors that act in all its phases of PRH provision from policy design to implementation and realisation”.[1] This specific definition on PRH combines the domestic definition of governance with Wijburg’s understanding of governance on the local level. Within the Chinese context, the national government provides policies and creates nationwide operational methods, whilst local governments implement and formulate the policies locally (Yan et al., 2021). Critics point out that a more decentralised governance structure complicates the public accountability of housing provision. Peters and Pierre (2006, p. 40) distinguish problems concerning the ‘isolation’ and ‘enforcement’ of accountability. The former refers to demarcation, as it is easier to measure the performance of a government housing agency directly responsible for new build and operations, than those from the private sector in an indirect role trying to stimulate and facilitate other actors and contracting out construction and operations (Shamsul Haque, 2000). The latter relates to the accountability deficit that arises when responsibility is transferred from democratically governed municipal agencies to actors without a representative institutional arrangement, and thus without control mechanisms for tenants or the wider population (Mullins, 2006). Throughout history, understanding of governing has evolved together with the role of government. The state plays a different role in capitalism, corporatism and socialism, which has varying effects on local and/or (inter)national levels. Whilst the above paragraphs describe housing governance within a democratic governance regime, transferring the conceptual debate to autocratic or hybrid regimes would pose difficulties. Thus, finding a unique definition of housing governance applicable in all spheres remains a challenge, and the specific context must be carefully considered. Important challenges remain, and as housing provision mechanisms evolve, further exploration of housing governance, especially on a municipal level, are likely to gain importance (Hoekstra, 2020). [1] “Housing provision is a physical process of creating and transferring a dwelling to its occupiers, its subsequent use and physical reproduction and at the same time, a social process dominated by the economic interests involved” ibid.

Created on 16-02-2022 | Update on 21-02-2022

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Community Empowerment

Author: Z.Tzika (ESR10)

Area: Community participation

Community empowerment appears in the literature of participatory action research (Minkler, 2004), participatory planning (Jo & Nabatchi, 2018), and community development (Luttrell et al., 2009) as a key element of participatory practices, understanding it as a process that enables communities to take control of their lives and their environments (Rappaport, 2008; Zimmerman, 2000). Many argue that community participation becomes meaningless if it does not lead to, or pass through community empowerment. As the term is being used in diverse and ubiquitous ways, it runs the risk of ending up as an empty definition and a catch-all phrase (McLaughlin, 2015). It is therefore important to specify the perspective through which we will view the term and clarify the nuances.  Since its origins, empowerment has been used in two different ways. Firstly, top-down as the power that had been ‘granted’ by a higher authority, such as the state or a religious institution, and secondly, bottom-up, as a process by which groups or individuals come to develop the capacity to act and acquire power. Examples of the latter can be found in social groups such as feminists working in nongovernmental organizations throughout the global south in the 1970s, who found a way to address social issues and inequalities that enabled social transformation based on women’s self-organization (Biewener & Bacqué, 2015). The term was gradually appropriated by welfare, neoliberal, and social-neoliberal agendas whose priority was individual agency and choice. In neoliberal rationality, empowerment is related to efficiency, economic growth, business productivity, and individual rational choice to maximize profit in a competitive market economy. In social liberalism agendas, empowerment is understood as ‘effective agency’, where ‘agency’ is not an inherent attribute, but something that needs to be constructed through ‘consciousness-raising’ (McLaughlin, 2016). A broader definition sees empowerment as a social action process through which individuals, communities, and organizations take control of their lives in the context of changing the social and political environment to improve equity and quality of life (Rappaport, 2008; Zimmerman, 2000). Rowlands (1997), refers to four types of empowerment: power over, as the ability to influence and coerce; power to, to organize and change existing hierarchies; power with, as the power from the collective action and power within, as the power from the individual consciousness. Using this classification, Biewener & Bacqué (2015), adopting a feminist approach, understand empowerment as a multilevel construct with three interrelated dimensions: 1) an internal, psychological one, where ‘power within’ and ‘power to’ are developed, 2) an organizational, where ‘power with’ and ‘power over’ are strengthened and 3) a social or political level, where institutional and structural change is made possible through collective action. Thus, community empowerment links the individual level, which involves self-determination, growth of individual awareness, and self-esteem, to the collective level, relating critical consciousness and capacity building with the structural level, where collective engagement and transformative social action take place. This view of empowerment, which considers its goals and processes, has a social dimension that is lacking in other approaches that prioritize individual empowerment. Aside from the feminist movements, the philosophy and practices of community empowerment have been greatly influenced by the work of Paulo Freire, a Brazilian educator and an advocate on critical pedagogy. Freire proposed a dialogic problem-solving process based on equality and mutual respect between students and teachers; that engaged them in a process of iterative listening-discussing-acting. Through structured dialogue, group participants shared their experiences, discussed common problems, and looked for root causes and the connections among “problems behind the problems as symptoms” (Freire, 1970). The term conscientization, that Freire proposed, refers to the consciousness that arises through the involvement of people in the social analysis of conditions and their role in changing them. This awareness enables groups to be reflexive and open spaces, to enact change or to understand those limited situations that may deter change (Barndt, 1989). Empowerment can be understood as both a process and an outcome (Jo & Nabatchi, 2018). As a process, it refers to “the development and implementation of mechanisms to enable individuals or groups to gain control, develop skills and test knowledge”(Harrison & Waite, 2015) and it entails the creation of new subjects who have developed a critical consciousness and the formation of groups with a ‘collective agency’ ‚ or ‘social collective identity’ (Biewener & Bacqué, 2015). Empowerment as an outcome refers to “an affective state in which the individual or group feels that they have increased control, greater understanding and are involved and active” (Harrison & Waite, 2015). This can lead to a transformation of the social conditions by challenging the structures and institutionalized forms that reproduce inequalities. The values and the significance of community empowerment can be further applied in the participatory and community-based approaches of the housing sector. Examples of such approaches in the housing provision are the housing cooperatives, and self-developed and self-managed housing groups. Housing cooperatives aim at promoting co-creation to engage future residents, professionals, and non-profit organizations in all the stages of a housing project: problem-framing, designing, developing, cohabiting, managing, and maintaining. Such organisational models stress the importance and pave the way for community empowerment by uniting individuals with similar interests and ideals, enabling them to have housing that responds to their needs, preferences, and values. The participation of the residents aims to strengthen their sense of ownership of the process, the democratic decision-making and management, and the social collective identity, making community empowerment an integral characteristic of cooperative housing initiatives. With this social perspective, residents can gain individual and collective benefits while contributing to fairer and more sustainable urban development on a larger scale (Viskovic Rojs et al., 2020).

Created on 03-06-2022 | Update on 03-06-2022

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Sustainability

Author: E.Roussou (ESR9)

Area: Community participation

Sustainability is primarily defined as “the idea that goods and services should be produced in ways that do not use resources that cannot be replaced and that do not damage the environment” (Cambridge Advanced Learner’s Dictionary & Thesaurus, n.d.) and is often used interchangeably with the term “sustainable development”(Aras & Crowther, 2009). As defined by the UN, sustainable development is the effort to “meet the needs of the present without compromising the ability of future generations to meet their own needs” (United Nations, 1987) and is often interpreted as the strategies adopted towards sustainability with the latter being the overall goal/vision (Diesendorf, 2000). Both of these relatively general and often ambiguous terms have been a focal point for the past 20 years for researchers, policy makers, corporations as well as local communities, and activist groups, among others, (Purvis et al., 2019). The ambiguity and vagueness that characterise both of these terms have contributed to their leap into the global mainstream as well as the broad political consensus regarding their value and significance (Mebratu, 1998; Purvis et al., 2019), rendering them one of the dominant discourses in environmental, socio-political and economic issues (Tulloch, 2013). It is, however, highly contested whether their institutionalisation is a positive development. Tulloch, and Tulloch & Nielson (2013; 2014) argue that these terms -as they are currently understood- are the outcome of the “[colonisation of] environmentalist thought and action” which, during the 1960s and 1970s, argued that economic growth and ecological sustainability within the capitalist system were contradictory pursuits. This “colonisation” resulted in the disempowerment of such discourses and their subsequent “[subordination] to neoliberal hegemony” (Tulloch & Neilson, 2014, p. 26). Thus, sustainability and sustainable development, when articulated within neoliberalism, not only reinforce such disempowerment, through practices such as greenwashing, but also fail to address the intrinsic issues of a system that operates on, safeguards, and prioritises economic profit over social and ecological well-being (Jakobsen, 2022). Murray Bookchin (1982), in “The Ecology of Freedom” contends that social and environmental issues are profoundly entangled, and their origin can be traced to the notions of hierarchy and domination. Bookchin perceives the exploitative relationship with nature as a direct outcome of the development of hierarchies within early human societies and their proliferation ever since. In order to re-radicalise sustainability, we need to undertake the utopian task of revisiting our intra-relating, breaking down these hierarchical relations, and re-stitching our social fabric. The intra-relating between and within the molecules of a society (i.e. the different communities it consists of) determines how sustainability is understood and practised (or performed), both within these communities and within the society they form. In other words, a reconfigured, non-hierarchical, non-dominating intra-relationship is the element that can allow for an equitable, long-term setting for human activity in symbiosis with nature (Dempsey et al., 2011, p. 290). By encouraging, striving for, and providing the necessary space for all voices to be heard, for friction and empathy to occur, the aforementioned long-term setting for human activity based on a non-hierarchical, non-dominating intra-relating is strengthened, which augments the need for various forms of community participation in decision-making, from consulting to controlling. From the standpoint of spatial design and architecture, community participation is already acknowledged as being of inherent value in empowering communities (Jenkins & Forsyth, 2009), while inclusion in all facets of creation, and community control in management and maintenance can improve well-being and social reproduction (Newton & Rocco, 2022; Turner, 1982). However, much like sustainability, community participation has been co-opted by the neoliberal hegemony; often used as a “front” for legitimising political agendas or as panacea to all design problems, community participation has been heavily losing its significance as a force of social change (Smith & Iversen, 2018), thus becoming a depoliticised, romanticised prop. Marcus Miessen (2011) has developed a critical standpoint towards what is being labelled as participation; instead of a systematic effort to find common ground and/or reach consensus, participation through a cross-benching approach could be a way to create enclaves of disruption, i.e. processes where hierarchy and power relations are questioned, design becomes post-consensual spatial agency and participation turns into a fertile ground for internal struggle and contestation. Through this cross-benching premise, community participation is transformed into a re-politicised spatial force. In this context, design serves as a tool of expressing new imaginaries that stand against the reproduction of the neoliberal spatial discourse. Thus, sustainability through community participation could be defined as the politicised effort to question, deconstruct and dismantle the concept of dominance by reconfiguring the process of intra-relating between humans and non-humans alike.

Created on 08-06-2022 | Update on 09-06-2022

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Sustainability Built Environment

Author: M.Alsaeed (ESR5), K.Hadjri (Supervisor)

Area: Design, planning and building

Sustainability of the built environment The emergence of the contemporary environmental movement between the 1960s and 1970s and its proposals to remedy the consequences of pollution can be seen as one of the first steps in addressing environmental problems (Scoones, 2007). However, the term “sustainable” only gained wider currency when it was introduced into political discourse by the Club of Rome with its 1972 report “The Limits to Growth”, in which the proposal to change growth trends to be sustainable in the far future was put forward (Grober, 2007; Kopnina & Shoreman-Ouimet, 2015a; Meadows et al., 1972). Since then, the use of the term has grown rapidly, especially after the publication of the 1978 report “Our Common Future”, which became a cornerstone of debates on sustainability and sustainable development (Brundtland et al., 1987; Kopnina & Shoreman-Ouimet, 2015a). Although the two terms are often used indistinctively, the former refers to managing resources without depleting them for future generations, while the latter aims to improve long-term economic well-being and quality of life without compromising the ability of future generations to meet their needs (Kopnina & Shoreman-Ouimet, 2015b; UNESCO, 2015). The Brundtland Report paved the way for the 1992 Earth Summit, which concluded that an effective balance must be found between consumption and conservation of natural resources (Scoones, 2007). In 2000, the United Nations General Assembly published the 8 Millennium Development Goals (UN, 2000), which led to the 17 Sustainable Development Goals (SDGs) published in 2016 (UN, 2016). The 17 SDGs call on all countries to mobilise their efforts to end all forms of poverty, tackle inequalities and combat climate change (UN, 2020; UNDP, 2018). Despite the rapidly growing literature on sustainability, the term remains ambiguous and lacks a clear conceptual foundation (Grober, 2007; Purvis et al., 2019). Murphy (2012) suggests that when defining sustainability, the question should be: Sustainability, of what? However, one of the most prominent interpretations of sustainability is the three pillars concept, which describes the interaction between the social, economic and environmental components of society (Purvis et al., 2019). The environmental pillar aims to improve human well-being by protecting natural capital -e.g. land, air and water- (Morelli, 2011). The economic sustainability pillar focuses on maintaining stable economic growth without damaging natural resources (Dunphy et al., 2000). Social sustainability, on the other hand, aims to preserve social capital and create a practical social framework that provides a comprehensive view of people's needs, communities and culture (Diesendorf, 2000). This latter pillar paved the way for the creation of a fourth pillar that includes human and culture as a focal point in sustainability objectives (RMIT, 2017). Jabareen (2006) describes environmental sustainability as a dynamic, inclusive and multidisciplinary concept that overlaps with other concepts such as resilience, durability and renewability. Morelli (2011) adds that it can be applied at different levels and includes tangible and intangible issues. Portney (2015) takes Morelli's explanation further and advocates that environmental sustainability should also promote industrial efficiency without compromising society's ability to develop (Morelli, 2011; Portney, 2015). Measuring the built environment sustainability level is a complex process that deploys quantitative methods, including (1) indexes (e.g. energy efficiency rate), (2) indicators (e.g. carbon emissions and carbon footprint), (3) benchmarks (e.g. water consumption per capita) and (4) audits (e.g. building management system efficiency) (Arjen, 2015; Berardi, 2012; James, 2014; Kubba, 2012). In recent years, several rating or certification systems and practical guides have been created and developed to measure sustainability, most notably the Building Research Establishment Environmental Assessment Method (BREEAM) introduced in the UK in 1990 (BRE, 2016) and the Leadership in Energy and Environmental Design (LEED) established in the US in 2000 (USGBC, 2018). In addition, other overlapping methodologies and certification frameworks have emerged, such as the European Performance of Buildings Directive (EPBD) in 2002 (EPB, 2003) and the European Framework for Sustainable Buildings, also known as Level(s) in 2020 (EU, 2020), amongst others. The sustainability of the built environment aims to reduce human consumption of natural resources and the production of waste while improving the health and comfort of inhabitants and thus the performance of the built environment elements such as buildings and spaces, and the infrastructure that supports human activities (Berardi, 2012; McLennan, 2004). This aim requires an effective theoretical and practical framework that encompasses at least six domains, including land, water, energy, indoor and outdoor environments, and economic and cultural preservation (Ferwati et al., 2019). More recently, other domains have been added, such as health and comfort, resource use, environmental performance, and cost-benefit and risk (EU, 2020). Sustainability of the built environment also requires comprehensive coordination between the architectural, structural, mechanical, electrical and environmental systems of buildings in the design, construction and operation phases to improve performance and avoid unnecessary resource consumption (Yates & Castro-Lacouture, 2018).

Created on 24-06-2022 | Update on 16-11-2022

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Urban Commons

Author: A.Pappa (ESR13)

Area: Community participation

Urban commons are shared resources in the city that are managed by their users in a collaborative and non-profit-oriented way. The concept is based on the idea that urban resources and services that represent fundamental rights in the city should be accessible to and governed by the urban dwellers, to support the social capital and the sustainability of the urban communities. Hence, their value lies mostly in the social benefit produced during their use and they are therefore different from commodities that follow traditional market principles of profit maximisation and private ownership (Dellenbaugh-Losse et al., 2015). The concept of urban commons is an extrapolation in the urban context of the notion of commons which historically refers to natural resources available to all and not owned by any individual, such as air, water and land. The commons discourse became significantly popular thanks to the fundamental contribution of Elinor Ostrom (1990) and particularly after she was awarded the Nobel in Economics in 2009. Ostrom presented cases and design principals for the collective management of common resources by those that use and benefit from them, challenging the predominant negative connotations that had peaked with Garret Hardin’s (1968) Tragedy of the Commons where he analysed the impossible sustainability of common pool resources due to individual benefits. During the last fifteen years, a vast body of academic literature on urban commons has been produced, linking the notion to other urban theories, such as the right to the city (Harvey, 2008; Lefebvre, 1996), biopolitics (Angelis & Stavrides, 2009; Hardt & Negri, 2009; Linebaugh, 2008; Parr, 2015; Stavrides, 2015, 2016), peer-to-peer urbanism and sharing economy (Dellenbaugh-Losse et al., 2015; Iaione, 2015; Iaione et al., 2019; McLaren & Agyeman, 2015; Shareable, 2018). The notion of the urban commons encompasses resources, people and social practices (Dellenbaugh-Losse et al., 2015): Commons resources are urban assets of various types, characteristics and scales (Dellenbaugh-Losse et al., 2015). Examples of commons resources include physical spaces, such as community gardens, street furniture and playgrounds; intangible elements such as culture and public art; services such as safety; digital spaces, such as internet access. Urban commons literature and practices have attempted to determine several typological categorisations of the urban commons resources, the most notable being that of Hess (2008), who classified them as cultural, knowledge, markets, global, traditional, infrastructure, neighbourhood, medical and health commons. The commoners are the group that uses and manages the urban commons resources. It is a self-defined and organically formed group of individuals whose role is to collectively negotiate the boundaries and the rules of the management of the commons resources (Dellenbaugh-Losse et al., 2015). In a neighbourhood setting, for example, the commoners may be individual residents, or community groups, cooperatives, NGOs and local authorities. De Angelis and Stavrides (2010) points out that commoners might include diverse groups or communities that are not necessarily homogenous. Commoning refers to the collaborative participatory process of accessing, negotiating and governing the commons resources. The term was introduced by Peter Linebaugh (2008) and refers to the “social process that creates and reproduces the commons” (Angelis & Stavrides, 2010). Commoning is a form of public involvement for the public good (Lohmann, 2016). Commoning implies a commitment to solidarity and cooperation, to the creation of added value to the community, to democracy and inclusiveness and is connected to a hacking culture(Dellenbaugh-Losse et al., 2015). Hence, commoning practices can include various activities such as co-creation, capacity building and placemaking, support through learning, innovation, performing art, protest, urban gardening and commuting. In contemporary societies in crisis, the urban commons theory is often used as a counter-movement to the commodification of urban life and as a response to complex issues, proving essential for the well-being of marginalised communities and for the provision of affordable and sustainable housing. Urban commons management conveys the re-appropriation of urban values (Borch & Kornberger, 2015) breaking silos of expertise and knowledge by adopting a collaborative approach to defining and solving the problems at stake. The practice of urban commons helps to build values of openness, experimentation, creativity, trust, solidarity and commitment within stakeholder groups.

Created on 14-10-2022 | Update on 18-10-2022

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