Next Article in Journal
Olive Pulp and Exogenous Enzymes Feed Supplementation Effect on the Carcass and Offal in Broilers: A Preliminary Study
Previous Article in Journal
Soil Health Impacts of Rubber Farming: The Implication of Conversion of Degraded Natural Forests into Monoculture Plantations
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Perspective

Edible Green Infrastructure for Urban Regeneration and Food Security: Case Studies from the Campania Region

by
Alessio Russo
1,* and
Giuseppe T. Cirella
2,*
1
School of Arts, University of Gloucestershire, Cheltenham GL50 4AZ, UK
2
Faculty of Economics, University of Gdansk, 81-824 Sopot, Poland
*
Authors to whom correspondence should be addressed.
Agriculture 2020, 10(8), 358; https://doi.org/10.3390/agriculture10080358
Submission received: 2 June 2020 / Revised: 9 August 2020 / Accepted: 13 August 2020 / Published: 14 August 2020
(This article belongs to the Section Agricultural Product Quality and Safety)

Abstract

:
Ten identified edible green infrastructure (EGI)-related urban regeneration case studies within the Campania region, Italy, are explored in relation to local community development, involvement, and education. Urban space and agriculture are promoted as sustainably planned networks for edible food components and structures. Within an urban ecosystem, city planners are actively promoting urban agriculture after an increase in the availability of unused land. Advantages for public health include stress reduction and physical activity, as well as sustainability of urban gardens by way of far-sighted urban planning. Case studies within the Campania region illustrate EGI know-hows and awareness, and they elucidate upon a number of beneficial reasons for its implementation. Within the Campania region, all five provinces showed positive impacts when using EGI for urban regeneration and well-being. Recent developments from the COVID-19 pandemic are reinforcing a rethink of food security and food supply chains.

1. Introduction

Cities produce less than 10% of their food and rely on water, energy, fuel, and construction materials from external sources [1]. A cause-and-effect reproach from escalating global population brings to the forefront the need to re-examine how urban spaces are developed and used, and how urban inhabitants are fed [2]. Furthermore, food insecurity is an important health problem and an under-recognized social determinant of health [3]. With the escalation of populations in cities, important urban environmental services in correspondence with ecosystem services play a vital role in urban health and its overall landscape [4]. A “green”-friendly, vibrant, and constructive community promotes well-being, essential to sustainable development; when correlated with urban food security, it is a safe and sound concept of healthy living intergenerationally. Green infrastructure is gaining momentum. The integration of green and gray infrastructure can produce lower cost and more resilient services [5]. Multifunctional and connected green infrastructure systems are linked to human well-being and city resilience [6]. Green infrastructure such as green roofs, urban parks, green walls, and rain gardens provide several ecosystem services [4,7]. Green roofs, for example, are reported to reduce temperature at street level ranging from 0.03–3 °C and to remove PM10 pollutants at roof level ranging from 0.42–9.1 g/m2 per year [8].
The link between green infrastructure and human well-being implies that equitable access and distribution of quality green spaces is a human rights issue [9]. Recently, the concept of green infrastructure was bolstered with a novel approach called edible green infrastructure (EGI) that can improve resilience and quality of life in cities and can boost food insurance [4].
EGI is a sustainable planned network of edible food components and structures within the urban ecosystem which are managed and designed to provide primarily provisioning ecosystem services [10,11]. EGI typologies are macro-categorized in conjunction with urban agriculture, with eight sub-classifications: (1) edible urban forests and edible urban greening, (2) edible forest gardens, (3) historic gardens and parks and botanic gardens, (4) school gardens, (5) allotment gardens and community gardens, (6) domestic and home gardens, (7) edible green roofs and vegetable rain gardens, and (8) edible green walls and facades [11,12]. EGI also includes urban foraging practice from formal and informal urban green spaces [13,14,15]. An example of this practice can be found in the city of Andernach, Germany, where edible plants are grown in urban greenspaces in which citizens can harvest for free, resulting in a better diet and increased social interaction [14]. However, edible plants in urban areas can be contaminated by pollutants [11,16]. Entwistle et al. [17] sampled nearly 280 paired soil and crop samples across 31 urban gardens in Newcastle-upon-Tyne, United Kingdom. They found that Pb concentrations in 98% of the sampled soils were above the United Kingdom soil guideline for urban agriculture sites (80 mg/kg), but the majority of crop samples had Pb levels < 0.1 mg/kg fresh weight [17].
A number of cities are already integrating different types of EGI into their urban management plans; however, management and planning endeavors still need to consider context-specific geographic (e.g., climatic zones and soil characteristics), social (e.g., community development, educational benefits, and equity), and economic (e.g., employment opportunities and inexpensive food sources) requirements [12].
Urban agriculture and EGI have the potential to increase the sustainability and resilience of urban communities [18]. In particular, community urban gardens can support community resilience in terms of disasters and pandemics (e.g., the COVID-19 pandemic) [19]. As such, the coronavirus lockdown is driving more urban dwellers to cultivate fruit and vegetables locally—especially at home [20]. Urban agriculture can be used for the sustainable regeneration of urban environments [11,21,22,23,24]. Urban regeneration is a key focus for public policy throughout Europe, in which critical focus continues to explore aspects of its most deprived neighborhoods. There was a sporadic decline in these neighborhoods from a variety causes, including globalization and related structural influences [25]. Urban regeneration, in this context, hints at a European-centric practice that closes the gap in developing an overall better EGI approach.
According to the Urban Development Network Program II (URBACT II) report, the state of the art on sustainable regeneration in urban areas stipulates “regeneration policies and processes within a city, which seek to address inter-related problems in order to consider, reduce, and mitigate their environmental impact” [26]. Such policies, plans, and actions led us to conclude that the minimization of required inputs (i.e., energy, water, food, materials, etc.) and processed outputs (i.e., waste, heat, air and water pollution, carbon emissions, etc.) are dimensional to EGI practices (Table 1).
Worldwide local authorities are now investing in food-growing projects as part of their urban regeneration programs [27]. The urban agriculture and EGI literature center on the importance of community development and offer tool-oriented research for social regeneration, reducing crime and discrimination, and generating ecosystem services [28]. EGI as a nature-based solution provides an appealing enhancement to quality of life, health, and well-being—essential for local governance and inner-city development. Examples of its use include (1) inner-city lanes reduced to encourage greenways to combat air pollutants and encourage alterative transport, (2) restoration of polluted and degraded waterways, and (3) urban renewal processes through the regenerative process of assistive urban agricultural advancements (i.e., regeneration of residential and industrial areas). This can be extremely important for cities undergoing transitional change (e.g., a post-industrial shift). Examples of this type of transition can include abandoned industrial sites and unused infrastructure removed and de-toxified by using bioremediation (i.e., the process that uses plants to degrade and reduce or detoxify waste products and pollutants) to then be converted into EGI [29,30,31,32,33,34]. However, remediation should be made very carefully to guarantee that contamination problems are fully mitigated [35]. Transformative public green spaces can be used for recreation, converted into community gardens and urban farms—enriching social cohesion and regenerating disadvantaged urban areas [21,36]. Urban agriculture and EGI as tools of sustainable landscape design were brought into European and American cities by landscape architects and artists from the early 1970s [37]. In 1982, two acres of wheat were planted and harvested on a landfill near the World Trade Center in New York by the American–Hungarian artist Agnes Denes. The artist stated that “placing it at the foot of the World Trade Center, a block from Wall Street, facing the Statue of Liberty, also had symbolic importance. It represented food, energy, commerce, world trade, [and] economics. It referred to mismanagement, waste, world hunger, and ecological concerns” [38].
In the past, the European URBACT II project, i.e., based on sustainable food in urban communities, generated a body of knowledge ranging from food production to social inclusion, food education, sustainable regeneration, and artistic projects in 10 European cities [39]. However, to our knowledge, there are no peer-reviewed studies in the Campania region that discussed the role of EGI for urban regeneration. This perspective study fills this research gap and introduces important examples in terms of the main benefits and aims of EGI implementation. Moreover, this perspective considers the growing need to contribute toward two of the United Nations Sustainable Development Goals (SDGs)—specifically, SDG 3 (ensure healthy lives and promote well-being for all at all ages) and SDG 11 (make cities and human settlements inclusive, safe, resilient, and sustainable)—by targeting the need for urban food security and adding significant knowledge base at the case study level [10]. In detail, we identify and examine 10 EGI-related sustainable urban regeneration case studies within the Campania region, Italy, which assist in developing local community involvement and education, and we focus on the trends within the discipline.

2. Case Studies

A number of Italian municipalities apply the Food and Agriculture Organization of the United Nations (FAO) support tool to assist with low-income households and “victims of unemployment [to] improve their own social status as well as their city” [40]. Allotment gardens, “orti urbani” in Italian, are components of EGI that increased diffusively throughout Italian cities in recent years (i.e., orti urbani increased 4% with two million square meters in 77 key urban centers [41] between 2016 and 2017). This phenomenon pressed municipalities to adopt regulations and allotment-based management schemes within an urban agricultural context. In accordance with the Regional Law No. 5, dated 30 March 2012, the Campania region considers and backs the multifunctional agro-oriented advancement of social services, well-being, education, and infrastructure development. The region put together regionwide oversight developing its social agricultural programs—a platform that provisions “eco-friendly development and a bottom-up stance in the form of EGI governance” [29]. In 2009, the region published a number of policies directed at “social and community gardens” with three key components: “social assistance, town planning, and zonal management” [42].
In terms of health benefits, a number of factors contribute to the development of an alternative EGI system, via a self-production of agricultural means, including (1) food and environmental education (i.e., in partnership with third-party organizations), (2) development of bartering among tenants, (3) recovery of traditional crops, (4) development of organic agriculture, (5) promotion of new forms of socialization, (6) training in biological horticultural techniques and orthotherapy, (7) psychosocial rehabilitation, and (8) physical and motor skills development [43]. In recognition of these policies, many urban agriculture and EGI-oriented projects were initiated and can be found throughout the region, especially within the provinces of Salerno and Naples (Figure 1). Several of these urban agriculture projects were grouped in an interregional network and mapped online [44]. The database contains 23 projects: one each in Turin, Milan, and Potenza and 20 within the Campania region. Regionally, within the context of Italy, we considered the main benefits of 10 EGI case studies within the Campania region using a desktop study and on-site verification [26]. The main benefits are listed in Table 2.

2.1. Province of Salerno

Within the city of Cava de Tirreni, near Salerno, the ongoing project “Matti per l’orto” successfully centered on persons with mental disorders for eight years. Its high rate of success focused on presenting persons with mental disorders the opportunity to learn, cooperate, and interact within the community by producing alternative urban food sources. Another project, within the subregion of Cilento, called “Gardens of the Mediterranean diet” explores dietary health and offers the opportunity for young people to learn about farming and food productivity. More recently, Legambiente, the environmental offshoot of the opposition party in power, started the “OrtoMondo” project within the township of Capaccio Paestum in which 30 migrants from a nearby migrant center oversee 11 of its nearby garden allotments [45].
Throughout the province of Salerno, and greater Campania region for that matter, examples of EGI-oriented projects illustrate continued commitment and educational grassroots understanding of the intrinsic value of agricultural self-production. A key example, set out in 2001 as another Legambiente initiative, is the first community garden experiment built inside the archaeological park at Pontecagnano [46]. The park, made up of 22 hectares, remains and is preserved as one of the most important Etruscan settlements in Italy (Figure 2).
Presently within the archaeological park, the community gardens are divided into a number of sections, including 54 individual 100-m2 plots assigned to pensioners over 55; one plot of 1000 m2 divided by waterways, named the “ortone”, allocated to an association which supplies local and small groups the ability to purchase sub-plots of 50 m2; a horticultural therapy section of about 50 m2 assigned to the Department of Mental Health; pedagogical gardens assigned to the local schools; a section assigned to the Christian Associations of Italian Workers; a section assigned to the Campania Rheumatic Disease Association; one distinctive “sentimental mood-oriented” garden designed to attract and entice the five senses covering about 250 m2 [46,47,48] (Figure 3). As such, the development of the park also attracts a fair share of tourism, creating an overall socially positive impact and useful blueprint for other areas throughout the region and beyond.

2.2. Province of Benevento

Love and respect for nature are taught at the comprehensive “Bosco Lucarelli” Institute in Benevento. This institute is an example of an edible school garden [11,49] that began offering instructional classes from February 2018 in “educational gardening”. Throughout the school year, tutorial studies include applied and theoretical classes in which students participate in growing vegetables in flowerbeds throughout the institute’s buildings. The initiative stems from a collaboration between the city of Benevento, the “Bosco Lucarelli” Institute, and the landscaping company “Vivai Barretta Garden” [50].
Another good example is the “Buon orto fa buon sangue” initiative (i.e., translated in English to “Good vegetable gardens make good blood”), that is, an urban agriculture project promoted by the Associations Gramigna, Fratres Torrecuso [51]. Mini-allotments were created by Benevento’s Local Health Authority assigning citizens, informal groups, and associations with designated plots of land city-wide. With the creation of these gardens, an urban agriculture polo center was created which includes, in addition to these mini allotments, the “Orto di Casa Betania” social farm, managed by the Cooperativa La Solidarietà and the “Sale della Terra” non-profit consortium. In particular, in partnership with various cooperatives from Benevento, several rehabilitative therapeutic projects were launched using the Personal Health Budget Model [52]. Social activities are currently being carried out at the Garden of Casa Betania and on other lands throughout Benevento. The project was developed from the desire to make agriculture and urban gardens a tool that promotes quality of life, environmental sustainability, and convivial sociability—increasing the individual and collective well-being of participants [51].

2.3. Province of Naples

Regionwide, Naples leads the way in the number of urban regeneration projects. Its numerous EGI projects span throughout the city and surrounding suburbs. An example of urban regeneration, via an EGI approach, is De Filippo park, located in Ponticelli, an eastern suburb of Naples and one of the most degraded, overcrowded, and permeated crime-ridden areas. This degraded area was transformed into a variety of allotment gardens which provision EGI in the form of gardening of vegetable crops [40] (Figure 4). To assist with the clean-up of the area, the local health department put together a community-based project in conjunction with the Lilliput Day Center. The project sports the slogan “Social garden: share—join—unite” and communally works with the Naples firm ERA Coopertiva Sociale, which is accompanied by a group of Neapolitan-based non-government organizations (NGOs) [42].
Throughout De Filippo park, the aim is to create urban-focused gardens and reduce crime. The extent of the project sparked interest not only from devoted users, but from concerned citizens, the community, and local associations (e.g., the Catholic church and local neighborhood watch) [42]. The combined project’s intent is to trigger a community-wide protection and care program in defense and protection of the urban garden space. The objective of the park’s urban gardens extends to the complete rejuvenation and augmentation of green space and creation of a territorial culture in favor of an EGI urban agricultural approach. To date, members come from a wide array of backgrounds (e.g., schools, associations, town committees, churches, and even the local archaeology organization) and are offered (throughout the area) custody of small plots to garden. The Lilliput Day Center, in conjunction with local law enforcement, collates and forms the social networking that promotes the project. Notable advantages to the users include EGI gardening know-hows, proficiency in farming, and, for the unemployed, the chance to reintegrate back into the workforce and society at large [42].
At first, the work of resettling De Filippo park was mostly stalled due to vandalism, with important work tools and material stolen and a number of persons threatened; however, local involvement at all levels persevered the project and, to date, made a difference with the park’s restorative usage. One aspect worth discussing is the rehabilitative extent of persons who otherwise would be detached from society. People affected by pathological addiction or a criminal past are presented with a positive feedback loop and path forward out of the world of crime. In addition, the park’s initiatives engage the elderly, mentally challenged, unemployed, and unmotivated the opportunity to connect and learn within the controlled, protected confines of the park. The process of cultivating, nurturing, and harvesting food offers workers a sense of accomplishment and community identity [42].
Each month, participants meet to plan management strategies for the garden space and identify potential concerns (e.g., cooperatively allocating space for members and deciding if further protective measures should be enforced—including a complete ban on chemo-pesticide use, as well as park access). Apart from a zero tolerance to chemical pesticides, the use of a dedicated land surveyor assisted in developing better plot design and reduced issues concerning any plot disputes. By way of focus group, the park’s gardeners also successfully received additional funding from the region and national government—analogous with many other Italian cities that stress EGI. With regard to waste disposal, the urban gardens fall under the support of Naples’ waste management services, and they regularly have organic waste removed weekly [40].
In the month of March of 2016, the city of Naples held a public event that promoted urban agriculture throughout the city and region. This event helped spur awareness for the key urban gardens in the city—De Filippo park being one of them. During the event, urban gardens had the opportunity to exhibit the benefits of EGI and discuss various projects, operational entities, and organizational implementation and performance. After the event, interest was sparked from the Lilliput Day Center, Ponticelli gardeners, and stakeholders banding together to hold a second major event inside the urban garden of Ponticelli, with the slogan “Let’s Grow Legality” [40]—with reference to the struggle the suburb faced and continues to endure in promoting EGI and smart, urban gardening.
Another project that is in a degraded and high-crime zone can be found in the redeveloped and ongoing rejuvenated district of Scampia. A number of areas and spaces throughout the district, in particular the area known as Villa Comunale (i.e., renamed Ciro Esposito park) and Piazza Giovanni Paolo II (i.e., the town square), exhibit a number of encouraging re-appropriation and aggregative green spaces (Figure 5). The unused structures give back to citizens an active role in changing their community and, overall, their district’s unfavorable reputation. Direct involvement of citizens, civil organizations, and local institutions are involved in promoting the following EGI-aimed rejuvenation, including (1) increased usability of space and livability of the neighborhood, (2) recovery and redevelopment of unused structures, green areas, and green spaces for social, sporting, and economic purposes, and (3) increased levels of belonging and participation at a cultural and community level. This project transformed and fulfilled EGI activities (e.g., allotment gardening)—inside the park [53]—to expand upon the community’s lack of safe social and interactive spaces.

2.4. Province of Caserta

In the province of Caserta, a notable project is “Orti.net, coltiviamo la socialit@” (i.e., translated in English to “Orti.net, societal cultivation”). The geography of the project encompasses the southern province of Caserta and some northern parts of the province of Naples. The area, formerly known as the “Land of Work”, presently fronts the name the “Land of Fire”. This name change is related to the presence of toxic waste and bonfires that relate to activities integrative to criminal organizations (e.g., Camorra) [54,55]. Throughout this area, these environmental concerns are at a state of emergency and, more often than not, intersect with the economic and socially under-privileged. The under-privileged often include the elderly, people with disabilities, and migrant populations. The Orti.net, coltiviamo la socialit@ project focuses on giving people social space by way of cultivable vegetable gardens (i.e., a practice known as of social farming). The aim of the project is to promote and enhance environmentally sustainable action and sustainable EGI-oriented agriculture.
One aspect of the project, held within the township of Casale di Teverolaccio di Succivo, Caserta, incorporates students from local schools and universities in Aversa and Capua. The project teaches via its eco-learning laboratories about urban gardening, social agriculture, and EGI. The specific objective of the project supports and promotes responsible involvement of citizenry by teaching a better understanding of the common good in terms of civic relationships with one another in correlation with social responsibility [55].

2.5. Province of Avellino

The “Irpinia Solidale” Voluntary Service Center, based in the city of Avellino, launched a number of projects that provision EGI-oriented urban allotment gardens. The aim was to reclaim green urban areas, redevelop them, and donate new small strips of abandoned land for agro-urban farming. The projects endow responsible biodiversity thinking, rediscover peasant traditions and human relationships, and build educative community-oriented nature-based solutions. Moreover, there is an encouraging level of solidarity among disadvantaged groups, including socio-integrative “green” spaces where EGI plays an active role in securing social networks and offering a positive cyclic-community response [56].

3. Concluding Remarks

The Campania region has several environmental, social, and criminal issues; nonetheless, application of the EGI approach may provide further food security and healthy living conditions. The development of numerous EGI-related regenerative projects and programs are exemplary for urban planners and thinkers alike; they can transform ruinous, abandoned, protected, or other types of urban-oriented landscape into a usable food source and lifestyle advantage. This perspective examined EGI with respect to the three-pillar approach (i.e., ecological, social, and economic co-benefits) by improving our understanding of food sources and, in particular, their proximity for city-dwellers [12,42]. In doing so, we recognized that increasing food security and decreasing food transport distances open up a vast array of interconnected advantages and services, since the majority of people worldwide live in urbanized areas. The concept reinforces low energy and minimizes chemical input practices, as well as decreases human consumption of processed foods, and it teaches people from all socioeconomic levels the equitable benefits of locally grown food. Moreover, EGI provides human health and well-being, and different EGI typologies provide different benefits, e.g., psychological and restorative benefits for allotment garden users versus domestic gardens [57].
Allotment gardens can be both tangible and intangible, as well as used for exercise, recreation, and community networking. These benefits can be extended to include space for meditation and solitude, as well as hobbyists being able to grow their own food in an idiosyncratic manner and for personal reasons. Allotment gardens have a social atmosphere to them. In conjunction with other EGI urban agricultural types, they offer excluded groups or individuals the ability to participate and become involved in the community at large. In this way, allotments can contribute to a sense of self-worth, as well as community—helping to shape a person’s livelihood and encourage overall social integration [58]. Negative aspects can include a lack of societal recognition outside of the project, especially if persons throughout the community do not appreciate the allotment-based system. A need to cater, as well as create a safe project environment, is key. This can require a number of resources which are not always available, including financial support, space allocation, and security (e.g., patrol and digital surveillance). As allotment gardens usually have restricted access, Colinas et al. [59] proposed that public produce, i.e., “specific types of urban agriculture wherein food is legally grown in public spaces and freely accessible to passersby” [59], might impact the community in a positive manner and perhaps encourage its widespread use and acceptance.
Like in the Campania region, many cities in Europe promote EGI [60]. For example, in the municipality of Paris, France, one-third of its green space is planned to be transformed into urban farms via three approaches: food security and education (i.e., by introducing a food to plate concept), high-rise farming (i.e., based upon the Parisculteurs project started in 2016), and workforce development (i.e., by offering persons the ability to make a living from the practice). Respectively, the Parisculteurs project comprises 75 projects situated throughout the city, covering 15 hectares and producing more than 500 tons of food [61,62]. From an observational perspective, this urban transformative phenomenon was seen throughout much of the developed world from the Far East of Asia [63,64] to Western Europe [12,14], and North America [65,66]. Moreover, international cases extend to the developing world, which is seeing a rise in interest. In Belem, Brazil, Madaleno [67] elucidated how the city implemented the concept of growing one’s own food as an important secondary source of food security—teaching its urbanite population the notion of grassroots food production and food economics. Urban agriculture, from this example, specifies animal husbandry, fruit trees, and “crops of basic grains and horticulture, which coexist in the city with tree crops, and the raising of rabbits, poultry, or other stock” [67]. As a result, edible areas can broaden the scope of urban agriculture by adding additional sources of nutrition, as well as creating environmental benefits (e.g., urban-based ecosystem services). Other important points that should not be overlooked include the impact upon the poor and needy in which urban planners can reuse (i.e., via regenerative practices) urban areas otherwise lost. In this sense, close attention to the different EGI typologies and developmental options should be site-specific. The assessment of implementing EGI may, therefore, play a role in providing city planners and policymakers with further recommendations for green space conservation and management. Such research should take account of how the greening and usage of EGI in urban environments (i.e., via urban design factors) can prevent crime (e.g., widespread graffiti and vandalism found throughout much of the cities researched in the Campania region [68,69]). In such circumstances, the design of EGI-friendly environments can provision safe spaces. Future research, beyond the scope of this work, should look at individual benefits in relation to the COVID-19 pandemic and its effects on food security and food supply chains. The use of EGI-friendly, agri-urban areas could also play an important role in post-lockdown—above all, for urban dwellers wanting to get in touch with less cementified surroundings [70,71]. Likewise, the health benefits of urban greening [72], in this regard, overlaps with social agricultural research since particularly vulnerable populations may have restricted movement in and out of their household. As such, the use EGI could be seen as essential—in terms of urban and social well-being—for these individuals.

Author Contributions

Conceptualization, investigation, and resources, A.R.; writing—original draft preparation, A.R.; methodology, validation, formal analysis, writing—review and editing, and visualization, A.R. and G.T.C. All authors have read and agreed to the published version of the manuscript.

Funding

This work was partially supported by the Polo Center of Sustainability, Italy, and the University of Gdansk, Poland.

Acknowledgments

We would like to thank the municipalities and personnel whose work and devotion from the ten case study projects reflect the broad level of EGI development needed throughout the Campania region. We consider, where applicable, the projects to be applicable to other parts of Italy and beyond.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Ramaswami, A.; Russell, A.G.; Culligan, P.J.; Sharma, K.R.; Kumar, E. Meta-principles for developing smart, sustainable, and healthy cities. Science 2016, 352, 940–943. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  2. Ackerman, K.; Conard, M.; Culligan, P.; Plunz, R.; Sutto, M.P.; Whittinghill, L. Sustainable food systems for future cities: The potential of urban agriculture. Econ. Soc. Rev. Irel. 2014, 45, 189–206. [Google Scholar]
  3. Murthy, V.H. Food insecurity: A public health issue. Public Health Rep. 2016, 131, 655–657. [Google Scholar] [CrossRef] [Green Version]
  4. Russo, A.; Escobedo, F.J.; Zerbe, S. Quantifying the local-scale ecosystem services provided by urban treed streetscapes in Bolzano, Italy. AIMS Environ. Sci. 2016, 3, 58–76. [Google Scholar] [CrossRef]
  5. Browder, G.; Ozment, S.; Bescos, I.R.; Gartner, T. Integrating Green and Gray: Creating Next Generation Infrastructure; World Bank and World Resources Institute: Washington, DC, USA, 2019. [Google Scholar]
  6. Zuniga-Teran, A.A.; Gerlak, A.K.; Mayer, B.; Evans, T.P.; Lansey, K.E. Urban resilience and green infrastructure systems: Towards a multidimensional evaluation. Curr. Opin. Environ. Sustain. 2020, 44, 42–47. [Google Scholar] [CrossRef]
  7. Wang, Y.; Bakker, F.; de Groot, R.; Wörtche, H. Effect of ecosystem services provided by urban green infrastructure on indoor environment: A literature review. Build. Environ. 2014, 77, 88–100. [Google Scholar] [CrossRef]
  8. Francis, L.F.M.; Jensen, M.B. Benefits of green roofs: A systematic review of the evidence for three ecosystem services. Urban For. Urban Green. 2017, 28, 167–176. [Google Scholar] [CrossRef]
  9. Venter, Z.S.; Shackleton, C.M.; Van Staden, F.; Selomane, O.; Masterson, V.A. Green Apartheid: Urban green infrastructure remains unequally distributed across income and race geographies in South Africa. Landsc. Urban Plan. 2020, 203, 103889. [Google Scholar] [CrossRef]
  10. Russo, A.; Cirella, G.T. Edible green infrastructure for urban regeneration: Case studies from the Campania Region, Italy. In Proceedings of the 4th International Symposium on Infrastructure Development, Hasanuddin University and Manado State Polytechnic, Manado, Indonesia, 12–14 October 2018. [Google Scholar]
  11. Russo, A.; Escobedo, F.J.; Cirella, G.T.; Zerbe, S. Edible green infrastructure: An approach and review of provisioning ecosystem services and disservices in urban environments. Agric. Ecosyst. Environ. 2017, 242, 53–66. [Google Scholar] [CrossRef]
  12. Russo, A.; Cirella, G.T. Edible urbanism 5.0. Palgrave Commun. 2019, 5, 1–9. [Google Scholar] [CrossRef]
  13. McLain, R.J.; Hurley, P.T.; Emery, M.R.; Poe, M.R. Gathering “wild” food in the city: Rethinking the role of foraging in urban ecosystem planning and management. Local Environ. 2014, 19, 220–240. [Google Scholar] [CrossRef] [Green Version]
  14. Landor-Yamagata, J.; Kowarik, I.; Fischer, L. Urban Foraging in Berlin: People, Plants and Practices within the Metropolitan Green Infrastructure. Sustainability 2018, 10, 1873. [Google Scholar] [CrossRef] [Green Version]
  15. Shackleton, C.M.; Hurley, P.T.; Dahlberg, A.C.; Emery, M.R.; Nagendra, H. Urban foraging: A ubiquitous human practice overlooked by urban planners, policy, and research. Sustainability 2017, 9, 1884. [Google Scholar] [CrossRef] [Green Version]
  16. Antisari, L.V.; Orsini, F.; Marchetti, L.; Vianello, G.; Gianquinto, G. Heavy metal accumulation in vegetables grown in urban gardens. Agron. Sustain. Dev. 2015, 35, 1139–1147. [Google Scholar] [CrossRef]
  17. Entwistle, J.A.; Amaibi, P.M.; Dean, J.R.; Deary, M.E.; Medock, D.; Morton, J.; Rodushkin, I.; Bramwell, L. An apple a day? Assessing gardeners’ lead exposure in urban agriculture sites to improve the derivation of soil assessment criteria. Environ. Int. 2019, 122, 130–141. [Google Scholar] [CrossRef]
  18. Ferreira, A.J.D.; Guilherme, R.I.M.M.; Ferreira, C.S.S.; de Oliveira, M.d.F.M.L. Urban agriculture, a tool towards more resilient urban communities? Curr. Opin. Environ. Sci. Health 2018, 5, 93–97. [Google Scholar] [CrossRef]
  19. Shimpo, N.; Wesener, A.; McWilliam, W. How community gardens may contribute to community resilience following an earthquake. Urban For. Urban Green. 2019, 38, 124–132. [Google Scholar] [CrossRef]
  20. Chandran, R. Grow Your Own: Urban Farming Is Flourishing during the Coronavirus Lockdowns; United Nations: London, UK, 2020. [Google Scholar]
  21. ICLEI. Nature-Based Solutions for Sustainable Urban Development (ICLEI Briefing Sheet); ICLEI: New York, NY, USA, 2017. [Google Scholar]
  22. Mancebo, F. Urban Agriculture for Urban Regeneration in the Sustainable City. In Quality of Life in Urban Landscapes; Grifoni, R.C., D’Onofrio, R., Sargolini, M., Eds.; Springer: Cham, Switzerland, 2018; pp. 311–317. [Google Scholar]
  23. Mancebo, F. Gardening the City: Addressing Sustainability and Adapting to Global Warming through Urban Agriculture. Environments 2018, 5, 38. [Google Scholar] [CrossRef] [Green Version]
  24. Mancebo, F. Confronting the Dark Side of Urban Agriculture. 2016. Available online: https://www.thenatureofcities.com/2016/04/08/confronting-the-dark-side-of-urban-agriculture/ (accessed on 10 August 2020).
  25. Colantonio, A.; Dixon, T. Urban Regeneration and Social Sustainability: Best Practice from European Cities; Wiley-Blackwell: London, UK, 2010; ISBN 978-1-405-19419-8. [Google Scholar]
  26. Czischke, D.; Moloney, C.; Turcu, C. State of the Art on Sustainable Regeneration in Urban Areas, URBACT II Capitalisation; URBACT: Saint-Denis, France, 2014. [Google Scholar]
  27. Garnett, T. City Harvest: The Feasibility of Growing More Food in London; Sustain: London, UK, 1999. [Google Scholar]
  28. Sousa, R.; Sales, D. Urban Agriculture: The Allotment Gardens as Structures of Urban Sustainability. In Advances in Landscape Architecture; InTech: London, UK, 2013. [Google Scholar]
  29. Regional Council of Campania. Regional Law n. 5: Norme in Materia di Agricoltura Sociale e Disciplina delle Fattorie e Degli Orti Sociali e Modifiche alla Legge Regionale 7 Marzo 1996, n. 11; Regional Government of Campania: Naples, Italy, 2012.
  30. Jansson, J.K.; Hofmockel, K.S. Soil microbiomes and climate change. Nat. Rev. Microbiol. 2020, 18, 35–46. [Google Scholar] [CrossRef]
  31. Hou, D.; O’Connor, D.; Igalavithana, A.D.; Alessi, D.S.; Luo, J.; Tsang, D.C.W.; Sparks, D.L.; Yamauchi, Y.; Rinklebe, J.; Ok, Y.S. Metal contamination and bioremediation of agricultural soils for food safety and sustainability. Nat. Rev. Earth Environ. 2020, 1, 366–381. [Google Scholar] [CrossRef]
  32. Cassidy, E.S.; West, P.C.; Gerber, J.S.; Foley, J.A. Redefining agricultural yields: From tonnes to people nourished per hectare. Environ. Res. Lett. 2013, 8, 034015. [Google Scholar] [CrossRef]
  33. Tóth, G.; Hermann, T.; Da Silva, M.R.; Montanarella, L. Heavy metals in agricultural soils of the European Union with implications for food safety. Environ. Int. 2016, 88, 299–309. [Google Scholar] [CrossRef] [PubMed]
  34. Mulligan, C.N.; Yong, R.N.; Gibbs, B.F. Remediation technologies for metal-contaminated soils and groundwater: An evaluation. Eng. Geol. 2001, 60, 193–207. [Google Scholar] [CrossRef]
  35. Hallett, S.; Hoagland, L.; Toner, E. Urban Agriculture: Environmental, Economic, and Social Perspectives. In Horticultural Reviews; John Wiley & Sons, Inc.: Hoboken, NJ, USA, 2016; Volume 44, pp. 65–120. [Google Scholar]
  36. Włodarczyk-Marciniak, R.; Sikorska, D.; Krauze, K. Residents’ awareness of the role of informal green spaces in a post-industrial city, with a focus on regulating services and urban adaptation potential. Sustain. Cities Soc. 2020, 59, 102236. [Google Scholar] [CrossRef]
  37. Alon-Mozes, T. Landscape Architecture and Agriculture: Common Seeds and Diverging Sprigs in Israeli Practice. Landsc. J. 2009, 28, 166–180. [Google Scholar] [CrossRef]
  38. Hoban, P. Agnes Denes’ Prophetic Wheatfield Remains As Relevant As Ever. Available online: https://www.architecturaldigest.com/story/agnes-denes-prophetic-wheatfield-remains-as-relevant-as-ever (accessed on 9 August 2020).
  39. Jégou, F.; Carey, J. Creating Space for Sustainable Food Systems in Urban Communities: Practical Approaches and Examples for Cities; Strategic Design Scenarios Publishing: Brussels, Belgium, 2015; ISBN 9782960131413. [Google Scholar]
  40. Rusciano, V.; Civero, G.; Scarpato, D. Urban Gardening as a New Frontier of Wellness: Case Studies from the City of Naples. Int. J. Sustain. Econ. Soc. Cult. Context 2017, 13, 39–49. [Google Scholar] [CrossRef]
  41. Istat Ambiente Urbano. Available online: https://www.istat.it/it/archivio/225505 (accessed on 2 June 2020).
  42. Russo, A.; Cirella, G.T. Edible Green Infrastructure 4.0 for Food Security and Well-being: Campania Region, Italy. In International Guidelines on Urban and Territorial Planning. Compendium of Inspiring Practices: Health Edition; Quinlan, V., Ed.; UN Habitat: Nairobi, Kenya, 2018; p. 72, HS/080/18E. [Google Scholar]
  43. Regional Council of Campania. B.U.R.C. n. 69 of 16/11/2009; Regional Government of Campania: Naples, Italy, 2009.
  44. Ortoinrete Il Network. Available online: http://www.ortoinrete.it/il-network/ (accessed on 2 June 2020).
  45. Legambiente Campania. Orti Urbani di Legambiente; Legaambientale: Naples, Italy, 2018. [Google Scholar]
  46. Organisation for Economic Co-operation and Development. The Italian case studies. COM/TAD/CA/ENV/EPOC(2012)11/FINAL. In Providing Agri-Environmental Public Goods through Collective Action; OECD: Rome, Italy, 2013; pp. 191–203. [Google Scholar]
  47. Marella, R. Lo spazio urbano come bene comune. Sci. Del Territ. Firenze Univ. Press 2015, 3, 78–87. [Google Scholar] [CrossRef]
  48. Legambiente. Legambiente Occhi Verdi; Legaambientale: Rome, Italy, 2016. [Google Scholar]
  49. Fischer, L.K.; Brinkmeyer, D.; Karle, S.J.; Cremer, K.; Huttner, E.; Seebauer, M.; Nowikow, U.; Schütze, B.; Voigt, P.; Völker, S. Biodiverse edible schools: Linking healthy food, school gardens and local urban biodiversity. Urban For. Urban Green. 2019, 40, 35–43. [Google Scholar] [CrossRef]
  50. TV7. Bosco Lucarelli: Al Via Progetto Sperimentale su Coltivazione Orti Urbani. Available online: https://www.tvsette.net/2018/02/01/bosco-lucarelli-al-via-progetto-sperimentale-su-coltivazione-orti-urbani/ (accessed on 2 June 2020).
  51. Ortoinrete Gramigna—Orto di Casa Betania—Benevento. Available online: http://www.ortoinrete.it/il-network/gramigna-orto-di-casa-betania/ (accessed on 2 June 2020).
  52. Ridente, P.; Mezzina, R. From Residential Facilities to Supported Housing: The Personal Health Budget Model as a Form of Coproduction. Int. J. Ment. Health 2016, 45, 59–70. [Google Scholar] [CrossRef]
  53. Esperienze con il Sud Valorizziamo Scampia. Available online: http://www.napolicittasolidale.it/portal/ncs/primo-piano/5067-valorizziamo-scampia.html (accessed on 14 May 2020).
  54. Ferrante, M.C.; Fusco, G.; Monnolo, A.; Saggiomo, F.; Guccione, J.; Mercogliano, R.; Clausi, M.T. Food contamination by PCBs and waste disposal crisis: Evidence from goat milk in Campania (Italy). Chemosphere 2017, 186, 396–404. [Google Scholar] [CrossRef]
  55. Geofilos Orti.net. Available online: www.orti.net (accessed on 2 June 2020).
  56. Irpinia Solidale. Orti sociali: Al Via le Manifestazioni di Interesse per Partecipare al Nuovo Progetto del CSV. Available online: http://www.orticalab.it/Orti-Sociali-al-via-le (accessed on 14 May 2020).
  57. Young, C.; Hofmann, M.; Frey, D.; Moretti, M.; Bauer, N. Psychological restoration in urban gardens related to garden type, biodiversity and garden-related stress. Landsc. Urban Plan. 2020, 198, 103777. [Google Scholar] [CrossRef]
  58. Acton, L. Allotment Gardens: A Reflection of History, Heritage, Community and Self. Pap. Inst. Archaeol. 2011, 21, 46. [Google Scholar] [CrossRef] [Green Version]
  59. Colinas, J.; Bush, P.; Manaugh, K. The socio-environmental impacts of public urban fruit trees: A Montreal case-study. Urban For. Urban Green. 2019, 45, 126132. [Google Scholar] [CrossRef]
  60. Bell, S.; Fox-Kämper, R.; Keshavarz, N.; Benson, M.; Caputo, S.; Noori, S.; Voigt, A. Urban Allotment Gardens in Europe; Routledge: New York, NY, USA, 2016; ISBN 9781315686608. [Google Scholar]
  61. Ville de Paris. Les Parisculteurs project. Available online: http://www.parisculteurs.paris/en/ (accessed on 18 July 2020).
  62. Wong, K. Paris to Turn a Third of its Green Space into Urban Farms. Available online: https://edition.cnn.com/style/article/urban-farms-in-paris/index.html (accessed on 18 July 2020).
  63. Van Dijk, M.P. Three Ecological Cities, Examples of Different Approaches in Asia and Europe. In Eco-City Planning; Wong, T.C., Yuen, B., Eds.; Springer: Dordrecht, The Netherlands, 2011; pp. 31–50. ISBN 978-94-007-0383-4. [Google Scholar]
  64. Chui, E. Doomed Elderly People in a Booming City: Urban Redevelopment and Housing Problems of Elderly People in Hong Kong. Hous. Theory Soc. 2001, 18, 158–166. [Google Scholar] [CrossRef]
  65. Russo, A.; Cirella, G.T. Urban Sustainability: Integrating Ecology in City Design and Planning. In Sustainable Human–Nature Relations: Environmental Scholarship, Economic Evaluation, Urban Strategies; Cirella, G.T., Ed.; Springer: Singapore, 2020; pp. 187–204. [Google Scholar]
  66. McLain, R.; Poe, M.; Hurley, P.T.; Lecompte-Mastenbrook, J.; Emery, M.R. Producing edible landscapes in Seattle’s urban forest. Urban For. Urban Green. 2012, 11, 187–194. [Google Scholar] [CrossRef] [Green Version]
  67. Madaleno, I. Urban agriculture in Belem, Brazil. Cities 2000, 17, 73–77. [Google Scholar] [CrossRef]
  68. Allum, F. Becoming a camorrista: Criminal culture and life choices in Naples. J. Mod. Ital. Stud. 2010, 6, 324–347. [Google Scholar] [CrossRef]
  69. Blackburn, K.; Neanidis, K.C.; Rana, M.P. A theory of organized crime, corruption and economic growth. Econ. Theory Bull. 2017, 5, 227–245. [Google Scholar] [CrossRef] [Green Version]
  70. Mushtaq, R.; Shoib, S.; Shah, T.; Mushtaq, S. Relationship Between Loneliness, Psychiatric Disorders and Physical Health? A Review on the Psychological Aspects of Loneliness. J. Clin. Diagn. Res. 2014, 8. [Google Scholar] [CrossRef]
  71. Rajkumar, R.P. COVID-19 and mental health: A review of the existing literature. Asian J. Psychiatr. 2020, 52, 102066. [Google Scholar] [CrossRef]
  72. Russo, A.; Cirella, G.T. Modern Compact Cities: How Much Greenery Do We Need? Int. J. Environ. Res. Public Health 2018, 15, 2180. [Google Scholar] [CrossRef] [PubMed] [Green Version]
Figure 1. Key urban agricultural and EGI-oriented projects labeled (i.e., yellow points) within the provinces of the Campania region, Italy. Source: Google Earth.
Figure 1. Key urban agricultural and EGI-oriented projects labeled (i.e., yellow points) within the provinces of the Campania region, Italy. Source: Google Earth.
Agriculture 10 00358 g001
Figure 2. Example of a restorative dig site within the archaeological park in Pontecagnano, Salerno. Left—archaeological dig site; right—map of archaeological dig site. Source: Photographs taken by A. Russo on 16 July 2018.
Figure 2. Example of a restorative dig site within the archaeological park in Pontecagnano, Salerno. Left—archaeological dig site; right—map of archaeological dig site. Source: Photographs taken by A. Russo on 16 July 2018.
Agriculture 10 00358 g002
Figure 3. Urban agricultural and EGI integrated zoning within the archaeological ark in Pontecagnano, Salerno. Top left—park map; top right—entrance allotment garden; bottom left—allotment garden; bottom right—allotment garden socialization space. Source: Photographs taken by A. Russo on 16 July 2018.
Figure 3. Urban agricultural and EGI integrated zoning within the archaeological ark in Pontecagnano, Salerno. Top left—park map; top right—entrance allotment garden; bottom left—allotment garden; bottom right—allotment garden socialization space. Source: Photographs taken by A. Russo on 16 July 2018.
Agriculture 10 00358 g003
Figure 4. De Filippo park of Ponticelli, Naples. Top—allotment gardens; bottom—aerial view of the park. Source: Top—photographs taken by A. Russo on 30 May 2018; bottom—Google Earth
Figure 4. De Filippo park of Ponticelli, Naples. Top—allotment gardens; bottom—aerial view of the park. Source: Top—photographs taken by A. Russo on 30 May 2018; bottom—Google Earth
Agriculture 10 00358 g004
Figure 5. Aerial view of Ciro Esposito park, Scampia, Naples. Source: Google Earth.
Figure 5. Aerial view of Ciro Esposito park, Scampia, Naples. Source: Google Earth.
Agriculture 10 00358 g005
Table 1. Types of regeneration policies, plans, and actions from an environmental dimension. EGI—edible green infrastructure; URBACT II—Urban Development Network Program II.
Table 1. Types of regeneration policies, plans, and actions from an environmental dimension. EGI—edible green infrastructure; URBACT II—Urban Development Network Program II.
Energy Transportation
Energy efficiency in buildings
Energy demand management and fuel poverty (nonphysical)
Energy generation (renewables)
District heating and smart grids
Cycling and walking
Public transportation and modal shift
“Smart travel” and car pooling
LandWater
Densification of existing urban areas
Urban infill
Change of land use in response to local needs
Water conservation
Sustainable urban drainage
WasteFood
Waste recycling and reductionUrban agriculture
EGI
Others
Urban biodiversity and sustainable landscape architecture
Use of local construction materials and contractors
“Taxation” on consumption (non-physical)
Behavioral “nudges” for more pro-environmental behavior (non-physical)
adapted from the URBACT II report [26].
Table 2. EGI case studies in the Campania region.
Table 2. EGI case studies in the Campania region.
ProvinceCase StudyEGI TypeMain Benefits and Aims
SalernoMatti per l’ortoAllotment garden
Sustainable social integration of mentally ill, disabled, and minors at risk
Encourage senior citizens (i.e., over 65 years of age) urban farming and leisure time (with particular attention to the most disadvantaged)
Urban regeneration (i.e., recover and remake fractional areas usable and productive for small needs)
Food security
Gardens of the Mediterranean dietUrban farm, domestic garden
Healthy diet
Food security
OrtoMondoAllotment garden
Migrant inclusion
archaeological parkAllotment garden
Tourism
Education
Horticultural therapy
Cultural events
Benevento“Bosco Lucarelli” InstituteSchool garden
Education
Buon orto fa buon sangueAllotment garden, urban farm
Environmental sustainability
Convivial sociability
Food security
NaplesDe Filippo parkUrban park
Crime reduction
Horticultural therapy
Education
Ciro Esposito parkUrban park
Crime reduction
Education
CasertaOrti.net, coltiviamo la socialit@CasertaAllotment garden
Social agriculture
Urban regeneration
Education
Food security
AvellinoIrpinia SolidaleAllotment garden
Biodiversity thinking
Rediscover peasant traditions and human relationships
Build educative community-oriented nature-based solutions
Urban regeneration

Share and Cite

MDPI and ACS Style

Russo, A.; Cirella, G.T. Edible Green Infrastructure for Urban Regeneration and Food Security: Case Studies from the Campania Region. Agriculture 2020, 10, 358. https://doi.org/10.3390/agriculture10080358

AMA Style

Russo A, Cirella GT. Edible Green Infrastructure for Urban Regeneration and Food Security: Case Studies from the Campania Region. Agriculture. 2020; 10(8):358. https://doi.org/10.3390/agriculture10080358

Chicago/Turabian Style

Russo, Alessio, and Giuseppe T. Cirella. 2020. "Edible Green Infrastructure for Urban Regeneration and Food Security: Case Studies from the Campania Region" Agriculture 10, no. 8: 358. https://doi.org/10.3390/agriculture10080358

APA Style

Russo, A., & Cirella, G. T. (2020). Edible Green Infrastructure for Urban Regeneration and Food Security: Case Studies from the Campania Region. Agriculture, 10(8), 358. https://doi.org/10.3390/agriculture10080358

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop