Informatics Educational Institutions & Programs

Kupittaa Park [fi] (Kupittaanpuisto) is a large urban open space area in Turku, Southwest Finland. At the same time, it is also the largest and oldest park in Finland.[1][2]
Asramam Maidan in Kollam city, India. It is the largest open space available in any of the city limits in Kerala state.
A grassy area with tall trees leaving shadows from the sun above. In the distance are small rowhouses, and a street is at the right.
Washington Park in Troy, NY, U.S, an example of privately owned urban open space.

In land-use planning, urban green spaces are open-space areas reserved for parks and other "green spaces", including plant life, water features – also referred to as blue spaces – and other kinds of natural environment.[3] Most urban open spaces are green spaces, but occasionally include other kinds of open areas. The landscape of urban open spaces can range from playing fields, to highly maintained environments, to relatively natural landscapes.

Generally considered open to the public, urban green spaces are sometimes privately owned, such as higher education campuses, neighborhood/community parks/gardens, and institutional or corporate grounds. Areas outside city boundaries, such as state and national parks as well as open space in the countryside, are not considered urban open space. Streets, piazzas, plazas and urban squares are not always defined as urban open space in land use planning. Urban green spaces have wide-reaching positive impacts on the health of individuals and communities near the green space.[3]

Urban greening policies are important for revitalizing communities, reducing financial burdens of healthcare and increasing quality of life. By promoting the development of parks, green roofs, and community gardens, these policies contribute to cleaner air, mitigate urban heat effects, and create spaces for recreation and social interaction. Most policies focus on community benefits and reducing negative effects of urban development, such as surface runoff and the urban heat island effect.[4] Historically, access to urban green space has favored wealthier and more privileged communities; thus, recent urban greening has increasingly focused on environmental justice concerns, and community engagement in the greening process.[5] In particular, in cities with economic decline, such as the Rust Belt in the United States, urban greening has broad community revitalization impacts.[5]

Urban areas have greatly expanded, resulting in over half of the world's population being located in urban locations.[6] As the population continues to grow, this number is predicted to be at two-thirds of people living in urban areas by 2050.[6]

Definitions and concepts

The World Health Organization (WHO) defined urban green spaces as "all urban land covered by vegetation of any kind".[3] When doing research, some experts use "urban open space" to describe a broader range of open areas. One definition holds that "As the counterpart of development, urban open space is a natural and cultural resource, synonymous with neither 'unused land' nor 'park and recreation areas'." Another defines urban open space as "land and/or water area with its surface open to the sky, consciously acquired or publicly regulated to serve conservation and urban shaping function in addition to providing recreational opportunities."[7] In almost all instances, the space referred to by the term is green space, focused on natural areas.[8]

The spaces that are part of "public space" are broadly construed, including meeting or gathering places that exist outside the home and workplace. These foster resident interaction and opportunities for contact and proximity.[9] This definition implies a higher level of community interaction and places a focus on public involvement rather than public ownership or stewardship.

Benefits

The benefits that urban open space provides to citizens can be broken into four basic forms: recreation, ecology, aesthetic value, and positive health impacts. Psychological research shows that benefits gained by visitors to urban green spaces increased with their biodiversity,[10][11][12] indicating that "green" alone is not optimal; the quality of the urban green space is important as well.

Recreational

Sad Janka Kráľa park in Bratislava (Slovakia)

Urban open space is often appreciated for the recreational opportunities it provides. Examples of recreation in urban open spaces include active recreation (such as organized sports and individual exercise) and passive recreation. Research shows that when open spaces are attractive and accessible, people are more likely to engage in physical activity.[13] Time spent in an urban open space for recreation offers a reprieve from the urban environment and a break from over-stimulation.[14] Studies done on physically active adults middle-aged and older show that there are amplified benefits when physical activities are coupled with green space environments. Such coupling leads to decreased levels of stress, lowers the risk for depression, and increases the frequency of participation in exercise.[15]

Ecological

Blackstone Park Conservation District, an urban conservation area in Providence, Rhode Island.

Green spaces may improve the air quality of urban areas and provide habitat for wildlife, improving the overall ecological health of urban environments. They may also reduce the risk of flooding by providing rainwater drainage.[16]

Aesthetic

The aesthetic value of urban open spaces is self-evident. People enjoy viewing nature, especially when it is otherwise extensively deprived, as is the case in urban environments. Therefore, open space offers the value of "substituting gray infrastructure."[17] One researcher states how attractive neighborhoods contribute to positive attitudes and social norms that encourage walking and community values.[18] Properties near urban open space tend to have a higher value. One study was able to demonstrate that, "a pleasant view can lead to a considerable increase in house price, particularly if the house overlooks water (8–10%) or open space (6–12%)."[19] Certain benefits may be derived from exposure to virtual versions of the natural environment, too. For example, people who were shown pictures of scenic, natural environments had increased brain activity in the region associated with recalling happy memories, compared to people that were shown pictures of urban landscapes.[20]

Impact on health

The World Health Organization considers urban green spaces as important to human health. These areas have a positive impact on mental and physical health.[21] Urban open spaces often include trees or other shrubbery that contribute to moderating temperatures and decreasing air pollution.[22][23] Perceived general health is higher in populations with a higher percentage of green space in their environments.[24] Urban open space access has also been directly related to reductions in the prevalence and severity of chronic diseases resulting from sedentary lifestyles, to improvements in mental well-being, and to reductions in population-wide health impacts from climate change.[25]

Mechanism of urban open space health effects

Access to urban open space encourages physical activity and reduces ambient air pollution, heat, traffic noise and emissions.[26] All are factors which contribute to the risks of chronic disease and mental illness. Individuals and families who lived closer to ‘formal’ parks or open space were more likely to achieve the recommended amounts of physical activity.[27] Better respiratory health is associated with cleaner air quality.[28] Cleaner air quality affects rates of chronic disease in populations exposed. “High concentrations of ambient particles can trigger the onset of acute myocardial infarction and increase hospitalization for cardiovascular disease”.[29] Besides an association with lower Body Mass Index (BMI)/obesity rates, this physical activity can increase lung function and be a protective factor against respiratory disease.[30] Exposure to nature improves the immune system. Contact of the human body with soil, turf, or forest floor, exposes it to many microorganisms which boost the immune system.[31]

Reductions in chronic disease rates

Improved access to green space is associated with reductions in cardiovascular disease symptoms, improved rates of physical activity, lower incidence of obesity, and improved respiratory health. Lower rates of cardiovascular biomarkers are associated with access to green space, showing a reduction in cardiovascular disease risk in populations living within 1 km of green space. Not only does access to urban green space reduce risk of cardiovascular disease, but increased access has been shown to improve recovery from major adverse cardiovascular events and lower all-cause mortality.[26] Relationships have been found between increased access to green space, improved rates of physical activity, and reduced BMI.[27] The percentage of sedentary and moderately active persons making use of an urban park increased when access to the park was improved.[32]

Reductions in mental illness rates and improvement of social cohesion

Globally, mental illness is linked to eight million deaths each year.[33] In urban areas, limited access to green space and poor quality of green spaces available may contribute to poor mental health outcomes; according to some studies, people living in cities and towns may have weaker mental health in comparison to people living in less crowded areas. Urban green spaces are pieces of nature in the cities designed to try to solve the problem.[34] The distance an individual lives from a green space or park and the proportion of land designated as open space/parks has been shown to be inversely related to anxiety/mood disorder treatment counts in the community. Improved mental health may therefore be related to both measures – to distance from open space and proportion of open space within a neighborhood.[35] Even when physical activity rates are not shown to increase with greater access to green space, greater access to green space has been shown to decrease stress and improve social cohesion.[36]

Effects on respiratory health

Adequate urban green space access can be associated with better respiratory health outcomes, as long as green space areas meet certain requirements. A study showed that mortality due to pneumonia and chronic lower respiratory diseases could be reduced by minimizing fragmentation of green spaces and increasing the largest patch percentage of green space.[37] Vegetation type (trees, shrubs and herbaceous layers) and lack of management (pruning, irrigation and fertilization) has been shown to affect a higher capacity to provide the ecosystem services of air purification and climate regulation within green urban spaces.[38] The types of plants and shrubs are important because areas with large tree canopies can contribute to asthma and allergic sensitization.[39]

Impacts on high temperatures

Urban areas tend to have higher temperatures than their surrounding undeveloped areas because of Urban heat islands, UHIs. Urban heat islands are areas with man-made infrastructure that contribute to increased temperatures.[23][40] The average temperature during the day in cities can be 18–27 degrees Fahrenheit higher than in the surrounding rural regions.[23] This is an example of one type of UHI, surface heat islands. Surface heat islands encompass the area from the ground to the top of the tree-line. It is usually higher during the day when direct sunlight reaches urban structures (often with darker materials than natural areas) including the main contributor, pavement. The other type of UHI, atmospheric heat islands, are from above the tree-line to the level in the atmosphere where the urban area no longer has an effect. This type of heat island has increased heat at night due to the release of heat from infrastructure that built up throughout the day.[23]

Green spaces within urban areas can help reduce these increased temperatures through shading and evapotranspiration.[40][41] Shading comes from the taller plants, such as trees, that can contribute to lowering the surface heat island effect. The shade provides protection from the sun for vulnerable populations, such as children, during periods of increased temperature, during the summer months or during a heat wave. Tree cover prevents some solar radiation from reaching the ground with its leaves and branches.[22][23] This reduces the effect of surface urban heat islands. Open spaces that include any type of vegetation help offset the high temperatures through the natural process of evapotranspiration. Evapotranspiration releases water into the air therefore dissipating heat.[22] There are many elements of an urban open space that can contribute to the mitigation of urban heat islands including the type of open space (park or nature reserve), type of plant species, and the density of vegetation.[22] Green spaces contribute to the reduction of local heat, decreasing the overall effect of UHIs. The larger the distribution of green spaces, the bigger the area of heat reduction. Green spaces that are clustered together will have an additive heat reduction resulting in a greater decrease in temperature in the local area compared to surrounding areas.[41]

Impacts on air quality

Human activity has increased air pollution in the Earth's atmosphere and trees play an essential role in removing human-made pollutants from the air, aka particulate matter (PM). Trees produce oxygen and absorb CO2. In urban green spaces, trees filter out man-made pollutants. Air quality data collected on cities with and without urban green space has shown that areas with an abundance of trees have considerably less air pollutants, i.e. O3, PM10, NO2, SO2, and CO.[42] As air pollutants accumulate in the atmosphere, vulnerable populations, such as children, may suffer from increased incidences[spelling?] of respiratory disease.[42] Particulate matter or particle pollution with a diameter of 10 microns (PM10) or 2.5 microns (PM2.5) is associated with heart diseases and respiratory diseases including lung cancer.[43]

Globally, particulate matter has increased over 28% in indoor air and 35% in outdoor air. Children spend most of their time at school, around 10 hours daily, and the indoor and outdoor air has a large impact on their health. Schools located in urban areas have higher particulate matter than schools in rural areas. Compared with children in schools located in rural areas, children who attend schools located in industrial areas and urban cities have higher levels of urinary PAHs (polycyclic aromatic hydrocarbons) metabolites, which is linked to air pollution.[44]

Green spaces can reduce the pollution of particulate matter by preventing distribution of particulates from pollutants or by reducing the particulate matter from traveling to other places.[43] There is a disagreement about the association of living near green spaces or having high exposure to greenness and illness such as allergies, rhinitis, and eye and nose symptoms.[45] Higher exposure to tree canopy and pollen was associated with a high risk of prevalence rhinitis, allergic sensitization, wheezing, and asthma among children 7 years-old.[39] More studies are needed to explain the effect of urban green spaces on children relating to air quality. These studies should take into consideration the interconnectedness of tree species, geographic areas, temperature, and other pollutant-like traffic.[45]

For children and adolescents

Impacts on physical health

The adolescent years are important for children due to it being a time of growth, development, and instillation of habits. When children are given the opportunity to be active, they typically take advantage of it. Children with a greater access to parks and recreational facilities through urban green space have been found to be more active than children who lack access.[46] The access to green spaces has shown an association with recreational walking, increased physical activity, and reduced sedentary time in all ages.[47] In coordination, it has been seen that higher residential green space is associated with lower BMI scores.[6] If children are given the opportunity to be active and maintain a healthy BMI in their adolescent years, they are less likely to be obese as adults.[46]

Impacts on mental health

Children exposed to urban green spaces have the opportunity to expend energy by interacting with their environment and other people through exercise. One study has shown that without access to urban green spaces, some children have problems with hyperactivity, peer interactions, and good conduct.[6] The important interactions with nature, animals, and peers have been positively influential in child development and reduction in behavioral issues such as Attention Deficit Hyperactivity Disorder (ADHD).[46][47] With urban green space giving children the opportunity to get outside and expend energy, children are more focused in school and have a better working memory and reduced inattentiveness.[48]

Another facet of urban green space improving mental health is giving children access to a community. Recreational activities and playing at the park gives children opportunities to interact with other children and develop a social circle and social skills in general.[47] Children with a good social network feel socially included, promoting more confidence and well-being in their everyday lives. Overall, the bonding experiences that result from urban green spaces tie in with a child's cognitive and social development.[49]

Ocotal forest, Mexico City

A 2021 study found that higher exposure to woodland urban green spaces or urban forest but not grassland is associated with improved cognitive development and reduced risks of mental problems for urban adolescents.[50][51]

History

Ancient Rome

The term "rus in urbe" meaning "country in the city" was used in Rome around the first century C.E.[52] Urban planning in Rome valued the natural landscape and took account for environmental factors. It was thought that by building a city with regard to the local countryside, the people living there would be healthier and happier.[53] English landscapes would later take inspiration from Roman urban planning concepts in their own open spaces.[54]

Islamic Era

Islamic gardens are distinctive green spaces that blend cultural, religious, and practical elements, serving as earthly representations of paradise. Typically featuring symmetrical designs, often in a four-fold pattern called chahar bagh or chahār bāgh with fountains, flowing channels, or reflective pools. Modern interpretations of Islamic gardens can be found in various locations, such as the Islamic Gardens at King's Cross in London, which showcase contemporary landscaped spaces representing the diversity of Muslim culture.[55] The concept of Islamic gardens spread widely from Persia to Spain, North Africa, and India, influencing garden design across various Islamic empires. While maintaining core principles, these gardens often incorporated local elements and adapted to regional climate.[56][57]

London

Main article: Parks and open spaces in London
Aerial view of Hyde Park in London, England

London, England has a long history of urban open space, which has influenced development of modern parks, and is among the greenest capital cities in the world.[58]

The basis for many urban open spaces seen today across Europe and the West began its process of development in London in the 17th and 18th centuries. What would eventually become urban open green space began as paved public plazas. Though they were intended to be open to the public, these spaces began to be re-designated as private parks around the late eighteenth century. It was during this period that the areas became pockets of green in the urban environment, commonly modelled after the natural wild of the countryside.[59]

The first parks to reverse the trend of privatization and again be opened to the public were England's royal parks in the nineteenth century. This was done in response to the extensive and unexpected population movement from the country into cities. As a result, "the need for open space was socially and politically pressing… The problems, to which the provision of parks was expected to offer some relief, were easy to describe: overcrowding, poverty, squalor, ill-health, lack of morals and morale, and so on".[60]

China

China's Fourteenth Five-Year Plan's Climate Change Special Plan emphasizes ecologically-oriented urban planning, including the use of urban green rings.[61]: 114 

Segmentation of urban open spaces was particularly prominent in America during the twentieth century. Since the late 1800s romantic park systems, open space designers have been concerned with guiding, containing or separating urban growth, distributing recreation, and/or producing scenic amenity, mostly within the framework of geometric abstractions."[62] Such segmentation was especially prominent in the 1990s, when urban open spaces took a path similar to that of parks, following the modernization trend of segmentation and specialization of areas.[63] As modernity stressed "increased efficiency, quantifiability, predictability, and control… In concert with the additional social divisions",[63] open spaces grew more specific in purpose.

In the 20th century, places like Scandinavia saw a proliferation of urban open spaces and began adopting a lifestyle supported by the extra urban breathing room. An example of this can be seen in Copenhagen where an area closed to car traffic in 1962 developed, in just a few decades, a culture of public political gatherings and outdoor cafes emerged.[64]

Non-sustainable gardening, including mowing, use of chemical fertilisers, herbicides and pesticides harm green spaces.[65][66] Contrariwise, one of the conditions for good urban open space is sustainable gardening.[67]

At the beginning of the 21st century, studies began to show that living in areas near water (known as "blue spaces") considerably improved physical and mental health, increasing life longevity.[34]

Inequalities

Neighborhoods with higher percentages of minority residents often have lower access to open space and parks as the result of past red-lining policies and current inequities in funding priorities.[68] Urban open space is under strong pressure. Due to increasing urbanization, combined with a spatial planning policy of densification, more people face the prospect of living in less green residential environments, especially people from low economic strata. This may cause environmental inequality with regard to the distribution of (access) to public green space.[69] The parks that do exist in minority neighborhoods are often small (with lower acreage per person than parks in majority ethnicity neighborhoods), not well maintained, unsafe, or are otherwise ill-suited for community needs.[70] A large epidemiological study[71] concluded that wealthier individuals were generally healthier than individuals with a lower income, explained by the pattern that wealthier individuals reside in areas more concentrated with green space. Urban open spaces in higher socioeconomic neighborhoods were also more likely to have trees that provided shade, a water feature (e.g. pond, lake or creek), walking and cycling paths, lighting, signage regarding dog access and signage restricting other activities as well.[72] This difference in access has been proven, however, further study is needed to evaluate the exact health impacts.

A study conducted in Australia provided insight into how there is a correlation between community development/community safety and natural open space within the community. Open areas allow community members to engage in highly social activities and facilitate the expansion of social networks and friendship development. As people become more social they decrease the perceptions of fear and mistrust allowing a sense of community.[9] Distant or lack of adequate green space, therefore, may contribute to higher rates of inactivity and greater health effects among minority populations.[73]

Green gentrification

This section is an excerpt from Environmental gentrification.[]
Environmental, ecological or green gentrification is a process in which cleaning up pollution or providing green amenities increases local property values and attracts wealthier residents to a previously polluted or disenfranchised neighbourhood.[74][75][76] Green amenities include green spaces, parks, green roofs, gardens and green and energy efficient building materials.[77] These initiatives can heal many environmental ills from industrialization and beautify urban landscapes. Additionally, greening is imperative for reaching a sustainable future. However, if accompanied by gentrification, these initiatives can have an ambiguous social impact.[78] More specifically, in certain cases the introduction of green amenities might lead to (1) the physical displacement of low income households due to soaring housing costs,[76] and/or (2) the cultural, social, and political displacement of long-time residents.[79] First coined by Sieg et al. (2004),[80] environmental gentrification is a relatively new concept, although it can be considered as a new hybrid of the older and wider topics of gentrification and environmental justice. Social implications of greening projects specifically with regards to housing affordability and displacement of vulnerable citizens. Greening in cities can be both healthy and just.

See also

  • Blue space – Areas dominated by surface waterbodies
  • Eco-cities – Human settlement closely modeled on natural ecosystems
  • Green belt – Largely undeveloped, wild, or agricultural land surrounding urban areas
  • Green track – Railway trackbed planted with grass or other vegetation
  • Greening – Process of incorporating more environmentally friendly behaviors or systems
  • Greenway (landscape) – Shared-use path or linear park with vegetation
    • Linear park – Long strip of naturally occurring land for recreation
    • Rail trail – Railroad bed converted to a recreational trail
  • Open space reserve – Conserved land or water
  • Park – Area of naturally occurring land set aside for visitor enjoyment and other purposes
  • Particulates – Microscopic solid or liquid matter suspended in the Earth's atmosphere
  • Principles of Intelligent Urbanism – Theory of urban planning
  • Sustainable city – City designed with consideration for social, economic, environmental impact
  • Urban forest – Collection of trees within a city, town or a suburb
  • Urban prairie – Vacant urban land reverted to green space
  • Urban reforestation – Planting of trees in urban environments
  • Urban vitality – Intensity of use of an urban area
  • Village green – Common open area within a settlement
  • Wildlife corridor – Connecting wild territories for animals

References

  1. ^ Kupittanpuisto – Kupittaa Park
  2. ^ Kupittaa Park – Kiss My Turku
  3. ^ a b c Urban green spaces: a brief for action. UN City, Denmark: World Health Organization Regional Office for Europe. 2017.
  4. ^ "Nature of Cities". Regeneration.org. Retrieved 2021-10-16.
  5. ^ a b "Ep. 51: Urban Greening with Sandra Albro". Sustainability Defined. Retrieved 2020-08-21.
  6. ^ a b c d Kondo, Michelle (Mar 2018). "Urban Green Space and Its Impact on Human Health". International Journal of Environmental Research and Public Health. 15 (3): 445. doi:10.3390/ijerph15030445. PMC 5876990. PMID 29510520.
  7. ^ Myers, Marilyn (1975). "Decision Making in Allocating Metropolitan Open Space: State of the Art". Transactions of the Kansas Academy of Science. 78 (3/4): 149–153. doi:10.2307/3627339. JSTOR 3627339.
  8. ^ "Terminology of Urban Open and Green Spaces". ResearchGate. Retrieved 2020-08-21.
  9. ^ a b Francis, Jacinta; Giles-Corti, Billie; Wood, Lisa; Knuiman, Matthew (December 2012). "Creating sense of community: The role of public space". Journal of Environmental Psychology. 32 (4): 401–409. doi:10.1016/j.jenvp.2012.07.002.
  10. ^ Fuller, R. A.; Irvine, K. N.; Devine-Wright, P.; Warren, P. H.; Gaston, K. J. (2007). "Psychological benefits of green-space increase with biodiversity". Biology Letters. 3 (4): 390–394. doi:10.1098/rsbl.2007.0149. PMC 2390667. PMID 17504734.
  11. ^ Jabbar, Muhammad; Yusoff, Mariney Mohd; Shafie, Aziz (2022). "Assessing the role of urban green spaces for human well-being: a systematic review". GeoJournal. 87 (5): 4405–4423. doi:10.1007/s10708-021-10474-7. PMC 8290137. PMID 34305268.
  12. ^ Kruize, Hanneke; van der Vliet, Nina; Staatsen, Brigit; Bell, Ruth; Chiabai, Aline; Muiños, Gabriel; Higgins, Sahran; Quiroga, Sonia; Martinez-Juarez, Pablo; Aberg Yngwe, Monica; Tsichlas, Fotis; Karnaki, Pania; Lima, Maria Luísa; García de Jalón, Silvestre; Khan, Matluba; Morris, George; Stegeman, Ingrid (2019). "Urban Green Space: Creating a Triple Win for Environmental Sustainability, Health, and Health Equity through Behavior Change". International Journal of Environmental Research and Public Health. 16 (22): 4403. doi:10.3390/ijerph16224403. PMC 6888177. PMID 31717956.
  13. ^ Hartig, Terry. "Three steps to understanding restorative environments as health resources." Open Space People Space. Ed. Catharine Ward Thompson and Penny Travlou. London, England: Taylor and Francis, 2007.
  14. ^ Berman, Marc G.; Jonides, John; Kaplan, Stephen (December 2008). "The Cognitive Benefits of Interacting With Nature". Psychological Science. 19 (12): 1207–1212. doi:10.1111/j.1467-9280.2008.02225.x. hdl:2027.42/150702. PMID 19121124. S2CID 4998427.
  15. ^ Astell-Burt, Thomas; Feng, Xiaoqi; Kolt, Gregory S. (November 2013). "Mental health benefits of neighbourhood green space are stronger among physically active adults in middle-to-older age: Evidence from 260,061 Australians". Preventive Medicine. 57 (5): 601–606. doi:10.1016/j.ypmed.2013.08.017. PMID 23994648.
  16. ^ Zhang, Fan; Qian, Haochen (2024-07-01). "A comprehensive review of the environmental benefits of urban green spaces". Environmental Research. 252: 118837. doi:10.1016/j.envres.2024.118837. ISSN 0013-9351.
  17. ^ Eysenbach, Mary. "Park System Function and Services." From Recreation to Re-creation. American Planning Association, 2008.
  18. ^ Ward Thompson, Catharine (June 2013). "Activity, exercise and the planning and design of outdoor spaces" (PDF). Journal of Environmental Psychology. 34: 79–96. doi:10.1016/j.jenvp.2013.01.003. hdl:20.500.11820/5d8e3904-d95b-4026-8679-64841e986979.
  19. ^ Luttik, Joke (May 2000). "The value of trees, water and open space as reflected by house prices in the Netherlands". Landscape and Urban Planning. 48 (3–4): 161–167. Bibcode:2000LUrbP..48..161L. doi:10.1016/S0169-2046(00)00039-6.
  20. ^ Kim, Gwang-Won; Jeong, Gwang-Woo; Kim, Tae-Hoon; Baek, Han-Su; Oh, Seok-Kyun; Kang, Heoung-Keun; Lee, Sam-Gyu; Kim, Yoon Soo; Song, Jin-Kyu (2010). "Functional Neuroanatomy Associated with Natural and Urban Scenic Views in the Human Brain: 3.0T Functional MR Imaging". Korean Journal of Radiology. 11 (5): 507–13. doi:10.3348/kjr.2010.11.5.507. PMC 2930158. PMID 20808693.
  21. ^ Schantz P. 2022. Can nature really affect our health? A short review of studies. I: Why Cities Need Large Parks – Large Parks in Large Cities, (ed. R. Murray), London: Routledge
  22. ^ a b c d Shishegar, Nastaran (Jan 2013). "The Impact of Green Areas on Mitigating Urban Heat Island Effect: A Review". The International Journal of Environmental Sustainability. 9 (1): 119–130. doi:10.18848/2325-1077/CGP/v09i01/55081.
  23. ^ a b c d e "Reducing Urban Heat Islands: Compendium of Strategies" (PDF). U.S. Environmental Protection Agency.
  24. ^ Maas, Jolanda; Verheij, Robert A.; Groenewegen, Peter P.; Vries, Sjerp de; Spreeuwenberg, Peter (1 July 2006). "Green space, urbanity, and health: how strong is the relation?". Journal of Epidemiology & Community Health. 60 (7): 587–592. doi:10.1136/jech.2005.043125. PMC 2566234. PMID 16790830.
  25. ^ Kingsley, Marianne (April 2019). "Commentary – Climate change, health and green space co-benefits". Health Promotion and Chronic Disease Prevention in Canada: Research, Policy and Practice. 39 (4): 131–135. doi:10.24095/hpcdp.39.4.04. PMC 6553580. PMID 31021064.
  26. ^ a b Yeager, Ray; Riggs, Daniel W.; DeJarnett, Natasha; Tollerud, David J.; Wilson, Jeffrey; Conklin, Daniel J.; O'Toole, Timothy E.; McCracken, James; Lorkiewicz, Pawel; Xie, Zhengzhi; Zafar, Nagma; Krishnasamy, Sathya S.; Srivastava, Sanjay; Finch, Jordan; Keith, Rachel J.; DeFilippis, Andrew; Rai, Shesh N.; Liu, Gilbert; Bhatnagar, Aruni (18 December 2018). "Association Between Residential Greenness and Cardiovascular Disease Risk". Journal of the American Heart Association. 7 (24): e009117. doi:10.1161/jaha.118.009117. PMC 6405613. PMID 30561265.
  27. ^ a b Coombes, Emma; Jones, Andrew P.; Hillsdon, Melvyn (March 2010). "The relationship of physical activity and overweight to objectively measured green space accessibility and use". Social Science & Medicine. 70 (6): 816–822. doi:10.1016/j.socscimed.2009.11.020. PMC 3759315. PMID 20060635.
  28. ^ Pengelly, L. David; Kerigan, Anthony T.; Goldsmith, Charles H.; Inman, Elizabeth M. (8 March 2012). "The Hamilton Study: Distribution of Factors Confounding the Relationship between Air Quality and Respiratory Health". Journal of the Air Pollution Control Association. 34 (10): 1039–1043. doi:10.1080/00022470.1984.10465852. PMID 6491057.
  29. ^ Jiang, Xu-Qin; Mei, Xiao-Dong; Feng, Di (2016). "Air pollution and chronic airway diseases: what should people know and do?". Journal of Thoracic Disease. 8 (1): E31 – E40. doi:10.3978/j.issn.2072-1439.2015.11.50. PMC 4740163. PMID 26904251.
  30. ^ "Physical Activity and Respiratory Conditions". Physiopedia.
  31. ^ Dunphy, Siobhán (27 October 2020). "Exposure to forest floor enhances young immune systems, study finds". European Scientist. Retrieved 6 November 2020.
  32. ^ Vert, Cristina; Carrasco-Turigas, Glòria; Zijlema, Wilma; Espinosa, Ana; Cano-Riu, Lia; Elliott, Lewis R.; Litt, Jill; Nieuwenhuijsen, Mark J.; Gascon, Mireia (October 2019). "Impact of a riverside accessibility intervention on use, physical activity, and wellbeing: A mixed methods pre-post evaluation". Landscape and Urban Planning. 190: 103611. Bibcode:2019LUrbP.19003611V. doi:10.1016/j.landurbplan.2019.103611. hdl:10230/43564.
  33. ^ Insel, T. (2015, February 24). Mortality and Mental Disorders. Retrieved October 15, 2019 from https://www.nimh.nih.gov/about/directors/thomas-insel/blog/2015/mortality-and-mental-disorders.shtml.
  34. ^ a b Georgiou, Michail; Chastin, Sebastien (18 March 2021). "This is how urban 'blue spaces' can improve our health". World Economic Forum, The Conversation. Retrieved 29 July 2021.
  35. ^ Nutsford, D.; Pearson, A. L.; Kingham, S. (November 2013). "An ecological study investigating the association between access to urban green space and mental health". Public Health. 127 (11): 1005–1011. doi:10.1016/j.puhe.2013.08.016. PMID 24262442.
  36. ^ Groenewegen, Peter P.; van den Berg, Agnes E.; Maas, Jolanda; Verheij, Robert A.; de Vries, Sjerp (September 2012). "Is a Green Residential Environment Better for Health? If So, Why?". Annals of the Association of American Geographers. 102 (5): 996–1003. doi:10.1080/00045608.2012.674899. S2CID 128496396.
  37. ^ Shen, Yu-Sheng; Lung, Shih-Chun Candice (23 February 2017). "Mediation pathways and effects of green structures on respiratory mortality via reducing air pollution". Scientific Reports. 7 (1): 42854. Bibcode:2017NatSR...742854S. doi:10.1038/srep42854. PMC 5322332. PMID 28230108.
  38. ^ Vieira, Joana; Matos, Paula; Mexia, Teresa; Silva, Patrícia; Lopes, Nuno; Freitas, Catarina; Correia, Otília; Santos-Reis, Margarida; Branquinho, Cristina; Pinho, Pedro (January 2018). "Green spaces are not all the same for the provision of air purification and climate regulation services: The case of urban parks". Environmental Research. 160: 306–313. Bibcode:2018ER....160..306V. doi:10.1016/j.envres.2017.10.006. hdl:10400.5/14872. PMID 29040950.
  39. ^ a b Lovasi, Gina S.; O’Neil-Dunne, Jarlath P.M.; Lu, Jacqueline W.T.; Sheehan, Daniel; Perzanowski, Matthew S.; MacFaden, Sean W.; King, Kristen L.; Matte, Thomas; Miller, Rachel L.; Hoepner, Lori A.; Perera, Frederica P.; Rundle, Andrew (April 2013). "Urban Tree Canopy and Asthma, Wheeze, Rhinitis, and Allergic Sensitization to Tree Pollen in a New York City Birth Cohort". Environmental Health Perspectives. 121 (4): 494–500. doi:10.1289/ehp.1205513. PMC 3620770. PMID 23322788.
  40. ^ a b Rizwan, Ahmed Memon; Dennis, Leung; Liu, Chunho (2008). "A Review on the Generation, Determination, and Mitigation of Urban Heat Island". Journal of Environmental Sciences. 20 (1): 120–8. Bibcode:2008JEnvS..20..120R. doi:10.1016/S1001-0742(08)60019-4. hdl:2286/R.I.55343. PMID 18572534.
  41. ^ a b Zhanga, Yujia; Murray, Alan; Turner, B (Sep 2017). "Optimizing green space locations to reduce daytime and nighttime urban heat island effects in Phoenix, Arizona". Landscape and Urban Planning. 165: 162–171. Bibcode:2017LUrbP.165..162Z. doi:10.1016/j.landurbplan.2017.04.009. hdl:2286/R.I.45448.
  42. ^ a b Nowak, David. "The Effects of Urban Trees on Air Quality" (PDF). USDA Forest Service.
  43. ^ a b Kloog, I. (Apr 2019). "Air pollution, ambient temperature, green space, and preterm birth". Current Opinion in Pediatrics. 31 (2): 237–243. doi:10.1097/MOP.0000000000000736. PMID 30640892. S2CID 58585445.
  44. ^ Oliveria, M.; Slezakova, K.; Delerue-Matos, C.; Morais, S. (Mar 2019). "Children environmental exposure to particulate matter and polycyclic aromatic hydrocarbons and biomonitoring in school environments: A review on indoor and outdoor exposure levels, major sources, and health impacts". Environment International. 124: 180–204. Bibcode:2019EnInt.124..180O. doi:10.1016/j.envint.2018.12.052. hdl:10400.22/16142. PMID 30654326.
  45. ^ a b Tischer, C.; Gascon, M.; Fernandez-Somoano, A.; Tardon, A.; Lertxundi Materola, A.; Ibarluzea, J.; Ferrero, A.; Cirach, M.; Vrijheid, M.; Fuertes, E.; Dalmau-Buena, A.; Nieuwenhuijsen, M.; Anto, J.; Sunyer, J.; Dadvand, P. (Jun 2017). "Urban green and grey space in relation to respiratory health in children". The European Respiratory Journal. 49 (6): 1502112. doi:10.1183/13993003.02112-2015. hdl:10044/1/59870. PMID 28642307.
  46. ^ a b c Wolch, Jennifer; Byrne, Jason; Newell, Joshua (May 2014). "Urban green space, public health, and environmental justice: The challenge of making cities 'just green enough'". Landscape and Urban Planning. 125: 234–244. Bibcode:2014LUrbP.125..234W. doi:10.1016/j.landurbplan.2014.01.017. hdl:10072/62481. S2CID 54706182.
  47. ^ a b c Braubach, Matthias; Egorov, Andrey; Mudu, Pierpaolo; Thompson, Catharine; Martuzzi, Marco (Sep 2017). "Effects of Urban Green Space on Environmental Health, Equity and Resilience". Nature-Based Solutions to Climate Change Adaptation in Urban Areas. Theory and Practice of Urban Sustainability Transitions (Nature-Based Solutions to Climate Change Adaptation in Urban Areas ed.). Effects of urban green space on environmental health, equity, and resilience: Springer. pp. 187–205. doi:10.1007/978-3-319-56091-5_11. ISBN 978-3-319-56091-5.
  48. ^ Dadvand, Payam; Nieuwenhuijsen, Mark; Esnaola, Mikel; Basagana, Xavier; Alvarez-Pedrerol, Mar; Rivas, Ioar; Lopez-Vincente, Monica; Pascual, Montserrat De Castro; Su, Jason; Jerrett, Michael; Querol, Xavier; Sunyer, Jordi (June 2015). "Green spaces and cognitive development in primary schoolchildren". Proceedings of the National Academy of Sciences. 112 (26): 7937–42. Bibcode:2015PNAS..112.7937D. doi:10.1073/pnas.1503402112. PMC 4491800. PMID 26080420.
  49. ^ Jennings, V.; Larson, L.; Yun, J. (Feb 2016). "Advancing sustainability through urban green space: cultural ecosystem services, equity, and social determinants of health". International Journal of Environmental Research and Public Health. 13 (2): 196. doi:10.3390/ijerph13020196. PMC 4772216. PMID 26861365.
  50. ^ Woodyatt, Amy. "City children have better mental health and cognition if they live near woodlands". CNN. Retrieved 14 August 2021.
  51. ^ Maes, Mikaël J. A.; Pirani, Monica; Booth, Elizabeth R.; Shen, Chen; Milligan, Ben; Jones, Kate E.; Toledano, Mireille B. (19 July 2021). "Benefit of woodland and other natural environments for adolescents' cognition and mental health". Nature Sustainability. 4 (10): 851–858. Bibcode:2021NatSu...4..851M. doi:10.1038/s41893-021-00751-1. hdl:10044/1/98026. ISSN 2398-9629. S2CID 236096013.
  52. ^ "A brief history of urban green spaces". Urban Rambles. 2015-12-28. Retrieved 2018-10-25.
  53. ^ Giovagnorio, Ilaria; Usai, Daniela; Palmas, Alessandro; Chiri, Giovanni Marco (July 2017). "The environmental elements of foundations in Roman cities: A theory of the architect Gaetano Vinaccia". Sustainable Cities and Society. 32: 42–55. Bibcode:2017SusCS..32...42G. doi:10.1016/j.scs.2017.03.002.
  54. ^ Ward Thompson, Catharine (March 2011). "Linking landscape and health: The recurring theme". Landscape and Urban Planning. 99 (3–4): 187–195. Bibcode:2011LUrbP..99..187W. doi:10.1016/j.landurbplan.2010.10.006.
  55. ^ "Islamic Gardens at King's Cross". Aga Khan Centre. Retrieved 2024-11-27.
  56. ^ Fann, Bayt Al (2022-09-05). "Islamic Gardens". Bayt Al Fann. Retrieved 2024-11-27.
  57. ^ Features, Bonnie L. Grant last updated in (2014-12-29). "Islamic Garden Plants: Creating Islamic Gardens And Landscapes". gardeningknowhow. Retrieved 2024-11-27.
  58. ^ Ledsom, Alex. "What Is London's National Park City Status And Which Other Cities Will Follow?". Forbes.
  59. ^ Lawrence, Henry W. (March 1993). "The Greening of the Squares of London: Transformation of Urban landscapes and Ideals". Annals of the Association of American Geographers. 83 (1): 90–118. doi:10.1111/j.1467-8306.1993.tb01924.x.
  60. ^ Taylor, Hilary A. (1995). "Urban Public Parks, 1840-1900: Design and Meaning". Garden History. 23 (2): 201–221. doi:10.2307/1587078. JSTOR 1587078.
  61. ^ Curtis, Simon; Klaus, Ian (2024). The Belt and Road City: Geopolitics, Urbanization, and China's Search for a New International Order. New Haven and London: Yale University Press. doi:10.2307/jj.11589102. ISBN 9780300266900. JSTOR jj.11589102.
  62. ^ Roberts, William H. "Design of Metropolitan Open Space Based on Natural Process." Metropolitan Open Space and Natural Process. Philadelphia, Pennsylvania: University of Pennsylvania, 1970.
  63. ^ a b Young, Terence. "Modern Urban Parks." Geographical Review 1995. Pp. 535–551.
  64. ^ Gehl, Jan. "Public Spaces for a Changing Public Life." Open Space People Space. Ed. Catharine Ward Thompson and Penny Travlou. London, England: Taylor and Francis, 2007.
  65. ^ Coates, Peter (2004). "Emerging from the Wilderness: (or, From Redwoods to Bananas): Recent Environmental History in the United States and the Rest of the Americas". Environment and History. 10 (4): 407–38. doi:10.3197/0967340042772676.
  66. ^ Alumai, Alfred. "Urban Lawn Management: Addressing the Entomological, Agronomic, Economic, and Social Drivers." PhD., Ohio State University, 2008.
  67. ^ "Sustainable Sites FAQs". Retrieved 7 April 2011.
  68. ^ Rigolon, Alessandro; Németh, Jeremy (25 July 2018). "What Shapes Uneven Access to Urban Amenities? Thick Injustice and the Legacy of Racial Discrimination in Denver's Parks". Journal of Planning Education and Research. 41 (3): 312–325. doi:10.1177/0739456X18789251. S2CID 149537951.
  69. ^ Groenewegen, Peter P; van den Berg, Agnes E; de Vries, Sjerp; Verheij, Robert A (7 June 2006). "Vitamin G: effects of green space on health, well-being, and social safety". BMC Public Health. 6 (1): 149. doi:10.1186/1471-2458-6-149. PMC 1513565. PMID 16759375.
  70. ^ Rigolon, Alessandro (September 2016). "A complex landscape of inequity in access to urban parks: A literature review". Landscape and Urban Planning. 153: 160–169. Bibcode:2016LUrbP.153..160R. doi:10.1016/j.landurbplan.2016.05.017.
  71. ^ Mitchell, Richard; Popham, Frank (November 2008). "Effect of exposure to natural environment on health inequalities: an observational population study" (PDF). The Lancet. 372 (9650): 1655–1660. doi:10.1016/S0140-6736(08)61689-X. PMID 18994663. S2CID 37232884.
  72. ^ Crawford, David; Timperio, Anna; Giles-Corti, Billie; Ball, Kylie; Hume, Clare; Roberts, Rebecca; Andrianopoulos, Nick; Salmon, Jo (December 2008). "Do features of public open spaces vary according to neighbourhood socio-economic status?". Health & Place. 14 (4): 889–893. doi:10.1016/j.healthplace.2007.11.002. PMID 18086547.
  73. ^ Wen, Ming; Zhang, Xingyou; Harris, Carmen D.; Holt, James B.; Croft, Janet B. (19 January 2013). "Spatial Disparities in the Distribution of Parks and Green Spaces in the USA". Annals of Behavioral Medicine. 45 (S1): 18–27. doi:10.1007/s12160-012-9426-x. PMC 3590901. PMID 23334758.
  74. ^ Assaad, Rayan H.; Jezzini, Yasser (1 May 2024). "Green gentrification vulnerability index (GGVI): A novel approach for identifying at-risk communities and promoting environmental justice at the census-tract level". Cities. 148: 104858. doi:10.1016/j.cities.2024.104858. ISSN 0264-2751.
  75. ^ Banzhaf, H. Spencer; McCormick, Eleanor (2006). "Moving beyond cleanup: Identifying the crucibles of environmental gentrification". NCEE Working Paper Series.
  76. ^ a b Dooling, Sarah (2009). "Ecological gentrification: A research agenda exploring justice in the city". International Journal of Urban and Regional Research. 33 (3): 621–639. doi:10.1111/j.1468-2427.2009.00860.x.
  77. ^ Jezzini, Yasser; Assaf, Ghiwa; Assaad, Rayan H. (January 2023). "Models and Methods for Quantifying the Environmental, Economic, and Social Benefits and Challenges of Green Infrastructure: A Critical Review". Sustainability. 15 (9): 7544. doi:10.3390/su15097544. ISSN 2071-1050.
  78. ^ Assaad, Rayan H.; Jezzini, Yasser (14 May 2024). "Assessing and predicting green gentrification susceptibility using an integrated machine learning approach". Local Environment. 29 (8): 1099–1127. Bibcode:2024LoEnv..29.1099A. doi:10.1080/13549839.2024.2353058. ISSN 1354-9839.
  79. ^ Goossens, Cedric; Oosterlynck, Stijn; Bradt, Lieve (20 April 2020). "Livable streets? Green gentrification and the displacement of longtime residents in Ghent, Belgium". Urban Geography. 41 (4): 550–572. doi:10.1080/02723638.2019.1686307.
  80. ^ Sieg, Holger; Smith, V. Kerry; Banzhaf, H. Spencer; Walsh, Randall (2004). "Estimating the general equilibrium benefits of large changes in spatially delineated public goods". International Economic Review. 45 (4): 1047–77. CiteSeerX 10.1.1.462.768. doi:10.1111/j.0020-6598.2004.00297.x. S2CID 154409046.

Further reading

source: https://en.wikipedia.org/wiki/Urban_open_space