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Intensity Island Decrease, Non-rooftop ?

When discussing “Intensity Island Decrease, Non-rooftop,” it’s important to understand the context. This likely refers to efforts to mitigate the “heat island effect” in urban areas, but focusing on solutions beyond just rooftop installations. Here’s a breakdown:

Understanding the Heat Island Effect:

  • The urban heat island effect occurs when cities experience significantly warmer temperatures than surrounding rural areas.
  • This is due to factors like:
    • Dark surfaces (roads, buildings) that absorb heat.
    • Lack of vegetation and evaporative cooling.
    • Waste heat from vehicles and air conditioning.

Non-Rooftop Strategies for Mitigation:

To decrease the intensity of urban heat islands, strategies beyond rooftop solutions are essential. These include:

  • Increased Green Infrastructure:
    • Urban parks and green spaces: These provide shade and evaporative cooling.
    • Green streets: Planting trees along streets to provide shade and reduce pavement temperatures.
    • Permeable pavements: These allow water to infiltrate the ground, reducing runoff and promoting evaporative cooling.
  • Cool Pavements and Surfaces:
    • Reflective pavements: Materials that reflect sunlight and absorb less heat.
    • Cool roofs (beyond residential): implementing cool roof technology on large commercial and industrial buildings.
  • Urban Planning and Design:
    • Strategic placement of buildings and green spaces: To maximize shading and airflow.
    • Reducing urban density: where possible.
    • Improving urban ventilation.
  • Water features:
    • Creating water features in urban areas, such as fountains or ponds, can help to cool the surrounding air through evaporation.

Key Considerations:

  • These strategies often require integrated planning and collaboration between various stakeholders, including city planners, engineers, and policymakers.
  • The effectiveness of these strategies can vary depending on local climate conditions and urban characteristics.

By implementing a combination of these non-rooftop solutions, cities can effectively reduce the intensity of the urban heat island effect and create more comfortable and sustainable urban environments.

What is Intensity Island Decrease, Non-rooftop ?

The phrase “Intensity Island Decrease, Non-rooftop” refers to efforts aimed at reducing the urban heat island effect, but with a focus on strategies that go beyond simply installing cool roofs. Here’s a more detailed explanation:

Urban Heat Island Effect:

  • Cities tend to be significantly warmer than surrounding rural areas. This phenomenon is known as the urban heat island effect.
  • It’s caused by factors like:
    • Dark surfaces (asphalt, concrete) that absorb and retain heat.
    • A lack of vegetation, which reduces evaporative cooling.
    • Heat generated by vehicles, air conditioners, and industrial activity.

“Intensity Island Decrease, Non-rooftop” Strategies:

This concept emphasizes solutions that address the heat island effect at ground level and throughout the urban environment, rather than solely on rooftops. Key strategies include:

  • Green Infrastructure:
    • Expanding urban parks and green spaces.
    • Planting trees along streets and in other public areas.
    • Implementing green walls and vertical gardens.
    • Using permeable pavements that allow water to infiltrate the ground.
  • Cool Pavements:
    • Replacing traditional asphalt with reflective or porous pavement materials.
  • Urban Design:
    • Designing buildings and streets to maximize shading and airflow.
    • Creating wind corridors to promote ventilation.
    • Adding water features such as fountains.
  • Transportation:
    • Reducing the amount of heat produced from vehicles.
    • Promoting public transport and walking or cycling.

In essence, “Intensity Island Decrease, Non-rooftop” means taking a comprehensive approach to cooling cities by focusing on ground-level and broader urban planning solutions.

Who is required Intensity Island Decrease, Non-rooftop ?

The need for “Intensity Island Decrease, Non-rooftop” measures is relevant to a wide range of stakeholders, primarily those involved in urban planning, environmental management, and public health. Here’s a breakdown of who is most concerned and why:

  • City Planners and Urban Designers:
    • They are responsible for shaping the physical environment of cities.
    • They need to incorporate heat mitigation strategies into urban development plans, zoning regulations, and infrastructure projects.
  • Environmental Agencies and Organizations:
    • They focus on protecting the environment and mitigating the impacts of climate change.
    • They work to implement policies and programs that reduce the urban heat island effect.
  • Public Health Officials:
    • They are concerned about the health impacts of extreme heat, such as heatstroke and respiratory problems.
    • They need to develop strategies to protect vulnerable populations from heat-related illnesses.
  • Local Governments and Municipalities:
    • They are responsible for managing public spaces, infrastructure, and services.
    • They need to implement heat mitigation measures in parks, streets, and public buildings.
  • Residents of Urban Areas:
    • They are directly affected by the urban heat island effect, which can lead to discomfort, health problems, and increased energy costs.
    • Therefore any resident of a city is affected, and therefore has a stake in these measures.
  • Building Owners and Developers:
    • While the focus is “non-rooftop” they still have a large impact on the surrounding enviornment.
    • They can contribute by using cool pavement around buildings, and by adding green spaces around buildings.

In essence, anyone who lives, works, or has a vested interest in the well-being of urban areas is a stakeholder in efforts to reduce the urban heat island effect.

When is required Intensity Island Decrease, Non-rooftop ?

The need for “Intensity Island Decrease, Non-rooftop” measures is becoming increasingly urgent, and there isn’t one single “time” when it’s required. Rather, it’s an ongoing and accelerating need. Here’s a breakdown of when it’s particularly important:

  • During periods of rapid urbanization:
    • As cities grow, the heat island effect intensifies. Therefore, these mitigation strategies need to be integrated into urban planning from the outset.
  • During heat waves:
    • Heat waves are becoming more frequent and intense due to climate change. Non-rooftop cooling measures can provide crucial relief during these extreme events.
  • In regions with hot climates:
    • Cities in already hot climates are particularly vulnerable to the heat island effect. Proactive measures are essential to prevent further warming.
  • When planning infrastructure projects:
    • Any new road, building, or public space should be designed with heat mitigation in mind. This includes using cool pavements, planting trees, and incorporating green spaces.
  • When addressing climate change adaptation:
    • Reducing the urban heat island effect is a key strategy for adapting to the impacts of climate change. It helps to protect vulnerable populations and reduce energy consumption.
  • Continuously:
    • It is not a one time fix. Urban environments are dynamic, and therefore the management of heat island effect must also be dynamic. Meaning that it is something that needs constant attention, and updating.

In essence, the need for these measures is:

  • Proactive: To prevent the heat island effect from worsening.
  • Reactive: To mitigate the impacts of existing heat islands and heat waves.

Therefore, it is something that is needed now, and will be needed increasingly into the future.

COURTESY : Seeker

Where is required Intensity Island Decrease, Non-rooftop ?

The need for “Intensity Island Decrease, Non-rooftop” measures is prevalent in virtually all urban environments, but some areas are particularly vulnerable. Here’s a breakdown of where these measures are most urgently required:

1. Densely Populated Urban Centers:

  • Large metropolitan areas: Cities with high concentrations of buildings, roads, and other impervious surfaces experience the most intense heat island effects. Examples include:
    • New York City
    • Los Angeles
    • Chicago
    • Tokyo
    • Mumbai
  • These areas often have limited green space, exacerbating the problem.

2. Cities in Hot Climates:

  • Regions with naturally high temperatures are especially susceptible to the amplified heat of urban heat islands.
  • Cities in:
    • The Southwestern United States (e.g., Phoenix, Las Vegas)
    • The Middle East
    • Tropical regions
  • These locations can experience dangerously high temperatures, posing significant health risks.

3. Areas with Limited Green Space:

  • Neighborhoods and districts lacking parks, trees, and other vegetation are particularly vulnerable.
  • Low-income communities often have less access to green space, creating environmental inequities.

4. Areas with High Concentrations of Pavement:

  • Industrial zones, parking lots, and extensive road networks absorb and retain heat, contributing to localized hot spots.

5. Developing Cities:

  • Rapid urbanization in developing countries is leading to the expansion of heat islands.
  • It’s crucial to implement sustainable urban planning practices to mitigate the effects of heat islands in these growing cities.

In essence:

  • Any urban area where the built environment dominates over natural landscapes requires “Intensity Island Decrease, Non-rooftop” measures.
  • The severity of the need varies depending on factors like climate, population density, and the availability of green space.
  • It is a global problem, that is affecting almost all populated areas.

How is required Intensity Island Decrease, Non-rooftop ?

Effectively implementing “Intensity Island Decrease, Non-rooftop” measures requires a multi-faceted approach, combining policy, planning, and practical implementation. Here’s a breakdown of how it can be achieved:

1. Strategic Urban Planning and Policy:

  • Integrating heat mitigation into urban design:
    • Develop zoning regulations that encourage green spaces and permeable surfaces.
    • Incorporate heat island mitigation into city master plans.
    • Prioritize the preservation and expansion of urban forests.
  • Implementing cool pavement policies:
    • Mandate the use of reflective or permeable pavement materials in new road construction and resurfacing projects.
    • Provide incentives for businesses and homeowners to use cool pavements.
  • Promoting green infrastructure:
    • Establish funding programs for urban park development and tree planting initiatives.
    • Create incentives for the development of green walls and vertical gardens.
    • Implement policies that protect existing green spaces.

2. Practical Implementation:

  • Expanding urban green spaces:
    • Create new parks and green spaces in underserved neighborhoods.
    • Plant trees along streets, in parking lots, and in other public areas.
    • Develop community gardens and urban farms.
  • Implementing cool pavement technologies:
    • Use reflective coatings on existing asphalt surfaces.
    • Install permeable pavement in parking lots and sidewalks.
    • Experiment with new cool pavement technologies.
  • Enhancing urban water features:
    • Create or restore urban wetlands and ponds.
    • Install fountains and other water features in public spaces.
  • Improving urban ventilation:
    • Design buildings and streets to maximize airflow.
    • Create wind corridors to channel breezes through urban areas.

3. Community Engagement and Education:

  • Raising public awareness:
    • Educate residents about the urban heat island effect and its impacts.
    • Promote the benefits of green infrastructure and cool pavements.
  • Encouraging community participation:
    • Organize tree planting events and community garden projects.
    • Involve residents in the planning and implementation of heat mitigation measures.

4. Interdisciplinary Collaboration:

  • Working across sectors:
    • Foster collaboration between city planners, engineers, environmental scientists, and public health officials.
    • Encourage partnerships between government agencies, businesses, and community organizations.

By combining these strategies, cities can effectively reduce the intensity of the urban heat island effect and create more comfortable, sustainable, and resilient urban environments.

Case study is Intensity Island Decrease, Non-rooftop ?

It’s important to understand that “Intensity Island Decrease, Non-rooftop” is a broad concept, and case studies often involve a combination of strategies. However, here are some examples that highlight key aspects of non-rooftop heat island mitigation:

1. Madrid, Spain: Matadero Madrid

  • This case study focuses on the transformation of a former industrial site into an arts center.
  • Researchers analyzed the microclimate and evaluated the impact of various non-rooftop solutions.
  • The study emphasized the potential of Nature-Based Solutions (NBSs) like:
    • Increasing green areas.
    • Implementing tree canopies.
    • Using fabric canopies for shading.
  • This case demonstrates how careful urban planning and the integration of NBSs can improve thermal comfort in urban spaces.

Key Takeaways:

  • Highlights the importance of microclimate analysis in urban planning.
  • Demonstrates the effectiveness of combining various NBSs.

2. Singapore: “Garden City” Initiatives

  • Singapore has implemented a comprehensive “Garden City” strategy that emphasizes:
    • Extensive tree planting.
    • The creation of parks and green spaces.
    • The integration of greenery into building facades and infrastructure.
  • This approach has helped to mitigate the urban heat island effect and improve the city’s overall environmental quality.
  • Singapore is a very dense urban enviroment, and therefore provides a good example of how to implement these strategies in such an enviroment.

Key Takeaways:

  • Shows the impact of long-term, integrated urban greening strategies.
  • Demonstrates the importance of government commitment and policy.

General Observations:

  • Many cities are incorporating cool pavement technologies into their infrastructure projects.
  • Urban forestry initiatives are becoming increasingly common, with cities planting trees along streets and in public spaces.
  • The use of permeable pavements is also gaining traction, particularly in areas prone to flooding.

These case studies illustrate that effective heat island mitigation requires a combination of strategies tailored to the specific context of each city.

COURTESY : HOME TUBE

White paper on Intensity Island Decrease, Non-rooftop ?

Unfortunately, finding a single, definitive “white paper” specifically titled “Intensity Island Decrease, Non-rooftop” might be difficult. This is because the concept is often addressed within broader documents and research related to urban heat island mitigation, climate change adaptation, and sustainable urban planning.

However, I can point you towards the types of documents and resources that cover the information you’re looking for:

Where to Find Relevant Information:

  • Reports from Environmental Agencies:
    • Organizations like the U.S. Environmental Protection Agency (EPA) and similar agencies in other countries publish reports and guides on urban heat island mitigation. These often include information on non-rooftop strategies.
    • These agencies will often provide best practice guidlines, and case study information.
  • Academic Research and Journals:
    • Scientific journals and research papers provide in-depth analysis of urban heat island effects and mitigation strategies.
    • Platforms like ResearchGate and Google Scholar can be valuable resources for finding this information.
  • Urban Planning Organizations:
    • Organizations focused on urban planning and sustainable development often publish reports and guidelines on heat island mitigation.
    • Organizations that focus on sustainable infrastructure.
  • Government Publications:
    • Many city and regional governments produce documents outlining their strategies for addressing the urban heat island effect. These may include specific policies and initiatives related to non-rooftop solutions.

Key Themes and Concepts in These Documents:

When searching for information, look for documents that cover these topics:

  • Green Infrastructure:
    • Urban forestry
    • Green streets
    • Permeable pavements
  • Cool Pavements and Surfaces:
    • Reflective pavements
    • Urban albedo
  • Urban Design and Planning:
    • Microclimate analysis
    • Urban ventilation
    • Heat vulnerability assessments

By exploring these resources, you can gain a comprehensive understanding of the strategies and best practices for “Intensity Island Decrease, Non-rooftop.”

Industrial application of Intensity Island Decrease, Non-rooftop ?

When considering the industrial application of “Intensity Island Decrease, Non-rooftop,” it’s crucial to recognize that industries significantly contribute to the urban heat island effect. Therefore, they also have a substantial role in mitigating it. Here’s how these principles apply to industrial settings:

Key Industrial Applications:

  • Industrial Site Design and Layout:
    • Factories and industrial parks can be designed with green infrastructure in mind. This includes:
      • Planting trees and creating green buffer zones around facilities.
      • Using permeable pavement in parking lots and roadways within industrial complexes.
      • Creating retention ponds or other water features to provide evaporative cooling.
    • Orienting buildings to maximize natural ventilation and minimize solar heat gain.
  • Cool Pavement and Surface Implementation:
    • Large industrial parking lots and loading areas are prime candidates for cool pavement technologies.
    • Using reflective coatings on industrial building walls and non-rooftop surfaces.
  • Industrial Process Modifications:
    • Reducing waste heat from industrial processes.
    • Implementing water-efficient cooling systems.
    • Optimizing energy consumption to minimize heat generation.
  • Logistics and Transportation:
    • Industries can contribute by optimizing logistics to reduce vehicle emissions and heat generation.
    • Promoting the use of electric vehicles and other low-emission transportation within industrial complexes.
  • Material choices:
    • Choosing materials that have a higher albedo, meaning that they reflect more sunlight, and therefore absorb less heat.

Benefits for Industries:

  • Reduced Energy Costs:
    • Cooling measures can reduce the need for air conditioning, leading to significant energy savings.
  • Improved Worker Comfort and Productivity:
    • Reducing heat stress can create a more comfortable and productive work environment.
  • Enhanced Corporate Social Responsibility:
    • Implementing sustainable practices can enhance a company’s reputation and demonstrate its commitment to environmental stewardship.
  • Regulatory Compliance:
    • As cities increasingly implement heat mitigation policies, industries that take proactive measures can ensure compliance and avoid potential penalties.

In essence, industries can play a vital role in reducing the urban heat island effect by integrating sustainable design and operational practices into their facilities and processes.

Research and development of Intensity Island Decrease, Non-rooftop ?

Research and development (R&D) plays a crucial role in advancing “Intensity Island Decrease, Non-rooftop” strategies. Here’s a look at key areas of R&D:

1. Materials Science:

  • Cool Pavement Technologies:
    • Developing new materials with higher solar reflectance and thermal emissivity.
    • Improving the durability and longevity of cool pavement coatings.
    • Researching permeable pavement designs that enhance evaporative cooling.
  • Green Infrastructure Materials:
    • Developing soil amendments and growing mediums that optimize water retention and plant growth in urban environments.
    • Researching innovative materials for green walls and vertical gardens.

2. Urban Climatology and Modeling:

  • Microclimate Analysis:
    • Using advanced sensor technologies and computer simulations to understand the complex interactions of heat, wind, and vegetation in urban spaces.
    • Developing models to predict the effectiveness of different heat mitigation strategies.
  • Remote Sensing and Data Analysis:
    • Using satellite imagery and aerial surveys to map urban heat islands and monitor the performance of mitigation measures.
    • Developing algorithms to analyze large datasets and identify heat vulnerability hotspots.

3. Engineering and Design:

  • Green Infrastructure Design:
    • Developing innovative designs for urban parks, green streets, and other green spaces that maximize cooling benefits.
    • Engineering solutions for integrating green infrastructure into existing urban infrastructure.
  • Urban Ventilation:
    • Researching building and street designs that promote natural ventilation and airflow.
    • Developing strategies for creating wind corridors in dense urban environments.

4. Social Sciences and Policy Research:

  • Heat Vulnerability Assessments:
    • Identifying populations that are most vulnerable to heat-related illnesses.
    • Developing strategies for targeted interventions and public health campaigns.
  • Policy and Economic Analysis:
    • Evaluating the effectiveness of different heat mitigation policies and programs.
    • Developing economic models to assess the costs and benefits of heat island reduction.

Key Trends in R&D:

  • Nature-Based Solutions (NBS): There’s a growing emphasis on using NBS to mitigate the urban heat island effect.
  • Smart Technologies: The integration of sensors, data analytics, and artificial intelligence is enabling more precise and effective heat management.
  • Interdisciplinary Collaboration: R&D efforts are increasingly involving collaboration between scientists, engineers, urban planners, and policymakers.

By investing in these R&D areas, we can develop more effective and sustainable solutions for reducing the urban heat island effect.

COURTESY : Leaf of Life

References

  1. ^ Phelan, Patrick E.; Kaloush, Kamil; Miner, Mark; Golden, Jay; Phelan, Bernadette; Silva, Humberto; Taylor, Robert A. (4 November 2015). “Urban Heat Island: Mechanisms, Implications, and Possible Remedies”. Annual Review of Environment and Resources. 40 (1): 285–307. doi:10.1146/annurev-environ-102014-021155. S2CID 154497357.
  2. ^ Jump up to:a b Solecki, William D.; Rosenzweig, Cynthia; Parshall, Lily; Pope, Greg; Clark, Maria; Cox, Jennifer; Wiencke, Mary (2005). “Mitigation of the heat island effect in urban New Jersey”. Global Environmental Change Part B: Environmental Hazards. 6 (1): 39–49. doi:10.1016/j.hazards.2004.12.002. S2CID 153841143.
  3. ^ United States Environmental Protection Agency (2008). Reducing urban heat islands: Compendium of strategies (Report). pp. 7–12.
  4. ^ Jump up to:a b Li, Y.; Zhao, X. (2012). “An empirical study of the impact of human activity on long-term temperature change in China: A perspective from energy consumption”. Journal of Geophysical Research. 117 (D17): D17117. Bibcode:2012JGRD..11717117L. doi:10.1029/2012JD018132.
  5. ^ Wang, K. (February 6, 2017). “Comparing the diurnal and seasonal variabilities of atmospheric, and surface urban heat islands based on the Beijing Urban Meteorological Network”. Journal of Geophysical Research: Atmospheres. 122 (4): 2131–2154. Bibcode:2017JGRD..122.2131W. doi:10.1002/2016JD025304.
  6. ^ Glossary of Meteorology (2019). “Urban Heat Island”. American Meteorological Society. Retrieved 2019-04-12.
  7. ^ Chakraborty, T. and Lee, X. (2019). “A simplified urban-extent algorithm to characterize surface urban heat islands on a global scale and examine vegetation control on their spatiotemporal variability”. International Journal of Applied Earth Observation and Geoinformation. 74: 269–280. Bibcode:2019IJAEO..74..269C. doi:10.1016/j.jag.2018.09.015. S2CID 53715577.
  8. ^ Waldrop, M. Mitchell (19 October 2022). “What can cities do to survive extreme heat?”. Knowable Magazine. doi:10.1146/knowable-101922-2. Retrieved 6 December 2022.
  9. ^ “Nature of Cities”. Regeneration.org. Retrieved 2021-10-16.
  10. ^ Jump up to:a b Younes, Jaafar; Ghali, Kamel; Ghaddar, Nesreen (August 2022). “Diurnal Selective Radiative Cooling Impact in Mitigating Urban Heat Island Effect”. Sustainable Cities and Society. 83: 103932. Bibcode:2022SusCS..8303932Y. doi:10.1016/j.scs.2022.103932. S2CID 248588547.
  11. ^ Jump up to:a b Khan, Ansar; Carlosena, Laura; Feng, Jie; Khorat, Samiran; Khatun, Rupali; Doan, Quang-Van; Santamouris, Mattheos (19 January 2022). “Optically Modulated Passive Broadband Daytime Radiative Cooling Materials Can Cool Cities in Summer and Heat Cities in Winter”. Sustainability. 14 (3): 1110. doi:10.3390/su14031110. hdl:2454/46738.
  12. ^ Jump up to:a b c “Cities, Settlements and Key Infrastructure”. Climate Change 2022 – Impacts, Adaptation and Vulnerability. 2023. pp. 907–1040. doi:10.1017/9781009325844.008. ISBN 978-1-009-32584-4.
  13. ^ Sharifi, Ayyoob (2020). “Trade-offs and conflicts between urban climate change mitigation and adaptation measures: A literature review”. Journal of Cleaner Production. 276: 122813. Bibcode:2020JCPro.27622813S. doi:10.1016/j.jclepro.2020.122813. S2CID 225638176.
  14. ^ Jump up to:a b “Glossary”. Climate Change 2022 – Impacts, Adaptation and Vulnerability. 2023. pp. 2897–2930. doi:10.1017/9781009325844.029. ISBN 978-1-009-32584-4.
  15. ^ “Urban Heat Islands | Center for Science Education”. scied.ucar.edu. Retrieved 2024-07-02.
  16. ^ Jump up to:a b US Envrionmental Protection Agency, OAR (2014-06-17). “Learn About Heat Islands”. www.epa.gov. Retrieved 2024-07-01.
  17. ^ Zhou, Decheng; Zhang, Liangxia; Hao, Lu; Sun, Ge; Liu, Yongqiang; Zhu, Chao (2016). “Spatiotemporal trends of urban heat island effect along the urban development intensity gradient in China”. Science of the Total Environment. 544: 617–626. Bibcode:2016ScTEn.544..617Z. doi:10.1016/j.scitotenv.2015.11.168. ISSN 0048-9697. PMID 26674691.
  18. ^ Liou, Yuei-An; Tran, Duy-Phien; Nguyen, Kim-Anh (2022-02-22). “Diurnal and Seasonal Characteristics of Surface Urban Heat Island in Taiwan”. (CETA 2021) 2021 International Conference on Computer Engineering, Technologies and Applications. ISSN 2516-2314.
  19. ^ Amorim, Margarete Cristiane de Costa Trindade; Dubreuil, Vincent; Amorim, Amanda Trindade (2021). “Day and night surface and atmospheric heat islands in a continental and temperate tropical environment”. Urban Climate. 38: 100918. Bibcode:2021UrbCl..3800918A. doi:10.1016/j.uclim.2021.100918. ISSN 2212-0955.
  20. ^ Shastri, Hiteshri; Barik, Beas; Ghosh, Subimal; Venkataraman, Chandra; Sadavarte, Pankaj (2017-01-09). “Flip flop of Day-night and Summer-Winter Surface Urban Heat Island Intensity in India”. Scientific Reports. 7 (1): 40178. Bibcode:2017NatSR…740178S. doi:10.1038/srep40178. ISSN 2045-2322. PMC 5220321. PMID 28067276.
  21. ^ Mohajerani, Abbas; Bakaric, Jason; Jeffrey-Bailey, Tristan (2017-07-15). “The urban heat island effect, its causes, and mitigation, with reference to the thermal properties of asphalt concrete”. Journal of Environmental Management. 197: 522–538. Bibcode:2017JEnvM.197..522M. doi:10.1016/j.jenvman.2017.03.095. ISSN 0301-4797. PMID 28412623.
  22. ^ Jump up to:a b Manoli, Gabriele; Fatichi, Simone; Bou-Zeid, Elie; Katul, Gabriel G. (2020-03-31). “Seasonal hysteresis of surface urban heat islands”. Proceedings of the National Academy of Sciences. 117 (13): 7082–7089. Bibcode:2020PNAS..117.7082M. doi:10.1073/pnas.1917554117. ISSN 0027-8424. PMC 7132285. PMID 32184330.
  23. ^ Imhoff, Marc L.; Zhang, Ping; Wolfe, Robert E.; Bounoua, Lahouari (2010-03-15). “Remote sensing of the urban heat island effect across biomes in the continental USA”. Remote Sensing of Environment. 114 (3): 504–513. Bibcode:2010RSEnv.114..504I. doi:10.1016/j.rse.2009.10.008. hdl:2060/20110015410. ISSN 0034-4257.
  24. ^ Cui, Yu Yan; Foy, Benjamin de (2012-05-01). “Seasonal Variations of the Urban Heat Island at the Surface and the Near-Surface and Reductions due to Urban Vegetation in Mexico City”. Journal of Applied Meteorology and Climatology. 51 (5): 855–868. Bibcode:2012JApMC..51..855C. doi:10.1175/JAMC-D-11-0104.1. ISSN 1558-8424.
  25. ^ Han, Liying; Lu, Linlin; Fu, Peng; Ren, Chao; Cai, Meng; Li, Qingting (2023). “Exploring the seasonality of surface urban heat islands using enhanced land surface temperature in a semi-arid city”. Urban Climate. 49: 101455. Bibcode:2023UrbCl..4901455H. doi:10.1016/j.uclim.2023.101455.
  26. ^ “Executive Summary: Creating and Mapping an Urban Heat Island Index for California” (PDF). CalEPA | California Environmental Protection Agency. October 2016. Archived (PDF) from the original on 2019-07-31. Retrieved 2024-07-24.
  27. ^ Jump up to:a b “Understanding the Urban Heat Island Index | CalEPA”. CalEPA | California Environmental Protection Agency. Archived from the original on 2017-12-19. Retrieved 2024-07-24.
  28. ^ Jump up to:a b “Creating and Mapping an Urban Heat Island Index for California” (PDF). CalEPA | California Environmental Protection Agency. October 2016. Archived (PDF) from the original on 2019-07-31. Retrieved 2024-07-24.
  29. ^ Steeneveld, G. J. (2011). “Quantifying urban heat island effects and human comfort for cities of variable size and urban morphology in the Netherlands”. Journal of Geophysical Research. 116 (D20): D20129. Bibcode:2011JGRD..11620129S. doi:10.1029/2011JD015988.
  30. ^ Kershaw, T. J.; Sanderson, M.; Coley, D.; Eames, M. (2010). “Estimation of the urban heat island for UK climate change projections”. Building Services Engineering Research and Technology. 31 (3): 251–263. doi:10.1177/0143624410365033. hdl:10871/13934.
  31. ^ Theeuwes, N. E.; Steeneveld, G. J.; Ronda, R. J.; Holtslag, A. A. M. (2017). “A diagnostic equation for the daily maximum urban heat island effect for cities in northwestern Europe”. International Journal of Climatology. 37 (1): 443–454. Bibcode:2017IJCli..37..443T. doi:10.1002/joc.4717. S2CID 131437962.
  32. ^ Jump up to:a b c Myrup, Leonard O. (1969). “A Numerical Model of the Urban Heat Island”. Journal of Applied Meteorology. 8 (6): 908–918. Bibcode:1969JApMe…8..908M. doi:10.1175/1520-0450(1969)008<0908:ANMOTU>2.0.CO;2.
  33. ^ n.n. “ENVI-met-Alternativen für Mac — Altapps.net”. de.altapps.net (in German). Retrieved 2022-06-01.
  34. ^ Jump up to:a b Oke, T. R. (1982). “The energetic basis of the urban heat island”. Quarterly Journal of the Royal Meteorological Society. 108 (455): 1–24. Bibcode:1982QJRMS.108….1O. doi:10.1002/qj.49710845502. S2CID 120122894.
  35. ^ Jump up to:a b Hoehne, Christopher G.; Chester, Mikhail V.; Sailor, David J.; King, David A. (4 July 2022). “Urban Heat Implications from Parking, Roads, and Cars: a Case Study of Metro Phoenix”. Sustainable and Resilient Infrastructure. 7 (4): 272–290. Bibcode:2022SusRI…7..272H. doi:10.1080/23789689.2020.1773013. S2CID 225553384.
  36. ^ Kumar, Rahul; Mishra, Vimal; Buzan, Jonathan; Kumar, Rohini; Shindell, Drew; Huber, Matthew (25 October 2017). “Dominant control of agriculture and irrigation on urban heat island in India”. Scientific Reports. 7 (1): 14054. Bibcode:2017NatSR…714054K. doi:10.1038/s41598-017-14213-2. PMC 5656645. PMID 29070866.
  37. ^ Larsson, Naomi (10 May 2018). “US cities losing 36 million trees a year, researchers find”. The Guardian. Retrieved 10 May 2018.
  38. ^ Santos, Fabiane (23 August 2013). “Trees – the Natural Air Conditioners”. Scientific Scribbles. University of Melbourne. Archived from the original on 2022-04-07.
  39. ^ Gorsevski, V.; Luvall, J.; Quattrochi, D.; Taha, H. (1998). “Air Pollution Prevention Through Urban Heat Island Mitigation: An Update on the Urban Heat Island Pilot Project” (PDF). Lawrence Berkeley National Lab. (LBNL). CiteSeerX 10.1.1.111.4921. LBNL-42736.
  40. ^ Sailor, D. J. (2011). “A review of methods for estimating anthropogenic heat and moisture emissions in the urban environment”. International Journal of Climatology. 31 (2): 189–199. Bibcode:2011IJCli..31..189S. doi:10.1002/joc.2106. S2CID 54835415.
  41. ^ Chen, F.; Kusaka, H.; Bornstein, R.; Ching, J.; Grimmond, C. S. B.; Grossman-Clarke, S.; Loridan, T.; Manning, K. W.; Martilli, A.; Miao, S.; Sailor, D.; Salamanca, F. P.; Taha, H.; Tewari, M.; Wang, X.; Wyszogrodzki, A. A.; Zhang, C. (2011). “The integrated WRF/urban modelling system: Development, evaluation, and applications to urban environmental problems”. International Journal of Climatology. 31 (2): 273. Bibcode:2011IJCli..31..273C. doi:10.1002/joc.2158. S2CID 54686199.
  42. ^ Mansourmoghaddam, Mohammad; Alavipanah, Seyed Kazem (2022). “Study and prediction of land surface temperature changes of Yazd city: assessing the proximity and changes of land cover”. RS and GIS for Natural Resources. 12 (4): 1–27.
  43. ^ Union of Concerned Scientists. “Rising Temperatures, Worsening Ozone Pollution.” Climate Change and Your Health (2011): n. pag. Print.
  44. ^ “Technical Summary”. Climate Change 2022 – Impacts, Adaptation and Vulnerability. 2023. pp. 37–118. doi:10.1017/9781009325844.002. ISBN 978-1-009-32584-4.
  45. ^ Arizona Board of Regents (2006). “Urban Climate – Climate Study and UHI”. Arizona State University. Archived from the original on 2007-11-23. Retrieved 2007-08-02.
  46. ^ van Heerwaarden, Chiel C. & Vilà-Guerau de Arellano, J. (2008). “Relative humidity as an indicator for cloud formation over heterogeneous land surfaces”. Journal of the Atmospheric Sciences. 65 (10): 3263–3277. Bibcode:2008JAtS…65.3263V. doi:10.1175/2008JAS2591.1. S2CID 56010396.
  47. ^ Fuchs, Dale (2005-06-28). “Spain goes hi-tech to beat drought”. The Guardian. Retrieved 2007-08-02.
  48. ^ Goddard Space Flight Center (2002-06-18). “NASA Satellite Confirms Urban Heat Islands Increase Rainfall Around Cities”. National Aeronautics and Space Administration. Archived from the original on June 12, 2008. Retrieved 2009-07-17.
  49. ^ Zhou, Decheng; Zhao, Shuqing; Zhang, Liangxia; Sun, Ge; Liu, Yongqiang (10 June 2015). “The footprint of urban heat island effect in China”. Scientific Reports. 5: 11160. Bibcode:2015NatSR…511160Z. doi:10.1038/srep11160. PMC 4461918. PMID 26060039.
  50. ^ Peterson, T. C.; Gallo, K. P.; Lawrimore, J.; Owen, T. W.; Huang, A.; McKittrick, D. A. (1999). “Global rural temperature trends”. Geophysical Research Letters. 26 (3): 329–332. Bibcode:1999GeoRL..26..329P. doi:10.1029/1998GL900322.
  51. ^ J. Zhang, Guang; Cai, Ming; Hu, Aixue (27 January 2013). “Energy consumption and the unexplained winter warming over northern Asia and North America”. Nature Climate Change. 3 (5): 466–470. Bibcode:2013NatCC…3..466Z. doi:10.1038/nclimate1803.
  52. ^ Broadbent, Ashley Mark; Krayenhoff, Eric Scott; Georgescu, Matei (13 August 2020). “The motley drivers of heat and cold exposure in 21st century US cities”. Proceedings of the National Academy of Sciences. 117 (35): 21108–21117. Bibcode:2020PNAS..11721108B. doi:10.1073/pnas.2005492117. PMC 7474622. PMID 32817528.
  53. ^ Clarke, J. F. (1972). “Some effects of the urban structure on heat mortality”. Environmental Research. 5 (1): 93–104. Bibcode:1972ER……5…93C. doi:10.1016/0013-9351(72)90023-0. PMID 5032928.
  54. ^ Kovats, R. Sari; Hajat, Shakoor (April 2008). “Heat Stress and Public Health: A Critical Review”. Annual Review of Public Health. 29 (1): 41–55. doi:10.1146/annurev.publhealth.29.020907.090843. PMID 18031221.
  55. ^ Adams-Fuller, Terri (2023-07-01). “Extreme Heat Is Deadlier Than Hurricanes, Floods and Tornadoes Combined”. Scientific American. Retrieved 2024-05-02.
  56. ^ “The Impacts of Extreme Heat on Mental Health”. Psychiatric Times. 2019-07-30. Retrieved 2024-05-02.
  57. ^ Cho, Hyunkuk (May 2017). “The effects of summer heat on academic achievement: A cohort analysis”. Journal of Environmental Economics and Management. 83: 185–196. Bibcode:2017JEEM…83..185C. doi:10.1016/j.jeem.2017.03.005.
  58. ^ Jump up to:a b c d “Assessment of International Urban Heat Island Research” (PDF). U.S. Department of Energy Report. Navigant Consulting. Archived from the original (PDF) on 17 February 2013. Retrieved 30 April 2014.
  59. ^ Jump up to:a b Koppe, Christina; Kovats, Sari; Jendritzky, Gerd; Menne, Bettina (2004). “Heat-waves: risks and responses”. Health and Global Environmental Change Series. 2. Archived from the original on 2023-03-22. Retrieved 2014-05-07.
  60. ^ Shi, Yuan; Katzschner, Lutz; Ng, Edward (March 2018). “Modelling the fine-scale spatiotemporal pattern of urban heat island effect using land use regression approach in a megacity”. Science of the Total Environment. 618: 891–904. Bibcode:2018ScTEn.618..891S. doi:10.1016/j.scitotenv.2017.08.252. PMID 29096959.
  61. ^ Wang, Pin; Goggins, William B.; Shi, Yuan; Zhang, Xuyi; Ren, Chao; Ka-Lun Lau, Kevin (June 2021). “Long-term association between urban air ventilation and mortality in Hong Kong”. Environmental Research. 197: 111000. Bibcode:2021ER….19711000W. doi:10.1016/j.envres.2021.111000. PMID 33745928. S2CID 232310626.
  62. ^ Weng, Qihao; Firozjaei, Mohammad Karimi; Sedighi, Amir; Kiavarz, Majid; Alavipanah, Seyed Kazem (19 May 2019). “Statistical analysis of surface urban heat island intensity variations: A case study of Babol city, Iran”. GIScience & Remote Sensing. 56 (4): 576–604. Bibcode:2019GISRS..56..576W. doi:10.1080/15481603.2018.1548080. S2CID 134003294.
  63. ^ Yuan, F. (2007). “Comparison of impervious surface area and normalized difference vegetation index as indicators of surface urban heat island effects in Landsat imagery”. Remote Sensing of Environment. 106 (3): 375–386. Bibcode:2007RSEnv.106..375Y. doi:10.1016/j.rse.2006.09.003.
  64. ^ NYS DEC. “Streams Tributary to Onondaga Lake Biological Assessment.” Dec.ny.gov. N.p., 2008. Web. 12 September 2013.
  65. ^ “Fish Kill Event – McLoud Run”. Iowa DNR Fish Kill Database.
  66. ^ Tipler, Paul A. & Mosca, Gene (2007). Physics for Scientists and Engineers. Macmillan. p. 686. ISBN 978-1-4292-0124-7.
  67. ^ “Urban Climate – Climate Study and UHI”. United States Environmental Protection Agency. 2009-02-09. Retrieved 2009-06-18.
  68. ^ “Islands in the Sun”. Institute on the Environment. University of Minnesota. Archived from the original on 2016-03-03. Retrieved 2014-11-11.
  69. ^ “Cool Pavement Report” (PDF). Environmental Protection Agency. June 2005. pp. 21, 43. Retrieved 2013-01-15.
  70. ^ Jump up to:a b c Shochat, Eyal; Warren, Paige S.; Faeth, Stanley H.; Mclntyre, Nancy E.; Hope, Diane (April 2006). “From Patterns to Emerging Processes in Mechanistic Urban Ecology”. Trends in Ecology & Evolution. 21 (4): 186–91. doi:10.1016/j.tree.2005.11.019. PMID 16701084.
  71. ^ Tang, Teri (2014-06-05). “Where are the Insects?”. School of Life Sciences. Arizona State University. Retrieved 19 October 2014.
  72. ^ Chang, Sheng-chieh (2000-06-23). “Energy Use”. Environmental Energies Technology Division. Archived from the original on March 11, 2009. Retrieved 2009-06-18.
  73. ^ “Aging and Weathering of Cool Roofing Membranes” (PDF). Cool Roofing Symposium. 2005-08-23. Archived from the original (PDF) on 2011-11-15. Retrieved 2010-08-16.
  74. ^ Jump up to:a b Rosenfeld, Arthur H.; Akbari, Hashem; Romm, Joseph J.; Pomerantz, Melvin (1998). “Cool communities: strategies for heat island mitigation and smog reduction” (PDF). Energy and Buildings. 28 (1): 51–62. Bibcode:1998EneBu..28…51R. doi:10.1016/S0378-7788(97)00063-7.
  75. ^ Salamanca, F.; Georgescu, M.; Mahalov, A.; Moustaoui, M.; Wang, M. (27 May 2014). “Anthropogenic heating of the urban environment due to air conditioning”. Journal of Geophysical Research: Atmospheres. 119 (10): 5949–5965. Bibcode:2014JGRD..119.5949S. doi:10.1002/2013JD021225.
  76. ^ Jump up to:a b “Making roofs white or reflective is the best way to keep a city cool”. New Scientist. Retrieved 2024-07-11.
  77. ^ Albers, R. A. W.; Bosch, P. R.; Blocken, B.; van den Dobbelsteen, A. A. J. F.; van Hove, L. W. A.; Spit, T. J. M.; van de Ven, F.; van Hooff, T.; Rovers, V. (January 2015). “Overview of challenges and achievements in the climate adaptation of cities and in the Climate Proof Cities program” (PDF). Building and Environment. 83: 1–10. Bibcode:2015BuEnv..83….1A. doi:10.1016/j.buildenv.2014.09.006. hdl:1874/309149.
  78. ^ Michał Kaszewski: „Miejska wyspa ciepła – sposoby jej ograniczania”: Wykład popularno-naukowy: „Miejska wyspa ciepła – sposoby jej ograniczania”[unreliable source?]
  79. ^ Jump up to:a b Rosenfeld, Arthur H.; Romm, Joseph J.; Akbari, Hashem; Lloyd, Alan C. (February 1997). “Painting the town white—and green”. Technology Review. 100 (2): 52–59.
  80. ^ “Top 22 Benefits of Trees”. Tree People. Retrieved 7 July 2014.
  81. ^ “Trees and Vegetation”. EPA.gov. 2014-02-28. Retrieved 7 July 2014.
  82. ^ Jump up to:a b c Zinzi, M.; Agnoli, S. (2012). “Cool and green roofs. An energy and comfort comparison between passive cooling and mitigation urban heat island techniques for residential buildings in the Mediterranean region”. Energy and Buildings. 55: 66–76. Bibcode:2012EneBu..55…66Z. doi:10.1016/j.enbuild.2011.09.024.
  83. ^ “Comprehensive Cool Roof Guide from the Vinyl Roofing Division of the Chemical Fabrics and Film Association”. Archived from the original on 2013-09-21.
  84. ^ “Cool Pavement Report” (PDF). Environmental Protection Agency. June 2005. p. 14. Retrieved 2009-02-06.
  85. ^ Gore, Al; Steffen, A. (2008). World Changing: A User’s Guide for the 21st Century. New York: Abrams. p. 258.
  86. ^ Yaghoobian, N.; Kleissl, J. (2012). “Effect of reflective pavements on building energy use”. Urban Climate. 2: 25–42. Bibcode:2012UrbCl…2…25Y. doi:10.1016/j.uclim.2012.09.002.
  87. ^ Yang, Jiachuan; Wang, Zhihua; Kaloush, Kamil E. (October 2013), Unintended Consequences: A Research Synthesis Examining the Use of Reflective Pavements to Mitigate the Urban Heat Island Effect (PDF), Tempe, Arizona: NCE SMART Innovations, archived from the original (PDF) on 2013-12-02, retrieved 2013-11-25
  88. ^ “Whitest-ever paint could help cool heating Earth, study shows”. The Guardian. April 15, 2021. Retrieved April 16, 2021.
  89. ^ Li, Xiangyu; Peoples, Joseph; Yao, Peiyan; Ruan, Xiulin (12 May 2021). “Ultrawhite BaSO 4 Paints and Films for Remarkable Daytime Subambient Radiative Cooling”. ACS Applied Materials & Interfaces. 13 (18): 21733–21739. doi:10.1021/acsami.1c02368. PMID 33856776. S2CID 233259255.
  90. ^ “Green (Planted) Roofs”. Archived from the original on 2011-07-28. Retrieved 2010-08-07.
  91. ^ Liu, Hongqing; Kong, Fanhua; Yin, Haiwei; Middel, Ariane; Zheng, Xiandi; Huang, Jing; Xu, Hairong; Wang, Ding; Wen, Zhihao (2021). “Impacts of green roofs on water, temperature, and air quality: A bibliometric review”. Building and Environment. 196: 107794. Bibcode:2021BuEnv.19607794L. doi:10.1016/j.buildenv.2021.107794. ISSN 0360-1323.
  92. ^ “Four Barriers to Implementing Green Roofs – And How to Overcome Them | Nicole Holmes”. Living Architecture Monitor. Retrieved 2024-07-01.
  93. ^ Jump up to:a b c Teotónio, Inês; Silva, Cristina Matos; Cruz, Carlos Oliveira (2021). “Economics of green roofs and green walls: A literature review”. Sustainable Cities and Society. 69: 102781. Bibcode:2021SusCS..6902781T. doi:10.1016/j.scs.2021.102781. ISSN 2210-6707.
  94. ^ Feng, Haibo; Hewage, Kasun N. (2018). “Economic benefits and costs of green roofs”. Nature based strategies for urban and building sustainability. Butterworth-Heinemann. pp. 307–318. doi:10.1016/B978-0-12-812150-4.00028-8. ISBN 978-0-12-812150-4.
  95. ^ “Stormwater Management Objectives” (PDF). www.gosnells.wa.gov.au.
  96. ^ Wang, Junsong; Meng, Qinglin; Zou, Ya; Qi, Qianlong; Tan, Kanghao; Santamouris, Mat; He, Bao-Jie (August 2022). “Performance synergism of pervious pavement on stormwater management and urban heat island mitigation: A review of its benefits, key parameters, and co-benefits approach”. Water Research. 221: 118755. Bibcode:2022WatRe.22118755W. doi:10.1016/j.watres.2022.118755. PMID 35728492.
  97. ^ Hiltrud Pötz & Pierre Bleuze (2011). Urban green-blue grids for sustainable and dynamic cities. Delft: Coop for life. ISBN 978-90-818804-0-4.
  98. ^ Chiesura, Anna (2004). “The role of urban parks for the sustainable city”. Landscape and Urban Planning. 68 (1): 129–138. Bibcode:2004LUrbP..68..129C. doi:10.1016/j.landurbplan.2003.08.003.
  99. ^ “Sustainable trade infrastructure in Africa: A key element for growth and prosperity?”. International Centre for Trade and Sustainable Development.
  100. ^ “Nachhaltigesinvestment 2016”. Archived from the original on 2017-01-23. Retrieved 2022-03-19.
  101. ^ Staddon, Chad; Ward, Sarah; De Vito, Laura; Zuniga-Teran, Adriana; Gerlak, Andrea K.; Schoeman, Yolandi; Hart, Aimee; Booth, Giles (September 2018). “Contributions of green infrastructure to enhancing urban resilience”. Environment Systems and Decisions. 38 (3): 330–338. Bibcode:2018EnvSD..38..330S. doi:10.1007/s10669-018-9702-9. S2CID 62800263.
  102. ^ Heo, Se-Yeon; Lee, Gil Ju; Song, Young Min (2022). “Heat-shedding with photonic structures: radiative cooling and its potential”. Journal of Materials Chemistry C. 10 (27): 9915–9937. doi:10.1039/D2TC00318J. S2CID 249695930.
  103. ^ Zhou, Kai; Miljkovic, Nenad; Cai, Lili (March 2021). “Performance analysis on system-level integration and operation of daytime radiative cooling technology for air-conditioning in buildings”. Energy and Buildings. 235: 110749. Bibcode:2021EneBu.23510749Z. doi:10.1016/j.enbuild.2021.110749. S2CID 234180182.
  104. ^ Howard, Luke (2012) [1818]. The Climate of London Deduced from Meteorological Observations. Vol. 1. Cambridge University Press. ISBN 9781108049511.
  105. ^ Heidorn, Keith C. (2009). “Luke Howard: The Man Who Named The Clouds”. Islandnet.com. Retrieved 2009-06-18.
  106. ^ Stewart, Iain D. (December 2019). “Why should urban heat island researchers study history?”. Urban Climate. 30: 100484. Bibcode:2019UrbCl..3000484S. doi:10.1016/j.uclim.2019.100484. S2CID 203337407.
  107. ^ Masson, Valéry; Lemonsu, Aude; Hidalgo, Julia; Voogt, James (2020-10-17). “Urban Climates and Climate Change”. Annual Review of Environment and Resources. 45 (1): 411–444. doi:10.1146/annurev-environ-012320-083623.
  108. ^ Díaz, J.; Jordán, A.; García, R.; López, C.; Alberdi, J.; Hernández, E.; Otero, A. (1 February 2014). “Heat waves in Madrid 1986–1997: effects on the health of the elderly”. International Archives of Occupational and Environmental Health. 75 (3): 163–170. doi:10.1007/s00420-001-0290-4. PMID 11954983. S2CID 31284700.
  109. ^ Harlan, Sharon L.; Brazel, Anthony J.; Prashad, Lela; Stefanov, William L.; Larsen, Larissa (December 2006). “Neighborhood microclimates and vulnerability to heat stress”. Social Science & Medicine. 63 (11): 2847–2863. doi:10.1016/j.socscimed.2006.07.030. hdl:2286/R.I.55228. PMID 16996668.
  110. ^ US Environmental Protection Agency, OAR (2019-11-06). “Heat Islands and Equity”. www.epa.gov. Retrieved 2024-04-18.
  111. ^ Wilson, Bev (October 2020). “Urban Heat Management and the Legacy of Redlining”. Journal of the American Planning Association. 86 (4): 443–457. doi:10.1080/01944363.2020.1759127.
  112. ^ Adams, Kaitlyn; Knuth, Colette Steward (January 2024). “The effect of urban heat islands on pediatric asthma exacerbation: How race plays a role”. Urban Climate. 53: 101833. Bibcode:2024UrbCl..5301833A. doi:10.1016/j.uclim.2024.101833.
  113. ^ Zhu, Pengyu; Zhang, Yaoqi (March 2008). “Demand for urban forests in United States cities”. Landscape and Urban Planning. 84 (3–4): 293–300. Bibcode:2008LUrbP..84..293Z. doi:10.1016/j.landurbplan.2007.09.005.
  114. ^ De Chant, Tim (2008). “Urban Trees Reveal Income Inequality”. Landscape and Urban Planning. 84 (3). Per Square Mile. Bibcode:2008LUrbP..84..293Z. doi:10.1016/j.landurbplan.2007.09.005. Retrieved 7 May 2014.
  115. ^ Chant, Tim (2008). “Urban Trees reveal income inequality”. Landscape and Urban Planning. 84 (3). Bibcode:2008LUrbP..84..293Z. doi:10.1016/j.landurbplan.2007.09.005. Retrieved 7 July 2014.
  116. ^ DeSilver, Drew (2021-08-02). “As national eviction ban expires, a look at who rents and who owns in the U.S.” Pew Research Center. Retrieved 2024-05-02.
  117. ^ Ramirez, Rachel (2022-07-20). “Faced with more deadly heat waves, US cities are taking an unprecedented step”. CNN. Archived from the original on 2023-01-06. Retrieved 2023-01-06.
  118. ^ Moloney, Anastasia (2022-11-09). “How ‘chief heat officers’ keep cities cool as the world warms”. Reuters. Archived from the original on 2023-01-06. Retrieved 2023-01-06.
  119. ^ Markey, Edward J. (2020-07-22). “S.4280 – 116th Congress (2019–2020): Preventing HEAT Illness and Deaths Act of 2020”. www.congress.gov. Retrieved 2021-10-26.
  120. ^ “New federal bill supports heat island mitigation”. U.S. Green Building Council. Retrieved 2021-10-26.
  121. ^ New York City Regional Heat Island Initiative (October 2006). “Mitigating New York City’s Heat Island With Urban Forestry, Living Roofs, and Light Surfaces” (PDF). New York State Energy Research and Development Authority. p. ii. Retrieved 2009-06-18.[permanent dead link]
  122. ^ Wilmsen, Carl. Partnerships for Empowerment: Participatory Research for Community-based Natural Resource Management. London, England: Earthscan, 2008. Print.
  123. ^ “Cool solutions for urban heat islands | Stanford Woods Institute for the Environment”. woods.stanford.edu. October 26, 2023. Retrieved 2024-05-02.
  124. ^ KristinaP. “Collaborative Heat Mapping Research Project”. Virginia Foundation for Independent Colleges. Retrieved 2024-05-02.
  125. ^ “Cool Neighborhoods NYC”. NYC Mayor’s Office of Climate and Environmental Justice. 2017-06-14. Retrieved 2024-05-02.
  126. ^ Balasubramanian, D. (2020-02-15). “Urban heat islands in India”. The Hindu. ISSN 0971-751X. Retrieved 2024-10-23.
  127. ^ “Mumbai’s spendings will be double of New York’s to manage urban heat generated due to concretisation”. The Times of India. 2024-02-06. ISSN 0971-8257. Retrieved 2024-10-23.

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