Urban heat island: Difference between revisions
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{{Short description| |
{{Short description|Situation where cities are warmer than surrounding areas}} |
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{{About|higher temperatures in cities due to urbanization effects|effects of climate change on city temperatures|climate change and cities}} |
{{About|higher temperatures in cities due to urbanization effects|effects of climate change on city temperatures|climate change and cities}} |
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{{merge from|Urban dust dome|date=October 2023|discuss=Talk:Urban dust dome#This article should be consolidated with "Urban Heat Island" article}} |
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[[Urban area]]s usually experience the '''urban heat island''' ('''UHI''') effect, that is, they are significantly warmer than surrounding [[rural area]]s. The [[temperature]] difference is usually larger at night than during the day,<ref name="Phelan">{{cite journal |last1=Phelan |first1=Patrick E. |last2=Kaloush |first2=Kamil |last3=Miner |first3=Mark |last4=Golden |first4=Jay |last5=Phelan |first5=Bernadette |last6=Silva |first6=Humberto |last7=Taylor |first7=Robert A. |title=Urban Heat Island: Mechanisms, Implications, and Possible Remedies |journal=Annual Review of Environment and Resources |date=4 November 2015 |volume=40 |issue=1 |pages=285–307 |doi=10.1146/annurev-environ-102014-021155 |s2cid=154497357 |doi-access=free }}</ref> and is most apparent when [[wind]]s are weak, under [[Block (meteorology)|block]] conditions, noticeably during the [[summer]] and [[winter]]. |
[[Urban area]]s usually experience the '''urban heat island''' ('''UHI''') effect, that is, they are significantly warmer than surrounding [[rural area]]s. The [[temperature]] difference is usually larger at night than during the day,<ref name="Phelan">{{cite journal |last1=Phelan |first1=Patrick E. |last2=Kaloush |first2=Kamil |last3=Miner |first3=Mark |last4=Golden |first4=Jay |last5=Phelan |first5=Bernadette |last6=Silva |first6=Humberto |last7=Taylor |first7=Robert A. |title=Urban Heat Island: Mechanisms, Implications, and Possible Remedies |journal=Annual Review of Environment and Resources |date=4 November 2015 |volume=40 |issue=1 |pages=285–307 |doi=10.1146/annurev-environ-102014-021155 |s2cid=154497357 |doi-access=free }}</ref> and is most apparent when [[wind]]s are weak, under [[Block (meteorology)|block]] conditions, noticeably during the [[summer]] and [[winter]]. |
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The main cause of the UHI effect is from the modification of land surfaces while [[waste heat]] generated by energy usage is a secondary contributor.<ref name="dx.doi.org">{{cite journal | last1 = Solecki | first1 = William D. | last2 = Rosenzweig | first2 = Cynthia | last3 = Parshall | first3 = Lily | last4 = Pope | first4 = Greg | last5 = Clark | first5 = Maria | last6 = Cox | first6 = Jennifer | last7 = Wiencke | first7 = Mary | year = 2005 | title = Mitigation of the heat island effect in urban New Jersey | journal = Global Environmental Change Part B: Environmental Hazards | volume = 6 | issue = 1| pages = 39–49 | doi = 10.1016/j.hazards.2004.12.002 | s2cid = 153841143 }}</ref><ref>{{Cite report|url=https://www.epa.gov/heat-islands/heat-island-compendium|title=Reducing urban heat islands: Compendium of strategies|last=United States Environmental Protection Agency|date=2008|pages=7–12}}</ref><ref name="liyan2012">{{Cite journal | last1 = Li | first1 = Y. | last2 = Zhao | first2 = X. | doi = 10.1029/2012JD018132 | title = An empirical study of the impact of human activity on long-term temperature change in China: A perspective from energy consumption | journal = Journal of Geophysical Research | volume = 117 | issue = D17 | pages = D17117 | year = 2012 |bibcode = 2012JGRD..11717117L | doi-access = free }}</ref> |
The main cause of the UHI effect is from the modification of land surfaces while [[waste heat]] generated by energy usage is a secondary contributor.<ref name="dx.doi.org">{{cite journal | last1 = Solecki | first1 = William D. | last2 = Rosenzweig | first2 = Cynthia | last3 = Parshall | first3 = Lily | last4 = Pope | first4 = Greg | last5 = Clark | first5 = Maria | last6 = Cox | first6 = Jennifer | last7 = Wiencke | first7 = Mary | year = 2005 | title = Mitigation of the heat island effect in urban New Jersey | journal = Global Environmental Change Part B: Environmental Hazards | volume = 6 | issue = 1| pages = 39–49 | doi = 10.1016/j.hazards.2004.12.002 | s2cid = 153841143 }}</ref><ref>{{Cite report|url=https://www.epa.gov/heat-islands/heat-island-compendium|title=Reducing urban heat islands: Compendium of strategies|last=United States Environmental Protection Agency|date=2008|pages=7–12}}</ref><ref name="liyan2012">{{Cite journal | last1 = Li | first1 = Y. | last2 = Zhao | first2 = X. | doi = 10.1029/2012JD018132 | title = An empirical study of the impact of human activity on long-term temperature change in China: A perspective from energy consumption | journal = Journal of Geophysical Research | volume = 117 | issue = D17 | pages = D17117 | year = 2012 |bibcode = 2012JGRD..11717117L | doi-access = free }}</ref> Urban areas occupy about 0.5% of the Earth's land surface but host more than half of the world's population.<ref>{{Cite journal |last=Wang |first=K. |date=February 6, 2017 |title=Comparing the diurnal and seasonal variabilities of atmospheric, and surface urban heat islands based on the Beijing Urban Meteorological Network |journal=Journal of Geophysical Research: Atmospheres |volume=122 |issue=4 |pages=2131–2154 |bibcode=2017JGRD..122.2131W |doi=10.1002/2016JD025304 |doi-access=free}}</ref> As a population center grows, it tends to expand its area and increase its average temperature. The term '''heat island''' is also used; the term can be used to refer to any area that is relatively hotter than the surrounding, but generally refers to human-disturbed areas.<ref>{{cite web |author=Glossary of Meteorology |year=2019 |title=Urban Heat Island |url=http://glossary.ametsoc.org/wiki/Urban_heat_island |access-date=2019-04-12 |publisher=[[American Meteorological Society]]}}</ref> |
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Monthly [[precipitation (meteorology)|rainfall]] is greater downwind of cities, partially due to the UHI. Increases in heat within urban centers increases the length of [[growing season]]s and decreases the occurrence of weak [[tornado]]es. The UHI decreases [[air quality]] by increasing the production of pollutants such as [[ozone]], and decreases water quality as warmer waters flow into area streams and put stress on their [[ecosystem]]s. |
Monthly [[precipitation (meteorology)|rainfall]] is greater downwind of cities, partially due to the UHI. Increases in heat within urban centers increases the length of [[growing season]]s and decreases the occurrence of weak [[tornado]]es. The UHI decreases [[air quality]] by increasing the production of pollutants such as [[ozone]], and decreases water quality as warmer waters flow into area streams and put stress on their [[ecosystem]]s. |
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Not all cities have a distinct urban heat island, and the heat island characteristics depend strongly on the background climate of the area in which the city is located.<ref name="SUE">{{cite journal|author=T. |
Not all cities have a distinct urban heat island, and the heat island characteristics depend strongly on the background climate of the area in which the city is located.<ref name="SUE">{{cite journal |author=Chakraborty |first=T. |last2=Lee |first2=X. |name-list-style=and |year=2019 |title=A simplified urban-extent algorithm to characterize surface urban heat islands on a global scale and examine vegetation control on their spatiotemporal variability |journal=International Journal of Applied Earth Observation and Geoinformation |volume=74 |pages=269–280 |bibcode=2019IJAEO..74..269C |doi=10.1016/j.jag.2018.09.015 |s2cid=53715577}}</ref> The impact in a city can change a lot based on its local environment. Heat can be reduced by tree cover and green space which act as sources of shade and promote [[Evapotranspiration|evaporative]] cooling.<ref name="Waldrop">{{cite journal |last1=Waldrop |first1=M. Mitchell |title=What can cities do to survive extreme heat? |journal=Knowable Magazine |date=19 October 2022 |doi=10.1146/knowable-101922-2 |doi-access=free |url=https://knowablemagazine.org/article/society/2022/what-can-cities-do-survive-extreme-heat |access-date=6 December 2022}}</ref> Other options include [[green roof]]s, [[passive daytime radiative cooling]] applications, and the [[reflective surfaces (climate engineering)|use of lighter-colored surfaces]] and less absorptive building materials. These reflect more sunlight and absorb less heat.<ref>{{Cite web|title=Nature of Cities|url=https://regeneration.org/nexus/nature-of-cities|access-date=2021-10-16|website=Regeneration.org }}</ref><ref name=":2" /><ref name=":13" /> |
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[[Climate change]] is not the cause of urban heat islands but it is causing more frequent and more intense [[heat wave]]s which in turn amplify the urban heat island effect in cities.<ref name=":1">{{cite book |doi=10.1017/9781009325844.008 |chapter=Cities, Settlements and Key Infrastructure |title=Climate Change 2022 – Impacts, Adaptation and Vulnerability |date=2023 |pages=907–1040 |isbn=978-1-009-32584-4 }}</ref>{{rp|993}} Compact, dense [[Urban Development|urban development]] may increase the urban heat island effect, leading to higher temperatures and increased exposure.<ref>{{Cite journal |last=Sharifi |first=Ayyoob |date=2020 |title=Trade-offs and conflicts between urban climate change mitigation and adaptation measures: A literature review |journal=Journal of Cleaner Production |volume=276 |page=122813 |doi=10.1016/j.jclepro.2020.122813 |s2cid=225638176 }}</ref> |
[[Climate change]] is not the cause of urban heat islands but it is causing more frequent and more intense [[heat wave]]s which in turn amplify the urban heat island effect in cities.<ref name=":1">{{cite book |doi=10.1017/9781009325844.008 |chapter=Cities, Settlements and Key Infrastructure |title=Climate Change 2022 – Impacts, Adaptation and Vulnerability |date=2023 |pages=907–1040 |isbn=978-1-009-32584-4 }}</ref>{{rp|993}} Compact, dense [[Urban Development|urban development]] may increase the urban heat island effect, leading to higher temperatures and increased exposure.<ref>{{Cite journal |last=Sharifi |first=Ayyoob |date=2020 |title=Trade-offs and conflicts between urban climate change mitigation and adaptation measures: A literature review |journal=Journal of Cleaner Production |volume=276 |page=122813 |doi=10.1016/j.jclepro.2020.122813 |bibcode=2020JCPro.27622813S |s2cid=225638176 }}</ref> |
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⚫ | A definition of ''urban heat island'' is: "The relative warmth of a city compared with surrounding rural areas."<ref name=":4">{{cite book |doi=10.1017/9781009325844.029 |chapter=Glossary |title=Climate Change 2022 – Impacts, Adaptation and Vulnerability |date=2023 |pages=2897–2930 |isbn=978-1-009-32584-4 }}</ref>{{rp|2926}} This relative warmth is caused by "heat trapping due to land use, the configuration and design of the [[built environment]], including street layout and building size, the heat-absorbing properties of urban building materials, reduced ventilation, reduced greenery and water features, and domestic and industrial heat emissions generated directly from human activities".<ref name=":4" />{{rp|2926}} |
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==Description == |
==Description == |
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[[File:Urban heat island.svg| |
[[File:Urban heat island.svg|upright=1.4|thumb|Mechanism of the urban heat island effect: the densely-built [[downtown]] areas tend to be warmer than suburban residential areas or rural areas. ]] |
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[[File:HeatIsland Kanto en.png|thumb|upright=1.55|[[Tokyo]], an example of an urban heat island. Normal temperatures of Tokyo go up higher than those of the surrounding area.]] |
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=== Diurnal variability === |
=== Diurnal variability === |
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[[File:Urban heat island variation.jpg|upright=1. |
[[File:Urban heat island variation.jpg|upright=1.55|thumb|Cities often experience stronger urban heat island effects at night; effects can vary with location and topography of metropolitan areas.]] |
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Throughout the daytime, particularly when the skies are cloudless, urban surfaces are warmed by the absorption of [[solar radiation]]. Surfaces in the urban areas tend to warm faster than those of the surrounding rural areas. By virtue of their high [[Heat capacity|heat capacities]], urban surfaces act as a reservoir of heat energy. For example, concrete can hold roughly 2,000 times as much heat as an equivalent volume of air. |
Throughout the daytime, particularly when the skies are cloudless, urban surfaces are warmed by the absorption of [[solar radiation]]. Surfaces in the urban areas tend to warm faster than those of the surrounding rural areas. By virtue of their high [[Heat capacity|heat capacities]], urban surfaces act as a reservoir of heat energy. For example, concrete can hold roughly 2,000 times as much heat as an equivalent volume of air.{{cn|date=July 2024}} As a result, high daytime surface temperatures within the UHI can be easily seen via thermal [[remote sensing]]. As is often the case with daytime heating, this warming also has the effect of generating [[Atmospheric convection|convective]] winds within the urban [[Planetary boundary layer|boundary layer]]. At night, the situation reverses. The absence of solar heating leads to the decrease of atmospheric convection and the stabilization of urban boundary layer. If enough stabilization occurs, an [[Inversion (meteorology)|inversion layer]] is formed. This traps urban air near the surface, keeping surface air warm from the still-warm urban surfaces, resulting in warmer nighttime air temperatures within the UHI. |
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Generally speaking, the difference in temperature between the urban and surrounding rural area is more pronounced at night than in daytime.<ref>{{Cite web |title=Urban Heat Islands {{!}} Center for Science Education |url=https://scied.ucar.edu/learning-zone/climate-change-impacts/urban-heat-islands |access-date=2024-07-02 |website=scied.ucar.edu}}</ref> For example, in the United States, the temperature in urban areas tends to be warmer than the surrounding area by about |
Generally speaking, the difference in temperature between the urban and surrounding rural area is more pronounced at night than in daytime.<ref>{{Cite web |title=Urban Heat Islands {{!}} Center for Science Education |url=https://scied.ucar.edu/learning-zone/climate-change-impacts/urban-heat-islands |access-date=2024-07-02 |website=scied.ucar.edu}}</ref> For example, in the United States, the temperature in urban areas tends to be warmer than the surrounding area by about 1–7 °F (0.6–4 °C) during the daytime, and about 2–5 °F (1–3 °C) warmer at night.<ref name=":22">{{Cite web |last=US Envrionmental Protection Agency |first=OAR |date=2014-06-17 |title=Learn About Heat Islands |url=https://www.epa.gov/heatislands/learn-about-heat-islands |access-date=2024-07-01 |website=www.epa.gov |language=en}}</ref> However, the difference is more pronounced during the day in arid climates such as those in southeastern China and Taiwan.<ref>{{Cite journal |last1=Zhou |first1=Decheng |last2=Zhang |first2=Liangxia |last3=Hao |first3=Lu |last4=Sun |first4=Ge |last5=Liu |first5=Yongqiang |last6=Zhu |first6=Chao |date=2016 |title=Spatiotemporal trends of urban heat island effect along the urban development intensity gradient in China |url=https://doi.org/10.1016/j.scitotenv.2015.11.168 |journal=Science of the Total Environment |volume=544 |pages=617–626 |doi=10.1016/j.scitotenv.2015.11.168 |pmid=26674691 |bibcode=2016ScTEn.544..617Z |issn=0048-9697}}</ref><ref>{{Cite journal |last1=Liou |first1=Yuei-An |last2=Tran |first2=Duy-Phien |last3=Nguyen |first3=Kim-Anh |date=2022-02-22 |title=Diurnal and Seasonal Characteristics of Surface Urban Heat Island in Taiwan |url=https://easychair.org/publications/preprint/MjGx |journal=(CETA 2021) 2021 International Conference on Computer Engineering, Technologies and Applications |language=en-US |issn=2516-2314}}</ref> Studies have shown that diurnal variability is impacted by several factors including local climate and weather, seasonality, humidity, vegetation, surfaces, and materials in the built environment.<ref>{{Cite journal |last1=Amorim |first1=Margarete Cristiane de Costa Trindade |last2=Dubreuil |first2=Vincent |last3=Amorim |first3=Amanda Trindade |date=2021 |title=Day and night surface and atmospheric heat islands in a continental and temperate tropical environment |url=https://doi.org/10.1016/j.uclim.2021.100918 |journal=Urban Climate |volume=38 |pages=100918 |doi=10.1016/j.uclim.2021.100918 |bibcode=2021UrbCl..3800918A |issn=2212-0955}}</ref><ref name=":22" /><ref>{{Cite journal |last1=Shastri |first1=Hiteshri |last2=Barik |first2=Beas |last3=Ghosh |first3=Subimal |last4=Venkataraman |first4=Chandra |last5=Sadavarte |first5=Pankaj |date=2017-01-09 |title=Flip flop of Day-night and Summer-Winter Surface Urban Heat Island Intensity in India |journal=Scientific Reports |language=en |volume=7 |issue=1 |pages=40178 |doi=10.1038/srep40178 |pmid=28067276 |issn=2045-2322|pmc=5220321 |bibcode=2017NatSR...740178S }}</ref><ref>{{Cite journal |last1=Mohajerani |first1=Abbas |last2=Bakaric |first2=Jason |last3=Jeffrey-Bailey |first3=Tristan |date=2017-07-15 |title=The urban heat island effect, its causes, and mitigation, with reference to the thermal properties of asphalt concrete |url=https://www.sciencedirect.com/science/article/pii/S0301479717303201 |journal=Journal of Environmental Management |volume=197 |pages=522–538 |doi=10.1016/j.jenvman.2017.03.095 |pmid=28412623 |bibcode=2017JEnvM.197..522M |issn=0301-4797}}</ref> |
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=== Seasonal variability === |
=== Seasonal variability === |
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Seasonal variability is less well understood than diurnal variability of the urban heat island temperature difference.<ref name=":8">{{Cite journal | |
Seasonal variability is less well understood than diurnal variability of the urban heat island temperature difference.<ref name=":8">{{Cite journal |last1=Manoli |first1=Gabriele |last2=Fatichi |first2=Simone |last3=Bou-Zeid |first3=Elie |last4=Katul |first4=Gabriel G. |date=2020-03-31 |title=Seasonal hysteresis of surface urban heat islands |journal=Proceedings of the National Academy of Sciences |language=en |volume=117 |issue=13 |pages=7082–7089 |doi=10.1073/pnas.1917554117 |doi-access=free |pmid=32184330 |issn=0027-8424|pmc=7132285 |bibcode=2020PNAS..117.7082M }}</ref> Complex relationships between precipitation, vegetation, solar radiation, and surface materials in various local climate zones play interlocking roles that influence seasonal patterns of temperature variation in a particular urban heat island.<ref name=":8" /><ref>{{Cite journal |last1=Imhoff |first1=Marc L. |last2=Zhang |first2=Ping |last3=Wolfe |first3=Robert E. |last4=Bounoua |first4=Lahouari |date=2010-03-15 |title=Remote sensing of the urban heat island effect across biomes in the continental USA |url=https://doi.org/10.1016/j.rse.2009.10.008 |journal=Remote Sensing of Environment |volume=114 |issue=3 |pages=504–513 |doi=10.1016/j.rse.2009.10.008 |bibcode=2010RSEnv.114..504I |issn=0034-4257|hdl=2060/20110015410 |hdl-access=free }}</ref><ref>{{Cite journal |last1=Cui |first1=Yu Yan |last2=Foy |first2=Benjamin de |date=2012-05-01 |title=Seasonal Variations of the Urban Heat Island at the Surface and the Near-Surface and Reductions due to Urban Vegetation in Mexico City |journal=Journal of Applied Meteorology and Climatology |language=EN |volume=51 |issue=5 |pages=855–868 |doi=10.1175/JAMC-D-11-0104.1 |issn=1558-8424|doi-access=free |bibcode=2012JApMC..51..855C }}</ref><ref>{{Cite journal |last1=Han |first1=Liying |last2=Lu |first2=Linlin |last3=Fu |first3=Peng |last4=Ren |first4=Chao |last5=Cai |first5=Meng |last6=Li |first6=Qingting |date=2023 |title=Exploring the seasonality of surface urban heat islands using enhanced land surface temperature in a semi-arid city |journal=Urban Climate |language=en |volume=49 |pages=101455 |doi=10.1016/j.uclim.2023.101455|doi-access=free |bibcode=2023UrbCl..4901455H }}</ref> |
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== Measurements and predictions == |
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=== Urban Heat Island Index (UHII) === |
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One method to quantify the UHI effect within urban areas is the UHI Index created by the [[California Environmental Protection Agency|Californian EPA]] in 2015. It compares the temperature of a surveyed area and rural reference points upwind from the surveyed area, at a height of two meters above ground level. The difference in temperature in degrees [[Celsius]] is taken hourly and differences with an increased urban temperature compared to the reference points are summed up, creating an amount of degree-Celsius-hours, which is the UHI Index of the surveyed area. The measure of Celsius-hours might be averaged over many days, but is specified as Celsius-hours per averaged day.<ref>{{Cite web |date=October 2016 |title=Executive Summary: Creating and Mapping an Urban Heat Island Index for California |url=https://calepa.ca.gov/wp-content/uploads/sites/6/2016/10/UrbanHeat-Report-ExSummary.pdf |url-status=live |archive-url=https://web.archive.org/web/20190731003514/https://calepa.ca.gov/wp-content/uploads/sites/6/2016/10/UrbanHeat-Report-ExSummary.pdf |archive-date=2019-07-31 |access-date=2024-07-24 |website=CalEPA {{!}} California Environmental Protection Agency}}</ref><ref name=":6">{{Cite web |title=Understanding the Urban Heat Island Index {{!}} CalEPA |url=https://calepa.ca.gov/climate/urban-heat-island-index-for-california/understanding-the-urban-heat-island-index/ |url-status=live |archive-url=https://web.archive.org/web/20171219054828/https://calepa.ca.gov/climate/urban-heat-island-index-for-california/understanding-the-urban-heat-island-index/ |archive-date=2017-12-19 |access-date=2024-07-24 |website=CalEPA {{!}} California Environmental Protection Agency}}</ref><ref name=":7">{{Cite web |date=October 2016 |title=Creating and Mapping an Urban Heat Island Index for California |url=https://calepa.ca.gov/wp-content/uploads/sites/6/2016/10/UrbanHeat-Report-Report.pdf |url-status=live |archive-url=https://web.archive.org/web/20190731003434/https://calepa.ca.gov/wp-content/uploads/sites/6/2016/10/UrbanHeat-Report-Report.pdf |archive-date=2019-07-31 |access-date=2024-07-24 |website=CalEPA {{!}} California Environmental Protection Agency}}</ref> |
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The index was created to estimate the expected use of air conditioning and resulting [[greenhouse gas emissions]] in California.<ref name=":6" /> The index does not consider values of or differences in wind-speed, humidity, or [[Solar irradiance|solar influx]], which might influence [[Apparent temperature|perceived temperature]] or the operation of air conditioners.<ref name=":7" /> |
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=== Models and simulations === |
=== Models and simulations === |
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If a city or town has a good system of taking weather observations the UHI can be measured directly.<ref>{{cite journal |last1=Steeneveld |first1=G.J. |year=2011 |title=Quantifying urban heat island effects and human comfort for cities of variable size and urban morphology in the Netherlands |journal=Journal of Geophysical Research |volume=116 |issue=D20 |pages=D20129 |bibcode=2011JGRD..11620129S |doi=10.1029/2011JD015988 |doi-access=free}}</ref> An alternative is to use a complex simulation of the location to calculate the UHI, or to use an approximate empirical method.<ref>{{cite journal |last1=Kershaw |first1=T. J. |last2=Sanderson |first2=M. |last3=Coley |first3=D. |last4=Eames |first4=M. |year=2010 |title=Estimation of the urban heat island for UK climate change projections |journal=Building Services Engineering Research and Technology |volume=31 |issue=3 |pages=251–263 |doi=10.1177/0143624410365033 |doi-access=free |
If a city or town has a good system of taking weather observations the UHI can be measured directly.<ref>{{cite journal |last1=Steeneveld |first1=G. J. |year=2011 |title=Quantifying urban heat island effects and human comfort for cities of variable size and urban morphology in the Netherlands |journal=Journal of Geophysical Research |volume=116 |issue=D20 |pages=D20129 |bibcode=2011JGRD..11620129S |doi=10.1029/2011JD015988 |doi-access=free}}</ref> An alternative is to use a complex simulation of the location to calculate the UHI, or to use an approximate empirical method.<ref>{{cite journal |last1=Kershaw |first1=T. J. |last2=Sanderson |first2=M. |last3=Coley |first3=D. |last4=Eames |first4=M. |year=2010 |title=Estimation of the urban heat island for UK climate change projections |journal=Building Services Engineering Research and Technology |volume=31 |issue=3 |pages=251–263 |doi=10.1177/0143624410365033 |doi-access=free |hdl-access=free |hdl=10871/13934}}</ref><ref>{{cite journal |last1=Theeuwes |first1=N. E. |last2=Steeneveld |first2=G. J. |last3=Ronda |first3=R. J. |last4=Holtslag |first4=A. A. M. |year=2017 |title=A diagnostic equation for the daily maximum urban heat island effect for cities in northwestern Europe |journal=International Journal of Climatology |volume=37 |issue=1 |pages=443–454 |bibcode=2017IJCli..37..443T |doi=10.1002/joc.4717 |s2cid=131437962}}</ref> Such models allow the UHI to be included in estimates of future temperatures rises within cities due to climate change. |
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Leonard O. Myrup published the first comprehensive numerical treatment to predict the effects of the urban heat island (UHI) in 1969.<ref name=":3">{{cite journal |last1=Myrup |first1=Leonard O. |year=1969 |title=A Numerical Model of the Urban Heat Island |journal=Journal of Applied Meteorology |volume=8 |issue=6 |pages=908–918 |bibcode=1969JApMe...8..908M |doi=10.1175/1520-0450(1969)008<0908:ANMOTU>2.0.CO;2 |doi-access=free}}</ref> The heat island effect was found to be the net result of several competing physical processes. In general, reduced evaporation in the city center and the thermal properties of the city building and paving materials are the dominant parameters.<ref name=":3" /> Modern simulation environments include [[ENVI-met]], which simulates all interactions between building and ground surfaces, plants and ambient air.<ref>{{Cite web |last=n.n. |title=ENVI-met-Alternativen für Mac — Altapps.net |url=https://de.altapps.net/soft/envi-met?platform=mac |access-date=2022-06-01 |website=de.altapps.net |language=de}}</ref> |
Leonard O. Myrup published the first comprehensive numerical treatment to predict the effects of the urban heat island (UHI) in 1969.<ref name=":3">{{cite journal |last1=Myrup |first1=Leonard O. |year=1969 |title=A Numerical Model of the Urban Heat Island |journal=Journal of Applied Meteorology |volume=8 |issue=6 |pages=908–918 |bibcode=1969JApMe...8..908M |doi=10.1175/1520-0450(1969)008<0908:ANMOTU>2.0.CO;2 |doi-access=free}}</ref> The heat island effect was found to be the net result of several competing physical processes. In general, reduced evaporation in the city center and the thermal properties of the city building and paving materials are the dominant parameters.<ref name=":3" /> Modern simulation environments include [[ENVI-met]], which simulates all interactions between building and ground surfaces, plants and ambient air.<ref>{{Cite web |last=n.n. |title=ENVI-met-Alternativen für Mac — Altapps.net |url=https://de.altapps.net/soft/envi-met?platform=mac |access-date=2022-06-01 |website=de.altapps.net |language=de}}</ref> |
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== Causes == |
== Causes == |
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[[File:High-rise buildings of Manhattan during sunset.jpg|thumb| |
[[File:High-rise buildings of Manhattan during sunset.jpg|thumb|High-rise buildings of [[Manhattan]], an example of dense urban living]] |
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[[File:newyork heat island.jpg|thumb|Thermal (top) and vegetation (bottom) locations around [[New York City]] via infrared satellite imagery. A comparison of the images shows that where vegetation is dense, temperatures are lower.]] |
[[File:newyork heat island.jpg|thumb|Thermal (top) and vegetation (bottom) locations around [[New York City]] via infrared satellite imagery. A comparison of the images shows that where vegetation is dense, temperatures are lower.]] |
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{{See also|Heatwave#Formation}} |
{{See also|Heatwave#Formation}} |
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⚫ | There are several causes of an urban heat island (UHI) |
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=== Urban design === |
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{{See also|Urban design}} |
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⚫ | There are several causes of an urban heat island (UHI) related to common [[urban design]] aspects. For example, dark surfaces absorb significantly more [[solar radiation]], which causes urban concentrations of roads and buildings to heat more than suburban and rural areas during the day;<ref name="dx.doi.org" /> materials commonly used in urban areas for pavement and roofs, such as [[concrete]] and [[Asphalt concrete|asphalt]], have significantly different thermal bulk properties (including [[specific heat capacity|heat capacity]] and [[thermal conductivity]]) and surface radiative properties ([[albedo]] and [[emissivity]]) than the surrounding rural areas. This causes a change in the [[Earth's energy budget|energy budget]] of the urban area, often leading to higher temperatures than surrounding rural areas.<ref name="Okeljnljn">{{cite journal |author=Oke |first=T. R. |year=1982 |title=The energetic basis of the urban heat island |journal=Quarterly Journal of the Royal Meteorological Society |volume=108 |issue=455 |pages=1–24 |bibcode=1982QJRMS.108....1O |doi=10.1002/qj.49710845502 |s2cid=120122894}}</ref> |
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[[Pavers (flooring)|Pavements]], [[parking lot]]s, roads or, more generally speaking [[transport infrastructure]], contribute significantly to the urban heat island effect.<ref name=":5">{{cite journal |last1=Hoehne |first1=Christopher G. |last2=Chester |first2=Mikhail V. |last3=Sailor |first3=David J. |last4=King |first4=David A. |title=Urban Heat Implications from Parking, Roads, and Cars: a Case Study of Metro Phoenix |journal=Sustainable and Resilient Infrastructure |date=4 July 2022 |volume=7 |issue=4 |pages=272–290 |doi=10.1080/23789689.2020.1773013 |bibcode=2022SusRI...7..272H |s2cid=225553384 }}</ref> For example, pavement infrastructure is a main contributor to urban heat during summer afternoons in [[Phoenix, Arizona|Phoenix]], United States.<ref name=":5" /> |
[[Pavers (flooring)|Pavements]], [[parking lot]]s, roads or, more generally speaking [[transport infrastructure]], contribute significantly to the urban heat island effect.<ref name=":5">{{cite journal |last1=Hoehne |first1=Christopher G. |last2=Chester |first2=Mikhail V. |last3=Sailor |first3=David J. |last4=King |first4=David A. |title=Urban Heat Implications from Parking, Roads, and Cars: a Case Study of Metro Phoenix |journal=Sustainable and Resilient Infrastructure |date=4 July 2022 |volume=7 |issue=4 |pages=272–290 |doi=10.1080/23789689.2020.1773013 |bibcode=2022SusRI...7..272H |s2cid=225553384 }}</ref> For example, pavement infrastructure is a main contributor to urban heat during summer afternoons in [[Phoenix, Arizona|Phoenix]], United States.<ref name=":5" /> |
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Other causes of a UHI are due to geometric effects. The tall buildings within many urban areas provide multiple surfaces for the reflection and absorption of sunlight, increasing the efficiency with which urban areas are heated. This is called the "[[Urban canyon|urban canyon effect]]". Another effect of buildings is the blocking of wind, which also inhibits cooling by [[convection]] and prevents pollutants from dissipating. Waste heat from automobiles, air conditioning, industry, and other sources also contributes to the UHI.<ref name="liyan2012" /><ref>{{Cite journal |last1=Sailor |first1=D. J. |year=2011 |title=A review of methods for estimating anthropogenic heat and moisture emissions in the urban environment |journal=International Journal of Climatology |volume=31 |issue=2 |pages=189–199 |bibcode=2011IJCli..31..189S |doi=10.1002/joc.2106 |s2cid=54835415}}</ref><ref>{{Cite journal |last1=Chen |first1=F. |last2=Kusaka |first2=H. |last3=Bornstein |first3=R. |last4=Ching |first4=J. |last5=Grimmond |first5=C. S. B. |last6=Grossman-Clarke |first6=S. |last7=Loridan |first7=T. |last8=Manning |first8=K. W. |last9=Martilli |first9=A. |last10=Miao |first10=S. |last11=Sailor |first11=D. |last12=Salamanca |first12=F. P. |last13=Taha |first13=H. |last14=Tewari |first14=M. |last15=Wang |first15=X. |year=2011 |title=The integrated WRF/urban modelling system: Development, evaluation, and applications to urban environmental problems |journal=International Journal of Climatology |volume=31 |issue=2 |pages=273 |bibcode=2011IJCli..31..273C |doi=10.1002/joc.2158 |s2cid=54686199 |last16=Wyszogrodzki |first16=A. A. |last17=Zhang |first17=C.}}</ref> |
Other causes of a UHI are due to geometric effects. The tall buildings within many urban areas provide multiple surfaces for the reflection and absorption of sunlight, increasing the efficiency with which urban areas are heated. This is called the "[[Urban canyon|urban canyon effect]]". Another effect of buildings is the blocking of wind, which also inhibits cooling by [[convection]] and prevents pollutants from dissipating. Waste heat from automobiles, air conditioning, industry, and other sources also contributes to the UHI.<ref name="liyan2012" /><ref>{{Cite journal |last1=Sailor |first1=D. J. |year=2011 |title=A review of methods for estimating anthropogenic heat and moisture emissions in the urban environment |journal=International Journal of Climatology |volume=31 |issue=2 |pages=189–199 |bibcode=2011IJCli..31..189S |doi=10.1002/joc.2106 |s2cid=54835415}}</ref><ref>{{Cite journal |last1=Chen |first1=F. |last2=Kusaka |first2=H. |last3=Bornstein |first3=R. |last4=Ching |first4=J. |last5=Grimmond |first5=C. S. B. |last6=Grossman-Clarke |first6=S. |last7=Loridan |first7=T. |last8=Manning |first8=K. W. |last9=Martilli |first9=A. |last10=Miao |first10=S. |last11=Sailor |first11=D. |last12=Salamanca |first12=F. P. |last13=Taha |first13=H. |last14=Tewari |first14=M. |last15=Wang |first15=X. |year=2011 |title=The integrated WRF/urban modelling system: Development, evaluation, and applications to urban environmental problems |journal=International Journal of Climatology |volume=31 |issue=2 |pages=273 |bibcode=2011IJCli..31..273C |doi=10.1002/joc.2158 |s2cid=54686199 |last16=Wyszogrodzki |first16=A. A. |last17=Zhang |first17=C.}}</ref> |
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Heat islands can be affected by proximity to different types of land cover, so that proximity to barren land causes urban land to become hotter and proximity to vegetation makes it cooler.<ref>{{Cite journal |last1=Mansourmoghaddam |first1=Mohammad |last2=Alavipanah |first2=Seyed Kazem |date=2022 |title=Study and prediction of land surface temperature changes of Yazd city: assessing the proximity and changes of land cover |url=https://girs.bushehr.iau.ir/article_682083.html?lang=en |journal=RS and GIS for Natural Resources |volume=12 |issue=4 |pages=1–27}}</ref> |
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⚫ | High levels of pollution in urban areas can also increase the UHI, as many forms of pollution change the radiative properties of the atmosphere.<ref name="Okeljnljn" /> UHI not only raises urban temperatures but also increases ozone concentrations because ozone is a [[greenhouse gas]] whose formation will accelerate with the increase of temperature.<ref>Union of Concerned Scientists. "Rising Temperatures, Worsening Ozone Pollution." Climate Change and Your Health (2011): n. pag. Print.</ref> |
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=== Air pollution === |
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⚫ | High levels of [[air pollution]] in urban areas can also increase the UHI, as many forms of pollution change the radiative properties of the atmosphere.<ref name="Okeljnljn" /> UHI not only raises urban temperatures but also increases ozone concentrations because ozone is a [[greenhouse gas]] whose formation will accelerate with the increase of temperature.<ref>Union of Concerned Scientists. "Rising Temperatures, Worsening Ozone Pollution." Climate Change and Your Health (2011): n. pag. Print.</ref> |
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=== Climate change as an amplifier === |
=== Climate change as an amplifier === |
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{{Further|Climate change and cities|Climate change adaptation#Heatwaves}} |
{{Further|Climate change and cities|Climate change adaptation#Heatwaves}} |
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Climate change is not a cause but an amplifier of the urban heat island effect. The [[IPCC Sixth Assessment Report]] from 2022 summarized the available research accordingly: "Climate change increases [[heat stress]] risks in cities [...] and amplifies the urban heat island across Asian cities at 1.5°C and 2°C warming levels, both substantially larger than under present climates [...]."<ref>{{cite book |doi=10.1017/9781009325844.002 |chapter=Technical Summary |title=Climate Change 2022 – Impacts, Adaptation and Vulnerability |date=2023 |pages=37–118 |isbn=978-1-009-32584-4 }}</ref>{{rp|66}} |
Climate change is not a cause but an amplifier of the urban heat island effect. The [[IPCC Sixth Assessment Report]] from 2022 summarized the available research accordingly: "Climate change increases [[heat stress]] risks in cities [...] and amplifies the urban heat island across Asian cities at 1.5 °C and 2 °C warming levels, both substantially larger than under present climates [...]."<ref>{{cite book |doi=10.1017/9781009325844.002 |chapter=Technical Summary |title=Climate Change 2022 – Impacts, Adaptation and Vulnerability |date=2023 |pages=37–118 |isbn=978-1-009-32584-4 }}</ref>{{rp|66}} |
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The report goes on to say: "In a warming world, increasing air temperature makes the urban heat island effect in cities worse. One key risk is [[Heat wave|heatwaves]] in cities that are likely to affect half of the future global urban population, with negative impacts on human health and economic productivity."<ref name=":1" />{{rp|993}} |
The report goes on to say: "In a warming world, increasing air temperature makes the urban heat island effect in cities worse. One key risk is [[Heat wave|heatwaves]] in cities that are likely to affect half of the future global urban population, with negative impacts on human health and economic productivity."<ref name=":1" />{{rp|993}} |
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=== On weather and climate === |
=== On weather and climate === |
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Aside from the effect on temperature, UHIs can produce secondary effects on local meteorology, including the altering of local wind patterns, the development of [[cloud]]s and [[fog]], the [[humidity]], and the rates of precipitation.<ref>{{cite web|title=Urban Climate – Climate Study and UHI |url=http://asusmart.com/urbanclimate.php |archive-url=https://archive.today/20071123091726/http://asusmart.com/urbanclimate.php |url-status=dead |archive-date=2007-11-23 |publisher=[[Arizona State University]] |year=2006 |author=Arizona Board of Regents |access-date=2007-08-02 }}</ref> |
Aside from the effect on temperature, UHIs can produce secondary effects on local meteorology, including the altering of local wind patterns, the development of [[cloud]]s and [[fog]], the [[humidity]], and the rates of precipitation.<ref>{{cite web|title=Urban Climate – Climate Study and UHI |url=http://asusmart.com/urbanclimate.php |archive-url=https://archive.today/20071123091726/http://asusmart.com/urbanclimate.php |url-status=dead |archive-date=2007-11-23 |publisher=[[Arizona State University]] |year=2006 |author=Arizona Board of Regents |access-date=2007-08-02 }}</ref> The extra heat provided by the UHI leads to greater upward motion, which can induce additional shower and thunderstorm activity. In addition, the UHI creates during the day a local low pressure area where relatively moist air from its rural surroundings converges, possibly leading to more favorable conditions for cloud formation.<ref name="Hee">{{cite journal |author1=van Heerwaarden |first=Chiel C. |author2=Vilà-Guerau de Arellano |first2=J. |name-list-style=amp |year=2008 |title=Relative humidity as an indicator for cloud formation over heterogeneous land surfaces |url=http://library.wur.nl/WebQuery/wurpubs/373271 |journal=Journal of the Atmospheric Sciences |volume=65 |issue=10 |pages=3263–3277 |bibcode=2008JAtS...65.3263V |doi=10.1175/2008JAS2591.1 |s2cid=56010396 |doi-access=free}}</ref> Rainfall rates downwind of cities are increased between 48% and 116%. Partly as a result of this warming, monthly rainfall is about 28% greater between {{convert|20|and|40|mi|km}} downwind of cities, compared with upwind.<ref>{{cite news| title=Spain goes hi-tech to beat drought | first=Dale | last=Fuchs | newspaper=[[The Guardian]] | date=2005-06-28 | url=https://www.theguardian.com/weather/Story/0,2763,1516375,00.html | access-date=2007-08-02}}</ref> Some cities show a total precipitation increase of 51%.<ref>{{cite web|url=http://www.gsfc.nasa.gov/topstory/20020613urbanrain.html|title=NASA Satellite Confirms Urban Heat Islands Increase Rainfall Around Cities|author=Goddard Space Flight Center|publisher=[[National Aeronautics and Space Administration]]|date=2002-06-18|access-date=2009-07-17 |archive-url = https://web.archive.org/web/20080612173654/http://www.gsfc.nasa.gov/topstory/20020613urbanrain.html |archive-date = June 12, 2008|url-status=dead|author-link= Goddard Space Flight Center}}</ref> |
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One study concluded that cities change the climate in area |
One study concluded that cities change the climate in area two–four times larger than their own area.<ref>{{cite journal |last1=Zhou |first1=Decheng |last2=Zhao |first2=Shuqing |last3=Zhang |first3=Liangxia |last4=Sun |first4=Ge |last5=Liu |first5=Yongqiang |title=The footprint of urban heat island effect in China |journal= Scientific Reports|volume=5 |pages=11160 |date=10 June 2015 |bibcode=2015NatSR...511160Z |doi=10.1038/srep11160 |pmid=26060039 |pmc=4461918 }}</ref> One 1999 comparison between urban and rural areas proposed that urban heat island effects have little influence on [[Instrumental temperature record|global mean temperature trends]].<ref>{{cite journal |last1=Peterson |first1=T. C. |last2=Gallo |first2=K. P. |last3=Lawrimore |first3=J. |last4=Owen |first4=T. W. |last5=Huang |first5=A. |last6=McKittrick |first6=D. A. |year=1999 |title=Global rural temperature trends |url=https://digitalcommons.unl.edu/natrespapers/187 |journal=Geophysical Research Letters |volume=26 |issue=3 |pages=329–332 |bibcode=1999GeoRL..26..329P |doi=10.1029/1998GL900322 |doi-access=free}}</ref> Others suggested that urban heat islands affect global climate by impacting the jet stream.<ref>{{cite journal |last1=J. Zhang |first1=Guang |last2=Cai |first2=Ming |last3=Hu |first3=Aixue |title=Energy consumption and the unexplained winter warming over northern Asia and North America |journal=Nature Climate Change |volume=3 |issue=5 |pages=466–470 |date=27 January 2013 |doi=10.1038/nclimate1803 |bibcode=2013NatCC...3..466Z }}</ref> |
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=== On human health === |
=== On human health === |
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{{See also|Heat illness|Effects of climate change on human health#Higher global temperatures and heat waves (direct risk)}} |
{{See also|Heat illness|Effects of climate change on human health#Higher global temperatures and heat waves (direct risk)}} |
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[[File:Atlanta thermal.jpg|thumb|upright=1.3|Image of [[Atlanta|Atlanta, Georgia]], showing temperature distribution, with blue showing cool temperatures, red warm, and hot areas appear white]] |
[[File:Atlanta thermal.jpg|thumb|upright=1.3|Image of [[Atlanta|Atlanta, Georgia]], showing temperature distribution, with blue showing cool temperatures, red warm, and hot areas appear white]] |
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UHIs have the potential to directly influence the health and welfare of urban residents. As UHIs are characterized by increased temperature, they can potentially increase the magnitude and duration of heat waves within cities. The number of individuals exposed to extreme temperatures is increased by the UHI-induced warming.<ref>{{cite journal |last1=Broadbent |first1=Ashley Mark |last2=Krayenhoff |first2=Eric Scott |last3=Georgescu |first3=Matei |title=The motley drivers of heat and cold exposure in 21st century US cities |journal=Proceedings of the National Academy of Sciences |date=13 August 2020 |volume=117 |issue=35 |pages=21108–21117 |doi=10.1073/pnas.2005492117 |pmid=32817528 |pmc=7474622 |bibcode=2020PNAS..11721108B |doi-access=free }}</ref> The nighttime effect of UHIs can be particularly harmful during a heat wave, as it deprives urban residents of the cool relief found in rural areas during the night.<ref name="Clarke">{{cite journal | |
UHIs have the potential to directly influence the health and welfare of urban residents. As UHIs are characterized by increased temperature, they can potentially increase the magnitude and duration of heat waves within cities. The number of individuals exposed to extreme temperatures is increased by the UHI-induced warming.<ref>{{cite journal |last1=Broadbent |first1=Ashley Mark |last2=Krayenhoff |first2=Eric Scott |last3=Georgescu |first3=Matei |title=The motley drivers of heat and cold exposure in 21st century US cities |journal=Proceedings of the National Academy of Sciences |date=13 August 2020 |volume=117 |issue=35 |pages=21108–21117 |doi=10.1073/pnas.2005492117 |pmid=32817528 |pmc=7474622 |bibcode=2020PNAS..11721108B |doi-access=free }}</ref> The nighttime effect of UHIs can be particularly harmful during a heat wave, as it deprives urban residents of the cool relief found in rural areas during the night.<ref name="Clarke">{{cite journal |author=Clarke |first=J. F. |year=1972 |title=Some effects of the urban structure on heat mortality |journal=Environmental Research |volume=5 |issue=1 |pages=93–104 |bibcode=1972ER......5...93C |doi=10.1016/0013-9351(72)90023-0 |pmid=5032928}}</ref> |
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Increased temperatures have been reported to cause [[heat illness]]es, such as [[heat stroke]], [[heat exhaustion]], [[heat syncope]], and [[heat cramps]].<ref name="Review1">{{cite journal |last=Kovats |first=R. Sari |author2=Hajat, Shakoor |date=April 2008 |title=Heat Stress and Public Health: A Critical Review |journal=Annual Review of Public Health |volume=29 |issue=1 |pages=41–55 |doi=10.1146/annurev.publhealth.29.020907.090843 |pmid=18031221 |doi-access=free}}</ref> |
Increased temperatures have been reported to cause [[heat illness]]es, such as [[heat stroke]], [[heat exhaustion]], [[heat syncope]], and [[heat cramps]].<ref name="Review1">{{cite journal |last=Kovats |first=R. Sari |author2=Hajat, Shakoor |date=April 2008 |title=Heat Stress and Public Health: A Critical Review |journal=Annual Review of Public Health |volume=29 |issue=1 |pages=41–55 |doi=10.1146/annurev.publhealth.29.020907.090843 |pmid=18031221 |doi-access=free}}</ref><ref name=":9">Gunawardena, K. R. (2015). ''Heat vulnerability: risk to health and wellbeing in the built environment [M.Phil Paper]'', University of Cambridge, Cambridge.</ref> |
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Extreme heat is the deadliest form of weather in the U.S. Per a study by Professor Terri Adams-Fuller, heat |
Extreme heat is the deadliest form of weather in the U.S. Per a study by Professor Terri Adams-Fuller, heat waves kill more people in the U.S. than hurricanes, floods, and tornadoes combined.<ref>{{Cite web |last=Adams-Fuller |first=Terri |date=2023-07-01 |title=Extreme Heat Is Deadlier Than Hurricanes, Floods and Tornadoes Combined |url=https://www.scientificamerican.com/article/extreme-heat-is-deadlier-than-hurricanes-floods-and-tornadoes-combined/ |access-date=2024-05-02 |website=Scientific American |language=en}}</ref> These heat illnesses are more common within medium-to-large metro areas than the rest of the U.S., largely in part due to UHIs. Heat illnesses can also be compounded when combined with air pollution which is common in many urban areas.<ref name=":9" /> |
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Heat exposure can have adverse effects on mental health. Increases in temperature can contribute to increased aggression, as well as more cases of domestic violence and substance abuse.<ref>{{Cite web |date=2019-07-30 |title=The Impacts of Extreme Heat on Mental Health |url=https://www.psychiatrictimes.com/view/impacts-extreme-heat-mental-health |access-date=2024-05-02 |website=Psychiatric Times |language=en}}</ref> Greater heat can also negatively impact school performance and education. According to a study by Hyunkuk Cho of Yeungnam University, an increased number of days with extreme heat each year correlates to a decrease in student test scores.<ref>{{cite journal |last1=Cho |first1=Hyunkuk |title=The effects of summer heat on academic achievement: A cohort analysis |journal=Journal of Environmental Economics and Management |date=May 2017 |volume=83 |pages=185–196 |doi=10.1016/j.jeem.2017.03.005 |bibcode=2017JEEM...83..185C }}</ref> |
Heat exposure can have adverse effects on mental health. Increases in temperature can contribute to increased aggression, as well as more cases of domestic violence and substance abuse.<ref>{{Cite web |date=2019-07-30 |title=The Impacts of Extreme Heat on Mental Health |url=https://www.psychiatrictimes.com/view/impacts-extreme-heat-mental-health |access-date=2024-05-02 |website=Psychiatric Times |language=en}}</ref> Greater heat can also negatively impact school performance and education. According to a study by Hyunkuk Cho of Yeungnam University, an increased number of days with extreme heat each year correlates to a decrease in student test scores.<ref>{{cite journal |last1=Cho |first1=Hyunkuk |title=The effects of summer heat on academic achievement: A cohort analysis |journal=Journal of Environmental Economics and Management |date=May 2017 |volume=83 |pages=185–196 |doi=10.1016/j.jeem.2017.03.005 |bibcode=2017JEEM...83..185C }}</ref> |
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High UHI intensity correlates with increased concentrations of air pollutants that gathered at night, which can affect the next day's [[Air pollution|air quality]].<ref name="DOE">{{cite web |title=Assessment of International Urban Heat Island Research |url=http://www.eereblogs.energy.gov/buildingenvelope/file.axd?file=2011%2F10%2Fuhi_report.pdf |url-status=dead |archive-url=https://web.archive.org/web/20130217201143/http://www.eereblogs.energy.gov/buildingenvelope/file.axd?file=2011%2f10%2fuhi_report.pdf |archive-date=17 February 2013 |access-date=30 April 2014 |work=U.S. Department of Energy Report |publisher=Navigant Consulting}}</ref> These pollutants include [[volatile organic compounds]], [[carbon monoxide]], [[nitrogen oxides]], and [[Particulates|particulate matter]].<ref name="WHO">{{cite journal |last=Koppe |first=Christina |author2= |
High UHI intensity correlates with increased concentrations of air pollutants that gathered at night, which can affect the next day's [[Air pollution|air quality]].<ref name="DOE">{{cite web |title=Assessment of International Urban Heat Island Research |url=http://www.eereblogs.energy.gov/buildingenvelope/file.axd?file=2011%2F10%2Fuhi_report.pdf |url-status=dead |archive-url=https://web.archive.org/web/20130217201143/http://www.eereblogs.energy.gov/buildingenvelope/file.axd?file=2011%2f10%2fuhi_report.pdf |archive-date=17 February 2013 |access-date=30 April 2014 |work=U.S. Department of Energy Report |publisher=Navigant Consulting}}</ref> These pollutants include [[volatile organic compounds]], [[carbon monoxide]], [[nitrogen oxides]], and [[Particulates|particulate matter]].<ref name="WHO">{{cite journal |last=Koppe |first=Christina |author2=Kovats |first2=Sari |author3=Jendritzky |first3=Gerd |author4=Menne |first4=Bettina |year=2004 |title=Heat-waves: risks and responses |url=http://www.euro.who.int/en/publications/abstracts/heat-waves-risks-and-responses |url-status=dead |journal=Health and Global Environmental Change Series |volume=2 |archive-url=https://web.archive.org/web/20230322220743/https://www.euro.who.int/en/publications/abstracts/heat-waves-risks-and-responses |archive-date=2023-03-22 |access-date=2014-05-07}}</ref><ref name=":10">Gunawardena, K. (2018). ''Fundamentals of Urban Heat Islands: Concise guide for architects and urban planners'', University of Cambridge, Cambridge.</ref> The production of these pollutants combined with the higher temperatures in UHIs can quicken the production of [[ozone]].<ref name=DOE/> Ozone at surface level is considered to be a harmful pollutant.<ref name=DOE/> Studies suggest that increased temperatures in UHIs can increase polluted days but also note that other factors (e.g. [[Atmospheric pressure|air pressure]], [[cloud cover]], [[wind speed]]) can also have an effect on pollution.<ref name=DOE/> |
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Studies from [[Hong Kong]] have found that areas of the city with poorer outdoor urban air ventilation tended to have stronger urban heat island effects<ref>{{cite journal |last1=Shi |first1=Yuan |last2=Katzschner |first2=Lutz |last3=Ng |first3=Edward |title=Modelling the fine-scale spatiotemporal pattern of urban heat island effect using land use regression approach in a megacity |journal=Science of the Total Environment |date=March 2018 |volume=618 |pages=891–904 |doi=10.1016/j.scitotenv.2017.08.252 |pmid=29096959 |bibcode=2018ScTEn.618..891S }}</ref> and had significantly higher all-cause mortality<ref>{{cite journal |last1=Wang |first1=Pin |last2=Goggins |first2=William B. |last3=Shi |first3=Yuan |last4=Zhang |first4=Xuyi |last5=Ren |first5=Chao |last6=Ka-Lun Lau |first6=Kevin |title=Long-term association between urban air ventilation and mortality in Hong Kong |journal=Environmental Research |date=June 2021 |volume=197 |pages=111000 |doi=10.1016/j.envres.2021.111000 |pmid=33745928 |s2cid=232310626 }}</ref> compared to areas with better ventilation. Another study employing advanced statistical methods in Babol city, Iran, revealed a significant increase in Surface Urban Heat Island Intensity (SUHII) from 1985 to 2017, influenced by both geographic direction and time. This research, enhancing the understanding of SUHII's spatial and temporal variations, emphasizes the need for precise urban planning to mitigate the health impacts of urban heat islands.<ref>{{cite journal |last1=Weng |first1=Qihao |last2=Firozjaei |first2=Mohammad Karimi |last3=Sedighi |first3=Amir |last4=Kiavarz |first4=Majid |last5=Alavipanah |first5=Seyed Kazem |title=Statistical analysis of surface urban heat island intensity variations: A case study of Babol city, Iran |journal=GIScience & Remote Sensing |date=19 May 2019 |volume=56 |issue=4 |pages=576–604 |doi=10.1080/15481603.2018.1548080 |bibcode=2019GISRS..56..576W |s2cid=134003294 }}</ref> Surface UHI's are more prominent during the day and are measured using the land surface temperature and remote sensing.<ref>{{Cite journal |last=Yuan |first=F |date=2007 |title=Comparison of impervious surface area and normalized difference vegetation index as indicators of surface urban heat island effects in Landsat imagery |journal=Remote Sensing of Environment |volume=106 |issue=3 |pages=375–386|doi=10.1016/j.rse.2006.09.003 |
Studies from [[Hong Kong]] have found that areas of the city with poorer outdoor urban air ventilation tended to have stronger urban heat island effects<ref>{{cite journal |last1=Shi |first1=Yuan |last2=Katzschner |first2=Lutz |last3=Ng |first3=Edward |title=Modelling the fine-scale spatiotemporal pattern of urban heat island effect using land use regression approach in a megacity |journal=Science of the Total Environment |date=March 2018 |volume=618 |pages=891–904 |doi=10.1016/j.scitotenv.2017.08.252 |pmid=29096959 |bibcode=2018ScTEn.618..891S }}</ref> and had significantly higher all-cause mortality<ref>{{cite journal |last1=Wang |first1=Pin |last2=Goggins |first2=William B. |last3=Shi |first3=Yuan |last4=Zhang |first4=Xuyi |last5=Ren |first5=Chao |last6=Ka-Lun Lau |first6=Kevin |title=Long-term association between urban air ventilation and mortality in Hong Kong |journal=Environmental Research |date=June 2021 |volume=197 |pages=111000 |doi=10.1016/j.envres.2021.111000 |pmid=33745928 |bibcode=2021ER....19711000W |s2cid=232310626 }}</ref> compared to areas with better ventilation. Another study employing advanced statistical methods in Babol city, Iran, revealed a significant increase in Surface Urban Heat Island Intensity (SUHII) from 1985 to 2017, influenced by both geographic direction and time. This research, enhancing the understanding of SUHII's spatial and temporal variations, emphasizes the need for precise urban planning to mitigate the health impacts of urban heat islands.<ref>{{cite journal |last1=Weng |first1=Qihao |last2=Firozjaei |first2=Mohammad Karimi |last3=Sedighi |first3=Amir |last4=Kiavarz |first4=Majid |last5=Alavipanah |first5=Seyed Kazem |title=Statistical analysis of surface urban heat island intensity variations: A case study of Babol city, Iran |journal=GIScience & Remote Sensing |date=19 May 2019 |volume=56 |issue=4 |pages=576–604 |doi=10.1080/15481603.2018.1548080 |bibcode=2019GISRS..56..576W |s2cid=134003294 }}</ref> Surface UHI's are more prominent during the day and are measured using the land surface temperature and remote sensing.<ref>{{Cite journal |last=Yuan |first=F. |date=2007 |title=Comparison of impervious surface area and normalized difference vegetation index as indicators of surface urban heat island effects in Landsat imagery |journal=Remote Sensing of Environment |volume=106 |issue=3 |pages=375–386 |bibcode=2007RSEnv.106..375Y |doi=10.1016/j.rse.2006.09.003}}</ref> |
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=== On water bodies and aquatic organisms === |
=== On water bodies and aquatic organisms === |
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UHIs also impair [[water quality]]. Hot pavement and rooftop surfaces transfer their excess heat to stormwater, which then drains into storm sewers and raises water temperatures as it is released into streams, rivers, ponds, and lakes. Additionally, increased urban water body temperatures lead to a [[Biodiversity loss|decrease in biodiversity]] in the water.<ref>NYS DEC. "Streams Tributary to Onondaga Lake Biological Assessment." Dec.ny.gov. N.p., 2008. Web. 12 September 2013.</ref> For example, in August 2001, rains over [[Cedar Rapids, Iowa]] led to a {{convert|10.5|C-change}} rise in the nearby stream within one hour, resulting in a [[fish kill]] which affected an estimated 188 fish.<ref>{{cite web |title=Fish Kill Event |
UHIs also impair [[water quality]]. Hot pavement and rooftop surfaces transfer their excess heat to stormwater, which then drains into storm sewers and raises water temperatures as it is released into streams, rivers, ponds, and lakes. Additionally, increased urban water body temperatures lead to a [[Biodiversity loss|decrease in biodiversity]] in the water.<ref>NYS DEC. "Streams Tributary to Onondaga Lake Biological Assessment." Dec.ny.gov. N.p., 2008. Web. 12 September 2013.</ref> For example, in August 2001, rains over [[Cedar Rapids, Iowa]] led to a {{convert|10.5|C-change}} rise in the nearby stream within one hour, resulting in a [[fish kill]] which affected an estimated 188 fish.<ref>{{cite web |title=Fish Kill Event – McLoud Run |url=https://programs.iowadnr.gov/fishkill/events/478 |website=Iowa DNR Fish Kill Database}}</ref> Since the temperature of the rain was comparatively cool, the deaths could be attributed to the hot pavement of the city. Similar events have been documented across the American Midwest, as well as Oregon and California.<ref>{{cite book |author1=Tipler |first=Paul A. |url=https://books.google.com/books?id=BMVR37-8Jh0C&pg=PA686 |title=Physics for Scientists and Engineers |author2=Mosca |first2=Gene |publisher=[[Macmillan Publishers (United States)|Macmillan]] |year=2007 |isbn=978-1-4292-0124-7 |page=686 |name-list-style=amp}}</ref> Rapid temperature changes can be stressful to aquatic ecosystems.<ref>{{cite web | title=Urban Climate – Climate Study and UHI | url=http://www.epa.gov/hiri/about/index.htm | publisher=[[United States Environmental Protection Agency]] | date=2009-02-09 | access-date=2009-06-18 }}</ref> |
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With the temperature of the nearby buildings sometimes reaching a difference of over {{convert|50|F-change}} from the near-surface air temperature, precipitation warms rapidly, and run-off into nearby streams, lakes and rivers (or other bodies of water) to provide excessive [[thermal pollution]]. The increase in thermal pollution has the potential to increase water temperature by {{convert|20|to|30|F-change}}. This increase causes the fish species inhabiting the body of water to undergo thermal stress and shock due to the rapid change in temperature of their habitat.<ref>{{cite web |title=Islands in the Sun |url=http://islands.environment.umn.edu/research/themes/ |url-status=dead |archive-url=https://web.archive.org/web/20160303221028/http://islands.environment.umn.edu/research/themes/ |archive-date=2016-03-03 |access-date=2014-11-11 |website=Institute on the Environment |publisher=University of Minnesota}}</ref> |
With the temperature of the nearby buildings sometimes reaching a difference of over {{convert|50|F-change}} from the near-surface air temperature, precipitation warms rapidly, and run-off into nearby streams, lakes and rivers (or other bodies of water) to provide excessive [[thermal pollution]]. The increase in thermal pollution has the potential to increase water temperature by {{convert|20|to|30|F-change}}. This increase causes the fish species inhabiting the body of water to undergo thermal stress and shock due to the rapid change in temperature of their habitat.<ref>{{cite web |title=Islands in the Sun |url=http://islands.environment.umn.edu/research/themes/ |url-status=dead |archive-url=https://web.archive.org/web/20160303221028/http://islands.environment.umn.edu/research/themes/ |archive-date=2016-03-03 |access-date=2014-11-11 |website=Institute on the Environment |publisher=University of Minnesota}}</ref> |
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=== On energy usage for cooling === |
=== On energy usage for cooling === |
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[[File:NASA SLC Urban Heat Island Effect Roof.jpg|upright=1. |
[[File:NASA SLC Urban Heat Island Effect Roof.jpg|upright=1.55|thumb|Images of [[Salt Lake City]] show positive correlation between white reflective roofs and cooler temperatures. Image A depicts an aerial view of Salt Lake City, Utah, site of 865000 sqft white reflective roof. Image B is a thermal infrared image of same area, showing hot (red and yellow) and cool (green and blue) spots. The reflective vinyl roof, not absorbing solar radiation, is shown in blue surrounded by other hot spots.]] |
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Another consequence of urban heat islands is the increased energy required for [[air conditioning]] and [[refrigeration]] in cities that are in comparatively hot climates. The heat island effect costs [[Los Angeles]] about [[US$]] 100 million per year in energy (in the year 2000).<ref>{{cite web |author=Sheng-chieh |
Another consequence of urban heat islands is the increased energy required for [[air conditioning]] and [[refrigeration]] in cities that are in comparatively hot climates. The heat island effect costs [[Los Angeles]] about [[US$]] 100 million per year in energy (in the year 2000).<ref>{{cite web |author=Chang |first=Sheng-chieh |date=2000-06-23 |title=Energy Use |url=http://eetd.lbl.gov/HeatIsland/EnergyUse/ |url-status=dead |archive-url=https://web.archive.org/web/20090311050754/http://eetd.lbl.gov/heatisland/EnergyUse/ |archive-date=March 11, 2009 |access-date=2009-06-18 |publisher=Environmental Energies Technology Division}}</ref> Through the implementation of heat island reduction strategies, significant annual net energy savings have been calculated for northern locations such as Chicago, Salt Lake City, and Toronto.<ref>{{cite web |date=2005-08-23 |title=Aging and Weathering of Cool Roofing Membranes |url=http://vinylroofs.org/wp-content/uploads/2011/06/aging_weathering.pdf |url-status=dead |archive-url=https://web.archive.org/web/20111115021825/http://vinylroofs.org/wp-content/uploads/2011/06/aging_weathering.pdf |archive-date=2011-11-15 |access-date=2010-08-16 |publisher=Cool Roofing Symposium}}</ref> |
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Every year in the U.S. 15% of energy goes towards the [[air conditioning]] of buildings in these urban heat islands. It was reported in 1998 that "the air conditioning demand has risen 10% within the last 40 years."<ref name="Rosenfeld98">{{cite journal |last1=Rosenfeld |first1=Arthur H. |last2=Akbari |first2=Hashem |last3=Romm |first3=Joseph J. |last4=Pomerantz |first4=Melvin |date=1998 |title=Cool communities: strategies for heat island mitigation and smog reduction |url=https://coolcolors.lbl.gov/assets/docs/Papers/EnergyandBuilding-98%20(RosenfeldAkbari-CoolCommunities).pdf |journal=Energy and Buildings |volume=28 |issue=1 |pages=51–62 |doi=10.1016/S0378-7788(97)00063-7|bibcode=1998EneBu..28...51R }}</ref> |
Every year in the U.S. 15% of energy goes towards the [[air conditioning]] of buildings in these urban heat islands. It was reported in 1998 that "the air conditioning demand has risen 10% within the last 40 years."<ref name="Rosenfeld98">{{cite journal |last1=Rosenfeld |first1=Arthur H. |last2=Akbari |first2=Hashem |last3=Romm |first3=Joseph J. |last4=Pomerantz |first4=Melvin |date=1998 |title=Cool communities: strategies for heat island mitigation and smog reduction |url=https://coolcolors.lbl.gov/assets/docs/Papers/EnergyandBuilding-98%20(RosenfeldAkbari-CoolCommunities).pdf |journal=Energy and Buildings |volume=28 |issue=1 |pages=51–62 |doi=10.1016/S0378-7788(97)00063-7|bibcode=1998EneBu..28...51R }}</ref> |
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Increases in air conditioning use also serve to worsen the effects of UHIs at night. While cooler nights are often a reprieve from heat waves during the day, the residual heat created by the use of air conditioning systems can lead to higher nighttime temperatures. According to a study by Professor Francisco Salamanca Palou and colleagues, this residual heat can cause nighttime increases of up to 1° |
Increases in air conditioning use also serve to worsen the effects of UHIs at night. While cooler nights are often a reprieve from heat waves during the day, the residual heat created by the use of air conditioning systems can lead to higher nighttime temperatures. According to a study by Professor Francisco Salamanca Palou and colleagues, this residual heat can cause nighttime increases of up to 1 °C in urban areas.<ref>{{cite journal |last1=Salamanca |first1=F. |last2=Georgescu |first2=M. |last3=Mahalov |first3=A. |last4=Moustaoui |first4=M. |last5=Wang |first5=M. |title=Anthropogenic heating of the urban environment due to air conditioning |journal=Journal of Geophysical Research: Atmospheres |date=27 May 2014 |volume=119 |issue=10 |pages=5949–5965 |doi=10.1002/2013JD021225 |bibcode=2014JGRD..119.5949S }}</ref> Increased energy use from air conditioners also contributes to carbon emissions, which doubly exacerbates the effects of UHIs. |
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== Options for reducing heat island effects == |
== Options for reducing heat island effects == |
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[[File:Ogród botaniczny UMCS.png|thumb|left|Botanical Garden in [[Lublin]], Poland]] |
[[File:Ogród botaniczny UMCS.png|thumb|left|Botanical Garden in [[Lublin]], Poland]] |
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Strategies to improve [[urban resilience]] by reducing excessive heat in cities include: Planting trees in cities, [[Reflective surfaces (climate engineering)|cool roofs (painted white or with reflective coating)]] and light-coloured concrete, [[green infrastructure]] (including [[green roof]]s), [[passive daytime radiative cooling]].<ref>{{Cite web | |
Strategies to improve [[urban resilience]] by reducing excessive heat in cities include: Planting trees in cities, [[Reflective surfaces (climate engineering)|cool roofs (painted white or with reflective coating)]] and light-coloured concrete, [[green infrastructure]] (including [[green roof]]s), [[passive daytime radiative cooling]].<ref name="auto">{{Cite web | title=Making roofs white or reflective is the best way to keep a city cool |url=https://www.newscientist.com/article/2438111-making-roofs-white-or-reflective-is-the-best-way-to-keep-a-city-cool/ |access-date=2024-07-11 |website=New Scientist |language=en-US}}</ref><ref name=":10" /> |
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The temperature difference between urban areas and the surrounding suburban or rural areas can be as much as {{convert|5|C-change|abbr=on}}. Nearly 40 percent of that increase is due to the prevalence of dark roofs, with the remainder coming from dark- |
The temperature difference between urban areas and the surrounding suburban or rural areas can be as much as {{convert|5|C-change|abbr=on}}. Nearly 40 percent of that increase is due to the prevalence of dark roofs, with the remainder coming from dark-coloured pavement and the declining presence of vegetation. The heat island effect can be counteracted slightly by using white or reflective materials to build houses, roofs, pavements, and roads, thus increasing the overall albedo of the city.<ref>{{cite journal |last1=Albers |first1=R. A. W. |last2=Bosch |first2=P. R. |last3=Blocken |first3=B. |last4=van den Dobbelsteen |first4=A. A. J. F. |last5=van Hove |first5=L. W. A. |last6=Spit |first6=T. J. M. |last7=van de Ven |first7=F. |last8=van Hooff |first8=T. |last9=Rovers |first9=V. |date=January 2015 |title=Overview of challenges and achievements in the climate adaptation of cities and in the Climate Proof Cities program |url=https://pure.tue.nl/ws/files/3986648/901695708161161.pdf |journal=Building and Environment |volume=83 |pages=1–10 |bibcode=2015BuEnv..83....1A |doi=10.1016/j.buildenv.2014.09.006 |hdl=1874/309149}}</ref> |
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Concentric expansion of cities is |
Concentric expansion of cities is unfavourable in terms of the urban heat island phenomenon. It is recommended to plan the development of cities in strips, consistent with the hydrographic network, taking into account green areas with various plant species.<ref>Michał Kaszewski: „Miejska wyspa ciepła – sposoby jej ograniczania": [https://up.lublin.pl/blog/12845/ Wykład popularno-naukowy: „Miejska wyspa ciepła – sposoby jej ograniczania"]{{rs|date=May 2024}}</ref> In this way, it was planned to build urban settlements stretching over large areas, e.g. [[Kielce]], [[Szczecin]] and [[Gdynia]] in Poland, [[Copenhagen]] in Denmark and [[Hamburg]], [[Berlin]] and [[Kiel]] in Germany. |
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=== Planting trees in cities === |
=== Planting trees in cities === |
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{{Main|Urban forest|Urban forestry}} |
{{Main|Urban forest|Urban forestry}} |
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Planting trees around the city can be another way of increasing albedo and decreasing the urban heat island effect. It is recommended to plant [[deciduous]] trees because they can provide many benefits such as more shade in the summer and not blocking warmth in winter.<ref name="Rosenfield97">{{cite journal |last1=Rosenfeld |first1=Arthur H. |last2=Romm |first2=Joseph J. |last3=Akbari |first3=Hashem |last4=Lloyd |first4=Alan C. |title=Painting the town white—and green |journal=Technology Review |date=February 1997 |volume=100 |issue=2 |pages=52–59 }}{{cbignore|bot=medic}}</ref> Trees are a necessary feature in combating most of the urban heat island effect because they reduce air temperatures by {{convert|10|F-change|C-change}},<ref>{{cite web |title=Top 22 Benefits of Trees |url=http://www.treepeople.org/top-22-benefits-trees |access-date=7 July 2014 |website=Tree People}}</ref> and surface temperatures by up to {{convert|20|-|45|F-change|C-change}}.<ref>{{cite web |date=2014-02-28 |title=Trees and Vegetation |url=http://www.epa.gov/heatisland/mitigation/trees.htm |access-date=7 July 2014 |website=EPA.gov}}</ref> Another benefit of having trees in a city is that trees also help fight global warming by absorbing CO2 from the atmosphere. |
Planting trees around the city can be another way of increasing albedo and decreasing the urban heat island effect. <ref>{{Cite journal |last1=Gunawardena |first1=K. R. |last2=Wells |first2=M. J. |last3=Kershaw |first3=T. |date=2017-04-15 |title=Utilising green and bluespace to mitigate urban heat island intensity |url=https://linkinghub.elsevier.com/retrieve/pii/S0048969717301754 |journal=Science of the Total Environment |volume=584-585 |pages=1040–1055 |doi=10.1016/j.scitotenv.2017.01.158 |issn=0048-9697}}</ref><ref>Gunawardena, K. R., & Kershaw, T. (2016). Green and blue-space significance to urban heat island mitigation. In S. Emmit & K. Adeyeye, eds., ''Integrated Design International Conference (ID@50)'', Bath: University of Bath, pp. 1–15.</ref> It is recommended to plant [[deciduous]] trees because they can provide many benefits such as more shade in the summer and not blocking warmth in winter.<ref name="Rosenfield97">{{cite journal |last1=Rosenfeld |first1=Arthur H. |last2=Romm |first2=Joseph J. |last3=Akbari |first3=Hashem |last4=Lloyd |first4=Alan C. |title=Painting the town white—and green |journal=Technology Review |date=February 1997 |volume=100 |issue=2 |pages=52–59 }}{{cbignore|bot=medic}}</ref> Trees are a necessary feature in combating most of the urban heat island effect because they reduce air temperatures by {{convert|10|F-change|C-change}},<ref>{{cite web |title=Top 22 Benefits of Trees |url=http://www.treepeople.org/top-22-benefits-trees |access-date=7 July 2014 |website=Tree People}}</ref> and surface temperatures by up to {{convert|20|-|45|F-change|C-change}}.<ref>{{cite web |date=2014-02-28 |title=Trees and Vegetation |url=http://www.epa.gov/heatisland/mitigation/trees.htm |access-date=7 July 2014 |website=EPA.gov}}</ref> Another benefit of having trees in a city is that trees also help fight global warming by absorbing {{CO2}} from the atmosphere. |
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=== Cool roofs and light-coloured concrete === |
=== Cool roofs and light-coloured concrete === |
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{{Main|Reflective surfaces (climate engineering)}} |
{{Main|Reflective surfaces (climate engineering)}} |
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[[File:20080708 Chicago City Hall Green Roof.JPG|thumb|Green roof of [[Chicago City Hall]]]] |
[[File:20080708 Chicago City Hall Green Roof.JPG|thumb|Green roof of [[Chicago City Hall]]]] |
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Painting rooftops white has become a common strategy to reduce the heat island effect.<ref name="autogenerated3">{{cite journal |last1=Zinzi |first1=M. |last2=Agnoli |first2=S. |date=2012 |title=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 |journal=Energy and Buildings |volume=55 |pages=66–76 |doi=10.1016/j.enbuild.2011.09.024 |bibcode=2012EneBu..55...66Z }}</ref> In cities, there are many dark |
Painting rooftops white has become a common strategy to reduce the heat island effect.<ref name="autogenerated3">{{cite journal |last1=Zinzi |first1=M. |last2=Agnoli |first2=S. |date=2012 |title=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 |journal=Energy and Buildings |volume=55 |pages=66–76 |doi=10.1016/j.enbuild.2011.09.024 |bibcode=2012EneBu..55...66Z }}</ref> In cities, there are many dark coloured surfaces that absorb the heat of the sun in turn lowering the albedo of the city.<ref name="autogenerated3" /> White rooftops allow high solar reflectance and high solar emittance, increasing the albedo of the city or area the effect is occurring.<ref name="autogenerated3" /> |
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Additionally, covering rooftops with a reflective coating, has shown to be an effective measure to reduce solar heat gain. A study led by Oscar Brousse from University College London, which simulated the impact of various cooling measures in London found that rooftops, which were either painted white or had reflective coating, proved to be the most effective solution for reducing outdoor temperatures at the pedestrian level, outperforming solar panels, green roofs, and tree cover. The study simulated the impact of various cooling measures in London during a 2018 heatwave, finding that the so-called cool roofs could reduce average outdoor temperatures by 1.2 °C, and up to 2 °C in certain areas. In comparison, additional tree cover reduced temperatures by 0.3 °C and solar panels by 0.5° C.<ref |
Additionally, covering rooftops with a reflective coating, has shown to be an effective measure to reduce solar heat gain. A study led by Oscar Brousse from University College London, which simulated the impact of various cooling measures in London found that rooftops, which were either painted white or had reflective coating, proved to be the most effective solution for reducing outdoor temperatures at the pedestrian level, outperforming solar panels, green roofs, and tree cover. The study simulated the impact of various cooling measures in London during a 2018 heatwave, finding that the so-called cool roofs could reduce average outdoor temperatures by 1.2 °C, and up to 2 °C in certain areas. In comparison, additional tree cover reduced temperatures by 0.3 °C and solar panels by 0.5° C.<ref name="auto"/> |
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Relative to remedying the other sources of the problem, replacing dark roofing requires the least amount of investment for the most immediate return. A [[cool roof]] made from a reflective material such as vinyl reflects at least 75 percent of the sun's rays, and emit at least 70 percent of the solar radiation absorbed by the building envelope. Asphalt built-up roofs (BUR), by comparison, reflect 6 percent to 26 percent of solar radiation.<ref>{{cite web |title=Comprehensive Cool Roof Guide from the Vinyl Roofing Division of the Chemical Fabrics and Film Association |url=http://vinylroofs.org/resources/coof-roofing-codes-programs-standards/index.html |url-status=dead |archive-url=https://web.archive.org/web/20130921054154/http://vinylroofs.org/resources/coof-roofing-codes-programs-standards/index.html |archive-date=2013-09-21 }}</ref> |
Relative to remedying the other sources of the problem, replacing dark roofing requires the least amount of investment for the most immediate return. A [[cool roof]] made from a reflective material such as vinyl reflects at least 75 percent of the sun's rays, and emit at least 70 percent of the solar radiation absorbed by the building envelope. Asphalt built-up roofs (BUR), by comparison, reflect 6 percent to 26 percent of solar radiation.<ref>{{cite web |title=Comprehensive Cool Roof Guide from the Vinyl Roofing Division of the Chemical Fabrics and Film Association |url=http://vinylroofs.org/resources/coof-roofing-codes-programs-standards/index.html |url-status=dead |archive-url=https://web.archive.org/web/20130921054154/http://vinylroofs.org/resources/coof-roofing-codes-programs-standards/index.html |archive-date=2013-09-21 }}</ref> |
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Using light- |
Using light-coloured concrete has proven effective in reflecting up to 50% more light than asphalt and reducing ambient temperature.<ref name="coolpave 2">{{cite web | title=Cool Pavement Report | url=http://www.epa.gov/heatisland/resources/pdf/CoolPavementReport_Former%20Guide_complete.pdf | date=June 2005 | publisher=[[Environmental Protection Agency]] | page=14| access-date=2009-02-06}}</ref> A low albedo value, characteristic of black asphalt, absorbs a large percentage of solar heat creating warmer near-surface temperatures. Paving with light-coloured concrete, in addition to replacing asphalt with light-coloured concrete, communities may be able to lower average temperatures.<ref name="worldchange">{{cite book |author=Gore |first=Al |title=World Changing: A User's Guide for the 21st Century |author2=Steffen |first2=A. |publisher=Abrams |year=2008 |location=New York |pages=258}}</ref> However, research into the interaction between reflective pavements and buildings has found that, unless the nearby buildings are fitted with reflective glass, solar radiation reflected off light-coloured pavements can increase building temperatures, increasing air conditioning demands.<ref name=Yaghoobian>{{Cite journal | last1 = Yaghoobian | first1 = N. | last2 = Kleissl | first2 = J. | doi = 10.1016/j.uclim.2012.09.002 | title = Effect of reflective pavements on building energy use | journal = Urban Climate | volume = 2 | pages = 25–42 | year = 2012 | bibcode = 2012UrbCl...2...25Y | doi-access = free }}</ref><ref>{{Citation |
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|title = Unintended Consequences: A Research Synthesis Examining the Use of Reflective Pavements to Mitigate the Urban Heat Island Effect |
|title = Unintended Consequences: A Research Synthesis Examining the Use of Reflective Pavements to Mitigate the Urban Heat Island Effect |
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|url = http://ncesmart.asu.edu/docs/smart/unintended-consequences-1013.pdf |
|url = http://ncesmart.asu.edu/docs/smart/unintended-consequences-1013.pdf |
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=== Green infrastructure === |
=== Green infrastructure === |
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{{Main|Green infrastructure|Green roof}} |
{{Main|Green infrastructure|Green roof}} |
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[[File:Budapest, CAF Urbos 3, 4.jpg|thumb|alt=Grassed tramway track in Budapest, Hungary|[[Green track|Grassed tramway track]] in Budapest, Hungary]] |
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[[Green roofs]] are excellent insulators during the warm weather months and the plants cool the surrounding environment. Plants can improve air quality as they absorb carbon dioxide and concomitantly produce oxygen.<ref>{{cite web |title=Green (Planted) Roofs |url=http://vinylroofs.org/resources/green-planted-roofs/index.html |access-date=2010-08-07 |archive-date=2011-07-28 |archive-url=https://web.archive.org/web/20110728163054/http://www.vinylroofs.org/resources/green-planted-roofs/index.html |url-status=dead }}</ref> Green roofs can also have positive impacts on stormwater management and energy consumption.<ref>{{Cite journal |last1=Liu |first1=Hongqing |last2=Kong |first2=Fanhua |last3=Yin |first3=Haiwei |last4=Middel |first4=Ariane |last5=Zheng |first5=Xiandi |last6=Huang |first6=Jing |last7=Xu |first7=Hairong |last8=Wang |first8=Ding |last9=Wen |first9=Zhihao |date=2021 |title=Impacts of green roofs on water, temperature, and air quality: A bibliometric review |url=https://doi.org/10.1016/j.buildenv.2021.107794 |journal=Building and Environment |volume=196 |pages=107794 |doi=10.1016/j.buildenv.2021.107794 |bibcode=2021BuEnv.19607794L |issn=0360-1323}}</ref> Cost can be a barrier to implementing a green roof.<ref>{{Cite web |title=Four Barriers to Implementing Green Roofs – And How to Overcome Them {{!}} Nicole Holmes |url=https://livingarchitecturemonitor.com/articles/four-barriers-to-implementing-green-roofs-and-how-to-overcome-them-fa23 |access-date=2024-07-01 |website=Living Architecture Monitor |language=en-US}}</ref><ref name=":12">{{Cite journal |last1=Teotónio |first1=Inês |last2=Silva |first2=Cristina Matos |last3=Cruz |first3=Carlos Oliveira |date=2021 |title=Economics of green roofs and green walls: A literature review |url=https://doi.org/10.1016/j.scs.2021.102781 |journal=Sustainable Cities and Society |volume=69 |pages=102781 |doi=10.1016/j.scs.2021.102781 |bibcode=2021SusCS..6902781T |issn=2210-6707}}</ref> Several factors influence the cost of a green roof, including design and soil depth, location, and the price of labor and equipment in that market, which is typically lower in more developed markets where there is more experience designing and installing green roofs.<ref>{{Cite book |last1=Feng |first1=Haibo |title=Nature based strategies for urban and building sustainability |last2=Hewage |first2=Kasun N. |publisher=Butterworth-Heinemann |year=2018 |pages=307–318 |chapter=Economic benefits and costs of green roofs |doi=10.1016/B978-0-12-812150-4.00028-8|isbn=978-0-12-812150-4 }}</ref> The individualized context of each green roof presents a challenge for making broad comparisons and assessments, and focusing only on monetary costs may leave out the social, environmental, and public health benefits green roofs provide.<ref name=":12" /> Global comparisons of green roof performance are further challenged by the lack of a shared framework for making such comparisons.<ref name=":12" /> |
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Stormwater management is another option to help mitigate the effect of the urban heat island. Stormwater management is the controlling the water produced by the storm in a way that protects property and infrastructure.<ref>https://www.gosnells.wa.gov.au/sites/default/files/seamless/3_stormwater_management.pdf</ref> Urban infrastructure like streets, sidewalks, and parking lots do not allow for water to penetrate into the earth's surface causing water to flood. By using stormwater management, you can control the flow of the water in ways that can mitigate UHI effect. One way is using a stormwater management technique called pervious pavement system (PPS). This technique has been used in over 30 countries and found to be successful in stormwater management and UHI mitigation. The PPS allows water to flow through the pavement allowing for the water to be absorbed causing the area to be cooled by evaporation.<ref>{{cite journal |last1=Wang |first1=Junsong |last2=Meng |first2=Qinglin |last3=Zou |first3=Ya |last4=Qi |first4=Qianlong |last5=Tan |first5=Kanghao |last6=Santamouris |first6=Mat |last7=He |first7=Bao-Jie |title=Performance synergism of pervious pavement on stormwater management and urban heat island mitigation: A review of its benefits, key parameters, and co-benefits approach |journal=Water Research |date=August 2022 |volume=221 |pages=118755 |doi=10.1016/j.watres.2022.118755 |pmid=35728492 |bibcode=2022WatRe.22118755W }}</ref> |
Stormwater management is another option to help mitigate the effect of the urban heat island. Stormwater management is the controlling the water produced by the storm in a way that protects property and infrastructure.<ref>{{Cite web | url=https://www.gosnells.wa.gov.au/sites/default/files/seamless/3_stormwater_management.pdf | title=Stormwater Management Objectives | website=www.gosnells.wa.gov.au}}</ref> Urban infrastructure like streets, sidewalks, and parking lots do not allow for water to penetrate into the earth's surface causing water to flood. By using stormwater management, you can control the flow of the water in ways that can mitigate UHI effect. One way is using a stormwater management technique called pervious pavement system (PPS). This technique has been used in over 30 countries and found to be successful in stormwater management and UHI mitigation. The PPS allows water to flow through the pavement allowing for the water to be absorbed causing the area to be cooled by evaporation.<ref>{{cite journal |last1=Wang |first1=Junsong |last2=Meng |first2=Qinglin |last3=Zou |first3=Ya |last4=Qi |first4=Qianlong |last5=Tan |first5=Kanghao |last6=Santamouris |first6=Mat |last7=He |first7=Bao-Jie |title=Performance synergism of pervious pavement on stormwater management and urban heat island mitigation: A review of its benefits, key parameters, and co-benefits approach |journal=Water Research |date=August 2022 |volume=221 |pages=118755 |doi=10.1016/j.watres.2022.118755 |pmid=35728492 |bibcode=2022WatRe.22118755W }}</ref> |
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[[Green parking lot]]s use vegetation and surfaces other than asphalt to limit the urban heat island effect. |
[[Green parking lot]]s use vegetation and surfaces other than asphalt to limit the urban heat island effect. |
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{{excerpt|green infrastructure|paragraphs=1}} |
{{excerpt|green infrastructure|paragraphs=1}} |
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=== Passive daytime radiative cooling === |
=== Passive daytime radiative cooling === |
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{{Main|Passive daytime radiative cooling}} |
{{Main|Passive daytime radiative cooling}} |
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A passive daytime radiative cooling roof application can double the energy savings of a white roof, attributed to high solar reflectance and thermal emittance in the [[infrared window]],<ref name=":352">{{cite journal |last1=Heo |first1=Se-Yeon |last2=Lee |first2=Gil Ju |last3=Song |first3=Young Min |title=Heat-shedding with photonic structures: radiative cooling and its potential |journal=Journal of Materials Chemistry C |date=2022 |volume=10 |issue=27 |pages=9915–9937 |doi=10.1039/D2TC00318J |s2cid=249695930 }}</ref> with the highest cooling potential in hot and dry cities such as [[Phoenix, Arizona|Phoenix]] and [[Las Vegas]].<ref name=":36">{{Cite journal |last1=Zhou |first1=Kai |last2=Miljkovic |first2=Nenad |last3=Cai |first3=Lili |date=March 2021 |title=Performance analysis on system-level integration and operation of daytime radiative cooling technology for air-conditioning in buildings |journal=Energy and Buildings |volume=235 |page=110749 |doi=10.1016/j.enbuild.2021.110749 |bibcode=2021EneBu.23510749Z |s2cid=234180182 }}</ref> When installed on roofs in dense urban areas, passive daytime radiative cooling panels can significantly lower outdoor surface temperatures at the pedestrian level.<ref name=":2">{{Cite journal |last1=Younes |first1=Jaafar |last2=Ghali |first2=Kamel |last3=Ghaddar |first3=Nesreen |date=August 2022 |title=Diurnal Selective Radiative Cooling Impact in Mitigating Urban Heat Island Effect |journal=Sustainable Cities and Society |volume=83 |page=103932 |doi=10.1016/j.scs.2022.103932 |s2cid=248588547 }}</ref><ref name=":13">{{cite journal |last1=Khan |first1=Ansar |last2=Carlosena |first2=Laura |last3=Feng |first3=Jie |last4=Khorat |first4=Samiran |last5=Khatun |first5=Rupali |last6=Doan |first6=Quang-Van |last7=Santamouris |first7=Mattheos |title=Optically Modulated Passive Broadband Daytime Radiative Cooling Materials Can Cool Cities in Summer and Heat Cities in Winter |journal=Sustainability |date=19 January 2022 |volume=14 |issue=3 |pages=1110 |doi=10.3390/su14031110 |doi-access=free |hdl=2454/46738 |hdl-access=free }}</ref> |
A passive daytime radiative cooling roof application can double the energy savings of a white roof, attributed to high solar reflectance and thermal emittance in the [[infrared window]],<ref name=":352">{{cite journal |last1=Heo |first1=Se-Yeon |last2=Lee |first2=Gil Ju |last3=Song |first3=Young Min |title=Heat-shedding with photonic structures: radiative cooling and its potential |journal=Journal of Materials Chemistry C |date=2022 |volume=10 |issue=27 |pages=9915–9937 |doi=10.1039/D2TC00318J |s2cid=249695930 }}</ref> with the highest cooling potential in hot and dry cities such as [[Phoenix, Arizona|Phoenix]] and [[Las Vegas]].<ref name=":36">{{Cite journal |last1=Zhou |first1=Kai |last2=Miljkovic |first2=Nenad |last3=Cai |first3=Lili |date=March 2021 |title=Performance analysis on system-level integration and operation of daytime radiative cooling technology for air-conditioning in buildings |journal=Energy and Buildings |volume=235 |page=110749 |doi=10.1016/j.enbuild.2021.110749 |bibcode=2021EneBu.23510749Z |s2cid=234180182 }}</ref> When installed on roofs in dense urban areas, passive daytime radiative cooling panels can significantly lower outdoor surface temperatures at the pedestrian level.<ref name=":2">{{Cite journal |last1=Younes |first1=Jaafar |last2=Ghali |first2=Kamel |last3=Ghaddar |first3=Nesreen |date=August 2022 |title=Diurnal Selective Radiative Cooling Impact in Mitigating Urban Heat Island Effect |journal=Sustainable Cities and Society |volume=83 |page=103932 |doi=10.1016/j.scs.2022.103932 |bibcode=2022SusCS..8303932Y |s2cid=248588547 }}</ref><ref name=":13">{{cite journal |last1=Khan |first1=Ansar |last2=Carlosena |first2=Laura |last3=Feng |first3=Jie |last4=Khorat |first4=Samiran |last5=Khatun |first5=Rupali |last6=Doan |first6=Quang-Van |last7=Santamouris |first7=Mattheos |title=Optically Modulated Passive Broadband Daytime Radiative Cooling Materials Can Cool Cities in Summer and Heat Cities in Winter |journal=Sustainability |date=19 January 2022 |volume=14 |issue=3 |pages=1110 |doi=10.3390/su14031110 |doi-access=free |hdl=2454/46738 |hdl-access=free }}</ref> |
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== Society and culture == |
== Society and culture == |
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=== History of research === |
=== History of research === |
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The phenomenon was first investigated and described by [[Luke Howard]] in the 1810s, although he was not the one to name the phenomenon.<ref>{{cite book |last=Howard |first=Luke |url=https://books.google.com/books?id=dsoO-3LF0GoC&pg=PP1 |title=The Climate of London Deduced from Meteorological Observations |date=2012 |publisher=Cambridge University Press |isbn=9781108049511 |volume=1 |author-link=Luke Howard |orig-year=1818}}</ref> A description of the very first report of the UHI by Luke Howard said that the urban center of London was warmer at night than the surrounding countryside by {{convert|3.7|F-change|C-change|order=flip}}.<ref>{{cite web |author=Keith C. |
The phenomenon was first investigated and described by [[Luke Howard]] in the 1810s, although he was not the one to name the phenomenon.<ref>{{cite book |last=Howard |first=Luke |url=https://books.google.com/books?id=dsoO-3LF0GoC&pg=PP1 |title=The Climate of London Deduced from Meteorological Observations |date=2012 |publisher=Cambridge University Press |isbn=9781108049511 |volume=1 |author-link=Luke Howard |orig-year=1818}}</ref> A description of the very first report of the UHI by Luke Howard said that the urban center of London was warmer at night than the surrounding countryside by {{convert|3.7|F-change|C-change|order=flip}}.<ref>{{cite web |author=Heidorn |first=Keith C. |year=2009 |title=Luke Howard: The Man Who Named The Clouds |url=http://www.islandnet.com/~see/weather/history/howard.htm |access-date=2009-06-18 |publisher=Islandnet.com}}</ref> |
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Investigations of the urban atmosphere continued throughout the nineteenth century. Between the 1920s and the 1940s, researchers in the emerging field of local climatology or [[microscale meteorology]] in Europe, Mexico, India, Japan, and the United States pursued new methods to understand the phenomenon. |
Investigations of the urban atmosphere continued throughout the nineteenth century. Between the 1920s and the 1940s, researchers in the emerging field of local climatology or [[microscale meteorology]] in Europe, Mexico, India, Japan, and the United States pursued new methods to understand the phenomenon. |
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=== Aspects of social inequality === |
=== Aspects of social inequality === |
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{{main|Urban heat inequity}} |
{{main|Urban heat inequity}} |
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Some studies suggest that the effects of UHIs on health may be disproportionate, since the impacts may be unevenly distributed based on a variety of factors such as age,<ref name="WHO" /><ref name="Diaz article">{{cite journal |last=Díaz |first=J. |author2=Jordán, A. |author3=García, R. |author4=López, C. |author5=Alberdi, J. |author6=Hernández, E. |author7=Otero, A. |date=1 February 2014 |title=Heat waves in Madrid 1986–1997: effects on the health of the elderly |journal=International Archives of Occupational and Environmental Health |volume=75 |issue=3 |pages=163–170 |doi=10.1007/s00420-001-0290-4 |pmid=11954983 |s2cid=31284700}}</ref> ethnicity and socioeconomic status.<ref name="Harlan article">{{cite journal |last=Harlan |first=Sharon L. |author2=Brazel, Anthony J. |author3=Prashad, Lela |author4=Stefanov, William L. |author5=Larsen, Larissa |date=December 2006 |title=Neighborhood microclimates and vulnerability to heat stress |journal=Social Science & Medicine |volume=63 |issue=11 |pages=2847–2863 |doi=10.1016/j.socscimed.2006.07.030 |pmid=16996668 |hdl=2286/R.I.55228|hdl-access=free }}</ref> This raises the possibility of health impacts from UHIs being an [[environmental justice]] issue. Studies have shown that [[communities of color]] in the United States have been disproportionately affected by UHI.<ref>{{Cite web |last=US |
Some studies suggest that the effects of UHIs on health may be disproportionate, since the impacts may be unevenly distributed based on a variety of factors such as age,<ref name="WHO" /><ref name="Diaz article">{{cite journal |last=Díaz |first=J. |author2=Jordán, A. |author3=García, R. |author4=López, C. |author5=Alberdi, J. |author6=Hernández, E. |author7=Otero, A. |date=1 February 2014 |title=Heat waves in Madrid 1986–1997: effects on the health of the elderly |journal=International Archives of Occupational and Environmental Health |volume=75 |issue=3 |pages=163–170 |doi=10.1007/s00420-001-0290-4 |pmid=11954983 |s2cid=31284700}}</ref> ethnicity and socioeconomic status.<ref name="Harlan article">{{cite journal |last=Harlan |first=Sharon L. |author2=Brazel, Anthony J. |author3=Prashad, Lela |author4=Stefanov, William L. |author5=Larsen, Larissa |date=December 2006 |title=Neighborhood microclimates and vulnerability to heat stress |journal=Social Science & Medicine |volume=63 |issue=11 |pages=2847–2863 |doi=10.1016/j.socscimed.2006.07.030 |pmid=16996668 |hdl=2286/R.I.55228|hdl-access=free }}</ref> This raises the possibility of health impacts from UHIs being an [[environmental justice]] issue. Studies have shown that [[communities of color]] in the United States have been disproportionately affected by UHI.<ref>{{Cite web |last=US Environmental Protection Agency |first=OAR |date=2019-11-06 |title=Heat Islands and Equity |url=https://www.epa.gov/heatislands/heat-islands-and-equity |access-date=2024-04-18 |website=www.epa.gov |language=en}}</ref><ref>{{cite journal |last1=Wilson |first1=Bev |title=Urban Heat Management and the Legacy of Redlining |journal=Journal of the American Planning Association |date=October 2020 |volume=86 |issue=4 |pages=443–457 |doi=10.1080/01944363.2020.1759127 }}</ref><ref>{{cite journal |last1=Adams |first1=Kaitlyn |last2=Knuth |first2=Colette Steward |title=The effect of urban heat islands on pediatric asthma exacerbation: How race plays a role |journal=Urban Climate |date=January 2024 |volume=53 |pages=101833 |doi=10.1016/j.uclim.2024.101833 |bibcode=2024UrbCl..5301833A }}</ref> |
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There is a correlation between neighborhood income and tree canopy cover.<ref name="Demand">{{cite journal |last1=Zhu |first1=Pengyu |last2=Zhang |first2=Yaoqi |title=Demand for urban forests in United States cities |journal=Landscape and Urban Planning |date=March 2008 |volume=84 |issue=3–4 |pages=293–300 |doi=10.1016/j.landurbplan.2007.09.005 }}</ref> Low-income neighborhoods tend to have significantly fewer trees than neighborhoods with higher incomes.<ref name="Income Inequality">{{cite journal |last=De Chant |first=Tim |title=Urban Trees Reveal Income Inequality |url=http://persquaremile.com/2012/05/17/urban-trees-reveal-income-inequality/ |publisher=Per Square Mile |doi=10.1016/j.landurbplan.2007.09.005 |access-date=7 May 2014}}</ref> Researchers hypothesized that less-well-off neighborhoods do not have the financial resources to plant and maintain trees. [[Affluent]] neighborhoods can afford more trees, on "both public and private property |
There is a correlation between neighborhood income and tree canopy cover.<ref name="Demand">{{cite journal |last1=Zhu |first1=Pengyu |last2=Zhang |first2=Yaoqi |title=Demand for urban forests in United States cities |journal=Landscape and Urban Planning |date=March 2008 |volume=84 |issue=3–4 |pages=293–300 |doi=10.1016/j.landurbplan.2007.09.005 |bibcode=2008LUrbP..84..293Z }}</ref> Low-income neighborhoods tend to have significantly fewer trees than neighborhoods with higher incomes.<ref name="Income Inequality">{{cite journal |last=De Chant |first=Tim |title=Urban Trees Reveal Income Inequality |journal=Landscape and Urban Planning |date=2008 |volume=84 |issue=3 |url=http://persquaremile.com/2012/05/17/urban-trees-reveal-income-inequality/ |publisher=Per Square Mile |doi=10.1016/j.landurbplan.2007.09.005 |bibcode=2008LUrbP..84..293Z |access-date=7 May 2014}}</ref> Researchers hypothesized that less-well-off neighborhoods do not have the financial resources to plant and maintain trees. [[Affluent]] neighborhoods can afford more trees, on "both public and private property".<ref>{{cite journal |last1=Chant |first1=Tim |title=Urban Trees reveal income inequality |url=http://persquaremile.com/2012/05/17/urban-trees-reveal-income-inequality/ |doi=10.1016/j.landurbplan.2007.09.005 |access-date=7 July 2014 |journal=Landscape and Urban Planning|date=2008 |volume=84 |issue=3 |bibcode=2008LUrbP..84..293Z }}</ref> One reason for this discrepancy is that wealthier homeowners and communities can afford more land, which can be kept open as [[green belt|green space]], whereas poorer housing often takes the form of [[Renting|rentals]], where landowners try to maximize their [[profit (economics)|profit]] by putting as much housing [[population density|density]] as possible on their land.<ref>{{Cite web |last=DeSilver |first=Drew |date=2021-08-02 |title=As national eviction ban expires, a look at who rents and who owns in the U.S. |url=https://www.pewresearch.org/short-reads/2021/08/02/as-national-eviction-ban-expires-a-look-at-who-rents-and-who-owns-in-the-u-s/ |access-date=2024-05-02 |website=Pew Research Center |language=en-US}}</ref> |
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=== Chief heat officers === |
=== Chief heat officers === |
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=== United States === |
=== United States === |
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Bill S.4280,<ref>{{Cite web |last=Markey |first=Edward J. |date=2020-07-22 |title=S.4280 |
Bill S.4280,<ref>{{Cite web |last=Markey |first=Edward J. |date=2020-07-22 |title=S.4280 – 116th Congress (2019–2020): Preventing HEAT Illness and Deaths Act of 2020 |url=https://www.congress.gov/bill/116th-congress/senate-bill/4280 |access-date=2021-10-26 |website=www.congress.gov}}</ref> introduced to the U.S. Senate in 2020, would authorize the National Integrated Heat Health Information System Interagency Committee (NIHHIS) to tackle extreme heat in the United States.<ref>{{Cite web |title=New federal bill supports heat island mitigation |url=https://www.usgbc.org/articles/new-federal-bill-supports-heat-island-mitigation |access-date=2021-10-26 |publisher=U.S. Green Building Council}}</ref> Successful passage of this legislation would fund NIHHIS for five years and would instate a $100 million grant program within NIHHIS to encourage and fund urban heat reduction projects, including those using cools roofs and pavements and those improving [[Heating, ventilation, and air conditioning|HVAC]] systems. As of July 22, 2020 the bill has not moved past introduction to Congress. |
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The city of New York determined that the cooling potential per area was highest for street trees, followed by living roofs, light covered surface, and open space planting. From the standpoint of cost effectiveness, light surfaces, light roofs, and curbside planting have lower costs per temperature reduction.<ref>{{cite web |author=New York City Regional Heat Island Initiative |date=October 2006 |title=Mitigating New York City's Heat Island With Urban Forestry, Living Roofs, and Light Surfaces |url=http://www.nyserda.ny.gov/programs/environment/emep/project/6681_25/06-06%20Complete%20report-web.pdf |access-date=2009-06-18 |publisher=New York State Energy Research and Development Authority |page=ii}}{{Dead link|date=October 2022|bot=InternetArchiveBot|fix-attempted=yes}}</ref> |
The city of New York determined that the cooling potential per area was highest for street trees, followed by living roofs, light covered surface, and open space planting. From the standpoint of cost effectiveness, light surfaces, light roofs, and curbside planting have lower costs per temperature reduction.<ref>{{cite web |author=New York City Regional Heat Island Initiative |date=October 2006 |title=Mitigating New York City's Heat Island With Urban Forestry, Living Roofs, and Light Surfaces |url=http://www.nyserda.ny.gov/programs/environment/emep/project/6681_25/06-06%20Complete%20report-web.pdf |access-date=2009-06-18 |publisher=New York State Energy Research and Development Authority |page=ii}}{{Dead link|date=October 2022|bot=InternetArchiveBot|fix-attempted=yes}}</ref> |
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In a case study of the [[Los Angeles Basin]] in 1998, simulations showed that even when trees are not strategically placed in these urban heat islands, they can still aid in minimization of pollutants and energy reduction. It is estimated that with this wide-scale implementation, the city of Los Angeles can annually save $100M with most of the savings coming from cool roofs, lighter colored pavement, and the planting of trees. With a citywide implementation, added benefits from the lowering smog-level would result in at least one billion dollars of saving per year.<ref name="Rosenfeld98" /> |
In a case study of the [[Los Angeles Basin]] in 1998, simulations showed that even when trees are not strategically placed in these urban heat islands, they can still aid in minimization of pollutants and energy reduction. It is estimated that with this wide-scale implementation, the city of Los Angeles can annually save $100M with most of the savings coming from cool roofs, lighter colored pavement, and the planting of trees. With a citywide implementation, added benefits from the lowering smog-level would result in at least one billion dollars of saving per year.<ref name="Rosenfeld98" /> |
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Los Angeles [[TreePeople]] is an example of how [[tree planting]] can empower a community. |
Los Angeles [[TreePeople]] is an example of how [[tree planting]] can empower a community. TreePeople provides the opportunity for people to come together, build capacity, community pride and the opportunity to collaborate and [[Social network|network]] with each other.<ref>Wilmsen, Carl. Partnerships for Empowerment: Participatory Research for Community-based Natural Resource Management. London, England: Earthscan, 2008. Print.</ref> |
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Los Angeles has also begun to implement a Heat Action Plan to address the city's needs at a more granular level than the solutions provided by the state of California. The city uses the LA Equity Index in an effort to ensure that the effects of extreme heat are mitigated in an equitable manner.<ref>{{Cite web |date=October 26, 2023 |title=Cool solutions for urban heat islands {{!}} Stanford Woods Institute for the Environment |url=https://woods.stanford.edu/news/cool-solutions-urban-heat-islands |access-date=2024-05-02 |website=woods.stanford.edu |language=en}}</ref> |
Los Angeles has also begun to implement a Heat Action Plan to address the city's needs at a more granular level than the solutions provided by the state of California. The city uses the LA Equity Index in an effort to ensure that the effects of extreme heat are mitigated in an equitable manner.<ref>{{Cite web |date=October 26, 2023 |title=Cool solutions for urban heat islands {{!}} Stanford Woods Institute for the Environment |url=https://woods.stanford.edu/news/cool-solutions-urban-heat-islands |access-date=2024-05-02 |website=woods.stanford.edu |language=en}}</ref> |
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==== Virginia ==== |
==== Virginia ==== |
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In 2021, Climate Adaptation Planning Analysis (CAPA) received funding from the [[National Oceanic and Atmospheric Administration]] to conduct Heat Mapping across the United States.<ref>{{Cite web |last=KristinaP |title=Collaborative Heat Mapping Research Project |url=https://www.vfic.org/vfic-programs/stem-faculty-initiative/collaborative-heat-mapping-research-project/ |access-date=2024-05-02 |website=Virginia Foundation for Independent Colleges |language=en-US}}</ref> Ten areas from [[Virginia]] |
In 2021, Climate Adaptation Planning Analysis (CAPA) received funding from the [[National Oceanic and Atmospheric Administration]] to conduct Heat Mapping across the United States.<ref>{{Cite web |last=KristinaP |title=Collaborative Heat Mapping Research Project |url=https://www.vfic.org/vfic-programs/stem-faculty-initiative/collaborative-heat-mapping-research-project/ |access-date=2024-05-02 |website=Virginia Foundation for Independent Colleges |language=en-US}}</ref> Ten areas from [[Virginia]] – Abington, Arlington, Charlottesville, Farmville, Harrisonburg, Lynchburg, Petersburg, Richmond, Salem, Virginia Beach and Winchester – participated in the heat watch campaign. This campaign consisted of 213 Volunteers brought together by campaign organizers who made 490,423 Heat Measurements across 70 Routes total. After taking measurements throughout the day, equipment and data was sent back to CAPA where it was analyzed using machine learning algorithms. After analysis of the data, CAPA came back together with campaign organizers from each area to discuss potential plans for each town in the future. |
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==== New York ==== |
==== New York ==== |
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New York City implemented its "Cool Neighborhoods NYC" program in 2017 intending to mitigate the effects of extreme urban heat. One of the plan's ambitions was to increase funding for the city's Low-Income Home Energy Assistance Program. Specifically, the plan sought to increase funding for cooling solutions for lower-income families.<ref>{{Cite web |date=2017-06-14 |title=Cool Neighborhoods NYC |url=https://climate.cityofnewyork.us/reports/cool-neighborhoods-nyc/ |access-date=2024-05-02 |website=NYC Mayor's Office of Climate and Environmental Justice |language=en-US}}</ref> |
New York City implemented its "Cool Neighborhoods NYC" program in 2017 intending to mitigate the effects of extreme urban heat. One of the plan's ambitions was to increase funding for the city's Low-Income Home Energy Assistance Program. Specifically, the plan sought to increase funding for cooling solutions for lower-income families.<ref>{{Cite web |date=2017-06-14 |title=Cool Neighborhoods NYC |url=https://climate.cityofnewyork.us/reports/cool-neighborhoods-nyc/ |access-date=2024-05-02 |website=NYC Mayor's Office of Climate and Environmental Justice |language=en-US}}</ref> |
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=== India === |
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Several cities in India experience significant urban heat island effects due to rapid urbanization, loss of green cover, and extensive concretization. A report by ''The Hindu'' highlights that metropolitan areas like Delhi, Bengaluru, Chennai, Jaipur, Ahmedabad, Mumbai, and Kolkata have seen temperature differences ranging from 1°C to 6°C compared to their rural surroundings. These urban heat islands not only increase the local temperatures but also exacerbate the impacts of heatwaves, leading to higher energy consumption for cooling and posing health risks to vulnerable populations.<ref>{{Cite news |last=Balasubramanian |first=D. |date=2020-02-15 |title=Urban heat islands in India |url=https://www.thehindu.com/sci-tech/science/urban-heat-islands-in-india/article30830560.ece |access-date=2024-10-23 |work=The Hindu |language=en-IN |issn=0971-751X}}</ref> |
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==== Mumbai ==== |
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Mumbai, India's financial hub and one of the most densely populated cities globally, is significantly affected by the urban heat island effect. Rapid urbanization, extensive concretization, and loss of green spaces have led to higher temperatures in the city compared to its surroundings. According to a report, Mumbai is projected to spend twice as much as New York City to manage urban heat generated due to concretization. This increased expenditure highlights the severity of the urban heat island effect in Mumbai and its impact on the city's infrastructure and residents.<ref>{{Cite news |date=2024-02-06 |title=Mumbai's spendings will be double of New York's to manage urban heat generated due to concretisation |url=https://timesofindia.indiatimes.com/city/mumbai/mumbais-spendings-will-be-double-of-new-yorks-to-manage-urban-heat-generated-due-to-concretisation/articleshow/107465459.cms |access-date=2024-10-23 |work=The Times of India |issn=0971-8257}}</ref> |
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==See also== |
==See also== |
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* {{annotated link|Urban climatology}} |
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* {{annotated link|Urban reforestation}} |
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* {{annotated link|Tropical night}} |
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* {{annotated link|Urban dust dome}} |
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==References== |
==References== |
Latest revision as of 04:41, 7 December 2024
Urban areas usually experience the urban heat island (UHI) effect, that is, they are significantly warmer than surrounding rural areas. The temperature difference is usually larger at night than during the day,[1] and is most apparent when winds are weak, under block conditions, noticeably during the summer and winter. The main cause of the UHI effect is from the modification of land surfaces while waste heat generated by energy usage is a secondary contributor.[2][3][4] Urban areas occupy about 0.5% of the Earth's land surface but host more than half of the world's population.[5] As a population center grows, it tends to expand its area and increase its average temperature. The term heat island is also used; the term can be used to refer to any area that is relatively hotter than the surrounding, but generally refers to human-disturbed areas.[6]
Monthly rainfall is greater downwind of cities, partially due to the UHI. Increases in heat within urban centers increases the length of growing seasons and decreases the occurrence of weak tornadoes. The UHI decreases air quality by increasing the production of pollutants such as ozone, and decreases water quality as warmer waters flow into area streams and put stress on their ecosystems.
Not all cities have a distinct urban heat island, and the heat island characteristics depend strongly on the background climate of the area in which the city is located.[7] The impact in a city can change a lot based on its local environment. Heat can be reduced by tree cover and green space which act as sources of shade and promote evaporative cooling.[8] Other options include green roofs, passive daytime radiative cooling applications, and the use of lighter-colored surfaces and less absorptive building materials. These reflect more sunlight and absorb less heat.[9][10][11]
Climate change is not the cause of urban heat islands but it is causing more frequent and more intense heat waves which in turn amplify the urban heat island effect in cities.[12]: 993 Compact, dense urban development may increase the urban heat island effect, leading to higher temperatures and increased exposure.[13]
Definition
[edit]A definition of urban heat island is: "The relative warmth of a city compared with surrounding rural areas."[14]: 2926 This relative warmth is caused by "heat trapping due to land use, the configuration and design of the built environment, including street layout and building size, the heat-absorbing properties of urban building materials, reduced ventilation, reduced greenery and water features, and domestic and industrial heat emissions generated directly from human activities".[14]: 2926
Description
[edit]Diurnal variability
[edit]Throughout the daytime, particularly when the skies are cloudless, urban surfaces are warmed by the absorption of solar radiation. Surfaces in the urban areas tend to warm faster than those of the surrounding rural areas. By virtue of their high heat capacities, urban surfaces act as a reservoir of heat energy. For example, concrete can hold roughly 2,000 times as much heat as an equivalent volume of air.[citation needed] As a result, high daytime surface temperatures within the UHI can be easily seen via thermal remote sensing. As is often the case with daytime heating, this warming also has the effect of generating convective winds within the urban boundary layer. At night, the situation reverses. The absence of solar heating leads to the decrease of atmospheric convection and the stabilization of urban boundary layer. If enough stabilization occurs, an inversion layer is formed. This traps urban air near the surface, keeping surface air warm from the still-warm urban surfaces, resulting in warmer nighttime air temperatures within the UHI.
Generally speaking, the difference in temperature between the urban and surrounding rural area is more pronounced at night than in daytime.[15] For example, in the United States, the temperature in urban areas tends to be warmer than the surrounding area by about 1–7 °F (0.6–4 °C) during the daytime, and about 2–5 °F (1–3 °C) warmer at night.[16] However, the difference is more pronounced during the day in arid climates such as those in southeastern China and Taiwan.[17][18] Studies have shown that diurnal variability is impacted by several factors including local climate and weather, seasonality, humidity, vegetation, surfaces, and materials in the built environment.[19][16][20][21]
Seasonal variability
[edit]Seasonal variability is less well understood than diurnal variability of the urban heat island temperature difference.[22] Complex relationships between precipitation, vegetation, solar radiation, and surface materials in various local climate zones play interlocking roles that influence seasonal patterns of temperature variation in a particular urban heat island.[22][23][24][25]
Measurements and predictions
[edit]Urban Heat Island Index (UHII)
[edit]One method to quantify the UHI effect within urban areas is the UHI Index created by the Californian EPA in 2015. It compares the temperature of a surveyed area and rural reference points upwind from the surveyed area, at a height of two meters above ground level. The difference in temperature in degrees Celsius is taken hourly and differences with an increased urban temperature compared to the reference points are summed up, creating an amount of degree-Celsius-hours, which is the UHI Index of the surveyed area. The measure of Celsius-hours might be averaged over many days, but is specified as Celsius-hours per averaged day.[26][27][28]
The index was created to estimate the expected use of air conditioning and resulting greenhouse gas emissions in California.[27] The index does not consider values of or differences in wind-speed, humidity, or solar influx, which might influence perceived temperature or the operation of air conditioners.[28]
Models and simulations
[edit]If a city or town has a good system of taking weather observations the UHI can be measured directly.[29] An alternative is to use a complex simulation of the location to calculate the UHI, or to use an approximate empirical method.[30][31] Such models allow the UHI to be included in estimates of future temperatures rises within cities due to climate change.
Leonard O. Myrup published the first comprehensive numerical treatment to predict the effects of the urban heat island (UHI) in 1969.[32] The heat island effect was found to be the net result of several competing physical processes. In general, reduced evaporation in the city center and the thermal properties of the city building and paving materials are the dominant parameters.[32] Modern simulation environments include ENVI-met, which simulates all interactions between building and ground surfaces, plants and ambient air.[33]
Causes
[edit]Urban design
[edit]There are several causes of an urban heat island (UHI) related to common urban design aspects. For example, dark surfaces absorb significantly more solar radiation, which causes urban concentrations of roads and buildings to heat more than suburban and rural areas during the day;[2] materials commonly used in urban areas for pavement and roofs, such as concrete and asphalt, have significantly different thermal bulk properties (including heat capacity and thermal conductivity) and surface radiative properties (albedo and emissivity) than the surrounding rural areas. This causes a change in the energy budget of the urban area, often leading to higher temperatures than surrounding rural areas.[34]
Pavements, parking lots, roads or, more generally speaking transport infrastructure, contribute significantly to the urban heat island effect.[35] For example, pavement infrastructure is a main contributor to urban heat during summer afternoons in Phoenix, United States.[35]
Another major reason is the lack of evapotranspiration (for example, through lack of vegetation) in urban areas.[36] The U.S. Forest Service found in 2018 that cities in the United States are losing 36 million trees each year.[37] With a decreased amount of vegetation, cities also lose the shade and evaporative cooling effect of trees.[38][39]
Other causes of a UHI are due to geometric effects. The tall buildings within many urban areas provide multiple surfaces for the reflection and absorption of sunlight, increasing the efficiency with which urban areas are heated. This is called the "urban canyon effect". Another effect of buildings is the blocking of wind, which also inhibits cooling by convection and prevents pollutants from dissipating. Waste heat from automobiles, air conditioning, industry, and other sources also contributes to the UHI.[4][40][41]
Heat islands can be affected by proximity to different types of land cover, so that proximity to barren land causes urban land to become hotter and proximity to vegetation makes it cooler.[42]
Air pollution
[edit]High levels of air pollution in urban areas can also increase the UHI, as many forms of pollution change the radiative properties of the atmosphere.[34] UHI not only raises urban temperatures but also increases ozone concentrations because ozone is a greenhouse gas whose formation will accelerate with the increase of temperature.[43]
Climate change as an amplifier
[edit]Climate change is not a cause but an amplifier of the urban heat island effect. The IPCC Sixth Assessment Report from 2022 summarized the available research accordingly: "Climate change increases heat stress risks in cities [...] and amplifies the urban heat island across Asian cities at 1.5 °C and 2 °C warming levels, both substantially larger than under present climates [...]."[44]: 66
The report goes on to say: "In a warming world, increasing air temperature makes the urban heat island effect in cities worse. One key risk is heatwaves in cities that are likely to affect half of the future global urban population, with negative impacts on human health and economic productivity."[12]: 993
There are unhelpful interactions between heat and built infrastructure: These interactions increase the risk of heat stress for people living in cities.[12]: 993
Impacts
[edit]On weather and climate
[edit]Aside from the effect on temperature, UHIs can produce secondary effects on local meteorology, including the altering of local wind patterns, the development of clouds and fog, the humidity, and the rates of precipitation.[45] The extra heat provided by the UHI leads to greater upward motion, which can induce additional shower and thunderstorm activity. In addition, the UHI creates during the day a local low pressure area where relatively moist air from its rural surroundings converges, possibly leading to more favorable conditions for cloud formation.[46] Rainfall rates downwind of cities are increased between 48% and 116%. Partly as a result of this warming, monthly rainfall is about 28% greater between 20 and 40 miles (32 and 64 km) downwind of cities, compared with upwind.[47] Some cities show a total precipitation increase of 51%.[48]
One study concluded that cities change the climate in area two–four times larger than their own area.[49] One 1999 comparison between urban and rural areas proposed that urban heat island effects have little influence on global mean temperature trends.[50] Others suggested that urban heat islands affect global climate by impacting the jet stream.[51]
On human health
[edit]UHIs have the potential to directly influence the health and welfare of urban residents. As UHIs are characterized by increased temperature, they can potentially increase the magnitude and duration of heat waves within cities. The number of individuals exposed to extreme temperatures is increased by the UHI-induced warming.[52] The nighttime effect of UHIs can be particularly harmful during a heat wave, as it deprives urban residents of the cool relief found in rural areas during the night.[53]
Increased temperatures have been reported to cause heat illnesses, such as heat stroke, heat exhaustion, heat syncope, and heat cramps.[54][55]
Extreme heat is the deadliest form of weather in the U.S. Per a study by Professor Terri Adams-Fuller, heat waves kill more people in the U.S. than hurricanes, floods, and tornadoes combined.[56] These heat illnesses are more common within medium-to-large metro areas than the rest of the U.S., largely in part due to UHIs. Heat illnesses can also be compounded when combined with air pollution which is common in many urban areas.[55]
Heat exposure can have adverse effects on mental health. Increases in temperature can contribute to increased aggression, as well as more cases of domestic violence and substance abuse.[57] Greater heat can also negatively impact school performance and education. According to a study by Hyunkuk Cho of Yeungnam University, an increased number of days with extreme heat each year correlates to a decrease in student test scores.[58]
High UHI intensity correlates with increased concentrations of air pollutants that gathered at night, which can affect the next day's air quality.[59] These pollutants include volatile organic compounds, carbon monoxide, nitrogen oxides, and particulate matter.[60][61] The production of these pollutants combined with the higher temperatures in UHIs can quicken the production of ozone.[59] Ozone at surface level is considered to be a harmful pollutant.[59] Studies suggest that increased temperatures in UHIs can increase polluted days but also note that other factors (e.g. air pressure, cloud cover, wind speed) can also have an effect on pollution.[59]
Studies from Hong Kong have found that areas of the city with poorer outdoor urban air ventilation tended to have stronger urban heat island effects[62] and had significantly higher all-cause mortality[63] compared to areas with better ventilation. Another study employing advanced statistical methods in Babol city, Iran, revealed a significant increase in Surface Urban Heat Island Intensity (SUHII) from 1985 to 2017, influenced by both geographic direction and time. This research, enhancing the understanding of SUHII's spatial and temporal variations, emphasizes the need for precise urban planning to mitigate the health impacts of urban heat islands.[64] Surface UHI's are more prominent during the day and are measured using the land surface temperature and remote sensing.[65]
On water bodies and aquatic organisms
[edit]UHIs also impair water quality. Hot pavement and rooftop surfaces transfer their excess heat to stormwater, which then drains into storm sewers and raises water temperatures as it is released into streams, rivers, ponds, and lakes. Additionally, increased urban water body temperatures lead to a decrease in biodiversity in the water.[66] For example, in August 2001, rains over Cedar Rapids, Iowa led to a 10.5 °C (18.9 °F) rise in the nearby stream within one hour, resulting in a fish kill which affected an estimated 188 fish.[67] Since the temperature of the rain was comparatively cool, the deaths could be attributed to the hot pavement of the city. Similar events have been documented across the American Midwest, as well as Oregon and California.[68] Rapid temperature changes can be stressful to aquatic ecosystems.[69]
With the temperature of the nearby buildings sometimes reaching a difference of over 50 °F (28 °C) from the near-surface air temperature, precipitation warms rapidly, and run-off into nearby streams, lakes and rivers (or other bodies of water) to provide excessive thermal pollution. The increase in thermal pollution has the potential to increase water temperature by 20 to 30 °F (11 to 17 °C). This increase causes the fish species inhabiting the body of water to undergo thermal stress and shock due to the rapid change in temperature of their habitat.[70]
Permeable pavements may reduce these effects by percolating water through the pavement into subsurface storage areas where it can be dissipated through absorption and evaporation.[71]
On animals
[edit]Species that are good at colonizing can use conditions provided by urban heat islands to thrive in regions outside of their normal range. Examples of this include the grey-headed flying fox (Pteropus poliocephalus) and the common house gecko (Hemidactylus frenatus).[72] Grey-headed flying foxes, found in Melbourne, Australia, colonized urban habitats following the increase in temperatures there. Increased temperatures, causing warmer winter conditions, made the city more similar in climate to the more northerly wildland habitat of the species.
With temperate climates, urban heat islands will extend the growing season, therefore altering breeding strategies of inhabiting species.[72] This can be best observed in the effects that urban heat islands have on water temperature (see effects on water bodies).
Urban heat islands caused by cities have altered the natural selection process.[72] Selective pressures like temporal variation in food, predation and water are relaxed causing a new set of selective forces to roll out. For example, within urban habitats, insects are more abundant than in rural areas. Insects are ectotherms. This means that they depend on the temperature of the environment to control their body temperature, making the warmer climates of the city perfect for their ability to thrive. A study done in Raleigh, North Carolina conducted on Parthenolecanium quercifex (oak scales), showed that this particular species preferred warmer climates and were therefore found in higher abundance in urban habitats than on oak trees in rural habitats. Over time spent living in urban habitats, they have adapted to thrive in warmer climates than in cooler ones.[73]
On energy usage for cooling
[edit]Another consequence of urban heat islands is the increased energy required for air conditioning and refrigeration in cities that are in comparatively hot climates. The heat island effect costs Los Angeles about US$ 100 million per year in energy (in the year 2000).[74] Through the implementation of heat island reduction strategies, significant annual net energy savings have been calculated for northern locations such as Chicago, Salt Lake City, and Toronto.[75]
Every year in the U.S. 15% of energy goes towards the air conditioning of buildings in these urban heat islands. It was reported in 1998 that "the air conditioning demand has risen 10% within the last 40 years."[76]
Increases in air conditioning use also serve to worsen the effects of UHIs at night. While cooler nights are often a reprieve from heat waves during the day, the residual heat created by the use of air conditioning systems can lead to higher nighttime temperatures. According to a study by Professor Francisco Salamanca Palou and colleagues, this residual heat can cause nighttime increases of up to 1 °C in urban areas.[77] Increased energy use from air conditioners also contributes to carbon emissions, which doubly exacerbates the effects of UHIs.
Options for reducing heat island effects
[edit]Strategies to improve urban resilience by reducing excessive heat in cities include: Planting trees in cities, cool roofs (painted white or with reflective coating) and light-coloured concrete, green infrastructure (including green roofs), passive daytime radiative cooling.[78][61]
The temperature difference between urban areas and the surrounding suburban or rural areas can be as much as 5 °C (9.0 °F). Nearly 40 percent of that increase is due to the prevalence of dark roofs, with the remainder coming from dark-coloured pavement and the declining presence of vegetation. The heat island effect can be counteracted slightly by using white or reflective materials to build houses, roofs, pavements, and roads, thus increasing the overall albedo of the city.[79]
Concentric expansion of cities is unfavourable in terms of the urban heat island phenomenon. It is recommended to plan the development of cities in strips, consistent with the hydrographic network, taking into account green areas with various plant species.[80] In this way, it was planned to build urban settlements stretching over large areas, e.g. Kielce, Szczecin and Gdynia in Poland, Copenhagen in Denmark and Hamburg, Berlin and Kiel in Germany.
Planting trees in cities
[edit]Planting trees around the city can be another way of increasing albedo and decreasing the urban heat island effect. [81][82] It is recommended to plant deciduous trees because they can provide many benefits such as more shade in the summer and not blocking warmth in winter.[83] Trees are a necessary feature in combating most of the urban heat island effect because they reduce air temperatures by 10 °F (5.6 °C),[84] and surface temperatures by up to 20–45 °F (11–25 °C).[85] Another benefit of having trees in a city is that trees also help fight global warming by absorbing CO2 from the atmosphere.
Cool roofs and light-coloured concrete
[edit]Painting rooftops white has become a common strategy to reduce the heat island effect.[86] In cities, there are many dark coloured surfaces that absorb the heat of the sun in turn lowering the albedo of the city.[86] White rooftops allow high solar reflectance and high solar emittance, increasing the albedo of the city or area the effect is occurring.[86]
Additionally, covering rooftops with a reflective coating, has shown to be an effective measure to reduce solar heat gain. A study led by Oscar Brousse from University College London, which simulated the impact of various cooling measures in London found that rooftops, which were either painted white or had reflective coating, proved to be the most effective solution for reducing outdoor temperatures at the pedestrian level, outperforming solar panels, green roofs, and tree cover. The study simulated the impact of various cooling measures in London during a 2018 heatwave, finding that the so-called cool roofs could reduce average outdoor temperatures by 1.2 °C, and up to 2 °C in certain areas. In comparison, additional tree cover reduced temperatures by 0.3 °C and solar panels by 0.5° C.[78]
Relative to remedying the other sources of the problem, replacing dark roofing requires the least amount of investment for the most immediate return. A cool roof made from a reflective material such as vinyl reflects at least 75 percent of the sun's rays, and emit at least 70 percent of the solar radiation absorbed by the building envelope. Asphalt built-up roofs (BUR), by comparison, reflect 6 percent to 26 percent of solar radiation.[87]
Using light-coloured concrete has proven effective in reflecting up to 50% more light than asphalt and reducing ambient temperature.[88] A low albedo value, characteristic of black asphalt, absorbs a large percentage of solar heat creating warmer near-surface temperatures. Paving with light-coloured concrete, in addition to replacing asphalt with light-coloured concrete, communities may be able to lower average temperatures.[89] However, research into the interaction between reflective pavements and buildings has found that, unless the nearby buildings are fitted with reflective glass, solar radiation reflected off light-coloured pavements can increase building temperatures, increasing air conditioning demands.[90][91]
There are specific paint formulations for daytime radiative cooling that reflect up to 98.1% of sunlight.[92][93]
Green infrastructure
[edit]Green roofs are excellent insulators during the warm weather months and the plants cool the surrounding environment. Plants can improve air quality as they absorb carbon dioxide and concomitantly produce oxygen.[94] Green roofs can also have positive impacts on stormwater management and energy consumption.[95] Cost can be a barrier to implementing a green roof.[96][97] Several factors influence the cost of a green roof, including design and soil depth, location, and the price of labor and equipment in that market, which is typically lower in more developed markets where there is more experience designing and installing green roofs.[98] The individualized context of each green roof presents a challenge for making broad comparisons and assessments, and focusing only on monetary costs may leave out the social, environmental, and public health benefits green roofs provide.[97] Global comparisons of green roof performance are further challenged by the lack of a shared framework for making such comparisons.[97]
Stormwater management is another option to help mitigate the effect of the urban heat island. Stormwater management is the controlling the water produced by the storm in a way that protects property and infrastructure.[99] Urban infrastructure like streets, sidewalks, and parking lots do not allow for water to penetrate into the earth's surface causing water to flood. By using stormwater management, you can control the flow of the water in ways that can mitigate UHI effect. One way is using a stormwater management technique called pervious pavement system (PPS). This technique has been used in over 30 countries and found to be successful in stormwater management and UHI mitigation. The PPS allows water to flow through the pavement allowing for the water to be absorbed causing the area to be cooled by evaporation.[100]
Green parking lots use vegetation and surfaces other than asphalt to limit the urban heat island effect.
Passive daytime radiative cooling
[edit]A passive daytime radiative cooling roof application can double the energy savings of a white roof, attributed to high solar reflectance and thermal emittance in the infrared window,[106] with the highest cooling potential in hot and dry cities such as Phoenix and Las Vegas.[107] When installed on roofs in dense urban areas, passive daytime radiative cooling panels can significantly lower outdoor surface temperatures at the pedestrian level.[10][11]
Society and culture
[edit]History of research
[edit]The phenomenon was first investigated and described by Luke Howard in the 1810s, although he was not the one to name the phenomenon.[108] A description of the very first report of the UHI by Luke Howard said that the urban center of London was warmer at night than the surrounding countryside by 2.1 °C (3.7 °F).[109]
Investigations of the urban atmosphere continued throughout the nineteenth century. Between the 1920s and the 1940s, researchers in the emerging field of local climatology or microscale meteorology in Europe, Mexico, India, Japan, and the United States pursued new methods to understand the phenomenon.
In 1929, Albert Peppler used the term in a German publication believed to be the first instance of an equivalent to urban heat island: städtische Wärmeinsel (which is urban heat island in German).[110] Between 1990 and 2000, about 30 studies were published annually; by 2010, that number had increased to 100, and by 2015, it was more than 300.[111]
Leonard O. Myrup published the first comprehensive numerical treatment to predict the effects of the urban heat island (UHI) in 1969.[32] His paper surveys UHI and criticizes then-existing theories as being excessively qualitative.
Aspects of social inequality
[edit]Some studies suggest that the effects of UHIs on health may be disproportionate, since the impacts may be unevenly distributed based on a variety of factors such as age,[60][112] ethnicity and socioeconomic status.[113] This raises the possibility of health impacts from UHIs being an environmental justice issue. Studies have shown that communities of color in the United States have been disproportionately affected by UHI.[114][115][116]
There is a correlation between neighborhood income and tree canopy cover.[117] Low-income neighborhoods tend to have significantly fewer trees than neighborhoods with higher incomes.[118] Researchers hypothesized that less-well-off neighborhoods do not have the financial resources to plant and maintain trees. Affluent neighborhoods can afford more trees, on "both public and private property".[119] One reason for this discrepancy is that wealthier homeowners and communities can afford more land, which can be kept open as green space, whereas poorer housing often takes the form of rentals, where landowners try to maximize their profit by putting as much housing density as possible on their land.[120]
Chief heat officers
[edit]Beginning in the 2020s, a number of cities worldwide began creating Chief Heat Officer positions to organize and manage work counteracting the urban heat island effect.[121][122]
Examples
[edit]The examples and perspective in this article deal primarily with the United States and do not represent a worldwide view of the subject. (March 2023) |
United States
[edit]Bill S.4280,[123] introduced to the U.S. Senate in 2020, would authorize the National Integrated Heat Health Information System Interagency Committee (NIHHIS) to tackle extreme heat in the United States.[124] Successful passage of this legislation would fund NIHHIS for five years and would instate a $100 million grant program within NIHHIS to encourage and fund urban heat reduction projects, including those using cools roofs and pavements and those improving HVAC systems. As of July 22, 2020 the bill has not moved past introduction to Congress.
The city of New York determined that the cooling potential per area was highest for street trees, followed by living roofs, light covered surface, and open space planting. From the standpoint of cost effectiveness, light surfaces, light roofs, and curbside planting have lower costs per temperature reduction.[125]
Los Angeles
[edit]A hypothetical "cool communities" program in Los Angeles has projected in 1997 that urban temperatures could be reduced by approximately 3 °C (5 °F) after planting ten million trees, reroofing five million homes, and painting one-quarter of the roads at an estimated cost of US$1 billion, giving estimated annual benefits of US$170 million from reduced air-conditioning costs and US$360 million in smog related health savings.[83]
In a case study of the Los Angeles Basin in 1998, simulations showed that even when trees are not strategically placed in these urban heat islands, they can still aid in minimization of pollutants and energy reduction. It is estimated that with this wide-scale implementation, the city of Los Angeles can annually save $100M with most of the savings coming from cool roofs, lighter colored pavement, and the planting of trees. With a citywide implementation, added benefits from the lowering smog-level would result in at least one billion dollars of saving per year.[76]
Los Angeles TreePeople is an example of how tree planting can empower a community. TreePeople provides the opportunity for people to come together, build capacity, community pride and the opportunity to collaborate and network with each other.[126]
Los Angeles has also begun to implement a Heat Action Plan to address the city's needs at a more granular level than the solutions provided by the state of California. The city uses the LA Equity Index in an effort to ensure that the effects of extreme heat are mitigated in an equitable manner.[127]
Virginia
[edit]In 2021, Climate Adaptation Planning Analysis (CAPA) received funding from the National Oceanic and Atmospheric Administration to conduct Heat Mapping across the United States.[128] Ten areas from Virginia – Abington, Arlington, Charlottesville, Farmville, Harrisonburg, Lynchburg, Petersburg, Richmond, Salem, Virginia Beach and Winchester – participated in the heat watch campaign. This campaign consisted of 213 Volunteers brought together by campaign organizers who made 490,423 Heat Measurements across 70 Routes total. After taking measurements throughout the day, equipment and data was sent back to CAPA where it was analyzed using machine learning algorithms. After analysis of the data, CAPA came back together with campaign organizers from each area to discuss potential plans for each town in the future.
New York
[edit]New York City implemented its "Cool Neighborhoods NYC" program in 2017 intending to mitigate the effects of extreme urban heat. One of the plan's ambitions was to increase funding for the city's Low-Income Home Energy Assistance Program. Specifically, the plan sought to increase funding for cooling solutions for lower-income families.[129]
India
[edit]Several cities in India experience significant urban heat island effects due to rapid urbanization, loss of green cover, and extensive concretization. A report by The Hindu highlights that metropolitan areas like Delhi, Bengaluru, Chennai, Jaipur, Ahmedabad, Mumbai, and Kolkata have seen temperature differences ranging from 1°C to 6°C compared to their rural surroundings. These urban heat islands not only increase the local temperatures but also exacerbate the impacts of heatwaves, leading to higher energy consumption for cooling and posing health risks to vulnerable populations.[130]
Mumbai
[edit]Mumbai, India's financial hub and one of the most densely populated cities globally, is significantly affected by the urban heat island effect. Rapid urbanization, extensive concretization, and loss of green spaces have led to higher temperatures in the city compared to its surroundings. According to a report, Mumbai is projected to spend twice as much as New York City to manage urban heat generated due to concretization. This increased expenditure highlights the severity of the urban heat island effect in Mumbai and its impact on the city's infrastructure and residents.[131]
See also
[edit]- Urban climatology – Scientific study of atmosphere and the urban environment
- Urban reforestation – Planting of trees in urban environments
- Tropical night – Night with unusually high temperatures
- Urban dust dome
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