Urban resilience

From Wikipedia, the free encyclopedia
Jump to: navigation, search

Urban resilience is defined as the “capability to prepare for, respond to, and recover from significant multi-hazard threats with minimum damage to public safety and health, the economy, and security"[1] of a given urban area. Contemporary academic discussion of urban resilience focuses on three distinct threats; climate change, natural disasters and terrorism.[2][3] This article will initially focus on the challenges and disasters specific to climate change, and future additions on counter-terrorism, other disasters (earthquakes, tsunamis, solar flares, etc.) and sustainable energy strategies are welcome and encouraged.

The urban impacts of climate change vary widely across geographical and developmental scales. A recent study [4] of 616 cities (home to 1.7 billion people, with a combined GDP of USD 35 trillion, half of the world's total economic output), found that floods endanger more city residents than any other natural peril, followed by earthquakes and storms. This article will define and discussing the challenges of heat waves, droughts and flooding. Resilience-boosting strategies will be introduced and outlined. Resilience is especially important in urban areas, because over the past century there has been a considerable increase in urbanisation and urban sprawl. Half of the world’s population now lives in cities, a figure that is set to rise to 80% by 2050.[5] Mass density of people makes them especially vulnerable both to the impacts of acute disasters and the slow, creeping effects of the changing climate; all making resilience planning critically important.

Heat waves and droughts[edit]

Heat waves are becoming increasingly prevalent as the global climate changes. The 1980 United States heat wave and drought killed 10,000 people. In 1988 a similar heat wave and drought killed 17,000 American citizens.[6] In August 2003 the UK saw record breaking summer temperatures with average temperatures persistently rising above 32 °C. Nearly 3,000 deaths were contributed to the heat wave in the UK during this period, with an increase of 42% in London alone.[7] This heat wave claimed more than 40,000 lives across Europe.[8] Research indicates that by 2040 over 50% of summers will be warmer than 2003 and by 2100 those same summer temperatures will be considered cool.[9] The 2010 northern hemisphere summer heat wave was also disastrous, with nearly 5,000 deaths occurring in Moscow.[10] In addition to deaths, these heat waves also cause other significant problems. Extended periods of heat and droughts also cause widespread crop losses, spikes in electricity demand, forest fires, air pollution and reduced biodiversity in vital land and marine ecosystems.[11] Agricultural losses from heat and drought might not occur directly within the urban area, but it certainly affects the lives of urban dwellers. Crop supply shortages can lead to spikes in food prices, food scarcity, civic unrest and even starvation in extreme cases. In terms of the direct fatalities from these heat waves and droughts, they are statistically concentrated in urban areas,[12] and this is not just in line with increased population densities, but is due to social factors and the urban heat island effect.

Urban heat islands[edit]

Urban heat island (UHI) refers to the presence of an inner-city microclimate in which temperatures are comparatively higher than in the rural surroundings. Recent studies have shown that summer daytime temperatures can reach up to 10 °C hotter in a city centre than in rural areas and between 5–6 °C warmer at night.[13] The causes of UHI are no mystery, and are mostly based on simple energy balances and geometrics. The materials commonly found in urban areas (concrete and asphalt) absorb and store heat energy much more effectively than the surrounding natural environment. The black colouring of asphalt surfaces (roads, parking lots and highways) is able to absorb significantly more electromagnetic radiation, further encouraging the rapid and effective capture and storage of heat throughout the day. Geometrics come into play as well, as tall buildings provide large surfaces that both absorb and reflect sunlight and its heat energy onto other absorbent surfaces. These tall buildings also block the wind, which limits convective cooling. The sheer size of the buildings also blocks surface heat from naturally radiating back into the cool sky at night.[14] These factors, combined with the heat generated from vehicles, air conditioners and industry ensure that cities create, absorb and hold heat very effectively.

Social factors for heat vulnerability[edit]

The physical causes of heat waves and droughts and the exacerbation of the UHI effect are only part of the equation in terms of fatalities; social factors play a role as well. Statistically, senior citizens represent the majority of heat (and cold) related deaths within urban areas[15] and this is often due to social isolation. In rural areas, seniors are more likely to live with family or in care homes, whereas in cities they are often concentrated in subsidised apartment buildings and in many cases have little to no contact with the outside world.[16] Like other urban dwellers with little or no income, most urban seniors are unlikely to own an air conditioner. This combination of factors leads to thousands of tragic deaths every season, and incidences are increasing each year.[17]

Adapting for heat and drought resilience[edit]

Greening, reflecting & whitening urban spaces[edit]

Greening urban spaces is among the most frequently mentioned strategies to address heat effects. The idea is to increase the amount of natural cover within the city. This cover can be made up of grasses, bushes, trees, vines, water, rock gardens; any natural material. Covering as much surface as possible with green space will both reduce the total quantity of thermally absorbent artificial material, but the shading effect will reduce the amount of light and heat that reaches the concrete and asphalt that cannot be replaced by greenery.[18] Trees are among the most effective greening tool within urban environments because of their coverage/footprint ratio. Trees require a very small physical area for planting, but when mature, they provide a much larger coverage area. This both absorbs solar energy for photosynthesis (improving air quality and mitigating global warming), reducing the amount of energy being trapped and held within artificial surfaces, but also casts much-needed shade on the city and its inhabitants. Shade itself does not lower the ambient air temperature, but it greatly reduces the perceived temperature and comfort of those seeking its refuge.[19] A popular method of reducing UHI is simply increasing the albedo (light reflectiveness) of urban surfaces that cannot be ‘greened’. This is done by using reflective paints or materials where appropriate, or white and light-coloured options where reflections would be distracting or dangerous. Glazing can also be added to windows to reduce the amount of heat entering buildings.[20] Green roofs are also a resilience-boosting option, and have synergies with flood resilience strategies as well.

Social strategies[edit]

There are various strategies to increase the resilience of those most vulnerable to urban heat waves. As established, these vulnerable citizens are primarily socially isolated seniors. Other vulnerable groups include young children (especially those facing abject poverty or living in informal housing), people with underlying health problems, the infirm or disabled and the homeless. Accurate and early prediction of heat waves is of fundamental importance, as it gives time for the government to issue extreme heat alerts. Urban areas must prepare and be ready to implement heat-wave emergency response initiatives. Seasonal campaigns aimed to educate the public on the risks associated with heat waves will help prepare the broad community, but in response to impending heat events more direct action is required.[21] Local government must quickly communicate with the groups and institutions that work with heat-vulnerable populations. Cooling centres should be opened in libraries, community centres and government buildings. These centres ensure free access to air conditioning and water. In partnership with government and non-government social services, paramedics, police, firefighters, nurses and volunteers; the above-mentioned groups working with vulnerable populations should carry out regular door-to-door visits during these extreme heat scenarios. These visits should provide risk assessment, advice, bottled water (for areas without potable tap water) and the offer of free transportation to local cooling centres.[22]

Food and water supplies[edit]

Heat waves and droughts can reap massive damage on agricultural areas vital to providing food staples to urban populations. Reservoirs and aquifers quickly dry up due to increased demand on water for drinking, industrial and agricultural purposes. The end result can be shortages and price spikes for food and with increasing frequency, shortages of drinking water as observed with increasing severity seasonally in China[23] and throughout most of the developing world.[24] From an agricultural standpoint, farmers can be required to plant more heat and drought-resistant crops. Agricultural practices can also be streamlined to higher levels of hydrological efficiency. Reservoirs should be expanded and new reservoirs and water towers should be constructed in areas facing critical shortages.[25] Grander schemes of damming and redirecting rivers should also be considered if possible. For saltwater coastal cities, desalination plants provide a possible solution to water shortages. Infrastructure also plays a role in resilience, as in many areas aging pipelines result in leakage and possible contamination of drinking water. In Kenya’s major cities, Nairobi and Mombasa, between 40–50% of drinking water is lost through leakage.[26] In these types of cases, replacements and repairs are clearly needed.


Flooding, either from weather events, rising sea levels or infrastructure failures are a major cause of death, disease and economic losses throughout the world. Climate change and rapidly expanding urban settlements are two factors that are leading to the increasing occurrence and severity of urban flood events, especially in the developing world.[27][28][29] Storm surges can affect coastal cities and are caused by low pressure weather systems, like cyclones and hurricanes.[30] Flash floods and river floods can affect any city within a floodplain or with inadequate drainage infrastructure. These can be caused by large quantities of rain or heavy rapid snow melt. With all forms of flooding, cities are increasingly vulnerable because of the large quantity of paved and concrete surfaces. These impermeable surfaces cause massive amounts of runoff and can quickly overwhelm the limited infrastructure of storm drains, flood canals and intentional floodplains. Many cities in the developing world simply have no infrastructure to redirect floodwaters whatsoever.[31] Around the world, floods kill thousands of people every year and are responsible for billions of dollars in damages and economic losses.[32] Flooding, much like heat waves and droughts, can also wreak havoc on agricultural areas, quickly destroying large amounts of crops. In cities with poor or absent drainage infrastructure, flooding can also lead to the contamination of drinking water sources (aquifers, wells, inland waterways) with salt water, chemical pollution, and most frequently, viral and bacterial contaminants.[33]

Flood flow in urban environment[edit]

The flood flow in urbanised areas constitutes a hazard to the population and infrastructure. Some recent catastrophes included the inundations of Nîmes (France) in 1998 and Vaison-la-Romaine (France) in 1992, the flooding of New Orleans (USA) in 2005, the flooding in Rockhampton, Bundaberg, Brisbane during the 2010–2011 summer in Queensland (Australia). Flood flows in urban environments have been studied relatively recently despite many centuries of flood events.[31] Some researchers mentioned the storage effect in urban areas. Several studies looked into the flow patterns and redistribution in streets during storm events and the implication in terms of flood modelling.[34]

Some research considered the criteria for safe evacuation of individuals in flooded areas.[35] But some recent field measurements during the 2010–2011 Queensland floods showed that any criterion solely based upon the flow velocity, water depth or specific momentum cannot account for the hazards caused by the velocity and water depth fluctuations.[31] These considerations ignore further the risks associated with large debris entrained by the flow motion.[35]

Adapting for flood resilience[edit]

Urban greening[edit]

Replacing as many non-porous surfaces with green space as possible will create more areas for natural ground (and plant-based) absorption of excess water. Gaining popularity are different types of green roofs. Green roofs vary in their intensity, from very thin layers of soil or rockwool supporting a variety of low or no-maintenance mosses or sedum species to large, deep, intensive roof gardens capable of supporting large plants and trees but requiring regular maintenance and more structural support.[36] The deeper the soil, the more rainwater it can absorb and therefore the more potential floodwater it can prevent from reaching the ground. One of the best strategies, if possible, is to simply create enough space for the excess water. This involves planning or expanding areas of parkland in or adjacent to the zone where flooding is most likely to occur. Excess water is diverted into these areas when necessary, as in Cardiff, around the new Millennium Stadium.[37] Floodplain clearance is another greening strategy that fundamentally removes structures and pavement built on floodplains and returns them to their natural habitat which is capable of absorbing massive quantities of water that otherwise would have flooded the built urban area.[33]

Flood-water control[edit]

Levees and other flood barriers are indispensable for cities on floodplains or along rivers and coasts. In areas with lower financial and engineering capital, there are cheaper and simpler options for flood barriers. UK engineers are currently conducting field tests of a new technology called the SELOC (Self-Erecting Low-Cost Barrier). The barrier itself lies flat on the ground, and as the water rises, the SELOC floats up, with its top edge rising with the water level. A restraint holds the barrier in the vertical position. This simple, inexpensive flood barrier has great potential for increasing urban resilience to flood events[37] and shows significant promise for developing nations with its low cost and simple, fool-proof design. The creation or expansion of flood canals and/or drainage basins can help direct excess water away from critical areas[38] and the utilisation of innovative porous paving materials on city streets and car parks allow for the absorption and filtration of excess water.[20]

During the January 2011 flood of the Brisbane River (Australia), some unique field measurements about the peak of the flood showed very substantial sediment fluxes in the Brisbane River flood plain, consistent with the murky appearance of floodwaters.[39][40] The field deployment in an inundated street of the CBD showed also some unusual features of flood flow in an urban environment linked with some local topographic effects.

Structural resilience[edit]

In most developed nations, all new developments are assessed for flood risks. The aim is to ensure flood risk is taken into account in all stages of the planning process to avoid inappropriate development in areas of high risk. When development is required in areas of high risk, structures should be built to flood-resistant standards and living or working areas should be raised well above the worst-case scenario flood levels. For existing structures in high-risk areas, funding should be allocated to i.e. raise the electrical wiring/sockets so any water that enters the home can not reach the electrics. Other solutions are to raise these structures to appropriate heights[41] or make them floating[42] or considerations should be made to relocate or rebuild structures on higher ground.

Emergency response[edit]

As with all disasters, flooding requires a specific set of disaster response plans. Various levels of contingency planning should be established, from basic medical and selective evacuation provisions involving local emergency responders right the way up to full military disaster relief plans involving air-based evacuations, search and rescue teams and relocation provisions for entire urban populations. Clear lines of responsibility and chains of command must be laid out, and tiered priority response levels should be established to address the immediate needs of the most vulnerable citizens first. For post-flooding repair and reconstruction sufficient emergency funding should be set aside proactively.[43]

Educational programs related to urban resilience[edit]

The emergence of urban resilience as an educational topic has experienced an unprecedented level of growth due in large part to a series of natural disasters including the 2004 Indian Ocean earthquake and tsunami, 2005 Hurricane Katrina, the 2011 Tohoku earthquake and tsunami, and Hurricane Sandy in 2012. Two of the more well-recognized programs are Harvard Graduate School of Design's Master's program in Risk and Resilience, and Tulane University's Disaster Resilience Leadership Academy. There are also several workshops available related to the U.S. Federal Emergency Management Agency and the Department of Homeland Security.


  1. ^ Wilbanks, T (2007). "The Research Component of the Community and Regional Resilience Initiative (CARRI)". Presentation at the Natural Hazards Center, University of Colorado-Boulder. 
  2. ^ Coaffee, J (2008). "Risk, resilience, and environmentally sustainable cities". Energy Policy 36 (12): 4635. doi:10.1016/j.enpol.2008.09.048. Retrieved May 18, 2011. 
  3. ^ Pickett, S. T. A.; Cadenasso, M. L.; et al. (2004). "Resilient cities: meaning, models, and metaphor for integrating the ecological, socio-economic, and planning realms". Landscape and Urban Planning 69 (4): 373. doi:10.1016/j.landurbplan.2003.10.035. Retrieved May 19, 2011. 
  4. ^ Mind the Risk: A global ranking of cities under threat from natural disasters
  5. ^ Dowe, M. "Urbanisation and Climate Change". Retrieved May 16, 2011. 
  6. ^ National Climatic Data Center. "Billion Dollar U.S. Weather Disasters". Retrieved May 17, 2011. 
  7. ^ Office of National Statistics. "Health Statistics Quarterly". Retrieved May 17, 2011. 
  8. ^ Robine, Jean-Marie et al. (2008). "Death toll exceeded 46,000 in Europe during the summer of 2003". Comptes Rendus Biologies 331 (2): 173. doi:10.1016/j.crvi.2007.12.001. PMID 18241810. 
  9. ^ CABE. "Integrate green infrastructure into urban areas". Retrieved May 16, 2011. 
  10. ^ Sinclair, Lulu. "Death Rate Surges in Russian Heatwave". Sky News Online HD. Retrieved May 17, 2011. 
  11. ^ Kane, S; Shogren, J. F. (2000). "Linking Adaptation and Mitigation in Climate Change Policy". Climatic Change 45 (1): 83. doi:10.1023/A:1005688900676. Retrieved May 18, 2011. 
  12. ^ Karl, T. R.; Trenberth, K. E. (2003). "Modern Global Climate Change". Science 302 (5651): 1720. doi:10.1126/science.1090228. PMID 14657489. Retrieved May 18, 2011. 
  13. ^ "London’s Urban Heat Island: A Summary for Decision Makers". Mayor of London. Retrieved May 16, 2011. 
  14. ^ Oke, T. R. (1982). "The energetic basis of the urban heat island". Quarterly Journal of the Royal Meteorological Society 108: 17. doi:10.1002/qj.49710845502. 
  15. ^ Keatinge, W. R.; Donaldson, G. C.; et al. (2000). "Heat related mortality in warm and cold regions of Europe: observational study". BMJ 321 (7262): 671. doi:10.1136/bmj.321.7262.670. PMC 27480. PMID 10987770. Retrieved May 18, 2011. 
  16. ^ Cannuscio, C.; Block, J.; et al. (2003). "Social Capital and Successful Aging: The Role of Senior Housing". Annals of Internal Medicine 139 (2): 397. doi:10.7326/0003-4819-139-5_part_2-200309021-00003. Retrieved May 16, 2011. 
  17. ^ Bernard, S. M.; McGeehin, M. A. (2004). "Municipal Heat Wave Response Plans". Am J Public Health 94 (9): 1521. doi:10.2105/AJPH.94.9.1520. PMC 1448486. PMID 15333307. Retrieved May 16, 2011. 
  18. ^ Shashua-Bar, L.; Hoffman, M. E. (2000). "Vegetation as a climatic component in the design of an urban street: An empirical model for predicting the cooling effect of urban green areas with trees". Energy and Buildings 31 (3): 229. 
  19. ^ Tidball, K.G; Krasnym first2=M.E. (2007). "From risk to resilience: What role for community greening and civic ecology in cities?". Social Learning Towards a more Sustainable World: 152. Retrieved May 18, 2001. 
  20. ^ a b "Urban Heat Island Mitigation". Environmental Protection Agency. Retrieved May 17, 2011. 
  21. ^ Weir, E. (2002). "Heat wave: first, protect the vulnerable". CMAJ 167 (2): 169. Retrieved May 19, 2011. 
  22. ^ Kovats, R. S.; Kristie, L. E. (2006). "Heatwaves and public health in Europe". The European Journal of Public Health 16 (6): 595. doi:10.1093/eurpub/ckl049. Retrieved May 17, 2011. 
  23. ^ Cheng, H.; Hu, Y.; et al. (2009). "Meeting China’s Water Shortage Crisis: Current Practices and Challenges". Environmental Science & Technology 43 (2): 242. doi:10.1021/es801934a. Retrieved May 17, 2011. 
  24. ^ Ivey, J. L.; Smithers, J.; et al. (2004). "Community Capacity for Adaptation to Climate-Induced Water Shortages: Linking Institutional Complexity and Local Actors". Environmental Management 33 (1): 41. doi:10.1007/s00267-003-0014-5. Retrieved May 19, 2011. 
  25. ^ Pimentel et al. (1997). "Water Resources: Agriculture, the Environment, and Society: an Assessment of the Status of Water Resources". American Institute of Biological Sciences 160. JSTOR 1313020. 
  26. ^ Njiru, C. (2000). "Improving urban water services: private sector participation". Proceedings of the 26th WEDC Conference. Retrieved May 18, 2011. 
  27. ^ IPCC (2001). Climate Change 2001: The Scientific Basis. Contribution of Working Group I to the Third Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge University Press. p. 881. 
  28. ^ IPCC (2007). Climate Change 2007: Impacts, Adaptation and Vulnerability. Summary for Policymakers. Contribution of Working Group II to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge University Press. 
  29. ^ Chanson, Hubert (2011). "The 2010–2011 Floods in Queensland (Australia): Observations, First Comments and Personal Experience". La Houille Blanche (Paris: Societe Hydrotechnique de France) (1): 5–11. ISSN 0018-6368. Retrieved April 22, 2011. 
  30. ^ Flather, R.A. et al. (1994). "A storm surge prediction model for the northern Bay of Bengal with application to the cyclone disaster in April 1991". American Meteorological Society. Retrieved May 20, 2011. 
  31. ^ a b c Brown, Richard; Chanson, Hubert; McIntosh, Dave; Madhani, Jay (2011). "Turbulent Velocity and Suspended Sediment Concentration Measurements in an Urban Environment of the Brisbane River Flood Plain at Gardens Point on 12–13 January 2011". Hydraulic Model Report No. CH83/11 (Brisbane, Australia: The University of Queensland, School of Civil Engineering) (CH83/11): 120 pp. ISBN 978-1-74272-027-2. 
  32. ^ Tanner, T.; Mitchell, T.; et al. (2009). "Urban Governance for Adaptation: Assessing Climate Change Resilience in Ten Asian Cities". IDS Working Papers 2009 (315): 31. doi:10.1111/j.2040-0209.2009.003152.x. 
  33. ^ a b Godschalk, D. (2003). "Urban Hazard Mitigation: Creating Resilient Cities". Natural Hazards Review 4 (3): 138. doi:10.1061/(asce)1527-6988(2003)4:3(136). Retrieved May 16, 2001. 
  34. ^ Werner, MGF; Hunter, NM; Bates, PD (2006). "Identifiability of Distributed Floodplain Roughness Values in Flood Extent Estimation". Journal of Hydrology (314): 139–157. 
  35. ^ a b Chanson, H., Brown, R., McIntosh, D. (2014). Human body stability in floodwaters: the 2011 flood in Brisbane CBD. Proceedings of the 5th IAHR International Symposium on Hydraulic Structures (ISHS2014), 25–27 June 2014, Brisbane, Australia, H. CHANSON and L. TOOMBES Editors, 9 pages (DOI: 10.14264/uql.2014.48) (ISBN 978-1-74272-115-6). doi:10.14264/uql.2014.48. ISBN 978-1-74272-115-6. 
  36. ^ Mentens, J.; Raes, D.; et al. (2006). "Green roofs as a tool for solving the rainwater runoff problem in the urbanized 21st century?". Landscape and Urban Planning 77 (3): 221. doi:10.1016/j.landurbplan.2005.02.010. Retrieved May 20, 2011. 
  37. ^ a b Nathan, S. "Urban planning engineers explore anti-flood options". Retrieved May 17, 2011. 
  38. ^ Colten, C. E.; Kates, R. W.; Laska, S. B. "Community resilience: Lessons from New Orleans and Hurricane Katrina". CARRI Research Report 3, Community and Regional Resilience Initiative. Oak Ridge National Laboratory, Oak Ridge. CiteSeerX: 
  39. ^ Richard Brown, Hubert Chanson (2012). "Suspended sediment properties and suspended sediment flux estimates in an inundated urban environment during a major flood event". Water Resources Research (USA: AGU) (48): Paper W11523, 15 pages. Bibcode:2012WRR....4811523B. doi:10.1029/2012WR012381. ISSN 0043-1397. 
  40. ^ Brown, Richard; Chanson, Hubert (2013). "Turbulence and Suspended Sediment Measurements in an Urban Environment during the Brisbane River Flood of January 2011". Journal of Hydraulic Engineering-ASCE (Reston VA, USA: ASCE) (139): 244–252. doi:10.1061/(ASCE)HY.1943-7900.0000666. ISSN 0733-9429. 
  41. ^ Carmin, J.; Roberts, I.; Anguelovski (2009). "Planning Climate Resilient Cities: Early Lessons from Early Adapters". Paper presented at the World Bank Urban Research Symposium on Climate Change: 29. Retrieved May 19, 2011. 
  42. ^ Amphibious houses
  43. ^ Coaffee, J.; D. Murakami Wood et al. (2009). The Everyday resilience of the city: how cities respond to terrorism and disaster. Basingstoke, UK: Palgrave Macmillan.