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Sustainable drainage system

From Wikipedia, the free encyclopedia

Retention ponds such as this one in Dunfermline, Scotland are considered components of a sustainable drainage system.
Retention ponds such as this one in Dunfermline, Scotland are considered components of a sustainable drainage system.

Sustainable drainage systems (also known as SuDS,[1] SUDS,[2][3] or sustainable urban drainage systems[4]) are a collection of water management practices that aim to align modern drainage systems with natural water processes.[5] SuDS efforts make urban drainage systems more compatible with components of the natural water cycle such as storm surge overflows, soil percolation, and bio-filtration. These efforts hope to mitigate the effect human development has had or may have on the natural water cycle, particularly surface runoff and water pollution trends.[6] SuDS have become popular in recent decades as our understanding of how urban development affects natural environments, as well as concern for climate change and sustainability, have increased. SuDS often use built components that mimic natural features in order to integrate urban drainage systems into the natural drainage systems or a site as efficiently and quickly as possible. SUDS infrastructure has become a large part of the Blue-Green Cities demonstration project in Newcastle-upon-Tyne.[7]

History of drainage systems

Drainage systems have been found in ancient cities over 5,000 years old, including Minoan, Indus, Persian, and Mesopotamian civilizations.[8] These drainage systems focused mostly on reducing nuisances from localized flooding and waste water. Rudimentary systems made from brick or stone channels constituted the extent of urban drainage technologies for centuries. Cities in Ancient Rome also employed drainage systems to protect low-lying areas from excess rainfall. When builders began constructing aqueducts to import fresh water into cities, urban drainage systems became integrated into water supply infrastructure for the first time as a unified urban water cycle.[9]

London Sewage system being built in 1860
London Sewage system being built in 1860

Modern drainage systems did not appear until the 19th century in Western Europe, although most of these systems were primarily built to deal with sewage issues rising from rapid urbanization. One such example is that of the London sewerage system, which was constructed to combat massive contamination of the River Thames. At the time, the River Thames was the primary component of London's drainage system, with human waste concentrating in the waters adjacent to the densely populated urban center. As a result, several epidemics plagued London's residents and even members of Parliament, including events known as the 1854 Broad Street cholera outbreak and the Great Stink of 1858.[10] The concern for public health and quality of life launched several initiatives, which ultimately led to the creation of London's modern sewerage system designed by Joseph Bazalgette.[11] This new system explicitly aimed to ensure waste water was redirected as far away from water supply sources as possible in order to reduce the threat of waterborne pathogens. Since then, most urban drainage systems have aimed for similar goals of preventing public health crises.

Within past decades, as climate change and urban flooding have become increasingly urgent challenges, drainage systems designed specifically for environmental sustainability have become more popular in both academia and practice. The first sustainable drainage system to utilize a full management train including source control in the UK was the Oxford services motorway station designed by SuDS specialists Robert Bray Associates[12] Originally the term SUDS described the UK approach to sustainable urban drainage systems. These developments may not necessarily be in "urban" areas, and thus the "urban" part of SuDS is now usually dropped to reduce confusion. Other countries have similar approaches in place using a different terminology such as best management practice (BMP) and low-impact development in the United States,[13] water-sensitive urban design (WSUD) in Australia,[14] low impact urban design and development (LIUDD) in New Zealand,[15] and comprehensive urban river basin management in Japan.[14]


Traditional urban drainage systems are limited by various factors including volume capacity, damage or blockage from debris and contamination of drinking water. Many of these issues are addressed by SuDS systems by bypassing traditional drainage systems altogether and returning rainwater to natural water sources or streams as soon as possible. Increasing urbanisation has caused problems with increased flash flooding after sudden rain. As areas of vegetation are replaced by concrete, asphalt, or roofed structures, leading to impervious surfaces, the area loses its ability to absorb rainwater. This rain is instead directed into surface water drainage systems, often overloading them and causing floods.

The goal of all sustainable drainage systems is to use rainfall to recharge the water sources of a given site. These water sources are often underlying the water table, nearby streams, lakes, or other similar freshwater sources. For example, if a site is above an unconsolidated aquifer, then SuDS will aim to direct all rain that falls on the surface layer into the underground aquifer as quickly as possible. To accomplish this, SuDS use various forms of permeable layers to ensure the water is not captured or redirected to another location. Often these layers include soil and vegetation, though they can also be artificial materials.

The paradigm of SuDS solutions should be that of a system that is easy to manage, requiring little or no energy input (except from environmental sources such as sunlight, etc.), resilient to use, and being environmentally as well as aesthetically attractive. Examples of this type of system are basins (shallow landscape depressions that are dry most of the time when it's not raining), rain gardens (shallow landscape depressions with shrub or herbaceous planting), swales (shallow normally-dry, wide-based ditches), filter drains (gravel filled trench drain), bioretention basins (shallow depressions with gravel and/or sand filtration layers beneath the growing medium), reed beds and other wetland habitats that collect, store, and filter dirty water along with providing a habitat for wildlife.

A common misconception of SuDS is that they reduce flooding on the development site. In fact the SuDS is designed to reduce the impact that the surface water drainage system of one site has on other sites. For instance, sewer flooding is a problem in many places. Paving or building over land can result in flash flooding. This happens when flows entering a sewer exceed its capacity and it overflows. The SuDS system aims to minimise or eliminate discharges from the site, thus reducing the impact, the idea being that if all development sites incorporated SuDS then urban sewer flooding would be less of a problem. Unlike traditional urban stormwater drainage systems, SuDS can also help to protect and enhance ground water quality.

Examples of SuDS

Because SuDS describe a collection of systems with similar components or goals, there is a large crossover between SuDS and other terminologies dealing with sustainable urban development.[16] The following are examples generally accepted as components in a SuDS system:

Roadside bioswale designed to filter storm water runoff from street surfaces
Roadside bioswale designed to filter storm water runoff from street surfaces


A bioswale is a shallow depression in a piece of land meant to gather and filter stormwater runoff by directing polluted rainwater through soil and vegetation. Besides the environmental benefits bioswales provide, they are commonly used in public spaces due to their aesthetic qualities and generally low difficulty of installation and maintenance.[17] Bioswales are designed linearly and slightly sloped in order to drain water throughout its components and into the soil as opposed to simply collecting it in a standing location.[18] Although bioswales provide passive means to filter runoff indefinitely, they are limited by their momentary capacity for runoff volume. As such, they can be easily flooded over if rainfall events, adjacent surfaces, and soil characteristics are not adequately considered.

Bioswales are found in various settings across the globe, particularly in densely built urban areas with paved streets. In Nashville, Tennessee, a renovation of historic Deaderick Street near the city center included bioswales meant to filter runoff from the street surfaces. Its developers claim that the intervention has reduced the amount of runoff entering Nashville's sewer system by over 1.2 million gallons annually.[19]

Permeable pavement

Permeable pavement systems aim to provide a manner for water that falls on hardscaping to seep through to the soil below. This is accomplished by either dividing traditional pavement materials into sections, or using a porous pavement material.

In China, paved urban areas have grown rapidly since the 2000s, with dozens of cities supporting populations over one million. In response, the Chinese government has commissioned the design of several "sponge cities" which employ SuDS at urban scales throughout the country.[20] One such example is Nanhui, a Shanghai suburb designed to combat rising sea levels on China’s eastern coast. Nanhui, previously known as Lingang, uses permeable pavement for roads and public right-of-ways to reduce the effects large urban infrastructure has on the natural water cycle.[21] It is the organic combination of modern green new technology and society, environment, human culture for social progress.[22]


Artificial wetlands can be constructed in areas that see large volumes of storm water surges or runoff. Built to replicate shallow marshes, wetlands as BMPs gather and filter water at scales larger than bioswales or rain gardens. Unlike bioswales, artificial wetlands are designed to replicate natural wetlands processes as opposed to having an engineered mechanism within the artificial wetland. Because of this, the ecology of the wetland (soil components, water, vegetation, microbes, sunlight processes, etc.) becomes the primary system to remove pollutants.[23] Water in an artificial wetland tends to be filtered slowly in comparison to systems with mechanized or explicitly engineered components.

Wetlands can be used to concentrate large volumes of runoff from urban areas and neighborhoods. In 2012, the South Los Angeles Wetlands Park was constructed in a densely populated inner-city district as a renovation for a former LA Metro bus yard. The park is designed to capture runoff from surrounding surfaces as well as storm water overflow from the city's current drainage system.[24]

Trounce Pond in Saskatoon, Canada serves as a storm water detention basin within the local drainage system.
Trounce Pond in Saskatoon, Canada serves as a storm water detention basin within the local drainage system.

Detention basins

Detention basins (or retention basins) are storm water detention areas meant to offset excess water that could overrun the capacity of the current filtration or drainage systems. Detention basins reduce peak discharge into drainage systems by methods including slowing runoff velocity, holding excess volume, and trapping sediment that could disrupt drainage systems downstream. Basins can be either wet or dry, depending on whether the default state of the basin is filled with water or only anticipates it during storm surges.

Xang Thoi Pond in Cần Thơ, Vietnam, is an example of urban retrofitting to reduce flooding through detention basins. Cần Thơ, a large city on the Mekong Delta, is susceptible to seasonal floods and intense rainfall. In response, the local government included urban flooding solutions as part of a wider national infrastructural initiative.[25]

Green roof

Green roofs are landscaped or vegetated areas on the roofs of buildings, usually built to mimic natural landscaping or ground-level parks. Green roofs help drainage systems by offsetting peak discharge from otherwise hardscape surfaces, and filtering rainwater directly as it falls. They also have the added advantage of reducing energy consumption for buildings that would otherwise be receiving direct sunlight onto their roofs throughout the day.[26]

As part of the 2015 United Nations Climate Change Conference, Argentina agreed to reduce greenhouse gas emissions as part of a global effort to combat climate change. Consequentially, many of Argentina's cities have passed resolutions requiring or encouraging new developments to implement green roofs. In Buenos Aires, the city government provides tax reductions to developments that incorporate green roofs along with other LEED criteria.

See also


  1. ^ Sustainable Drainage System (SuDs) for Stormwater Management: A Technological and Policy Intervention to Combat Diffuse Pollution, Sharma, D., 2008
  2. ^ "CIRIA guide to SUDS". Retrieved 2014-01-21.
  3. ^ Scottish Government. Planning Services (2001). "Planning and Sustainable Urban Drainage Systems." Planning Advice Note 61. 2001-07-27.
  4. ^ "Sustainable Urban Drainage Systems". Retrieved 2020-11-15.
  5. ^ CIRIA SuDS Manual (Document reference : CIRIA C753), 2015
  6. ^ Hoang, L (2016). "System interactions of stormwater management using sustainable urban drainage systems and green infrastructure". Urban Water Journal. 13 (7): 739–758. doi:10.1080/1573062X.2015.1036083.
  7. ^ O’Donnell, E. C.; Lamond, J. E.; Thorne, C. R. (2017). "Recognising barriers to implementation of Blue-Green Infrastructure: a Newcastle case study". Urban Water Journal. 14 (9): 964–971. doi:10.1080/1573062X.2017.1279190. ISSN 1573-062X.
  8. ^ Angelakis, Andreas; De Feo, Giovanni; Laureano, Pietro; Zourou, Anastasia (2013-07-08). "Minoan and Etruscan Hydro-Technologies". Water. 5 (3): 972–987. doi:10.3390/w5030972. ISSN 2073-4441.
  9. ^ Burian Steven J.; Edwards Findlay G. (2002). "Historical Perspectives of Urban Drainage". Global Solutions for Urban Drainage. Proceedings: 1–16. doi:10.1061/40644(2002)284. ISBN 978-0-7844-0644-1.
  10. ^ "Re-Smelling London's Great Stink Of 1858". All That's Interesting. 2017-12-07. Retrieved 2019-04-21.
  11. ^ "BBC - History - Joseph Bazalgette". Retrieved 2019-04-21.
  12. ^ CIRIA Oxford Motorway Services Case Study
  13. ^ "Reducing Stormwater Costs through Low Impact Development Strategies and Practices". Fact Sheet. Washington, D.C.: U.S. Environmental Protection Agency (EPA). December 2007. EPA 841/F-07/006A.
  14. ^ a b Chen, Chi-Feng; Sheng, Ming-Yang; Chang, Chia-Ling; Kang, Shyh-Fang; Lin, Jen-Yang (2014). "Application of the SUSTAIN Model to a Watershed-Scale Case for Water Quality Management". Water. 6 (12): 3575–3589. doi:10.3390/w6123575. ISSN 2073-4441.
  15. ^ Eckart, Kyle; McPhee, Zach; Bolisetti, Tirupati (2017). "Performance and implementation of low impact development – A review". Science of the Total Environment. 607–608: 413–432. Bibcode:2017ScTEn.607..413E. doi:10.1016/j.scitotenv.2017.06.254. PMID 28704668.
  16. ^ Campos, Priscila Celebrini de Oliveira; Paz, Tainá da Silva Rocha; Lenz, Letícia; Qiu, Yangzi; Alves, Camila Nascimento; Simoni, Ana Paula Roem; Amorim, José Carlos Cesar; Lima, Gilson Brito Alves; Rangel, Maysa Pontes; Paz, Igor (2020). "Multi-Criteria Decision Method for Sustainable Watercourse Management in Urban Areas". Sustainability. 12 (16): 6493. doi:10.3390/su12166493.
  17. ^ "Bioswales". 2013-11-10. Retrieved 2019-04-21.
  18. ^ "Bioswales". National Association of City Transportation Officials. 2013-07-11. Retrieved 2019-04-21.
  19. ^ "reStreets". Retrieved 2019-04-21.
  20. ^ Li Xiaoning; Li Junqi; Fang Xing; Gong Yongwei; Wang Wenliang (2016). "Case Studies of the Sponge City Program in China". World Environmental and Water Resources Congress 2016. Proceedings: 295–308. doi:10.1061/9780784479858.031. ISBN 9780784479858.
  21. ^ Roxburgh, Helen (27 Dec 2017). "China's 'sponge cities' are turning streets green to combat flooding". The Guardian.
  22. ^ Bao-jie He, JinZhu, Dong-Xue Zhao, Zhong-Hua Gou, Jin-Da Qi, Junsong Wang (2019). "Co-benefits approach Opportunities for implementing sponge city and urban heat island mitigation/amp". Land Use Policy. 86: 147–157. doi:10.1016/j.landusepol.2019.05.003.
  23. ^ Constructed wetlands. Kandasamy, Jaya., Vigneswaran, Saravanamuthu, 1952-. New York: Nova Science Publishers. 2008. ISBN 9781616680817. OCLC 847617134.CS1 maint: others (link)
  24. ^ Fuentes, Ed (2012-02-14). "Innovative Wetlands Park Opens in South Los Angeles". KCET. Retrieved 2019-04-21.
  25. ^ "Urban retention basin in developing city: from theoretical effectiveness to practical feasibility". ResearchGate. Retrieved 2019-04-21.
  26. ^ Friedman, Avi, 1952- (2012). Fundamentals of sustainable dwellings. Washington, DC: Island Press. ISBN 9781610912112. OCLC 785911199.CS1 maint: multiple names: authors list (link)

External links

This page was last edited on 12 February 2021, at 06:22
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