Stormwater is water that originates during precipitation events. It may also be used to apply to water that originates with snowmelt that enters the stormwater system. Stormwater that does not soak into the ground becomes surface runoff, which either flows directly into surface waterways or is channeled into storm sewers, which eventually discharge to surface waters.
Stormwater is of concern for two main issues: one related to the volume and timing of runoff water (flooding) and the other related to potential contaminants that the water is carrying, i.e. water pollution.
Stormwater is also a resource and ever growing in importance as the world's human population demand exceeds the availability of readily available water. Techniques of stormwater harvesting with point source water management and purification can potentially make urban environments self-sustaining in terms of water.
- 1 History
- 2 Stormwater pollution
- 3 Stormwater runoff as a source of pollution
- 4 Urban flooding
- 5 Stormwater management
- 6 Integrated water management
- 7 Regulation in the United States
- 8 Public education campaigns
- 9 See also
- 10 References
- 11 Further reading
- 12 External links
Since humans began living in concentrated village or urban settings, stormwater runoff has been an issue. During the Bronze Age, housing took a more concentrated form, and impervious surfaces emerged as a factor in the design of early human settlements. Some of the early incorporation of stormwater engineering is evidenced in ancient Greece.
Because impervious surfaces (parking lots, roads, buildings, compacted soil) do not allow rain to infiltrate into the ground, more runoff is generated than in the undeveloped condition. This additional runoff can erode watercourses (streams and rivers) as well as cause flooding after the stormwater collection system is overwhelmed by the additional flow. Because the water is flushed out of the watershed during the storm event, little infiltrates the soil, replenishes groundwater, or supplies stream baseflow in dry weather.
A first flush is the initial runoff of a rainstorm. During this phase, polluted water entering storm drains in areas with high proportions of impervious surfaces is typically more concentrated compared to the remainder of the storm. Consequently these high concentrations of urban runoff result in high levels of pollutants discharged from storm sewers to surface waters.:216
Pollutants entering surface waters during precipitation events is termed polluted runoff. Daily human activities result in deposition of pollutants on roads, lawns, roofs, farm fields, etc. When it rains or there is irrigation, water runs off and ultimately makes its way to a river, lake, or the ocean. While there is some attenuation of these pollutants before entering the receiving waters, the quantity of human activity results in large enough quantities of pollutants to impair these receiving waters.
Stormwater runoff as a source of pollution
In addition to the pollutants carried in stormwater runoff, urban runoff is being recognized as a cause of pollution in its own right. In natural catchments (watersheds) surface runoff entering waterways is a relatively rare event, occurring only a few times each year and generally after larger storm events. Before development occurred most rainfall soaked into the ground and contributed to groundwater recharge or was recycled into the atmosphere by vegetation through evapotranspiration .
Modern drainage systems which collect runoff from impervious surfaces (e.g., roofs and roads) ensure that water is efficiently conveyed to waterways through pipe networks, meaning that even small storm events result in increased waterway flows.
In addition to delivering higher pollutants from the urban catchment, increased stormwater flow can lead to stream erosion, encourage weed invasion, and alter natural flow regimes. Native species often rely on such flow regimes for spawning, juvenile development, and migration.
In some areas, especially along the U.S. coast, polluted runoff from roads and highways may be the largest source of water pollution. For example, about 75 percent of the toxic chemicals getting to Seattle, Washington's Puget Sound are carried by stormwater that runs off paved roads and driveways, rooftops, yards, and other developed land.
More recently, stormwater is being recognized as a major cause of urban flooding. Urban flooding is the inundation of land or property in a built-up environment caused by stormwater overwhelming the capacity of drainage systems, such as storm sewers. Although triggered by single events such as flash flooding or snow melt, urban flooding is a condition, characterized by its repetitive, costly and systemic impacts on communities.
Where properties are built with basements, urban flooding is the primary cause of basement and sewer backups. Although the number of casualties from urban flooding is usually limited, the economic, social and environmental consequences can be considerable: in addition to direct damage to property and infrastructure (highways, utilities and services), chronically wet houses are linked to an increase in respiratory problems and other illnesses.
Urban flooding has significant economic implications. In the U.S., industry experts estimate that wet basements can lower property values by 10-25 percent and are cited among the top reasons for not purchasing a home. According to the U.S Federal Emergency Management Agency (FEMA) almost 40 percent of small businesses never reopen their doors following a flooding disaster. In the UK, urban flooding is estimated to cost £270 million a year in England and Wales; 80,000 homes are at risk.
A study of Cook County, Illinois, identified 177,000 property damage insurance claims made across 96 percent of the county’s ZIP codes over a five-year period from 2007-2011. This is the equivalent of one in six properties in the County making a claim. Average payouts per claim were $3,733 across all types of claims, with total claims amounting to $660 million over the five years examined.
Managing the quantity and quality of stormwater is termed, "Stormwater Management." The term Best Management Practice (BMP) is often used to refer to both structural or engineered control devices and systems (e.g. retention ponds) to treat or store polluted stormwater, as well as operational or procedural practices. Stormwater management includes both technical and institutional aspects, including:
- control of flooding and erosion;
- control of hazardous materials to prevent release of pollutants into the environment (source control);
- planning and construction of stormwater systems so contaminants are removed before they pollute surface waters or groundwater resources;
- acquisition and protection of natural waterways or rehabilitation;
- building "soft" structures such as ponds, swales or wetlands or Green Infrastructure solutions to work with existing or "hard" drainage structures, such as pipes and concrete channels;
- development of funding approaches to stormwater programs potentially including stormwater user fees and the creation of a stormwater utility;
- development of long-term asset management programs to repair and replace aging infrastructure;
- revision of current stormwater regulations to address comprehensive stormwater needs;
- enhancement and enforcement of existing ordinances to make sure property owners consider the effects of stormwater before, during and after development of their land;
- education of a community about how its actions affect water quality, and about what it can do to improve water quality; and
- planning carefully to create solutions before problems become too great.
Integrated water management
Integrated water management (IWM) of stormwater has the potential to address many of the issues affecting the health of waterways and water supply challenges facing the modern urban city.
Also known as low impact development (LID) in the United States, or Water Sensitive Urban Design (WSUD) in Australia, IWM has the potential to improve runoff quality, reduce the risk and impact of flooding and deliver an additional water resource to augment potable supply.
The development of the modern city often results in increased demands for water supply due to population growth, while at the same time altered runoff predicted by climate change has the potential to increase the volume of stormwater that can contribute to drainage and flooding problems. IWM offers several techniques including stormwater harvest (to reduce the amount of water that can cause flooding), infiltration (to restore the natural recharge of groundwater), biofiltration or bioretention (e.g., rain gardens) to store and treat runoff and release it at a controlled rate to reduce impact on streams and wetland treatments (to store and control runoff rates and provide habitat in urban areas).
There are many ways of achieving LID. The most popular is to incorporate land-based solutions to reduce stormwater runoff through the use of retention ponds, bioswales, infiltration trenches, sustainable pavements (such as permeable paving), and others noted above. LID can also be achieved by utilizing engineered, manufactured products to achieve similar, or potentially better, results as land-based systems (underground storage tanks, stormwater treatment systems, biofilters, etc.). The proper LID solution is one that balances the desired results (controlling runoff and pollution) with the associated costs (loss of usable land for land-based systems versus capital cost of manufactured solution). Green (vegetated) roofs are also another low cost solution.
IWM as a movement can be regarded as being in its infancy and brings together elements of drainage science, ecology and a realization that traditional drainage solutions transfer problems further downstream to the detriment of our environment and precious water resources.
Regulation in the United States
In the United States, the Environmental Protection Agency (EPA) is charged with regulating stormwater pursuant to the Clean Water Act (CWA). The goal of the CWA is to restore all "Waters of the United States" to their "fishable" and "swimmable" conditions. Point source discharges, which originate mostly from municipal wastewater (sewage) and industrial wastewater discharges, have been regulated since enactment of the CWA in 1972. Pollutant loadings from these sources are tightly controlled and limited. However, despite these controls, thousands of water bodies in the U.S. remain classified as "impaired," meaning that they contain pollutants at levels higher than is considered safe by EPA for the intended beneficial use of the water. Much of this impairment is due to polluted runoff.
Under the CWA, point source discharges to "Waters of the United States" require National Pollution Discharge Elimination System (NPDES) permits. To address the nationwide problem of stormwater pollution, Congress broadened the CWA definition of "point source" in 1987 to include industrial stormwater discharges and municipal separate storm sewer systems ("MS4"). These facilities were required to obtain NPDES permits. This 1987 expansion was promulgated in two phases: Phase I and Phase II. Phase I required that all municipalities of 100,000 persons or more, industrial dischargers, and construction sites of 5 acres (20,000 m2) or more have NPDES permits for their stormwater discharges. Phase I permits were issued in much of the U.S. in 1991. Phase II required that all municipalities, industrial dischargers, construction sites of 1 acre (4,000 m2) or more, and other large property owners (such as school districts) have NPDES permits for their stormwater discharges. Phase II rules came into effect in 2003.
EPA issued a new Construction General Permit (CGP) in July 2008. This permit expires in 2011 and continues the provisions of the previous permit. In December 2009 EPA issued new discharge standards, called effluent guidelines, for construction sites. These requirements set a new national minimum standard for erosion controls and sediment controls, and pollution prevention measures. The effluent guideline provisions will be incorporated into the next round of EPA and state general permits.
State and local requirements
EPA has authorized 46 states to issue NPDES permits. In addition to implementing the NPDES requirements, many states and local governments have enacted their own stormwater management laws and ordinances, and some have published stormwater treatment design manuals. Some of these state and local requirements have expanded coverage beyond the federal requirements. For example, the State of Maryland requires erosion and sediment controls on construction sites of 5,000 sq ft (460 m2) or more. It is not uncommon for state agencies to revise their requirements and impose them upon counties and cities; daily fines ranging as high as $25,000 can be imposed for failure to modify their local stormwater permitting for construction sites, for instance.
Nonpoint source pollution management
Agricultural runoff (except for concentrated animal feeding operations, or "CAFO") is considered by the CWA to be nonpoint source pollution. It is not included in the CWA definition of "point source" and therefore not subject to NPDES permit requirements. The 1987 CWA amendments established a non-regulatory program at EPA for nonpoint source pollution management consisting of research and demonstration projects. Related programs are conducted by the Natural Resources Conservation Service (NRCS) in the U.S. Department of Agriculture.
Public education campaigns
Education is a key component of stormwater management. A number of agencies and organizations have launched campaigns to teach the public about stormwater pollution, and how they can contribute to solving it. Thousands of local governments in the U.S. have developed education programs as required by their NPDES stormwater permits.
One example of a local educational program is that of the West Michigan Environmental Action Council (WMEAC), which has coined the term Hydrofilth to describe stormwater pollution, as part of its "15 to the River" campaign. (During a rain storm, it may take only 15 minutes for contaminated runoff in Grand Rapids, Michigan to reach the Grand River.) Its outreach activities include a rain barrel distribution program and materials for homeowners on installing rain gardens.
- Trimble, Stanley W. (2007). Encyclopedia of Water Science. Boca Raton, FL: CRC Press. ISBN 0-8493-9627-1.
- C. Michael Hogan, "Phaistos Fieldnotes." The Modern Antiquarian (2007).
- Schueler, Thomas R. "The Importance of Imperviousness." Reprinted in The Practice of Watershed Protection. 2000. Center for Watershed Protection, Ellicott City, MD.
- Metcalf, Leonard; Eddy, Harrison P. (1916). American Sewerage Practice: Disposal of Sewage III. New York: McGraw-Hill. p. 154.
- Alex Maestre and Robert Pitt; Center for Watershed Protection (2005)."The National Stormwater Quality Database, Version 1.1: A Compilation and Analysis of NPDES Stormwater Monitoring Information." Report prepared for U.S. Environmental Protection Agency, Washington, DC. September 4, 2005.
- Washington State Department of Ecology. “Control of Toxic Chemicals in Puget Sound, Phase 2: Development of Simple Numerical Models", 2008
- Indoor Air Quality (IAQ) Scientific Findings Resource Bank (IAQ-SFRB), “Health Risks or Dampness or Mold in Houses” http://www.iaqscience.lbl.gov/dampness-risks-house.html
- The Prevalence and Cost of Urban Flooding. Chicago: Center for Neighborhood Technology, 2013. http://www.cnt.org/media/CNT_PrevalenceAndCostOfUrbanFlooding.pdf
- “Protecting Your Businesses,” last updated March, 2013 http://www.fema.gov/protecting-yourbusinesses
- Parliamentary Office of Science and Technology, London, UK. “Urban Flooding.” Postnote 289, July 2007 http://www.parliament.uk/documents/post/postpn289.pdf
- The Prevalence and Cost of Urban Flooding. Rep. Chicago: Center for Neighborhood Technology, 2013 http://www.cnt.org/media/CNT_PrevalenceAndCostOfUrbanFlooding.pdf
- Washington State Department of Ecology (2005). Olympia, WA. "Stormwater Management Manual for Western Washington." Publication No. 05-10-029.
- Debo, Tom; Reese, Andrew (2003). "Chapter 2. Stormwater Management Programs". Municipal Stormwater Management. Boca Raton, FL: CRC Press. ISBN 1-56670-584-3.
- Prince George's County, Maryand. Department of Environmental Resources (PGDER). Larry Coffman et al. (1999). Low-Impact Development Design Strategies, An Integrated Design Approach. Published by U.S. Environmental Protection Agency, Washington, D.C. Document No. EPA 841-B-00-003, June 1999.
- "Water Sensitive Urban Design - Melbourne Water". Wsud.melbournewater.com.au. Retrieved 2011-12-05.
- Federal Water Pollution Control Amendments of 1972, P.L. 92-500.
- Water Quality Act of 1987, P.L. 100-4. Added CWA section 402(p), 33 U.S.C. § 1342(p).
- U.S. Environmental Protection Agency (EPA). Washington, DC. "Construction General Permit". Accessed 2013-08-26.
- EPA (2013). "Amendments to Effluent Limitations Guidelines and Standards for the Construction and Development Point Source Category."
- EPA (June 2009). "EPA Unveils Watershed Central." Nonpoint Source News-Notes. #87. 1-3.
- EPA (2008). "NPDES State Program Status." Accessed 2010-02-10.
- Maryland Department of the Environment (2009). Baltimore, MD. "Maryland Stormwater Design Manual."
- State of Maryland. Code of Maryland Regulations (COMAR). Activities for Which Approved Erosion and Sediment Control Plans are Required. Sec. 26.17.01.05.
- EPA (2013). "Stormwater Discharges From Municipal Separate Storm Sewer Systems."
- West Michigan Environmental Action Council (WMEAC), Grand Rapids, MI. "Stop Hydrofilth." Accessed 2013-08-26.
- WMEAC. "15 to the River" Accessed 2013-08-26.
- WMEAC. "Rain Gardens... beautiful solutions for water pollution." Accessed 2013-08-26.
- Stormwater at the Open Directory Project
- EPA Stormwater Permit Program
- Stormwater Magazine - a stormwater trade journal
- Storm Water Solutions magazine - stormwater trade publication
- International Stormwater Best Management Practices (BMP) Database
- Minnesota Stormwater Manual (cold weather stormwater management)