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[[File:Swales.png|500 px|thumb|alt=photos of swales|<font size=3>Photos, from left to right, of dry swale, wet swale, and step pool. Images courtesy of Limnotech.</font size>]]
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[[File:Swale terminology flowchart.png|300px|thumb|alt=flowchart for swale terminology|<font size=3>Flowchart used to determine type of swale. Click on image to enlarge.</font size>]]
  
[[File:Swale terminology flowchart.png|300px|thumb|alt=flowchart for swale terminology|<font size=3>Flowchart used to determine type of swale. Click on image to enlarge.</font size>]]
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{{alert|Swales can be an important tool for retention and detention of stormwater runoff. Depending on design and construction, swales may provide additional benefits, including cleaner air, carbon sequestration, improved biological habitat, and aesthetic value. See the section [[Green Stormwater Infrastructure (GSI) and sustainable stormwater management]].|alert-success}}
  
In the following discussion, swales are identified as filtration or infiltration practices. Swales are considered filtration practices when an underdrain is employed and infiltration practices when an underdrain is absent. Impermeable check dams may be utilized for either configuration. Engineered media is typically utilized in filtration swales and not utilized for infiltration swales.
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In the following discussion, swales are identified as [https://stormwater.pca.state.mn.us/index.php?title=Glossary#F filtration] or [https://stormwater.pca.state.mn.us/index.php?title=Glossary#I infiltration] practices. Swales are considered filtration practices when an [https://stormwater.pca.state.mn.us/index.php?title=Glossary#U underdrain] is employed and infiltration practices when an underdrain is absent. Impermeable [https://stormwater.pca.state.mn.us/index.php?title=Check_dams_for_stormwater_swales check dams] may be utilized for either configuration. [https://stormwater.pca.state.mn.us/index.php?title=Design_criteria_for_bioretention#Materials_specifications_-_filter_media Engineered media] is typically utilized in filtration swales and not utilized for infiltration swales.
  
The figure to the right provides a way to differentiate between types of swales used as stormwater BMPs. Section drawings are included on this page. For images of various swale details, [https://stormwater.pca.state.mn.us/index.php?title=CADD_images_for_individual_best_management_practices#Swales link here].
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The flowchart to the right provides a way to differentiate between types of swales used as stormwater [https://stormwater.pca.state.mn.us/index.php?title=Glossary#B best management practices] (BMPs). Section drawings are included on this page. For images of various swale details, [https://stormwater.pca.state.mn.us/index.php?title=CADD_images_for_individual_best_management_practices#Swales link here].
  
 
==Design variants==
 
==Design variants==
 
This section describes the design variants used in this manual. Other names occur in the literature but they can be fit into one of these variants, as described below.
 
This section describes the design variants used in this manual. Other names occur in the literature but they can be fit into one of these variants, as described below.
  
*wetland channel: wet swale
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*wetland channel: [[Wet swale (wetland channel)|wet swale]]
*grass swale: dry swale
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*grass swale: [https://stormwater.pca.state.mn.us/index.php?title=Dry_swale_(Grass_swale) dry swale]
 
*grass channel: dry swale
 
*grass channel: dry swale
*regenerative stormwater conveyance: step pool swale
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*regenerative stormwater conveyance: [https://stormwater.pca.state.mn.us/index.php?title=High-gradient_stormwater_step-pool_swale step pool swale]
 
*bioswale: can be used for any of the five variants discussed in this section
 
*bioswale: can be used for any of the five variants discussed in this section
 
*vegetated filter or filter strip: [[Pretreatment|pretreatment]] practices
 
*vegetated filter or filter strip: [[Pretreatment|pretreatment]] practices
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[[file:typical dry swale profile section with check dams and draintile.png|300 px|thumb|alt=swale diagrams|<font size=3>Typical dry swale profiles and sections. Diagrams include dry swales without underdrain (infiltration) and with underdrain (filtration). Click on image to enlarge.</font size>]]
 
[[file:typical dry swale profile section with check dams and draintile.png|300 px|thumb|alt=swale diagrams|<font size=3>Typical dry swale profiles and sections. Diagrams include dry swales without underdrain (infiltration) and with underdrain (filtration). Click on image to enlarge.</font size>]]
  
A dry swale without an underdrain is a relatively shallow, gently sloping, vegetated conveyance channel that prevents standing water via infiltration into in situ soils. This type of practice may be used in tandem with check dams to increase water quality volume retention. Infiltration is the dominant unit process for stormwater control.
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[[File:Step pool detail.png|300px|thumb|alt=detail step pool|<font size=3>Step pool detail.</font size>]]
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A dry swale without an underdrain is a relatively shallow, gently sloping, vegetated conveyance channel that prevents standing water via [https://stormwater.pca.state.mn.us/index.php?title=Glossary#I infiltration] into in situ soils. This type of practice may be used in tandem with check dams to increase water quality volume retention. Infiltration is the dominant unit process for stormwater control.
  
 
===Dry swales with underdrain (biofiltration)===
 
===Dry swales with underdrain (biofiltration)===
A dry swale with an underdrain is a relatively shallow, gently sloping, vegetated conveyance channel that has an engineered soil media mix and is designed with an underdrain to prevent standing water due to insufficient native soil infiltration rates. This type of practice may be used in tandem with check dams and/or impermeable liners. Filtration is the dominant unit process for stormwater control.
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A dry swale with an [https://stormwater.pca.state.mn.us/index.php?title=Glossary#U underdrain] is a relatively shallow, gently sloping, vegetated conveyance channel that has an [https://stormwater.pca.state.mn.us/index.php?title=Design_criteria_for_bioretention#Materials_specifications_-_filter_media engineered soil media mix] and is designed with an underdrain to prevent standing water due to insufficient native soil infiltration rates. This type of practice may be used in tandem with check dams and/or impermeable liners. [https://stormwater.pca.state.mn.us/index.php?title=Glossary#F Filtration] is the dominant unit process for stormwater control.
  
 
===Wet swales (biofiltration)===
 
===Wet swales (biofiltration)===
A wet swale is a relatively shallow, gently sloping, vegetated conveyance channel that holds water. A wet swale acts as a relatively long and linear shallow biofiltration treatment system, and may be used in tandem with check dams to increase water quality volume retention. Wet swales may be planted with emergent wetland plant species to improve pollutant removal. Settling and nutrient uptake by plants are the dominant unit processes for stormwater control.
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A wet swale is a relatively shallow, gently sloping, vegetated conveyance channel that holds water. A wet swale acts as a relatively long and linear shallow [https://stormwater.pca.state.mn.us/index.php?title=Bioretention_terminology biofiltration] treatment system, and may be used in tandem with [https://stormwater.pca.state.mn.us/index.php?title=Check_dams_for_stormwater_swales check dams] to increase water quality volume retention. Wet swales may be planted with [https://stormwater.pca.state.mn.us/index.php?title=Plants_for_swales emergent wetland plant species] to improve pollutant removal. Settling and nutrient uptake by plants are the dominant unit processes for stormwater control.
  
 
===Step pools with no underdrain (bioinfiltration)===
 
===Step pools with no underdrain (bioinfiltration)===
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==Specific design applications for various land uses==
 
==Specific design applications for various land uses==
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[[file:Bioretention parking lot island.jpg|thumb|300px|alt=schematic showing a bioretention parking lot island|<font size=3>A bioretention parking lot island. Note the use of other BMPs, including permeable pavement and tree trenches. (Source: [http://www.minnehahacreek.org/ Minnehaha Creek Watershed District</font size>])]]
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It should be noted that the layout of the swale area will vary according to individual sites, and to specific site constraints such as underlying soils, existing vegetation, drainage, location of utilities, sight distances for traffic, and aesthetics. Designers are encouraged to be creative in determining how to integrate swales into their respective site designs. With this in mind, the following are presented as alternative options.
 
It should be noted that the layout of the swale area will vary according to individual sites, and to specific site constraints such as underlying soils, existing vegetation, drainage, location of utilities, sight distances for traffic, and aesthetics. Designers are encouraged to be creative in determining how to integrate swales into their respective site designs. With this in mind, the following are presented as alternative options.
  
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==Additional information==
 
==Additional information==
*[http://pubs.ext.vt.edu/content/dam/pubs_ext_vt_edu/426/426-119/426-119_pdf.pdf Virginia Cooperative Extension]. Virginia Tech – Virginia State University. Urban Stormwater: Terms and Definitions.
 
 
*[[Bioretention terminology]]
 
*[[Bioretention terminology]]
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<noinclude>
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[[Category:Level 3 - Best management practices/Structural practices/Wet swale]]
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[[Category:Level 3 - Best management practices/Structural practices/Dry swale]]
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[[Category:Level 3 - Best management practices/Structural practices/Step pool]]
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</noinclude>

Latest revision as of 00:06, 31 January 2023

photos of swales
Photos, from left to right, of dry swale, wet swale, and step pool. Images courtesy of Limnotech.
flowchart for swale terminology
Flowchart used to determine type of swale. Click on image to enlarge.
Green Infrastructure: Swales can be an important tool for retention and detention of stormwater runoff. Depending on design and construction, swales may provide additional benefits, including cleaner air, carbon sequestration, improved biological habitat, and aesthetic value. See the section Green Stormwater Infrastructure (GSI) and sustainable stormwater management.

In the following discussion, swales are identified as filtration or infiltration practices. Swales are considered filtration practices when an underdrain is employed and infiltration practices when an underdrain is absent. Impermeable check dams may be utilized for either configuration. Engineered media is typically utilized in filtration swales and not utilized for infiltration swales.

The flowchart to the right provides a way to differentiate between types of swales used as stormwater best management practices (BMPs). Section drawings are included on this page. For images of various swale details, link here.

Design variants

This section describes the design variants used in this manual. Other names occur in the literature but they can be fit into one of these variants, as described below.

  • wetland channel: wet swale
  • grass swale: dry swale
  • grass channel: dry swale
  • regenerative stormwater conveyance: step pool swale
  • bioswale: can be used for any of the five variants discussed in this section
  • vegetated filter or filter strip: pretreatment practices
  • vegetated swale: can be used for pretreatment or any of the five variants discussed in this section
  • biofiltration: a swale designed for filtration (dry swale or step pool with underdrain, or wet swale)
  • bioinfiltration: a swale designed for infiltration (dry swale or step pool with no underdrain, typically having check dams)

Dry swales with no underdrain (bioinfiltration)

swale diagrams
Typical dry swale profiles and sections. Diagrams include dry swales without underdrain (infiltration) and with underdrain (filtration). Click on image to enlarge.
detail step pool
Step pool detail.

A dry swale without an underdrain is a relatively shallow, gently sloping, vegetated conveyance channel that prevents standing water via infiltration into in situ soils. This type of practice may be used in tandem with check dams to increase water quality volume retention. Infiltration is the dominant unit process for stormwater control.

Dry swales with underdrain (biofiltration)

A dry swale with an underdrain is a relatively shallow, gently sloping, vegetated conveyance channel that has an engineered soil media mix and is designed with an underdrain to prevent standing water due to insufficient native soil infiltration rates. This type of practice may be used in tandem with check dams and/or impermeable liners. Filtration is the dominant unit process for stormwater control.

Wet swales (biofiltration)

A wet swale is a relatively shallow, gently sloping, vegetated conveyance channel that holds water. A wet swale acts as a relatively long and linear shallow biofiltration treatment system, and may be used in tandem with check dams to increase water quality volume retention. Wet swales may be planted with emergent wetland plant species to improve pollutant removal. Settling and nutrient uptake by plants are the dominant unit processes for stormwater control.

Step pools with no underdrain (bioinfiltration)

A step pool with no underdrain is a type of conveyance channel used in areas with steep terrain that uses a series of pools, conveyance channels, and checks to slow down water and increase infiltration into in situ soils. A step pool with no underdrain is similar to a dry swale with no underdrain, with the main difference being the step pool is employed on relatively steep longitudinal slopes. Infiltration is the dominant unit process for stormwater control.

Step pools with underdrain (biofiltration)

A step pool with an underdrain is a type of vegetated conveyance channel used in areas with steep terrain that uses a series of pools, conveyance channels, and checks to slow down water and is designed with an underdrain to prevent standing water due to insufficient native soil infiltration rates. A step pool with an underdrain is similar to a dry swale with an underdrain, with the main difference being the step pool is employed on relatively steep longitudinal slopes. Filtration is the dominant unit process for stormwater control.

Specific design applications for various land uses

schematic showing a bioretention parking lot island
A bioretention parking lot island. Note the use of other BMPs, including permeable pavement and tree trenches. (Source: Minnehaha Creek Watershed District)

It should be noted that the layout of the swale area will vary according to individual sites, and to specific site constraints such as underlying soils, existing vegetation, drainage, location of utilities, sight distances for traffic, and aesthetics. Designers are encouraged to be creative in determining how to integrate swales into their respective site designs. With this in mind, the following are presented as alternative options.

On-lot systems

On-lot systems are designed to receive flows from gutters, and/or other impervious surfaces. These applications of swales tend to be simpler in design and relatively smaller in size.

Parking lot islands (curbless)

In a paved area with no curb, pre-cast car-stops or a “ribbon curb” can be installed along the pavement perimeter to protect the swale area. This application of swale should only be attempted where shallow grades allow for sheet flow conditions over level entrance areas. Water may be pooled into the parking area where parking spaces are rarely used to achieve an element of stormwater quantity control beyond the confines of the swale surface area.

Parking lot islands (curb-cut)

For curb-cut entrance approaches, the water is diverted into the swale through the use of an inlet deflector block, which has ridges that channel the runoff into the swale. Special attention to erosion control and pre-treatment should be given to the concentrated flow produced by curb-cuts.

Road medians and traffic islands

A multifunctional landscape can be created by utilizing road medians and islands for swales. There is no minimum width recommended for traffic islands from street edge to edge. A buffer may be necessary along the outside curb perimeter to minimize the possibility of drainage seeping under the pavement section, and creating “frost heave” during winter months. Alternately, the installation of a geotextile filter fabric “curtain wall” along the perimeter of the swale will accomplish the same effect.

Additional information

This page was last edited on 31 January 2023, at 00:06.