Difference between revisions of "Swales"

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===Design===
 
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The objective of these design recommendations are to maximize the distribution of ponded water along the whole BMP. Detailed design may require iteration of the dam heights and distances along each section of a long swale. </p>
 
The objective of these design recommendations are to maximize the distribution of ponded water along the whole BMP. Detailed design may require iteration of the dam heights and distances along each section of a long swale. </p>
 
*Dams may be constructed of any resilient and waterproof material, including: rock gabions, earth berms, coarse aggregate or rip-rap, concrete, metal or wood.  
 
*Dams may be constructed of any resilient and waterproof material, including: rock gabions, earth berms, coarse aggregate or rip-rap, concrete, metal or wood.  
*Energy dissipation and erosion control measures should be installed in the 1 - 2 m  downstream of each dam. Examples include large aggregate or <h4>Other components</h4>
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*Energy dissipation and erosion control measures should be installed in the 1 - 2 m  downstream of each dam. Examples include large aggregate or [[Turf reinforcement|turf reinforcement]]
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<li>[[Underdrain]]</li>
 
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<li>[[Biomedia]]</li>
 
<li>[[Biomedia]]</li>
<li>[[Turf reinforcement|turf reinforcement]]</li>
 
 
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Revision as of 19:52, 11 July 2017

This article is about installations designed to capture and convey surface runoff along a vegetated channel.

Overview[edit]

Swales are linear landscape features consisting of a drainage channel with gently sloping sides. Underground they may be filled with engineered soil and/or contain a water storage layer of coarse gravel material. Two variations on a basic swale are recommended as low impact development strategies, although using a combination design of both may increase the benefits:
Bioswales are sometimes referred to as 'dry swales', 'vegetated swales', 'water quality swales' or 'inline bioretention'. This type of structure is similar to a bioretention cell but with a long linear shape (surface area typically >2:1 length:width )
Enhanced Grass Swales are a lower maintenance alternative, but generally have lower stormwater management potential. The enhancement over a basic grass swale is in the addition of check dams to slow surface water flow and create small temporary pools of water which can infiltrate the underlying soil.

Swales are an ideal technology for:

  • Sites with long linear landscaped areas, such as parking lots
  • Connecting with one or more other types of LID
Types of Swales
PropertyBioswaleEnhanced Grass Swale
Surface waterMinimal
Any surface flow can be slowed with check dams
Ponding is encouraged with check dams
Engineered soilBiomedia requiredAmendment preferable when possible
UnderdrainCommonUncommon
MaintenanceMedium to highLow
Stormwater benefitHighMedium
Biodiversity benefitIncreased with native plantingLower

The fundamental components of a swale are:

  • Graded channel
  • Planting

Additional components may include:

  • Biomedia - an engineered soil mix
  • Underdrain with clean out and inspection ports
  • Impermeable membrane to prevent infiltration to soils below
  • Check dams

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Planning Considerations[edit]

  • Although linear design (surface area typically >2:1 length:width) is a feature of a swale, an absolute minimum width is 0.6 m is required for bioswales to have healthy plant growth, and to facilitate construction.
  • Grassed swales are usually mown as part of routine maintenance, so the cross section will be parabolic or trapzoidal in shape. The minimum width for this type is 2 m.
  • Swales may be graded along longitudinal slopes between 0.5 - 6 %.
    • Check dams are required on slopes > 3 %.
    • Slopes > 6% can accommodate a series of stepped bioretention cells, each overflowing with a weir, into the next.

    Design[edit]

    Pre-treatment and inlets

    For more detail see article on Pre-treatment and inlets

    To minimize erosion and maximize the functionality of the swale, sheet flow of surface water should be directed into the side of the BMP. Vegetated filter strips and shallow side slopes are ideal. Alternatively, a series of curb inlets can be employed, where each has some form of flow spreading incorporated. Single point inflow can cause increased erosion and sedimentation which will damage vegetation and contribute to BMP failure. Again, flow spreading devices can mitigate these processes, where concentrated point inflow is required.

    Check dams

    Check dams are a feature of enhanced swales. They promote infiltration and evaporation by promoting limited ponding. To design check dams into a swale:

    1. The height of each dam is determined by the depth of ponded water that will infiltrate in 24 hours. The infiltration may be into the native soils, into biomedia, or some other soil amendment may be proposed in the design.
    2. Dams are usually installed between 10-20 m along the swale. They are distributed such that the crest of each dam is at approximately the same elevation as the toe of the upstream dam. If the slope along the swale varies, so should the distance between the dams.
    The objective of these design recommendations are to maximize the distribution of ponded water along the whole BMP. Detailed design may require iteration of the dam heights and distances along each section of a long swale.

    • Dams may be constructed of any resilient and waterproof material, including: rock gabions, earth berms, coarse aggregate or rip-rap, concrete, metal or wood.
    • Energy dissipation and erosion control measures should be installed in the 1 - 2 m downstream of each dam. Examples include large aggregate or turf reinforcement

    Other components

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    Performance[edit]

    Performance Content

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    Incentives and Credits[edit]

    In Ontario

    City of Mississauga
    The City of Mississauga has a stormwater management credit program which includes RWH as one of their recommended site strategies[1].

    LEED BD + C v. 4

    SITES v.2


    See Also[edit]


    External Links[edit]


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