Difference between revisions of "Inspection and Maintenance: Bioretention & Bioswales"
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| rowspan="3"|'''[[Bioretention: Construction checklist|Filter Bed]]''' | | rowspan="3"|'''[[Bioretention: Construction checklist|Filter Bed]]''' | ||
|Local or average sediment accumulation ≥ 5 cm in depth. | |Local or average sediment accumulation ≥ 5 cm in depth. | ||
|*At [[inlets]] remove [[stone]] and use vacuum equipment or rake and shovel to remove sediment. For large areas or BMPs, use of a small excavator may be preferable. Restore grades with filter media that meets design specifications. Test surface infiltration rate (one test for every 25 m2 of filter bed area) to confirm it is > 25 mm/h. Replace [[stone]], [[mulch]] and [[vegetation]] coverage (re-use/transplant where possible). If problem persists, add [[pretreatment]] device(s) or investigate the source(s). | | | ||
*At [[inlets]] remove [[stone]] and use vacuum equipment or rake and shovel to remove sediment. For large areas or BMPs, use of a small excavator may be preferable. Restore grades with filter media that meets design specifications. Test surface infiltration rate (one test for every 25 m2 of filter bed area) to confirm it is > 25 mm/h. Replace [[stone]], [[mulch]] and [[vegetation]] coverage (re-use/transplant where possible). If problem persists, add [[pretreatment]] device(s) or investigate the source(s). | |||
|- | |- | ||
|Surface ponding remains for >48 hours or surface infiltration rate is <25 mm/h. | |Surface ponding remains for >48 hours or surface infiltration rate is <25 mm/h. | ||
|*Remove sediment as described above. Core aerate (for sodded bioretention); or remove stone, sediment, mulch, and plant cover and till the exposed filter media to a depth of 20 cm; or remove and replace the uppermost 15 cm of material with filter media that meets specifications. Test surface infiltration rate (one test for every 25 m2 of filter bed area) to confirm it is > 25 mm/h. Replace stone, mulch and plants (re-use/ transplant where possible). | | | ||
*Remove sediment as described above. Core aerate (for sodded bioretention); or remove stone, sediment, mulch, and plant cover and till the exposed filter media to a depth of 20 cm; or remove and replace the uppermost 15 cm of material with filter media that meets specifications. Test surface infiltration rate (one test for every 25 m2 of filter bed area) to confirm it is > 25 mm/h. Replace stone, mulch and plants (re-use/ transplant where possible). | |||
|- | |- | ||
|Damage to filter bed or slide slope is present (e.g., [[erosion]] rills, animal burrows, sink holes, ruts) | |Damage to filter bed or slide slope is present (e.g., [[erosion]] rills, animal burrows, sink holes, ruts) | ||
|*Regrade damaged portion by raking and replant or restore [[mulch]]/[[stone]] cover. Animal burrows, sink holes and compacted areas should be tilled to 20 cm depth prior to re-grading. If problems persist, consider adding flow spreading device to prevent [[erosion]] or barriers to discourage foot or vehicular traffic. | |* | ||
Regrade damaged portion by raking and replant or restore [[mulch]]/[[stone]] cover. Animal burrows, sink holes and compacted areas should be tilled to 20 cm depth prior to re-grading. If problems persist, consider adding flow spreading device to prevent [[erosion]] or barriers to discourage foot or vehicular traffic. | |||
|- | |- | ||
|'''[[Vegetation]]''' | |'''[[Vegetation]]''' |
Revision as of 14:03, 8 April 2022
Overview[edit]
Bioretention treats stormwater by slowing it down, filtering it through soil and plant roots, soaking it into the ground and evaporating it back to the atmosphere. Runoff water is delivered to the practice through inlets such as curb cuts, spillways or other concrete structures, sheet flow from pavement edges, or pipes connected to catchbasins or roof downspouts. The planting bed and side slopes are typically covered with a mixture of plants, mulch and stone. Water in excess of its storage capacity overflows to another BMP or the municipal storm sewer. Filtered water is either infiltrated into the underlying soil to replenish groundwater, or collected by a sub-drain (i.e., underground perforated pipe) and discharged to the storm sewer system or another BMP. Depending on the permeability of the underlying soil or other constraints, it may be designed with no sub-drain for full infiltration, with a sub-drain for partial infiltration, or with an impermeable liner and sub-drain for a no infiltration practice. The sub-drain pipe may feature a flow restrictor (e.g., orifice cap or valve) for gradually releasing detained water and optimizing the amount drained by infiltration. Key components of bioretention practices for inspection and maintenance described further below.
Associated Terminology[edit]
- Bioretention cell: A flat-bottomed, depressed planting bed containing filter media soil, a gravel water storage layer and optional sub-drain pipe(s); Also known as a rain garden.
- Stormwater planters: A bioretention cell contained within an engineered (e.g., concrete) structure.
- Biofilter: Bioretention cell or swale with an impermeable liner or containment structure and sub-drain.
- Dry swale or Bioretention swale: A gently sloping, linear oriented bioretention practice designed to be capable of conveying water across an elevation gradient. Also known as a bioswale or dry swale.
How to Preserve Basic BMP Function[edit]
- Maintain grading of the filter bed (or grass filter strip if present) at curb cut inlets so at least 5 cm of the back of the curb is visible through regular sediment removal and regrading.
- To avoid over-compaction of the filter media soil, any maintenance tasks involving vehicle or foot traffic on the filter bed should not be performed during wet weather.
- For bioretention with sod (i.e., turf grass) as vegetation cover, maintain with a push mower or the lightest mulching ride mower available and core aerate and dethatch annually in the spring to help maintain permeability.
- Pruning of mature trees should be performed under the guidance of a Certified Arborist.
- Woody vegetation should not be planted or allowed to become established where snow will be piled/stored during Winter.
- Removal of sediment from the filter bed surface should be done with rake and shovel, or vacuum equipment to minimize plant disturbance. If a small excavator is to be used, keep it off the BMP footprint to avoid damage to side slopes/embankments and over-compaction of the filter media.
Key Components and I&M Tasks[edit]
Component | Description | Inspection & Maintenance Tasks |
---|---|---|
Contributing Drainage Area (CDA) |
Area(s) from which runoff directed to the BMP originates; includes both impervious and pervious areas. |
|
Pretreatment |
Devices or features that retain trash, debris and sediment; help to extend the operating life cycle; examples are eavestrough screens, catch basin inserts and sumps, oil and grit separators, geotextile-lined inlets, gravel trenches, grass filter strips and forebays. |
|
Inlets |
Structures that deliver water to the BMP (e.g., Curb cuts, spillways, pavement edges, catch basins, pipes). |
|
Perimeter |
Side slopes or structures that define the BMP footprint; may be covered by a mixture of vegetation, mulch and stone with slopes up to 2:1 (H:V), or concrete or masonry structures with vertical walls. |
|
Filter Bed |
Flat or gently sloping area composed of a 0.5 to 1 m deep layer of filter media soil covered by a mixture of vegetation, mulch and stone where surface ponding and filtration of runoff occurs. |
|
Vegetation |
A mixture of deep rooting perennial plants, tolerant to both wet and dry conditions and salt (if receiving pavement runoff); can include grasses, flowers, shrubs and trees; roots uptake water and return it to the atmosphere; provide habitat for organisms that break down trapped pollutants and help maintain soil structure and permeability. |
|
Overflow Outlet |
Structures that convey overflows to another BMP or municipal storm sewer. |
|
Sub-drain |
Optional component; perforated pipe(s) surrounded by gravel and may be wrapped in geotextile filter fabric; installed below the filter media soil layer to collect and convey treated water to an adjacent drainage system; may also include a flow restrictor. |
|
Monitoring well |
Perforated standpipe that extends from the bottom of the BMP to above the invert of the overflow outlet. Allows measurement of subsurface water level to track drainage performance over time. |
|
Rehabilitation & Repair[edit]
Component | Problem | Rehabilitation Tasks |
---|---|---|
Inlets |
Inlet is producing concentrated flow and causing filter bed erosion. |
|
Filter Bed | Local or average sediment accumulation ≥ 5 cm in depth. |
|
Surface ponding remains for >48 hours or surface infiltration rate is <25 mm/h. |
| |
Damage to filter bed or slide slope is present (e.g., erosion rills, animal burrows, sink holes, ruts) | *
Regrade damaged portion by raking and replant or restore mulch/stone cover. Animal burrows, sink holes and compacted areas should be tilled to 20 cm depth prior to re-grading. If problems persist, consider adding flow spreading device to prevent erosion or barriers to discourage foot or vehicular traffic. | |
Vegetation |
Vegetation is not thriving and filter media is low in organic matter (<3%) or extractable phosphorus (<10 mg/kg) |
|
Sub-drain |
Sub-drain perforated pipe is obstructed by sediment or roots. |
|
References[edit]
- ↑ TRCA. 2016. Fact Sheet - Inspection and Maintenance of Stormwater Best Management Practices: Bioretention. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf