Difference between revisions of "Infiltration"
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Infiltration of stormwater into underlying soils is one mechanism to achieving MECP [[runoff volume control targets]]. In many areas of Ontario, where municipal supplies of potable water are drawn from aquifers, it's also an important mechanism for groundwater recharge. | Infiltration of stormwater into underlying soils is one mechanism to achieving MECP [[runoff volume control targets]]. In many areas of Ontario, where municipal supplies of potable water are drawn from aquifers, it's also an important mechanism for groundwater recharge. | ||
− | {{textbox| | + | {{textbox|Drainage via infiltration to underlying native subgrade soil can be achieved through a number of LID BMP types: |
*[[Infiltration chambers]] (underground) | *[[Infiltration chambers]] (underground) | ||
*[[Infiltration trenches]] (underground) | *[[Infiltration trenches]] (underground) |
Revision as of 16:50, 10 March 2022
Infiltration of stormwater into underlying soils is one mechanism to achieving MECP runoff volume control targets. In many areas of Ontario, where municipal supplies of potable water are drawn from aquifers, it's also an important mechanism for groundwater recharge.
Drainage via infiltration to underlying native subgrade soil can be achieved through a number of LID BMP types:
- Infiltration chambers (underground)
- Infiltration trenches (underground)
- Exfiltration systems (underground)
- Bioretention (surface)
- Bioswales (surface)
- Stormwater Tree Trenches (surface)
- Permeable pavements (surface)
- Dry ponds or infiltration basins (surface)
Constraints[edit]
Infiltration practices are not recommended:
- over-swelling clays or unstable subsoils,
- contaminated soils or sites with high risk of contamination from on-site activities (i.e. pollution hot spots),
- in areas of known or implied karst topography,
- on unstable or steep slopes (>15%),
- to treat construction site runoff,
- to treat combined sewer overflows,
- in flood prone areas where the wastewater system is sensitive to groundwater conditions causing sewer backups,
- in areas where the ecology and natural hydrology are dependent upon surface water,
- in areas where increased infiltration will result in elevated groundwater levels that will damage critical utilities or private property, or
- where prohibitions and/or restrictions exist per approved Drinking Water Source Protection Plans (e.g. should not be used to treat pavement runoff within 2 year time of travel wellhead protection areas; see MOECC guidance).
Infiltration facilities should be designed with modifications where:
- the underlying bedrock is within 1 m below the bottom of the proposed BMP, or
- the seasonal high groundwater level (i.e. water table) comes within 1 m below the bottom of the proposed BMP.
Designing with constraints[edit]
Infiltration can still be optimized over 'tight' soils with infiltration rates ≤ 15 mm/hr:
- See underdrains for bioretention and tree pits, trenches and soil cells, and
- Results from STEP studies of infiltration practices on low permeability soils
Where infiltration is impossible, LID design alternatives exist which can still capture and retain stormwater:
Planning[edit]
Hydrogeology[edit]
The Conservation Authorities Geoscience Group has prepared a guidance document which attempts to standardize the hydrogeological study requirements for development applications made to Conservation Authorities. It is a helpful guide for all low impact development applications which include infiltration. It is provided with the caveat that not all sections or content are necessary or appropriate for every case. Pre-consultation with your local conservation authority and municipality is strongly recommended in all cases.