Difference between revisions of "Infiltration"
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<p>Infiltration of stormwater into underlying soils is one the priority level 1. mechanisms to achieve MOECC Runoff Volume Control targets. | <p>Infiltration of stormwater into underlying soils is one the priority level 1. mechanisms to achieve MOECC Runoff Volume Control targets. | ||
{{TextBox|1= Infiltration is promoted through a number of LID BMPs: | {{TextBox|1= Infiltration is promoted through a number of LID BMPs: | ||
*[[Infiltration chambers | *[[Infiltration chambers]] (underground) | ||
*[[ | *[[Infiltration trenches]] (underground) | ||
*[[Dry ponds]] (surface) | |||
*[[Bioretention cells]] (surface) | *[[Bioretention cells]] (surface) | ||
*[[Bioswales]] (surface) | *[[Bioswales]] (surface) | ||
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<li>Where prohibitions and/or restrictions exist per approved Source Protection Plans (see MOECC guidance). | <li>Where prohibitions and/or restrictions exist per approved Source Protection Plans (see MOECC guidance). | ||
</ol> | </ol> | ||
<p> | |||
===Designing within constraints=== | |||
Infiltration can still be optimized over 'tight' soils with infiltration rates ≤ 15 mm/hr: | Infiltration can still be optimized over 'tight' soils with infiltration rates ≤ 15 mm/hr: | ||
<li>[[Bioretention:_Partial_infiltration|Partially infiltrating bioretention]]</li></ | <ul> | ||
<li>[[Bioretention: Internal water storage |Bioretention with internal water storage]]</li> | |||
<li>[[Bioretention:_Partial_infiltration|Partially infiltrating bioretention]]</li> | |||
</ul> | |||
Where infiltration is impossible, LID design alternatives exist which can still capture and retain stormwater: | |||
<ul> | <ul> | ||
<li>[[Bioretention: Non-infiltrating | Bioretention planters]]</li> | <li>[[Bioretention: Non-infiltrating | Bioretention planters]]</li> |
Revision as of 13:17, 3 August 2017
Infiltration of stormwater into underlying soils is one the priority level 1. mechanisms to achieve MOECC Runoff Volume Control targets.
Infiltration is promoted through a number of LID BMPs:
- Infiltration chambers (underground)
- Infiltration trenches (underground)
- Dry ponds (surface)
- Bioretention cells (surface)
- Bioswales (surface)
Constraints[edit]
Infiltration practices are not recommended:
- Where the bedrock is within 1 m below the bottom of the proposed BMP,
- Where the seasonal high groundwater level comes within 1 m below the bottom of the proposed BMP,
Or in areas where increased infiltration will result in elevated groundwater levels, which can be demonstrated to damage critical utilities or private property, - Over swelling clays or unstable sub-soils,
- Over contaminated soils or sites with high risk of contamination from onsite activities,
- In flood prone areas where the wastewater system is sensitive to groundwater conditions causing sewer backups, and where LID BMPs have been found to be ineffective,
- In areas where the ecology and natural hydrology are dependent upon surface water,
- Where prohibitions and/or restrictions exist per approved Source Protection Plans (see MOECC guidance).
Designing within constraints[edit]
Infiltration can still be optimized over 'tight' soils with infiltration rates ≤ 15 mm/hr:
Where infiltration is impossible, LID design alternatives exist which can still capture and retain stormwater:
Planning[edit]
Soil infiltration rate
Infiltration tests must be undertaken at the location, depth and with a head of water that replicates the proposed design.
Catchment area | Consequence of failure | ||
---|---|---|---|
No damage or inconvenience | Minor damage or inconvenience to external structures (e.g. ponding in parking lot) | Significant damage to buildings or infrastructure (e.g. flooding damage) | |
<100 m2 | 1.5 | 2 | 10 |
100 - 1000 m2 | 1.5 | 3 | 10 |
Groundwater
The bottom of the infiltration BMP must ≥ 1 m vertically separated from the seasonally high water table, and underlying bedrock. This reduces the risk of contaminating groundwater and helps to ensure reliable infiltration rates throughout the year.
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