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)  | ||
| Line 19: | Line 20: | ||
<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 08:17, 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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