Difference between revisions of "Infiltration"
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<p>[[Infiltration: Testing|Infiltration tests]] must be undertaken at the location, depth and with a head of water that replicates the proposed design. </p>  | <p>[[Infiltration: Testing|Infiltration tests]] must be undertaken at the location, depth and with a head of water that replicates the proposed design. </p>  | ||
<table>  | <table>  | ||
| − | <table class = "table-responsive table table-striped">  | + |     <table class="table-responsive table table-striped">  | 
| − | <caption><strong>Suggested safety factors to be applied to measured percolation rate when designing infiltration facilities</strong></caption>  | + |         <caption><strong>Suggested safety factors to be applied to measured percolation rate when designing infiltration facilities</strong></caption>  | 
| − | <tr class="success">  | + |         <tr class="success">  | 
| − | <th rowspan="2">Catchment area</th><th colspan="3" class="text-center">Consequence of failure</th>  | + |             <th rowspan="2"  class="text-center">Catchment area</th>  | 
| − | <tr class="success">  | + |             <th colspan="3" class="text-center">Consequence of failure</th>  | 
| − | <th>No damage or inconvenience</th><th>Minor damage or inconvenience to external structures (e.g. ponding in parking lot)</th><th>Significant damage to buildings or infrastructure (e.g. flooding damage)</th></tr>  | + |             <tr class="success">  | 
| − | <tr><td> <100 m<sup>2</sup></td><td>1.5</td><td>2</td><td>10</td></tr>  | + |                 <th  class="text-center">No damage or inconvenience</th>  | 
| − | <tr><td style="white-space: nowrap"> 100 - 1000 m<sup>2</sup><td>1.5</td><td>3</td><td>10</td></tr>  | + |                 <th  class="text-center">Minor damage or inconvenience to external structures (e.g. ponding in parking lot)</th>  | 
| − | </table>  | + |                 <th  class="text-center">Significant damage to buildings or infrastructure (e.g. flooding damage)</th>  | 
| + |             </tr>  | ||
| + |             <tr>  | ||
| + |                 <td  class="text-center"><100 m<sup>2</sup></td>  | ||
| + |                 <td  class="text-center">1.5</td>  | ||
| + |                 <td  class="text-center">2</td>  | ||
| + |                 <td  class="text-center">10</td>  | ||
| + |             </tr>  | ||
| + |             <tr>  | ||
| + |                 <td style="white-space: nowrap"  class="text-center"> 100 - 1000 m<sup>2</sup>  | ||
| + |                     <td  class="text-center">1.5</td>  | ||
| + |                     <td  class="text-center">3</td>  | ||
| + |                     <td  class="text-center">10</td>  | ||
| + |             </tr>  | ||
| + |     </table>  | ||
<h4>Groundwater</h4>  | <h4>Groundwater</h4>  | ||
<p> 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. </p>  | <p> 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. </p>  | ||
Revision as of 14:37, 10 July 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 and trenches (underground)
 - Infiltration basins (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).
 
Infiltration can still be optimized over 'tight' soils with infiltration rates ≤ 15 mm/hr:
Without infiltration, many 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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