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12/19/2001 Env Bd Packet
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12/19/2001 Env Bd Packet
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Environmental Board
Env Bd Document Type
Env Bd Packet
Meeting Date
12/19/2001
Env Bd Meeting Type
Regular
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Infiltration Basins <br />The design storm for an infiltration basin is typically a frequent, small storm such as the 1-year event. This <br />provides treatment for the "first flush" of stormwater runoff. Infiltration basins provide total peak discharge, <br />runoff volume and water quality control for all storm events equal to or less than the design storm. This infiltra- <br />tion reduces the volume of' runoff, removes many pollutants and provides stream baseflow and groundwater recharge. <br />Infiltration basins have limited capabilities for controlling peak discharge for storms greater than the design <br />storm. Because infiltration basins will not significantly affect peak discharges of runoff, they are best used in <br />conjunction with other BMPs; downstream detention is often still needed to meet peak - runoff -rate requirements. <br />Dissolved pollutants are effectively controlled for storm events Tess than the design storm, but these substances <br />may not be removed from the runoff water as it infiltrates, and some of them could move to the groundwater. For <br />this reason, the impact of infiltrated runoff on the groundwater should be considered, although in most cases, the <br />magnitude of this impact is unknown. Chloride from road salt is an example of a soluble material that will not be <br />removed during the infiltration process. Currently, there is much disagreement as to whether chlorides do indeed <br />pose a significant threat to groundwater. A general guideline for groundwater protection is to design infiltration <br />basins with the bottom of the basin a minimum of 3 feet above the seasonally high groundwater table. This is <br />consistent with the MPCA's guidelines for septic systems (MPCA, 2000). If the water table is too close to the <br />ground surface, infiltration practices should not be used. <br />Figure 1 provides a schematic of a typical infiltration basin. Figure 2 shows an infiltration basin with pretreat- <br />ment in the form of a settling pond. <br />Advantages <br />• Reduces the volume of runoff from a drainage area <br />• Can be very effective for removing fine sediment, trace metals, nutrients, bacteria, and oxygen- demanding <br />substances (organics) <br />• Reduces downstream flooding and protects streambank integrity <br />• Reduces the size and cost of downstream stormwater control facilities and/or storm drain systems by infiltrat- <br />ing stormwater in upland areas <br />• Provides groundwater recharge and baseflow in nearby streams <br />• Reduces local flooding <br />• Appropriate for small sites (2 acres or Tess) <br />Limitations <br />• Potentially high failure rates due to improper siting, design and lack of maintenance, especially if pretreat- <br />ment is not incorporated into the design <br />• Depending on soil conditions and groundwater depth, a risk of groundwater contamination may exist <br />• Not appropriate for treating significant loads of sediment and other pollutants due to the potential for clogging <br />3-156 Minnesota Urban Small Sites BMP Manual <br />
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