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*Information on [[Stormwater infiltration and constraints on infiltration|site constraints]] (shallow soil, karst, etc.) | *Information on [[Stormwater infiltration and constraints on infiltration|site constraints]] (shallow soil, karst, etc.) | ||
*Guidance on [[Pre-treatment|pretreatment]] | *Guidance on [[Pre-treatment|pretreatment]] | ||
− | *[[Construction specifications for | + | *[[Construction specifications for infiltration|Construction specifications for infiltration BMPs]] |
− | *Information on [[Operation and maintenance of | + | *Information on [[Operation and maintenance of infiltration basin|operation and maintenance of infiltration BMPs]]. |
==Links to MIDS pages== | ==Links to MIDS pages== |
For an infiltration basin system, all stormwater captured by the BMP is infiltrated into the underlying soil between rain events. All pollutants in the infiltrated water are credited as being reduced. Pollutants in the stormwater that bypasses the BMP are not reduced.
For infiltration basin systems, the user must input the following parameters to calculate the volume and pollutant load reductions associated with the BMP.
The following are requirements or recommendations for inputs into the MIDS calculator. If the following are not met, an error message will inform the user to change the input to meet the requirement. *The basin must meet the drawdown time requirement specified. The drawdown time requirement is checked by comparing the user defined drawdown time with the calculated drawdown time (DDTcalc), which is given by
\(DDT_{calc} = D_O / (I_R / 12)\)
Where
If the DDTcalc is greater than the user defined required drawdown time then the user will be prompted to enter a new overflow depth or infiltration rate.
Required treatment volume, or the volume of stormwater runoff delivered to the BMP, equals the performance goal (1.1 inches or user-specified performance goal) times the impervious area draining to the BMP plus any water routed to the BMP from an upstream BMP. This stormwater is delivered to the BMP instantaneously following the Kerplunk method.
The volume reduction achieved by a BMP compares the capacity of the BMP to the required treatment volume. The Volume reduction capacity of BMP is calculated using BMP inputs provided by the user. For this BMP, the Volume reduction capacity is equal to the amount of stormwater that can be instantaneously captured above the media and below the overflow point. The captured volume (V) is given by
\(V= [(A_O+A_M)/2*(D_O)]\)
Where:
The Volume of retention provided by BMP is the amount of volume credit the BMP provides toward the performance goal. This value is equal to the lesser of the Volume reduction capacity of BMP calculated using the above method or the Required treatment volume. This check makes sure that the BMP is not getting more credit than the amount of water it receives. For example, if the BMP is oversized the user will only receive credit for the Required treatment volume routed to the BMP, which corresponds with meeting the performance goal for the site.
Pollutant load reductions are calculated on an annual basis. Therefore, the first step in calculating annual pollutant load reductions is converting the Volume reduction capacity of BMP, which is an instantaneous volume reduction, to an annual volume reduction percentage. This is accomplished through the use of performance curves developed from multiple modeling scenarios. The performance curves use the Volume reduction capacity of BMP, the infiltration rate of the underlying soils, the contributing watershed percent impervious area, and the size of the contributing watershed to calculate a percent annual volume reduction. While oversizing a BMP above the Required treatment volume will not provide additional credit towards the performance goal volume, it may provide additional pollutant reduction.
A 100 percent removal is credited for all pollutants associated with the reduced volume of stormwater since these pollutants are either attenuated within the media or pass into the underlying soil with infiltrating water . Pollutants in the stormwater that bypasses the BMP through overflow are not reduced. A schematic of the removal rates can be seen in the sidebar.
NOTE: The user can modify event mean concentrations (EMCs) on the Site Information tab in the calculator. Default concentrations are 54.5 milligrams per liter for total suspended solids (TSS) and 0.3 milligrams per liter for total phosphorus (particulate plus dissolved). The calculator will notify the user if the default is changed. Changing the default EMC will result in changes to the total pounds of pollutant reduced.
An infiltration basin can be routed to any other BMP, except for a green roof and a swale side slope or any BMP that would cause stormwater to be rerouted back to the infiltration basin already in the stormwater runoff treatment sequence. All BMPs can be routed to an infiltration basin, except for a swale side slope.
The following general assumptions apply in calculating the credit for an infiltration basin. If these assumptions are not followed, the volume and pollutant reduction credits cannot be applied.
An infiltration basin is to be constructed in a watershed that contains a 1.4 acre parking lot surrounded by 0.8 acres of pervious area (turf area and the infiltration BMP area). All of the runoff from the watershed will be treated by the infiltration basin. The soils across the area have a unified soils classification of SM (HSG type B soil). The infiltration basin is designed to have 1 foot of ponding depth below the overflow point (e.g. surface outlet or invert of a pipe). The surface area of the infiltration basin at the overflow point will be 6534 square feet. The surface area will be 5600 square feet at the soil/media surface. Following the MPCA Construction Stormwater General Permit requirement, the infiltration basin needs to drawdown in a 48 hour time period. The following steps detail how this system would be set up in the MIDS calculator.
Step 1: Determine the watershed characteristics of your entire site. For this example we have a 2.2 acre site with 1.4 acres of impervious area and 0.8 acres of pervious area in type B soils. The pervious area includes the turf area and the area of the infiltration basin.
Step 2: Fill in the site specific information into the Site Information tab. This includes entering a Zip Code (55414 for this example) and the watershed information from Step 1. The Managed Turf area includes the turf area and the area of the infiltration basin. Zip code and impervious area must be filled in or an error message will be generated. Other fields on this screen are optional.
Step 3: Go to the Schematic tab and drag and drop the Infiltration basin/Underground Infiltration icon into the Schematic Window.
Step 4: Open the BMP properties for the infiltration basin by right clicking on the Infiltration basin/Underground infiltration icon and selecting “Edit BMP properties”, or by double clicking on the Infiltration basin/Underground Infiltration icon.
Step 5: If help is needed, click on the Minnesota Stormwater Manual Wiki link or the Help button to review input parameter specifications and calculation specific to the Infiltration basin/Underground infiltration BMP.
Step 6: Determine the watershed characteristics for the infiltration basin. For this example the entire site is draining to the infiltration basin. The watershed parameters therefore include a 2.2 acre site with 1.4 acres of impervious area and 0.8 acres of pervious turf area in type B soils. There is no routing for this BMP. Fill in the BMP specific watershed information (1.4 acres on impervious cover and 0.8 acres of Managed turf in B soils).
Step 7: Enter in the BMP design parameters into the “BMP parameters” tab. Infiltration basin/Underground Infiltration requires the following entries.
Step 8: Click on BMP Summary tab to view results for this BMP.
Step 9: Click on the OK button to exit the BMP properties screen.
Step 10: Click on Results tab to see overall results for the site.