4c - Wet Detention Control Practices 1 1 2013 International Low Impact Development Symposium August 18, 2013 Saint Paul, Minnesota John Voorhees, PE, PH AECOM Madison, WI Entering Wet Detention Pond Data into the Model Model Output
4c - Wet Detention Control Practices
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2013 InternationalLow Impact Development Symposium
August 18, 2013Saint Paul, Minnesota
John Voorhees, PE, PHAECOM
Madison, WI
Entering Wet Detention Pond Data into the Model
Model Output
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•NURP (1983) found particulates reduced by between 0% (for small ponds and large drainage areas) and 90+% for large ponds. For well designed ponds BOD and COD removals were 70%, and heavy metals between 60 – 95%.
•Oliver (1981) reported 88% reductions in SS and 54% and 60% reductions for COD and total phosphorus.
•Yousef (1986) found 85% removal of soluble nutrients due to plant uptake.
WinSLAMM assumes a 3.0 ft scour depth for complete settling; reduces treatment effectiveness for shallower depths.
Pond routing is performed using the Modified Puls – Storage Indication Method.
Time increments are established by the user; default = 6 minutes.
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Snowmelt can contribute the majority of the annual pollutant loads from urban areas that experience heavy winter snowfalls.
Summer runoff is typically only considered in the design of stormwater controls
Cold weather hinders all stormwater control processes (such as infiltration, settling, and plant uptake)
Deicing salts are a special threat to urban groundwater quality
Surface area of pond
Water quality volume (live storage above lowest pond water surface elevation, usually the pond volume between the water quality outlet and the emergency spillway)
Depth of water over the sediment to prevent scour
Stage‐discharge relationship for all outlets
Particle size distribution of inflowing particulates
Hydrograph of influent flows
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Ideal Settling: Particle path is vector sum of particle velocity through pond and settling (upflow) velocity
L = Pond Length
D = Outlet Depth
V = Water Velocity through Pond
v = Settling Velocity
Qout = Outflow from Pond
A = Pond Surface Area
Particle settling is a function of the pond outflow rate and the pond surface area only. This calculation is applied to each flow entering the pond during continuous modeling.
The “dead” storage is needed to prevent scour of previously deposited material and should be at least 3 ft deep over the sediment. Sediment storage volume is also needed and can be estimated using the program, or should be at least 2 ft deep.
Sediment Storage
Water Quality “Live” Storage
Scour Protection“Dead” Storage
Additional Storage for Emergency Spillway and Freeboard
3 ft minimum
2 ft minimum
Lowest Invert Elevation
Conceptual Issues – Pond Geometry and Scour
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33% Removal at Sediment Level of 5 ft.50% Removal at Sediment Level of 4.5 ft.
100% Sediment Removal Up to 3 ft. Stage
1. Pond Geometry2. Flow, Initial Stage and Particle Size Data3. Outlet Information
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Pond Datum is always zero ft.
3 ft
Pond Geometry
Information
Flow, Initial Stage and
Particle Size Information
Particle Size Distribution File not accessible if
Flows and Particle Sizes transferred
through the drainage system
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Pond Outlet Information
Broad Crested
Weir
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Orifice
Stone Weeper
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V-Notch Weir
60 degrees
h
Sharp Crested Weir
Evaporation and Water
Withdraw Rate
Natural Seepage and Other Outflow
Seepage Basin
Vertical Stand Pipe
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Wet Detention Pond Model Results
Wet Detention Pond Output
For this Example, the Wet Detention Pond is the only control practice.
Note pollutant reduction.
Wet Detention Pond Model Results
Wet Detention Pond Output
For this Example, the Wet Detention Pond overflowed during the model run – this message flags that fact
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Outfall Runoff Volume
Pond Outlet
Structure Failure (over-
topping)
Maximum Flushing Ratio
Maximum Peak Reduction Factor
Maximum Stage
Stage Outflow
Stone Weeper Flow Detailed Output by Time Step Pond Water Balance Stage Area Storage Values
Questions?