eric strecker3
TRANSCRIPT
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Eric W. Strecker, [email protected]
Overview of Unit Processes Approach for BMP Selection and
Design
BMP Overview
Overview of Unit Processes Approach for BMP Selection and
Design
BMP Overview
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Dry Extended Detention BasinsDry Extended Detention Basins
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Dry Extended Detention Basins (cont.)Dry Extended Detention Basins (cont.)
DescriptionPonds without a permanent pool of water that are designed to detain the runoff from a water quality design storm and completely drain within 36 - 72 (typically 48) hours
DescriptionPonds without a permanent pool of water that are designed to detain the runoff from a water quality design storm and completely drain within 36 - 72 (typically 48) hours
Flood control potentialRecreational multi-use potentialHydromodification control potential
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Dry Extended Detention Basins (cont.)Dry Extended Detention Basins (cont.)
Major Treatment ProcessesFlow attenuationSome volume reductionSedimentationSome aeration / volatilization
Primary Pollutants RemovedSedimentParticulate-bound nutrients and metalsPetroleum hydrocarbons
Major Treatment ProcessesFlow attenuationSome volume reductionSedimentationSome aeration / volatilization
Primary Pollutants RemovedSedimentParticulate-bound nutrients and metalsPetroleum hydrocarbons
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Dry Extended Detention Basins (cont.)Dry Extended Detention Basins (cont.)
Critical Design ParametersStorage capacity (including sediment)Length-to-width ratioStage-discharge relationship (outlet design)Flow rate diversion for off-line facilities
Critical Design ParametersStorage capacity (including sediment)Length-to-width ratioStage-discharge relationship (outlet design)Flow rate diversion for off-line facilities
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Dry Extended Detention Basins (cont.)Dry Extended Detention Basins (cont.)
Max Elevation of Extended Detention Pool Emergency
Spillway
Outfall
Low Flow Channel
Sediment Forebay
Inflow
Maintenance Access Rd
Safety Bench
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Dry Extended Detention Basins (cont.)Dry Extended Detention Basins (cont.)
Outfall Erosion Protection
Embankment
Riser Pipe
Forebay
Influent Pipe
WQ Elevation
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Dry Extended Detention Basins (cont.)Dry Extended Detention Basins (cont.)
Forebay
Influent Pipe Overflow Spillway
Flood Control
Water Quality Control
Hydromodification ControlEnergy Dissipation
Energy Dissipation
Critical Flow Outlet Pipe
Infiltration
Multi-Stage Orifice Outlet Structure
Vegetated Low-flow Channel
Combination Facility
Forebay
Flood Control
Water Quality Control
Hydromodification Control
Infiltration
Perforated Riser Pipe Outlet Structure
Vegetated Low-flow Channel
Energy Dissipation
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Dry Extended Detention Basins (cont.)Outlet Design
25-yr Outlet Design
2-yr Design Outlet
Emergency Spillway
Perforated Riser Water Quality Outlet
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Routine Maintenance ActivitiesTrash and debris removalSediment removal from inlet/forebay and outletVegetation upkeep (e.g. mowing and pruning), removal of woody vegetation and noxious weedsVector controlPump or valve maintenanceFrequencies dictated by condition of pond (monthly, quarterly, or annually)
Routine Maintenance ActivitiesTrash and debris removalSediment removal from inlet/forebay and outletVegetation upkeep (e.g. mowing and pruning), removal of woody vegetation and noxious weedsVector controlPump or valve maintenanceFrequencies dictated by condition of pond (monthly, quarterly, or annually)
Dry Extended Detention Basins (cont.)Dry Extended Detention Basins (cont.)
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Infrequent Maintenance ActivitiesSediment removal from main pond areaBank or berm stabilization/erosion repair, if neededEnergy dissipator repairRegrading and revegetationFrequency dictated as needed (10 – 20 years)
Infrequent Maintenance ActivitiesSediment removal from main pond areaBank or berm stabilization/erosion repair, if neededEnergy dissipator repairRegrading and revegetationFrequency dictated as needed (10 – 20 years)
Dry Extended Detention Basins (cont.)Dry Extended Detention Basins (cont.)
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Vegetated SwalesVegetated Swales
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Vegetated Swales (cont.)Vegetated Swales (cont.)
DescriptionShallow, open channels with low-lying vegetation covering the side slopes and bottom.
DescriptionShallow, open channels with low-lying vegetation covering the side slopes and bottom.
Easily integrated into site landscaping Perfect application for roadsCan potentially replace storm drain infrastructureSome hydromodification control potential
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Vegetated Swales (cont.)Vegetated Swales (cont.)
Major Treatment ProcessesFiltrationSome volume reduction (infiltration)Some sedimentationSome soil adsorption and plant uptake
Primary Pollutants RemovedSedimentParticulate-bound nutrients and metalsPetroleum hydrocarbons
Major Treatment ProcessesFiltrationSome volume reduction (infiltration)Some sedimentationSome soil adsorption and plant uptake
Primary Pollutants RemovedSedimentParticulate-bound nutrients and metalsPetroleum hydrocarbons
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Vegetated Swales (cont.)Vegetated Swales (cont.)
Critical Design ParametersHydraulic retention timeMinimum lengthMaximum widthFlow rate, velocity, & depthSlope
Critical Design ParametersHydraulic retention timeMinimum lengthMaximum widthFlow rate, velocity, & depthSlope
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Check Dam
Outlet
Inlet
Flow Spreader
Roadway
Energy Dissipater
Low-flowUnderdrain
Side Slope
Vegetated Swales (cont.)Vegetated Swales (cont.)
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Vegetated Swales (cont.)Vegetated Swales (cont.)
Bottom Width(recommended 2 ft min,channel divider if >10ft)
Roadway Surface
Topsoil / Mulch
Water Quality DepthFlood Flow Depth
Grass height exceeds design flow by 2”
Freeboard
Shoulder
Swale Vegetation:Small plants, tall grasses and
shrubs
Underdrain if slope < 1.5%
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Routine Maintenance ActivitiesTrash and debris removalVegetation upkeep (e.g. mowing, pruning) and removal of noxious weedsVector control
Infrequent Maintenance ActivitiesSediment removal at inletRegrading and revegetation if erosion occurs or standing water is presentUnderdrain clean out or replacement (if present)
Routine Maintenance ActivitiesTrash and debris removalVegetation upkeep (e.g. mowing, pruning) and removal of noxious weedsVector control
Infrequent Maintenance ActivitiesSediment removal at inletRegrading and revegetation if erosion occurs or standing water is presentUnderdrain clean out or replacement (if present)
Vegetated Swales (cont.)Vegetated Swales (cont.)
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Filter StripsFilter Strips
Source: Caltrans
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Filter Strips (cont.)Filter Strips (cont.)
DescriptionMildly sloping vegetated slopes that receive sheet flow runoff from adjacent impervious surfaces.
DescriptionMildly sloping vegetated slopes that receive sheet flow runoff from adjacent impervious surfaces.
Easily integrated into existing landscapingApplicable to roads and parking lots
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Filter Strips (cont.)Filter Strips (cont.)
Major Treatment ProcessesFiltrationSome volume reduction (infiltration)Some sedimentationSome soil adsorption and plant uptake
Primary Pollutants RemovedSedimentParticulate-bound nutrients and metalsPetroleum hydrocarbons
Major Treatment ProcessesFiltrationSome volume reduction (infiltration)Some sedimentationSome soil adsorption and plant uptake
Primary Pollutants RemovedSedimentParticulate-bound nutrients and metalsPetroleum hydrocarbons
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Filter Strips (cont.)Filter Strips (cont.)
Critical Design ParametersSheet flow retention timeMinimum lengthFlow rate, velocity, & depth
Critical Design ParametersSheet flow retention timeMinimum lengthFlow rate, velocity, & depth
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Filter Strips (cont.)Filter Strips (cont.)
Pavement Surface
Flow Spreader (gravel) Filter Strip
Topsoil / Compost Mix
Length “L”1’ Min
Collector Ditch / Swale
Optional trench drain or perforated underdrain
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Filter Strips (cont.)Filter Strips (cont.)
Filter Strip
Flow Spreader Extending Entire Length of Pavement
Collector Ditch/ Storm Drain
Pavement Surface 150’ Max Recommended
Filter Strip Length “L”
1’ Min.
Width “W”
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Filter Strip (cont.)Filter Strip (cont.)
Pavement
Compost / Mulch Mix
Perforated underdrain pipe
Grass/vegetation
Filter fabric
Gravel backfill; depth depends on storage requirements
Gravel trench in no-vegetation zone
Enhanced Filter Strip / Bioslope
Source: Low Impact Development Center
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Routine Maintenance ActivitiesTrash and debris removalVegetation upkeep (e.g. mowing, pruning) and removal of noxious weedsVector control
Infrequent Maintenance ActivitiesSediment removalRegrading and revegetationUnderdrain clean out or replacement (if present)
Routine Maintenance ActivitiesTrash and debris removalVegetation upkeep (e.g. mowing, pruning) and removal of noxious weedsVector control
Infrequent Maintenance ActivitiesSediment removalRegrading and revegetationUnderdrain clean out or replacement (if present)
Filter Strips (cont.)Filter Strips (cont.)
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BioretentionBioretention
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Bioretention (cont.)Bioretention (cont.)
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Bioretention (cont.)Bioretention (cont.)
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Bioretention (cont.)Bioretention (cont.)
DescriptionVegetated (i.e., landscaped) shallow depressions with amended soils that retain, infiltrate, and evapotranspire runoff.
DescriptionVegetated (i.e., landscaped) shallow depressions with amended soils that retain, infiltrate, and evapotranspire runoff.
Easily integrated into site landscapingSome recreational multi-use potentialHydromodification control potential
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Bioretention (cont.)Bioretention (cont.)
Major Treatment ProcessesFiltration and sedimentationVolume reduction (infiltration & evapotranspiration)Soil adsorption and plant uptakeMicrobial decomposition
Primary Pollutants RemovedSedimentNutrients (total and some dissolved nitrogen and phosphorus)Metals (total and some dissolved)Petroleum hydrocarbonsPathogens
Major Treatment ProcessesFiltration and sedimentationVolume reduction (infiltration & evapotranspiration)Soil adsorption and plant uptakeMicrobial decomposition
Primary Pollutants RemovedSedimentNutrients (total and some dissolved nitrogen and phosphorus)Metals (total and some dissolved)Petroleum hydrocarbonsPathogens
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Bioretention (cont.)Bioretention (cont.)
Critical Design ParametersPonding depthEngineered soil depth and specificationPresence or absence of an underdrainNative soil infiltration rate if no underdrain present
Critical Design ParametersPonding depthEngineered soil depth and specificationPresence or absence of an underdrainNative soil infiltration rate if no underdrain present
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Bioretention (cont.)Bioretention (cont.)
Overflow Catch Basin
Parking Lot Sheet Flow
Curb Stops
Outlet
Underdrain Collection System
Stone Diaphragm
Optional Sand Layer
Grass Filter Strip
Gravel Curtain Drain Overflow
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Bioretention (cont.)Bioretention (cont.)
Gravel Curtain Drain
Optional Sand Filter Layer
Curb StopStone Diaphragm
Underdrain Bioretention Soil Media
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Routine Maintenance ActivitiesTrash and debris removalVegetation upkeep (e.g. mowing, pruning) and removal of noxious weedsVector control
Infrequent Maintenance ActivitiesSediment removalRegrading and revegetationUnderdrain clean out or replacement
Routine Maintenance ActivitiesTrash and debris removalVegetation upkeep (e.g. mowing, pruning) and removal of noxious weedsVector control
Infrequent Maintenance ActivitiesSediment removalRegrading and revegetationUnderdrain clean out or replacement
Bioretention (cont.)Bioretention (cont.)
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Buckman Heights Apartments
Buckman Heights Apartments
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Buckman Heights ApartmentsBuckman Heights Apartments
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Apartment Courtyard Biofiltration System
Apartment Courtyard Biofiltration System
Runoff is directed to center planter and either infiltrates or overflows into small inlets
42Figure I.6.12
Buckman Heights ApartmentsBuckman Heights Apartments
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Hydrological Source Control –Stormwater Planter Boxes
Hydrological Source Control –Stormwater Planter Boxes
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Portland Ultra Urban Biofiltration
Portland Ultra Urban Biofiltration
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Portland Version of Green StreetsPortland Version of Green Streets
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Portland Version of Retro-fit Green StreetsPortland Version of Retro-fit Green Streets
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Planting/Storage MediaPlanting/Storage Media
The planting media placed in the cell shall be highly permeable and high in organic matter (e.g., loamy sand mixed thoroughly with compost amendment) and a surface mulch layer.Planting media shall consist of 60 to 70% sand, 15 to 25% compost, and 10 to 20% clean topsoil. The organic content of the soil mixture should be 8% to 12%; the pH range should be 5.5 to 7.5.Sand should be free of stones, stumps, roots or other similar objects larger than 5 millimeters, and have the following gradation:
The planting media placed in the cell shall be highly permeable and high in organic matter (e.g., loamy sand mixed thoroughly with compost amendment) and a surface mulch layer.Planting media shall consist of 60 to 70% sand, 15 to 25% compost, and 10 to 20% clean topsoil. The organic content of the soil mixture should be 8% to 12%; the pH range should be 5.5 to 7.5.Sand should be free of stones, stumps, roots or other similar objects larger than 5 millimeters, and have the following gradation:
Particle Size (ASTM D422) % Passing
#4 100 #6 88-100 #8 79-97 #50 11-35 #200 5-15
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Planting/Storage MediaPlanting/Storage Media
Compost should be free of stones, stumps, roots or other similar objects larger than ¾ inches; have a particle size of 98% passing through ¾” screen or smaller; and meet the following characteristics:Soluble Salt Concentration: < 10 mmhos/cm (dS/m)pH: 5.0-8.5Moisture: 30-60% wet weight basisOrganic Matter: 30-65% dry weight basisStability (Carbon Dioxide evolution rate): >80% relative to positive controlMaturity (Seed emergence and seedling vigor): >80% relative to positive controlPhysical contaminants: < 1% dry weight basis
Compost should be free of stones, stumps, roots or other similar objects larger than ¾ inches; have a particle size of 98% passing through ¾” screen or smaller; and meet the following characteristics:Soluble Salt Concentration: < 10 mmhos/cm (dS/m)pH: 5.0-8.5Moisture: 30-60% wet weight basisOrganic Matter: 30-65% dry weight basisStability (Carbon Dioxide evolution rate): >80% relative to positive controlMaturity (Seed emergence and seedling vigor): >80% relative to positive controlPhysical contaminants: < 1% dry weight basis
Importance of “Engineering” the SoilsImportance of “Engineering” the Soils
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Vegetated Roofs – Detention and EvapotranspirationVegetated Roofs – Detention and Evapotranspiration
Gap World Headquarters, San Bruno, CA
Parking Garage, Oakland, CA
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City of Portland -Simplified ApproachCity of Portland -Simplified Approach
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Hamilton Ecoroof westside rainfall and runoffJune 28-29, 2002 storm event 0.73“
Hamilton Ecoroof westside rainfall and runoffJune 28-29, 2002 storm event 0.73“
-20
0
20
40
60
80
100
0
Time - hours
Gal
lons
Rain
Flow
Total catchment 3,692 sf, ecoroof 2,690 sf, * impervious surfaces 527 sf, pavers on sand base 475 sf *If the 239 gallons of rainfall from the impervious surfaces is removed then no runoff would have occurred
Total catchment 3,692 sf, ecoroof 2,690 sf, * impervious surfaces 527 sf, pavers on sand base 475 sf *If the 239 gallons of rainfall from the impervious surfaces is removed then no runoff would have occurred
Hydrological Source Control-
ET Losses
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Portland RoofPortland Roof
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Infiltration FacilitiesInfiltration Facilities
Source: Wisconsin Department of Natural Resources
Source: Low Impact Development Center
Infiltration Basin
Infiltration Trench
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Infiltration Facilities (cont.)Infiltration Facilities (cont.)
Source: Portland Bureau of Environmental Services
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WetpondsWetponds
Source: UDFCD 62
Stormwater WetlandsStormwater Wetlands
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Stormwater Wetlands (cont.)Stormwater Wetlands (cont.)
DescriptionConstructed, natural treatment system consisting of a sediment forebay and permanent micro-pools with aquatic vegetation covering a significant portion of the basin.
DescriptionConstructed, natural treatment system consisting of a sediment forebay and permanent micro-pools with aquatic vegetation covering a significant portion of the basin.
Flood control potentialRecreational multi-use potentialHydromodification control potential
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Stormwater Wetlands (cont.)Stormwater Wetlands (cont.)
Major Treatment ProcessesSedimentation (incl. natural flocculation)Microbial decomposition/transformationSome volume reduction (evapotranspiration)Soil adsorption and plant uptake
Primary Pollutants RemovedCoarse and fine sedimentTotal and dissolved metals Nutrients, but may also be a source during dormant periods if the plants are not cut backPetroleum hydrocarbons
Major Treatment ProcessesSedimentation (incl. natural flocculation)Microbial decomposition/transformationSome volume reduction (evapotranspiration)Soil adsorption and plant uptake
Primary Pollutants RemovedCoarse and fine sedimentTotal and dissolved metals Nutrients, but may also be a source during dormant periods if the plants are not cut backPetroleum hydrocarbons
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Stormwater Wetlands (cont.)Stormwater Wetlands (cont.)
Critical Design ParametersRetention timeDepth distributionLength to width ratioBase flow
Critical Design ParametersRetention timeDepth distributionLength to width ratioBase flow
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Stormwater Wetlands (cont.)Stormwater Wetlands (cont.)
Shallow water with emergent Cattails Shallow water with
emergent Bulrush
Open water areas
Inlet
Outlet structure
Open water pool, depth = 4-6 ft.
Shallow water depth = 1-2 ft
Small storm water quality pool, depth ~3-4 ft.
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Stormwater Wetlands (cont.)Stormwater Wetlands (cont.)
Routine Maintenance ActivitiesTrash and debris removalPerimeter landscape maintenanceVector control
Infrequent Maintenance ActivitiesSediment removal from inlet and outletRemoval of algal mats and control of fringe vegetation
Routine Maintenance ActivitiesTrash and debris removalPerimeter landscape maintenanceVector control
Infrequent Maintenance ActivitiesSediment removal from inlet and outletRemoval of algal mats and control of fringe vegetation
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Sand FiltersSand Filters
Source: UDFCD
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Sand Filter (cont.)Sand Filter (cont.)
DescriptionBasin or vault system with a thick sand filter bed and an extensive underdrain.
DescriptionBasin or vault system with a thick sand filter bed and an extensive underdrain.
Recreational multi-use potential
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Sand Filters (cont.)Sand Filters (cont.)
Major Treatment ProcessesFiltrationSome adsorptionSome surface sedimentation
Primary Pollutants RemovedCoarse and fine sedimentParticulate-bound metals, nutrients, and pathogensPetroleum hydrocarbons
Major Treatment ProcessesFiltrationSome adsorptionSome surface sedimentation
Primary Pollutants RemovedCoarse and fine sedimentParticulate-bound metals, nutrients, and pathogensPetroleum hydrocarbons
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Sand Filters (cont.)Sand Filters (cont.)
Critical Design ParametersMaximum emptying timeMedia depth and particle gradationUnderdrain flow capacity
Critical Design ParametersMaximum emptying timeMedia depth and particle gradationUnderdrain flow capacity
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Sand Filters (cont.)Sand Filters (cont.)
Routine Maintenance ActivitiesTrash and debris removalSurface scraping (top 2 to 4 inches)Vector Control
Infrequent Maintenance ActivitiesVegetation managementSand replacementUnderdrain clean out or replacement
Routine Maintenance ActivitiesTrash and debris removalSurface scraping (top 2 to 4 inches)Vector Control
Infrequent Maintenance ActivitiesVegetation managementSand replacementUnderdrain clean out or replacement
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Sand Filters (cont.)Sand Filters (cont.)
Recreational Multi-Use Sand Filter
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Cartridge FiltersCartridge Filters
StormFilter™™
CDS Media Filtration System Source: CDS Technologies, Inc.
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Hydrodynamic SeparatorsHydrodynamic Separators
CDS UnitSource: CDS Technologies, Inc.
VortechnicsSource: Stormwater 360o, Inc.
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Proprietary BiotreatmentProprietary Biotreatment
Filterra®®
Source: AmericastSource: Americast
StormTreat™™Source: StormTreat System, Inc.Source: StormTreat System, Inc.
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Low Impact DevelopmentExample Project OverviewLow Impact DevelopmentExample Project Overview
New club house and restaurant and relocation of the golf course operationsA new hotel, restaurant, & spa located where existing club house and golf operations areaTourist-serving fractionalized ownership condominiums
New club house and restaurant and relocation of the golf course operationsA new hotel, restaurant, & spa located where existing club house and golf operations areaTourist-serving fractionalized ownership condominiums
ReRe--development and New Developmentdevelopment and New Development
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Client Specified Desired Project Water Quality and Hydrology Goals
Client Specified Desired Project Water Quality and Hydrology Goals
No changes in pre/post in hydrology
No increase in runoff volume
No increase in infiltrationShow an improvement in water quality
No irrigation runoff
Eliminate all runoff to Morning Canyon
No changes in pre/post in hydrology
No increase in runoff volume
No increase in infiltrationShow an improvement in water quality
No irrigation runoff
Eliminate all runoff to Morning Canyon
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Why These Goals?Why These Goals?
Project drains to a State defined “Area of Special Biological Significance” – Crystal Cove
Morning Canyon has had erosion problems from increased runoff
Seeps downstream of the site are a concern
Client wanted quick permitting process and environmental community acceptance
Project drains to a State defined “Area of Special Biological Significance” – Crystal Cove
Morning Canyon has had erosion problems from increased runoff
Seeps downstream of the site are a concern
Client wanted quick permitting process and environmental community acceptance
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No Change in Hydrology!No Change in Hydrology!
Manage the “ET” Sponge
Necessitated a detailed analysis of precipitation, runoff, shallow soil soaking and drying, and deeper infiltration
to ascertain what conditions to match
Manage the “ET” Sponge
Necessitated a detailed analysis of precipitation, runoff, shallow soil soaking and drying, and deeper infiltration
to ascertain what conditions to match
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Pre- and Post-Hydrology No BMPsPre- and Post-Hydrology No BMPs
Water BalanceExisting Conditions
12%
83%
5%
Water Balance Developed Conditions
51%46%
3%
Runof f Evap & Trans Groundw ater
About 83% Evapotranspiration
Pre-Development!
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Evaluated “Standard” LID ApproachEvaluated “Standard” LID Approach
How much of the site would we have to have in biofiltration areas to meet goals?
With:Various depths of amended, moisture holding soils and
Limited infiltration.
Result: 30% of site would have to be in bioswales to meet project goals!
How much of the site would we have to have in biofiltration areas to meet goals?
With:Various depths of amended, moisture holding soils and
Limited infiltration.
Result: 30% of site would have to be in bioswales to meet project goals!
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stormwater treatment system includes:
Biofiltration
Cisterns to capture runoff from all developed areas of the project of the equivalent of 1.26” of rainfall over the project impervious areas.
Use of the irrigation storage reservoirs to store the cistern outflow from all area of the Project
Plan BPlan B
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What to do with
the water?
What to do with
the water?
Golf Golf CourseCourse
(of (of course)!course)!
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Water Balance for All Years ModeledWater Balance for All Years Modeled
Water Balance w/ 10 Day Cisterns & Reservoirs
6.23
113.91
2.94
Water BalanceExisting Conditions
7.22
50.65
3.49
Water Balance Developed Conditions
32.27
88.06
2.74
Runof f Evap & Trans Groundw ater
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Average Annual TSS & Nutrient Loads Average Annual TSS & Nutrient Loads
Modeled Constituent - Loads TSS TP TKN Nitrate-N
Modeled Area Site Conditions
(tons) (lbs) (lbs) (lbs)
Existing 0.903 6.30 48.5 10.6
Developed w/o PDFs 2.51 25.7 197 32.6
Dev w/ PDFs 0.410 4.94 33.8 7.02
Pelic
an P
oint
Pro
ject
A
rea
(49.
7 ac
res)
% Change -55% -22% -30% -34%
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SummarySummaryLow Impact Development Techniques Can Reduce hydrological changes
Possible to match pre-development surface hydrology
More difficult if desire is to match surface and sub-surface hydrology
EPA and other manuals have oversold some of the benefits based upon flood design hydrology approach used to estimate hydrological performance
Low Impact Development Techniques Can Reduce hydrological changes
Possible to match pre-development surface hydrology
More difficult if desire is to match surface and sub-surface hydrology
EPA and other manuals have oversold some of the benefits based upon flood design hydrology approach used to estimate hydrological performance
89
ConclusionsConclusions