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IDEAL Stormwater BMP Modeling Framework

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Dry or Wet Detention Basin. Outflow From Watershed. Watershed Modeling Framework ... Wet/Dry Ponds, VFS, Bioretention cells, Sand filter, Bioswale, User ... – PowerPoint PPT presentation

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Title: IDEAL Stormwater BMP Modeling Framework


1
IDEAL Stormwater BMP Modeling Framework
  • June 13, 2008
  • Joe Fersner, PE

2
Integrated Design and Evaluation
Assessment of Loadings
  • History/Background of IDEAL
  • Modeling Approach
  • State of the model

3
IDEAL
  • A first of its kind post-construction water
    quality model for designing stormwater BMPs and
    calculating their trapping efficiencies.
  • Uses
  • BMP design for small to large developments
    projects
  • TMDL compliance
  • Antidegradation restrictions
  • Watershed master planning
  • LID design

4
Development History
5
A Regulatory Dilemma
1999
2002
2003
2004
2001
2000
  • Compliance with Antidegradation TMDLs
  • Needed an explicit BMP model
  • Model Hydrology Hydrualics and pollutant yield
    from urban areas.
  • Estimate BMP performance.
  • Base predictions on accepted predictive
    procedures.

6
IDEAL Initiated
2001
2004
2005
2002
2003
  • Woolpert hired by OCRM
  • Scope of Model
  • Literature review
  • Watershed Framework
  • Post Construction BMP Design Aid Manual and IDEAL
    Spreadsheet

7
IDEAL Development
  • Primary Researchers
  • Dr Bill Barfield Oklahoma State University
  • Dr. John Hayes Clemson University

8
IDEAL OCRM version
  • BMP Trapping
  • Sedimentology and soil isotherms
  • Hydrology
  • Single storm and Total annual runoff
  • 4 pollutants
  • 3 BMPs
  • Pond routing
  • Single watershed
  • Post-construction

9
Watershed Modeling Framework
Directly Connected Impervious Sub Basin
Directly Connected Impervious Sub Basin
Pervious Sub Basin
VFS
VFS
Dry or Wet Detention Basin
Outflow From Watershed
10
IDEAL OCRM Model Limitations
  • Only for use on the SC coast
  • Limited outlet configurations
  • Numerous spreadsheet constraints
  • Untested BMP algorithms
  • No resuspension, denitrification, direct loading
    on BMP, or bacteria growth.

11
Greenville County
2002
2004
2005
2001
2003
  • Woolpert hired by Greenville County
  • Isotherms and Rainfall Analysis
  • Continue to use spreadsheet

12
Greenville County
2003
2004
2005
2001
2002
  • Dry pond verification study

13
Greenville County
2004
2001
2002
2003
2005
  • Visual Basic Graphic
  • User Interface
  • (VB GUI) developed
  • Bioretention research begun
  • Multiple watersheds
  • Literature review
  • Swales
  • Engineered Devices

14
Greenville County
2003
2005
2004
2001
2002
Sept
  • EPA BMP Design Manual
  • EPA/600/R-04/121

15
Greenville County
2005
2006
2003
2004
2002
  • Bioretention cell added and revised
  • Greenhouse study
  • Greenville Co. study
  • Fecal Coliform loading function

16
Greenville County
17
Greenville County
18
Greenville County
2006
2005
2003
2004
2002
  • Sand filter and bioswale added
  • Conceptual algorithms developed for engineered
    devices
  • Conveyance routing algorithms
  • Pipe, Channel, Simple translation
  • Model presented to EPA Region 4
  • VB GUI revised to current layout
  • Distributed Jan 2007 to GC engineers

19
Greenville County
  • Object oriented VB.net Drag n Drop version

20
Summary of versions
21
Modeling Framework
22
Rainfall Statistics
  • Design Storms
  • Annual Distribution
  • of Storms

12 Storms 0.25 to 10.5
23
Hydrology
  • SCS Runoff Curve Number Method
  • Excess Runoff Hydrograph from
  • Gamma distribution unit hydrograph
  • Unit rainfall for Storm Type (I, Ia, II, III)

24
Sediment Yield
  • Pervious Areas - MUSLE
  • Impervious Areas - EMC Approach
  • EMC varies with type of impervious area
  • Modeling dependability improves as local data is
    collected
  • Model Sediment Size Distribution
  • Used to determine sediment trapping in Vegetated
    Filter Strip and in ponds
  • Nutrients and bacteria are sorbed on the exchange
    phase of the clay particles, hence need to know
    concentration of clay size particles
  • Pervious areas based on CREAMS equations
  • Impervious areas based on NURP data

25
Nutrient and Bacteria Loading
  • Modeling Nutrients
  • Yield based on event mean concentrations (EMCs)
    for each chemical
  • EMCs vary based on land use
  • Modeling Indicator Bacteria
  • Yield based on event mean concentrations (EMCs)
    for bacteria
  • EMCs highly variable
  • National average 15,000 number/100ml
  • Death due to natural mortality (1st order), UV
    exposure, and temperature
  • Growth rate (1st order) factored

26
BMP Trapping
  • Predicts trapping of sediments in ponds through
    overflow rate calculations for 5 particle
    classes.
  • Predicts nutrient trapping by settling of
    particulate matter and sorbed portion on trapped
    active clay content of the sediment by isotherms.
  • Predicts bacteria trapping using isotherms and
    mortality
  • Vegetated Filter Strip (VFS) trapping uses the KY
    VFS
  • model

27
Output
  • Graphical and
  • Text

28
State of the Model
29
IDEAL
  • Development team in Stillwater, OK
  • Project managed from Columbia, SC
  • Version available for Greenville County, SC and
    SC coastal areas (July 2008).

30
Ongoing Improvements
  • Improvements to conveyance routing and BMP
    interconnectivity relationships.
  • Enhanced Bioswale research with EPA-ORD, Edison,
    NJ
  • CAD interface
  • Engineered Devices

31
Future Steps
  • Expansion of Isotherms to more geographic areas
  • Rainfall statistics for additional geographic
    areas
  • Engineered device algorithms development
  • GIS interface
  • Optimization
  • Large scale watershed considerations
  • Continue to do performance enhancement
  • Continue to use best science available and
    support the model

32
Contact Info
  • Support
  • Ideal_support_at_woolpert.com
  • General Questions and Sales
  • Stormops_at_woolpert.com
  • Download the Greenville County version from
  • http//www.woolpert.com/asp/events/IDEAL.asp

33
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