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Stormwater Best Management Practices in an Ultra-Urban Setting: Selection and Monitoring
Table of Contents
List of Tables
List of Figures
- Introduction and Purpose
- Background
- Report Development
- Report Organization
- Stormwater Management in the Ultra-Urban Environment
- Introduction
- The Ultra-Urban Environment
- Target Water Quality Parameters
- Urban Stormwater Management
- Ultra-Urban BMP Technologies
- Ultra-Urban Design Considerations
- Best Management Practices in an Ultra-Urban Setting
- Overview of BMPs
- Infiltration Practices/Bioretention
- Description and Purpose
- Design Alternatives
- Detention and Retention/Wetland Practices
- Description and Purpose
- Design Alternatives
- Filtration Practices
- Description and Purpose
- Design Alternatives
- Vegetated Swales/Filter Strips
- Description and Purpose
- Design Alternatives
- Water Quality Inlets
- Description and Purpose
- Design Alternatives
- Porous Pavements
- Description and Purpose
- Design Alternatives
- Streetsweeping
- Description and Purpose
- Design Alternatives
- Other Nonstructural BMPs
- Introduction
- Options and Strategies for Implementation
- Effectiveness
- Cost Considerations
- New and Innovative Practices
- Description and Purpose
- Alum Injection Systems
- MCTT System
- Biofilters
- Vegetated Rock Filters
- Vertical Filter Systems
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- Monitoring Program Development
- Introduction
- The Phases of a Monitoring Program
- Monitoring Program Planning Phase
- Management Goals
- Physical Site and BMP Characterization
- Project Resources and Physical Site Constraints
- Monitoring Objectives
- Monitoring Program Design Phase
- Data Quality Objectives
- Sampling Design Plan
- Data Management Plan
- Quality Assurance Project Plan
- Monitoring Program Implementation Phase
- Equipment Installation and Testing Procedures
- Finalization of Field Operating Procedures
- Preliminary Review of Testing and/or Initial Monitoring Results
- Sampling Design Plan and Implementation Review
- Monitoring Program Evaluation Phase
- Data Analysis Techniques
- Reference Conditions
- Prioritizing Constituents
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- Selected BMP Monitoring Studies
- Introduction
- Case Study Presentations
- Monitoring Case Study - Two exfiltration trenches located near Miami International Airport in Dade County, Florida
- Monitoring Case Study - Modified dry pond BMP and grassed swale BMP, Charlottesville, Virginia
- Monitoring Case Study - Delaware sand filter BMPs at Airpark, Alexandria, Virginia
- Monitoring Case Study - Modified Delaware sand filter BMPs at Alaska Marine Lines, Seattle, Washington
- Monitoring Case Study - Compost stormwater treatment system, Hillsboro, Oregon
- Monitoring Case Study - Vertical volume recovery structure (VVRS), Orlando, Florida
- Monitoring Case Study - Vegetated water quality buffer strips, Austin, Texas
- Monitoring Case Study - Streetsweeping BMP evaluation, Port of Seattle, Washington
- Monitoring Case Study - Packed bed filter BMP near Lake Beardall, Orlando, Florida
- Selection of Best Management Practices
- Introduction
- The Elements of a BMP Selection Process
- The Scoping Phase
- Management Goals and Objectives
- Site Characterization
- Screening of Structural BMPs
- Screening Nonstructural BMPs
- Evaluation Phase
- Evaluation of Structural BMPs
- Evaluation of Nonstructural BMPs
- Multiple BMP Treatment Train
- Final Selection Phase
- Cost Effectiveness
- Management and Public Acceptance
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- Constituents and sources in highway runoff
- Constituents of highway runoff
- Overview of BMPs
- Site considerations
- Management considerations
- Pollutant removal effectiveness (%)
- Estimated pollutant removal effectiveness for water quality trenches (%)
- Estimated pollutant removal effectiveness for infiltration basins (%)
- Detention and retention BMP options
- Pollutant removal effectiveness of detention ponds (%)
- Pollutant removal effectiveness for wetlands (%)
- Pollutant removal effectiveness for underground sand filters (%)
- Pollutant removal effectiveness for surface sand filters (%)
- Pollutant removal effectiveness of organic filters (%)
- Pollutant removal effectiveness for swales (%)
- Pollutant removal effectiveness for filter strips (%)
- Pollutant removal effectiveness for porous pavement (%)
- Efficiencies of mechanical (broom) and vacuum-assisted sweepers
- PM-10 Particulate removal efficiencies for various sweepers
- Constituents and sources in highway runoff
- Constituents of highway runoff, ranges of average values reported in the literature
- Example of BMP characteristics relevant to developing a monitoring program
- Primary constituent removal mechanisms in selected BMP categories
- Typical costs associated with establishment of an automated BMP monitoring station
- Summary of water quality and sediment sampling techniques
- Data analysis with greater than 15% nondetects
- Swale section and slope data
- Pond pollutant removal efficiency (individual storms)
- Swale pollutant removal efficiency (individual storms)
- Design parameters
- Pollutant removal efficiencies (%)
- Filter medium characteristics
- Effectiveness for filter no. 3 (%)
- Effectiveness for filter no. 6 (%)
- Mass balance pollutant removal efficiencies for three seasons of testing (%)
- Removal efficiency of the sump
- Removal efficiency of the VVRS
- VVRS system removal efficiency
- Mean of sample concentrations based on buffer width
- Mean of sample concentrations based on vegetative cover
- Comparison of pollutant load reductions from various sweeping frequencies and wet vaults (%)
- Medium type and vegetation for packed bed filter system
- Overall system mass balance removal efficiency
- Overall system removal efficiency (%) for three different flow rates
- Example of how management objectives can be used to derive screening criteria
- Primary function of BMPs and ability to address management objectives
- Site considerations for structural BMPs
- Constituents and sources in highway runoff
- Constituents of highway runoff, ranges of average values reported in the literature
- General transport and BMP removal processes for selected constituents
- Pollutant removal effectiveness (%)
- Relative rankings of cost elements and effective life of structural BMP options
- Nonstructural BMPs and their constituent removal mechanisms
- Mass-balance pollutant removal efficiencies for constituents and BMPs of interest
- Nonstructural BMP constituent removal effectiveness
- Example of potential ranking factors for final selection
- Relative rankings of cost elements and effective life of BMP options
- BMP selection process illustration: Example #1
- Final selection phase illustration: Example #2
- BMP selection process illustration: Example #3
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- Changes in runoff flow resulting from increased impervious area (adapted from North Carolina Department of Natural Resources and Community Development, as cited in Livingston and McCarron, 1992)
- Location of ultra-urban monitoring studies based on BMP type (number of symbols indicates the number of BMP evaluations)
- Underground trench with oil/grit chamber (adapted from Schueler, 1987)
- Median strip trench design (adapted from Schueler, 1987)
- Schematic of an infiltration basin design (Young et al., 1996)
- Parking edge and perimeter without curb (Prince George's County, Maryland, 1993)
- Design Variations
- Cross-section view of a standard extended detention pond system (Schueler, 1992)
- Schematic design of a shallow ED marsh system (adapted from Schueler, 1992)
- Movement of water through a detention pond-wetlands system (Martin and Smoot, 1986)
- Basic CMP stormwater detention system (adapted from Pacific Corrugated Pipe, 1995)
- Original D.C. underground sand filter system (Young et al., 1996)
- Delaware sand filter with grated inlets (Bell et al., 1995)
- Austin sand filter with full sedimentation protection (Young et al., 1996)
- Typical peat-sand filter cross section (Young et al., 1996)
- Cross section of a StormFilter siphon-actuated cartridge (Stormwater Management, 1998)
- Channels and swales (Claytor & Schueler, 1996)
- Dry swale (adapted from Claytor & Schueler, 1996)
- Wet swale (adapted from Claytor & Schueler, 1996)
- Typical filter strip (adapted from Claytor & Schueler, 1996)
- Schematic of an oil/grit separator (OGS) (adapted from Schueler, 1987)
- Typical features of a catch basin insert (King County, Washington, 1995)
- Stormceptor7 operation during average flow conditions (Stormceptor7, 1995)
- Downstream Defender (H.I.L. Technology, 1996)
- Vortechs Stormwater Treatment System (Vortechnics, 1996)
- Types of grid and modular pavements (Virginia Soil and Water Commission, 1990)
- Typical applications of modular block porous pavement (not to scale) (Urban Drainage and Flood Control District, 1992)
- Schematic of typical porous pavement section (Young et al., 1996)
- Modular block porous pavement (adapted from Urban Drainage and Flood Control District, 1992)
- Levels of involvement in nonstructural BMP programs that may be part of watershed planning for stormwater management (adapted from Greenfield & LeCouteur, 1994)
- Maintenance yard nonstructural BMPs (adapted from CDM, 1993)
- Materials handling measures (adapted from CDM, 1993)
- General schematic of the MCTT (Pitt, 1996)
- StormTreat7 System Tank (adapted from StormTreat Systems, 1996)
- Vegetated rock filter (adapted from Claytor and Schueler, 1996)
- Typical vertical filtration system (Tenney et al., 1995)
- Key phases for the development of a monitoring program
- Components of the program planning phase
- Development of monitoring objectives
- Components of the monitoring program design phase
- Upstream-downstream design
- Paired watershed approach
- Distribution of BOD and suspended solids with depth (Marsalek, 1973)
- Sample monitoring configuration (Young et al., 1996)
- Flow proportional composite sampling to determine EMC (D'Andrea et al., 1993)
- Rainfall frequency
- Example of flow duration curve
- Example of sampling strategy based on flow duration curve
- Locations of the two study areas in east-central Dade County (McKenzie and Irwin, 1988)
- Schematic section of a typical exfiltration trench (adapted from McKenzie and Irwin, 1988)
- Sketch of Massie Road parking lot and detention pond (Yu et al., 1993)
- Layout of detention pond (Yu et al., 1993)
- Outfall structure details at detention pond (adapted from Yu et al., 1993)
- Modified swale with barrier to lateral flow (Yu et al., 1993)
- Cross section of swale at each of four weir locations (Yu et al., 1993)
- General layout of AirPark filters (adapted from Bell et al., 1995)
- Cross-section of filter chamber (adapted from Spearman and Beard, 1995)
- Prototype compost stormwater filter (cross section) (Stewart, 1992)
- Prototype compost stormwater filter (plan view) (adapted from Stewart, 1992)
- Prototype compost stormwater filter (long cross section) (adapted from Stewart, 1992)
- Vertical Volume Recovery Structure system at rest prior to rainfall event (adapted from Dyer, Riddle, Mills, & Precourt, 1996)
- Vertical Volume Recovery Structure full utilization of treatment volume (Dyer, Riddle, Mills, & Precourt, 1996)
- Vertical Volume Recovery Structure backwash operation (Dyer, Riddle, Mills, & Precourt, 1996)
- Test plot configuration (Glick et al., 1993)
- Collection flume and collection bottle layout (Glick et al., 1993)
- Sampling locations (Dyer, Riddle, Mills, & Precourt, 1995)
- Key phases of a BMP selection process
NOTICE
This document is disseminated under the sponsorship of the Department of Transportation in the interest of information exchange. The United States Government assumes no liability for its contents or use thereof. The contents of this report reflect the view of the contractor, who is responsible for the accuracy of the data presented herein. The contents do not necessarily reflect the official views or policy of the Department of Transportation. This report does not constitute a standard, specification, or regulation.
The United States Government does not endorse products of manufactures. Trade or manufacturers' names appear herein only because they are considered essential to the object of this document.
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Questions and feedback should be directed to Marlys Osterhues (marlys.osterhues@dot.gov, 202-366-2052).
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