Examples of Stormwater Control Devices
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Urban Flooding Mitigation Techniques: a Systematic Review and Future Studies
water Review Urban Flooding Mitigation Techniques: A Systematic Review and Future Studies Yinghong Qin 1,2 1 College of Civil Engineering and Architecture, Guilin University of Technology, Guilin 541004, China; [email protected]; Tel.: +86-0771-323-2464 2 College of Civil Engineering and Architecture, Guangxi University, 100 University Road, Nanning 530004, China Received: 20 November 2020; Accepted: 14 December 2020; Published: 20 December 2020 Abstract: Urbanization has replaced natural permeable surfaces with roofs, roads, and other sealed surfaces, which convert rainfall into runoff that finally is carried away by the local sewage system. High intensity rainfall can cause flooding when the city sewer system fails to carry the amounts of runoff offsite. Although projects, such as low-impact development and water-sensitive urban design, have been proposed to retain, detain, infiltrate, harvest, evaporate, transpire, or re-use rainwater on-site, urban flooding is still a serious, unresolved problem. This review sequentially discusses runoff reduction facilities installed above the ground, at the ground surface, and underground. Mainstream techniques include green roofs, non-vegetated roofs, permeable pavements, water-retaining pavements, infiltration trenches, trees, rainwater harvest, rain garden, vegetated filter strip, swale, and soakaways. While these techniques function differently, they share a common characteristic; that is, they can effectively reduce runoff for small rainfalls but lead to overflow in the case of heavy rainfalls. In addition, most of these techniques require sizable land areas for construction. The end of this review highlights the necessity of developing novel, discharge-controllable facilities that can attenuate the peak flow of urban runoff by extending the duration of the runoff discharge. -
Stormwater Best Management Practices (BMP) Toolbox
NORTH CAROLINA DEPARTMENT OF TRANSPORTATION STORMWATER BEST MANAGEMENT PRACTICES TOOLBOX North Carolina Department of Transportation Version 2, April 2014 Disclaimer DISCLAIMER This Toolbox is not intended to be a comprehensive design reference on structural Best Management Practices (BMPs). Its intended uses are as follows: This Toolbox was developed by North Carolina Department of Transportation (NCDOT) Hydraulics Unit for use on linear drainage systems designed and constructed by or in association with NCDOT-funded projects. This Toolbox is not intended for use on non-NCDOT roads or projects. Any use of this Toolbox by non-NCDOT entities is the responsibilities of the user, and is done so at the user’s risk. The user assumes the full responsibility in determining the applicability of this Toolbox for the purposes below: o Design and construction of drainage system and/or stormwater BMPs o Compliance with other Federal and State regulatory requirements o Meeting the NCDOT design standards for non-NCDOT roads and projects The design criteria in this Toolbox are guidelines. However, unique circumstances may require the designer to deviate from them. Should a specific situation require deviation from specified methods, procedures, and criteria presented in this Toolbox, approval for a variance is required from the State Hydraulics Engineer, or his designees. The user shall indemnify and hold harmless NCDOT and/or its employees from any claim, demand, suit, liability and expense (including attorney’s fees and other costs of litigation) -
Infiltration Trench
APPENDIX F Alternative Stormwater Treatment Control Measure Fact Sheets Appendix F – Alternative Stormwater Treatment Control Measure Fact Sheets Table of Contents LID-1: Infiltration Basin ................................................................................................. F-1 LID-2: Infiltration Trench ............................................................................................. F-10 LID-3: Dry Well ........................................................................................................... F-18 T-1: Stormwater Planter ............................................................................................. F-26 T-2: Tree-Well Filter ................................................................................................... F-36 T-3: Sand Filter .......................................................................................................... F-45 T-4: Vegetated Swales ............................................................................................... F-55 T-5: Proprietary Stormwater Treatment Control Measures ......................................... F-67 HM-1: Extended Detention Basin ............................................................................... F-72 HM-2: Wet Pond ........................................................................................................ F-86 June 2015 F-i LID-1: Infiltration Basin Description An infiltration basin is a shallow earthen basin constructed in naturally permeable soil designed for retaining and -
IN EUROPE with Special Reference to Underground Resources
Bull. Org. mond. Sante' 1957, 16, 707-725 Bull. Wld Hlth Org. SANITARY ENGINEERING AND WATER ECONOMY IN EUROPE With Special Reference to Underground Resources W. F. J. M. KRUL Professor, Technische Hogeschool, Delft; Director, Rijksinstituut voor Drinkwatervoorziening, The Hague, Netherlands SYNOPSIS The author deals with a wide variety of aspects of water economy and the development of water resources, relating them to the sanitary engineering problems they give rise to. Among those aspects are the balance between available resources and water needs for various purposes; accumulation and storage of surface and ground water, and methods of replenishing ground water supplies; pollution and purification; and organizational measures to deal with the urgent problems raised by the heavy demands on the world's water supply as a result of both increased population and the increased need for agricultural and industrial development. The author considers that at the national level over-all plans for developing the water economy of countries might well be drawn up by national water boards and that the economy of inter-State river basins should receive international study. In such work the United Nations and its specialized agencies might be of assistance. The Fourth European Seminar for Sanitary Engineers, held at Opatija, Yugoslavia, in 1954, dealt with surface water pollution, as seen from the angle of public health. It was pointed out that, especially in heavily indus- trialized countries, there is a great task to be fulfilled by sanitary engineers in the purification of waste waters of different kinds, in the sanitation of streams and in the adaptation of more or less polluted surface water to the needs of different kinds of consumers. -
C-9. Level Spreader-Filter Strip (LS-FS)
NCDEQ Stormwater Design Manual C-9. Level Spreader-Filter Strip (LS-FS) Design Objective A level spreader-filter strip (LS-FS) consists of an LS that is typically a poured concrete lip and a FS that is graded and grassed that filters and infiltrates stormwater. The LS does not remove pollutants by itself; however, it is an indispensable device needed to bring about pollutant removal in the FS. The vegetation and soils in the FS remove pollutants primarily via filtration and infiltration. The LS-FS is a Secondary SCM. Design Intensity The design intensity for an LS-FS is 0.75 inch per hour. Important Links Rule 15A NCAC 2H .1059. MDC for Permeable Pavement SCM Credit Document, C-9. Credit for Level Spreader-Filter Strips ________________________________________________________________________________________________________ C-9. Level Spreader-Filter Strip 1 Revised: 11/20/2020 NCDEQ Stormwater Design Manual Figure 1: Plan View of an LS-FS Adjacent to a Riparian Buffer Figure 2: Cross-Section of an LS-FS ________________________________________________________________________________________________________ C-9. Level Spreader-Filter Strip 2 Revised: 11/20/2020 NCDEQ Stormwater Design Manual Guidance on the MDC LS-FS MDC 1: Level Spreader Length The level spreader shall be a minimum of ten feet in length per one cubic foot per second of stormwater flow that is directed to it. Figure 3: Level Spreader Lip (NCSU) The designer should calculate the peak flow for the design intensity (0.75 inches per hour) and multiply that result by 10 feet per cfs to determine the required length of the level spreader. This length requirement is based on achieving a non-erosive velocity throughout the FS and an overland flow depth of approximately 1.2 inches across the FS. -
3.1 Infiltration Basin
3.1 INFILTRATION BASIN Type of BMP LID ‐ Infiltration Treatment Mechanisms Infiltration, Evapotranspiration (when vegetated), Evaporation, and Sedimentation Maximum Treatment Area 50 acres Other Names Bioinfiltration Basin Description An Infiltration Basin is a flat earthen basin designed to capture the design capture volume, VBMP. The stormwater infiltrates through the bottom of the basin into the underlying soil over a 72 hour drawdown period. Flows exceeding VBMP must discharge to a downstream conveyance system. Trash and sediment accumulate within the forebay as stormwater passes into the basin. Infiltration basins are highly effective in removing all targeted Figure 1 – Infiltration Basin pollutants from stormwater runoff. See Appendix A, and Appendix C, Section 1 of Basin Guidelines, for additional requirements. Siting Considerations The use of infiltration basins may be restricted by concerns over ground water contamination, soil permeability, and clogging at the site. See the applicable WQMP for any specific feasibility considerations for using infiltration BMPs. Where this BMP is being used, the soil beneath the basin must be thoroughly evaluated in a geotechnical report since the underlying soils are critical to the basin’s long term performance. To protect the basin from erosion, the sides and bottom of the basin must be vegetated, preferably with native or low water use plant species. In addition, these basins may not be appropriate for the following site conditions: Industrial sites or locations where spills of toxic materials may occur Sites with very low soil infiltration rates Sites with high groundwater tables or excessively high soil infiltration rates, where pollutants can affect ground water quality Sites with unstabilized soil or construction activity upstream On steeply sloping terrain Infiltration basins located in a fill condition should refer to Appendix A of this Handbook for details on special requirements/restrictions Riverside County - Low Impact Development BMP Design Handbook rev. -
Philadelphia Stormwater Manual V2.1 Philadelphia Stormwater Manual V2.1 This Pageintentionallyleftblank Simplified Approach Design Criteria Rooftop Systems
7 Stormwater Management Practice Design Guidelines 7.1 Green Roofs 7.2 Rain Barrels and Cisterns 7.3 Filter Strips 7.4 Filters 7.5 Bioinfiltration / Bioretention 7.6 Detention Basins 7.7 Berms and Retentive Grading 7.8 Swales 7.9 Constructed Wetlands (see PA Stormwater BMP Manual) 7.10 Ponds & Wet Basins (see PA Stormwater BMP Manual) 7.11 Subsurface Vaults 7.12 Subsurface Infiltration 7.13 Porous Pavement 7.14 Pre-fabricated and Proprietary Designs (see PA Stormwater BMP Manual) 7.15 Inlet and Outlet Controls Philadelphia Stormwater Manual v2.1 This Page Intentionally Left Blank Philadelphia Stormwater Manual v2.1 Simplified Approach Design Criteria Rooftop Systems This section provides the following information about eco-roofs and roof gardens: S Typical cross section S Description S General specifications S Checklist of minimal information to be shown on the permit drawings S Construction inspection requirements and schedule S Link to landscaping requirements S Link to example landscaping plans S Link to operation and maintenance requirements S Link to photos 7.1 S Link to drawings 7.1 S Eco-roof Central City F.A.R. bonus guidelines Green roofs (vegetated roof/eco roof/roof garden) consist of a layer of vegetation that completely covers an otherwise conventional flat or pitched roof. The hydrologic response of a green roof bears closer resemblance to a lawn or meadow than impervious surface. The green roof system is composed of multiple layers including waterproofing, a drainage City of Portland, OR layer, engineered planting media, and specially selected plants. Vegetated roof covers can be optimized to achieve water quantity and quality benefits. -
OP LEVEL SPREADERS (Outlet Pipe Discharges)
Anderson County Technical Specification WQ-10: OP LEVEL SPREADERS (Outlet Pipe Discharges) 1.0 Level Spreaders 1.1 Description Use Level Spreaders for Outlet Pipe Discharges as an energy dissipater to disperse concentrated runoff uniformly. Use Level Spreaders for peak design flow rates up to 30 cubic feet per second (cfs). Level spreaders are constructed at a virtually zero percent grade across a slope consisting of a permanent structure used to disperse or “spread” concentrated flow thinly over the Level Spreader lip. The main purpose is to spread potentially erosive concentrated flow over a wide area to reduce erosion at the outlet. Use Level Spreaders for Outlet Pipe Discharges to convey runoff from pipe outfalls uniformly onto downstream areas. Level Spreaders are applicable: • As outlets for diversion structures. • Where uniform, sheet flow can be achieved down slope of Level Spreaders. • As a segment of a stormwater BMP treatment series. • Where runoff from an impervious surface is uneven and/or runoff is released as concentrated flow, such as through curb cuts or slope drains. Do not use Level Spreaders: • Where discharge slopes exceed 6% for wooded/forested areas or 8% for thick ground cover/grass areas. • Where there are draws or concentrated flow channels located within the down slope area of a proposed Level Spreader. • Where the runoff water will re-concentrate after release from the level spreader before reaching an outlet designed for concentrated flow. • Where there will be traffic over the Level Spreader. Depending on the use, Level Spreader elements may include a forebay, Level Spreader lip, pipe drain and turf reinforcement matting (TRM) or Class A or B riprap. -
Storm Water Permitting Requirements for Construction Activities
Storm Water Permitting Requirements for Construction Activities John Mathews Storm Water Program Manager Division of Surface Water Why Permit Storm Water? Impacts During Construction • Not an issue until we add rainfall… Impacts During Construction Impacts During Construction • Large amounts of sediment are transported downstream and embed streams. Impacts During Construction • A healthy versus an embedded stream bottom. Post-Construction Impacts • Efficient runoff and pollution delivery Post-Construction Impacts • Stream Erosion (erosion and downcutting) Post-Construction Impacts • Stream Erosion (erosion and downcutting) History of the Construction General Permit (CGP) Increased Sediment Storage; Required Basic Erosion and Skimmers on Sediment Control, Sediment Basins; Very General Post- Allowed Offsite Major Update of Post- Construction, ≥5 Mitigation of Post- Construction acres of disturbance Construction Requirements 1992 2003 2008 2013 2018 ≥ 1 acre; Added Minor Changes Specific Post- construction, Large ≥ 5 and Small (1-5 ac) Sites Authorizes Storm Water Discharge From • Construction activities - clearing, grading, excavating, grubbing and/or filling – that disturb ≥ 1 acres – or will disturb < 1 acre of land but are part of a larger common plan of development or sale that will ultimately disturb ≥ 1 acres • Associated support activities (on-site or contiguous batch plants, borrow pits, & material storage areas) A Statewide Permit • But two watersheds have special conditions (the Big Darby and portions of the Olentangy) • Submittal -
Stormwater Management Dry Wells and Infiltration Basins
WENTWORTH WATERSHED RESTORATION AND PROTECTION STRATEGIES 1 Stormwater Management Dry Wells and Infiltration Basins DRY WELL A dry well is essentially small subsurface leaching basins. It consists of a small pit filled with stone, or a small structure surrounded by stone, used to temporarily store and infiltrate runoff from a very limited contributing area. Dry wells are well-suited to receive roof runoff via building gutter and downspout systems. Runoff enters the structure through an inflow pipe, inlet grate, or through surface infiltration. The runoff is stored in the structure and/or void spaces in the stone fill. Properly sited and designed dry wells provide treatment of runoff as pollutants become bound to the soils under and adjacent to the well, as the water percolates into the ground. The infiltrated stormwater contributes to recharge of the groundwater table. A commercially manufactured drywell being installed to capture water from roof downspout. Stormwater Runoff Dry Wells and Infiltration Basins (continued) 2 INFILTRATION BASINS Infiltration basins are structures designed to temporarily store runoff, allowing all or a portion of the water to infiltrate into the ground. The structure is designed to completely drain between storm events. In a properly sited and designed infiltration basin, water quality treatment is provided by runoff pollutants binding to soil particles beneath the basin as water percolates into the subsurface. Biological and chemical processes occurring in the soil also contribute to the breakdown of pollutants. Infiltrated water is recharged to the underlying groundwater. Subsurface infiltration basins may comprise a subsurface manifold system with associated crushed stone storage bed, or specially-designed chambers (with or without perforations) bedded in or above crushed stone. -
Level Spreader
Level Spreader Update: Design, Construction, and Maintenance Level spreaders are required structural stormwater practices that are often employed upslope of vegetative filter strips (VFS). This publication presents an update on the design, construction, and maintenance of level spreaders in North Carolina. Publications that provide an overview and parking lots. These surfaces in- on level spreaders include Urban crease the volume of stormwater runoff Stormwater Structural Best Manage- generated and the rate of conveyance ment Practices, AG-588-01, and Level to surface waters, leading to changes in Spreaders: Overview, Design, and the hydrologic cycle, including reduced Maintenance, AG-588-09W, of the groundwater recharge. Traditional urban Urban Waterways series. A companion developments also cause increased Urban Waterways publication to this pollutant loading to surface waters. fact sheet reviews recent research find- Structural stormwater best manage- ings on level spreaders (Level Spreader ment practices (BMPs) are often used Update: Performance and Research, to mitigate these impacts. Stormwater AG-588-21W). BMPs are treatment systems designed Urban development in North Caro- to reduce flooding and remove pollut- lina has led to construction of imperme- ants from runoff, thereby reducing the able surfaces such as rooftops, roads, loads of common pollutants, including A BMP FOR NEAR-SURFACE SEASONALLY HIGH WATER TABLES. Bioretention and permeable pavement, two common stormwater BMPs, cannot be used when seasonally high water tables are within 2-3 feet of ground sur- face, due to concerns with groundwater contamination. In eastern North Carolina, where slopes are low and high water tables are common, LS-VFS systems could potentially be employed in lieu of Evidence of seasonal high water table on a construction site these practices. -
Chapter 6 - Infiltration Bmps
Chapter 6 - Infiltration BMPs Infiltration measures control stormwater quantity and quality by retaining runoff on-site and discharging it into the ground through absorption, straining, microbial decomposition and trapping of particulate matter. Infiltration systems should not be used if the intercepted runoff is anticipated to contain pollutants that can affect groundwater quality, such as hydrocarbons, nitrate, and chloride. When the subsoils are appropriate, an infiltration basin can be suitable for treating and controlling the runoff from very small to very large drainage areas. However, some commercial or industrial sites may have contaminants that may not be treatable by soil filtration and should be avoided. Figure 6-1 shows a typical infiltration basin. IMPORTANT: This chapter describes three common Infiltration BMPs: infiltration basins, dry wells, and infiltration trenches. In addition to these infiltration techniques, there are several Low Impact Design (LID) techniques that rely on infiltration in small systems dispersed throughout a site, rather than an end- of-pipe technique such as the infiltration basin. Sizing: Infiltration systems must be designed to retain a runoff volume equal to 1.0 inch times the subcatchment's impervious area plus 0.4 inch times the subcatchment's landscaped developed area and infiltrate this volume into the ground. The infiltration system must drain completely within 24 to 48 hours following the runoff event. Complete drainage is necessary to maintain aerobic conditions in the underlying soil to favor bacteria that aid in pollutant attenuation and to allow the system to recover its storage capacity before the next storm event. Site Suitability: The following are some recommendations on the suitability of a site: Soil Permeability: The permeability of the soil at the depth of the base of the proposed infiltration system should be no less than 0.50 inches per hour and no greater than 2.41 inches per hour.