Urban Flooding Mitigation Techniques: a Systematic Review and Future Studies
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Managing Storm Water Runoff to Prevent Contamination of Drinking Water
United States Office of Water EPA 816-F-01-020 Environmental Protection (4606) July 2001 Agency Source Water Protection Practices Bulletin Managing Storm Water Runoff to Prevent Contamination of Drinking Water Storm water runoff is rain or snow melt that flows off the land, from streets, roof tops, and lawns. The runoff carries sediment and contaminants with it to a surface water body or infiltrates through the soil to ground water. This fact sheet focuses on the management of runoff in urban environments; other fact sheets address management measures for other specific sources, such as pesticides, animal feeding operations, and vehicle washing. SOURCES OF STORM WATER RUNOFF Urban and suburban areas are predominated by impervious cover including pavements on roads, sidewalks, and parking lots; rooftops of buildings and other structures; and impaired pervious surfaces (compacted soils) such as dirt parking lots, walking paths, baseball fields and suburban lawns. During storms, rainwater flows across these impervious surfaces, mobilizing contaminants, and transporting them to water bodies. All of the activities that take place in urban and suburban areas contribute to the pollutant load of storm water runoff. Oil, gasoline, and automotive fluids drip from vehicles onto roads and parking lots. Storm water runoff from shopping malls and retail centers also contains hydrocarbons from automobiles. Landscaping by homeowners, around businesses, and on public grounds contributes sediments, pesticides, fertilizers, and nutrients to runoff. Construction of roads and buildings is another large contributor of sediment loads to waterways. In addition, any uncovered materials such as improperly stored hazardous substances (e.g., household Parking lot runoff cleaners, pool chemicals, or lawn care products), pet and wildlife wastes, and litter can be carried in runoff to streams or ground water. -
Design Standards for Stormwater Detention and Retention for Pima County
Pima County Regional Flood Control District Design Standards for Stormwater Detention and Retention Supplement to Title 16, Chapter 16.48, Runoff Detention Systems Floodplain and Erosion Hazard Management Ordinance Pima County Regional Flood Control District 97 E. Congress St., 3rd Floor Tucson, AZ 85701-1791 (520) 724 -4600 June 2014 _________________ Design Standards for Stormwater Detention and Retention for Pima County REVISIONS Because of ongoing regulatory and technical changes in the fields of floodplain and stormwater management, revisions to this manual will be required from time to time. Such revisions will be approved by the Floodplain Administrator. Hard copy (printed) revisions will not be distributed. It is the holder’s responsibility to keep the document current by periodically checking the Regional Flood Control District’s web page for new digital versions. The revision history of the document is listed below. Chronology of Publication, Updates and Revisions Description Date First Edition June 2014 Chapter 6 Revised to Include Benefits of February 2015 Multiple-Use Basins I _________________ Design Standards for Stormwater Detention and Retention for Pima County TABLE OF CONTENTS No. Description Page No. 1. INTRODUCTION ................................................................................................. 1 1.1 Purpose ......................................................................................................................1 1.2 Ordinance Overview and Detention Requirements ..................................................2 -
Pollutant Association with Suspended Solids in Stormwater in Tijuana, Mexico
Int. J. Environ. Sci. Technol. (2014) 11:319–326 DOI 10.1007/s13762-013-0214-3 ORIGINAL PAPER Pollutant association with suspended solids in stormwater in Tijuana, Mexico F. T. Wakida • S. Martinez-Huato • E. Garcia-Flores • T. D. J. Pin˜on-Colin • H. Espinoza-Gomez • A. Ames-Lo´pez Received: 24 July 2012 / Revised: 12 February 2013 / Accepted: 23 February 2013 / Published online: 16 March 2013 Ó Islamic Azad University (IAU) 2013 Abstract Stormwater runoff from urban areas is a major Introduction source of many pollutants to water bodies. Suspended solids are one of the main pollutants because of their Stormwater pollution is a major problem in urban areas. association with other pollutants. The objective of this The loadings and concentrations of water pollutants, such study was to evaluate the relationship between suspended as suspended solids, nutrients, and heavy metals, are typi- solids and other pollutants in stormwater runoff in the city cally higher in urban stormwater runoff than in runoff from of Tijuana. Seven sites were sampled during seven rain rural areas (Vaze and Chiew 2004). Stormwater has events during the 2009–2010 season and the different become a significant contributor of pollutants to water particle size fractions were separated by sieving and fil- bodies. These pollutants can be inorganic (e.g. heavy tration. The results have shown that the samples have high metals and nitrates) and/or organic, such as polycyclic concentration of total suspended solids, the values of which aromatic hydrocarbons and phenols from asphalt pavement ranged from 725 to 4,411.6 mg/L. The samples were ana- degradation (Sansalone and Buchberger 1995). -
Highlights from WERF Stormwater Research and Future Opportunities
Highlights from WERF Stormwater Research and Future Opportunities Jeff Moeller, P.E. Director of Water Technologies Water Environment Research Foundation [email protected] WEFTEC 2013 Stormwater Pavilion BMPs & Green Infrastructure "We still do not know one thousandth of one percent of what nature has revealed to us." - Albert Einstein What data is available on the performance of green infrastructure and BMPs? BMP Database Overview BMP Database includes over 530 BMP monitoring studies, including significant GI/LID BMPs From 2008-2013, a key focus has been to better integrate green infrastructure through: Monitoring Guidance (Updated) New Data Entry Spreadsheets Updated Analysis Results BMP Category Count BR Bioretention 31 BMP Summary BI Biofilter - Grass Strip 45 BS Biofilter-Grass Swale 41 Representative Green CO Composite 25 Infrastructure BMP Categories: DB Detention Basin 39 GR Green Roof 17 Bioretention IB Infiltration Basin 2 LD LID 2 Biofilters MD Manufactured Device 82 MF Media Filter 38 Green Roofs MP Maintenance Practice 28 Permeable Pavement OT Other 6 PP Porous Pavement 39 Rainwater Harvesting PT Percolation Trench 13 RP Retention Pond 75 Site-scale LID WB Wetland Basin 31 WC Wetland Channel 19 Total BMPs 533 CX Control/Ref. Sites 21 Quick Overview of 2012-13 Performance Summaries Updates: TSS, Nutrients, Metals, Bacteria, Volume Reduction New Detailed Analyses: Bioretention Volume Reduction Manufactured Device Unit Processes New On-line Tools: Map Interface Custom Statistical Queries On-line Search Tool BMP Database Vision International Stormwater BMP Database Urban Stormwater Construction Stormwater Agricultural BMPs BMPs Quality BMPs Partners: Partners: Partners: Partners: WERF University of Alabama IECA WERF NCGA EPA ASCE-EWRI MCGA FHWA Planned for 2013. -
Probabilistic Assessment of Urban Runoff Erosion Potential
307 Probabilistic assessment of urban runoff erosion potential J.A. Harris and B.J. Adams Abstract: At the planning or screening level of urban development, analytical modeling using derived probability distribution theory is a viable alternative to continuous simulation, offering considerably less computational effort. A new set of analytical probabilistic models is developed for predicting the erosion potential of urban stormwater runoff. The marginal probability distributions for the duration of a hydrograph in which the critical channel velocity is exceeded (termed exceedance duration) are computed using derived probability distribution theory. Exceedance duration and peak channel velocity are two random variables upon which erosion potential is functionally dependent. Reasonable agreement exists between the derived marginal probability distributions for exceedance duration and continuous EPA Stormwater Management Model (SWMM) simulations at more common return periods. It is these events of lower magnitude and higher frequency that are the most significant to erosion-potential prediction. Key words: erosion, stormwater management, derived probability distribution, exceedance duration. Résumé : Au niveau de la planification ou de la sélection en développement urbain, la modélisation analytique au moyen de la théorie de la distribution probabiliste dérivée est une alternative valable à la simulation continue car elle demande un effort computationnel beaucoup moindre. Dans le but de prédire le potentiel d’érosion par des eaux de ruissellement en milieu urbain, un nouvel ensemble de modèles probabilistes analytiques a été développé. Les distributions de probabilité marginales pour la durée d’un hydrogramme dans lequel la vélocité critique de courant dans le canal est dépassée (appelé durée de dépassement) sont calculées en utilisant la théorie de la distribution de probabilité dérivée. -
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) -
Comparison of Two Methods for Estimating Base Flow in Selected Reaches of the South Platte River, Colorado
Prepared in cooperation with the Colorado Water Conservation Board Comparison of Two Methods for Estimating Base Flow in Selected Reaches of the South Platte River, Colorado Scientific Investigations Report 2012–5034 U.S. Department of the Interior U.S. Geological Survey Comparison of Two Methods for Estimating Base Flow in Selected Reaches of the South Platte River, Colorado By Joseph P. Capesius and L. Rick Arnold Prepared in cooperation with the Colorado Water Conservation Board Scientific Investigations Report 2012–5034 U.S. Department of the Interior U.S. Geological Survey U.S. Department of the Interior KEN SALAZAR, Secretary U.S. Geological Survey Marcia K. McNutt, Director U.S. Geological Survey, Reston, Virginia: 2012 For more information on the USGS—the Federal source for science about the Earth, its natural and living resources, natural hazards, and the environment, visit http://www.usgs.gov or call 1–888–ASK–USGS. For an overview of USGS information products, including maps, imagery, and publications, visit http://www.usgs.gov/pubprod To order this and other USGS information products, visit http://store.usgs.gov Any use of trade, product, or firm names is for descriptive purposes only and does not imply endorsement by the U.S. Government. Although this report is in the public domain, permission must be secured from the individual copyright owners to reproduce any copyrighted materials contained within this report. Suggested citation: Capesius, J.P., and Arnold, L.R., 2012, Comparison of two methods for estimating base flow in selected reaches of the South Platte River, Colorado: U.S. Geological Survey Scientific Investigations Report 2012–5034, 20 p. -
Bmptrains Model
WHEN ARE HIGHER LEVELS OF STORMWATER LOAD REDUCTIONS REQUIRED AND USING LID BMPs TO ACHIEVE THEM BY: ERIC LIVINGSTON WATERSHED MANAGEMENT SERVICES, LLC Orlando, January 2020 PRESENTATION OVERVIEW WHEN? WHY? HOW? • Florida stormwater program • What and where are impaired waters? • Treatment requirements for impaired waters • Design criteria for Low Impact Design BMPs • LID design and BMPTRAINS load reduction effectiveness THE STORMWATER PROBLEM Humans cause: • Changes in land use, clearing of land • Compaction of soil, imperviousness • Development in floodplains, wetlands • Alteration of natural stormwater systems • Addition of efficient “drainage”systems • Addition of pollutants Resulting in: • Decreased recharge • Increased speed of runoff • Increased volume of runoff • Increased pollutant loads FLORIDA’S STORMWATER RULES 1979 Chapter 17- 4.248, F.A.C. 1982 Chapter 17- 25, F.A.C. 1994 Chapter 62- 25, F.A.C. 2013 Chapter 62-330, F.A.C DEP/WMD Applicant Handbooks ERP TECHNOLOGY BASED • Performance Standard • BMP Design Criteria • Presumption of compliance • Updating of BMP Design Criteria PERFORMANCE STANDARD FOR NEW STORMWATER DISCHARGES (62-40.432, FAC) Stormwater quality – Original Rule • 80% average annual load reduction • 95% average annual load reduction “Of Total Suspended Solids” Stormwater quality – 1990 – 62-40 revised • 80% average annual load reduction • 95% average annual load reduction “Of pollutants that cause or contribute to violations of water quality standards” BUT BMP DESIGN CRITERIA WERE NEVER UPDATED DESIGN CRITERIA PRESUMPTION REBUTTED! “This section provides an analysis of potential modifications to existing stormwater design criteria within the State of Florida to meet the performances objectives outlines in the Water Resource Implementation Rule (Chapter 62-40, FAC). -
Biogeochemical and Metabolic Responses to the Flood Pulse in a Semi-Arid Floodplain
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by DigitalCommons@USU 1 Running Head: Semi-arid floodplain response to flood pulse 2 3 4 5 6 Biogeochemical and Metabolic Responses 7 to the Flood Pulse in a Semi-Arid Floodplain 8 9 10 11 with 7 Figures and 3 Tables 12 13 14 15 H. M. Valett1, M.A. Baker2, J.A. Morrice3, C.S. Crawford, 16 M.C. Molles, Jr., C.N. Dahm, D.L. Moyer4, J.R. Thibault, and Lisa M. Ellis 17 18 19 20 21 22 Department of Biology 23 University of New Mexico 24 Albuquerque, New Mexico 87131 USA 25 26 27 28 29 30 31 present addresses: 32 33 1Department of Biology 2Department of Biology 3U.S. EPA 34 Virginia Tech Utah State University Mid-Continent Ecology Division 35 Blacksburg, Virginia 24061 USA Logan, Utah 84322 USA Duluth, Minnesota 55804 USA 36 540-231-2065, 540-231-9307 fax 37 [email protected] 38 4Water Resources Division 39 United States Geological Survey 40 Richmond, Virginia 23228 USA 41 1 1 Abstract: Flood pulse inundation of riparian forests alters rates of nutrient retention and 2 organic matter processing in the aquatic ecosystems formed in the forest interior. Along the 3 Middle Rio Grande (New Mexico, USA), impoundment and levee construction have created 4 riparian forests that differ in their inter-flood intervals (IFIs) because some floodplains are 5 still regularly inundated by the flood pulse (i.e., connected), while other floodplains remain 6 isolated from flooding (i.e., disconnected). -
Isotopes \&Amp\; Geochemistry: Tools for Geothermal Reservoir
E3S Web of Conferences 98, 08013 (2019) https://doi.org/10.1051/e3sconf/20199808013 WRI-16 Isotopes & Geochemistry: Tools For Geothermal Reservoir Characterization (Kamchatka Examples) Alexey Kiryukhin1,*, Pavel Voronin1, Nikita Zhuravlev1, Andrey Polyakov1, Tatiana Rychkova1, Vasily Lavrushin2, Elena Kartasheva1, Natalia Asaulova3, Larisa Vorozheikina3, and Ivan Chernev4 1Institute of Volcanology & Seismology FEB RAS, Piip 9, Petropavlovsk-Kamch., 683006, Russia 2Geological Institute RAS, Pyzhevsky 7, Moscow 119017, Russia 3Teplo Zemli JSC, Vilyuchinskaya 6, Thermalny, 684000, Russia 4Geotherm JSC, Ac. Koroleva 60, Petropavlovsk-Kamchatsky, 683980, Russia Abstract. The thermal, hydrogeological, and chemical processes affecting Kamchatka geothermal reservoirs were studied by using isotope and geochemistry data: (1) The Geysers Valley hydrothermal reservoirs; (2) The Paratunsky low temperature reservoirs; (3) The North-Koryaksky hydrothermal system; (4) The Mutnovsky high temperature geothermal reservoir; (5) The Pauzhetsky geothermal reservoir. In most cases water isotope in combination with Cl- transient data are found to be useful tool to estimate reservoirs natural and disturbed by exploitation recharge conditions, isotopes of carbon-13 (in CO2) data are pointed either active magmatic recharge took place, while SiO2 and Na-K geothermometers shows opposite time transient trends (Paratunsky, Geysers Valley) suggest that it is necessary to use more complicated geochemical systems of water/mineral equilibria. 1 Introduction Active pore space limitation mass transport velocities are typically greater than heat transport velocities. That is a fundamental reason why changes in the isotope and chemistry parameters of geofluids are faster than changes in the heat properties of producing geothermal reservoirs, which makes them pre-cursors to production parameter changes. In cases of inactive to rock chemical species, they can be used as tracers of fluid flow and boundary condition estimation. -
King County Drainage Maintenance Standards for Commercial and Multifamily Drainage Facilities
KING COUNTY DRAINAGE MAINTENANCE STANDARDS FOR COMMERCIAL AND MULTIFAMILY DRAINAGE FACILITIES Definitions, Defects & Maintenance Necessary to Bring to Standard June 2008 Contents A. Type I Catch Basin ............................................................................................................... 4 B. Type II Catch Basin ............................................................................................................. 5 C. Flow Restrictor .................................................................................................................... 7 D. Debris Barrier ..................................................................................................................... 8 E. Energy Dissipater/Dispersion Trench .................................................................................... 9 F. Pipe/Culvert ......................................................................................................................10 G. Ditch .................................................................................................................................10 H. Fencing .............................................................................................................................. 11 I. Access Road .......................................................................................................................13 J. Other—Specific to Ponds (Including Infiltration Ponds) ........................................................14 K. Other—Specific to Tanks (Including -
Problems and Solutions for Managing Urban Stormwater Runoff
Rained Out: Problems and Solutions for Managing Urban Stormwater Runoff Roopika Subramanian* The Clean Water Rule was the latest attempt by the Environmental Protection Agency and the Army Corps of Engineers to define “waters of the United States” under the Clean Water Act. While both politics and scholarship around this issue have typically centered on the jurisdictional status of rural waters, like ephemeral streams and vernal pools, the final Rule raised a less discussed issue of the jurisdictional status of urban waters. What was striking about the Rule’s exemption of “stormwater control features” was not that it introduced this urban issue, but that it highlighted the more general challenges of regulating stormwater runoff under the Clean Water Act, particularly the difficulty of incentivizing multibenefit land use management given the Act’s focus on pollution control. In this Note, I argue that urban stormwater runoff is more than a pollution-control problem. Its management also dramatically affects the intensity of urban water flow and floods, local groundwater recharge, and ecosystem health. In light of these impacts on communities and watersheds, I argue that the Clean Water Act, with its present limited pollution- control goal, is an inadequate regulatory driver to address multiple stormwater-management goals. I recommend advancing green infrastructure as a multibenefit solution and suggest that the best approach to accelerate its adoption is to develop decision-support tools for local government agencies to collaborate on green infrastructure projects. Introduction ..................................................................................................... 422 I. Urban Stormwater Runoff .................................................................... 424 A. Urban Stormwater Runoff: Multiple Challenges ........................... 425 B. Urban Stormwater Infrastructure Built to Drain: Local Responses to Urban Flooding .......................................................