Draft District of Columbia Stormwater Management Guidebook Page 10 Chapter 2
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SECTION 3 Erosion Control Measures
SECTION 3 Erosion Control Measures 1. SEEDING When • Bare soil is exposed to erosive forces from wind and or water. Why • A cost effective way to prevent erosion by protecting the soil from raindrop impact, flowing water and wind. • Vegetation binds soil particles together with a dense root system, increasing infiltration thereby reducing runoff volume and velocity. Where • On all disturbed areas except where non-vegetative stabilization measures are being used or where seeding would interfere with agricultural activity. Scheduling • During the recommended temporary and permanent seeding dates outlined below. • Dormant seeding is acceptable. How 1. Site Assessment. Determine site physical characteristics including available sunlight, slope, adjacent topography, local climate, proximity to sensitive areas or natural plant communities, and soil characteristics such as natural drainage class, texture, fertility and pH. 2. Seed Selection. Use seed with acceptable purity and germination tests that are viable for the planned seeding date. Seed that has become wet, moldy or otherwise damaged is unacceptable. Select seed depending on, location and intended purpose. A mixture of native species for permanent cover may provide some advantages because they have coevolved with native wildlife and other plants and typically play an important function in the ecosystem. They are also adapted to the local climate and soil if properly selected for site conditions; can dramatically reduce fertilizer, lime and maintenance requirements; and provide a deeper root structure. When re- vegetating natural areas, introduced species may spread into adjacent natural areas, native species should be used. Noxious or aquatic nuisance species shall not be used (see list below). If seeding is a temporary soil erosion control measure select annual, non-aggressive species such as annual rye, wheat, or oats. -
Green Roof for Stormwater Management in a Highly Urbanized Area: the Case of Seoul, Korea
sustainability Article Green Roof for Stormwater Management in a Highly Urbanized Area: The Case of Seoul, Korea Muhammad Shafique 1,2, Reeho Kim 1,2,* and Kwon Kyung-Ho 3 1 Department of Smart City and Construction Engineering, Korea Institute of Civil Engineering and Building Technology, University of Science & Technology (UST), 217, Gajeong-ro, Yuseong-gu, Daejeon 34113, Korea; shafi[email protected] 2 Environmental & Plant Engineering Research Institute, Korea Institute of Civil Engineering and Building Technology, 83, Goyangdae-ro, Ilsanseo-gu, Goyang-si, Gyeonggi-do 10223, Korea 3 Urban Water Cycle Research Center, Korea Institute of Safe Drinking Water Research, Anyang si, Gyeonggi-do 14059, Korea; [email protected] * Correspondence: [email protected]; Tel.: +82-31-9100-291 Received: 26 December 2017; Accepted: 21 February 2018; Published: 26 February 2018 Abstract: Urbanization changes natural pervious surfaces to hard, impervious surfaces such as roads, buildings and roofs. These modifications significantly affect the natural hydrologic cycle by increasing stormwater runoff rates and volume. Under these circumstances, green roofs offer multiple benefits including on-site stormwater management that mimics the natural hydrologic conditions in an urban area. It can retain a large amount of rainwater for a longer time and delay the peak discharge. However, there is very limited research that has been carried out on the retrofitted green roof for stormwater management for South Korean conditions. This study has investigated the performance of retrofitted green roofs for stormwater management in a highly urbanized area of Seoul, the capital city of Korea. In this study, various storm events were monitored and the research results were analyzed to check the performance of the green roof with controlling the runoff in urban areas. -
The Trade in Live Reef Food Fish Volume 1
THE TRADE IN LIVE REEF FOOD FISH GOING GOING GONE VOLUME 1 MAIN REPORT Acknowledgements This report was prepared by ADM Capital Foundation and the University of Hong Kong. We would like to thank Sam Inglis, Lisa Genasci, Jane Chu, Kathleen Ho and and Ellie Appleby for their diligence in reading and editing; Doug Woodring, who drove the initial concept; and DESIGNORM for their innovative and informative graphics. Rachel Wong helped to compile some of the data, and Liu Min, Joyce Wu and Felix Chan kindly provided data. We are grateful to the government staff of the Marine Department, the Agriculture, Fisheries and Conservation Department, the Fish Marketing Organization and the Customs and Excise Department for responding to our questions and clarifying issues raised, as well as reviewing an earlier draft, and to the many traders and participants of the trade who we interviewed. Disclaimer This document (the ‘Document’) has been prepared by ADM Capital Foundation (‘ADMCF’) for general introduction, overview and discussion purposes only and does not constitute definitive advice on regulatory, investment or legal issues. It should not be used as a substitute for taking regulatory, financial, tax or legal advice in any specific situation. Information provided in the report has been obtained from, or is based upon, sources believed to be reliable but have not been independently verified, and no guarantee, representation or warranty is made as to its accuracy or completeness. Information contained in this Document is current as of December 2017 and is subject to change without notice. Information contained in this Document relating to unrealised data and projections is indicative only, and has been based on unaudited, internal data and assumptions, which have not been independently verified and are subject to material corrections, verifications and amendments. -
Chapter 8 Drainage & Wastewater Infrastructure
Chapter 8 Drainage & Wastewater Infrastructure Chapter 8 Drainage and Wastewater Infrastructure .................................. 8-1 8.1 Key Terms ...................................................................................................................... 8-2 8.1.1 Abbreviations .................................................................................................................................... 8-2 8.1.2 Definitions ......................................................................................................................................... 8-3 8.2 General Information ..................................................................................................... 8-6 8.2.1 Comprehensive Plans, Codes, and Policies ................................................................................ 8-7 8.2.2 System Maps ...................................................................................................................................... 8-8 8.3 General Requirements .................................................................................................. 8-8 8.3.1 Standard Specifications and Plans ................................................................................................. 8-8 8.3.2 Regulations ........................................................................................................................................ 8-9 8.3.3 Industry Standards and other Agency Standards ..................................................................... 8-10 -
The Legal Basis in New Hampshire: Adopting Stormwater Zoning Ordinances and Land Development Regulations
The Legal Basis in New Hampshire: Adopting Stormwater Zoning Ordinances and Land Development Regulations FEDERAL LAW NPDES AND EPA The lack of a precise definition of MEP allows small Through the Phase 1 and Phase 2 NPDES MS4s flexibility in tailoring their programs to their CLEAN WATER ACT programs EPA sets water quality standards for actual needs. The Clean Water Act (CWA) originated as the point source and wastewater discharge permits. The MEP standard requires small MS4s to satisfy Federal Water Pollution Control Act of 1972 in EPA administers NH’s NPDES permit program the following six “minimum control measures”: response to unchecked dumping of pollution into and permits for stormwater and sewer overflow 1) Public Education and Outreach the nation’s surface waters. At that time, about discharges. Individual homes that are connected to 2) Public Participation 2 /3 of U.S. waters had been declared unsafe for a municipal system, use a septic system, or do not fishing and swimming. The CWA provides the basic produce surface discharge do not need an NPDES 3) Illicit Discharge Detection and Elimination structure for: permit. Industrial, municipal, and other facilities (IDDE) Program must obtain permits if their discharges go directly 4) Construction Site Runoff Controls 1) regulating discharges of pollution into the to surface waters. waters of the United States, and 5) Post-Construction Runoff Controls 6) Good House Keeping and Pollution Prevention 2) regulating quality standards for the nation’s NPDES STORMWATER PERMIT TYPES for Municipal Operations surface waters. Its objective is “to restore and The NPDES permit regulations cover 3 main maintain the chemical, physical, and biological classes of stormwater and wastewater discharges. -
Green Roof Irrigation Solutions on the Market
GREEN ROOF IRRIGATION Comprehensive Solutions for Rooftop Environments RESIDENTIAL & COMMERCIAL IRRIGATION | Built on Innovation® hunterindustries.com THE BETTER THE IRRIGATION, the Greener the Roof Green roofs have become key components of sustainability in urban environments. They help keep buildings cool, provide habitat for increased biodiversity, and improve local air quality. As the world’s leading manufacturer of irrigation products, we are committed to developing highly efficient solutions for all landscapes, including green roofs. With best-in-class subsurface and overhead irrigation options using top-level control systems, we offer the most versatile and robust green roof irrigation solutions on the market. Built on Innovation® When designing a green roof irrigation system, you can choose a subsurface, overhead, or combined approach. We provide an array of solutions for each method. SUBSURFACE OVERHEAD An absolute revolution in subsurface irrigation, When paired with Pro-Spray® pop-ups and shrub Eco-Mat® provides green roof designers with the adapters, high-efficiency MP Rotator® nozzles most efficient irrigation solution ever developed. provide an effective solution for green roof irrigation. Eco-Mat incorporates fleece-wrapped dripline with an Thanks to their slow and steady application rate, integrated synthetic fleece mat. Installed just beneath MP Rotator nozzles provide unmatched distribution the optimal root depth of the selected plant material, uniformity for overhead irrigation. Green roof soils Eco-Mat uses specialized technology to efficiently tend to be loose, so a slow precipitation rate from the irrigate from the bottom up with the following benefits: nozzle prevents fast drainage through the soil. The multi-trajectory, multi-stream application method • Effectively holds water for future use by plants of the MP Rotator cuts through wind while gently • Eliminates water loss due to wind and evaporation hydrating the landscape at an even rate that soils • Spreads water efficiently and evenly throughout the can better absorb. -
Green Architecture and Water Reuse: Examples from Different Countries
Green architecture and water reuse: examples from different countries This paper shows different examples from different countries (Italy, India, Tanzania) of green architectural solutions (green wall, green roof, roof wetland) in which water (rain and treated greywater) are reused as a resource, in order to reduce the use of drinking water for activities not needing a high quality of water. Authors: Fabio Masi, Anacleto Rizzo, Riccardo Bresciani Abstract Water is a valuable resource which should be better managed to develop a sustainable future. Green architecture is starting to be largely applied, principally for aesthetic improvement of urban centres. However, green architectural solutions provide different additional benefits, among which the reuse of rain and treated grey water. Hence, green architecture can be also viewed as an option to limit the waste of drinking water for applications where the required quality can be lower. In this paper we report the application of three different green architectural solutions in which rain and treated grey water are reused (roof wetland, green roof, and green wall) in three different countries (Tanzania, Italy, and India). Technical data: Roof constructed wetland (Tanzania): • Greywater reused for irrigation • Greywater consumption of max 4 m3 per day • Sewer network for greywater and blackwater segregation • Two-chamber tank (2 m3) as pre-treatment • Pumping station (1.1 kW power, 30 l/min) to feed CW on the roof • Horizontal flow constructed wetland (23 m2, HRT 0.8 d) for greywater treatment -
Green Infrastructure Designs
GREEN INFRASTRUCTURE DESIGNS SCALABLE SOLUTIONS TO LOCAL CHALLENGES UPDATE SEPTEMBER 2017 ABOUT DELTA INSTITUTE Founded in 1998, Delta Institute is a Chicago-based nonprofit organization working to build a more resilient environment and economy through sustainable solutions. Visit online at www.delta-institute.org. This publication was originally released in July 2015 with support from the National Oceanic and Atmospheric Administration through the Illinois Department of Natural Resources (IDNR, CFDA Number 11.419). The September 2017 update adds two new green infrastructure designs to the toolkit. Delta thanks Tim King PE, LEED AP BD+C and Luke Leising, AIA, PE, LEED AP O+M of Guidon Design for their work designing the initial five templates. Guidon Design, Inc. is a multi-disciplinary architecture and engineering firm. Delta also acknowledges the work of graduate students Loren Ayala and Liliana Hernandez-Gonzalez, civil and environmental engineering students at Northwestern University and Kimberly Grey, Chair of Chair of Civil & Environmental Engineering at Northwestern in developing the box tree filter and green roof designs. Additionally, Delta acknowledges Claire Costello, an undergraduate student at University of Chicago for her assistance reviewing, editing and preparing additional components for publication. Additionally, we are grateful to the following Calumet region communities for their contributions and review of the toolkit: Jodi Prout, City of Blue Island Jason Berry, City of Blue Island Dawn Haley, Village of Riverdale Mary Ryan, Village of Calumet Park Bryan Swanson, City of Calumet City Stan Urban, Village of Dolton Hildy Kingma, Village of Park Forest Ernestine Beck-Fulgham, Village of Robbins Finally, Delta Institute thanks Josh Ellis of the Metropolitan Planning Council, and the Calumet Stormwater Collaborative for their support of the project. -
Conceptual Green Infrastructure Design for the Blake Street Transit
2012 GREEN INFRASTRUCTURE TECHNICAL ASSISTANCE PROGRAM Urban Land Conservancy Denver, Colorado Conceptual Green Infrastructure Design for the Blake Street Transit-Oriented Development Site, City of Denver AUGUST 2013 Photo: Denver Housing Authority, Park Avenue Development EPA 830-R-13-002 About the Green Infrastructure Technical Assistance Program Stormwater runoff is a major cause of water pollution in urban areas. When rain falls in undeveloped areas, the water is absorbed and filtered by soil and plants. When rain falls on our roofs, streets, and parking lots, however, the water cannot soak into the ground. In most urban areas, stormwater is drained through engineered collection systems and discharged into nearby waterbodies. The stormwater carries trash, bacteria, heavy metals, and other pollutants from the urban landscape, polluting the receiving waters. Higher flows also can cause erosion and flooding in urban streams, damaging habitat, property, and infrastructure. Green infrastructure uses vegetation, soils, and natural processes to manage water and create healthier urban environments. At the scale of a city or county, green infrastructure refers to the patchwork of natural areas that provides habitat, flood protection, cleaner air, and cleaner water. At the scale of a neighborhood or site, green infrastructure refers to stormwater management systems that mimic nature by soaking up and storing water. These neighborhood or site-scale green infrastructure approaches are often referred to as low impact development. EPA encourages the use of green infrastructure to help manage stormwater runoff. In April 2011, EPA renewed its commitment to green infrastructure with the release of the Strategic Agenda to Protect Waters and Build More Livable Communities through Green Infrastructure. -
Stormwater Runoff Control: a Model Ordinance for Meeting Local Water Quality Management Needs
Volume 20 Issue 4 Fall 1980 Fall 1980 Stormwater Runoff Control: A Model Ordinance for Meeting Local Water Quality Management Needs Frank E. Maloney Richard G. Hamann Bram D. Canter Recommended Citation Frank E. Maloney, Richard G. Hamann & Bram D. Canter, Stormwater Runoff Control: A Model Ordinance for Meeting Local Water Quality Management Needs, 20 Nat. Resources J. 713 (1980). Available at: https://digitalrepository.unm.edu/nrj/vol20/iss4/2 This Article is brought to you for free and open access by the Law Journals at UNM Digital Repository. It has been accepted for inclusion in Natural Resources Journal by an authorized editor of UNM Digital Repository. For more information, please contact [email protected], [email protected], [email protected]. STORMWATER RUNOFF CONTROL: A MODEL ORDINANCE FOR MEETING LOCAL WATER QUALITY MANAGEMENT NEEDS FRANK E. MALONEY,* RICHARD G. HAMANN** and BRAM D. E. CANTER*** INTRODUCTION Water pollution abatement programs in the United States have been directed almost entirely toward the elimination of point sources of water pollution-defined in the Federal Water Pollution Control Act' as "any discernible, confined and discrete conveyance... from which pollutants are or may be discharged." 2 Yet officials of the En- vironmental Protection Agency estimate that fifty percent or more of the nation's water pollution is waste picked up from the land by rainfall, which then reaches ground and surface waters through run- off and seepage and not through a pipe or other point source of pollution.3 The waters which drain urban streets, construction sites, agricul- tural areas and other sites of intensive human use are often heavily *Professor of Law and Dean Emeritus, University of Florida Law Center; Director, Water Law Studies of the University of Florida; B.A., 1939, University of Toronto; J.D., 1942, University of Florida. -
Green Roofs the Basics
Green Roofs The Basics Green roofs, or living roofs, are vegetated rooftop systems that reduce stormwater runoff by 50-60% and can triple the life expectancy of a roof. They can be installed on just about any rooftop, but require that the structure be able to withstand extra weight. Green roofs are categorized into two types, extensive and intensive. Extensive systems are thinner, with a layer of growing media that is 6” or less. Intensive roofs have a thicker growing media layer and may include trees or rooftop meadows. Due to the weight associated with intensive rooftops, they are typically only installed in new construction projects. Blue Water Baltimore wants to help you make a difference. This document provides a brief overview of green roofs and helps you complete the Project Approval Form for the Water Audit Program. Additional resources are available at www.bluewaterbaltimore.org/water-audit- resource/. Why Should I Install a Green Roof? What Does it Cost? Cost per square foot typically Extend the life of your roof ranges from $15-30 per square Improve the view from overlooking windows foot at the residential scale. If Minimize stormwater runoff the roof needs to be reinforced, the cost will be higher. Green roofs are not for everyone. A rain garden or conservation landscaping may not sound as exciting, but these are much more affordable ways to reduce stormwater runoff. When you register for the Water Audit Program, a Blue Water Baltimore staff member will conduct a site visit to assess your property. We will help you determine if a green roof is a good option for you. -
Stormwater Treatment: ST-10
ACTIVITY: Detention Computations ST – 10 Δ volum (I1+I2) Description This stormwater treatment BMP will describe the purpose, basic formulas, minimum criteria, computational methods, and types of structures that are needed for stormwater detention calculations. Stormwater detention is a necessary component of most stormwater treatment BMPs, and is required for most types of site development and redevelopment by the Knoxville Stormwater and Street Ordinance. Approach The Stormwater and Street Ordinance of the City of Knoxville is posted at the City Engineering website and must be read carefully by anyone who attempts to perform stormwater calculations within the City of Knoxville. It contains provisions for fees, bonds, necessary permits, right-of-entry, definitions, easements and penalties that will not be addressed here. A major purpose of the Stormwater and Street Ordinance is to improve water quality (erosion control, illicit storm drain connections, illegal dumping) as well as control stormwater quantity and flooding. Major Points of Stormwater Detention The following list summarizes the major points from the Stormwater and Street Ordinance that relate particularly to stormwater detention: Stormwater detention is required for any property containing one or more of the following conditions (according to Section 22.5-23): 1. Road construction containing one-half acre or more of impervious surface. 2. Commercial, industrial, educational, institutional or recreational developments containing one acre or more of disturbed area. 3. Single-family or duplex residential development containing at least five acres of disturbed area or at least five lots. 4. Any development containing one-half acre or more of additional impervious area. 5. Any redevelopment that causes the improvement of 50% of the assessed value of the lot, building, or lot use.