Stormwater Drainage Design Overview
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Groundwater Recharge from a Changing Landscape
ST. ANTHONY FALLS LABORATORY Engineering, Environmental and Geophysical Fluid Dynamics Project Report No. 490 Groundwater Recharge from a Changing Landscape by Timothy Erickson and Heinz G. Stefan Prepared for Minnesota Pollution Control Agency St. Paul, Minnesota May, 2007 Minneapolis, Minnesota The University of Minnesota is committed to the policy that all persons shall have equal access to its programs, facilities, and employment without regard to race, religion, color, sex, national origin, handicap, age or veteran status. 2 Abstract Urban development of rural and natural areas is an important issue and concern for many water resource management organizations and wildlife organizations. Change in groundwater recharge is one of the many effects of urbanization. Groundwater supplies to streams are necessary to sustain cold water organisms such as trout. An investigation of the changes of groundwater recharge associated with urbanization of rural and natural areas was conducted. The Vermillion River watershed, which is both a world class trout stream and on the fringes of the metro area of Minneapolis and St. Paul, Minnesota, was used for a case study. Substantial changes in groundwater recharge could destroy the cold water habitat of trout. In this report we give first an overview of different methods available to estimate recharge. We then present in some detail two models to quantify the changes in recharge that can be expected in a developing area. We finally apply these two models to a tributary watershed of the Vermillion River. In this report we discuss several techniques that can be used to estimate groundwater recharge: (1) the recession-curve-displacement method and (2) the base-flow-separation method that both use only streamflow records (Rutledge 1993, Lee and Chen 2003); (3) a recharge map developed by the USGS for the state of Minnesota (Lorenz and Delin 2007); (4) a minimal recharge map developed by the Minnesota Geological Survey using statistical methods (Ruhl et al. -
Effects of Stormwater Runoff from Development by Robert Pitt, P.E
A River Network Publication Volume 14 | Number 3 - 2004 Effects of Stormwater Runoff from Development By Robert Pitt, P.E. Ph.D., University of Alabama ost people know that urban runoff is a problem, but very few realize just how harmful it can be for rivers, lakes and streams. In order to secure better control of urban runoff, we must make the public and its officials aware of the full extent of the problems that need to be prevented when new M development takes place. Urban runoff has been found to cause significant impacts on aquatic life. The effects are obviously most severe for waters draining heavily urbanized watersheds. However, some studies have shown important aquatic life impacts even for streams in watersheds that are less than ten percent urbanized. Most aquatic life impacts associated with urbanization are probably related to long- term problems caused by polluted sediments and food web disruption. Because ecological responses to watershed changes may take between 5 and 10 years to equilibrate, water monitoring conducted soon after disturbances or mitigation may not accurately reflect the long-term conditions that will eventually occur. The first changes due to urbanization will be to stream and groundwater hydrology, followed by fluvial morphology, then water quality, and finally the aquatic ecosystem. Effects of Stormwater Discharges on Aquatic Life Many studies have shown the severe detrimental effects of urban runoff on water Photo courtesy of Dr. Pitt organisms. These studies have generally examined receiving water conditions above and below a city, or by comparing two parallel streams, one urbanized and another nonurbanized. -
What Is the Difference Between an Arterial Street and a Non-Arterial (Local) Street?
WHAT IS THE DIFFERENCE BETWEEN AN ARTERIAL STREET AND A NON-ARTERIAL (LOCAL) STREET? Federal and State guidelines require that streets be classified based on function. Generally, streets are classified as either arterial streets or non-arterial streets. Cities can also use the designations to guide the nature of improvements on certain roadways, such as sidewalks or street calming devices. The primary function of arterials is to provide a high degree of vehicular mobility through effective street design and by limiting property access. The vehicles on arterials are often through traffic. Generally, the higher the classification of a street (Principal Arterial) being the highest), the greater the volumes, through movements, length of trips and the fewer the access points. Arterials in Shoreline are further divided into the three classes and are described as follows: • Principal Arterials have higher levels of local land access controls, with limited driveway access, and regional significance as major vehicular travel routes that connect between cities within a metropolitan area. Examples: Aurora Avenue N, NE 175th Street and 15th Avenue NE • Minor Arterials are generally designed to provide a high degree of intra-community connections and are less significant from a perspective of a regional mobility. Examples: Meridian Avenue N,N/ NE 185th Street and NW Richmond Beach Road • Collector Arterials assemble traffic from the interior of an area/community and deliver it to the closest Minor or Principal Arterials. Collector Arterials provide for both mobility and access to property and are designed to fulfill both functions. Examples: Greenwood Avenue N, Fremont Avenue N and NW Innis Arden Way. -
Miami-Dade County Drainage and Canals Flood Complaint Form
MIAMI-DADE COUNTY DRAINAGE AND CANALS FLOOD COMPLAINT FORM Service Request # _____________ Complaint Date Time AM PM Resident/Complainant Name Address Telephone Nearest Street Intersection of Flooding or Location of Flooding Is this the first time you report this? Yes No If No, date PLEASE SELECT ONLY ONE (1) COMPLAINT TYPE AND ANSWER RELATED QUESTIONS FOR BETTER SERVICE Type of Complaint 302 Clogged Storm Drain Is the water on top of drain now? Yes No How long does it take for the water to drain? What is the exact location of the drain? Is the area a new development? Yes No Was there a recent drainage project in the area? Yes No 303 Standing Water (No Drain) How deep is the water? How hard did it rain? Light Moderate Heavy Is your property flooded? Yes No Is your property in a new development? Yes No Where is the nearest drain? Flooding/Standing Water (Localized) Is the water flooding the inside of your residence? Yes No Is the water in your driveway / swale? Yes No Is the water across the roadway? Yes No Is it affecting traffic? Yes No How long does the water remain after rainfall? Page 1 of 2 MIAMI-DADE COUNTY DRAINAGE AND CANALS FLOOD COMPLAINT FORM Canal Complaints Solid waste (floating debris, bottles, cans, etc.) present Aquatic vegetation overgrown Needs mowing / treating vegetation on canal bank Bank instability due to Erosion / Collapses are present Culvert cleaning needed Damaged culvert / Headwall Encroachment of Easement / Right of Way Cutting / trimming of trees on a canal Right of Way needed Damaged Guardrails / Fence Canal Signs damaged / down Other Other Nature of Complaint For more information, call (305) 372-6688 Page 2 of 2 . -
Acid Sulfate Soil Materials
Site contamination —acid sulfate soil materials Issued November 2007 EPA 638/07: This guideline has been prepared to provide information to those involved in activities that may disturb acid sulfate soil materials (including soil, sediment and rock), the identification of these materials and measures for environmental management. What are acid sulfate soil materials? Acid sulfate soil materials is the term applied to soils, sediment or rock in the environment that contain elevated concentrations of metal sulfides (principally pyriteFeS2 or monosulfides in the form of iron sulfideFeS), which generate acidic conditions when exposed to oxygen. Identified impacts from this acidity cause minerals in soils to dissolve and liberate soluble and colloidal aluminium and iron, which may potentially impact on human health and the environment, and may also result in damage to infrastructure constructed on acid sulfate soil materials. Drainage of peaty acid sulfate soil material also results in the substantial production of the greenhouse gases carbon dioxide (CO2) and nitrous oxide (N2O). The oxidation of metal sulfides is a function of natural weathering processes. This process is slow however, and, generally, weathering alone does not pose an environmental concern. The rate of acid generation is increased greatly through human activities which expose large amounts of soil to air (eg via excavation processes). This is most commonly associated with (but not necessarily confined to) mining activities. Soil horizons that contain sulfides are called ‘sulfidic materials’ (Isbell 1996; Soil Survey Staff 2003) and can be environmentally damaging if exposed to air by disturbance. Exposure results in the oxidation of pyrite. This process transforms sulfidic material to sulfuric material when, on oxidation, the material develops a pH 4 or less (Isbell 1996; Soil Survey Staff 2003). -
Drainage Water Management R
doi:10.2489/jswc.67.6.167A RESEARCH INTRODUCTION Drainage water management R. Wayne Skaggs, Norman R. Fausey, and Robert O. Evans his article introduces a series of the most productive in the world. Drainage needed. Drainage water management, or papers that report results of field ditches or subsurface drains (tile or plastic controlled drainage, emerged as an effec- T studies to determine the effec- drain tubing) are used to remove excess tive practice for reducing losses of N in tiveness of drainage water management water and lower water tables, improve traf- drainage waters in the 1970s and 1980s. (DWM) on conserving drainage water ficability so that field operations can be The practice is inherently based on the and reducing losses of nitrogen (N) to sur- done in a timely manner, prevent water fact that the same drainage intensity is face waters. The series is focused on the logging, and increase yields. Drainage is not required all the time. It is possible to performance of the DWM (also called also needed to manage soil salinity in irri- dramatically reduce drainage rates during controlled drainage [CD]) practice in the gated arid and semiarid croplands. some parts of the year, such as the winter US Midwest, where N leached from mil- Drainage has been used to enhance crop months, without negatively affecting crop lions of acres of cropland contributes to production since the time of the Roman production. Drainage water management surface water quality problems on both Empire, and probably earlier (Luthin may also be used after the crop is planted local and national scales. -
Stormwater Management Regulations
City of Waco Stormwater Management Regulations 1.0 Applicability: These regulations apply to all development within the limits of the City of Waco as well as to any subdivisions within the extra territorial jurisdiction of the City of Waco. Any request for a variance from these regulations must be justified by sound Engineering practice. Other than those variances identified in these regulations as being at the discretion of the City Engineer, variances may only be granted as provided in the Subdivision Ordinance of the City of Waco or Chapter 28 – Zoning, of the Code of Ordinances of the City of Waco, as applicable. 1.1 Definitions: 100 year Floodplain Area inundated by the flood having a one percent chance of being exceeded in any one year (Base Flood). (Also known as Regulatory Flood Plain) Adverse Impact: Any impact which causes any of the following: Any increased inundation, of any building structure, roadway, or improvement. Any increase in erosion and/or sedimentation. Any increase in the upstream or downstream floodplane level. Any increase in the upstream or downstream floodplain boundaries. Floodplane The calculated elevation of floodwaters caused by the flood Elevation of a particular frequency. Drainage System System made up of pipes, ditches, streets and other structures designed to contain and transport surface water generated by a storm event. Treatment Removal/partial removal of pollutants from stormwater. Watercourse a natural or manmade channel, ditch, or swale where water flows either continuously or during rainfall events 1.2 Adverse Impact No preliminary or final plat or development plan or permit shall be approved that will cause an adverse drainage impact on any other property, based on the 2 yr, 10 1 yr, 25 yr and 100 yr floods. -
ALDOT PROJECT STPMB‐4918(250) Mcfarland Road from 0.1 Mile North of Old Pascagoula Road to Three Notch‐Kroner Road
ALDOT PROJECT STPMB‐4918(250) McFarland Road from 0.1 Mile North of Old Pascagoula Road to Three Notch‐Kroner Road On behalf of the Alabama Department of Transportation, welcome to the public involvement website for the project to construct McFarland Road from just north of the intersection of Old Pascagoula Road and McDonald Road to Three Notch‐Kroner Road. Due to the ongoing COVID‐19 Pandemic, this website will act as the primary method of public outreach for this project instead of ALDOT’s traditional in‐person meeting format. 1 Project Stakeholders • Alabama Department of Transportation (ALDOT) • Mobile County The proposed improvements are part of the Alabama Statewide Transportation Improvement Program and was included in the Mobile County Pay‐As‐You‐Go program. The project is being designed by Neel‐Schaffer, Inc. in coordination with Mobile County officials. The project is being funded through federal transportation dollars as well as Mobile County Pay‐As‐You‐Go funds. 2 The project is located in south Mobile County approximately ¾ of a mile north of I‐65 and CR‐39 (McDonald Road). For this project, two alternatives will be carried forward through detailed study. Both Alternative 1 and Alternative 2 begin just north of the intersection of Old Pascagoula Road and McDonald Road and end at the intersection of Ben Hamilton Road and Three Notch‐Kroner Road. The purpose of the proposed project is to relieve traffic congestion along McDonald Road and Three Notch‐Kroner Road. Congestion along McDonald Road and Three Notch Road is due to increased development in the area. -
The Groundwater Recharge Function of Small Wetlands in the Semi-Arid Northern Prairies
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Great Plains Research: A Journal of Natural and Social Sciences Great Plains Studies, Center for Spring 1998 The Groundwater Recharge Function of Small Wetlands in the Semi-Arid Northern Prairies Garth van der Kamp National Hydrology Research Institute, Environment Canada Masaki Hayashi University of Calgary, Canada Follow this and additional works at: https://digitalcommons.unl.edu/greatplainsresearch Part of the Other International and Area Studies Commons van der Kamp, Garth and Hayashi, Masaki, "The Groundwater Recharge Function of Small Wetlands in the Semi-Arid Northern Prairies" (1998). Great Plains Research: A Journal of Natural and Social Sciences. 366. https://digitalcommons.unl.edu/greatplainsresearch/366 This Article is brought to you for free and open access by the Great Plains Studies, Center for at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Great Plains Research: A Journal of Natural and Social Sciences by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. Great Plains Research 8 (Spring 1998):39-56 © Copyright by the Center for Great Plains Studies THE GROUNDWATER RECHARGE FUNCTION OF SMALL WETLANDS IN THE SEMI-ARID NORTHERN PRAIRIES Garth van der Kamp National Hydrology Research Institute, Environment Canada 11 Innovation Boulevard, Saskatoon, SK Canada S7N 3H5 and Masaki Hayashi Department ofGeology and Geophysics, University of Calgary 2500 University Drive, Calgary, AB Canada T2N IN4 Abstract. Small wetlands in the semi-arid northern prairie region are focal pointsfor groundwater recharge. Hence the groundwater recharge function of the wetlands is an important consideration in development of wetland conservation policies. -
Storm Drain Marking
Storm Drain Marking Part of the City of Ashland Curb to Creek Campaign A STEP -BY-STEP GUIDE FOR NEIGHBORHOOD VOLUNTEER LEADERS Ashland Parks & Recreation North Mountain Park Nature Center 620 North Mountain Avenue Ashland, OR 97520 Phone: (541) 488-6606 Fax: (541) 488-6607 Email: [email protected] 1 Table of Contents What is Storm Drain Marking …………………………………………….……. Page 3 The First Steps for Neighborhood Leaders ……………………................. Page 3 Neighborhood Registration Form .......................………………............. Page 4 Getting Ready to Mark …...................…………………………….……....... Page 5 List of Materials in Marking Kits ……………………………….…………….Page 6 How to Mark the Storm Drain ..…......…....………………………………Pages 6-9 Safety First Locate and Prepare Stomp the Pad Record Activity Telling Neighbors about Curb to Creek …………………………….…….. Page 10 The Final Steps ..………...........................................………………….…Page 11 Project Report Form …………………………….………………………......... Page 12 Adult Volunteer Consent Form……………….………………………......... Page 13 Youth Volunteer Consent Form..…………….………………………......... Page 14 2 WHAT IS STORM DRAIN MARKING ? Storm drain marking is an educational program designed to inform citizens about the hazards of dumping pollutants into storm drains. The placards remind people that storm drains flow untreated, directly into local streams and creeks. Ashland’s storm drains are NOT connected to the sewage treatment plant. By placing storm drain markers, you can take an active roll in preventing pollution in your neighborhood. Volunteers may also distribute door hangers, informing citizens about the proper disposal of chemicals that could harm wildlife and pollute waterways. Storm drain marking helps build community and mobilize grass roots environmental protection. Marking also helps educate your neighbors about the importance of watershed protection. If you are interested, you can become a neighborhood leader for your own Storm Drain Stomp event. -
2013 Stormwater Status Report
2013 Fairfax County � STORMWATER STATUS REPORT � A Fairfax County, Va., publication � June 2014 � Photos on cover (from top left): Fish sampling; Wolftrap Creek stream restoration in Vienna, VA; Fish – small mouth bass (Micropterus dolomieu) at Water Quality Field Day; Sampling station being serviced — Occoquan; Water Quality Field Day – Woodley Hills School; Tree planting; Stormwater Management Pond – Noman M. Cole, Jr., Pollution Control Plant. (photo credit Fairfax County) i Report prepared and compiled by: Stormwater Planning Division Department of Public Works and Environmental Services Fairfax County, Virginia 22035 703-324-5500, TTY 711 www.fairfaxcounty.gov/dpwes/stormwater June 2014 To request this information in an alternate format call 703-324-5500, TTY 711. Fairfax County is committed to nondiscrimination on the basis of disability in all county programs, services and activities. Reasonable accommodations will be provided upon request. For information, call 703-324-5500, TTY 711. ii This page was intentionally left blank. iii iv Table of Contents Table of Contents .............................................................................................................................. iv List of Figures ......................................................................................................................................... vi List of Tables .......................................................................................................................................... vi Acknowledgments -
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 .......................................................