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KENNEBEC SALMON RESTORATION: Innovation to Improve the Odds
FALL/ WINTER 2015 THE NEWSLETTER OF MAINE RIVERS KENNEBEC SALMON RESTORATION: Innovation to Improve the Odds Walking thigh-deep into a cold stream in January in Maine? The idea takes a little getting used to, but Paul Christman doesn’t have a hard time finding volunteers to do just that to help with salmon egg planting. Christman is a scientist with Maine Department of Marine Resource. His work, patterned on similar efforts in Alaska, involves taking fertilized salmon eggs from a hatchery and planting them directly into the cold gravel of the best stream habitat throughout the Sandy River, a Kennebec tributary northwest of Waterville. Yes, egg planting takes place in the winter. For Maine Rivers board member Sam Day plants salmon eggs in a tributary of the Sandy River more than a decade Paul has brought staff and water, Paul and crews mimic what female salmon volunteers out on snowshoes and ATVs, and with do: Create a nest or “redd” in the gravel of a river waders and neoprene gloves for this remarkable or stream where she plants her eggs in the fall, undertaking. Finding stretches of open stream continued on page 2 PROGRESS TO UNDERSTAND THE HEALTH OF THE ST. JOHN RIVER The waters of the St. John River flow from their headwaters in Maine to the Bay of Fundy, and for many miles serve as the boundary between Maine and Quebec. Waters of the St. John also flow over the Mactaquac Dam, erected in 1968, which currently produces a substantial amount of power for New Brunswick. Efforts are underway now to evaluate the future of the Mactaquac Dam because its mechanical structure is expected to reach the end of its service life by 2030 due to problems with the concrete portions of the dam’s station. -
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) -
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. -
Examples of Stormwater Control Devices
Stormwater Control Devices Filtration Basin A SHALLOW BASIN WITH ENGINEERED OR AMENDED SOIL AND AN UNDERDRAIN SYSTEM Filtration basins function by detaining stormwater in the basin. As stormwater infiltrates through the amended soil, sand, or engineered media, pollutants are filtered and adsorbed onto soil particles. Treated stormwater is directed to the receiving stream via the underdrain system. Filtration basins may be shaped like ponds or channels. To improve pollutant removal, the basin may be covered with grass, wetland species, or landscaped vegetation (see Bioretention Basin). Sand filters are considered filtration basins. Filtration basins may have outlet control structures and emergency spillways. However, all filtration basins have underdrain systems. Bioretention Basin A TYPE OF FILTRATION BASIN WITH ENGINEERED MEDIA , AN UNDERDRAIN SYSTEM , AND LANDSCAPED VEGETATION Bioretention basins use a landscaped mix of water- tolerant plants to improve pollutant removal. The vegetation is selected for its ability to physically filter and uptake stormwater pollutants. As with all filtration basins, stormwater is infiltrated through amended soil or an engineered media before it enters the underdrain system. Selected vegetation simulates various ecosystems such as forests, meadows, and hedgerows Bioretention basins are suited to drainage areas less than 1 acre. Bioretention basins may include outlet control structures and emergency spillways, but they will always have underdrain systems. Dry Detention Basin A SHALLOW , DRY BASIN WITH AN OUTLET PIPE OR ORIFICE AT THE INVERT OF THE BASIN Dry detention basins attenuate peak discharges and temporarily detain runoff to promote sedimentation of solids and infiltration. Runoff is slowly released from an outlet control structure at a steady flow rate to increase detention time. -
The Oxford Democrat E Leant
'; """ '"-'•;:-*2~*•^^-.-B- S ·"*' ρ 8fS5J v-· *· nyjij™ 'jpu "'■''.''..yf.lMJH "'.' Vlll'!!iLltl'4tt!'-'!iA^IP<l!ill J11 "'U1 W '-' P- "S" The Oxfordt Democrat. VOLUME 87. / SOUTH PARIS, MAINE, TUESDAY, JUNE 8, 1920. NUMBER 23. \ à PARK. rjK&RJCK FARMERS. Cross Pollinating. No Water Rebate* or Rate RevUloo at Desirable Stand For Sale in AMONG THE Attorneys Law. One might objoot to orow-polUnatloo Transaction of the actual businesi NORWAY. NEW ENGLAND NEWS BITH1L, MAJNX beoaute when such oroee-fertlHzatlon done at the special meeting of Soatl even I· Herrteh. »lHpC.P»rt South Paris. take· » "scrub" I· whlob Paria Village Corporation Tuesday U.ltoon 'iraao m flow.· place produced woree If did not mnoh Get The Wiit on Pine might be than either parent. log oocapy time, thongt pa Stanley place Street, IN TABLOID FORM » d. ax, for lbibt 1 tall ■aoh were the cue It would be the height the collateral dltoaaalon and general The many friends of Prof. John Barker Sooth Pari*, lg offered (or tale. ThI· U of folly to follow .the teaching of an filled oat the apace of an bonr, and ai 8tearns, «on of the late Jndge Seward 8. Auctioneer, Ready one Licensed Haying of In the moet desirable town. Be with the best tools for the work which will plaoee earlier letter In I hi· eerie·. It would be tlmea threatened to develop a little acri Steam·, may be Interested to learn tbat PARIS. MAIN*. prepared Caterpillar· and Other Things. waa ea SOOTH Hoase of eight room· with all modern far better for the Maine Agricultural mony, which, however, finally be la meeting with great sncoeaa aa ao Items of Interest Fran All >, <ms Moderate. -
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. -
Be It Enacted by the People of the State of Maine As Follows
APPROVED 017CHAPTER JUNE 21, 2019 463 BY GOVERNOR PUBLIC LAW STATE OF MAINE _____ IN THE YEAR OF OUR LORD TWO THOUSAND NINETEEN _____ H.P. 1262 - L.D. 1775 An Act To Protect Sustenance Fishing Be it enacted by the People of the State of Maine as follows: Sec. 1. 38 MRSA §420, sub-§1-B, ¶A, as enacted by PL 2001, c. 418, §3, is amended to read: A. The ambient criteria for mercury are as follows: (1) Ambient water quality criteria for aquatic life: (a) Freshwater acute: 1.7 micrograms per liter; (b) Freshwater chronic: 0.91 micrograms per liter; (c) Saltwater acute: 2.1 micrograms per liter; and (d) Saltwater chronic: 1.1 micrograms per liter; and (2) Fish tissue residue criterion for human health: 0.2 milligrams per kilogram in the edible portion of fish for all waters, except for those water body segments subject to a sustenance fishing designated use pursuant to article 4-A, which must have a fish tissue residue criterion for human health of 0.03 milligrams per kilogram in the edible portion of fish. Sec. 2. 38 MRSA §465-A, sub-§1, ¶C, as amended by PL 2013, c. 193, §4, is further amended to read: C. There may be no new direct discharge of pollutants into Class GPA waters. The Notwithstanding paragraph D, section 466-A or any other provision of law to the contrary, the following are exempt from this provision: (1) Chemical discharges for the purpose of restoring water quality approved by the department; (2) Aquatic pesticide or chemical discharges approved by the department and conducted by the department, the Department of Inland Fisheries and Wildlife or an agent of either agency for the purpose of restoring biological communities affected by an invasive species; Page 1 - 129LR2522(03)-1 018 (3) Storm water discharges that are in compliance with state and local requirements; (4) Discharges of aquatic pesticides approved by the department for the control of mosquito-borne diseases in the interest of public health and safety using materials and methods that provide for protection of nontarget species. -
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. -
Assessing the Biological Condition of Maine Streams and Rivers Using Benthic Algal Communities Thomas John Danielson
The University of Maine DigitalCommons@UMaine Electronic Theses and Dissertations Fogler Library 5-2010 Assessing the Biological Condition of Maine Streams and Rivers Using Benthic Algal Communities Thomas John Danielson Follow this and additional works at: http://digitalcommons.library.umaine.edu/etd Part of the Botany Commons, Ecology and Evolutionary Biology Commons, and the Plant Biology Commons Recommended Citation Danielson, Thomas John, "Assessing the Biological Condition of Maine Streams and Rivers Using Benthic Algal Communities" (2010). Electronic Theses and Dissertations. 356. http://digitalcommons.library.umaine.edu/etd/356 This Open-Access Dissertation is brought to you for free and open access by DigitalCommons@UMaine. It has been accepted for inclusion in Electronic Theses and Dissertations by an authorized administrator of DigitalCommons@UMaine. ASSESSING THE BIOLOGICAL CONDITION OF MAINE STREAMS AND RIVERS USING BENTHIC ALGAL COMMUNITIES By Thomas John Danielson B.S., University of Massachusetts, Amherst, 1993 B.B.A., University of Massachusetts, Amherst, 1993 M.E.M., Duke University, 1996 M.P.P., Duke University, 1996 A DISSERTATION Submitted in Partial Fulfillment of the Requirements for the Degree of Doctor of Philosophy (in Ecology and Environmental Science) The Graduate School The University of Maine May, 2010 Advisory Committee: Dr. Cynthia Loftin, Associate Professor of Wildlife Ecology, Advisor Dr. Susan Brawley, Professor of Biology Dr. David Courtemanch, Director, Division of Environmental Assessment, Maine Department of Environmental Protection Dr. Francis Drummond, Professor of Biology Dr. R. Jan Stevenson, Professor of Biology, Michigan State University ASSESSING THE BIOLOGICAL CONDITION OF MAINE STREAMS AND RIVERS USING BENTHIC ALGAL COMMUNITIES By Thomas John Danielson Dissertation Advisor: Dr. -
Aroostook River
REPORT OP' Al" EXPLORATION AND SURVEY OF TH~ TERRITORY ON TB:& AROOSTOOK RIVER, DURING THE SPRING AND AUTUMN OF 1838. BYE. HOLMES. AUGUSTA: SMITH & ROBINSON, PRINTERS TO THE STA.TE.. 1SS9. Printed by order of the House of Representatives of the Stale of Maine, 1839. __ _ __ .... _ AWbWWW:. dt »s&utZ.... r:1 •-=--=awww:: .40ildL.. :a a:;:Ca: EXPLORATION AND SURVEY OF THF. AROOSTOOK TERRITORY. ST ATE OF l\lAINE. IN BOARD OF INTERNAL IMPROVEMENTS, i April 23, 1838. S ORDERED, That the Land Agent is hereby authorized and empowered to cause an exploration and survey of the ArooPtook River and its tributary waters the ensuing year, by some suitable person witlt a par ticular reference to the settlement of that country and for a water communication between the Penobscot and Aroostook and Fish Rivers. LAND OFFICE, ? May 1st, 1838. S To EZEKIEL HoLl\rns, Esq. of Winthrop, Sir :-Pursuant to the above order of the Board of Internal Improve ments, you are authorized and requested to select suitable assistant~, and proceed as soon as practicable in the above mentioned exploration and survey, which you will finish in sucli a manner as in your opinion may best promote the jnterest of the State. You will make a recon noisance of the Sebois River and ascertain the practicability of a water communication between this river and La Pompique, also between the Little Machias and Fish Rivers, and at such other points on the Aroos took between the St. John and Penobscot Rivers, as you may deem advisable. You will examine the geology and mineralogy of the country, and present in your Report a topographical account of the same-describing the streams, mill sites, mounti'Lins, ponds, bogs, &c.; the growth, quality and extent of different soils, an<l in what direction it will be advisable to open roads and the facilities for making the same.