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HomeMy WebLinkAbout921185001 Stormwater Mgmt STORMWATER SITE PLAN KENNETH AND MARTHA SMITH RESIDENCE 266 EAGLE RIDGE DR. PORT HADLOCK, WA 98339 PARCEL NUMBER 921-185-001 Proponent Kenneth and Martha Smith 2620 Kingsbridge Circle Anchorage, Alaska 99504 Representative Larry Johnson and Rob Gruye Discovery Bay Construction PO Box 1410 Port Townsend, WA 98368 (360) 385-4372 DEPT, OF COMiv ~: '~ "OvELOPMENT iEXPIRES 3/28/0 q "] ~. z- o~ : APPROVED Eric Page, P.E. Willman Engineering, Inc. ~Y PO Box 1375 Pon Hadlock, WA 98339 l~~~_~_ [ (360) 379-9661 ~n. ~ ~~~~ May 2, 2002 TABLE OF CONTENTS,, L PROJECT OVERVIEW ............................................................................................................... IL PLOT PLAN - (SEE ATTACHED STORMWATER AND TESC PLAN) .................................. IlL CONDITIONS SUMMARY ......................................................................................................... IV. OFF SITE ANALYSIS .................................................................................................................. 3 V. ANALYSIS AND DESIGN OF STORMWATER FACILITIES ................................................. 4 VL SPECIAL REPORTS AND STUDIES ......................................................................................... 4 VH. BASIN AND COMMUNITY PLANNING AREAS ..................................................................... 4 VIII. OTHER PERMITS ....................................................................................................................... 4 IX. EROSION AND SEDIMENT CONTROL PLAN ........................................................................ 4 LARGE PARCEL EROSION AND SEDIMENT CONTROL PLAN ............................................... 4 PERMANENT STOtLMWATER QUALITY CONTROL PLAN ..................................................... 8 X. BOND QUANTITIES WORKSHEET .......................................................................................12 XL MAINTENANCE AND OPERATIONS ..................................................................................... 13 APPENDIX 'A' PROJECT VICINITY MAP APPENDIX 'B' SOIL CONSERVATION SERVICE PROJECT AREA MAP AND SOILS INFORMATION APPENDIX 'C' HYDROLOGICAL CALCULATIONS AND TIME OF CONCENTRATION CHART APPENDIX 'D' INTERCEPTOR SWALE SIZING CALCULATIONS APPENDIX 'E' CONVEYANCE PIPE SIZING CALCULATIONS APPENDIX 'F' FLOW SPREADER TRENCH SIZING CALCULATIONS ATTACHMENT STORMWATER AND TESC PLAN I. PROJECT OVERVIEW The applicant proposes construction of a single-family residence, garage, residential landscaping, and appurtenances on a parcel with an area of 4.90 acres. The property is described as Lot 1 of Eagle Ridge Large Lot Subdivision with Assessor's Parcel Number 921-185-001, and is accessed from Eagle Ridge Dr. II. PLOT PLAN - (See Attached Stormwater and TESC Plan) III. CONDITIONS SUMMARY The existing ground in the proposed development area slopes from west to east, at slopes ranging from seven to thirty percent. The elevations and orientations are similar to adjacent properties to the north and south. The parcel has been logged, and is currently vegetated with young second-growth deciduous trees and conifers. The parcel contains no improvements with the exception of an existing dirt road. This road begins at the proposed driveway entrance off of Eagle Ridge Dr. and wyes, extending to the proposed home site and to the northwest comer of the parcel. Surface Soil Conditions The site soils are mapped in the Soil Survey of the Jefferson County Area, Washington, August 1975, by the Soil Conservation Service (SCS). The soil type mapped in the project vicinity is Clallam gravelly sandy loam (CmD). The SCS describes Clallam gravelly sandy loam as a well-drained soil with a very slowly permeable layer at a depth of twenty to forty inches. The SCS description of Clallam gravelly sandy loam is as follows: The upper 23 inches of the soil is gravelly sandy loam that is grayish brown in the upper three inches and dark grayish brown in the lower twenty inches. This is underlain by a cemented layer. Storm Drainage Currently, and historically, stormwater enters the proposed development area from the west and exits the parcel to the east as shallow sheet flow, and likely subsurface flow. IV. OFF SITE ANALYSIS Stormwater from the proposed development area will be routed to a stormwater dispersal trench. Any overflow from this trench will be directed overland through a vegetated buffer toward the parcel's east property line. This vegetated buffer is approximately 700 feet in length, therefore this project is not anticipated to impact the adjacent right-of-way to the east. Water quality and quantity concerns will be addressed through dispersal of the stormwater into this buffer. After permanent vegetation is established, exposed soils will be minimized and risk of erosion from the project will be minimal. V. ANALYSIS AND DESIGN OF STORMWATER FACILITIES Stormwater runoff from the area proposed for development will be collected and routed through surface swales, catch basins, and storm drainage piping. All collected and controlled water will be directed into a stormwater flow dispersal trench. Prudent actions and maintenance of facilities will ensure long term water quality. The project alters approximately 1.20 acres of site cover, and site impervious area will be approximately 7,000 s.f. (3.3 percent of the total parcel area). A Large Parcel Erosion and Sediment Control Plan and Permanent Stormwater Quality Control Plan have been developed, to the standards of the Stormwater Management Manual for the Puget Sound Basin (SMM), February 1992 edition, and made a part of this report. VI. SPECIAL REPORTS AND STUDIES There are no other known special reports or studies relevant to this specific parcel. VII. BASIN AND COMMUNITY PLANNING AREAS There is no known basin plan for this locale. VIII. OTHER PERMITS A. An on-site septic system permit application has been prepared and submitted by John Scott Fleming Engineering, Inc.. B. A building permit together with associated ntility work permits will be required for the construction of the new home. IX. EROSION AND SEDIMENT CONTROL PLAN The total area of the site that will be disturbed is slightly greater than one acre. Further, the project will create more than 5,000 square feet of impervious area. Minimum Requirements #1 of Section 1-2.5, and Requirements #2 through #11 of Sections 1-2.6 through 1-2.15 of the SMM are therefore applicable. The Large Parcel Erosion and Sediment Control Plan (LPESC) included here addresses Minimum Requirement #1. The Permanent Stormwater Quality Control Plan (PSQC) included here addresses Minimum Requirement #2 through # 11. Lar.qe Parcel Erosion and Sediment Control Plan This LPESC plan addresses the fifteen items required under Minimum Requirement #1, Erosion and Sediment Control. MINIMUM REQU1RE~NT #1: EROSION AND SEDIMENT CONTROL Because the project includes land disturbing activity of' greater than one acre, Minimum Requirements #1 through #15 of section I-2.5 apply: 1. Stabilization and Sediment Trapping Criteria: All exposed and unworked soils shall be stabilized by suitable application of BMPs. From October 1 to April 30, no soils shall remain unstabilized for more than 2 days. From May 1 to September 30, no soils shall remain unstabilized for more than 7 days. Prior to leaving the site, stormwater runoff shall pass through a sediment pond or sediment trap, or other appropriate It is believed that due to the permeable nature of the site soils, erosion is not occurring at a fast rate. Prudent actions for continued stabilization for this area include timing of excavations to occur during the dryer portions of the year, covering of stockpiles of materials with visqueen sheeting during periods of precipitation, and stabilization of' site soils with seeding and mulching as necessary. For the excavation of the home foundation, a silt fence will not need to be erected around the lower portions of the excavation due to the presence of the vegetated buffer. Any soils stockpiles will be erodible given steep slope of the spoils and loose conditions, and should be covered with visqueen during inclement weather. Inlet filters are required for the catch basins and yard drains. Those areas that are disturbed, outside of the actual parking and building areas, will be revegetated by seeding and/or landscaping concurrent with the final grading and cleanup operations. Additional measures such as straw bale barriers or silt fences will be employed as needed during construction. 2. Delineate Clearing and Easement Limits Criteria: In the J~elc~ mark clearing limits and/or any easements, setbacks, sensitive/critical areas and their buffers, trees and drainage courses. The extent of clearing and grading is limited to the areas proposed for development as depicted on the stormwater site plan. Clearing limits and setbacks to sensitive/critical areas will be delineated in the field prior to the start of construction. 3. Protection of Adjacent Properties Criteria: Properties adjacent to the project site shall be protected from sediment deposition. The site shall be monitored during storm events and BMPs, such as hay bales and silt fences, will be employed as needed to protect the adjacent parcels. 4. Timing and Stabilization of Sediment Trapping Measures Criteria: Sediment ponds and traps, perimeter dikes, sediment barriers, and other BMPs intended to trap sediment on-site shall be constructed as a first step in grading. These BMPs shall be functional before land disturbing activities take place. Earthen structures such as dams, dikes, and diversions shall be seeded and mulched according to the timing indicated in Erosion and Sediment Control Requirement # 1. Permanent vegetation shall be used to provide final stabilization of the facilities concurrent with final grading and landscaping operations. 5. Cut and Fill Slopes Criteria: Cut and fill slopes shall be designed and constructed in a manner that will minimize erosion. In addition, slopes shall be stabilized in accordance with Erosion and Sediment Control Requirement # 1. The project will not have any significant cut and fill slopes. 6. Controlling Off-Site Erosion Criteria: Properties and waterways downstream from development sites shall be protected from erosion due to increases in the volume, velocity, and peak flow rate of stormwater runoff from the project site. See #1 and #3 above. 7. Stabilization of Temporary Conveyance Channels and Outlets Criteria: All temporary on-site conveyance channels shall be designed, constructed and stabilized to prevent erosion from the expected velocity of flow from a 2-year, 24-hour frequency storm for the developed condition. Stabilization adequate to prevent erosion of outlets, adjacent streambanks, slopes and downstream reaches shall be provided at the outlets of all conveyance systems. No temporary conveyance channels and outlets are anticipated for this project. 8. Storm Drain Inlet Protection Criteria: All storm drain inlets made operable during construction shall be protected so that storrnwater runoff shall not enter the conveyance system without first beingfiltered or otherwise treated to remove sediment. The storm drain catch basins shall be protected by filter fence as detailed and straw bale dams to prevent silt laden water from entering the storm drainage system. 9. Underground Utility Construction Criteria: The construction of underground utility lines shall be subject to the following criteria: (i) Where feasible, no more than 500feet of trench shall be opened at one time. (lO Where consistent with safely and space considerations, excavated material shall be placed on the uphill side of trenches. O'iO Trench dewatering devices shall discharge into a sediment trap or sediment pond. Underground utility installation shall conform to the guidelines set forth in the Washington State Department of Ecology Stormwater Management Manual for the Puget Sound Basin, latest edition (SMM). 10. Construction Access Routes Criteria: Wherever construction vehicle access routes intersect paved roads, provisions must be made to minimize the transport of sediment (mud) onto the paved road. If sediment is transported onto a road surface, the roads shall be cleaned thoroughly at the end of each day. Sediment shall be removed from roads by shoveling or sweeping and be transported to a controlled sediment disposal area. Street washing shall be allowed only after sediment is removed in this manner. Access to the site is from Eagle Ridge Dr., a paved private road. A temporary construction entrance is proposed for this project, as shown on the design plans. 11. Removal of Temporary BMPs Criteria: Ail temporary erosion and sediment control BMPs sha. ll be remove~,~ within 30 days after final site stabilization is achieved or afl'er the tempo~'!:~' BMPs are no longer needed Trapped sediment shall be removed or stabilized on site. Disturbed soil areas resulting from removal shall be permanently stabilized All temporary erosion and sediment control measures shall be removed within thirty days of final site stabilization or after the temporary measures are no longer needed. Trapped sediment shall be removed or stabilized on site. Disturbed soil areas resulting from removal of temporary BMPs shall be permanently stabilized. 12. Dewatering Construction Sites Criteria: Dewatering devices shall discharge into a sediment trap or sediment pond. Foundation drains will discharge through a catch basin to remove sediment from the waters to be discharged. 13. control of Pollutants Other Than Sediment on Construction Sites Criteria: All pollutants other than sediment that occur on-site during construction shall be handled and disposed of in a manner that does not cause contamination of stormwater. All pollutants that occur on-site during construction shall be handled and disposed of in a manner that does not cause contamination of stormwater and that is consistent with Washington State Department of Ecology Requirements. We do not anticipate other pollutants will be generated with this residential project, however, we acknowledge that proper response and disposal is essential. 14. Maintenance Criteria: All temporary and permanent erosion and sediment control BMPs shall be maintained and repaired as needed to assure continued performance of their intended function. All maintenance and repair shall be conducted in accordance with an approved manual. All temporary and permanent erosion and sediment control measures employed shall be maintained and repaired as needed to insure continued performance of their intended function. Ail maintenance and repair shall be conducted in accordance with the requirements of the SWMM. 15. Financial Liability Performance bonding, or other appropriate financial instruments, shall be required for all projects to ensure compliance with the approved erosion and sediment control plan. Jefferson County is not requiring a performance bond for this project. Permanent Stormwater Quality Control Plan This PSQC plan addresses Minimum Requirements #2 through #11. MINIMUM REQUIREMENT #2, PRESERVATION OF NATURAL DRAINAGE SYSTEMS Criteria: Natural drainage patterns shall be maintained, and discharges from the site shall occur at the natural location, to the maximum extent practicable. There are no natural drainage ways in the area proposed for development. Rather, natural flow exits the parcel as sheet flow downslope of the proposed development area. As it is the requirement to maintain the natural drainage pattern, a stormwater dispersal trench will be used to return the groundwater and stormwater runoff to the ground and the surface downslope of the proposed development area. MINIMUM REQUIREMENT #3, SOURCE CONTROL OF POLLUTION Criteria: Source control BMPs shall be applied to all projects to the maximum extent practicable. Source control BMPs shall be selected, designed, and maintained according to an approved manual. An adopted and implemented basin plan (Minimum Requirement #9) may be used to develop source control requirements that are tailored to a specific basin, however, in all circumstances, source control BMPs shall be required for all sites. During construction, proper maintenance of construction equipment, to eliminate leaks and spills, as well as adherence to the erosion and sediment control requirements as set forth in the LPESC Plan, should help alleviate the potential for pollution. At build-out, proper maintenance of stormwater facilities, in compliance with Section XI of this report, as well as the proper application of nutrients and pesticides to landscape areas should help lessen the potential for pollution on a long term basis. Only direct on-site stormwater runoff should be allowed to enter the stormwater infiltration system. No other discharges should be allowed. MINIMUM REQUIREMENT #4, RUNOFF TREATMENT BMPs Criteria: All projects shall provide treatment of stormwater. Treatment BMPs shall be sized to capture and treat the water quality design storm, defined as the &month, 24-hour return period storm. The first priority for treatment shall be to infiltrate as much as possible of the water quality design storm, only if site conditions are appropriate and ground water quality will not be impaired. Direct discharge of untreated stormwater to ground water is prohibited. All treatment BMPs shall be selected, designed, and maintained according to an approved manual. Stormwater treatment BMPs shall not be built within a natural vegetated buffer, except for necessary conveyance systems as approved by the local government. An adopted and implemented basin plan (Minimum Requirement #9) may be used to develop runoff treatment requirements that are tailored to a specific basin. Surface runoff' from the proposed development area will be directed to a stormwater dispersal trench as shown on the plan. This dispersal trench will act as an infiltration trench for most storm events, and those events not infiltrated will be dispersed as shallow sheet flow to the vegetated buffer downslope of the proposed development area. MINIMUM REQUIREMENT #5, STREAMBANK EROSION CONTROL Criteria: The requirement below applies only to situations where stormwater runoff is discharged directly or indirectly to a stream, and must be met in addition to meeting the requirements in Minimum Requirement #4, Runoff Treatment BMPs: Stormwater discharges to streams shall control streambank erosion by limiting the peak rate of runoff from individual development sites to 50 percent of the existing condition 2-year, 24-hour design storm while maintaining the existing condition peak runoff rate for the lO-year, 24-hour and l O0-year, 24-hour design storms. As the first priority, streambank erosion control BMPs shall utilize infiltration to the fullest extent practicable, only if site conditions are appropriate and ground water quality is protected. Streambank erosion control BMPs shall be selected, designed and maintained according to an approved manual. Stormwater treatment BMPs shall not be built within a natural vegetated buffer, except for necessary conveyance systems as approved by the local government. An adopted and implemented basin plan (Minimum Requirement #9) may be used to develop streambank erosion control requirements that are tailored to a specific basin. Not Applicable. MINIMUM REQUIREMENT #6, WETLANDS Criteria: The requirements below apply only to situations where stormwater discharges directly or indirectly through a conveyance system into a wetland, and must be met in addition to meeting the requirements in Minimum Standard #4, Runoff Treatment BMPs. (a) Stormwater discharges to wetlands must be controlled and treated to the extent necessary to meet the State Water Quality Standards, Chapter. 173-201 WAC, or Ground Water Quality Standards, Chapter. 173-200 WAC, as appropriate. Discharges to wetlands shall maintain the hydroperiod and flows of existing site conditions to the extent necessary to protect the characteristic uses of the wetland. Prior to discharging to a wetland, alternative discharge locations shall be evaluated, and natural water storage and infiltration opportunities outside the wetland shall be maximized. (c) Created wetlands that are intended to mitigate for loss of wetland acreage, function and value shall not be designed to also treat stormwater. (~t) In order for constructed wetlands to be considered treatment systems, they must be constructed on sites that are not wetlands and they must be managed for stormwater treatment. If these systems are not managed and maintained in accordance with an approved manual for a period exceeding three years these systems may no longer be considered constructed wetlands. Discharges from constructed wetlands to waters of the state (including discharges to natural wetlands) are regulated under Chapter. 90.48 RCW, Chapter. 173-201 WAC, and Chapter. 173- 200 WAC. (e) Stormwater treatment BMPs shall not be built within a natural vegetated buffer, except for necessary conveyance systems as approved by the local government. 10 An adopted and implemented basin plan (Minimum Requirement #9) may be used to develop requirements for wetlands that are tailored to a specific basin. Not Applicable. MINIMUM REQUIREMENT//7, WATER QUALITY SENSITIVE AREAS Criteria: Where local governments determine that the Minimum Requirements do not provide adequate protection of water quality sensitive areas, either on-site or within the basin, more stringent controls shall be required to protect water quality. Stormwater treatment BMPs shall not be built within a natural vegetated buffer, except for necessary conveyance systems as approved by the local government. An adopted and implemented basin plan (Minimum Requirement #9) may be used to develop requirements for water quality sensitive areas that are tailored to a specific basin. Not Applicable. MINIMUM REQUIREMENT//8, OFF-SITE ANALYSIS AND MITIGATION Criteria: All development projects shall conduct an analysis of off-site water quality impacts resulting from the project and shall mitigate these impacts. The analysis shall extend a minimum of one-fourth of a mile downstream from the project. 7he existing or potential impacts to be evaluated and mitigated shall include, at a minimum, but not be limited to: (0 excessive sedimentation (iO streambank erosion (~0 discharges to ground water contributing or [sic] recharge zones (~v) violations of water quality standards (v) spills and discharges of priority pollutants (i) Excessive sedimentation See Minimum Requirement #1, Erosion and Sediment Control, Items 1-! 5, found in the LPESC Plan. (ii) Streambank Erosion Not Applicable. (iii) Discharges to groundwater contributing or [sic] recharge zones Not Applicable. 11 (iv) Violations of water quality standards Runoff entering the stormwater system is not expected to contain significant contaminants. Proper dispersion of this stormwater will minimize the potential for violation of water quality standards. (v) Spills and discharges of priority pollutants Not Applicable. MINIMLrM REQUIREMENT//9, BASIN PLANNING Criteria: Adopted and implemented watershed-based basin plans may be used to modify any or all of the Minimum Requirements, provided that the level of protection for surface or ground water achieved by the basin plan will equal or exceed that which wouM be achieved by the Minimum Requirements in the absence of a basin plan. Basin plans shall evaluate and include, as necessary, retrofitting of BMPs for existing development an/or redevelopment in order to achieve watershed-wide pollutant reduction goals. Standards developed from basin plans shall not modify any of the above requirements until the basin plan is formally adopted and fully implemented by local government. Basin plans shall be developed according to an approved manual. Not Applicable. MINIMUM REQUIREMENT #10, MAINTENANCE AND OPERATIONS Criteria: An operation and maintenance schedule shall be provided for all proposed stormwater facilities and BMPs, and the party (or parties) responsible for maintenance an operation shall be identified See Section XI, Maintenance and Operations, in this report. MINIMUM REQUIILEMENT//11, FINANCIAL LIABILITY Criteria: Performance bonding or other appropriate financial instruments shall be required for all projects to ensure compliance with these standards. Jefferson County is not requiring a performance bond for this project. X. BOND QUANTITIES WORKSHEET Not Applicable. Xl. MAINTENANCE AND OPERATIONS Temporary Erosion and Sediment Control BMPs: Silt fences, inlet protections, and hay bale check dams as well as all other BM~s employed shall be inspected and cleaned after each large storm event, or when necessary. Silt and other material removed shall be disposed of in accordance with the guidelines established in the SMM. All other temporary and permanent measures employed shall be maintained in accordance with the SMM. The measures represented in this report are considered to be the minimum required to stabilize the site and protect adjacent properties. The project area should be closely monitored and other BMPs employed as needed. Permanent Stormwater Facilities - Flow dispersal trenches: After construction, the area downslope of the flow dispersal trench should be planted to aid in evaporating water and oxygenating the soil. Examples of appropriate vegetation are as follows: 1. Native vegetation of ferns, salal, rhododendrons and the like are preferred because they are not water seeking and they are low maintenance. 2. Grasses, clovers, wildflowers and other low-growing ground covers are acceptable. 3. Marsh grasses, elderberry, willow, maple, and alder are not acceptable because their root systems seek water and can damage the flow dispersal system. All vegetation should be kept trim and manageable. Sunlight and wind aid in evapotranspiration, but overgrown tangles impede the process. The flow dispersal trench area is not appropriate as a place for storage, buildings, etc. Permanent Stormwater Facilities- Catch basins: Catch basins shall be maintained and repaired as needed to assure continued performance of their intended function. Catch basins have a history of maintenance-related problems and it is imperative that a good maintenance program be established for the proper functioning. A typical problem is that sediment builds up inside the basin, restricting flow to the outlet or causing the sediment to bypass the catch basin' s sump and continue downstream to the flow dispersal facilities. To prevent this problem, catch basins should be routinely cleaned out when half of their sediment storage capacity is reached. 13 APPENDIX 'A' PROJECT VICINITY MAP VICINITY MAP 1' = 5000' Hadlock Scow Rd. Robbins Rd. OAK Chimacum ~ BAY Eagle Ridge Dr.,x,~ PROJECT SITE APPENDIX 'B' SOIL CONSERVATION SERVICE PROJECT AREA MAP SOILS INFORMATION JEFFERSON COUNTY AREA, WASHI R. lW.i R. 1E. ' · 1 FEET I (Joins sheet 52) I production of trees and for wildlife habitat and recreation firm; few fine roots penetrate upper few inches; medium acid; areas. Small areas, less than 10 percent of the total acreage, diffuse, smooth boundary (12 to 16 inches thick) C2--36 inches, very compact gravelly sandy loam glacial till. are under cultivation and are used for pasture and diversified (Many feet thick) home garden crops. Capability unit IVe-3; woodland group . 4d2. The A2 horizon ranges from gray to grayish brown. The B2 horizons range from grayish brown to dark grayish brown. The Cathcart gravelly silt loam, 30 to 50 percent slopes Clsim horizon is an olive-gray cemented layer that is 35 to 45 (C[ E) .--This steep soil is on glaciated uplands. Along the percent gravel and cobbles. Depth to the cemented layer ranges upper part. of the slopes bedrock is at a depth of 24 to 30 from 20 to 40 inches. The A2 and B2 horizons range from strongly acid to medium acid, and the Clsim horizon ranges from medium inches, and along the lower part of the slopes it is at a depth acid to slightly acid. of 30 to 40 inches. Runoff is rapid, and the hazard of water erosion is severe. This soil is well drained. Permeability is moderate above This soil is used mainly for production of trees and for the cemented layer. Roots penetrate to a depth of 20 to 40 recreation areas and wildlife habitat. Capability unit Vie-l; inches. This soil holds about 2 to 4 inches of water available woodland group 4d2. for plants. Runoff is slow to medium, and the hazard of water erosion is slight to moderate. The soil is saturated part of the time during the rainy season, and at times water moves Clallarn Series laterally, in places, above the cemented layer. The Clallam series consists of well-drained soils that have Most of the acreage of this soil is used for gro~4ng pasture a very slowly permeable cemented layer at a depth of 20 to of mixed grass and alfalfa or grass and clover. Home garden 40 inches. They are on uplands. Slopes range from 0 to 30 crops, berries, and vegetables are also grown. Capability percent. Elevation ranges from $0 to 1,000 feet. These soils unit IVe-1; woodland group 4d2. formed in glacial till under a forest of mixed coniferous and Clallam gravelly sandy loam, 15 to 30 percent slopes deciduous trees. Native vegetation is mainly Douglas-fir, (CmD).--This hilly soil is on glacial terraces on the breaks cedar, madrone, and willow. Annual precipitation ranges of canyons and steep drainageways. from 18 to 25 inches. The average annual air temperature is Runoff is medium, and the hazard of water erosion is 49°F. The above 32°F growing season ranges from 240 to moderate. This soil is used mainly for production of trees 270 days, and thc above 28°F growing season ranges from and for wildlife habitat and recreation areas. Capability 300 to 330 days. These soils are associated mainly with unit Vie-l; woodland group 4d2. Alderwood, Dick, Everett, Hoypus, Indianola, San~ Juan, To~send, and Whidbey soils. Coastal Beaches In a representative profile a thin layer of organic litter covers the surface. Thc upper 23 inches of the soil is gravelly Coastal beaches (Co & CW) consist of sandy and gravelly sandy loam that is gra)~ish brown in the upper 3 inches and sloping beaches in long, narrow strips. They are at the base dark gra~sh brown in the lower 20 inches. This is underlain of coastal bluffs or lowlands bordering thc Pacific Ocean in by a cemented layer, western Jefferson County and along the Straits of Juan de More than 60 percent of the acreage of Clallam soils has Fuca, Admiralty Inlet, and Hood Canal in eastern Jefferson been cleared and is used for pasture, hay, silage, berries, County. orchards, small grains, and vegetable gardens. Wooded areas Coastal beaches have no vegetation and are subject to are used as a source of woodland products and for wildlife continual wave action during high tides and storms. habitat and recreation areas. This land type is used for clam and oyster production and Clallam gravelly sandy loam, 0 to 15 percent slopes for recreation areas and wildlife habitat. Capability unit (CmC).--This nearly level to rolling soil is on terraces. VIIIw-1; not assigned to a woodland group. Most slopes range from 5 to 10 percent. Representative profile 1,650 feet west and 660 feet north Cut and Fill Land of southeast corner sec. 17, T. 30 N., R. I W.' Cut and fill land (Gu) consists of landfills in iow, depres- O1--2 inches to ~ inch, leaves, needles, and twigs, sional, wet or swampy areas. It is made up of a mixture of 02--~ inch to 0, ve~' dark grasdsh-brown (10YR 3/2), decom- posed organic matter; strongly acid. many types of soil material. One of the largest areas of Cut A2--4) to 3 inches, grayish~brown (10YR 5/2)gravelly sandy loam, and fill land is at the southwest end of Old Fort Flagler, light gray (2.5Y 7'2) and white (2.5Y 8/2) dry; weak, fine, between the marine bluffs and the beach, where a swampy granular structure' slightly hard, very friable, nonsticky, non- plastic; man); roo~s; about 20 percent gravel; medium acid; area was filled for a gunnery range. Capability unit VIIIw-1; abrupt, wavy boundary. (2 to 4 inches thick) not assigned to a woodland group. B21--3 to 14 inches, dark grayish-brown (2.5Y 4/2) gravelly sandy loam, light brownish gray (2.5Y 6/2) dry; weak, fine and me- dium, subangular blocky structure; slightly hard, very friable, Dabob Series nonsticky, nonplastic; many roots; few fine shot; about 35 percent gravel; medium acid; clear, wavy boundary. (8 to 19 The Dabob series consists of moderately well drained, roches thick) very gravelly soils that have a very slowly permeable ce- B22--14 to 23 inches, dark grayish-brown (2.5Y 4/2) gravelly mented layer at a depth of 20 to 36 inches. These soils are sandy loam, light, brownish gray (2.5Y 6/2) dry; weak, me- ' dium and coarse, subangular blocky structure; slightly hard, on glacial terraces. Slopes range from 0 to 30 percent. Ele- very friable, nonsticky, nonplastic; common roots; about 40 vation ranges from 100 to 800 feet. Thc Dabob soils formed percen1 gravel (including a few cobbles)' medium acid; gradual, under a coniferous-deciduous forest-in very gravelly glacial waw, boundary. (7 to 18 inches thick) till. Native vegetation is mainly Douglas-~fir, western hem- C]sim--2:-; t(, 3(; ~nc'h~, olive-gray (5Y 4/2), weakly cemented lock, willow, madrone, rhododendron, salal, and evergreen gravelly sandy loam, light gray (5Y 7/2) dry; common, medium and coarse, dark yellowish-brown (10YR 4,/4) and brown huckleberry. Annual precipitation ranges from 25 to 45 (7.sYR 4/4) motile- massive; extremely hard, extremely inches. The average annual air temperature is 49°F. The APPENDIX 'C' HYDROLOGICAL CALCULATIONS TIME OF CONCENTRATION CHARTS JOB · ~ ,: mm' 'm ' SHEET NO OF · CALCULATED BY DATE . . ENGINEERING, INC. 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"=-_.: ........ : .... ~_~ .0 _~_...~ ................. ~ ............ : ................................. !~__~L~!__C~..~.~: : .~i,~.-~.~ ...................... : . ................ ~ ................................... ~ ................ ? ............. ~ o ,<_ ~ ~-~_~ ~~ :, = ~ ~ ~ ~ ....... i .............................. : ............. ! ................. i ......... : .............. . ~ ...................................................... ................ : .............................. _.~..-...::...._i ................. i ....................................................................... i ................................................... i ................ : ............................................................................................... ............... ~ .................................. ........,......i..~,..t...-~__...~_.~/ .......... %'~ ......... .....~ ................... ~-~-~->-..~ ..................... ~-~ .......... i .............................................. ............................. ................ 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BOX 1375 ~RT HADL~K, WA 98339 360-379-9661 360-379-0150 F~ ~ -~ STORMWATER MANAGEMENT MANUAL FOR THE PUGET soUND BASIN  Table Iii-1.6 Hydrologic Soil Groups fos Soils in the Puget Sound Basin Hydrologic Soll Hydrologic Soil Soil TYl~ C_n, oup Soil Type Group Agncw C Coit~r C Ahl B Custer ND Ai~ C Dabob ND Alderwood C Delphi D Ar~nts, Ald~rwood B Dick ND Arents, Everett B Dinml D Ashoe B Dupont D ~ B Badmont C l~'ne, aon C Eda~dck C Baumgard B Eld B Baausite B Elwell B Belfast C Esquatzel B Balllngham D Everett A Ballingham variant C Everson D Boistfort B Galvin D Bow D Getchell A Briscot D Giles B Buckiey C Godfrey D Bunker B Greenwat~r A Cagey C Grove C Cartsborg ND Harstinc C Casey ND Hartnit ND Cassoiary. C Hoh ND Cathcart B Hoko ND Centralia B Hoodsport ND Chehalis B Hoogdal C Chesaw A Hoypus ND Cincbar B Huel ND Clallam C Indianola ND Clayton B Joins B Coastal beaches variable Jumpe ND Kepowsin C/D Kalaloch C Kamla C Remton D Kilchis C Republic B Kitaap C Riverwash variable Klaus ND Rober C Klonc ND Salal C Lares C Saikum B Lcbam B Sammamish D Lummi ND San Juan ND Lynnwood ND Scamman D Lysmir ND Schneider B Mai C Seattle D Manicy B Sckiu ND Maahei B Scmiahmoo D Maytown C Shaicar D McKcnm D Shano 'B McMurray ND Shciton C Melbourne B Si C Menzei ND Sinclair C Mixed Alluvial variable Skipopa D Molson B Skykomish B Mukilteo C/D Snahopish ND Naif B Snohomish D Nat'gar A Solduc B National ND Solleks ND Neiiton A Spare D III-l-9 . FEBRUARY, 1992 STORMWATERMANAGEMENT MANUAL FOR THE PUGET SOUND BASIN Table III-1.3 SCS Western Washington Runoff Curve Numbers (Published by SCS in 1982) Runoff curve numbers for selected agricultural, suburban and urban la~d use for T~r~e lA rainfall distribution, 24-hour storm duration. LAND USE DESCRIPTION CURVE NUMBERS BY HYDROLOGIC SOIL GROUP A B C D Cultivated land(l)= winter condition 86 91 94 95 Mountain open areas= iow growing brush & grasslands 74 82 89 92 Meadow or pasture: 65 78 85 89 Wood or forest land= undisturbed 42 64 76 81 Wood or forest land= young second growth or brush 55 72 81 86 Orchard= with cover crop 81 88 92 94 Open spaces, lawns, parks, golf courses, cemeteries, landscaping. Good condition: grass cover on k75% of the 68 80 86 90 area Fair condition: grass cover on 50-75% of 77 85 90 92 the area Gravel roads & parking lots: 76 85 89 91 Dirt roads a parking lots: 72 82 87 89 Impervious surfaces, pavement, roofs etc. 98 98 98 98 Open water bodies: lakes, wetlands, ponds etc. 100 100 100 100 Single family residential(2): Dwelling Unit/Gross Acre %Impervious(3) Separate curve number 1.0 DU/GA 15 shall be selected for 1.5 DU/GA 20 pervious & impervious 2.0 DU/GA 25 portions of the site 2.5 DU/GA 30 or basin 3.0 DU/GA 34 3.5 DU/GA 38 4.0 DU/GA 42 4.5 DU/GA 46 -~ 5.0 DU/GA 48 5.5 DU/GA 50 6.0 DU/GA 52 6.5 DU/GA 54 7.0 DU/GA 56 PUD's, condos, apartments, %impervious commercial businesses & must be industrial areas computed (1) For a more detailed description of agricultural land use curve numbers refer to National Engineering Handbook, Sec. 4, Hydrology, Chapter 9, August 1972. (2) Assumes roof and driveway runoff is directed into street/storm system. (3) The remaining pervious areas (lawn) are considered to be in good condition for these curve numbers. III-1-12 FEBRUARY, 1992 STORMWATER MANAGEMENT MANUAL FOR THE PUGET SOUND BASIN 124 123 122 121 _ i ! ~ f FRiD, t,~ HARBOR i'T; STANLEY / 35 . . ...? ~ ~',' ~, 4¢-,. ,1~ . ./ ~ . 50~ / 35 ~' ADA~ WASHINGTON Figure 25 ~5; 'NOAA ATLAS 2, Volume IX ISOPL~IALS ~ 2-YR 24-HR PRECIPITATi~N IN Pre,.red by U.S. De,.~ment of C~merce TENTHS OF A CH Nltlon~l Oce.nlc ~nd Atmo~Dheric ~mini~tration ; N~tion~l Weather Se~ice, Office of~Hydrology - i ~ Pre~r~ for U.S. Dep~men~ of A~riculture. ~ ~ ~il Con~e~tion Service. Engineering Division 124 123 122 121 III-1-44 FEBRU~Y , 1992 STORMWATER MANAGEMENT MANUAL FOR THE PUGET SOUND BASIN 124 123, 1221 121 \ ! / ,, i F~IDAY HAR {PORT STANL , \ / 175 TACuMA 30' / ,50 .~ WASHINGTON 0 10 20 30 40 ~ ' " ' MILES Figure 27 j ISOPLUVIALS 0F 10-YR 24-HR PRECIPITATION Prepare~ by U.~ De~ment of C~merce National ~elnic In~ Atmospheric A~minJstratio~ IN TENTHS OFf AN INCH !PreNr~ for U.S. Depl~me~t of A~Jculture. ~,~il Conae~at~on ~ce, Engineer~g Division 124 123 122 121 III-1-45 FEBRU~Y, 1992 STORMWATER MANAGEMENT MANUAL FOR THE PUGET SOUND BASIN 124 123 122 121 45 ..4~ 48 80 \ 100", WASHINGTON 40 · 10 0 10 20 30 40 ," ' ~' :- ] MILES ~---.-'" Figure 30 -- NOAA ATLAS 2, Volume IX ; ISOPLUVlALS (tF IO0-YR .24-HR PRECIPITI~TION IN TENTHS OF iAN INCH Nltion.l Weather : Prepared for U.S. Del~rtment · Soil Conservation DivLsi(m 12' 123 122 12i .... ,.... _~.,~..~ ~,.,, . , - :' 111-1-46 'FEBRUARY ~ 1992 STORMWATER MANAGEMENT MANUAL FOR THE PUGET SOUND BASIN Table III-1.4 "n" AND "k" Values Used in Time Calculations for Hydrographs "n~" Sheet Flow Equation Manning's Values (for the initial 300 ft. of travel) n~ Smooth surfaces (concrete, asphalt, gravel, or bare hand packed soil) 0.011 Fallow fields or loose soil surface (no residue) 0.05 Cultivated soil with residue cover (s~ 0.20 ft/ft) 0.06 Cultivated soil with residue cover (s> 0.20 ft/ft) 0.17 Short prairie grass and lawns 0.15 Dense grasses 0.24 Bermuda grass 0.41 Range (natural) 0.13 Woods or forest with light underbrush 0.40 Woods or forest with dense underbrush 0.80 *Manning values for sheet flow only, from Overton and Meadows 1976 (See TR-55, 1986) "k" Values Used in Travel Time/Time of Concentration Calculations Shallow Concentrated Flow (After the initial 300 ft. of sheet flow, R = 0.1) k~ 1. Forest with heavy ground litter and meadows (n = 0.10) 3 2. Brushy ground with some trees (n = 0.060) 5 3. Fallow or minimum tillage cultivation (n = 0.040) 8 4. High grass (n = 0.035) 9 5. Short grass, pasture and lawns (n = 0.030) 11 6. Nearly bare ground (n = 0.25) 13 7. Paved and gravel areas (n = 0.012) .. 27 Channel Flow {intermittent) {At the beg£nn£ng of vis£ble channels R ~ 0.2) kc 1. Forested swale with heavy ground litter (n = 0.10) 5 2. Forested drainage course/ravine with defined channel bed (n = 0.050) 10 3. Rock-lined waterway (n = 0.035) 15 4. Grassed waterway (n = 0.030) 17 5. Earth-lined waterway (n = 0.025) 20 6. CMP pipe (n = 0.024) 21 7. Concrete pipe (0.012) 42 8. Other waterways and pipe 0.508/n Channel Flow (Continuous stream, R = 0.4) ~ 9. Meandering stream with some pools (n.= 0.040) 20 10. Rock-lined stream (n = 0.035) 23 11. Grass-lined stream (n = 0.030) 27 12. Other streams, man-made channels and pipe 0.807/n** III-l-16 ~BRUARY, 1992 KING COUNTY DEPARTMENT OF PUBLIC WORKS Surface Water Management Division HYDROGRAPH PROGRAMS Version 4.21B I - INFO ON THIS PROGRAM 2 - SBUHYD 3 - MODIFIED SBUHYD 4 - ROUTE 5 - ROUTE2 6 - ADDHYD 7 - BASEFLOW 8 - PLOTHYD 9 - DATA 10 - RDFAC 11 - RETURN TO DOS 2 SBUH/SCS METHOD FOR COMPUTING RUNOFF HYDROGRAPH STORM OPTIONS: 1 - S.C.S. TYPE-lA 2 - 7-DAY DESIGN STORM 3 - STORM DATA FILE SPECIFY STORM OPTION: 1 S.C.S. TYPE-lA RAINFALL DISTRIBUTION ENTER: FREQ(YEAR), DURATION(HOUR), PRECIP(INCHES) 2,24,1.0 ((m_~o~~) ******************** S.C.S. TYPE-lA DISTRIBUTION ******************** ********* 2-YEAR 24-HOUR STORM **** 1.00" TOTAL PRECIP. ********* ENTER: A(PERV), CN(PERV), A(IMPERV), CN(IMPERV), TC FOR BASIN NO. 1 1.8,84,.16,98,42 DATA PRINT-OUT: AREA(ACRES) PERVIOUS IMPERVIOUS TC(MINUTES) A CN A CN 2.0 1.8 84.0 .2 98.0 42.0 PEAK-Q(CFS) T-PEAK(HRS) VOL(CU-FT) .03 8.17 1446 ENTER [d:][path]filename[.ext] FOR STORAGE OF COMPUTED HYDROGRAPH: 6month FILE ALREADY EXIST; OVERWRITE (Y or N) ? Y SPECIFY: C - CONTINUE, N - NEWSTORM, P - PRINT, S - STOP n STORM OPTIONS: 1 - S.C.S. TYPE-lA 2 - 7-DAY DESIGN STORM 3 - STORM DATA FILE SPECIFY STORM OPTION: 1 S.C.S. TYPE-lA RAINFALL DISTRIBUTION ENTER: FREQ(YEAR), DURATION(HOUR), PRECIP(INCHES) 2,24,1.5 ******************** S.C.S. TYPE-lA DISTRIBUTION ******************** ********* 2-YEAR 24-HOUR STORM **** 1.50" TOTAL PRECIP. ********* ENTER: A(PERV), CN(PERV), A(IMPERV), CN(IMPERV), TC FOR BASIN NO. 1 1.8,84,.16,98,42 DATA PRINT-OUT: AREA(ACRES) PERVIOUS IMPERVIOUS TC(MINUTES) A CN A CN 2.0 1.8 84.0 .2 98.0 42.0 PEAK-Q(CFS) T-PEAK(HRS) VOL(CU-FT) .10 8.00 3428 ENTER [d:][path]filename[.ext] FOR STORAGE OF COMPUTED HYDROGRAPH: 2year FILE ALREADY EXIST; OVERWRITE (Y or N) ? Y SPECIFY: C - CONTINUE, N - NEWSTORM, P - PRINT, S - STOP n STORM OPTIONS: 1 - S.C.S. TYPE-lA 2 - 7-DAY DESIGN STORM 3 - STORM DATA FILE SPECIFY STORM OPTION: 1 S.C.S. TYPE-lA RAINFALL DISTRIBUTION ENTER: FREQ(YEAR), DURATION(HOUR), PRECIP(INCHES) 10,24,2.2 ******************** S.C.S. TYPE-lA DISTRIBUTION ******************** ********* lO-YEAR 24-HOUR STORM **** 2.20" TOTAL PRECIP. ********* ENTER: A(PERV), CN(PERV), A(IMPERV), CN(IMPERV), TC FOR BASIN NO. 1 1.8,84,.16,98,42 DATA PRINT-OUT: AREA(ACRES) PERVIOUS IMPERVIOUS TC(MINUTES) A CN A CN 2.0 1.8 84.0 .2 98.0 42.0 PEAK-Q(CFS) T-PEAK(HRS) VOL(CU-FT) .25 8.00 6904 ENTER [d:][path]filename[.ext] FOR STORAGE OF COMPUTED HYDROGRAPH: lOyear FILE ALREADY EXIST; OVERWRITE (Y or N) ? Y SPECIFY: C - CONTINUE, N - NEWSTORM, P - PRINT, S - STOP n STO~ OPT !ONS: 1 - S.C.S. TYPE-lA 2 - 7-DAY DESIGN STORM 3 - STORM DATA FILE SPECIFY STORM OPTION: 1 S.C.S. TYPE-lA RAINFALL DISTRIBUTION ENTER: FREQ(YEAR), DURATION(HOUR), PRECIP(INCHES) 100,24,3.0 ******************** S.C.S. TYPE-lA DISTRIBUTION ******************** ********* IO0-YEAR 24-HOUR STORM **** 3.00" TOTAL PRECIP. ********* ENTER: A(PERV), CN(PERV), A(IMPERV), CN(IMPERV), TC FOR BASIN NO. 1 1.8,84,.16,98,42 DATA PRINT-OUT: AREA(ACRES) PERVIOUS IMPERVIOUS TC(MINUTES) A CN A CN 2.0 1.8 84.0 .2 98.0 42.0 PEAK-Q(CFS) T-PEAK(HRS) VOL(CU-FT) .46 8.00 11424 ENTER [d:][path]filename[.ext] FOR STORAGE OF COMPUTED HYDROGRAPH: lOOyear FILE ALREADY EXIST; OVERWRITE (Y or N) ? Y SPECIFY: C ~ CONTINUE, N - NEWSTORM, P - PRINT, S - STOP S i i i I APPENDIX 'D' INTERCEPTOR SWALE SIZING CALCULATIONS · ' JOB . · SHEET NO. OF ..... CALCULATED BY DATE ENGINEERING, INC. SCALE I ~ ~ ' ~ = A -~=, ~ ~ '~ ~= ......... L-?' .......... ~ ........ ~ .......... ~ ....... ~ .............. ~ .............. .............. ~ ................ ~ ................. ~ ........... ..... ~ .................. ~.._~.._,-~-~f ................ ~ .............. _~ .......................... >~ ................ ~,~_ ............... ~,__~ ..................................................... ~ /~--= : '~~]~ ................. ~,~f ............ :~ .............. ~:: ....... ................ ........................ :. ............ ~ ................ ~ ................ ~_..~ ......... ~. ......... ~...~..?....~ ........... ~ .......... ~ ................ ~ ................. L..~.....7..~......L..~A.....~ ............ E....~:...~_..~...~......,........~.~ ................................ [~...~._..~ ....... ~ .......... ............................................... ~. .............. ~ ................. , ....................... ~ ........................... ~ ............................. 5 ................. ~ ....... ~ ................. ~ ............... ~ .......... ~ .......... ~ ............................. 7'~?'"""~ ................. ~ .............. ~ ........... ................ ~ ............... ~ ................. ~ ................. : ............ ~ ........................ ~ ................. ........................... : ................................................................... ~ ........................... : .................................................................................................................................................. ~ ............... ~ ................................ ~ .................... : ................................................................................................... ................. :.. ~ ....... ~.~.~-~ ~__~.o~_~_z~ ...................................................... : ...... ~ ............ ~ ............. ~ ...... : ............. :___ ............................ ~ ............ .................. _~._:_~.O_d.l_ ~. ..~ .......................................... . .................................. ................ ~ ............................ ~ .............. ~ ................ ~ ............................ 7 .......... ~ ' ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ . 1 ~ OAK BAY ROAD/RO. BOX ~ 37~ ~RT HAD~K, WA 98339 360-S79-9661 360-~9-01 STORMWATER MANAGEMENT .M~_NUAL FOR THE PUOET SOUND BASIN Table III-1.5 V&luem of t~e Roughness Coeff£cien~ "n" Type of Channel Mann_,t~3's TYPe of Channel Manning's- and Description "n' and Description "n"' (Normal) (Normal) , , A. Constructed Cl~nnels 6. Sluggish.reaches, weedy 0.070 a. Earth, straight and uniform deep pools, 1. Clean~ recently completed 0.018 7. Very~.weedy, meches,-deep 0.100 2. Gravel, uniform section, 0.025 pools,-or fl~ys with 3. With sho~t grass, few 0.027. underbrush weeds b. Mountain streams, no vegetation b. Earth, winding and sluggish 0.025 in channel, :banks.usuailySteep, 1. No vegetation 0.025 trees and ~brush along banks 2. Grass, some weeds 0.030 sU~~~i~ stages 3. Dense weeds or-aquatic 1. Bottom:gravel,-:~bbles, and 0.040 plants In deep channels 0.035 few:~ 4. Earth bottom and rubble 2. Bott~:CObbles with large 0.050 sides 0.030 bo~ · , 5. Stony bottom and weedy a-2 R~i~ ~ banks 0.035 a~ P~m' ~!brush 6. Cobble bottom and dean 1. ShOrt~:grass. 0.030 sides 0.040 2. Highg~s 0.035 c. Rock lined b. Cultivated areas 1. Smooth and uniform 0.035 1. No crop 0.030 2. Jagged and irregular 0.040 2. Mature row crops 0.035 : d. Channels not maintained, 3. Mature field croPs 0.040 weeds and brush uncut c. Brush 1. Dense weeds, high as flow 1. Scattered:bruSh, heavy 0.050 depth 0.080 weeds 2. Clean bottom, brush on 2. ~Light brush and trees 0.060 sides 0.050 3. M~ium to~ ~h 0.070 3. Same, highest stage of 4. Heavy, dense :brush 0.100 flow 0.070 d. Trees · · 4. Der-me brush, high stage 1. Dense willows, straight 0.150 B. Natural Streams 0.100 2. Cleared~.~withtree 0.040 B-1 Minor streams (top width at stu~i! flood stage < 100 ft.) 3. S~ ~'with 0.060 a. Streanm on plain h iofspr°uts- 1. clean, straight, full stage 4. Heavy)~:of~timber,~a few 0.100 no riffs or deep pools 0.030 downt~;i:little 2. Same as above, but more und~~aoodstage stones and weeds 0.035 belOW branches 3. Clean, winding, some 5. same!:iaS~abOve; but with 0.120 pools and shoals 0.040 floOd ~:~e.i ~Ching 4. Same as above, but some branc~s ' weeds 0.040 ": . 5. Same as 4, but more stones 0.050 I II-1-17 FEBRUARY, ::1992 APPENDIX 'E' CONVEYANCE PIPE SIZING CALCULATIONS JOB ~,B ~., SHEET NO. OF CALCULATED BY DATE ENGINEERING INC SCALE : : OAK BAY ROAD/P.O. BOX 1375 PORT HADLOCK, WA 98339 360-379-9661 360-379-0150 FAX ~-( Pipe Capacity Calcul~.xis This spreadsheet is designed to calculate flow capacity and flow velocity for a silted or non-silted circular pipe assuming open channel flow properties. The principal formula is Manning's Equation. INPUT VALUES Manning's "n" for Pipe 0.0120 I ~anning's "n" for Invert Material 0.0000 Pipe Diameter (In.) 6.00 Pipe Slope, S (Ft/Ft) 0.0060 1 Depth of Invert Material (In.) 0.00 CALCULATED VALUES nl 0.0120 n2 0.0000 r (Ft.) 0'25 y (Ft.) 0.00 At (SF) 0.20 Ab (SF) 0.00 P1 (Ft.) 1.57 P2 (Ft.) 0.00 "n" I 0.0120 A (SF) I 0.20 P (Ft.) 1.57 Maximum Capacity (CFS) 0.47 Flow Velocity (FPS) 2.40 Page I Pipe Ca~y I This spreadsheet is designed to calculate ,flow capacity and flow ve~ooi~ for a silted or non-~ilted circular pipe assuming open channe~ flow properties, I The principal fon~u)a is Manning's Equation, INPUT VALUES I Manning's "n" for Pipe 0.0120 I Manning's "n" for Invert Material 0.0000 1 Pipe Diameter (In.) 4.00 I Pipe Slope, S (Ft/Ft) 0.1000 Depth of Invert Material (In.) 0.00 CALCULATED VALUES nl 0.0120 n2 0.0000 r (Ft.) 0.17 y (Ft.) 0.00 At (SE) 0.09 Ab (SF) 0.00 P1 (Ft.) 1.05 P2 (Ft.) 0.00 "n" 0.0120 A (SF) 0.09 P (Ft.) 1.05 iMaximum Capacity (CFS) 0.65 Flow Velocity (FPS) 7.49 Page I . Pipe Capacity Calculator, xls This spreadsheet is designed to calculate flow capacity and flow velocity for a silted or non-silted circular pipe assuming open channel flow properties. The principal formula is Manning's Equation. INPUT VALUES Manning's "n" for Pipe 0.0120 Manning's "n" for Invert Material 0.0000 Pipe Diameter (In.) 6.00 I Pipe Slope, S (Ft/Ft) 0.0350 I 1 Depth of Invert Material (In.) 0.00 CALCULATED VALUES nl 0.0120 n2 0.0000 r(Ft.) I 0.25 y (Ft.) 0.00 At (SF) 0.20 Ab (SF) 0.00 P1 (Ft.) 1.57 P2 (Ft.) 0.00 "n" 0.0120 n (SF) 0.20 P (Ft.) 1.57 Maximum Capacity (CFS) 1.14 Flow Velocity (FPS) 5.81 Page 1 inlet control conditions, which may be present or anticipated in the system, are not specifically addressed. Each pipe within the system is sized and sloped such that its barrel capacity at normal full flow (computed by Manning's Equation) is equal to or greater than the 25-Year design flow. The nomograph in Figure III-2.1 can be used for an approximate solution of Manning's Equation. For more precise results, or for partial pipe full conditions, solve Manning's Equation directly: V = 1.49 R~3 sla n or, using the continuity equation, Q = AV Q = 1.49 AR2/3sla n where: Q = Discharge in cfs V = Velocity in fps A = Area in ft2 n = Manning's roughness coefficient in s-ft1/6 (see Table III-2.2) ~ R = Hydraulic radius = area/wetted perimeter, in ft. s = Slope of the energy grade line in ft/ft For pipes flowing partially full, the actual velocity may be estimated from the hydraulic properties shown in Figure III-2.1 by calculating Q~II and VhlI and using the ratio .of Q4~ign/Qmll to find V and d (depth of flow). Table III-2.2 provides the recommended Manning's "n" values for preliminary design using the Uniform Flow Analysis Method for pipe systems. (Note, the "n" valves for this method are 15% higher in order to account entrance, exit, junction, and bend head losses.) Table III-2.2 Manning's "n" Values for Pipes Analysis Method Type of Pipe Material Backwater Uniform Flow Flow A. Concrete pipe and CPEP-smooth interiOr pipe 0.014 0.012. ~ B. Annular Corrugated Metal Pipe or Pipe-Arch: 1.2-2/3" x 1/2" corrugation (riveted) a. plain or fully coated 0.028 0.024 b. paved invert (40% of circumference paved): (1) flow full depth 0.021 0.018 (2) flow 0.8 depth 0.018 0.016 (3) flow 0.6 depth 0.015 0.013 c. treatment 5 0.015 0.013 2.3" x 1" corrugation 0.031 0.027 3.6" x 2" corrugation (field bolted) 0.035 0.030 C. Helical 2-2/3" x 1/2" corrugation and CPEP- single wall 0.028 0.024 D. Spiral rib metal pipe and PVC pipe 0.013 0.011 E. Ductile iron pipe cement lined 0.014 0 012 F. High density polyethylene pipe (butt fused only) 0.009 0.009 111-2-6 FEBRUARY, 1992 APPENDIX 'F' FLOW SPREADER TRENCH SIZING CALCULATIONS ~ JOB ~ SHEET NO, OF CALCULATED BY. DATE, ENGINEERING, INC. SCALE "i ........... ......................... ~ .............. : ............... ........................... _,...~ ................. F_%.~ .... ~~ ~ ~ ~~ ~ ~ ................. ~ ................. .................. ~ ..................................................................... ~ ................. ~ ........... : .............. ~ .............. ; ................. .............................................................. , OAK BAY ROAD]~O. BOX 1375 ~RT HADL~K, ~A 98339 3bO-379-9661 360-379-01~ ' JOB '% SHEET NO, OF CALCULATED BY. DATE, ENGINEERING INC ~"'~'~ OATI:" SCALE .......... : ....................... ; ................. ; ............................................. : ~ ........................................................................................................................................ ................................. ~ .......... ................. ............... ~ ~ ~ ........................... -- ~ ~ ;: ~ ~ ~ : ~, ~. ~ ~ ~ ~ , ................. ~ ................. ~: .................. ~ ................. ~ ~ ................ ~ :: .............. ~ , .........." ~J ~ ~ ,- ~ ~ .; ................ ~ .............. ~ .................. ~ ............. I ............ ~ ............. 7 ......~ .............. ~ ................ 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BOX 1375 ~RT ~DL~K, WA 98339 3&0-379-9661 360-379'01~ F~ ~- ~