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HomeMy WebLinkAboutMisc (2)E d= lw rmmPSIO i aaaaauaaaaaasaauu TECHNICAL INFORMATION REPORT for Wehrman Plat King County Tax Parcel Nos. 619900-0101, & 332305-9010 Pre -application No. Site Addresses: 122nd Avenue SE between SE 188th Street and SE 192nd Street Renton, Washington m, T A , ^� IGRAL Prepared by: Lorna M. Taylor, P.E. TEC Project No. 485-MW Date: February 29, 2012 485 Rainier Blvd N, Ste #142, P.Q. Box 1787 . Issaquah, Washington 98027 . telephone (425) 391-1415 • fax (425) 391-1551 Taylor a, jj- Engineering 41-Fi L -7 Consultants TECHNICAL INFORMATION REPORT for Wehrman Plat King County Tax Parcel Nos. 619900-0101, & 332305-9010 Pre -application No. Site Addresses: 122nd Avenue SE between SE 188th Street and SE 192"d Street Renton, Washington v � ' 4� �r r_ L� z J Prepared by: Lorna M. Taylor, P.E. isTEC Project No. 485-MVV Date: February 29, 2012 485 Rainier Blvd N, Ste #102, P.O Box 1787 • Issaquah, Washington 98027 . telephone (425) 391-1415 • fax (425) 391-1551 Technical Information Report Wehrman Plat TABLE OF CONTENTS Section Description Pane Number 1. Project Overview .......................................... 1 2. Conditions and Requirements Summary........... 1 3. Off -Site Analysis .......................................... 6 4. Flow Control and Water Quality Facility Analysis andDesign .................................................... 7 5. Conveyance System Analysis and Design........ 9 6. Special Reports and Studies ......................... 9 7. Other Permits ..... ......................................... 9 8. ESC Analysis and Design .............................. 9 9. Bond Quantities, Facility Summaries, and Declaration of Covenant ................................ 10 10. Operations and Maintenance Manual ............... 10 Appendices Appendix A: Figures 1. Technical Information Report (TIR) Worksheets 2. Site Location 3. Drainage Basins, Subbasins, & Site Characteristics 4. NRCS Soils Map Appendix B: Off -site Analysis Drainage System Table and Map Appendix B-1: Drainage Complaint Analysis Appendix C: Analysis and Design Appendix C-1: Detention Facilities Design Appendix C-2: Treatment Facilities Design Appendix C-3: Erosion Control Facilities Design Appendix C-4: Conveyance Facilities Design (pending) Appendix D: Maintenance Requirements for Privately Maintained Drainage Facilities Appendix E: Bond Quantities Worksheets (pending) Appendix F: Retention/Detention Facility Summary Sheet and Sketch TEC Technical Information Report Wehrman Plat SECTION 1 PROJECT OVERVIEW This Technical Information Report is submitted to the City of Renton in accordance with the City -adopted King County Surface Water Design Manual (KCSWDM) and the City of Renton Amendments thereto (Renton Amendment), dated February, 2010. It addresses stormwater runoff from the proposed Wehrman Plat, A "Level 1 Off -site Drainage Analysis and Preliminary Detention Sizing Calculations Report", dated December 2, 2004, and revised November 9, 2005, was previously approved by King County for this project, and portions of that report are referenced herein; however, the proposed plat layout has been modified and this TIR addresses the currently -proposed plat layout. The 6.74-acre Wehrman Plat site comprises 2 existing lots located at about 122nd Avenue SE, between SE 188th Street and SE 192� Street in Renton, Washington. The project proposes to subdivide the two lots into 30 residential lots, with almost all of the development proposed for the western lot, and only some open space and parks proposed for the eastern lot. The project will include the required infrastructure, including access roads, water and sanitary sewer service, storm runoff collection, conveyance, detention and treatment, and erosion control during construction. The project is required to undergo Full Drainage Review in accordance with Figure 1.1.2.A of the KCSWDM & Renton Amendment. Appendix A contains a Technical Information Report (TIR) worksheet for the project (Figure 1), as well as a Site Location Map (figure 2), Drainage Basins, Subbasins, and Site Characteristics figure (Figure 3), and a Soils map (Figure 4). More detailed site information is included in Appendix C with the existing and developed site runoff model data. SECTION 2 CONDITIONS AND REQUIREMENTS SUMMARY Following is the text of the King County Hearing Examiner's Preliminary Conditions of Approval, dated August 10, 2006. All of the conditions 1 -- 17 either have been addressed, or will be addressed for the project. 1. Compliance with all platting provisions of Title 19A of the King County Code. 2. All persons having an ownership interest in the subject property shall sign on the face of the final plat a dedication that includes the language set forth in King County Council Motion No. 5952. The plat shall comply with the base density and minimum density requirements of the R-6 zone classification. All lots shall meet the minimum dimensional requirements of the R-6 zone classification or shall be shown on the face of the approved preliminary plat, whichever is larger, except that minor revisions to the plat which do not result in substantial changes may be approved at the discretion of the Department of Development and Environment Services. Any/all plat boundary discrepancy shall be resolved to the satisfaction of DDES prior to the submittal of the final plat documents, As used in this condition, "discrepancy" is a boundary hiatus, an overlapping boundary or a physical appurtenance which indicates an encroachment, lines of possession or a conflict of title. 3. All construction and upgrading of public and private roads shall be done in accordance with the King County Road Standards established and adopted by Ordinance No. 11187, as amended (1993 KCRS). 4. The applicant shall obtain documentation by the King County Fire Protection Engineer certifying compliance with the fire flow standards of Chapter 17.08 of the King County Code. TEC Technical Information Report Wehrman Plat 5. Final plat approval shall require full compliance with the drainage provisions set forth in King County Code 9.04. Compliance may result in reducing the number and/or location of lots as shown on the approved preliminary plat. Preliminary review has identified the following conditions of approval which represent portions of the drainage requirements. All other applicable requirements in K.C.C. 9.04 and the Surface Water Design Manual (SWDM) must also be satisfied during engineering and final review. a. Drainage plans and analysis shall comply with the 1998 King County Surface Water Design Manual and applicable updates adopted by King County. DDES approval of the drainage and roadway plans is required prior to any construction. b. Current standard plan notes and ESC notes, as established by DDES Engineering Review, shall be shown on the engineering plans. c. The following note shall be shown on the final recorded plat: "All building downspouts, footing drains, and drains from all impervious surfaces such as patios and driveways shall be connected to the permanent storm drain outlet as shown on the approved construction drawings # on file with DDES and/or the King County Department of Transportation. This plan sha€€ be submitted with the application of any building permit. All connections of the drains must be constructed and approved prior to the final building inspection approval. For those lots that are designated for individual lot infiltration systems, the systems shall be constructed at the time of the building permit and shall comply with plans on file." d. The drainage detention facility shall be designed to meet at a minimum the Level 2 Flow Control and Basic Water Quality menu in the 1998 King County Surface Water Design Manual (KCSWDM). e. Storm drain stubs for future connection shall be provided along the west property line in general conformance with the Preliminary Grading and Storm Drainage Plan received April 19, 2006, unless otherwise approved by DDES. The applicant's geotechnical engineer shall provide recommendations for the design and construction of the proposed site grading, road design, rock or retaining walls and drainage detention facility design. The geotechnical engineer shall evaluate the site for potential groundwater seeps and provide design recommendations to address groundwater found. The geotechnical recommendations shall be included in the T.I.R. and incorporated into the design with submittal of the engineering plans. g. Special geotechnical construction inspection of the site grading, road construction, rock or retaining walls and drainage facility, is required to ensure compliance with the geotechnical recommendations. Inspection reports shall be submitted to the assigned Land Use Inspector during the construction phases of those facilities. A final construction report shall be submitted verifying compliance with the geotechnical recommendations. 6. The proposed subdivision shall comply with the 1993 King County Road Standards (KCRS) including the following requirements: a. Road A shall be improved at a minimum to the urban subaccess street standard. A temporary turnaround shall be provided at the south end of Road A. This improvement shall be designed in general conformance with the Preliminary Grading and Storm Drainage Plan received April 19, 2006, unless otherwise approved by DDES. It is intended that this improvement will match the proposed road improvements for the plat of Fleuve des Voiles File L04P0002. b. FRONTAGE and OFFSITE: The frontage and offsite portion of SE 1881" Street from the west property boundary west to the existing road pavement shall be improved at a minimum to the urban half -street standard. This improvement shall be designed in general conformance with the Preliminary Grading and Storm Drainage Plan received April 19, 2006. Other designs for this frontage and offsite improvement may be considered, as approved by DDES. TEC Technical Information Report Wehrman Plat c. Offsite Walkway Improvements: These walkway improvements shall be designed in general conformance with the conceptual school walkway plan submitted April 19, 2006, unless otherwise approved by DDES as providing sufficient safe walking conditions for resident schoolchildren to their pertinent bus stops/schools. These improvements shall include any necessary grading and storm drainage work necessary to either tight -line the abutting roadside ditches or relocate the ditches within existing right-of-way. • SE 1881h Street (120'h Avenue SE to match into the above 1/2-street improvement near the west plat boundary) shall be widened to provide an eight (8) foot wide paved shoulder along the south side of the street. • SE 1881h St (1161h Ave SE to 1201h Ave SE) shall be widened to provide a minimum 16 foot wide paved surface as measured from the construction centerline. This will provide an 11-foot wide travel lane and a 5-foot wide paved shoulder. • 1201h Ave SE (SE 1881h St to SE 1841h St.) shall be widened to provide a minimum 16 foot wide paved surface as measured from the construction centerline. This will provide an 11-foot wide travel lane and a 5-foot wide paved shoulder. d. Modifications to the above road conditions may be considered according to the variance provisions in Section 1.08 of the KCRS. 7. All utilities within proposed rights -of -way must be included within a franchise approved by the King County Council prior to final plat recording. 8. The applicant or subsequent owner shall comply with King County Code 14.75, Mitigation Payment System (MPS), by paying the required MPS fee and administration fee as determined by the applicable fee ordnance. The applicant has the option to either: (1) pay the MPS fee at the final plat recording, or (2) pay the MPS fee at the time of building permit issuance. If the first option is chosen, the fee paid shall be the fee in effect at the time of plat application and a note shall be placed on the face of the plat that reads, "All fees required by King County Code 14.75, Mitigation Payment System (MPS), have been paid." If the second option is chosen, the fee paid shall be the amount in effect as of the date of building permit application. 9. The proposed subdivision shall comply with the Sensitive Areas Code as outlined in K.C.C. 21A.24. Permanent survey marking and signs as specified in K.C.C. 21A.24.160 shall also be addressed prior to final plat approval. Temporary marking of sensitive areas and their buffers (e.g., with bright orange construction fencing) shall be placed on the site and shall remain in place until all construction activities are completed. 10. Preliminary plat review has identified the following specific requirements which apply to this project. All other applicable requirements from K.C.C. 21A.24 shall also be addressed by the applicant. A. Wetlands The Class 1 wetland shall have a minimum buffer of 100 feet, measured from the wetland edge. The wetland and its respective buffers shall be placed in a Sensitive Area Tract (SAT). A minimum building setback line of 15 feet shall be required from the edge of the tract. B. Streams The Class 2 stream used by salmonids shall have a minimum 100-foot buffer, measured from the ordinary high water mark (OHWM). The stream(s) and their respective buffers shall be placed in a Sensitive Area Tract (SAT). A minimum building setback line of 15 feet shall be required from the edge of the tract. C. Alterations to Streams or Wetlands If alterations of streams and/or wetlands are approved in conformance with K.C.C. 21A.24, then a detailed plan to mitigate for impacts from those alterations will be required to be reviewed and TEC Technical Information Report Wehrman Plat approved along with the plat engineering plans. A performance bond or other financial guarantee will be required at the time of plan approval to guarantee that the mitigation measures are installed according to the plan. Once the mitigation work is compieted to a DDES Senior Ecologist's satisfaction, the performance bond may be replaced by a maintenance bond for the remainder of the five-year monitoring period to guarantee the success of the mitigation. The applicant shall be responsible for the installation, maintenance and monitoring of any approved mitigation. The mitigation plan must be implemented prior to final inspection of the plat. D. Geotechnical The applicant shall delineate all on -site erosion hazard areas on the final engineering plans (erosion hazard areas are defined in K.C.C. 21A.06.415). The delineation of such areas shall be approved by a DDES geologist. The requirements found in K.C.C. 21A.24.220 concerning erosion hazard areas shall be met, including seasonal restrictions on clearing and grading activities. 11. The following note shall be shown on the final engineering plan and recorded plat: RESTRICTIONS FOR SENSITIVE AREA TRACTS AND SENSITIVE AREAS AND BUFFERS Dedication of a sensitive area tract/sensitive area and buffer conveys to the public a beneficial interest in the land within the tract/sensitive area and buffer. This interest includes the preservation of native vegetation for all purposes that benefit the public health, safety and welfare, including control of surface water and erosion, maintenance of slope stability, and protection of plant and animal habitat. The sensitive area tract/sensitive area and buffer imposes upon all present and future owners and occupiers of the land subject to the tract/sensitive area and buffer the obligation, enforceable on behalf of the public by King County, to leave undisturbed all trees and other vegetation within the tract/sensitive area and buffer. The vegetation within the tract/sensitive area and buffer may not be cut, pruned, covered by fill, removed or damaged without approval in writing from the King County Department of Development and Environmental Services or its successor agency, unless otherwise provided by law. The common boundary between the tract/sensitive area and buffer and the area of development activity must be marked or otherwise flagged to the satisfaction of King County prior to any clearing, grading, building construction or other development activity on a lot subject to the sensitive area tract/sensitive area and buffer. The required marking or flagging shall remain in place until all development proposal activities in the vicinity of the sensitive area are completed. No building foundations are allowed beyond the required 15-foot building setback line, unless otherwise provided by law. 12. Suitable recreation space shall be provided consistent with the requirements of K.C.C. 21A.14.180 and K.C.C. 21A. 14.190 (i.e., sport court[s], children's play equipment, picnic table[s], benches, etc.). a. A detailed recreation space plan (i.e., location, area calculations, dimensions, landscape specs, equipment specs, etc.) shall be submitted for review and approval by DDES and King County Parks prior to or concurrent with the submittal of engineering plans. b. A performance bond for recreation space improvements shall be posted prior to recording of the plat. 13. A homeowners' association or other workable organization shall be established to the satisfaction of DDES which provides for the ownership and continued maintenance of the recreation, open space and/or sensitive area tract(s). 14. Street trees shall be provided as follows (per KCRS 5.03 and K.C.C. 21 A.16.050): TEC C, Technical Information Report Wehrman Plat a. Trees shall be planted at a rate of one tree for every 40 feet of frontage along all roads. Spacing may be modified to accommodate sight distance requirements for driveways and intersections. b. Trees shall be located within the street right-of-way and planted in accordance with Drawing No. 5-009 of the 1993 King County Road Standards, unless King County Department of Transportation determines that trees should not be located in the street right-of-way. c. If King County determines that the required street trees should not be located within the right- of-way, they shall be located no more than 20 feet from the street right-of-way line. d. The trees shall be owned and maintained by the abutting lot owners or the homeowners association or other workable organization unless the county has adopted a maintenance program. Ownership and maintenance shall be noted on the face of the final recorded plat. e. The species of trees shall be approved by DDES if located within the right-of-way, and shall not include poplar, cottonwood, soft maples, gum, any fruit -bearing trees, or any other tree or shrub whose roots are likely to obstruct sanitary or storm sewers, or that is not compatible with overhead utility lines. f. The applicant shall submit a street tree plan and bond quantity sheet for review and approval by DDES prior to engineering plan approval. g. The applicant shall contact Metro Service Planning at �206) 684-1622 to determine if SE 188`h Street in the subject area is on a bus route. If SE 188' Street in the subject area is on a bus route, the street tree plan shall also be reviewed by Metro. h. The street trees must be installed and inspected, or a performance bond posted, prior to recording of the plat. If a performance bond is posted, the street trees must be installed and inspected within one year of recording of the plat. At the time of inspection, if the trees are found to be installed per the approved plan, a maintenance bond must be submitted or the performance bond replaced with a maintenance bond, and held for one year. After one year, the maintenance bond may be released after DDES has completed a second inspection and determined that the trees have been kept healthy and thriving. A landscape inspection fee shall also be submitted prior to plat recording. The inspection fee is subject to change based on the current county fees. 15. To implement K.C.C. 21A.38.230 which applies to the site, a detailed tree retention plan shall be submitted with the engineering plans for the subject plat. The tree retention plan (and engineering plans) shall be consistent with the requirements of K.C.C. 21A.38.230. No clearing of the subject property is permitted until the final tree retention plan is approved by LUSD. Flagging and temporary fencing of trees to be retained shall be provided, consistent with K.C.C. 21A.38.230.B.4. The placement of impervious surfaces, fill material, excavation work, or the storage of construction materials is prohibited within the fenced areas around preserved trees, except for grading work permitted pursuant to K.C.C. 21A.38.230.B.4.d.(2), 16. A note shall be placed on the final plat indicating that the trees shown to be retained on the tree retention plan shall be maintained by the future owners of the proposed lots, consistent with K.C.C. 21A.38.230.B.6. (Note that the tree retention plan shall be included as part of the final engineering plans for the subject plat.) 17. A note shall be placed on the final plat indicating that the trees shown to be retained on the tree retention plan shall be maintained by the future owners of the proposed lots, consistent with K.C.C. 21A.38.230.B.6. (Note that the tree retention plan shall be included as part of the final engineering plans for the subject plat.) TEC Technical Information Report Wehrman Plat The following summary describes how this new project will meet the "Core Requirements" and the "Special Requirements" that apply: Core Requirements 1. Discharge at the Natural Location: The site currently slopes, steeply in places, to the east and the Soos Creek wetlands. There is a drainage ditch and culvert system flowing east at the northern property boundary, along SE 188 Street. This drainage pathway will be maintained. Otherwise, there are no well-defined drainage paths on the site, and runoff occurs in a dispersed manner. The project proposes to detain all runoff from the developed portions of the property and to disperse detained runoff to the Soos Creek Wetlands. 2. Off --Site Analysis: A Level 1 offsite analysis was conducted for these plats as described in Section 3. 3. Flow Control: Runoff from the site will be controlled to meet the Conservation Flow Control requirements of the KCSWDM in a combination detention and treatment pond. Discharges from the pond will be to a dispersion/energy dissipation facility. Appendix C contains the KCRTS input and output. 4. Conveyance System: Pipe conveyance modeling is pending. See Section 5. 5. Erosion and Sedimentation Control: Runoff from the grading and trenching construction areas will be contained by temporary construction entrance(s), silt fencing and a sediment pond in accordance with the KCSWDM during construction. The ESC facilities will only be removed once all exposed site surfaces have been stabilized. Other temporary erosion and sedimentation control measures will be installed as needed. See Section 8. • 6. Maintenance and Operations: Until the City of Renton assumes responsibility for the maintenance, the combination detention and treatment pond should be maintained as described in Section 10 and Appendix D, which includes the KCSWM Maintenance Requirements for Privately Maintained Drainage Facilities. 7. Financial Guarantees and Liability: See Section 9. The bond quantities worksheet is included in Appendix E. 8. Water Quality: Treatment of runoff from the Pollution Generating Impervious Surfaces (PGIS) will be provided in the dead storage portion of the combination detention and treatment pond, which was sized according to the KCSWDM for Basic Water Quality Treatment. Appendix C contains the calculations used to size the treatment facilities. Special Requirements 1. Other Adopted Area -Specific Requirements: Not Applicable. 2. Floodplain/Floodway Delineation: Not Applicable. The 100-year floodplain for the adjacent Soos Creek wetlands does not extend onto the subject property. 3. Flood Protection Facilities: Not Applicable. 4, Source Controls: Not Applicable. 5. Oil Control: Not Applicable. SECTION 3 OFF -SITE ANALYSIS A Level 1 Offsite Drainage Analysis, by Barghausen Consulting Engineers, was submitted to King County for this project as part of the approved Preliminary Plat submittal. Since then, the downstream drainage path was verified, King County's IMAP database was again consulted, TEC Technical Information Report Wehrman Plat and the County's Drainage Complaints File was again solicited to make sure no subsequent pertinent drainage complaints have been lodged in the interim. The Level 1 Off -Site Drainage Analysis and Preliminary Detention Sizing Calculations report, dated December 2, 2004, and revised November 9, 2005, by Barghausen Consulting Engineers, Inc. is available under separate cover. Task 1. Study Area Definition and Maps The figures in Appendix B show the extent of the study area and the local topography. The first figure shows that the project site constitutes less than 15 percent of the area tributary to the point '/4 mile downstream from the site; therefore, a '/4 mile downstream analysis is deemed sufficient. The Site Plan drawings show more detailed topographic information on the project site. Task 2. Resource Review Agency mapping was reviewed and TEC contacted King County regarding documented drainage complaints in the vicinity. The NRSC soils map identifies site soils in the proposed development area as Alderwood Gravelly Sandy Loam, 0 — 6% slopes and 15 — 30% slopes. Task 3. Field Inspection In accordance with the KCSWDM, the existing site and off -site drainage systems were inspected on June 15, 2004, and several times since. Task 4. Drainage System Descriptions and Problem Descriptions There are no pertinent reports of drainage problems in the immediate vicinity of the project. The County's drainage complaints file was solicited again more recently, and the results of this 0 search are included in Appendix B. No additional pertinent drainage complaints have been logged in the interim. If the proposed drainage system fails, and the detention facility floods, the emergency overflow path for runoff would be into the adjacent Soos Creek wetlands. These wetlands feed Soos Creek, which flows south on the King County -owned property to the east of the project property. Task 5. Mitigation of Existing or Potential Problems To mitigate any water quantity impacts from the project, detention of runoff is proposed meeting Conservation Flow Control requirements in accordance with the King County Surface Water Design Manual (KCSWDM). Water quality impacts will be addressed in a Basic Water Quality treatment facility; a combination detention and treatment pond. SECTION 4 FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND DESIGN The following subsections describe the measurements and criteria used to size the detention and treatment facility. Existing Site Hydrology (Part A) The drainage on the existing site was analyzed for this project with KCRTS. Figures provided in the KCSWDM and KCRTS manual were used to determine project location and scale factor parameters. The figure in Appendix C shows that the existing site is entirely forested and so forested conditions were used in the KCRTS existing site modeling, which would be required for Conservation Flow Control, regardless_ The site soils are classified Alderwood Gravelly Sandy TEC • 0 • Technical Information Report Wehrman Plat Loam, either 0 - 6% or 15 — 30% slopes. Appendix C also contains the data and output from the existing site hydrologic analysis. Developed Site Hydrology (Part B) The proposed drainage system will route runoff to a detention pond which will discharge to a dispersion/energy dissipation facility draining to the adjacent Soos Creek wetlands. Appendix C contains the data and output from the developed site hydrologic analysis. The developed site conditions identified for this project and used in the KCRTS modeling are summarized below. Developed Site Conditions used for Hydrologic Modeling areas in acres Site Offsite Bypass Total Impervious 3.729 0.500 0.00 4.229 Landscaping 1.517 0.000 0.198 1.715 Pasture 0.000 6.200 0.00 6.200 Subtotal 5.247 6.700 0.198 12.145 Performance Standards (Part C) The Wehrman Plat project is subject to the requirements of the KCSWDM, for Conservation Flow Control and must meet Historic Site Conditions Level 2 flow control standards. Basic water quality treatment is required. Conveyance features must be sized to convey the 25-year developed runoff and their performance during the 100-year event should be checked to be sure that significant flooding would not occur as a result. Flow Control System (Part D) The flow control is provided in a combination detention/treatment pond. The following table summarizes the sizing requirements for the Level 2 detention pond. Detention Pond Requirements Required storage volume 68,625 cf Effective storage depth 5.0 ft Top area @ 1' freeboard 19,656 sf Bottom area 9,900 sf Orifice 41 diameter* 2.10" (2") Orifice #2 diameter 3.20" (3-118°) Orifice #2 height 3.00 ft As shown on the plans, the pond will provide 69,882 cubic feet of detention storage, Descriptions of the procedures used and calculations and computer output are included in Appendix C. 8 TEC Technical Information Report Wehrman Plat Water Quality (Part E) Runoff from the site will be treated in the dead storage portion of the combination detention and treatment facility, which was sized for Basic Water Quality Control. The following table summarizes the sizing requirements for the treatment pond. Treatment Facilities Site Pond Required wetpool volume (Vn) 17,899 cf Wetpool depth (cell 1 & cell 2) 4 ft & 2 ft Top area 6,608 sf Cell #1 volume (25% - 35%) 4,643 cf — 6,501 cf As shown on the plans, the pond will provide 25,588 cubic feet of treatment volume. Descriptions of the procedures used and calculations and computer output are included in Appendix C. SECTION 5 CONVEYANCE SYSTEM ANALYSIS AND DESIGN Pending. The County's backwater routine (KCBW) will be used to size conveyance piping. The proposed 12-inch diameter pipe system should convey the predicted 100-year peak flows without flooding. SECTION 6 SPECIAL REPORTS AND STUDIES 4DSeveral studies and reports were conducted and produced for this project and are available under separate cover as listed below. 1. Level 1 Off -site Drainage Analysis and Preliminary Detention Sizing Calculations prepared by Barghausen Consulting Engineers, Inc., dated December 2, 2004 and revised November 9, 2005. 2. Traffic Impact Analysis prepared by Heath & Associates, dated November 2005. 3. Geotech Engineering Study tudy prepared by Earth Consultants, Inc., dated December 22, 2005, 4, Wetland Delineation Report prepared by Barghausen Consulting Engineers, Inc., dated December 10, 2004. SECTION 7 OTHER PERMITS No other permits beyond those required by the City of Renton are anticipated to be required for this project. SECTION 8 ESC ANALYSIS AND DESIGN The project proposes to utilize the permanent pond location for temporary sediment retention. The permanent pond area is 19,656 square feet, which much larger than the 3,994 square feet required for the erosion control pond. The sizing calculations for the various elements included in the erosion control facilities are included in Appendix C. TEC Technical Information Report Wehrman Plat SECTION 9 is BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT • n Bond Quantities: The County's standard Bond Quantities Worksheet is pending. Facility Summaries: The County's Facilities Summary Sheet is included in Appendix F. Declaration of Covenant: Not applicable. All the drainage facilities are located in public rights - of -way, or dedicated drainage tracts, and will be maintained by the City two years after final construction approval. SECTION 10 OPERATIONS AND MAINTENANCE MANUAL The detention/treatment pond and all drainage and street work within public tracts and rights -of - ways will become the property of and will be maintained by the City of Renton two years after final construction approval. Until such time, the drainage facilities should be maintained as described in Appendix D (part of which was excerpted from the KCSWM Maintenance Requirements for Privately Maintained Drainage Facilities). 10 TEC • APPENDIX A FIGURES 1. Technical Information Report (TIR) Worksheets 2. Site Location Map 3. Drainage Basins, Subbasins, & Site Characteristics 4. NRCS Soils Map I� `V, C • .7 KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL TECHNICAL INFORMATION REPORT (TIR) WORKSHEET Project Owner' Phone - Address 5// 5-- _ ,very F Gf%r4 ��'2D3 Project Engineerr��,-z�,�a�p Company 22Z //1 C • Phone �f2.1"- 0 Landuse Services u ivisan / Short Subd. / UPD ❑ Building Services M/F / Commerical / SFR ❑ Clearing and Grading ❑ Right -of -Way Use ❑ Other Project Name lil�°lrrinatrl �r ____ DDES Permit## Location Township Range S Section 3 Site Address /22AW ❑ DFW HPA ❑ COE 404 ❑ DOE Dam Safety ❑ FEMA Floodplain ❑ COE Wetlands ❑ Other ❑ Shoreline Management Structural RockeryNault ❑ ESA Section 7 4E Technical Information Report Site improvement Plan (Engr. Plans) Type of Drainage Review paurilge/ Targeted/ Type (circle one): ulI / Modified / (circle): Site Small Site Date (include revision Date (include revision dates): dates): Date of Final: Date of Final: Type (circle one); Standard / Complex / Preapplication / Experimental / Blanket Description: (include conditions in TIR Section 2) Date of 2009 Surface Water Design Manual I 1/9'2009 2110 • • KING COUNTY, WAS14INGTON, SURFACE WATER DESIGN MANUAL TECHNICAL INFORMATION REPORT (TIR) WORKSHEET Community Plan : leee, IV n Special District Overlays: Drainage Basin: SQgS 6-C-e �< _ Stormwater Requirements: UU River/Stream ��D�C C*-,e GAS ❑ Lake Wetlands ❑ Closed Depression ❑ Floodpiain ❑ Other Soil Type 44/ ❑ High Groundwater Table (within 5 feet) ❑ Other ❑ Steep Slope ❑ Erosion Hazard ❑ Landslide Hazard ❑ coal Mine Hazard ❑ Seismic Hazard ❑ Habitat Protection Li Slopes e� ❑ Sole Source Aquifer ❑ Seeps/Springs Additional Sheets Attached AgCS f 1,;Lj 1F-5 �Z) 2009 Surface Water Design Manual 2 Erosion Potential 1/9/2009 -�lv KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL 0 TECHNICAL INFORMATION REPORT (TIR) WORKSHEET • • REFERENCE Rf Gore 2 — Offsite Anal Sensitive/Critical Areas SEPA ❑ Other LIMITATION / SITE CONSTRAINT R[Additional Sheets Attached I Park 3 . TtR'.. UMfy14f Y FI T :`: ro.U:de,00 T4 -simn $hest, ei.t reshcld. Threshold Discharge Area: name or description) Core Requirements (all 8 apply) Discharge at Natural Location Number of Natural Discharge Locations: OfFsite Analysis Level: 2 / 3 dated: Flow Control Level: 1 / 2 / 3 or Exemption Number Incl. facility summary sheet Small Site BMPs Conveyance System Spill containment located at: Erosion and Sediment Control ESC Site Supervisor Contact Phone: After Flours Phone: Maintenance and Operation Responsibility: Private / Public If Private, Maintenance Log Required: Yes / No Financial Guarantees and Provided: es No Liability Water Quality Type: asic / Sens. Lake ! Enhanced Basicm ! Bog (include facility summary sheet) or Exemption No. Landscape Management Plan: Yes / No Special Requirements as applicable) Area Specific Drainage Type: CDA / SDO / MDP / BPI LMP / Shared Fac. ! None Requirements Name: Floodplain/Fioodway Delineation Type: Major / Minor / Exemption / None 100-year Base Flood Elevation (or range): Datum: Flood Protection Facilities Describe: Source Control Describe landuse: (comm./industrial landuse) Describe any structural controls: 2009 Surface Water Design Manual 3 I/9/2009 411 o KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL • TECHNICAL INFORMATION REPORT (TIR) WORKSHEET • Oil Control High -use Site: Yes / No Treatment BMP: Maintenance Agreement: Yes / No Other Dr, Describe: dart 1*4�{�I€Yrl■T VASUER fwTS .i T 9i§Y 4PS E j£ i, tE MINIMUM ESC REQUIREMENTS MINIMUM ESC REQUIREMENTS DURING CONSTRUCTION AFTER CONSTRUCTION Clearing Limits Stabilize Exposed Surfaces Cover Measures CTRemove and Restore Temporary ESC Facilities Perimeter Protection 'Clean and Remove All Silt and Debris, Ensure Area Stabilization Operation of Permanent Facilities r�,� u Sediment Retention uTraffic r Flag Limits of SAO and open space Or Surface Water Collection preservation areas ❑ Other ErDewatering Control Dust Control Flow Control P dif,.1:4..S.TORMVV 'E omme >i rtl Ffow Control Type/ escrition Water Quality Type/Description E Detention ❑ Infiltration ❑ Regional Facility ❑ Shared Facility ❑ Fiow Control BMPs ❑ Other /7 / �"O1 ❑ Biofiltration Wetpool ❑ Media Filtration ❑ Oil Control ❑ Spill Control ❑ Flow Control BMPs ❑ Other L M . r� / �� 2009 Surface Water Design Manual 1 /9/2009 • • • KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL TECHNICAL INFORMATION REPORT (TIR) WORKSHEET Drainage Easement ❑ Covenant Native Growth Protection Covenant Tract ❑ Other ❑ Cast in Place Vault U"Retaining Wall ❑ Rockery > 4- High ❑ Structural on Steep Slope ❑ Other I, or a civil engineer under my supervision, have visited the site. Actual site conditions as observed were incorporated into this worksheet and the attached Technical Information Report, To the best of my knowledge the information vided here is accurate. /1-23 - 2009 Surface Water Design Manual E 1/9'2009 F/ t o • 0 a s t t ;=w 1 M1 E v F FE EN pg� :dFPFtFi � a n P � ng Renton e a e t ' r t C UL VOC—T S Yf,7Z:�-M rainy Basins, ubbas ns & Site Char. - F �p h V law, CIVrD slz::- - •PFA - • 7 2Lorr = -7-2` q<. l ne Intormwion included on tN8 niap ira' 0n caniri ed by King Crunly staff fmw a variety ❑f sourrrs and is subject to-changew Warranties,.exuress or implied., as to aMlracy, cnrnple'enesa, tianeiiness, cir rights to the use of such information. T#Iis-document is shah not be liable for any goner 31 special indirect, incidental, or eonscrtuentisl darriagos including; but not lfmited:tb lost revenue! inierrna".ion cor;lained on ibis rn.ap: Any sale of this map or information on this map is prohibited except by written perinki fon of King( Date. 9l2212U08 Source, 'K g ,n�:hly AIAP - S3tmsiUve 1 cas Qitlf3:1! new .metrokc govj,GESriMAP} jt notice. King County.mnkes no.rep intended for use as a survey pr(i[lui Jost profits resulting from ihs ust b. nty, ij6l sf7E P/bfvsED A%Yga . zart/ S�rdcc[TI�2E AIL42T F2" Dok! F�,*. 0 Soil Map —King Counhy Area, Washington (Wehrman Plat) V r�frters p :i0 6U 120 180 f] ' 00 LU{] 400 60Q Natural Resources Web Soil Survey 2.0 9/2212008 Conservation Suivice National Cooperative Sail Survey Page 1 of 3 0 0 0 0 MAP LEGEND Area of Interest (AOI) € Area of Interest (AOI) Solis L Soil Map Units Special Point Features W Blowout N Borrow Pit ,X. Clay Spot Closed Depression Gravel Pit Gravelly Spot Landfill Lava Flow ,16 Marsh R Mine or Quarry O Miscellaneous Water O Perennial water y Rock Outcrop f Saline Spot Sandy Spot Severely Eroded Spot (j Sinkhole 3> Slide or Slip fir Sodic Spot Spoil Area Q Stony Spot Soil Map —King County Area, Washington (Wehrman Plat) MAP INFORMATION M Very Stony Spot Original soil survey map sheets were prepared at publication scale. Viewing scale and printing scale, however, may vary from the Wet Spot original. Please rely on the bar scale on each map sheet for proper Other map measurements. Special Llne Features Source of Map: Natural Resources Conservation Service r^' Gully Web Soil Survey URL: http://websolisurvey.nres.usda.gov ' Coordinate System: UTM Zone 10N Short Steep Slope This product is generated from the USDA-NRCS certified data as of Other the version date(s) listed below. Political Features Soil Survey Area: King County Area, Washington Pubile Land Survey Survey Area Data: Version 4, Nov 21, 2006 0 Township and Range Date(s) aerial images were photographed: 7/10/1990; 711811990 0 Section The orthophoto or other base map on which the soil bales were Municipalities compiled and digitized probably differs from the background a Cities imagery displayed on these maps. As a result, some minor shifting Areas of map unit boundaries may be evident. ® Urban Water Features Oceans ,- Streams and Canals Transportation Rails Roads ,yr Interstate Highways r US Routes State Highways Local Roads Other Roads ODA Natural Resources Web Soil Survey 2.0 9/2212003 Conservation Service National Cooperative Soil Survey Page 2 of 3 • • • Soil Map —King County Area, Washington Map Unit Legend Wehrman Plat ikiEF„�. Fi.g,CRit1t� a Y ¢..„. F:iax <, .._��k.v: Sit Ag8 �Alderwood gravelly sandy loam, 13.9 67.2% 0 to 6 percent slopes 27.4% AgD Alderwood gravelly sandy loam, - -- -- 5.7 15 to 30 percent slopes ' No Norma sandy loam 1.1 5,4% Totals for Area of Interest (AO I) U Natural Resources Conservation Service Web Soil Survey 2.0 National Cooperative Soil Survey 20.7 912212008 Page 3 of 3 • APPENDIX B OFF -SITE ANALYSIS DRAINAGE SYSTEM TABLE AND MAP • 0 0 0 OFF -SITE ANALYSIS DRAINAGE SYSTEM TABLE SURFACE WATER DESIGN MANUAL, CORE REQUIREMENT #Z Basin: Soos Creek Subbasin Name: Subbasin Number: a ,.' �R a {E3jF� .•. �. l�d�"'$� a '�a'ar�:'Isci,.� @ i�or�$-�f i.1iE1 rI]�'iF�i ��((.,ee� ^f - - >3[ �A ' ,!✓5 Q.eAt..S x ,�. ,[� €itt i' t � r 't a....:1:"d �,, ..5..."C`._y - ', ('< resid e�f ,� ... s s s is..... ?'�T€¢:w Vic't27�n #�bttt fe, ,`.�f�eEihood ofpro _.,.< . .k< �� F �, �E�Sie_ .Fq� t.:z� Ci 9m�JUt'r'il -,eC:: ,�.x firer �l J �.. 3 €�,F ` ..- ,}^, � "`P�M°....'P i. *�3E�i.�. S^.'1:81� �IK, `•.`.Y.^�4[SM!f��i„R�jv p{�{ 1��aJj�Rl��[y e4 fT _ .. E'1 P A -- B Sheet flow and sub Soos Creek grassy 2% - 0' — 230' None noted Wet marshy area surface flow wetland area 3% B --- C Wetland/stream/ Soos Creek grassy 1 % - 230' — 790' None noted Wet marshy area, relatively channel flow, wetland area 2% inaccessible a rox. 150' wide C D 48" culvert Crossing 192nd 790' 890' None noted This culvert was not visible at the time of the inspection, but according to the previous downstream analysis, has conveyed 100- year flows without flooding. D - E Stream Soos Creek 0.5% - 890' — None noted Creek flows in a wide 1% 1,320 + wetland area. 98-4VnB04 17(" A • • £ ; rtv€, i�`<i" :: s ' qa FRt{1 j F 9 f E T�jE az ���rL€ 9R°s +ss�s �ECunsrearri [rae�► i [i F4 Y iff E•"R �' fie' 2t. ?• � _ t• f Er, f it � � � E �,, � • �eS ��hi: # ,# ._5 "tit `. 1 E —'�i i l/ Yr:. ! � � � � � � � 3�' � � t4 c'L Ei4iE-'� - <3�jE` ,� -- ��'+• �.+.,�. 1 '� � �E )k.F��E� E f .. Y� L ls�. ��y r✓ y �'� e- m ^ ft -Ap • • 0 -� MrsT srpil TOIRDST .lrw. L f •G CY _ F Eit "'SSS i E i r ¢: .. .. �. ILI F '� �' _ F „;, , ::?L�a h LF1Vi�^yY.W E�.e__wR �Z.—� iy �--�`-`••';,I. mi t x ` w. r e , oJ&r Sri E: .5 Dom Pri �. „ OWNS a 4; s 1c c—A .. V(a • • Ay • 5/(,p • • SECTION 3.2 RUNOFF COMPUTATION AND ANALYSIS METHODS KCRTS is the "Effective Impervious Area" (EIA), the total impervious area multiplied by the effective impervious fraction. See Table 3,2,21, p. 3-29 for effective impervious fractions that apply to standard impervious surfaces. Table 1.2.3.0 lists effective impervious factions for alternative materials and approaches. Non -effective impervious area (i.e., total impervious area less EIA) is assumed to have the same hydrologic response as the immediately surrounding pervious area. For example, for existing residential areas with rooftops draining to splash pads on lawns or landscaping, the non -effective portion of the roof areas would be treated as pasture for predevelopment conditions (if DU/GA < 4.0) and grass for post -development conditions. Note: Credits for infiltration/dispersion of downspouts on individual lots in proposed single family residential subdivisions are applied separately on a site -specific basis (see Note 3, Table 3.2.2.E). The effective impervious fraction can be selected from Table 3.2.2.E or determined from detailed site surveys. With the exception of figures for compacted gravel and dirt roads and parking lots, the figures in Table 3.2.2.E are average figures cited by the USGS (Dinicola, 1990). MIME OSHA % Impervious(1) Dwelling Units/Gross % Impervious Dwelling Units/Gross Acre Acre 1.0 DUIGA 15(2) 4.5 DU/GA 46 1.5 DU/GA 20 5.0 DU/GA 48 2.0 DU/GA 25 5.5 DU/GA 50 2.5 DU/GA 30 6.0 DU/GA 52 3.0 DU/GA 34 6.5 DU/GA 54 3.5 DU/GA 38 7.0 DU/GA 56 4.0 DU/GA 42 7.5 DU/GA 58 For PUDs, condominiums, apartments, commercial businesses, and industrial areas, percent impervious coverage must be computed. Notes: (1) Includes streets and sidewalks. (2) These figures should be adjusted by the effective impervious fraction given in Table 3.2.2.E, if applicable. Values from Table 3.2.2,E may be interpolated as necessary. I/9/2009 2009 Surface Water Design Manual 3-28 WX 3.2.2 KCRTS/RUNOFF FILES METHOD — GENERATING TIME SERIES W, i ;f. �..... �.' i; K i?! F1 1-'WiM G y�. ] s.4Y y .E � fix' ki �� s#,PSaasli'1%ga il 1•'�, i" _. h f hH rg$qp' YTEA✓ � TI Mxh € EP T -_ k L,j} � S`�. +�4 !u � n.�'�ayPYf4� i3ppiF O �Y "� @ fll� �p iLErii�. ��ii_ . EBB.. � •4F.} Y. � �W Land Use Predevelopment Post -Development Commercial, Industrial, or Roads with Collection System 0,95 1.00 Multi -Family or High Density Single Family"' (74 DU/GA) 0.80 1.00(3) Medium Density Single Familyp' (4 DU/GA) 0.66 1.00") Low Density Single Familyl2} (1 DUIGA) 0.50 00{31 Rural{21 (c 1 DU/GA) 0.40 1.00(3) Gravel/Dirt Roads and Parking Lots, Roads without 0.50 0.50 Collection System Notes: (1) The effective impervious fraction is the fraction of actual total impervious area connected to the drainage system. These figures should be used in the absence of detailed surveys or physical inspection (e.g., via pipe, channel, or short sheet flowpath). I21 Figures for residential areas include roadways. (3) Section 5.2 outlines where the use of Flow Control BMPs may be used to reduce the effective impervious area of the project Example Determining the KCRTS land use data for an existing 20-acre residential area, with an average lot size of 9600 square feet (4.5 DU/GA), surrounding a 5-acre forested open space tract would entail the following calculations; From Table 3.2.2.D, the portion of basin assumed impervious at 4.5 DU/GA Total Impervious = 0.46 x 20 acres = 9.2 acres D -IT( Existing Pervious (grass) = 20 acres - 9.2 acres = 10.8 acres (p , Existing Pervious (forest) = 5 acres From Table 3.2.2,E, the effective impervious area Effective Impervious Fraction = 0.8 (at 4.5 DU/GA) '0,5 Effective Impervious Area = 0.8 x 9.2 acres = 7.36_ acres -,>, 5 ( I - a _ 0, a _ Non -Effective Impervious. Area = 9.2 acres - 7.36 acres = 1.84 acres 0, Add the non -effective impervious area to the area of the surrounding pervious land cover. Total Grass Area = 10.8 acres + 1.84 acres = 12.64 acresv =Y �-! ���-�i� • �L, Total Forest Area = 5 acres Effective Impervious Area = 7.36 acres These are the acreages that would be input into the KCRTS model when creating the time series. 2009 Surface Water Design Manual 1/9/2009 3-29 • APPENDIX B-1 DRAINAGE COMPLAINT ANALYSIS • r5- • f WEHRMAN PROPERTY w M g s i , t • «✓.e F ,: .i .,. r v e kMF`« ple =33k� I IT 12, Y 0 KinolovWftw and Land ReSwAvism - Ift sw-111M: Se M 2w Printed: 06103/2008 12:51:41 PM IbMw Type Type of ProW n Addr= of Pr@WM Cmnalts 1977-0072 197MO80 1978-0081 1982-0539 1984-0313 1984-0314 1987-1049 1988-0238 1988-0238 1989-0003 1989-0192 1996-1550 1997-1179 1997-1179 1997-1179 1997-1301 1998-0926 2000-0398 2003-0545 2003-0762 2003-0909 2004-0952 2005-0244 2005-0316 2005-0446 2008-0253 2008-0254 C C C C R C C C ER C G C C NDA R C C C WQR W QA WQC C C C WQA R R FLDG 12202 SE 192ND ST PONDING 19248 121ST PL SE DRNG 19248 121ST PL SE FLDG 12600 SE 192ND ST FLDG 13250 SE 192ND ST FLDG 13250 SE 192ND ST FLDG 18431 120TH AVE PIPE 18431 120TH AVE DRNG 18612 120TH AVE DRNG 18612 120TH AVE DRNG 19121 124TH AVE DRAINAGE 19113 121ST PL DRAINAGE 19113 121 ST PL DRAINAGE 19113 121 ST PL DRAINAGE 19125 121STPL DRAINAGE 19133 121 ST PL DDM 12625 SE 192ND ST WQB 18601 126TH PL SE WQAI 19433 VASHON HWY SW WQDR 18601 126TH PL SE DTA 12701 SE 191 ST PL DDM 18617 126TH PL DTA 12503 SE 188TH PL WQAI 12600 SE 192ND ST DDM 19248 121STPL DDM 19210 121 ST PL SE SE SE SE SE SE SE SE SE SE SE SE SE EAST OF BENSON HWY EAST KENT AREA TO ROADS DIVA SE 192ND ST1134TH AVE SE TO RD COORD 04127187. NEW DRIVEWAY WILL IT FLOOD NEED EXTENSION OF 42" CULVERT INCREASED RUNOFFICHANNEL X PIPE NOT WORKING PLUGGED D1W CULVERT IMPACT TO INSTALLATION OF DRNG IN RMf INSTALLATION OF DRNG IN RIW INSTALLATION OF DRNG IN RIW.. SUBSTANDARD INSTL OF DRNG SYS PVT APPARENT OBSTRUCTION IN ROAD REQUEST TO DIVERT FLOW PROBLEM CORRECTED RP MOVED BMPS are ALL IN PLACE AUTO FLUID RESIDUE ON STREET AS A Referral from KC Roads. Flooding of Wet backyard caused by broken storm line? Backup in KC Rd conveyance system. BMPS IMPLEMENTED AS PART OF KENT ORPHAN FACILITY REVIEW FOR THE Page 1 of 1 • Tbras Page 686F2 Sj j' Z20 ? s� f,rrd 6$6F2 . 686F2 DreS+ 686F2r 686F21 68fiF2 686F2r 7 686 F2 it R 686F2 ITT 686 F 686F2� _ 686F2 15kdtiV— Qr, ��D 54E IgMoA 5 `. 686F2' r 6861`2 686F2 686F2 { 686F2 686F2 686F2(, 686F2 686F2 � � D 0 four ekd+ 686 F2 686F2 686F2: j 686F2 — D +$ 686F2 — - pp vje1+ • • PCSk-W Fu Note 7671 Date 91 ` �� Ra9ea� co.�oL �• llcl� Gr�JN1�, ifi�aCay dater aq� LBIId RB8ei�"c� - �raine�e 8er CUM Prated : W1412W 1-37!24 PM C"iWilt Typo 1Xpi of Pm*m I of PI'Oi lw Como" Ift pal Km�r t�N 19764110 C DRNG 13038 SE 188TH PL BLVD LN 886G2 1077.0072 C FLDG 12202 BE 192ND ST 686F2 1977-0074 C FLOG 13210 SE 192ND ST FILLIDRAIN WAY 686G2 1976.0080 C PONDING 19248 121ST PL SE EAST OF BENSON HWY 888F2 1978-0081 C DRNG 19248 121ST PL SE 68BF2 1981-0225 C FLDG 13210 $E 192ND ST DRAIN WAY FILLED 686G2 1982-0539 C FLDG 12600 $E 192ND ST EAST KENT AREA 66OF2 19134-0313 R FLDG 13250 SE 192N0ST TO ROADS DIVA 686F2 19WO314 C FLDG 1$250 BE 192ND Si SE 192ND ST/134TH AVE 5E 686F2 198"534 X DRNG 13250 SE 102ND ST LTR TO COMPLAINT 686G2 1980,0617 C DRNG 13432 SE 167TH ST FLDG ON SIDEWALK 886G2 198B.0818 C FLDG 13440 SE 182ND ST RFP:85-0832 NESPER 87.0770 686G2 198MM6 ER FLDG 13M BE 192ND ST (REF;W$32 NESPER) PVT PROD. 686G2 1966.7278 CL CLAIM #10373 688G2 1987-077D ` C FLDG 13440 SE 192ND ST FAIRWOOD SEE 86-0810 60602 1987-1049 C TO RD COORD 04/27187, 686F2 1986.0118 x DRNG 1325C 5E 192ND ST SEE 85.1278 NESPERIGL • FORSESTTRAf 66SU 1985-0238 C FLDG i8431 1207H AVE SE NEW DRIVEWAY WILL IT FLOOD 688F2 1988-0238 ER PIPE 18431 120TH AVE SE NEED EXTENSION OF 42" CULVERT 686F2 1968-0305 C BLOCKAGE 12716 SE 188TH PL EASEMENT-FAIRWOOD/WALL CONSTRUC 886132 198MD03 C DRNG 18812 120TH AVE SE INCREASED RUNOFFICHANNEL 686F2 1989-0192 C DRNG 16612 120TH AVE BE X PIPE NOT WORKING 686FZ 1989-0550 C EROSION 19118 130TH AVE SE OLD EASEMENT CHANNEL MAINTENANCE 586G2 19WO665 C DRNG 13300 BE 184TH PL WATER IN BASEMENT/YARD DRAIN CLOG 68602 1900.0056 C FLDG 12700 SE 107TH PL UTILITY EA$EMT CLOGGED 90.0259 686G2 1993.0250 C 'FLDG 12700 BE 187TH PL PV'r DITCH OVERFLOW 686G2 1990.1106 C DRNG 13517 BE 189TH PL CULVERT SLEW TRASH RACK/ CEDAR ES 68GG2 1990.1106 NDA DRNG 13517 SE 169TH PL CULVERT BLEW TRASH RACK CEDAR ES 688G2 1990-1166 C DRNG 111421 SE 189TH PLACE 13517 $S 169TH PL 698G2 1990-1155 NDA DRNG 13421 $E 189TH PLACE REF 90-1106 686G2 1990.1158 C DRNG 13429 BE 189TH PLACE 13517 SE 169TH PL 686G2 1990-1156 NDA DRNG 13429 BE 189TH PLACE REF 90-1106 680GZ 1990.1157 C DRNG 13436 SE 189TH PLACE 13517 BE 189TH PL 688G2 19-40 1157 NDA DRNIG 13435 SE 189TH PLACE REF 90-1106 688G2 1990.115E C DRNG 18917 5E 189TH PLACE 13$17 SE 189TH PL 688G2 1990.1158 NDA DRNG 10917 BE 189TH PLACE REF 90-1106 688G2 19ON1159 C DRNG 13523 SE 18STH PLACE 13517 SE 189TH PL 68502 Page 1 013 7� � TY1a of f�t'Dp M �I'n8 of Ptdl w Colulit� im po lumir 1990-1159 NDA DRNG 13523 SE 189TH PLACE REF 90.1106 686G2 1990-1160 C DRNG 13529 BE 189TH PLACE 13517 SE 189TH PL ma= 1990.1160 NDA DRNG 13529 BE 169TH PLACE REF 90-1 106 6B832 1990-1630 C FLDG 19114 130TH AVE BE STREAM OVERFLOW 888G2 1991.1090 C DRAINAGE 18532 131ST AVE SE WATER PONDS IN YARD 686G2 1991-1000 NDA DRAINAGE 18532 131ST AVE BE YARD PONDS 886G2 1991-1090 SR DRAINAGE 1802 131ST AVE SE TO CIP 68502 1903-0041 WQC SEDIMENT 13120 SE 192ND ST $$6G2 1994-0676 WQC GRE:ENH2O SE 192ND & 134TH A SE DUCK WEED B85G2 1995-01" WQC OIUCARS 19312 133RD AVE SE RESIDENTIAL CAR MAINTENANCE 1588G2 1995-0374 C FILLING SE 192ND & 134TH SE WETLAND - REFD TO DOES 06G2 199&0391 FUR POND? 19118 130TH PL 5E HOLD-GPR WILL CALL HER 4 MORE DETAI $86G2 199$,0301 NDA POND? 19118 130TH PL SE HOLD-GPR WILL CALL HER 4 MORE DETAI 66$G2 1996oD391 R POND? 19118 130TH PL SE HOLD-GPR WILL CALL HER 4 MORE DETAI 555G2 1990.0480 C CRK FLDS 13607 SE 192ND 7 GROUNDWATER IMPACT WATER PONDI 666G2 1906.0921 FCR R(D POND 13341 9E 195TH ST OUTLET PIPE 09STRUCTE E) A,95FSSMEN 686G2 1998-1428 C SWALE 1891E 129TH PLACE SE OFFSITE FLOW IMPACTING PVT DRNG BY 686G2 1996-1428 NDA SWALE 18914 129TH PLACE SE OFFSITE FLOW IMPACTING PVT DRNG 5Y 686G2 1996-1428 R SWALE 18914 129TH PLACE BE OFFSITE FLOW IMPACTING PVT DRNG SY 686G2 -.} 199$-1550 C DRNG 19121 124TH AVE SE PLUGGED DIW CULVER7 I MPACT TO PVT 886F24ir— I8W1894 C RUNOFF 13416 BE 167TH WATER OVER SIDEWALK GROUNDWATE 68BG2 1997-0040 C DRNG 13007 BE 1$8TH PL GROUNDWATERISHEETFLOW PONDING 656G2 1997.1179 G DRAINAGE 19113 121ST PL 5E NSTALLATION OF DRNG IN RN OLD/OFF 88BF2 1997-1179 NDA DRAINAGE 19113 121ST PL BE INSTALLATION OF DRNG IN RAV OLD/OFF 6WF2 1997.1179 R DRAINAGE 10113 121ST PL SE INSTALI ATION OF DRNG IN RW OLDIOFF 686F2 1997-1301 C DRAINAGE 19123 121ST PL $E SUBSTANDARD INSTL OF DRNG SYS PVT 6NF2 1997-1319 FOR DUMPING 21709 146TH ST E DUMPED BATTERY IN RID POND B86Ga 1993-0026 C DRAINAGE 19133 121ST PL SE APPARENT OBSTRUCTION IN ROAD DRN W15F2 1999-0174 FCR CLGINLEMT 13415 Sty 187TH PL INLET PIPE APPARENTLY OBSTRUCTED G86G2 1999#40 C SPRINGS 13518 SE 186TH PL NEW SFR GROUND WATER INFIL ONTO P 686G2 199D 0632 C EASEMENT 19114 130TH AVE BE INFO PROVIDED ABOUT RID POND ON PR 686G2 1999-0679 FOR FENCE 18932 133RD PL gE I,EANIN6 FENCE; N@IDS REPAIR 666G2 20OM398 C DDM 1262S BE 102ND ST REQUEST TO DIVERT FLOW DISCHARGIN 686F2 2000-0735 FCR MNM 19000 134TH AVE SE CEDAR BOARD FENCE ARC}UND PERIMET 686G2 2001.050 W(0P WQP 13120 SE 192ND ST 68$G2 2032.0094 Fi REM 13055 BE %2ND ST SWM#63 REME;ASURE OF ORIGINAL 17.7 6r16G2 2002.0094 FIR REM 13055 SE 192ND ST SWM483 REMEASURE OF ORIGINAL 17,7 6MG2 2002-0204 FCR MMG 19000 134TH AVE SE 1) PSE UTILITY BOX DAMAGED, CALLED 686G2 2002.0424 C DDM 13003 BE 186TH PL SINKHOLE DEVELOPED APPARENTLY OV 68OG2 2002.0424 NDA- DDM 13003 SE 188TH PL SINKHOLE DEVELOPED APPARENTLY QV 68602 Page 2V$ 0 - 5 000 Ty" f Yp of "ft A&M Of Pe06 mcwe 6g1�1�t8 1a'Qi �8 Fair 2002.0424 R DOM 13003 SE 188TH PL ' V APPARENT S NKH4LE DEVELOPED APPARENTLY 4V 6 6602 2003-0266 C DDIV 18759 130TH AVE SE LOCAL PONDING PROBLEM. MAY BE THE 696G2 2003.0545 WQR WQB 18801 12aTH PL SE BSSF2 2003.0762 WQA WQAI 19433 VASHON HWY SW BMPS ary ALL IN PLACE 686F2 2003-0909 WQC WQDR 18601 126TH PL SE AUTO FLUID RESIDUE ON STREET A$ A R 6861`2 • Svbsev, e0 ` G.a P � i rt �3 � � aYtt, , , d✓ i, Pe beGWer ad'eA i1S�Y-t�C 1'�n UL YDJr,-3i �/l�� "fPvp_r,` Page 3 of 3 • APPENDIX C ANALYSIS AND DESIGN 0 • • • MEHRMAN PLAU sffE COYERAGE AREAS LIMITS DISTUI E BYPASS I WETLANDS lj pETEt TI 'N jr. ;POW 4 1 LIMITS OF bISTURBANCE + : � 1 i 75 150 1 SCALE: 1" = 150 ft EXISTING SITE (SF): PROPOSED SITE (SF): OFF --SITE TRIB. AREA (SO: FOREST: 237,176 (5.445 AC) BUILDINGS: 103,971 (2.387 AC) IMPERVIOUS: 22,780 (0.500 AC) PAVEMENT: 43,942 (1.009 AC) PASTURE: 270,072 (6.200 AC) TOTAL: 237,176 (5.445 AC) SIDEWALK: 3,260 (0.075 AC) POND: 11,280 (0,295 AC) TOTAL: 291,852 (6.700 AC) IMP SUB —TOTAL: 162,453 (3.729 AC) LANDSCAPE: 65,095 (1.517 AC) TOTAL: 228,548 (5.247 AC) BYPASS (SF): LANDSCAPE: 8,628 (0.198 AC) 72 r � • Impervious Areas Summary for Detention and Treatment Sizing Project: Wehrman Plat Project #: 485-MW Date: 2/28/2012 Existin (s#j ac Proposed s ac F Buildings: 103,971 2,387 Pavement: 43,942 1.009 Sidewalk: 3,260 0.075 Forest: 237,176 5,445 Pond: 11,280 0.259 Subtotal: 237,176 5.445 Imp: 162,453 3.729 Landscape 66,095 1.517 Subtotal: 228,548 5.247 Landscape: 8,628 WNW 0.198 Imp: 21,780 0.500 Imp: 21,780 0.500 Pasture: 270.072 6.200 Pasture: 270.072 6.200 Subtotal: 291,852 6.700 Subtotal: 291.852 6.700 Tot, Imp.: 21,780 0.500 Tot. Imp.: 184,233 4.229 Tot. Pasture: 270,072 6.200 Tot. Grass: 66,095 1.517 Tot. Forest: 237,176 5.445 Tot. Pasture: 270,072 6.200 Total: 529,028 12,145 Bypass Grass: 8,628 0.198 Total: 529,028 12.145 Backcheck: 529,028 12,145 Backcheck: 529,028 12.145 Drainage Calcs MW.xlsx Imp Areas Summ. 2/28/2012 • Wehrman Plat Runoff Ca1cs 12/16/09 Flow Frequency Analysis Time Series File:exist.tsf Project Location:Sea-Tac ---Annual Peak Flow Rates --- Flow Rate Rank Time of Peak (CFS) Computed Peaks Computed Peaks Computed Peaks Computed Peaks Computed Peaks Computed Peaks Computed Peaks Computed Peaks . Flow Frequency Analysis Time Series File:dev.tsf Project Location:Sea-Tac ---Annual Peak Flow Rates --- Flow Rate Rank Time of Peak (CFS) Computed Peaks Computed Peaks Computed Peaks Computed Peaks Computed Peaks Computed Peaks Computed Peaks Computed Peaks sumpks.txt LogPearson III Coefficients Mean= -0.346 StdDev= C,202 Skew= 0,037 ----Flow Frequency Analysis------- - - Peaks - - Rank Return ?rob (CFS) Period 1.35 100.00 0.990 1.18 50.00 0.980 1.02 25.00 0.960 0.820 10.00 D.900 0.779 8.00 0.875 0.667 5.04 0.800 0.450 2.00 0.500 0.317 1.30 0.231 LogPearson III Coefficients Mean= 0.140 StdDev= 0.120 Skew= 0.391 -----Flow Frequency Analysis------- - - Peaks - - Rank Return Prob (CFS) Period 2.85 lOO.00 0.99C 2.58 50.00 0.980 2,32 25.00 0,960 1.99 10.00 0.900 1.92 8.00 0,875 1.73 5.00 0.800 1.36 2,00 0.500 1,11 1.30 0.231 Flow Frequency Analysis LogPearson III Coefficients Time Series File:bypass.tsf Mean= -1.791 StdDev= 0.213 Project Location:Sea-Tac Skew= C.249 ---Annual Peak Flow Rates --- Flow Rate Rank Time of Peak (CFS) Computed Peaks Computed Peaks Computed Peaks Computed Peaks Computed Peaks Computed Peaks Computed Peaks Computed Peaks Level 2 Det Pond (V deep) Int size = (1.18-(0,450*0.5)/36-1 = O.D27 1st int. = 0.450*0.5 = 0.225 Qmax (Orif 1) = 4/3*0.225-0.016 = 0.284 Ht (Orif 2) = 3/4*4 = 3' -----Flow Frequency Analysis------- - - Peaks - - Rank Return Prob )CFS) Period 0,055 100,00 0.990 D.047 5C.00 0.980 0.040 25.00 0.960 0.C31 10.00 0.9D0 0.029 8.00 0.875 0.024 5.OD 0.800 0.016 2,OD 0.500 0.011 1.30 0.231 Page 1 Wehrman Plat KCRTS runoff output file: pond.doc KCRTS Command ------------- CREATE a new Time Series -------------------------- Production of Runoff Time Series Project Location Sea-Tac Computing Series exist.tsf Regional Scale Factor 1.00 Data Type Historic Creating Hourly Time Series File Loading Time Series File:Co\KC_SWDM\KC_DATA\STTF60H.rnf Till Forest 5.72 acres Loading Time Series File:C:\KC_SWDM\KC_DATA\STTP60H.rrif Till Pasture 6.19 acres Loading Time Series File!C:\KC_SWDM\KC DATA\STE160H.rnf Impervious 0.55 acres -------------- Total Area 12.46 acres Peak Discharge: 1.16 CFS at 6:00 on Jan 9 in 1990 Storing Time Series File:exist.tsf Time Series Computed KCRTS Command ------------- CREATE a new Time Series ------------------------ Production of Runoff Time Series Project Location : Sea-Tac Computing Series dev.tsf Regional Scale Factor 1.D0 Data Type Historic Creating Hourly Time Series File _ Loading Time Series File;C:1KC SwpM1KC DATA\STTP60H.rnf Till Pasture 6.19 acres Loading Time Series File: C:\KC_SWDM\KC_DATA\STTG6DH.rnf Till Grass 1.74 acres Loading Time Series Fi:.e:C:\KC_SWDM\KC_DATA\STEI60H.rnf Impervious 4.28 acres -------------- Total Area 12.23 acres Peak Discharge: 2.70 CFS at 6:00 on Jan 9 in 1990 Storing Time Series File:dov.tsf Time Series Computed KCRTS Command ------------- CREATE a new Time Series ------------------------ Production of Runoff Time Series Project Location : Sea-Tac Computing Series : bypass.tsf Regional Scale Factor : 1.00 Data Type : Historic Creating Hourly Time Series File Loading Time Series File:C:\KC_SWDM\KC_DATA\STTG60H_rnf Till Grass 0.25 acres -------------- Total Area 0.25 acres Peak Discharge: 0.D53 CFS at 16:00 on Mar 3 in 1950 Storing Time Series File:bypass.tsf Time Series Computed KCRTS Command ------------- Enter the Analysis TOOLS Module ------------------------------- 0 Analysis Tools Command • • Compute -PEAKS -and -Flow -Frequencies Loading Time Series File:exist.tsf Flow Frequency Analysis LogPearson III Coefficierts -------------------------------------------------------- Time Series File:exist.tsf Mean= -0.346 StdDev= 0.202 Project Location:Sea-Tac Skew= 0.037 Frequencies & Peaks saved to File:exist.pks Analysis Tools Command ---------------------- Compute PEAKS and Flow Frequencies ------------------------------------ Loadirg Time Series File:dev,tsf Flow Frequency Analysis LogPearson III Coefficients -------------------------------------------------------- Time Series File dev.tsf Mean= 0.140 StdDev= 0-120 Project Location:Sea-Tac Skew= 0.391 Frequencies & Peaks saved to File:dev.pks Analysis Tools Command ---------------------- Compute PEAKS and Flow Frequencies ------------------- Loading Time Series File:bypass.tsf Flow Frequency Analysis LogPearson III Coefficients ---------------------------------------------------------- Time Series File:bypass.tsf Mean=-1,791 StdDev= 0.213 Project Location:Sea-TaC Skew= 0.249 Frequencies & Peaks saved to File:bypass.pks Analysis Tools Command ---------------------- RETURN to Previous Menu ----------------------- KCRTS Command ------------- eXit KCRTS PrOgram ---------------- �✓k • • 0 KCRTS Program -File Directory: C:IKC_SWDM%KC_DATA\ [C] CREATE a new Time Series ST 5.72 0,00 0,000000 Till Forest 6.19 0.00 0.000000 Till Pasture 0.00 0.00 0.000000 Till Grass 0.00 0.00 0.000000 Outwash Forest 0.00 0.00 0.000000 Outwash Pasture 0.00 0.00 0.000000 Outwash Grass 0,00 0.00 0.000000 Wetland 0.55 0.00 0.000000 Impervious Q.5 exist.tsf F 1.00000 T [C] CREATE a new Time Series ST 0.00 0.00 0.000000 Till Forest 6.19 0.00 0.000000 Till Pasture (. L 1.74 0,00 0.000000 Till Grass 1.52. 0,00 0.00 0.000000 Outwash Forest 0.00 0,00 0.000000 Outwash Pasture 0.00 0.00 0.000000 Outwash Grass 0,00 0.00 0.000000 Wetland 4,28 0.00 0.000000 Impervious q,13 dev.tsf F 1.00000 T [C] CREATE a new Time Series ST 0.00 0.00 0.000000 Till Forest 0.00 0.00 0.000000 Till Pasture 0.25 0.00 0,000000 Till Grass 0110 0.00 0.00 0.000000 Outwash Forest 0.00 0.00 0.000000 Outwash Pasture 0.00 0.00 0.000000 Outwash Grass 0.00 0.00 0.000000 Wetland 0.00 0.00 0.000000 Impervious bypass.tsf F 1.00000 T M Enter the Analysis TOOLS Module [P] Compute PEAKS and Flow Frequencies exist.tsf exist.pks [P] Compute PEAKS and Flow Frequencies dev.tsf dev.pks [P] Compute PEAKS and Flow Frequencies bypass.tsf bypass,pks [R] RETURN to Previous Menu [X] eXit KCRTS Program j) 414.1--Y �4 � � AMA, n'-9000 �' rf�22 -ur AAE& N 2e r 1 fA TD �, L.(,- I • L` 0 Wehrman Plat Runoff Calcs compare offsite flows to fully developed onsite flows to determine need for bypass. 7/29/08 Flow Frequency Analysis Time series File:offsite.tsf Project tocation:sea-Tac ---Annual Peak Flow Rates --- Flow Rate Rank Time of Peak (CFS) 0,520 3 2/09/01 15:00 0.270 7 1/05/02 16:00 0.524 2 2/28/03 3:00 0.152 8 8/26/04 2:00 0.301 6 1/05/05 8:00 0.501 4 1/18/06 16:00 0.476 5 11/24/06 4:00 0.985 1 1/09/08 6:00 computed Peaks Flow Frequency Analysis Time Series File:devsite.tsf Project Location:sea-Tac --Annual Peak Flow Rates --- Flow Rate Rank Time of Peak (CPS) 1.01 6 2/09/01 2:00 0.836 8 1/05/02 16:00 1.22 3 2/27/03 7:00 0.913 7 9/26/04 2:00 1.10 4 10/28/04 16:00 1.08 5 1/18/06 16:00 1.33 2 10/26/06 0:00 2.05 1 1/09/08 6:00 computed Peaks -----Flow Frequency Analysis -------- - - Peaks - - Rank Return Prob (CFS) period 0.985 1 100.00 0.990 0.524 2 25.00 0.960 0.520 3 10.00 0.900 0.501 4 5.00 0,800 0.476 5 3.00 0.667 0.301 6 2.00 0.500 0.270 7 1.30 0.231 0.152 8 1.10 0.091 0.832 50.00 0.980 -----Flow Frequency Analysis------- - - Peaks - - Rank Return Prob (CFS) Period 2.05 1 100.00 0.990 1,33 2 25.00 0,960 1.22 3 10.00 0.900 1.10 4 5.00 0.800 1.08 5 3.00 0.667 1.01 6 2.00 0.500 0.913 7 1.30 0.231 0.836 8 1,10 0.091 1.81 50.00 0.980 Existingg upstream (Offsite) 100-year Q = 0.985 cfs 50% of 100-year Developed (undetained) Q = 0.5n2.05 = 1.025 cfs 0.985cfs < 1.025cfs; therefore, no need to bypass offsite flows. KCRTS Program...File Directory: C:\KC_SWDM\KC_DATA\ [C] CREATE a new Time Series ST 40 0.00 0100 0.000000 Till Forest 6.20 0,00 0,000000 Till Pasture 0.00 0.00 0.000000 Till Grass 0.00 0.00 0.000000 outwash Forest 0.00 0.00 0.000000 outwash Pasture 0.00 0.00 0.000000 outwash Grass 0.00 0.00 0.000000 wetland 0.50 0.00 0.000000 Impervious offsite.tsf T 1.00000 T [C] CREATE a new Time Series ST 0.00 0,00 0.000000 Till Forest 0.00 0.00 0,000000 Till Pasture 1.79 0.00 0.000000 Till Grass 0.00 0.00 0.000000 Outwash Forest 0.00 0.00 0.000000 outwash Pasture 0.00 0.00 0.000000 outwash Grass 0.00 0.00 0.000000 wetland 3.53 0.00 0,000000 Impervious devsite.tsf T 1.00000 T [T] Enter the Analysis TOOLS Module [P] Compute PEAKS and Flow Frequencies offsite.tsf offsite.pks [[P] compute PEAKS and Flow Frequencies devsite.tsf devsite.pks [R] RETURN to Previous Menu [x] exit KCRTS Program • 0 j MPU-T- DATA f b� Xr S j TE FL 0,AJ C,0i' j s a tJ APPENDIX C-1 DETENTION FACILITIES DESIGN • • hrman Wetenti Plat Retention/Detention Facility Tyne of Facility: Detention Pond Side Slope: 3.00 H;1V Pond Bottom Length: 180.00 ft Pond Bottom width: 55.00 ft Pond Bottom Area: 9900, sq. ft Top Area at 1 ft. FS: 19656. sq. ft 0.451 acres Effective Storage Depth: 5.00 ft Stage 0 Elevation: 0,00 ft Storage Volume: 68625. cu. ft 1.575 ac-ft Riser Bead; 5.00 ft Riser Diameter: 12.00 inches Number of orifices: 2 Full Head Pipe Orifice # Height Diameter Discharge Diameter (ft) (in) (CFS) (in) 1 0.00 2.10 0.267 2 3.00 3,2C 0.393 6.0 Top Notch Weir: None Outflow Rating Curve: None Stage Elevation Storage Discharge Percolation Surf Area (ft) (ft) (cu. ft) (ac-ft) {cfs) (cfs) (sq. ft) 0.00 0.00 0. 0,000 0.000 0.00 9900, O.D2 0,02 198. 0.005 0.018 0.00 9928. 0.04 0.04 397. 0.009 0.025 0.00 9956. 0.07 0.07 697_ 0.016 0.031 0.00 9999. 0.09 0.09 897. 0,021 0,035 0.00 10027. 0.11 0,11 1098. 0.025 0.040 0.00 10056, 0.13 0.13 1299. 0,030 0.043 0.00 10084, 0.15 0.15 1501. 0.034 0.047 0,00 10112, 0.17 0.17 1703. 0.039 0.050 0.00 10141, 0.20 0.20 2008. 0.046 0.053 0.00 10183. 0.30 0.30 3034. 0,070 0.065 0.00 10326. 0.40 0.40 4374. 3.094 0.075 0.00 10470, 0.50 0.50 5128. 0.118 0.C64 0.00 10614. 0.60 0.60 6196. 0.142 0,092 C.00 10759. 0.70 0.70 7280_ 0.167 0,100 0.0C 109C5. 0.80 0.80 8377. 0.192 0.107 0.00 11051. 0.90 0.90 9490. 0.218 0,113 0.00 11198. 1.00 1.00 10617. C.244 0.119 C.00 11346. 1.10 1.10 11759. 0,270 0.125 0.00 11495, 1.20 1.20 12916, 0.297 0.131 0.00 11644. 1.30 1.30 14088. 0,323 0,136 0.00 11794. 1.40 1.40 15275. 0.351 0.141 0.00 11945, 1.50 1.30 16477. C.378 0.146 0.00 12096. 1.60 1.60 17694. 0.406 0.151 0.00 12246, 1.70 i.70 18926. 0,434 0.156 0.00 12401. 1.80 1.80 20174. 0.463 0.160 0.00 12555. 1.90 1,90 2i437. 0.492 0.165 0,00 12709. 2.00 2.00 22716, D.521 0.169 0.00 12864. 2.10 2.13 24010, 0.551 0.173 0.00 13020, 2.20 2.20 25320. 0.581 0.177 0.03 13176. 2,30 2.30 26645. 0.612 0.181 0.00 13333. 2.40 2,40 27987, 0,642 D.185 0,00 13491. 2,50 2.50 29344. 0.674 0.189 O.OD 13650. 2.60 2.60 30717, 0.705 0.193 0.00 13809_ 2,70 2.70 22106. 0.737 0.196 0.00 13969. 2.80 2.80 33511, 0,769 D.200 0.00 14130. 2,90 2.93 34932. 0.602 0,204 0.00 14292. 3.00 3,00 36369. 0,835 0.207 0.00 14454. 3.03 3.03 36803. 0.845 0.211 0.0D 14503. 3,07 3.10 3,07 3.10 17381, 37823. 1,111 0.868 0,220 0.234 1,CO 0.00 14568, 14617. 3.13 3.13 28262, 0,878 0.252 0.00 14666. 212 3,17 3.17 38850. 0.892 C.276 0.00 14731. 3.20 3.20 39292. 0,902 C,304 0.00 14781, 3.23 3.23 39737. 0,912 0,333 MO 14630, 3.27 3.27 40331. 0.926 0.360 0.00 14896, 3.30 3.30 40779. 0.936 0.369 0.00 14945. 3.40 3.40 42281, 0.971 0,396 0.00 15110, 3.50 3.50 43801. 1.006 0.420 0.00 15276. 3.60 3.60 45337. 1,041 0.442 0.00 15443, 3.70 3.70 46889. 1.076 0.462 0.00 15610. 3.80 3.60 48459. 1.112 0.482 0.00 15778, 3,90 3.90 50045. 1.149 0.500 0.00 15947. 4.00 4.00 51648. 1,186 0,517 0.00 16116. 4.10 4.10 53268. 1.223 0.534 0.00 16286. 4.20 4.20 54905. 1.260 0,549 0.00 16457. 4.30 4.30 56560, 1.298 0,565 0.00 16629. 4.43 4,40 58231. 1.337 0.580 0.00 16601, 4.50 4.50 59920. 1.376 0.594 0.00 16974. 4.60 4.60 61626, 1.415 O.E08 0.00 17148. 4.70 4,70 63349. 1.454 9.621 0.00 17322. 4.80 4.80 65090. 1.494 0.635 0.00 17497. 4.90 4.90 66849. 1.535 0.648 0.00 17673. 5.00 5.00 68625. 1.575 0.660 0.00 17850. 5.10 5.10 70419. 1.617 0.981 0.00 18027, 5.20 5.20 72230. 1.658 1.560 0.00 18205. 5,30 5.30 74060. 1.700 2.300 0.00 18384. 5,40 5.40 75907. 1.743 3.100 0.00 18564. 5.50 5.50 77773. 1,785 3.390 0.00 18744. 5.60 5.60 79656. 1.829 3.660 0.00 13925. 5.70 5.70 81558. 1.672 3.910 9.00 19107. 5.80 5.80 83478. 1.916 4.140 0.00 19289, 5.90 5.90 85416. 1.961 4.350 0.00 19472. 6.00 6.00 87372. 2.006 4.560 0100 19656. 6.i0 6.10 89347. 2.051 4.750 0.00 19841. 6.20 6.20 91340, 2.091 4.940 0.00 20026. 6.30 6.30 93352. 2.143 5.120 0.00 20212, 6.40 6.40 95383. 2,190 5.290 0100 20399. 6.50 6.50 97432, 2.237 5.460 0.00 20586. 6.60 6.60 99500. 2.284 5.620 0.00 20774. 6.70 6.70 101587. 2.332 5.780 0.00 20963. 6.80 6.80 103692. 2.380 5.930 0.00 21153. 6.90 6.90 105817. 2.429 6.080 0.00 21343. 7.00 7.00 1C7961. 2.478 6.220 0.00 21534. Hyd Inflow Outflow Peak Storage Stage E1ev {C•a-Ft} IAc-Ft} 1 1.57 1.13 5,13 5.13 70674. 1.627 2 1.82 1.08 5.12 5.12 70720, 1.623 3 2.7C 0.83 5.05 5.05 69600. 1.598 4 1.80 0.60 4.52 4.52 60215, 1.382 5 2.35 0.59 4.47 4.47 59412. 1.364 6 1.57 0.52 4,03 4.03 52'-50. 1."197 7 1.18 0,32 3,22 3.22 39611, 0.909 8 1.04 0.19 2.62 2.62 30980. C.711 Hyd R/D Facility Tributary Reservoir POC Outflow Outflow Inflow Inflow Target talc 1 1.13 0.02 ******** 1.35 1.14 2 1.08 0.03 *+**+*** ******* 1.09 3 0.83 0.05 ******** ******* 0.85 4 0.60 0.02 ******** ******* 0.61 5 0.59 0.03 ***w*xxx xxx***+ 0.60 6 0.52 0.02 ******** ******* 0.53 7 0.32 0.01 ******** ******* 0.33 8 0,19 0.01 *x**xxxx ***x**. 0.20 ---------------------------------- Route Time Series through Facility Inflow Time Series File:dev.tsf Outflow Time Series File:rdout FOC Time Series File:dsout 312 Inflow/Outflow Analysis Peak Inflow Discharge: 2.?0 CFS at 6:00 on ,Ian 9 in 1990 Peak Outflow Discharge: 1.13 CFS at 19:00 on Feb 9 in 1951 Peak Reservoir Stage: 5.13 Ft Peak Reservoir E1ev: 5.13 Ft Peak Reservoir Storage: 70874. Cu-Ft 1.627 Ac-Ft Add Time Series:bypass.tsf Peak Summed Discharge: 1.14 CFS at 19.00 on Feb 9 in 1951 Point of Compliance File:dsout.tsf Flow Frequency Analysis LogPearson III Coefficients Time Series File•rdout.tsf Mean- -0.5C3 StdDev= 0.231 Project Location.Sea-Tac Skew= 0.452 ---,Annual Peak Flow Rates--- -----Flow Frequency Analysis------- FlowRate Rank Time of Peak - - Peaks - - Rank Return Prob {CFS) (CFS) (ft) Period 0,193 39 2/17/49 9:00 1.13 5.13 1 89,50 0.989 0.412 14 3/05/50 5:00 1,Q8 5.12 2 32.13 0.969 1.13 1 2/09/51 19:00 0.834 5.05 3 19.58 0,949 0.172 45 2/01/52 4:00 0.649 4.91 4 14,08 0.929 0.194 37 1/12/53 7:00 0.633 4.79 5 10,99 0,909 0.371 19 1/06/54 7:00 0.596 4.52 6 9,01 0.889 0.406 15 2/OB/55 3:00 0.590 4.47 7 7.64 0.869 0.456 12 1/06/56 10:00 0.552 4.22 8 6.63 0.849 0.273 30 2/26/57 3:00 0.542 4.15 9 5.86 0.829 0.367 22 1/17/58 7:00 0.522 4.C3 10 5.24 0.809 0.201 32 1/24/59 16:00 0.520 4.02 11 4.75 0,789 0.633 5 11/21/59 3:00 0.456 3.67 12 4.34 0.769 0.325 26 11/24/60 11:00 0.442 3.60 13 3.99 0.749 0.165 47 1/03/62 9:00 0.412 3.47 14 3.70 0.729 0.314 27 11/26/62 10:00 0.408 3.45 15 3.44 0,709 0.205 31 1/02/64 0:00 0.384 3.36 16 3.22 0.690 0.376 18 12/01/64 2:00 0.380 3.34 17 3.03 0.670 0.197 36 12/28/65 18:DO C.376 3.33 16 2.85 0.650 0.380 17 12/13/66 9:00 C.371 3.31 i9 2.13 0,630 0.199 34 1/20/68 20:00 C,371 3.31 20 2.56 0.6i0 0.193 38 12/04/68 3:00 0.371 3.31 21 2.44 0,690 0.200 33 1/14/70 17:00 0.367 3.25 22 2.32 0.570 0.361 23 12/07/70 4:00 C.361 3.27 23 2.22 0.550 0.542 9 2/28/72 7:00 0.360 3.27 24 2.13 0.530 0.295 29 12/26/72 19:00 0.342 3.24 25 2.04 0.510 0.360 24 1/16/74 17:00 0.325 3.22 26 1.96 0.490 0.371 21 12/27/74 7:00 0.314 3.21 27 1.89 0.470 0.371 20 12/04/75 1:00 0.309 3.21 28 1.62 0.450 0.142 50 8/26/77 6:00 0.295 3.19 29 1.75 0.430 0.342 25 12/15/77 18:00 0,273 3.16 30 1.70 0.410 0.159 48 2/12/79 17:00 0.205 2.95 31 1.64 0.290 0.522 1C 12/15/79 13:00 0,201 2.83 32 1.59 0.370 0.198 35 12/27/80 8:00 0.200 2.B0 33 1.54 0,350 0.590 7 10/06/81 18:00 C.199 2,78 34 1.49 0.330 0.384 16 1/05/63 15:00 0.198 2.75 35 1.45 0.310 0.179 44 12/10/83 18:00 0.197 2.72 36 1.41 0.291 0.163 43 11/04/84 0:00 0.194 2.62 37 1.37 0.271 0.552 8 1/18/86 23:00 0.193 2.61 38 1.33 0.251 0.596 6 11/24/86 8:00 0.193 2.61 39 1,30 0,231 0.188 42 1/15/80 6:00 0.192 2.56 40 1.27 0.211 0.168 46 11/05/88 21:00 0.190 2.53 41 1.24 0.191 0.834 3 1/09/90 11:00 C.186 2.47 42 1.21 0.171 0.649 4 4/05/91 6:00 0.183 2.35 43 1.18 0.151 0,309 28 1/30/92 9:00 0,179 2.26 44 1.15 0.131 0.192 40 3/23/93 12.00 0.172 2.08 45 1.12 (),Ill C,144 49 2/17/94 21:00 0.168 1.97 46 1.10 0.091 0.442 13 2/19/95 22:00 0.165 1,69 47 1.08 0.071 1.08 2 2/09/96 2:00 C,159 1.77 48 1.05 0.051 0.520 11 1/02/97 12.00 0.144 1.46 49 1.03 0,031 0.19C 41 10/30/97 12:00 0.142 1.42 50 1.01 0.011 Computed Peaks 1,29 5.15 100.00 0.990 Computed Peaks 1.06 5.il 50.00 0.960 Computed Peaks 0.863 5.06 25.00 0.960 419 Computed Peaks 3.635 4.80 10.00 0.900 Computed Peaks 0.594 4.50 8.00 0.875 Computed Peaks 0.4B5 3.81 5.00 O.BOO Computed Peaks 0.202 3,20 2.00 0.500 Computed Peaks 0,208 3.01 1.30 0.231 Flow Frequency Analysis LogPearson Ill Coefficients Time Series File:dsout.tsf Mean- -0.493 Stdoev= 0.230 Project Location:Sea-Tac Skew= 0.448 ---Annual Peak Flow Rates--- -----Flow Frequency Analysis------- FlowRate Rank Time cf Peak - Peaks - - Rank Return Prob (CFS} (CFS) Period 0.199 38 2/17/49 9:00 1.14 1 89.50 0.989 0.419 14 3/05/50 5:00 1.09 2 32.13 0.969 1.14 1 2/09/51 19:00 0.848 3 19.58 0.949 0.177 45 1/30/52 16:00 0.664 4 14.08 0.929 0.198 39 1/12/53 7:00 0.648 5 10.99 0.909 0,379 20 1/06/54 7:00 0.610 6 9.01 O.8B9 0.418 15 2/C8/55 2:00 0.603 7 7.64 3,669 0.464 12 1/06/56 10:00 0.566 B 6.63 0.849 0.278 30 2/26/57 2:0D 0.554 9 5.86 0.829 0.374 22 1/17/58 6:00 0.533 10 5.24 0.809 0,207 32 1/24/59 14:00 0.529 11 4.75 0.789 0.646 5 11/21/59 2:00 0.464 12 4.34 0.769 0.332 26 11/24/60 11:00 0.452 13 3.99 0,749 0,169 47 1/03/62 8:00 C.419 14 3.70 0.729 0.320 27 11/26/62 10:00 C.418 15 3.44 0,709 0.212 31 1/02/64 0:00 0.394 16 3.22 0.690 0.364 18 12/01/64 2:00 0,389 17 3.03 0.670 0.202 36 12/28/65 18:00 0.384 18 2.85 0.650 0.389 17 12/13/66 9:00 0,260 19 2.'10 0.633 0.205 34 1/20/68 20:00 0,379 20 2.56 0.610 0.200 37 12/04/68 1:00 0.378 21 2.44 0.590 0.206 33 1/14/70 15:00 3.374 22 2.32 0.570 0.368 23 12/07/70 4:00 0.368 23 2.22 0,550 0.554 9 2/28/72 7:00 0.367 24 2.13 0.530 0.302 29 12/26/72 19:00 0.349 25 2.04 0.510 0.367 24 1/16/74 17:00 0,332 26 1.96 0.490 0.380 19 12/27/74 7:00 0.320 27 1.89 0.470 0.378 21 12/04/75 1:00 0.315 2B 1.82 0.450 0.144 50 8/26/77 6:00 0.302 29 1.75 0.430 0.349 25 12/15/77 18:00 0.278 30 1.70 0.410 0.163 48 2/12/79 18:00 0.212 31 1.64 0.390 0.533 10 12/15/79 12:00 0.207 32 1.59 0.37D 0.203 35 12/27/60 7:00 0.206 33 1.54 0.350 0.603 7 10/06/81 16:00 2,205 34 1.49 01330 0.394 16 1/05/63 15:00 0.203 35 1.45 0.310 0.184 44 12/10/83 18:00 3.202 36 1.41 0.291 0.107 43 11/03/84 23:00 0.200 37 1.37 0.271 0.566 B 1/18/86 23700 0.199 36 1.33 0,251 0.610 6 11/24/86 8:00 0.198 39 1.30 0.231 0.192 42 1/15/88 6:00 0.198 40 1.27 0,211 0.172 46 11/05/88 21:DO 0.196 41 1.24 0.191 0.848 3 1/D9/90 11:00 0.192 42 1.21 0.i71 0.664 4 4/05/91 6:00 0.187 43 1,18 0.151 0.315 28 1/30/92 9:OC 0.184 44 1.15 0.131 0.198 40 3/23/93 9:00 0.177 45 1.12 0.111 0.147 49 2/17/94 20:00 0,172 46 1.20 0.091 0.452 13 2/19/95 22:00 0.169 47 1.08 0.071 1.09 2 2/09/96 2:00 0.7-63 48 1.05 0.051 0,529 11 1/02/97 12:OC 0,147 49 1.03 0.031 C.196 41 10/30/97 12:OC 0.144 50 1.Di 0,011 Computed Peaks 1.31 100.00 0.990 Comnuted Peaks 1.08 50.00 0.980 Computed Peaks 0.677 25.00 0.960 Computed Peaks 0.647 10.00 0.900 Computed Peaks 0.605 8.00 0.875 Computed Peaks 0.495 5.0D 0.800 Computed Peaks 0.309 2.00 0.500 Comnuted Peaks 0.213 1.30 0.231 5/2 Flow Duration from Time Series File:rdcut.t5f- C�torf Count Frequency CDF Exceedence Prol-ability CFS % % 0.016 298015 68.040 68.040 31.960 0.320E+00 0.047 44834 10.236 78.276 21.724 0.217E+CD 0.079 38471 8,783 67.059 12.941 0,129E+00 0.110 23763 5.425 92.485 7,515 0,752E-01 0.142 15776 3.602 96.087 3.913 0.391E-01 0.173 9297 2.123 98.209 1.791 0,179E-01 0.205 5175 1.182 99.391 0,609 0.639E-C2 0.236 1042 0.238 99.629 0.371 0,371E-02 C.267 267 0.061 99.689 0,311 0.311E-02 0.299 207 0.047 99.737 0.263 0.263E-02 0.330 131 0.030 99.767 0,233 0.233E-02 0.362 148 0.034 99.800 0.200 0.200E-02 0.393 193 0.044 99.845 0.155 0.155E-02 0.425 135 0.031 99.875 0.125 0,125E-02 0.456 122 0,028 99.903 0.097 0.968E-03 0.4B8 86 0.020 99.923 0.077 0.772E-03 0.519 87 0.020 99.943 D.057 0.573E-03 0.550 68 0.016 99.958 0.042 0.418E-03 0.582 52 0.012 99.970 0.030 0.299E-03 0.613 58 0.013 99.983 0.017 0.167E-03 0.645 3B 0.009 99.992 0.00E 0,799E-04 0,676 19 0.004 99.996 0.004 0,365E-04 0,708 2 0,000 99.997 0.003 0.320E-04 0.739 1 0,000 99.997 0.003 0.297E-04 0.771 2 0.000 99.997 0.003 0.251E-04 0.802 1 0.000 99.99E 0.002 0.228E-04 0.833 1 0.000 99.99E 0.002 0.205E-04 0.865 3 0.001 99.999 0.001 0.137E-04 0.896 1 0.000 99.999 0.001 0.114E-04 0.928 0 0.000 99.999 0.00i 0.114E-04 0.959 0 0.000 99.999 0.001 0.114E-04 0,991 2 0.000 99.999 0.001 0.685E-05 1,02 1 0.000 100.000 0.000 0.457E-05 1.05 0 0.000 100,00C 0.000 0.457E-05 1.08 1 0.000 100.000 0.000 0.22BE--05 1.12 0 0.000 100.000 0.000 0.228E-05 Flow Duration from Time Series File:dsout.tsf Cutoff Count Frequency CDF Exceedence_Probability CFS % % % 0.016 298271 68.09E 68.096 31.902 0.319E+00 0,048 44865 10.243 78.342 21.65E 0,217E+00 0.080 38150 6.710 87.052 12.948 0.129E+00 0.112 23412 5.345 92.397 7.603 3.760E-01 0.143 15867 3,623 96.019 3.981 0.398E-01 0.175 9280 2.119 98.138 1.862 0.186E-01 0.207 5262 1,201 99.340 0.661 0.661E-02 0.239 1221 0.279 99.616 0.382 0.382E-02 0.271 298 0.068 99.686 0.314 0.314E-02 0.302 201 0.046 99.732 0.268 0.268E-02 0.334 142 0.032 99.765 0.235 0,235E-02 0.366 138 0.032 99.796 0.204 0.204E--02 0.398 195 0.045 99.841 0.159 0.159E-02 0.430 137 0.031 99.872 0.128 0.12BE-02 0.461 121 0.028 99.900 0.100 0.100E-02 0.493 89 0,020 99.920 0.080 0.801y-03 0.525 87 0.020 99,940 0.060 0.603E-03 0.557 67 0.015 99.955 0.045 0,450E-03 0.589 54 0.012 99.967 0.033 0.326E-03 0.620 63 0,014 99.982 0.018 0.183E-03 0.652 36 0,00E 99.990 0.010 0.100E-03 0.684 28 0.006 99.996 0.004 0,365E-04 0,716 0 0.000 99.996 0.004 0.365E-04 0.748 3 0.001 99.997 0.003 0.297E-04 0,779 2 0.000 99.997 0.003 0.251E-04 0.811 1 0,000 99.998 0.002 0.228E-04 0,843 1 0.000 99.998 0.002 0.205E-04 0.875 2 0.000 99.998 0.002 0,160E-04 lit 0 0 0,907 2 0.000 99.999 0.001 0.114E-04 0.938 O 0.000 99.999 0.001 0.114E-04 0.970 0 0.000 99.999 0.301 0.114E-04 1.00 i 0.000 99,999 0.001 0.913E-05 1.03 2 0.000 100,000 0.000 0.457E-05 1.07 0 0.000 100.000 0.000 0.457E-05 1.10 1 0.000 100,000 0.000 0.228E-05 1.13 0 0.000 10D.000 0.000 0.22BE-05 Duration Comparison Anaylsis Base File: exist.tsf New File: dsout.tsf Cutoff Units: Discharge in CFS -----Fraction of Time ----- ---------Check of Tolerance ------- Cutoff Base New %Change Probability Base New %Change 0.224 0.66E-02 0.43E-02 -35.5 1 0.66E-02 0.224 0.207 -7,5 0.296 0.32E-02 0.27E-02 -14.1 1 0.32E-02 0.296 0.268 -9.4 0.367 i 0,17E-02 0.20E-02 18.2 1 0,17E-02 0.367 0.387 5.3 0.439 I 0.91E-03 0.12E-02 32.5 1 0.91E-03 0.439 0.474 7.8 0.511 i 0.53E-C3 0.69E-03 30.0 I 0,53E-03 0.511 0.536 4.8 0.583 1 0.33E-03 D.35E-03 4.1 1 0.33E-03 0.583 0.566 0.6 0.654 i 0.20E-03 0.89E-04 -55.7 1 0,20E-03 0.654 0.611 -6.6 0.726 i 0.96E-04 0,32E-04 -66.7 j 0.96E-04 0.726 0,653 -10.1 0.798 I 0.55E-04 0.25E-04 -54.2 1 0.55E-04 0.798 0.667 -16.3 0.869 I 0.30E-04 0.16E-04 -46.2 k 0.30E-04 0.869 0.755 -13.1 0.941 I 0.14E-04 0.11E-04 -16.7 k 0,14E-04 0.941 0.863 -6.2 1.01 i 0.14E-04 0.68E-05 -50.0 [ 0,14E-04 1.01 0.883 -12.8 1.08 I 0.11E-04 0.46E-05 -60.0 1 0.11E-04 1.08 0.990 -8.7 1.16 i 0.23E-05 0.00E+00 -100.0 I 0,23E-05 1.16 1.14 -1.6 Maximum positive excursion = 0.039 cfs { 8.7%) occurring at 0.453 cfs on the Base Data:exist.tsf and at 0.492 cfs on the New Data:dsout,tsf Maximum negative excursion = 0.178 cfs (-20.8%) occurring at 0.858 cfs on the Base Data;exist.tsf and at 0.680 cfs on the New Data:dscut.tsf n � J I 1 • (SJO) a5jeuasia E Riser Overflow and Secondary Inlet "Jailhouse Window" (iteratively sizes the flow control riser and a "jailhoese window" secondary inlet using the sharp crested weir eqn.) Project: Wehrman Plat Date: 1018l2008 By: LT Rectangular, Sharp Crested Weir Q = C (L - 0.2H) H"3/2 C = 3.27 * 0.40HIP Q(100) =103 cfs H P L C Q 0,46 4.5 3.1 3.3 3.15 0.46 4.5 3.1 3.3 3.11 12" riser Jailhouse Window See Erosion Control Calculations for Emergency Overflow Spillway Sizing Drainage C2IC5 MW.xis Jailhouse Window Printed: 101812008 • APPENDIX C-2 TREATMENT FACILITIES DESIGN IE Treatment Pond Sizing Routine Project: Wehrman Piat Treatment Pond Date: 2/2812012 Blue represents manual entry fields Red represents calculated fields Step 1: Wetpool volume factor (f) ...either 3 or 4.5 f= 3 Step 2: Mean annual rainfall (R) ...from Fig. 6.4.1.A, pg 6-69 R = 0.47 in Step 3: Runoff (Vr) ... V r=(0.9Ai+0.25Atg+0.10Atf+0.01 Ao)xR/12 Ai = 151.173 sf Atg = 65,095 sf Atf = 0 sf Ao = 0 sf Vr = 5,966 cf Step 4: Wetpool volume (Vb) ...Vb=fVr Vb = 17,899 cf Step 5: Wetpool dimensions ...Vb=h(A1+A2)12 Solve by trial & error Al = 6,608 sf L = 47 ft 3f_ = 141 ft h= 4ft S= 3ft A2 = 2,678 sf 'Vb = 18,573 of If Vb calculated in Step 5 < Vb from Step 4, then increase h Cell 1 must contain 25% - 35% of total Wetpool volume Cell 1 required volume between 4,643 and 6,501 cf Cell (47x47) Cell (47x160) Al = 2,200 sf Al = 7,532 sf h= 4ft h= 2ft S= 3ft S= 3ft A2 = 525 sf A2 = 5,593 sf V = 5,449 cf V = 13,125 cf 'Vb = 18,574 cf This spreadsheet determines the required size and geometry for the wetpool. The physical constraints of the site and the detention sizing requirements will change the treatment pond dimensions; however, these minimum parameters must be met. Drainage Calcs MW.xlsx (Treatment Pond ) 2/28/2012 • APPENDIX C-3 EROSION CONTROL FACILITIES DESIGN • • 1/4 KCRTS Program... File Directory: KC_SWDM\KC—DATA\ CREATE a new Time Series ST 0.00 0.00 0,000000 Till Forest 6.20 0.00 0.000000 Till Pasture 1.79 0.00 0.000000 Till Grass 0.00 0.00 0.000000 Outwash Forest 0.00 0.00 0.000000 Outwash Pasture 0.00 0.00 0.000000 Outwash Grass 0.00 0.00 0.000000 wetland 4.03 0.00 0.000000 Impervious devl5.tsf T 1.00000 F (T Enter the Analysis TOOLS Module rrPi Compute PEAKS and Flow Frequencies devl5.tsf dev15.pks to Previous Menu NRETURN exit KCRTS Program • • S1 a" Ck)"—r� �— c S . 14 Flow Frequency Analysis Time Series File:devl5.tsf Project Location:sea-Tac ---Annual Peak Flow Rates --- Flow Rate Rank Time of Peak (US) 1.92 6 8/27/01 18:00 1.48 8 1/05/02 15:00 4.79 Z 12/08/02 17:15 1.55 7 8/23/04 14:30 2.33 5 11/17/04 5:00 2.39 4 10/27105 10:45 2.69 3 10/25/06 22:45 6.95 1 1/09/08 6:30 computed Peaks - -Pt,r�d C,.-fC �,- 'SA - ZD90 Q z r Wcbo (1 �I2-) 31lei4 41 0 -----Flow Frequency Analysis ------- - - Peaks - - Rank Return Prob (CFS) Period 6.95 1 100.00 0.990 4.79 2 25.00 0.960 2.69 3 10.00 0.900 2.39 4 5.00 0.800 2.33 5 3.00 0.667 1.92 6 2.00 0.500 6r 1.55 7 1.30 0.231 1.48 8 1.10 0.091 6.23 50.00 0.980 • • EC Pond Calculations Project: Wehrman Plat Date: 6-Oct-08 Q2 = 1.92 cfs Q10 = 2.69 cfs Qioo = 6.95 cfs Determine Pond Geometry SA = 2080*Q2 SA = 3,994 sf Size Discharge Mechanisms (from KCRTS flow frequency analysis) (from KCRTS flow frequency analysis) (from KCRTS flow frequency analysis) - Principal Spillway Must be at least 10" diameter to pass Q10 @ T head(from KCSWDM Fig 5.3.4.H) => If permanent control structure is used for EC, then riser must be at least 10" - Emergency Overflow Spillway - iterative solution below L=((Q100/3.21 *HA(3/2))-(2.4*H) H L 0.2 23.7 0.3 12.5 0.4 7.6 0.5 4.9 0.6 3.2 0.7 2.0 0.8 1.1 6' minimum length is req'd - Dewaterina Orifice Ao=4.81 *(10-6)*Ao*sgrt(h) AO = 0.01 sf D=13.54*sq rt(Ao) D = 1.68 in Drainage Calcs MW.xls EC Calcs 1016f2008 • C, E SECTION 5.3 DETENTION FACILITIES Riser Overflow The nomograph in Figure 5.3 AH may be used to determine the head (in feet) above a riser of given diameter and for a given flow (usually the I00-year peak flow for developed conditions). 100 FIGURE 5.3.4.H RISER INFLOW CURVES p IF ZMAM/A NNEW osim P, milli 0 PA 0111 DA HEAD IN FEET (measured from crest of riser) 10 Qwo,r=9.739 DH" Q o,n,e— =3.782 D214112 Q in cfs, D and H in feet Slope change occurs at weir -orifice transition I /24/2005 5-49 2005 Surface Water Design Manual • APPENDIX C-4 CONVEYANCE FACILITIES DESIGN (pending) • • I� U APPENDIX D MAINTENANCE REQUIREMENTS FOR PRIVATELY MAINTAINED DRAINAGE FACILITIES 17A 0 0 MAINTENANCE AND OPERATIONS MANUAL FOR PRIVATELY MAINTAINED DRAINAGE FACILITIES ADDRESS: 122nd Avenue SE between SE 1881h Street and SE 192"d Street Renton, Washington RETENTIONIDETENTION FACILITIES The purpose of the detention pond is to reduce the rate of runoff from the developed portions of the property. Water can flow freely into the pond, but orifices in the outflow riser restrict the outflow. When the inflow exceeds the capacity of the orifice, the excess water is "stored" in the pond, and released slowly after the storm abates. In order to function properly, the facility must also be kept free of accumulated sediment. The outlet and connection pipes also must be kept clean, as even a partial blockage could significantly impact the ability of the facility to store runoff. The facility should be visually inspected for sediment accumulation and blockages at least once each year and also after every major storm greater than or equal to a 10-year return frequency. WATER QUALITY TREATMENT FACILITIES The purpose of the permanently wet portions of the pond is to reduce the level of contaminants in the runoff water, through sedimentation and filtration, though the plants in the wetpond will also reduce pollutants though bic-uptake. It is essential that the water quality pond have calm conditions and be inspected regularly for accumulation of sediment. The pond should be 18 visually inspected for sediment accumulation and blockages at least once each year and also after every major storm greater than or equal to a I0-year return frequency_ CONVEYANCE SYSTEMS Pipes transport runoff from one place to another, in this case from catch basins to the pond, then to the downstream drainage system. To work properly, pipes must be kept free of silt and other debris. If pipes become blocked, surface flooding will usually occur. CATCH BASINS AND AREA DRAINS Catch basins collect surface drainage and direct it into storm conveyance pipes. They help prevent downstream drainage problems by trapping sediment and other debris that would otherwise flow downstream with the runoff. It is important to keep catch basins clean so accumulated silt is not flushed out during a significant storm. Also, if the outflow pipe becomes blocked with debris, surface flooding will usually occur. All catch basins should be inspected at least once each year and after major storms. Area drains convey runoff directly into conveyance pipes. To prevent surface flooding, their surface grates must be kept free of litter and debris. If dirt or other sediment gets into the pipes and they become blocked, the pipes will need to be cleaned, either manually or using a Vactor truck. The following tables identify maintenance issues, which should be addressed regularly, describing possible problems with the drainage system and their respective solutions. 0 Iis- • :7 • APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES NO. 1 - DETENTION PONDS Maintenance Defect or Problem Conditions When Maintenance Is Needed Results Expected When Component Maintenance Is Performed Site Trash and debris Any trash and debris which exceed t cubic foot Trash and debris cleared from site. per 1,000 square feet (this is about equal to the amount of trash it would take to fill up one standard size office garbage can). In general, there should be no visual evidence of dumping. Noxious weeds Any noxious or nuisance vegetation which may Noxious and nuisance vegetation constitute a hazard to County personnel or the removed according to applicable public. regulations. No danger of noxious vegetation where County personnel or the public might normally be. Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of pollution as oil, gasoline, concrete slurries or paint, according to applicable regulations. Source control BMPs implemented if appropriate. No contaminants present other than a surface oil film. Grass/groundcover Grass or groundcover exceeds 18 inches in Grass or groundcover mowed to a height. height no greater than 6 inches. Top or Side Slopes Rodent holes Any evidence of rodent holes if facility is acting Rodents removed or destroyed and of Dam, Berm or as a dam or berm, or any evidence of water dam or berm repaired. Embankment piping through dam or berm via rodent holes. Tree growth Tree growth threatens integrity of slopes, does Trees do not hinder facility not allow maintenance access, or interferes with performance or maintenance maintenance activity. !f trees are not a threat or activities. not interfering with access or maintenance, they do not need to be removed. Erosion Eroded damage over 2 inches deep where cause Slopes stabilized using appropriate of damage is still present or where there is erosion control measures. If erosion potential for continued erosion. Any erosion is occurring on compacted slope, a observed on a compacted slope. licensed civil engineer should be consulted to resolve source of erosion. Settlement Any part of a dam, berm or embankment that has Top or side slope restored to design settled 4 inches lower than the design elevation. dimensions. If settlement is significant, a licensed civil engineer should be consulted to determine the cause of the settlement. Storage Area Sediment Accumulated sediment that exceeds t 0% of the Sediment cleaned out to designed accumulation designed pond depth. pond shape and depth; pond reseeded if necessary to control erosion. Liner damaged Liner is visible or pond does not hold water as Liner repaired or replaced. (If Applicable) designed. Inlet/Outlet Pipe. Sediment Sediment filling 20% or more of the pipe. Inlet/outlet pipes clear of sediment. accumulation Trash and debris Trash and debris accumulated in inlet/outlet No trash or debris In pipes. pipes (includes floatables and non-floatables). Damaged Cracks wider than at the joint of the No cracks more than'/ -inch wide at inleUoutlef pipes or any evidence of soil entering the joint of the inlet outlet pipe. at the joints of the inlet/outlet pipes. Emergency Tree growth Tree growth impedes flow or threatens stability of Trees removed. Overflow/Spillway spillway. Rock missing Only one layer of rock exists above native soil in Spillway restored to design area five square feet or larger or any exposure of standards. native soil on the spillway. 1/9/2009 A-2 2009 Surface Water Design Manual —Appendix A APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES 11.5 • • • NO.4 - CONTROL STRUCTUREIFLOW RESTRICTOR Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When Component Maintenance is Performed Structure Trash and debris Trash or debris of more than % cubic foot which No Trash or debris blocking or is located immediately in front of the structure potentially blocking entrance to opening or is blocking capacity of the structure by structure. more than 10%. Trash or debris in the structure that exceeds'!, No trash or debris in the structure. the depth from the bottom of basin to invert the lowest pipe into or out of the basin. Deposits of garbage exceeding 1 cubic foot in No condition present which would volume. attract or support the breeding of insects or rodents. Sediment Sediment exceeds 60°% of the depth from the Sump of structure contains no bottom of the structure to the invert of the lowest sediment. pipe into or out of the structure or the bottom of the FROP-T section or is within 6 inches of the invert of the lowest pipe into or out of the structure or the bottom of the FROP-T section, Damage to frame Corner of frame extends more than'/. inch past Frame is even with curb. and/or top slab curb face into the street (If applicable), Top slab has holes larger than 2 square inches or Top slab is free of holes and cracks. cracks wider than % inch. Frame not sitting flush on top slab, i.e., Frame is sitting flush on top slab. separation of more than % inch of the frame from the top slab. Cracks in walls or Cracks wider than % inch and longer than 3 feet, Structure is sealed and structurally bottom any evidence of soil particles entering structure sound. through cracks, or maintenance person judges that structure is unsound. Cracks wider than Y: inch and longer than I foot No cracks more than'4 inch wide at at the joint of any inletloutlet pipe or any evidence the joint of inletloutlei pipe. of soil particles entering structure through cracks. Settlementl Structure has settled more than t inch or has Basin replaced or repaired to design misalignment rotated more than 2 inches out of alignment. standards Damaged pipe joints Cracks wider than 1/2-Inch at the joint of the inletloutlet pipes or any evidence of soil entering No cracks more than '!. -inch wide at the joint of inletloutlet pipes. the structure at the joint of the inletloutlet pipes. Contaminants and pollution Any evidence of contaminants or pollution such as oil, gasoline, concrete slurries or paint. Materials removed and disposed of according to applicable regulations. Source control BMPs implemented if appropriate. No contaminants present other than a surface oil film. Ladder rungs missing or unsafe Ladder is unsafe due to missing rungs, misalignment, rust, cracks, or sharp edges. Ladder meets design standards and allows maintenance person safe access. FROP-T Section Damage T section is not securely attached to structure T section securely attached to wall wall and outlet pipe structure should support at and outlet pipe. least 1,000 Ibs of up or down pressure. Structure is not in upright position (allow up to Structure in correct position. 10% from plumb). Connections to outlet pipe are not watertight or Connections to outlet pipe are water show signs of deteriorated grout. tight; structure repaired or replaced and works as designed. Any holes —other than designed holes --in the Structure has no holes other than structure. designed holes. Cleanout Gate Damaged or missing Cleanout gate is missing. Replace ceanout gate, 2009 Surface Water Design Manual — Appendix A A-7 U912009 4/15 1� u 0 APPENDIX A MAINTENANCE. REQUIREMENTS FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES NO.4 - CONTROL STRUCTUREIFLOW RESTRICTOR Maintenance Defect or Problem Condition When Maintenance Is Needed Results Expected When Component Maintenance is Performed Cleanout gate is not watertight. Gate is watertight and works as designed. Gate cannot be moved up and down by one Gate moves up and down easily and maintenance person. is watertight. Chainlrod leading to gate is missing or damaged. Chain is in place and works as designed, Orifice Plate Damaged or missing Control device is not working properly due to Plate is in place and works as missing, out of place, or bent orifice plate. designed. Obstructions Any trash, debris, sediment, or vegetation Plate is free of all obstructions and blocking the plate. works as designed. Overflow Pipe Obstructions Any trash or debris blocking (or having the Pipe is free of all obstructions and potential of blocking) the overflow pipe. works as designed. Deformed or damaged Lip of overflow pipe is bent or deformed. Overflow pipe does not allow lip overflow at an elevation lower than design Inlet/Outlet Pipe Sediment Sediment filling 20% or more of the pipe. Inlet/outlet pipes clear of sediment. accumulation Trash and debris Trash and debris accumulated in inletloutlet No trash or debris in pipes. pipes (includes f oatables and non-floatables). Damaged Cracks wider than Y3•inch at the joint of the No cracks more than %-inch wide at inlelYoutlet pipes or any evidence of soil entering the joint of the Inletloutlet pipe. at the joints of the inlet/outlet pipes. Metal Grates Unsafe grate opening Grate with opening wider than'/a inch. Grate opening meets design (If Applicable) standards. Trash and debris Trash and debris that is blocking more than 20% Grate free of trash and debris. of grate surface. footnote to guidelines for disposal Damaged or missing Grate missing or broken member(s) of the grate. Grate is in place and meets design standards. Manhole CoverlLid Coverllid not in place Cover/lid is missing or only partially in place. Cover/lid protects opening to Any open structure requires urgent structure. maintenance. Locking mechanism Mechanism cannot be opened by one Mechanism opens with proper tools. Not Working maintenance person with proper tools. Bolts cannot be seated. Self-locking cover/lid does not work. Coverllid difficult to One maintenance person cannot remove Coverllid can be removed and Remove coverllid after applying 80 lbs. of lift. reinstalled by one maintenance person. 1/9/2009 A-8 2009 Surface Water Design Manual — Appendix A is r� • APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES NO, 5 - CATCH BASINS AND MANHOLES Maintenance Defect or Problem Condition When Maintenance Is Needed Results Expected When Component Maintenance is Performed Structure Sediment Sediment exceeds 6D% of the depth from the Sump of catch basin contains no bottom of the catch basin to the invert of the sediment. lowest pipe into or out of the catch basin or is within 6 inches of the invert of the lowest pipe into or out of the catch basin. Trash and debris Trash or debris of more than'/: cubic foot which No Trash or debris blocking or is located immediately in front of the catch basin potentially blocking entrance to opening or is blocking capacity of the catch basin catch basin. by more than 10%. Trash or debris in the catch basin that exceeds No trash or debris in the catch basin. 113 the depth from the bottom of basin to invert the lowest pipe into or out of the basin. Dead animals or vegetation that could generate No dead animals or vegetation odors that could cause complaints or dangerous present within catch basin. gases (e.g., methane), Deposits of garbage exceeding 1 cubic foot in No condition present which would volume. attract or support the breeding of insects or rodents. Damage to frame Corner of frame extends more than'/. inch past Frame is even with curb. and/or top slab curb face into the street (If applicable). Top slab has holes larger than 2 square inches or Top slab is free of holes and cracks. cracks wider than Y. inch. Frame not silting flush on top slab, i.e., Frame is sitting flush on top slab. separation of more than 3/. inch of the frame from the top slab. Cracks in wails or Cracks wider than A inch and longer than 3 feet, Catch basin is sealed and bottom any evidence of soil particles entering catch structurally sound. basin through cracks, or maintenance person judges that catch basin is unsound. Cracks wider than % inch and longer than 1 foot No cracks more than'!. inch wide at at the joint of any in#etloutlet pipe or any evidence the joint of inlet/outlet pipe. of soil particles entering catch basin through cracks. Settlement/ Catch basin has settled more than 1 inch or has Basin replaced or repaired to design misalignment rotated more than 2 inches out of alignment. standards. Damaged pipe joints Cracks wider than at the joint of the No cracks more than V/-inch wide at inletloutlet pipes or any evidence of soil entering the joint of inletloutlet pipes. the catch basin at the joint of the inletloutlet pipes. Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of pollution as oil, gasoline, concrete slurries or paint. according to applicable regulations. Source control BMPs implemented if appropriate. No contaminants present other than a surface oil film. InletlOutlet Pipe Sediment Sediment filling 20% or more of the pipe. Inlet/outlet pipes Gear of sediment. accumulation Trash and debris Trash and debris accumulated in inleiloutlet No trash or debris in pipes. pipes (includes floatables and non-floatables). Damaged Cracks wider than'/riach at the joint of the No cracks more than'/. -inch wide at inlettoutlet pipes or any evidence of soif entering the joint of the inlet outlet pipe. at the joints of the inlet/outlet pipes. 2009 Surface Water Design Manual — Appendix A A-9 I /9 `2009 • • • APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES NO. 5 -- CATCH BASINS AND MANHOLES Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When Component Maintenance is Performed Metal Grates Unsafe grate opening Grate with opening wider than 716 inch. Grate opening meets design (Catch Basins) standards. Trash and debris Trash and debris that is blocking more than 20% Grate free of trash and debris. of grate surface. footnote to guidelines for disposal Damaged or missing Grate missing or broken member(s) of the grate, Grate is in place and meets design Any open structure requires urgent standards. maintenance. Manhole Cover/Lid Coverllid not in place Coverllid is missing or only partially in place. Coverllid protects opening to Any open structure requires urgent structure. maintenance. Locking mechanism Mechanism cannot be opened by one Mechanism opens with proper tools. Not Working maintenance person with proper tools. Baits cannot be seated. Self-locking covarllid does not work. Coverllid difficult to One maintenance person cannot remove Coverllid can be removed and Remove cover/lid after applying 80 lbs. of lift. reinstalled by one maintenance person. 119/2009 A-10 2009 Surface Water Design Manual — Appendix A • • • APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES NO, 6 - CONVEYANCE PIPES AND DITCHES Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When Component Maintenance is Performed Pipes Sediment & debris Accumulated sediment or debris that exceeds Water flaws freely through pipes. accumulation 20% of the diameter of the pipe. Vegetation/roots Vegetationtroots that reduce free movement of Water flows freely through pipes. water through pipes. Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of pollution as oil, gasoline, concrete slurries or paint. according to applicable regulations. Source control BMPs implemented if appropriate. No contaminants present other than a surface oil film. Damage to protective Protective coating is damaged; rust or corrosion Pipe repaired or replaced. coating or corrosion is weakening the structural integrity of any part of pipe. Damaged Any dent that decreases the cross section area of Pipe repaired or replaced. pipe by more than 20% or Is determined to have weakened structural integrity of the pipe. Ditches Trash and debris Trash and debris exceeds 1 cubic foot per 1,000 Trash and debris Geared from square feet of ditch and slopes, ditches. Sediment Accumulated sediment that exceeds 20% of the Ditch cleanedlflushed of all sediment accumulation design depth. and debris so that it matches design. Noxious weeds Any noxious or nuisance vegetation which may Noxious and nuisance vegetation constitute a hazard to County personnel or the removed according to applicable public. regulations. No danger of noxious vegetation where County personnel or the public might normally be. Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of pollution as oil, gasoline, concrete slurries or paint according to applicable regulations. Source control BMPs implemented if appropriate. No contaminants present other than a surface oil film. Vegetation Vegetation that reduces free movement of water Water flows freely through ditches. through ditches. Erosion damage to Any erosion observed on a ditch slope. Slopes are not eroding. slopes Rock lining out of One Payer or less of rock exists above native soil Replace rocks to design standards. place or missing (If area 5 square feet or more, any exposed native Applicable) soil. 2009 Surface Water Design Manual — Appendix A A-] ] ] /9/2009 �r S • • APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES NO.7 - DEBRIS BARRIERS (E.G., TRASH RACKS) Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When Component Maintenance is Performed. Site Trash and debris Trash or debris plugging more than 20% of the Barrier clear to receive capacity flow. area of the barrier. Sediment Sediment accumulation of greater than 20% of Barrier clear to receive capacity flow. accumulation the area of the barrier Structure Cracked broken or Structure which bars attached to is damaged - Structure barrier attached to is loose pipe is loose or cracked or concrete structure is sound. cracked, broken of loose. Bars Bar spacing Bar spacing exceeds 6 inches. Bars have at most 6 inche spacing. Damaged or missing Bars are bent out of shape more than 3 inches. Bars in place with no bends more bars than inch. Bars are missing or entire barrier missing. Bars in place according to design. Bars are loose and rust is causing 50% Repair or replace barrier to design deterioration to any part of barrier. standards. 1/9/2009 A-12 2009 Surface Water Design Manual —Appendix A U 1r u l� u APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES NO.8 -- ENERGY DISSIPATERS Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When Component Maintenance is Performed. Site Trash and debris Trash and/or debris accumulation. Dissipater clear of trash andlor debris Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of pollution as ofl, gasoline, concrete slurries or paint. according to applicable regulations. Source control BMPs implemented if appropriate. No contaminants present other than a surface oil film. Rock Pad Missing or moved Only one layer of rock exists above native soil in Rock pad prevents erosion. Rock area five square feet or larger or any exposure of native soil. Dispersion Trench Pipe plugged with Accumulated sediment that exceeds 20% of the Pipe cleanedlflushed so that it sediment design depth. matches design. Not discharging water Visual evidence of water discharging at Water discharges from feature by properly concentrated points along trench (normal sheet flow. conditlon is a "sheet flow" of water along trench). Perforations plugged. Over 114 of perforations in pipe are plugged with Perforations freely discharge flow, debris or sediment. Water flows out top of Water flows out of distributor catch basin during No flow discharges from distributor "distributor" catch any storm less than the design storm. catch basin. basin. Receiving area over- Water in receiving area is causing or has No danger of landslides. saturated potential of causing landslide problems. Gabions Damaged mesh Mesh of gabion broken, twisted or deformed so Mesh is intact, no rock miss}ng, structure Is weakened or rock may fall out. Corrosion Gabion mesh shows corrosion through more than A11 gabion mesh capable of % of its gage. containing rock and retaining designed form. Collapsed or Gabler basket shape deformed due to any Ali gabion baskets intact, structure deformed baskets cause. stands as designed. Missing rock Any rock missing that could cause gabion to No rock missing. loose structural integrity. Manhole/Chamber Worn or damaged Structure dissipating flow deteriorates to % or Structure fs in no danger of failing. post, baffles or side of original size or any concentrated worn spot chamber exceeding one square foot which would make structure unsound. Damage to wall. Cracks wider than 1/2-inch or any evidence of soil Manholelchamber is sealed and frame, bottom, and/or entering the structure through cracks, or structurally sound. top slab maintenance inspection personnel determines that the structure is not structurally sound. Damaged pipe joints Cracks wider than %-inch at the joint of the No soil or water enters and no water inletioutlet pipes or any evidence of soil entering discharges at the joint of inlet/outlet the structure at the joint of the inletloutlet pipes. pipes. 2009 Surface Water Design Manual — Appendix A A-13 1/9/2009 • 1� u • APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL., CONVEYANCE, AND WQ FACILITIES NO.9 - FENCING Maintenance befect or Problem Conditions When Maintenance Is Needed Results Expected When Component Maintenance is Performed site Erosion or holes Erosion or holes more than 4 inches high and 12- No access under the fence. under fence 18 Inches wide permitting access through an opening under a fence. Wood Posts, Boards Missing or damaged Missing or broken boards, post out of plumb by No gaps on fence due to missing or and Cross Members parts more than 6 inches or cross members broken broken boards, post plumb to within IM. inches, cross members sound. Weakened by rotting Any part showing structural deterioration due to All parts of fence are structurally or insects rotting or insect damage sound. Damaged or failed Concrete or metal attachments deteriorated or Post foundation capable of post foundation unable to support posts. supporting posts even in strong wind. Metal Posts, Raiis Damaged parts Post out of plumb more than 6 inches Post plumb to within 1'/, inches. and Fabric Top rails bent more than 6 inches. Top rail free of bends greater than 1 inch. Any part of fence (including post, top rails, and Fence is aligned and meets design fabric) more than 1 foot out of design alignment. standards. Missing or loose tension wire. Tension wire in place and hoUng fabric. Deteriorated paint or Part or parts that have a rusting or scaling Structurally adequate posts or parts protective coating condition that has affected structural adequacy. with a uniform protective coating. Openings in fabric Openings in fabric are such that an 8-inch Fabric mesh openings within 50% of diameter ball could fit through. I grid size. 1/9/2009 A-t4 2009 Surface Water Design Manual — Appendix A • • • APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES NO. 10 - GATES/BOLLARDSIACCESS BARRIERS Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When Component Maintenance is Performed Chain Link Fencing Damaged or missing Missing gate. Gates in place. Gate members Broken or missing hinges such that gate cannot Hinges intact and tubed. Gate is be easily opened and closed by a maintenance working freely. person. Gate is out of plumb more than 6 inches and Gate is aligned and vertical. more than t foot out of design alignment. Missing stretcher bar, stretcher bands, and ties. Stretcher bar, bands, and ties in place. Locking mechanism Locking device missing, no -functioning or does Locking mechanism prevents does not lack gate not link to ail parts. opening of gate. Openings in fabric Openings in fabric are such that an 8-inch Fabric mesh openings within 50% of diameter ball could fit through, grid sire. Bar Gate Damaged or missing Cross bar does not swing open or closed, is Cross bar swings fulty open and cross bar missing or is bent to where it does not prevent closed and prevents vehicle access. vehicle access. Locking mechanism Locking device missing, no -functioning or does Locking mechanism prevents does not lock gate not link to all parts. opening of gate. Support post Support post does not hold cross bar up. Cross bar held up preventing vehicle damaged access into facility. Bollards Damaged or missing Ballard broken, missing, does not fit into support No access for motorized vehicles to hole or hinge broken or missing, get into facility. Does not lock Locking assembly or lock missing or cannot be No access for motorized vehicles to attached to lock bollard in place. get into facility. Boulders Dislodged Boulders not located to prevent motorized vehicle No access for motorized vehicles to accessr get into facility. Circumvented Motorized vehicles going around or between No access for motorized vehicles to boulders, get into facility. 2009 Surface Water Design Manual — Appendix A A•15 1 /912009 • • • APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES NO. 11 -GROUNDS (LANDSCAPING) Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When Component Maintenance is Performed Site Trash or litter Any trash and debris which exceed 1 cubic foot Trash and debris cleared from site. per 1,000 square feet (this is about equal to the amount of trash it would take to fill up one standard size office garbage can). In general, there should be no visual evidence of dumping. Noxious weeds Any noxious or nuisance vegetation which may Noxious and nuisance vegetation constitute a hazard to County personnel or the removed according to applicable public. regulations. No danger of noxious vegetation where County personnel or the public might normally be. Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of pollution as oil, gasoline, concrete slurries or paint. according to applicable regulations. Source control BMPs implemented if appropriate. No contaminants present other than a surface oil film. Grass/groundcover Grass or groundcover exceeds 18 inches in Grass or groundcover mowed to a height. height no greater than 6 inches. Trees and Shrubs Hazard Any tree or limb of a tree identified as having a No hazard trees in facility. potential to fall and cause property damage or threaten human life. A hazard tree identified by a qualified arborist must be removed as soon as possible. Damaged Limbs or parts of trees or shrubs that are split or broken which affect more than 25% of the total Trees and shrubs with less than 5% of total foliage with split or broken foliage of the tree or shrub. limbs. Trees or shrubs that have been blown down or No blown down vegetation or knocked over. knocked over vegetation. Trees or shrubs free of injury. Trees or shrubs which are not adequately Tree or shrub in place and supported or are ieaning over, causing exposure adequately supported; dead or of the roots. diseased trees removed. t 1912009 A-I6 2009 Surface Water Design Manual — Appendix A I MS - • • • APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES NO. 12 - ACCESS ROADS Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When Component Maintenance Is Performod Site Trash and debris Trash and debris exceeds t cubic foot per 1,000 Roadway drivable by maintenance square feet (i.e., trash and debris would fill up vehicles. one standards size garbage can). Debris which could damage vehicle tires or Roadway drivable by maintenance prohibit use of road. vehicles. Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of pollution as oil, gasoline, concrete slurries or paint. according to applicable regulations. Source control BMPs implemented if appropriate. No contaminants present other than a surfaoe oil film. Blocked roadway Any obstruction which reduces clearance above Roadway overhead clear to 14 feet road surface to less than 14 feet. high. Any obstruction restricting the access to a 10- to At least 12-foot of width on access 12 foot width for a distance of more than 12 feet road. or any point restricting access to less than a 10 foot width. Road Surface Erosion, settlement, Any surface defect which hinders or prevents Road drivable by maintenance potholes, soft spots, maintenance access. vehicles. ruts Vegetation on road Trees or other vegetation prevent access to Maintenance vehicles can access surface facility by maintenance vehicles. facility. Shoulders and Erosion Erosion within 1 foot of the roadway more than 8 Shoulder free of erasion and Ditches inches wide and 6 inches deep. matching the surrounding road. Weeds and brush Weeds and brush exceed 18 inches in height or Weeds and brush cut to 2 inches in hinder maintenance access. height or cleared in such a way as to allow maintenance access. Modular Grid Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of Pavement pollution as oil, gasoline, concrete slurries or paint. according to applicable regulations. Source control BMPs implemented if appropriate. No contaminants present other than a surface oil film. Damaged or missing Access surface compacted because of broken on Access road surface restored so missing modular block. road infiltrates. 2009 Surface Water Design Manual — Appendix A A-17 11912009 E • APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES NO. 16 - WETPOND Maintenance Defect or Problem Condltion When Maintenance is Needed Results Expected When Component Maintenance Is Performed Site Trash and debris Any trash and debris accumulated on the Wetpond site free of any trash or wetpond site. debris. Noxious weeds Any noxious or nuisance vegetation which may Noxious and nuisance vegetation constitute a hazard to County personnel or the removed according to applicable public. regulations. No danger of noxious vegetation where County personnel or the public might normally be. Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of pollution as oil, gasoline, concrete slurries or paint according to applicable regulations, Source control BMPs implemented if appropriate. No contaminants present other than a surface oil film. Grass/ground cover Grass or groundcover exceeds 18 inches in Grass or groundcover mowed to a height. height nc greater than 6 inches. Side Slopes of Darn, Rodent holes Any evidence of rodent holes if facility is acting Rodents removed or destroyed and Berm, internal berm as a dam or berm, or any evidence of water dam or berm repaired. or Embankment plping through dam or berm via rodent holes. Tree growth Tree growth threatens integrity of dams, berms or Trees do not hinder facility slopes, does not allow maintenance access, or performance or maintenance interferes with maintenance activity. If trees are activities. not a threat to dam, berm or embankment integrity, are not interfering with access or maintenance or leaves do not cause a plugging problem they do not need to be removed. Erosion Eroded damage over 2 inches deep where cause Slopes stabilized using appropriate of damage is still present or where there is erosion control measures. If erosion potential for continued erosion. Any erosion is occurring on compacted slope, a observed on a compacted slope. licensed civil engineer should be consulted to resolve source of erosion. Top or Side Slopes Settlement Any part of a dam, berm or embankment that has Top or side slope restored to design of Dam, Berm, settled 4 inches lower than the design elevation. dimensions. if settlement is il berm or significant, a licensed civil engineer Embankment should be consulted to determine the cause of the settlement. irregular surface on Top of berm not uniform and level. Top of berm graded to design internal berm elevation. Pond Areas Sediment Accumulated sediment that exceeds 10% of the Sediment cleaned out to designed accumulation (except designed pond depth. pond shape and depth. first wetpool cell) Sediment Sediment accumulations in pond bottom that Sediment storage contains no accumulation (first exceeds the depth of sediment storage (1 foot) sediment. wetpoof cell) plus 6 inches. Liner damaged (if Liner is visible or pond does not hold water as Liner repaired or replaced. Applicable) designed Water level (first First cell empty, doesn't hold water. Water retained in first cell for most of , wetpool cell) the year. Algae mats (first Algae mats develop over more than 10% of the Algae mats removed (usually in the wetpool cell) water surface should be removed. late summer before Fall rains, especially in Sensitive Lake Protection Areas.) Gravity Drain Inoperable valve Valve will not open and close. Valve opens and closes normally. Valve won't seal Valve does not seal completely. Valve completely seals closed. Emergency Overflow Tree growth Tree growth impedes flow or threatens stability of Trees removed. Spillway spillway. 2009 Surface Water Design Manual —Appendix A A-21 1/9/2009 15/1s • 0 • APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL, CONVEYANCE, AND WQ FACILITIES NO. 16 - WETPOND Maintenance Defect or Problem Condition When Maintenance Is Needed Results Expected When Component Maintenance is YeHormad Rock missing Only one layer of rack exists above native soil in Spillway restored to design area five square feet or larger, or any exposure of standards. native soil at the top of out flow path of spillway. Rip -rap on inside slopes need not be replaced. InIetl00et Pipe Sediment Sediment filling 20% or more of the pipe. Inlot/outlet pipes dear of sediment. accumulation Trash and debris Trash and debris accumulated in inietloutlet No trash or debris in pipes. pipes (includes floatables and non-floatables). Damaged Cracks wider than' inch at the joint of the No cracks more than V.-inch wide at inletloutlet pipes or any evidence of soil entering the joint of the inletloutlet pipe. at the joints of the inlet/outlet pipes. 1 /9/2009 A-22 2009 Surface Water Design Manual _ Appendix A APPENDIX E BOND QUANTITIES WORKSHEETS (pending) �J • APPENDIX F RETENTION/DETENTION FACILITY SUMMARY SHEET & SKETCH L �J 1/� 0 KING COUNT', WASHINGTON, SURFACF WATER DESIGN MANUAL STORMWATER FACILITY SUMMARY SHEET DDES Permit Number (provide one Stormwater Facility Summary Sheet per Natural Discharge Location) Overview: cct Name Downstream Drainage Basins Major Basin Name Sba5 Immediate Basin Name f K Flow Control: Flow Control Facility Name/Number Co m6. Dck—r -A . f o-r d Facility Location S J5— Corr e!' 04 If none, Flow control provided in regional/shared facility (give location) No flow control required Exemption number General Facility Information: Type/Number of detention facilities: Type/Number of infiltration facilities: ponds ponds vaults tanks tanks trenches Control Structure Location _I Type of Control Structure N nI p ri Number of Orifices/Restrictions Size of Orifice/Restriction: No. 2 No. 3 No. 4 It No. 1 2110 3,wu Flow Control Performance Standard [',prl S .r,f 2009 Surface Water Design Manual 1/9/2009 I • • KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL Live Storage Volume �°j� (p2jDepth Volume Factor of Safety Number of Acres Served 15.2-15 Number of Lots 3n Dam Safety Regulations (Washington State Department of Ecology) Reservoir Volume above natural grade _ Depth of Reservoir above natural grade Facility Summary Sheet Sketch All detention, infiltration and water quality facilities must include a detailed sketch. 01 "x 17" reduced size plan sheets may be used) 2009 Surface Water Design Manual see raQ -any(xey"3 Ear, 2 1 /9/2009 31 q KING COUNTY, WASHING -:'ON, SURFACE Y ATER DFSIGN MANUAL Water Quality: Type/Number of water quality facilities/BMPs: biofiltration Swale (regular/wet/ or continuous inflow) large) combined detention/wetpond large) (wetpond portio basic r large) combined detention/wetvault filter strip flow dispersion farm management plan landscape management plan oil/water separator above (baffle or coalescing plate) Liner? catch basin inserts: Manufacturer pre -settling pond pre -settling structure: Manufacturer sand filter (basic or large) sand filter, linear (basic or sand filter vault (basic or sand bed depth (inches) stormwater wetland storm filter wetpond (basic or large) wetvault Is facility Lined? If so, what marker is used high flow bypass structure (e.g., flaw-splitter catch basin) source controls Design Information Water Quality design flow Water Quality treated volume (sandfilter) Water Quality storage volume (wetpool) 0 Facility Summary Sheet Sketch 2009 Surface Water Design Manual 3 1 /W2009 9/q �J �J KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL All detention, infiltration and water quality facilities must include a detailed sketch. (11"xI7" reduced size plan sheets may be used) rr — '�rtC� t n� .. S t� G��-C.a3 �+1 �Cc n � ! ✓l.� � �� ✓1 �1" 2009 Surface Water Design Manual 1/9/2009