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REVIEWED RESUB1 BLD2024-0134+Storm_Drainage_Report+5.14.2024_11.49.55_AM+4255826RESUB BLD2024-0134 May 14 2024 CITY OF EDMONDS DEVELOPMENT SERVICES 10429240 t" P i sw DEPARTMENT Single Family Residence 10429 240th PI SW Edmonds, WA 98020 BLD 2024-0134 Stormwater Site Plan Report Prepared for: Select Homes Date: January 30, 2024 Revised: May 13, 2024 go WASI l� d 36508W 0A� ��GISTER�'� i \j0NAL/ 5/13/2024 Prepared by: Rob Long, PE RAM Fnginininring, Inr, 19109 36'" Ave W, Suite 103, Lynnwood WA 98036 (425) 678-6960 RAMengineeringinc.com Job No. 23-035 10429 240th PI SW Single Family Residence Introduction: This summary report provides site design information for a single-family residence at 10429 240th PI SW. This report includes stormwater analysis to support permit review and approval. The property is located on the north side of 240t" PI SW in the Southwest 1/4 of Section 36, Township 27N, Range 3E, W.M. Site Address: Applicant: 10429 240th PI SW Select Homes Edmonds, WA 98020 8304 212th St SW Edmonds WA 98026 Tax Parcel Number: Contact: Kayla Clark Nichols 00564900100500 (425) 742-6044 TABLE OF CONTENTS SECTION PAGES A. Project Overview.............................................................................................................................. 5 B. Existing Conditions Summary........................................................................................................... 1 C. Developed Site Hydrology.............................................................................................................. 18 D. Soils Reports................................................................................................................................... 18 E. Construction SWPPPP Requirements................................................................................................ 2 F. Operation and Maintenance Guidelines............................................................................................ 8 RAMEngineering, Inc. RAM No. 23-035 10429 240th P1 SW SFR Stormwater Site Plan Report Page A. PROJECT OVERVIEW: This report provides engineering information for the proposed construction of a single family residence on a 0.263 acre parcel; the project is located on the north side of 2401h PI SW at 10429 2401h PI SW in the City of Edmonds. The applicant, Select Homes proposes to remove the existing residence to construct a new single family residence with an attached garage on the subject site. This report provides the evaluation for the new single family residential development. Summary of Minimum Requirements for Category 1 Project: Minimum Requirement #1 — Preparation of Stormwater Site Plan. The proposed site development consists of disturbing a majority of the 0.263 acres site while retaining the existing detached garage and pavement area (2,078 sf) off the back alley of site. The project will create/replace about 3,972 sf of hard surface area; thus, the project is classified as a Category 1 project per the City's classification system. Per ECDC 18.30, Category 1 projects must comply with Minimum Requirements No. 1 through No. 5. The civil site development plans and this report have been prepared to address the project's impacts. Minimum Requirement #2 — Construction Stormwater Pollution Prevention (SWPPP). A construction Stormwater Pollution Prevention Plan (SWPPP) has been incorporated into the site development plans. A summary of the site's erosion control measures that evaluates the typical 13 elements of a SWPPP are included in section E. The total site disturbance area (0.263 ac) of the project will not exceed one acre, thus a formal Notice of Intent application for NPDES coverage will not be made to the Department of Ecology. Minimum Requirement #3 —Source Control of Pollution. Specific source controls are not required for single family residential sites. General requirements for these sites include preventing the discharge of pollutants to the City's storm drainage system per Edmonds City Code Chapter 7.200 (Illicit Discharges). This includes common household items such as pesticides, herbicides, fertilizers, detergents and fluids from vehicle maintenance. Single family residences shall incorporate DOE's S411 BMPs for landscape and lawn vegetation management. Lawn and vegetation management can include control of objectionable weeds, insects, mold, bacteria, and other pests with pesticides. Examples include weed control on golf course lawns, access roads, and utility corridors and during landscaping; sap stain and insect control on lumber and logs; rooftop moss removal; killing nuisance rodents; fungicide application to patio decks, and residential lawn/plant care. It is possible to release toxic pesticides such as pentachlorophenol, carbamates, and organometallics to the environment by leaching and dripping from treated parts, container leaks, product misuse, and outside storage of pesticide contaminated materials and equipment. Poor management of the vegetation and poor application of pesticides or fertilizers can cause appreciable stormwater contamination. RAMEngineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page A-1 Minimum Requirement #4 — Preservation of Natural Drainage Systems and Outfalls. Most of the site slopes in a southerly direction towards 2401h PI SW, however the back detached garage and pavement area flows northerly towards the adjacent alley. The local underlying soils in the area consist of outwash sands and stormwater runoff disperses and infiltrates into the soils; due to the local well -draining soils, there are no existing stormwater pipe and catch basin systems in 240th PI SW or the adjacent alley to the north. Most hard surfaces in the area dissipate and infiltrate stormwater runoff. Additionally, there are no public stormwater pipe and catch -basin system in most of the surrounding roads. The % mile downstream path (gravity flow path) for runoff if it was not infiltrated generally flows in a south/southwest direction towards King County/City of Shoreline within the Storm Creek basin. See the Downstream Drainage Facility Map provided in Section C below. The site development will utilize the well -draining on -site soils and use an infiltration system onsite to manage stormwater runoff. Runoff flows from the new hard surfaces of the site will be collected and infiltrated in an onsite infiltration system. The infiltration system will have an overflow system that will be directed to 240th PI SW. The site is located within the upper reach of the Southwest Edmonds A watershed basin per the City of Edmonds maps (see section C). Minimum Requirement #5 — Onsite Stormwater Management. The proposed project is a category 1 project, thus is subject to the City's on -site stormwater management BMPs found in "List No. 1" in the City's code. A site -specific geotechnical evaluation of the site's soil demonstrates that infiltration is a viable option for stormwater management onsite. Therefore, the project will install an infiltration system that will fully mitigate (100% infiltration) the new and replace hard surface together with 25% of the existing hard surface to remain onsite. See the full stormwater design included in Section C below; a summary table of the project Stormwater Management BMPs are provided below. RAMEngineering, Inc. RAM No. 23-035 10429 240th P1 SW SFR Stormwater Site Plan Report Page A-2 MR#5 Stormwater Management BMP List No. 1 Evaluation Lawn and landscaped areas: BMP Viable Limitations / Infeasibility Criteria BMP T5.13: Post -Construction Soil Quality and Depth Yes BMP T5.13 shall be applied to the site post construction. (Volume V, Chapter 11) Roofs: BMP T5.30: Full Dispersion Infeasibility: A viable vegetated flow path 50 or 100 feet and (Volume V, Chapter 3) No less than 20% is not achievable onsite. BMP T5.10A: Downspout Full Infiltration Systems The project will install an infiltration system that will fully (Volume V, Chapter 4) Yes mitigate (100% infiltration) the new and replace hard surface together with 25% of the existing hard surface to remain onsite BMP T5.14 Rain Gardens However, the project will install an infiltration system that will (Volume V, Chapter 11) or fully mitigate (100% infiltration) the new and replace hard BMP T7.30: Bioretention Yes surface together with 25% of the existing hard surface to (Volume V, Chapter 7) remain onsite BMP T5.1013: Downspout Dispersion Systems Infeasibility: A viable vegetated flow path 50 or 100 feet and (Volume V, Chapter 4) No less than 20% is not achievable onsite. However, the project will install an infiltration system that will Detention Vaults or Pipes fully mitigate (100% infiltration) the new and replace hard (Edmonds Stormwater Addendum) Yes surface together with 25% of the existing hard surface to remain onsite However, the project will install an infiltration system that will BMP T5.10C: Perforated Stub -out fully mitigate (100% infiltration) the new and replace hard (Volume V, Chapter 4) Yes surface together with 25% of the existing hard surface to remain onsite Other Hard Surfaces: BMP T5.30: Full Dispersion Infeasibility: A viable vegetated flow path 50 or 100 feet and (Volume V, Chapter 3) No less than 20% is not achievable onsite. BMP T5.10A: Full Infiltration The project will install an infiltration system that will fully (Volume V, Chapter 4) mitigate (100% infiltration) the new and replace hard surface BMP T5.15: Permeable Pavement Yes together with 25% of the existing hard surface to remain (Volume V, Chapter 5) onsite BMP T5.14 Rain Gardens However, the project will install an infiltration system that will (Volume V, Chapter 11) or fully mitigate (100% infiltration) the new and replace hard BMP T7.30: Bioretention Yes surface together with 25% of the existing hard surface to (Volume V, Chapter 7) remain onsite BMP T5.12: Sheet Flow Dispersion Infeasibility: A viable vegetated flow path 50 or 100 feet and (Volume V, Chapter 3) No less than 20% is not achievable onsite. However, the project will install an infiltration system that will Detention Vaults or Pipes fully mitigate (100% infiltration) the new and replace hard (Edmonds Stormwater Addendum) Yes surface together with 25% of the existing hard surface to remain onsite RAMEngineering, Inc. RAM No. 23-035 10429 240th P1 SW SFR Stormwater Site Plan Report Page A-3 Parcel (Vicinity) Map: SW 36 27 3 .a.....� ...xmm wrtxmnaneum.reemmrtx ... .. Centerline ------- Lot Block Section ----- City Limit Gov Lot Subtliv ROW — Quarter ---- Taz Acct .. _... 7 inch Major Water Other Lot ------- Vac ROW ---- 16th Easement ... ..: ........... 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I +7 tV «.«.q = c S 1+ �' 3 Z 16 T .. _.iF 23� 90 1 4 TRA sv S -m OsF N: ty = m 2 O 1 2. 34 48-_--sW--.._.. _.. _..--'z saoK Z, o�-' v:�n 84 32 S0 51 52 SA 565 57 59 ii 2 APOSTLES; rn1 -----a238TH-9T--'j 0 2 , - 1 4005 : ESTAT 91 \ 33 49 58 1 '%t n OFTHE J TR 993 0 92 4P� 31 21 20 1� 3 I 0 01 D O _—237TH----r PL -- TR 992 _.. --- 3 4 �i' 2 2 r 3 4 7 o. cry th 7 ' p T 0 9 8 4 T`_._ .. 2 01 02 �..» 3-022 < > 3 _ 5 7 > "-.2 11 fi 5 GARDEN OF THE 01 �0 4 3-024 p Q c Q 6 43 Q 30 pT 22 19 LAST SUPPER 02gbw.. 3 j...".".,�.�.„ N d 5 O N 46 45 44 0029 23 18 12 RESTLAWN MEMORIAL ARDENS (4527) ILA Q 2 £ 025 o q 5 o M 42 i" 4 ! z GARDEN OF PRAYER GARDEN OF THE ; y 1 3-023 a 41 a 24 17 13 TF13 D GOOD SHEPHERD 1R 0, - 2 Z 2 ' 11 12 1J 5-026 FIR F ,5- L I 0 3 14 19 ,oas 12 - 28_.. 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RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page A-4 Site Plan: 240TH STREET SW — — — - N 8806'41 W 70. DOW 47' It CONN�CAON IlE 32 .3t i I EX GARAGE -- TO REMAIN ;] FF 327.3t I� I I I i 1 , � I H K SCHROEDERS R� r OF FOREST GLEN \\ ------- LOT 6------- 10'--4' (3034) PVC F0077NG DRAIN CONNEC770M O 20X MIN g AT AG I I J I ° I n I I i c SDCO 2 IE 324.0t I INSTALL 1-1/2' PE (160 PSI) FROM WA7ER METER TO L — — ._HOUSE DETAILS _(TRACER — — INSTALL NEW MAILBOX WiR£ TO BE INSTALLED Wf7H I WATER LINE) ON EXIS77NG STAND (REMOVE DAMAGED I 13 -4" PVC O 2.00X— MAILBOX DESIGNATED 17'-6' PVG O 5.85X FOR 10429). INFIL iRA710N TRENCH 17(L)xIO'(K9x3(D) ? 1 SEE DETAILS SHT DT--42 I -- --- — INSTALL i' WATER METER PEEL OVWSD S7D DETAIL W-IA ¢ 1' PE (160 PSI) FROM WATER ® MAIN TO METER & 1-1/2' PE (160) FROM METER TO HOUSE (SEE DETAIL. ON SHEET DT-: 02) (TRACERWTRE TO BE _ ---SS --= SS }INSTALLED WITH WATER LINE) EX 8' SEWER --------------- iliLL�� T . I I sDC0 _ _ !; ti 17 ,1 lE 326.Ot I ` 10' MIN LENGTH F007TNG YWE I DRAINGEOTECHLL �- CH I RECOMMENDAIIONS) 4' PERF PVC IE_32&6 �I gram tie' f —�j IE 32'. t - 81 CovER� II J .. PATIOi I H--328--a PROPOSED HOUSE PLAN 3110 I I n FF 32&30 I --326 I - 1lESD i 74 SSCO r. DRIVEWAY �O�LC \\ I, �A i I_ I B I I BUILDING ENVELOPE (T-) -' 4n HIK SCHROEDERS REPLAT I I OF FOREST GLEN �Iill� I LOT l�----------- 61� of I I � I 'k-WS Q(7YP — — — — — — — — — — — — — — - 0 —DRY U77IJ77ES C CONSTRUCTION W77H1N THE TREE PR07EC77ON AREA. THE PRO CT ARBORIST SHALL BE CONSULTED AND SUPERWSE ALL WORK WITHIN THE RETAIN TREE CRITICAL ROOT ZONE/CANOPY. JEL DRAIN y 0' MAX '— POWER POLE W/STREET LIGHT ——-%-W --- SSMH RIM=324.88 INSTALL T SANITARY SEWERPERT CLEANOUT AT THE PROPERTY IE 8' Z(W))=316.58 If 8' PVC(E)=316.68 UNE PER OVWSD STD DETAIL S-3 (SEE DETAIL ON SHEET DT-02) \ —SS----� CB 1 TYPE I INSTALL CHANNEL DRAIN O RIM 325.50 TOP 325.0 W 6' if 322.70 (IN -NW) NOS PRO CHANNEL GRAIN _.. 6,IE 321.00 (OUT-W) OR APPROVED EQUAL 4' IE 323.00 (OUT—S) (SEE DETAIL SHT DT-02) 240TH PL SW ---I---------------- fXIS7iNG WATER METER TO B£ R£MOVE�. (EXISTING WATER METER SHALL BE RETAINED NEW METER IS INSTALLED.UNTIL HOSE SPIGOT & AM SHAL[� BE INSTALLED FOR USE DURING CONS7RUC77ON) I RAN Engineering, Inc. RAM No. 23-035 .Ot _ APPROX. LOCATION OF EXIST SEWER LATERAL CONTRACTOR TO VERIFY LOCA77ON PRIOR TO CON57RUC77ON. (SEE SIDE SEWER N07ES) I `INSTALL ASPHALT DRIVEWAY APPROACH PER CITY STD DWG NO:. TR-,W (SEE SHEET DT-01) `S WWCM & REMOVE EXISTNG PAVEMENT AS TOUIR£D. NEAT LINE CUT, CLEAN, HEAT AND 7'ASp�C ,EEXRISTTNG PAVEMENT EDGES W7HSEAL WflHH AAR4000 AND,,S4ND. SAWCUT -9iALL BE MINIMUM 1-FT INTE THE EXISTING EDGE OF PAVEMENT. 10429 240th PI SW SFR Stormwater Site Plan Report Page A-5 B. EXISTING CONDITIONS SUMMARY Existing Conditions. The total site consists of 11,455 sf (0.263 acres) and is currently occupied by an existing single-family residence and detached garage. The existing house caught on fire and is currently vacant. The site's existing detached garage is accessed via an alley along the north boundary of the subject site. The existing house is surrounded by grass lawn and landscape areas. The site is surrounded by single family residences to the east, west, and north; and 240th PI SW along the southern boundary (see aerial photo below). The site generally slopes in a southwesterly direction at a relatively flat to moderate slope with only 5 feet of drop across the site. No defined drainage courses are found on -site, and most of the stormwater runoff would sheet flow southwesterly to 240th PI SW along the southerly boundary of the site. However, the existing detached garage and access driveway to the alley do slope northwesterly towards the alley. No known stream or wetlands are located on or adjacent to the site. Additional discussion of the local drainage basin and downstream path is discussed in Section C of this report. Soils: In accordance with the project's site -specific geotechnical engineering evaluation by Earth Solutions NW, LLC the on -site soils consist of outwash sands and gravels deposits (Everett series soil). As outlined in the geotechnical evaluation, the native sand outwash soils exhibit good infiltration characteristics and can be utilized for on -site infiltration. The geotechnical evaluation performed a small-scale PIT test on -site and measured an initial infiltration rate of 35.4 in/hr and recommends a design rate of 11.1 in/hr. A full soil description is included in the project's site specific geotechnical engineering study by Earth Solutions NW, LLC (attached below). Aerial Photo (City of Edmonds —GIIS, 2022 photo) �h!•�'�►a�c �i1a�i� RAMEngineering, Inc. RAM No. 23-035 2,40 9 10429 240th PI SW SFR Stormwater Site Plan Report Page B-1 C. DEVELOPED SITE HYDROLOGY. Developed Conditions. The proposed project includes the replacement and construction of a single family residence with an attached garage, and associated driveway and utilities. The existing detached garage and access driveway off the alley will be retained. The proposed new construction will create and/or replace 3,972 sf of hard surface. Per ECDC 18.30.060.D.5.b, a minimum of 25% of existing hard surfaces that are not controlled by existing approved stormwater management facility shall provide on -site stormwater management BMPs. Thus, the project site development will install an infiltration system along the south (lower) portion of the site to mitigate the new and replaced hard surfaces (3,972 sf) and a portion of the existing hard surface to remain (existing roof garage = 628 sf). The proposed infiltration trench system has been sized to mitigate a total hard surface area of 4,600 sf (0.106 ac). The following is a summary of the projects hard surface areas: New and Replaced Hard Surfaces = 3,972 sf (0.092 ac) Roof Area = 2,662 sf Walkway/Patio Area = 70 sf Driveway Area = 1,240 sf Existing Hard Surfaces (existing detached garage) = 628 sf (0.014 ac) Total Existing Hard Surface to Remain = 2,078 sf (Existing Detached garage, walk and driveway) Percent Retrofit Stormwater Control = 30.2% (628 / 2,078) Total Hard Surface Mitigation Area = 4,600 sf (0.106 ac), 3,972 sf + 628 sf In accordance with the Edmonds City Code (18.30) Category 1 projects shall meet MR#5 (see discussion in Section A above) and provide on -site stormwater management. To meet these criteria, the proposed hard surfaces of the site shall implement BMPs from "List No. 1" or meet the LID performance standard. As discussed above in the MR#5 evaluation above in Section A, an on -site infiltration trench system will be utilized to manage (full 100% infiltration) the project's new/replaced hard surfaces and a minimum of 25% of existing retrofit hard surface to remain. BMP T5.13: Post -Construction Soil Quality and Depth will be applied to the disturbed pervious areas of the site development. The project proposes to implement full (100%) hard surface infiltration onsite. The on -site infiltration trench will be sized using the DOE 2012 Western Washington Hydrology Model (WWHM2012) continuous runoff model. To mitigate the 4,600 sf of project hard surface area, the project will install a trench 10 feet wide, 17 feet long and 3.0 feet deep; filled with 1%z" to 3" washed drain rock (35% voids). A site specific geotechnical evaluation was made to assess the use of infiltration onsite. The evaluation determined infiltration is feasible onsite and recommends a long-term infiltration design rate of 11.1 in/hr. The developed runoff rates and storage calculations were performed using the DOE 2012 Western Washington Hydrology Model (WWHM2012) continuous runoff model. The below calculations demonstrate that the trench will fully mitigate (100% infiltration) the increased hard surfaces, see WWHM2012 input/printout on the following pages. RAMEngineering, Inc. RAM No. 23-035 10429 240th P1 SW SFR Stormwater Site Plan Report Page C-1 WWHM2012 PROJECT REPORT Project Name: 23-035 SFR Infiltration Site Name: 10429 240th SFR Site Address: RAM 23-035 City : Edmonds Report Date: 1/29/2024 MGS Regoin Puget East Data Start 1901/10/1 Data End : 2058/09/30 DOT Data Number: 03 Version Date: 2021/08/18 Version : 4.2.18 Low Flow Threshold for POC 1 : 50 Percent of the 2 Year High Flow Threshold for POC 1: 50 year PREDEVELOPED LAND USE Name : Basin 1 Bypass: No Groundwater: No Pervious Land Use acre A B, Forest, Flat .106 Pervious Total 0.106 Impervious Land Use acre Impervious Total 0 Basin Total 0.106 Element Flows To: Surface Interflow IaIYY[!I VY2IIla4GIIIslam]9 Name : Basin 1 Bypass: No Groundwater: No Pervious Land Use acre Pervious Total 0 Impervious Land Use acre ROOF TOPS FLAT 0.076 DRIVEWAYS MOD 0.028 SIDEWALKS FLAT 0.002 Impervious Total 0.106 Basin Total 0.106 Groundwater Element Flows To: Surface Interflow Groundwater Gravel Trench Bed 1 Gravel Trench Bed 1 PAN Engineering, Inc. 10429 240th PI SW SFR RAM No. 23-035 Stormwater Site Plan Report Page C-2 Name : Gravel Trench Bed 1 Bottom Length: 17.00 ft. Bottom Width: 10.00 ft. Trench bottom slope 1: 0 To 1 Trench Left side slope 0: 0 To 1 Trench right side slope 2: 0 To 1 Material thickness of first layer: 3 Pour Space of material for first layer: 0.35 Material thickness of second layer: 0 Pour Space of material for second layer: 0 Material thickness of third layer: 0 Pour Space of material for third layer: 0 Infiltration On Infiltration rate: 11.1 Infiltration safety factor: 1 Total Volume Infiltrated (ac-ft.): 39.284 Total Volume Through Riser (ac-ft.): 0.001 Total Volume Through Facility (ac-ft.): 39.285 Percent Infiltrated: 100 Total Precip Applied to Facility: 0 Total Evap From Facility: 0 Discharge Structure Riser Height: 2.9 ft. Riser Diameter: 8 in. i ' Schematic ��� RAN Engineering, Inc. RAM No. 23-035 E3 Facility Name Gravel -Trench Bed 1 Outlet 1 Outlet 2 Outlet 3 Downstream Connection 10 110 0 Facility Type lGravel Trench/Bed r Precipitation Applied to Facility Quick Trench r Evaporation Applied to Facility Facility Dimension Diagram Facility Dimensions Trench Length (ft) 117 Trench Bottom Width (ft) 10 Effective Total Depth (ft) 0 Top and bottom slope (HN) 0 Left Side Slope (HN) 0 Right Side Slope (HN) 0 Material Layers for Trench/Bed Layer 1 Thickness (ft) 0 Layer 1 porosity (0-1) 0,35 Layer 2 Thickness (ft) 0 Layer 2 porosity (0-1) 0 Layer 3 Thickness (ft) 0 Layer 3 porosity (0.1) 0 Infiltration Yes Measured Infiltration Rate (in/hr) Reduction Factor (infilt'factor) Use Wetted Surface Area (sidewalls) Total Volume Infiltrated (ac-ft) Total Volume Through Riser (ac-ft) Size Infiltration Trench Target %: 100 -:I Outlet Structure Data I Riser Height (ft) 2.9 . _-' Riser Diameter (in) Riser Type Flat Notch Type Orifice Diameter Height Number (in) (ft) 1 Fo----H Fo----H 2 fo --t-! to -! 3 Fo----d Fo--- --ld Trench Volume at Riser Head (ac-ft) .004 11.1 ^-1 Show Trench 10pen Table NO -�-i Initial Stage (ft) 0 39.284 Total Volume Through Faa ity act 39.285 0.001 Percent Infiltrated 100 10429 240th PI SW SFR Stormwater Site Plan Report Page C-3 Element Flows To: Outlet 1 Outlet 2 Gravel Trench Bed Hydraulic Table Stage(feet) Area(ac.) Volume(ac-ft.) Discharge(cfs) 0.0000 0.003 0.000 0.000 0.000 0.0333 0.003 0.000 0.000 0.043 0.0667 0.003 0.000 0.000 0.043 0.1000 0.003 0.000 0.000 0.043 0.1333 0.003 0.000 0.000 0.043 0.1667 0.003 0.000 0.000 0.043 0.2000 0.003 0.000 0.000 0.043 0.2333 0.003 0.000 0.000 0.043 0.2667 0.003 0.000 0.000 0.043 0.3000 0.003 0.000 0.000 0.043 0.3333 0.003 0.000 0.000 0.043 0.3667 0.003 0.000 0.000 0.043 0.4000 0.003 0.000 0.000 0.043 0.4333 0.003 0.000 0.000 0.043 0.4667 0.003 0.000 0.000 0.043 0.5000 0.003 0.000 0.000 0.043 0.5333 0.003 0.000 0.000 0.043 0.5667 0.003 0.000 0.000 0.043 0.6000 0.003 0.000 0.000 0.043 0.6333 0.003 0.000 0.000 0.043 0.6667 0.003 0.000 0.000 0.043 0.7000 0.003 0.001 0.000 0.043 0.7333 0.003 0.001 0.000 0.043 0.7667 0.003 0.001 0.000 0.043 0.8000 0.003 0.001 0.000 0.043 0.8333 0.003 0.001 0.000 0.043 0.8667 0.003 0.001 0.000 0.043 0.9000 0.003 0.001 0.000 0.043 0.9333 0.003 0.001 0.000 0.043 0.9667 0.003 0.001 0.000 0.043 1.0000 0.003 0.001 0.000 0.043 1.0333 0.003 0.001 0.000 0.043 1.0667 0.003 0.001 0.000 0.043 1.1000 0.003 0.001 0.000 0.043 1.1333 0.003 0.001 0.000 0.043 1.1667 0.003 0.001 0.000 0.043 1.2000 0.003 0.001 0.000 0.043 1.2333 0.003 0.001 0.000 0.043 1.2667 0.003 0.001 0.000 0.043 1.3000 0.003 0.001 0.000 0.043 1.3333 0.003 0.001 0.000 0.043 1.3667 0.003 0.001 0.000 0.043 1.4000 0.003 0.001 0.000 0.043 1.4333 0.003 0.002 0.000 0.043 1.4667 0.003 0.002 0.000 0.043 1.5000 0.003 0.002 0.000 0.043 1.5333 0.003 0.002 0.000 0.043 1.5667 0.003 0.002 0.000 0.043 1.6000 0.003 0.002 0.000 0.043 1.6333 0.003 0.002 0.000 0.043 1.6667 0.003 0.002 0.000 0.043 1.7000 0.003 0.002 0.000 0.043 1.7333 0.003 0.002 0.000 0.043 1.7667 0.003 0.002 0.000 0.043 1.8000 0.003 0.002 0.000 0.043 1.8333 0.003 0.002 0.000 0.043 1.8667 0.003 0.002 0.000 0.043 1.9000 0.003 0.002 0.000 0.043 1.9333 0.003 0.002 0.000 0.043 1.9667 0.003 0.002 0.000 0.043 2.0000 0.003 0.002 0.000 0.043 2.0333 0.003 0.002 0.000 0.043 RAN Engineering, Inc. RAM No. 23-035 Infilt(cfs) 10429 240th PI SW SFR Stormwater Site Plan Report Page C-4 2.0667 0.003 0.002 0.000 0.043 2.1000 0.003 0.002 0.000 0.043 2.1333 0.003 0.002 0.000 0.043 2.1667 0.003 0.003 0.000 0.043 2.2000 0.003 0.003 0.000 0.043 2.2333 0.003 0.003 0.000 0.043 2.2667 0.003 0.003 0.000 0.043 2.3000 0.003 0.003 0.000 0.043 2.3333 0.003 0.003 0.000 0.043 2.3667 0.003 0.003 0.000 0.043 2.4000 0.003 0.003 0.000 0.043 2.4333 0.003 0.003 0.000 0.043 2.4667 0.003 0.003 0.000 0.043 2.5000 0.003 0.003 0.000 0.043 2.5333 0.003 0.003 0.000 0.043 2.5667 0.003 0.003 0.000 0.043 2.6000 0.003 0.003 0.000 0.043 2.6333 0.003 0.003 0.000 0.043 2.6667 0.003 0.003 0.000 0.043 2.7000 0.003 0.003 0.000 0.043 2.7333 0.003 0.003 0.000 0.043 2.7667 0.003 0.003 0.000 0.043 2.8000 0.003 0.003 0.000 0.043 2.8333 0.003 0.003 0.000 0.043 2.8667 0.003 0.003 0.000 0.043 2.9000 0.003 0.004 0.000 0.043 2.9333 0.003 0.004 0.043 0.043 2.9667 0.003 0.004 0.121 0.043 3.0000 0.003 0.004 0.219 0.043 RAN Engineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page C-5 ANALYSIS RESULTS Stream Protection Duration Predeveloped Landuse Totals for POC #1 Total Pervious Area:0.106 Total Impervious Area:O Mitigated Landuse Totals for POC #1 Total Pervious Area:O Total Impervious Area:0.106 Flow Frequency Return Periods for Predeveloped. POC #1 Return Period Flow(cfs) 2 year 0.000053 5 year 0.00007 10 year 0.00008 25 year 0.000084 50 year 0.000084 100 year 0.000085 Flow Frequency Return Periods for Mitigated Return Period Flow(cfs) 2 year 0 5 year 0 10 year 0 25 year 0 50 year 0 100 year 0 ® Analysis ® .0 I-, - Cumulative Probability POC #1 1.0 0.1 xxxxx x x x -x - 0.1 x x x xxxxxxwoorak° 001 + 50' 0 001 x 70' LL 0.0001 0.5 1 2 5 10 20 30 50 70 80 90 95 98 160 Stream Protection Duration LID Duration Flow Frequency Water Quality Hydrograph Welland Input Volumes I LID Report Recharge Duration Recharge Predeveloped I Recharge Mitigated Analyze datasets Compact WDM Delete Selected I r Monthly FF 501 POC 1 Redeveloped flow r 0 s• 1000 Gravel Trench Bed 1 ALL OUTLETS Mitigated 1001 Gravel Trench Bed 1 OUTLET 1 Mitigated 1002 Gravel Trench Bed 1 OUTLET 2 Mitigated All Datasets Flow Stage Precip Evap POC 1 Flood Frequency Method (" Log Pearson Type III 17B Weibull Cunnane (: Gringorten RAN Engineering, Inc. RAM No. 23-035 9 Flow Frequency Flow(cfs) 0501 15m 0701 15m 0801 15m 2 Year = 0.0001 0.0316 0.0000 5 Year = 0.0001 0.0431 0.0000 10 Year = 0.0001 0.0514 0.0000 25 Year = 0.0001 0.0645 0.0000 50 Year = 0.0001 0.0766 0.0000 100 Year = 0.0001 0.0938 0.0000 Annual Peaks 1902 0.0000 0.0379 0.0000 1903 0.0000 0.0413 0.0000 1904 0.0001 0.0451 0.0000 1905 0.0000 0.0228 0.0000 1906 0.0000 0.0250 0.0000 1907 0.0001 0.0296 0.0000 1908 0.0001 0.0268 0.0000 1909 0.0001 0.0344 0.0000 1910 0.0001 0.0294 0.0000 1911 0.0001 0.0357 0.0000 1912 0.0001 0.0586 0.0000 1913 0.0000 0.0241 0.0000 1914 0.0001 0.0941 0.0000 1915 0.0000 0.0212 0.0000 1916 0.0001 0.0408 0.0000 1917 0.0000 0.0196 0.0000 1918 0.0000 0.0320 0.0000 1919 0.0000 0.0193 0.0000 1920 0.0001 0.0276 0.0000 1921 0.0000 0.0211 0.0000 1922 0.0001 0.0314 0.0000 1923 0.0001 0.0268 0.0000 1924 0.0000 0.0451 0.0000 1925 0.0000 0.0199 0.0000 1926 0.0001 0.0407 0.0000 1927 0.0001 0.0309 0.0000 1928 0.0000 0.0246 0.0000 1929 0.0001 0.0431 0.0000. 10429 240th PI SW SFR Stormwater Site Plan Report Page C-6 Stream Protection Duration Annual Peaks for Predeveloped and Mitigated Year Predeveloped Mitigated 1902 0.000 0.000 1903 0.000 0.000 1904 0.000 0.000 1905 0.000 0.000 1906 0.000 0.000 1907 0.000 0.000 1908 0.000 0.000 1909 0.000 0.000 1910 0.000 0.000 1911 0.000 0.000 1912 0.000 0.000 1913 0.000 0.000 1914 0.000 0.000 1915 0.000 0.000 1916 0.000 0.000 1917 0.000 0.000 1918 0.000 0.000 1919 0.000 0.000 1920 0.000 0.000 1921 0.000 0.000 1922 0.000 0.000 1923 0.000 0.000 1924 0.000 0.000 1925 0.000 0.000 1926 0.000 0.000 1927 0.000 0.000 1928 0.000 0.000 1929 0.000 0.000 1930 0.000 0.000 1931 0.000 0.000 1932 0.000 0.000 1933 0.000 0.000 1934 0.000 0.000 1935 0.000 0.000 1936 0.000 0.000 1937 0.000 0.000 1938 0.000 0.000 1939 0.000 0.000 1940 0.000 0.000 1941 0.000 0.000 1942 0.000 0.000 1943 0.000 0.000 1944 0.000 0.000 1945 0.000 0.000 1946 0.000 0.000 1947 0.000 0.000 1948 0.000 0.000 1949 0.000 0.000 1950 0.000 0.000 1951 0.000 0.000 1952 0.000 0.000 RAN Engineering, Inc. RAM No. 23-035 POC #1 10429 240th PI SW SFR Stormwater Site Plan Report Page C-7 1953 0.000 0.000 1954 0.000 0.000 1955 0.000 0.000 1956 0.000 0.000 1957 0.000 0.000 1958 0.000 0.000 1959 0.000 0.000 1960 0.000 0.000 1961 0.000 0.000 1962 0.000 0.000 1963 0.000 0.000 1964 0.000 0.000 1965 0.000 0.000 1966 0.000 0.000 1967 0.000 0.000 1968 0.000 0.000 1969 0.000 0.000 1970 0.000 0.000 1971 0.000 0.000 1972 0.000 0.013 1973 0.000 0.000 1974 0.000 0.000 1975 0.000 0.000 1976 0.000 0.000 1977 0.000 0.000 1978 0.000 0.000 1979 0.000 0.000 1980 0.000 0.000 1981 0.000 0.000 1982 0.000 0.000 1983 0.000 0.000 1984 0.000 0.000 1985 0.000 0.000 1986 0.000 0.000 1987 0.000 0.000 1988 0.000 0.000 1989 0.000 0.000 1990 0.000 0.000 1991 0.000 0.000 1992 0.000 0.000 1993 0.000 0.000 1994 0.000 0.000 1995 0.000 0.000 1996 0.000 0.000 1997 0.000 0.000 1998 0.000 0.000 1999 0.000 0.000 2000 0.000 0.000 2001 0.000 0.000 2002 0.000 0.000 2003 0.000 0.000 2004 0.000 0.000 2005 0.000 0.000 2006 0.000 0.000 RAM Engineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page C-8 2007 0.000 0.000 2008 0.000 0.000 2009 0.000 0.000 2010 0.000 0.000 2011 0.000 0.000 2012 0.000 0.000 2013 0.000 0.000 2014 0.000 0.000 2015 0.000 0.000 2016 0.000 0.000 2017 0.000 0.000 2018 0.000 0.000 2019 0.000 0.000 2020 0.000 0.000 2021 0.000 0.000 2022 0.000 0.000 2023 0.000 0.000 2024 0.000 0.000 2025 0.000 0.000 2026 0.000 0.000 2027 0.000 0.000 2028 0.000 0.000 2029 0.000 0.000 2030 0.000 0.000 2031 0.000 0.000 2032 0.000 0.000 2033 0.000 0.000 2034 0.000 0.000 2035 0.000 0.000 2036 0.000 0.000 2037 0.000 0.000 2038 0.000 0.000 2039 0.000 0.000 2040 0.000 0.000 2041 0.000 0.000 2042 0.000 0.000 2043 0.000 0.000 2044 0.000 0.000 2045 0.000 0.000 2046 0.000 0.000 2047 0.000 0.000 2048 0.000 0.000 2049 0.000 0.000 2050 0.000 0.000 2051 0.000 0.000 2052 0.000 0.000 2053 0.000 0.000 2054 0.000 0.000 2055 0.000 0.000 2056 0.000 0.000 2057 0.000 0.000 2058 0.000 0.000 RAM Engineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page C-9 Stream Protection Duration Ranked Annual Peaks for Predeveloped and Mitigated Rank Predeveloped Mitigated 1 0.0001 0.0130 2 0.0001 0.0000 3 0.0001 0.0000 4 0.0001 0.0000 5 0.0001 0.0000 6 0.0001 0.0000 7 0.0001 0.0000 8 0.0001 0.0000 9 0.0001 0.0000 10 0.0001 0.0000 11 0.0001 0.0000 12 0.0001 0.0000 13 0.0001 0.0000 14 0.0001 0.0000 15 0.0001 0.0000 16 0.0001 0.0000 17 0.0001 0.0000 18 0.0001 0.0000 19 0.0001 0.0000 20 0.0001 0.0000 21 0.0001 0.0000 22 0.0001 0.0000 23 0.0001 0.0000 24 0.0001 0.0000 25 0.0001 0.0000 26 0.0001 0.0000 27 0.0001 0.0000 28 0.0001 0.0000 29 0.0001 0.0000 30 0.0001 0.0000 31 0.0001 0.0000 32 0.0001 0.0000 33 0.0001 0.0000 34 0.0001 0.0000 35 0.0001 0.0000 36 0.0001 0.0000 37 0.0001 0.0000 38 0.0001 0.0000 39 0.0001 0.0000 40 0.0001 0.0000 41 0.0001 0.0000 42 0.0001 0.0000 43 0.0001 0.0000 44 0.0001 0.0000 45 0.0001 0.0000 46 0.0001 0.0000 47 0.0001 0.0000 48 0.0001 0.0000 49 0.0001 0.0000 50 0.0001 0.0000 51 0.0001 0.0000 RAN Engineering, Inc. RAM No. 23-035 POC #1 10429 240th PI SW SFR Stormwater Site Plan Report Page C-10 52 0.0001 0.0000 53 0.0001 0.0000 54 0.0001 0.0000 55 0.0001 0.0000 56 0.0001 0.0000 57 0.0001 0.0000 58 0.0001 0.0000 59 0.0001 0.0000 60 0.0001 0.0000 61 0.0001 0.0000 62 0.0001 0.0000 63 0.0001 0.0000 64 0.0001 0.0000 65 0.0001 0.0000 66 0.0001 0.0000 67 0.0001 0.0000 68 0.0001 0.0000 69 0.0001 0.0000 70 0.0001 0.0000 71 0.0001 0.0000 72 0.0001 0.0000 73 0.0001 0.0000 74 0.0001 0.0000 75 0.0001 0.0000 76 0.0001 0.0000 77 0.0001 0.0000 78 0.0001 0.0000 79 0.0001 0.0000 80 0.0001 0.0000 81 0.0001 0.0000 82 0.0001 0.0000 83 0.0001 0.0000 84 0.0001 0.0000 85 0.0001 0.0000 86 0.0001 0.0000 87 0.0001 0.0000 88 0.0001 0.0000 89 0.0001 0.0000 90 0.0000 0.0000 91 0.0000 0.0000 92 0.0000 0.0000 93 0.0000 0.0000 94 0.0000 0.0000 95 0.0000 0.0000 96 0.0000 0.0000 97 0.0000 0.0000 98 0.0000 0.0000 99 0.0000 0.0000 100 0.0000 0.0000 101 0.0000 0.0000 102 0.0000 0.0000 103 0.0000 0.0000 104 0.0000 0.0000 105 0.0000 0.0000 RAM Engineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page C-11 106 0.0000 0.0000 107 0.0000 0.0000 108 0.0000 0.0000 109 0.0000 0.0000 110 0.0000 0.0000 111 0.0000 0.0000 112 0.0000 0.0000 113 0.0000 0.0000 114 0.0000 0.0000 115 0.0000 0.0000 116 0.0000 0.0000 117 0.0000 0.0000 118 0.0000 0.0000 119 0.0000 0.0000 120 0.0000 0.0000 121 0.0000 0.0000 122 0.0000 0.0000 123 0.0000 0.0000 124 0.0000 0.0000 125 0.0000 0.0000 126 0.0000 0.0000 127 0.0000 0.0000 128 0.0000 0.0000 129 0.0000 0.0000 130 0.0000 0.0000 131 0.0000 0.0000 132 0.0000 0.0000 133 0.0000 0.0000 134 0.0000 0.0000 135 0.0000 0.0000 136 0.0000 0.0000 137 0.0000 0.0000 138 0.0000 0.0000 139 0.0000 0.0000 140 0.0000 0.0000 141 0.0000 0.0000 142 0.0000 0.0000 143 0.0000 0.0000 144 0.0000 0.0000 145 0.0000 0.0000 146 0.0000 0.0000 147 0.0000 0.0000 148 0.0000 0.0000 149 0.0000 0.0000 150 0.0000 0.0000 151 0.0000 0.0000 152 0.0000 0.0000 153 0.0000 0.0000 154 0.0000 0.0000 155 0.0000 0.0000 156 0.0000 0.0000 157 0.0000 0.0000 RAM Engineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page C-12 Stream Protection Duration POC #1 The Facility PASSED jW Analysis ijF w 0.00 0 v 0.00 O J 0.00 501 POC 1 Predeveloped 801 POC 1 Mitigated flow 0.00 r 6 1 10E-5 10E-4 10E-3 10E-2 10E-1 1 10 100 Percent Time Exceeding Stream Protection Duration LID Duration j Flow Frequency I Water Quality I Hydrograph f Welland Input Volumes I LID Report I Recharge Duration I Recharge Redeveloped I Recharge Mitigated Analyze datasets Compact WDM Delete Selected i F Monthly FF 501 POC 1 Predeveloped flow 801 POC 1 Mitigated flow All Datasets I Flow Stage _E!!S!Lj Evap POC 1 Flood Frequency Method (' Log Pearson Type III 17B C Weibull (- Cunnane 6 Gringotten The Facility PASSED. Flow(cfs) Predev Mit Percentage Pass/Fail 0.0000 4538 2 0 Pass 0.0000 4407 2 0 Pass 0.0000 4246 2 0 Pass 0.0000 4082 2 0 Pass 0.0000 3948 2 0 Pass 0.0000 3803 2 0 Pass 0.0000 3670 2 0 Pass 0.0000 3525 2 0 Pass 0.0000 3379 2 0 Pass 0.0000 3266 2 0 Pass 0.0000 3118 2 0 Pass 0.0000 2995 2 0 Pass 0.0000 2909 2 0 Pass 0.0000 2793 2 0 Pass 0.0000 2702 2 0 Pass 0.0000 2627 2 0 Pass 0.0000 2546 2 0 Pass 0.0000 2462 2 0 Pass 0.0000 2379 2 0 Pass 0.0000 2280 2 0 Pass 0.0000 2212 2 0 Pass 0.0000 2129 2 0 Pass 0.0000 2058 2 0 Pass RAN Engineering, Inc. RAM No. 23-035 F9 Facility PASSED I 'lov(cfs) Predev Mit Percentage Pass/Fail 1.0000 4538 2 0 Pass 1.0000 4407 2 0 Pass 1.0000 4246 2 0 Pass I.0000 4082 2 0 Pass I.0000 3948 2 0 Pass 1.0000 3803 2 0 Pass 1.0000 3670 2 0 Pass I.0000 3525 2 0 Pass 1.0000 3379 2 0 Pass 1.0000 3266 2 0 Pass 1.0000 3118 2 0 Pass 1.0000 2995 2 0 Pass I.0000 2909 2 0 Pass 1.0000 2793 2 0 Pass 1.0000 2702 2 0 Pass 1.0000 2627 2 0 Pass I.0000 2546 2 0 Pass 1.0000 2462 2 0 Pass 1.0000 2379 2 0 Pass 1.0000 2280 2 0 Pass 1.0000 2212 2 0 Pass 1.0000 2129 2 0 Pass 1.0000 2058 2 0 Pass I.0000 1983 2 0 Pass I.0000 1884 2 0 Pass 1.0000 1810 2 0 Pass 1.0000 1741 2 0 Pass 1.0000 1674 2 0 Pass 1.0000 1595 2 0 Pass 1.0000 1515 2 0 Pass I.0000 1424 2 0 Pass I.0000 1341 2 0 Pass 1.0000 1307 2 0 Pass 1.0000 1237 2 0 Pass , 10429 240th PI SW SFR Stormwater Site Plan Report Page C-13 0000 1983 2 0 Pass 0000 1884 2 0 Pass 0000 1810 2 0 Pass 0000 1741 2 0 Pass 0000 1674 2 0 Pass 0000 1595 2 0 Pass 0000 1515 2 0 Pass 0000 1424 2 0 Pass 0000 1341 2 0 Pass 0000 1307 2 0 Pass 0000 1237 2 0 Pass 0000 1187 2 0 Pass 0000 1151 2 0 Pass 0000 1099 2 0 Pass 0000 1068 2 0 Pass 0000 1017 2 0 Pass 0000 971 2 0 Pass 0000 939 2 0 Pass 0001 887 2 0 Pass 0001 867 2 0 Pass 0001 836 2 0 Pass 0001 816 2 0 Pass 0001 792 2 0 Pass 0001 765 2 0 Pass 0001 744 2 0 Pass 0001 719 2 0 Pass 0001 690 2 0 Pass 0001 634 2 0 Pass 0001 610 2 0 Pass 0001 591 2 0 Pass 0001 550 2 0 Pass 0001 505 2 0 Pass 0001 489 2 0 Pass 0001 481 2 0 Pass 0001 455 2 0 Pass 0001 435 2 0 Pass 0001 415 2 0 Pass 0001 399 2 0 Pass 0001 386 2 0 Pass 0001 364 2 0 Pass 0001 348 2 0 Pass 0001 333 2 0 Pass 0001 319 2 0 Pass 0001 310 2 0 Pass 0001 303 2 0 Pass 0001 295 2 0 Pass 0001 273 2 0 Pass 0001 258 2 0 Pass 0001 243 2 0 Pass 0001 240 2 0 Pass 0001 232 2 0 Pass 0001 225 2 0 Pass 0001 211 2 0 Pass 0001 189 2 1 Pass 0001 187 2 1 Pass 0001 185 2 1 Pass 0001 175 2 1 Pass 0001 163 2 1 Pass 0001 158 2 1 Pass 0001 137 2 1 Pass 0001 127 2 1 Pass 0001 124 2 1 Pass 0001 118 2 1 Pass 0001 113 2 1 Pass 0001 99 2 2 Pass 0001 96 2 2 Pass 0001 88 2 2 Pass 0001 78 2 2 Pass RAN Engineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page C-14 0.0001 73 2 2 Pass 0.0001 58 2 3 Pass 0.0001 54 2 3 Pass 0.0001 49 2 4 Pass 0.0001 47 2 4 Pass 0.0001 34 2 5 Pass 0.0001 30 2 6 Pass 0.0001 21 2 9 Pass 0.0001 10 2 20 Pass LID Report a - LID Report s POC TI :........... _.. LID Technique Usedfor Total Volume Volume Infiltration Cumulative Percent Water Quality Percent Comment Treatment? Needs Through Volume Volume Volume Water Quality Treatment Facility (ac-ft) Infiltration Infiltrated Treated (ac-ft) (ac-ft) Credit Gravel Trench Bed 1 POC ❑ 35.75 ❑ 100.00 Total Volume Infiltrated 35.75 0.00 0 OU 100.00 0.00 0% No Treat. Credit Compliance with LID Duration Standard 8% of 2-yr to 50% of Analysis 2-yr Result = Passed Perind and Impind Changes No changes have been made. This program and accompanying documentation are provided 'as -is' without warranty of any kind. The entire risk regarding the performance and results of this program is assumed by End User. Clear Creek Solutions Inc. and the governmental licensee or sublicensees disclaim all warranties, either expressed or implied, including but not limited to implied warranties of program and accompanying documentation. In no event shall Clear Creek Solutions Inc. be liable for any damages whatsoever (including without limitation to damages for loss of business profits, loss of business information, business interruption, and the like) arising out of the use of, or inability to use this program even if Clear Creek Solutions Inc. or their authorized representatives have been advised of the possibility of such damages. Software Copyright 0 by : Clear Creek Solutions, Inc. 2005-2024; All Rights Reserved. RAN Engineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page C-15 Additionally, all disturbed pervious (lawn and landscape) areas will preserve or restore the health and water - holding capacity of the soils by compost -amending (Per DOE BMP T5.13: Post -Construction Soil Quality and Depth). See attached City of Edmonds Standard Detail SD-642 criteria for BMP T5.13: Post -Construction Soil Quality and Depth. UNDISTURBED NATIVE VEGETATION UNDISTURBED NATIVE SOIL 2" ORGANIC MULCH 3" OF COMPOST INCORPORATED INTO 5" OF SITE SOIL (TOTAL AMENDED DEPTH OF 9.5 FOR A SETTLED DEPTH OF 8") SUBSOIL SCARIFIED 4" BELOW COMPOST AMENDED LAYER (12" BELOW SOIL SURFACE) 2" ORGANIC MULCH 6" IMPORTED TOPSOIL MIX (COMPACTED DEPTH) SUBSOIL IS SCARIFIED 6" BELOW IMPORTED TOPSOIL MIX UNDISTURBED PLANTS UNDISTURBED TURF (LAWN) (SEE NOTE 1) AREAS (SEE NOTE 1) PLANTING BEDS TURF (LAWN) AREAS 0" 8" UNDISTURBED TURF/LAWN/LANDSCAPE UNDISTURBED NATIVE SOIL STEEP SLOPE NOTE: AMENDED SOILS SHOULD NOT BE INSTALLED ON FINISHED SLOPES EXCEEDING 33%. AREAS EXCEEDING 337. SHALL BE STABILIZED PER THE ENGINEER/GEOTECH OF RECORD. ;RASS: SEED OR SOD .75" OF COMPOST INCORPORATED NTO 6.25" OF SITE SOIL (TOTAL 4MENDED DEPTH OF 9.5", FOR A SETTLED DEPTH OF 8") SUBSOIL SCARIFIED 4" BELOW ;OMPOST AMENDED LAYER ;12" BELOW SOIL SURFACE) OPTION 2 — AMEND IN PLACE OR STOCKPILE AND AMEND GENERAL NOTES: PLANTING BEDS TURF (LAWN) AREAS III�III�III�� GRASS: SEED OR SOD 11-III=111-III=III11 I 1I 1 11=1 I I —I 11 1I M I I I I I 111911-1I1=1IMINI -III=III=III=II�IIL�I 6" IMPORTED 1=1 I I-1 Ell III II—III-11 11 I 16 41M=1f�I 1=1 TOPSOIL MIX COMPACTED iEiTRI 1 I11111 1111 Ti > DEPTH) -P ;I_?v i SUBSOIL IS SCARIFIED 6" BELOW IMPORTED TOPSOIL MIX OPTION 3 — IMPORT TOPSOIL 1. AREAS OF NO DISTURBANCE SHALL BE FENCED AND EXISTING VEGETATION AND SOIL SHALL BE PROTECTED FROM CONSTRUCTION IMPACTS. 2. TO MEASURE SETTLED DEPTH, WATER SOIL SUFFICIENTLY TO FULLY SATURATE WITHOUT CAUSING EROSION. 3. COMPOST SHALL MEET SPEC. REQUIREMENTS IN THE 2017 EDMONDS STORMWATER ADDENDUM (CHECKLIST 7). 4. COMPACTION OF TOPSOIL (WHERE REQUIRED) TO BE TO 85% (MAX) OF THE MAXIMUM DRY DENSITY PER MODIFIED PROCTOR TEST (ASTM D1557). REVISION DATE CITY OF EDMONDS POST CONSTRUCTION SOIL APRIL 2021 QUALITY AND DEPTH PUBLIC WORKS STANDARD DEPARTMENT DETAIL 4's t 189�j APPROVED BY: R. ENGLISH S D — 6 42 RAMEngineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page C-16 Offsite Basin Analysis. The site is located in the Southwest Edmonds A watershed basin; the Southwest Edmonds A basin is a developed urban basin that primarily consists of single-family residences. The local area underlying soils consists of outwash sandy soils that are well -drained and create little to no stormwater runoff. Most hard surfaces in the area dissipate and infiltrate stormwater runoff. Additionally, there are no public stormwater pipe and catch -basin system in most of the surrounding roads. The % mile downstream path (gravity flow path) for runoff if it was not infiltrated generally flows in a south/southwest direction towards King County/City of Shoreline within the Storm Creek basin. Due to the fact the site's underlying soils are sandy and well -draining and there are no formal collection and conveyance system adjacent to the site, the project will utilize on -site infiltration to control stormwater runoff. The project does not propose to directly discharge to the city stormwater system (MS4). See the Downstream Drainage Facility Map and Watershed Basin Map delineating the local stormwater system and basin. Downstream Drainage Facility Map (City of Edmonds GIS) o � o I ,' • imir pi a ile Downstream Point 9 + . RAMEngineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page C-17 Watershed Basin Map: F I G U R E B- 1 CITY OF EDMONDS WATERSHEDS Deer Creek Perrinville Edmonds Marsh Puget Sound Edmonds Way `- Puget Sound Piped Fruitdale ®_ Shell Creek Good Hope Pond ` Shellabarger Halls Creek Southwest Edmonds A - Hindley Creek C Southwest Edmonds B Lake Ballinger L - Stilthouse Creek Lund's Gulch Talbot Park A Meadowdale A ® Talbot Park B Meadowdale B ® Terrace Creek Northstream i�� Westgate Pond Dutfall Creek 1000 2,000 Willow Creek 4,000 6.000 1 in = 2,000 ft Ne —rly of arty sort, ind.dirg accuracy, fitness, of me,chaMabilnv acwmpanythis protluR. March 30, 2010 N A A Lund's Gulch'" Meadowdale A s Mea2lowdale B " Z � -iamot°' \\\ Terrace Creek 8,000 ;reet Puge ; albotParkA aLb k lb1t Park B IF rl .uitdale Ssi Creek A pY �y I Good Hope Pond s3 hY 1 I ----loam so sw —' 1_7 B-- wy i If Shell Creek uah s, sw i barged .t i es Pe / 3 / a Westgate Pond Halls Creek / a ----------------- ill�w Creek ,• < 3 T; m zzam sisw JO •I _ i a i.-- \ i Creek ! ------- Edmonds Way I SITE Southwest Edmonds A - Lake Ballinger 240!h 51 S W O E Sbuthwest Edmonds B 1 L--------------------�— RAN Engineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page C-18 D. SOILS REPORTS: 1. Geotechnical Response to City Comments Letter Prepared by: Earth Solutions NW, LLC Date: May 10, 2024 Pages: 2 2. Geotechnical Evaluation Letter Prepared by: Earth Solutions NW, LLC Date: January 15, 2024 Pages: 15 MAN =ngineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page D-1 May 10, 2024 ES-9558.01 Select Homes, Inc. 8304 — 212' Street Southwest Edmonds, Washington 98026 Attention: Kayla Nichols Subject: Response to Comments Proposed Single -Family Residence 10429 — 240t" Place Southwest Edmonds, Washington Dear Kayla: Earth Solutions NW«C Earth Solutions NW LLC Geotechnical Engineering, Construction Observation/Testing and Environmental Services As requested, Earth Solutions NW, LLC (ESNW) has prepared this letter responding to the City of Edmonds review comments. The comments pertinent to the geotechnical aspects of the project are provided below, followed by our responses. ESNW prepared the referenced geotechnical evaluation for the subject project. Storm Drainage Report 2. — The Geotech report states that temporary storm mitigation will likely require interceptor trenches and sumps. Please provide a note in the SWPPP and/or the TESC plan. ESNW Response — Based on the permeability of the native soil, we anticipate storm runoff to infiltration on site, and the need for interceptor trenches or sumps is unlikely. Storm Drainage Report 3. — The geotechnical report states zones of perched groundwater seepage may be encountered within site excavation. Please suggest a BMP or method for dewatering for Element 10 of the SWPPP. ESNW Response — Based on the permeability of the native soil, it is unlikely that seepage is encountered and it is our opinion that project plans do not need to incorporate dewatering methods. Civil Plans 3. — It appears that the estimated finished grade over the infiltration facility is approximately 325.5' and the bottom of the proposed drywell is 319'. The Geotechnical report states that they encountered groundwater seepage at 6.5' below grade. Please confirm that the infiltration facility base is at least 1 foot above the seasonal groundwater table. 15365 NE 90" Street, Suite 100 • Redmond, WA 98052 • (425) 449-4704 3130 Varney Lane, Suite 105 Pasco, WA 99301 • (509) 905-0275 esnw.com Select Homes, Inc. May 10, 2024 ES-9558.01 Page 2 ESNW Response — The light groundwater seepage noted was a result of the high volume of water infiltrated during the pilot infiltration test completed within that test pit. Review of a boring that was completed near the intersection of 244th Street Southwest and 13th Avenue Northwest indicates that groundwater is present at depths of about 28.3 feet to 29.8 feet below the ground surface elevation (approximately 300 feet). Based on the subsurface conditions observed on site and the review of nearby deep subsurface data, it is our opinion that groundwater will not negatively impact the proposed drywell. ESNW shall be present on site during construction of the drywell to confirm anticipated subsurface conditions. Should you require additional information, or have questions, please call. Sincerely, EARTH SOLUTIONS NW, LLC 05/10/2024 Henry T. Wright, P.E. Associate Principal Engineer cc: RAM Engineering, Inc. Attention: Rob Long, P.E. References: • Stormwater Review Comments, provided by City of Edmonds, dated March 18, 2024 • Geotechnical Evaluation, prepared by ESNW, ES-9558, dated January 15, 2024 • Civil Plans, prepared by RAM Engineering, Inc. Earth Solutions NW. LLC January 15, 2024 ES-9558 Select Homes, Inc. 8304 — 212th Street Southwest Edmonds, Washington 98026 Attention: Kayla Nichols Subject: Geotechnical Evaluation Proposed Single -Family Residence 10429 — 240th Place Southwest Edmonds, Washington Greetings: Earth Solutions NW«c Earth Solutions NW LLC Geotechnical Engineering, Construction Observation/Testing and Environmental Services As requested, Earth Solutions NW, LLC (ESNW) has prepared this geotechnical evaluation for the proposed single-family residence. A summary of our subsurface exploration, laboratory analyses, and recommendations are provided in this letter report. Project & Site Description The subject site is located north of 240th Place Southwest, approximately 200 feet east of the intersection with 105th Place West, in Edmonds, Washington, as illustrated on the attached Vicinity Map (Plate 1). The site consists of a single tax parcel (Snohomish County Parcel No. 00564900100500) and totals about 0.26 acres of land area. The site is currently developed with a single-family residence and a detached garage building. Existing topography descends gently to the southwest, with less than five feet of elevation change across the parcel. Vegetation across the subject site consists of moderately sized trees along the property margins and landscaping elements. We understand the proposed project includes the removal of the existing single-family residence and the construction of a new single-family residence. Based on conceptual plans discussed with the client, the proposed residential structure will be two to three stories and will consist of relatively lightly loaded wood framing supported on conventional foundations. Based on our experience with similar developments, we estimate wall loads on the order of 1 to 2 kips per linear foot, column loads of less than 20 kips, and slab -on -grade loading of 150 pounds per square foot (psf). 15365 N.E. 90th Street, Suite 100 0 Redmond, WA 98052 6 (425) 449-4704 • FAX (425) 449-4711 Select Homes, Inc. January 15, 2024 Subsurface Conditions ES-9558 Page 2 An ESNW representative observed, logged, and sampled two test pits on November 16, 2023. The test pits were excavated at accessible areas of the site using a mini-trackhoe and operator provided by the client. A hand -auger exploration was completed in the front yard area to supplement the data collected with the excavator. The approximate locations of the test locations are depicted on Plate 2 (Subsurface Exploration Plan). Please refer to the attached soil logs for a more detailed description of subsurface conditions. Representative soil samples collected at the locations were evaluated in general accordance with Unified Soil Classification System (USCS) and United States Department of Agriculture (USDA) methods and procedures. Topsoil Topsoil was observed extending to a depth of approximately six inches below the existing ground surface (bgs) at the test locations. The topsoil was characterized by dark brown color and the presence of fine organic material. Fill Fill was not encountered during our subsurface exploration. Native Soil Underlying the topsoil, native soil encountered at the test locations consisted primarily of soils consistent with the makeup outwash deposits, including poorly graded sands and gravels (USCS: SP-SM, SP, and GP). The native soil was generally encountered in a damp condition at the time of exploration. The maximum exploration depth was approximately six and one-half feet bgs. Geologic Setting Geologic mapping identifies advance outwash (Qva) across the site and the nearby area. Advance outwash deposits consist primarily of a nonsorted mixture of silt, sand, and sub -rounded to well-rounded gravels. Outwash deposits are typically observed in a semi -compacted state as a result of glacial processes. USDA soil mapping identifies the Alderwood-urban land complex, 0 to 5 percent slopes, as the primary soil unit underlying the site. Alderwood series soils formed in glacial deposits. The urban land designation denotes areas that have been subject to historical mass grading. Based on our field observations, on -site native soils are representative of advance outwash deposits and Everett series soil. Earth Solutions NW. LLC Select Homes, Inc. January 15, 2024 Groundwater ES-9558 Page 3 Light groundwater seepage was observed at a depth of six and one-half feet bgs in TP-2. Groundwater seepage rates and elevations fluctuate depending on many factors, including precipitation duration and intensity, the time of year, and soil conditions. In general, groundwater flow rates are higher during the winter, spring, and early summer months. Critical Areas Evaluation A review of Edmonds Municipal Code Chapter 23.80 — Geologically Hazardous Areas (GHAs) was completed to evaluate whether GHAs recognized by the City of Edmonds (including erosion, landslide, and seismic hazard areas) exist on or near the subject site. Based on review of the Edmonds interactive parcel viewer, the subject site contains a potential erosion hazard area on the northwestern property boundary. Based on our on -site evaluation of the subject site, gradients within mapped potential erosion hazard area were observed to be roughly five percent slopes and do not classify as an erosion hazard area. Based on our site -specific field observations, it is our opinion the site does not contain, and is not immediately adjacent to, any geologic hazard areas. Structural Fill Structural fill is defined as compacted soil placed in foundation, slab -on -grade, roadway, permanent slope, retaining wall, and utility trench backfill areas. Structural fill placed and compacted during site grading activities should meet the following specifications and guidelines: • Structural fill material • Moisture content • Relative compaction (minimum) • Loose lift thickness (maximum) Granular soils* At or slightly above optimum** 95 percent (Modified Proctor) 12 inches The existing soil may not be suitable for use as structural fill unless the soil is at (or slightly above) the optimum moisture content at the time of placement and compaction. "* Soil shall not be placed dry of optimum and should be evaluated by ESNW during construction. Site Excavations Temporary site excavations over four feet in height should be sloped at a maximum inclination of 1 H:1 V (Horizontal:Vertical). If temporary site excavations cannot be achieved with the above slope inclination, ESNW should provide additional recommendations and shoring may be necessary. ESNW should observe site excavations to confirm adequate excavation stability. Earth Solutions NW. LLC Select Homes, Inc. January 15, 2024 Foundations ES-9558 Page 4 The proposed residential structure can be constructed on conventional continuous and spread footing foundations bearing on competent native soil, compacted native soil, or new structural fill placed directly on competent native soil. Competent native soil suitable for support of foundations will likely be encountered beginning at depths of two to three feet bgs. Compaction of the foundation subgrade areas may be prudent depending on the condition of the native soil exposed during construction. ESNW should be retained during construction to perform a foundation subgrade evaluation prior to formwork. Where loose or unsuitable conditions are encountered at foundation subgrade elevations, compaction of the soils to the specifications of structural fill, or overexcavation and replacement with structural fill will be necessary. Provided the proposed structures will be supported as recommended above, the following parameters can be used for foundation design: • Allowable soil bearing capacity 2,500 psf • Passive earth pressure • Coefficient of friction 300 pcf M1 The passive earth pressure value provided above assumes the foundations will be backfilled with structural fill. A factor -of -safety of 1.5 has been applied to the passive earth pressure and coefficient of friction values provided in this section. For short-term wind and seismic loading, a one-third increase in the allowable soil bearing capacity may be assumed. With structural loading as expected, total settlement in the range of one inch is anticipated, with differential settlement of about one-half inch. The majority of the settlements should occur during construction, as dead loads are applied. Slab -on -Grade Floors Slab -on -grade floors for the proposed structures should be supported on a well -compacted, firm, and unyielding subgrade. Where feasible, native soils exposed at the slab -on -grade subgrade level can likely be compacted in situ to the specifications described in this section. Unstable or yielding areas of subgrade should be recompacted, or overexcavated and replaced with suitable structural fill, prior to slab construction. A capillary break consisting of a minimum of four inches of free -draining crushed rock or gravel should be placed below the slab. The free -draining material should have a fines content of 5 percent or less (where the fines content is defined as the percent passing the Number 200 sieve, based on the minus three -quarter -inch fraction). In areas where slab moisture is undesirable, installation of a vapor barrier below the slab should be considered. If a vapor barrier is utilized, it should be a material specifically designed for use as a vapor barrier and should be installed in accordance with manufacturer specifications. Earth Solutions NW. LLC Select Homes, Inc. January 15, 2024 Retaining Walls ES-9558 Page 5 Retaining walls must be designed to resist earth pressures and applicable surcharge loads. The following parameters can be used for retaining wall design: • Active earth pressure (unrestrained condition) • At -rest earth pressure (restrained condition) • Traffic surcharge (passenger vehicles) • Passive earth pressure • Coefficient of friction • Seismic surcharge * Where H equals the retained height. 35 pcf 55 pcf 70 psf (rectangular distribution) 300 pcf 0.40 8H* The passive earth pressure and coefficient of friction values include a safety factor of 1.5. Additional surcharge loading from adjacent foundations, sloped backfill, or other loads should be included in the retaining wall design. Drainage should be provided behind retaining walls such that hydrostatic pressures do not develop. If drainage is not provided, hydrostatic pressures should be included in the wall design. Retaining walls should be backfilled with free -draining material or sheet drainage that extends along the height of the wall, and a distance of at least 18 inches behind the wall. The upper one foot of the wall backfill can consist of a less permeable soil, if desired. A perforated drain pipe should be placed along the base of the wall, and connected to an approved discharge location. Earth Solutions NW. LLC Select Homes, Inc. January 15, 2024 Seismic Design ES-9558 Page 6 The 2018 International Building Code (2018 IBC) recognizes the most recent edition of the Minimum Design Loads for Buildings and Other Structures manual (ASCE 7-16) for seismic design, specifically concerning earthquake loads. Based on the soil conditions encountered at the test locations, the parameters and values provided below are recommended for seismic design per the 2018 IBC. Parameter Value Site Class D* Mapped short -period spectral response acceleration, Ss (g) 1.281 Mapped 1-second period spectral response acceleration, S1 (g) 0.449 Short period site coefficient, Fa 1.000 Long -period site coefficient, Fv 1.851 ** Adjusted short -period spectral response acceleration, SMs (g) 1.281 Adjusted 1-second period spectral response acceleration, SMi (g) 0.831 ** Design short -period spectral response acceleration, SIDS (g) 0.854 Design 1-second period spectral response acceleration, SID, (g) 0.554** Assumes medium dense to dense native soil conditions, encountered to a maximum depth of six and one-half feet bgs during the November 2023 field exploration, remain medium dense to dense to at least 100 feet bgs. ** Values assume Fv may be determined using linear interpolation per Table 11.4-2 in ASCE 7-16. Drainage Zones of perched groundwater seepage may be encountered within site excavations. Temporary measures to control surface water runoff and groundwater during construction would likely involve passive elements such as interceptor trenches and sumps. ESNW should be consulted during preliminary grading to identify areas of seepage and to provide recommendations to reduce the potential for instability related to seepage effects. Finish grades must be designed to direct surface drain water away from the structure. Water must not be allowed to pond adjacent to the structure. Grades adjacent to the building should be sloped away from the building at a gradient of either at least 2 percent for a horizontal distance of 10 feet or the maximum allowed by adjacent structures. In our opinion, footing drains should be installed along building perimeter footings. However, elimination of footing drains can be considered if relatively free -draining soil is exposed at footing subgrade elevations. Earth Solutions NW. LLC Select Homes, Inc. January 15, 2024 Infiltration Evaluation ES-9558 Page 7 ESNW completed a small-scale Pilot Infiltration Test (PIT) to evaluate the feasibility of on -site infiltration BMPs from a geotechnical standpoint. In general, the native sand outwash deposits exhibit good infiltration characteristics and can be utilized for on -site infiltration to the extent practicable. In opinion, based on the results of in -situ infiltration testing, field observation, and laboratory analyses, full infiltration is feasible from a geotechnical standpoint. The small-scale PIT was completed in general accordance with the Department of Ecology Stormwater Management Manual for Western Washington, as adopted by the City of Edmonds, at test location TP-2. The PIT was completed at a depth of roughly two and one-half feet bgs and within a representative section of sand outwash deposits. For infiltration facilities interfacing with the native sand outwash deposits, the following design values (based on the results of the PIT) may be used: Test Pit ID Test Depth Ksat initial CFv CFT Um Ksat design TP-1 2.5 ft 35.4 in/hr 0.7 0.5 0.9 11.1 in/hr ESNW should review final drainage plans as well as observe infiltration facility excavation to confirm anticipated soil types are exposed in the facility subgrade. Limitations This report has been prepared for the exclusive use of Select Homes, Inc. and their representatives. The recommendations and conclusions provided in this report are professional opinions consistent with the level of care and skill that is typical of other members in the profession currently practicing under similar conditions in this area. A warranty is not expressed or implied. Variations in the soil and groundwater conditions observed at the test sites may exist and may not become evident until construction. ESNW should reevaluate the conclusions in this report if variations are encountered. Additional Services ESNW should be retained to provide additional geotechnical services in association with this project, including testing and consulting services during construction. ESNW should have an opportunity to review final project plans with respect to geotechnical recommendations provided in this letter. Earth Solutions NW. LLC Select Homes, Inc. January 15, 2024 ES-9558 Page 8 We appreciate the opportunity to be of service to you and trust this letter meets your current needs. Should you have any questions, or require additional information, please call. Sincerely, EARTH SOLUTIONS NW, LLC Samuel E. Suruda, L.G. Senior Staff Geologist �lT•W WA Z.Ir 53803 �FGISTER�� FSS/ONAk- 01 /15/2024 Henry T. Wright, P.E. Associate Principal Engineer Attachments: Plate 1 — Vicinity Map Plate 2 — Subsurface Exploration Plan Subsurface Exploration Logs Grain Size Distribution References: • Geologic Map of the Edmonds East and Part of the Edmonds West Quadrangles, Washington, prepared by James P. Minard, dated 1983 • Edmonds Municipal Code Chapter 23.80 — Geologically Hazardous Areas, updated August 2, 2023 • Edmonds Municipal Code Chapter 18.30 — Stormwater Management, updated July 1, 2022 • 2019 Stormwater Management Manual for Western Washington, endorsed by the City of Edmonds Earth Solutions NW. LLC ooD i ao �u o �� 6 i °�OWA tOiQ 0 �o� — - 228[h Street Southwest 228t Ibbppo s b Oeer Dr'N? I Qc1ooC q No Shednvood ek O G damn a "FOfeSt y°y°^ �� EdFnoo S o n ?� ��O CspoO fa d X Woodwy % p� Qoo u� oa o A' 9 9 ooaP 4 O❑ •� 0 a 231st Street Sou[hwes — �.� 81Pb coo❑.. 6 aqP _ Z I i 9 0, � �o _ _ 232nd Street Southwest 0 3 9 Q III F� Holly Lane a Edmonds 4 Z- ' F�monds m\ =I Maple Lane ,4 x eights o- a y Nottingham Road v ❑K-12 �u'.,1 �;�I Madrona Lane 235th Place Southwest 236th Street S Modrono \ 3 — K-8School �tnwest Snoline y 238th Street Southwest F ( Elementary 237[h Pla" theses m School \ \ t _ N // 238Ih S[ree[Sou \ • " m SITE'� 240[h Street Southwest 2401h Street Southwest \- West 3 vl N o. WA _j a-� Eagle.Lane 1Dl—_� — vP Firdale a 'GP qu �o n t oe e Befry. Lane N243rtl Place Sou[h'Neyo ^ AO Snohomish county _ _ Edmonds -------�---- J e� Klny County Norte 205th e[ - Northwest 2040,St¢ VY D F O o D o Z Z D North 202nd Street c o D o oD n c '.dthwest 201st Street Northwest 201s ^ m a 3o North 201 st Street Street o c Z Z Z .. "i D _ North 200th 5[reeG`u Northwest 199th Street o F � < < Northwest 198th Str- ,. c Z c ^ ost 198th Street s ., Northwest 197[h Street '.Z N <> ry �ch9P m \Richmond 'Po ° o YT 44 4 Northwest 195th Street `North 195th Street a Beach 9 < ?�P P J \ r- Albert Einstein `• e e o ,. ` Middle ZO \ A o o IM D —Northty� School. Northwest 192nd Street Richmond ich Saltwater Pork o 3 �5 r C° ?o Blue Heron C Reserve o �c Reference: NORTH Snohomish County, Washington Open StreetMap.org NOTE: This plate may contain areas of color. ESNW cannot be responsible for any subsequent misinterpretation of the information resulting from black & white reproductions of this plate. m ry v "'�- _--�-- North 188th Street¢' Northwest 185th Street v \ LL O. D Vicinity Map 10429 — 240th Place S.W. Edmonds, Washington Drawn MRS I Date 01 /03/20241 Proj. No. 9558 Checked SES Date Jan.2024 Plate 1 c ALLEY TP-21 I TP-1 24OTH PLACE S.W. LEGEND _ TP-1 Approximate Location of — ■ — ESNW Test Pit, Proj. No. ES-9558, Nov. 2023 HA-1 I Approximate Location of — • — ESNW Hand Auger Boring, Proj. No. ES-9558, Nov. 2023 Subject Site Existing Building NORTH NOT - TO - SCALE NOTE: The graphics shown on this plate are not intended for design purposes or precise scale measurements, but only to illustrate the approximate test locations relative to the approximate locations of existing and / or proposed site features. The information illustrated is largely based on data provided by the client at the time of our study. ESNW cannot be responsible for subsequent design changes or interpretation of the data by others. NOTE: This plate may contain areas of color. ESNW cannot be responsible for any subsequent misinterpretation of the information resulting from black & white reproductions of this plate. Subsurface Exploration Plan 10429 — 240th Place S.W. Edmonds, Washington Drawn MRS Date 01/03/2024 Proj. No. 9558 Checked SES Date Jan.2024 Plate 2 W I ,1� �� Well -graded gravel with Moisture Content Symbols m CU > GW or without sand, little to 0 c no fines Dry - Absence of moisture, dusty, dry to Cement grout U U j L 11 the touch ATD = At time surface seal 0 O o o of drilling g Bentonite o p o01 00(lo Poorly graded gravel with Damp Perceptible moisture, likely below chips o Z v UU o 0 0 0 GP or without sand, little to optimum MC Static water i LO C o Q�oQ no fines level (date) eall Co ° Moist - Damp but no visible water, likely o a) H a) at/near optimum MC - Filter pack with 65 0 a) tav, 0 0 uD op o GM Silty gravel with or without Wet - Water visible but not free draining, blank casing section o 0 2 � O Q 0 sand likely above optimum MC Screened casing o or Hydrotip with U) ° 0 .0 o Saturated/Water Bearing - Visible free filter pack o U) 0 � Clayey gravel with or water, typically below groundwater table End cap O -0-0 � ° L L LL C7 ^ GC without sand Terms Describing Relative Density and Consistency _ 0 co Z Coarse -Grained Soils: Test Symbols & Units Well -graded sand with u� O SW or without gravel, little to = Density SPT blows/foot Fines Fines Content ( ) oo N o c IL o°o°o°o°o°o °°°°°°°°°°° no fines Very Loose < 4 O LO U ._ U (n o MC =Moisture Content (%) Loose 4 to 9 ':: ca � 0 to , •:: •..:•.;: , . Poorly graded sand with DD = Dr Density cf Medium Dense 10 to 29 Y Y (P ) a)o v Sp or without gravel, little to o Z no fines Dense 30 to 49 Str = Shear Strength (tsf) 0 a)Very Dense _> 50 O U) PID = Photoionization Detector (ppm) co a� '.:' . SM Silty sand with or without o Lo c c :;: .::'•:. ;.. gravel Fine -Grained Soils: OC = Organic Content (%) e . •;. Consistency SPT blows/foot CEC = Cation Exchange Capacity (meq/100 g) : Very Soft < 2 � � SC Clayey sand with or LL = Liquid Limit (%) Soft 2 to 3 ^ without gravel Medium Stiff 4 to 7 PL = Plastic Limit (%) (%) Stiff 8 to 14 PI = Plasticity IndexLO CD Silt with or without sand IVIL or gravel; sandy or Very Stiff 15 to 29 gravelly silt Hard _> 30 0 0 0 U 0 F/// Clay of low to medium Y Component Definitions > a)—.1 plasticity; plasticity; lean clay with cn M t. or without sand or gravel; Descriptive Term Size Range and Sieve Number 00 cn E sandy or gravelly lean clay Boulders Larger than 12" — — _ � rn . — J U .5 Cobbles 3" to 12" �o _ OL Organic clay or silt of Zo — low plasticity Gravel 3" to No. 4 (4.75 mm) -0 to J �_ — Coarse Gravel 3" to 3/4" Fine Gravel 3/4" to No. 4 (4.75 mm) Elastic silt with or without d Sand No. 4 (4.75 mm) to No. 200 (0.075 mm) 0 0 o MH sand or gravel; sandy or Coarse Sand No. 4 (4.75 mm) to No. 10 (2.00 mm) c O (n g gravelly elastic silt Medium Sand No. 10 (2.00 mm) to No. 40 (0.425 mm) IL 2 >, - Fine Sand No. 40 (0.425 mm) to No. 200 (0.075 mm) 0 °o U O Clay of high plasticity; Silt and Clay Smaller than No. 200 (0.075 mm) o -0 LO CH fat clay with or without Modifier Definitions o E sand or gravel; sandy or J gravelly fat clay —_ Percentage by fn Weight (Approx.) Modifier CY OH Organic clay or silt of medium to high plasticity < 5 Trace (sand, silt, clay, gravel) 5 to 14 Slightly (sandy, silty, clayey, gravelly) o> ca o PT Peat, muck, and other 15 to 29 Sandy, silty, clayey, gravelly = �U) — = highly organic soils Q _> 30 Very (sandy, silty, clayey, gravelly) Classifications of soils in this geotechnical report and as shown on the exploration logs are based on visual — field and/or laboratory observations, which include density/consistency, moisture condition, grain size, and ii FILL Made Ground plasticity estimates, and should not be construed to imply field or laboratory testing unless presented herein. Visual -manual and/or laboratory classification methods of ASTM D2487 and D2488 were used as an identification guide for the Unified Soil Classification System. Earth Solutions NW L�c Earth Solutions NWLLC Geotechnical Engineering, Construction Observation/Testing and Environmental Services EXPLORATION LOG KEY Earth Solutions NW, LLC 15365 N.E. 90th Street, Suite 100 Redmond, Washington 98052 Telephone: 425-449-4704 Fax: 425-499-4711 BORING NUMBER HA-1 PAGE 1 OF 1 PROJECT NUMBER ES-9558 PROJECT NAME 10429 — 240th Place S.W. DATE STARTED 11/16/24 COMPLETED 11/16/24 GROUND ELEVATION DRILLING CONTRACTOR ESNW Rep LATITUDE 47.78080 LONGITUDE-122.37370 LOGGED BY SES CHECKED BY HTW GROUND WATER LEVEL: NOTES SZ AT TIME OF DRILLING SURFACE CONDITIONS Grass AFTER DRILLING w ww H w CO TESTS 2 J 0- o Q z c7 U) SP- SM MC = 9.2 2.5 .inac = Q MATERIAL DESCRIPTION Dark brown TOPSOIL, minimal root intrusions Brown poorly graded SAND with silt and gravel, medium dense, damp [USDA Classification: very gravelly loamy coarse SAND] Hand auger boring terminated at 2.5 feet below existing grade. No groundwater encountered during excavation. No caving observed. LIMITATIONS: Ground elevation (if listed) is approximate; the test location was not surveyed. Coordinates are approximate and based on the WGS84 datum. Do not rely on this test log as a standalone document. Refer to the text of the geotechnical report for a complete understanding of subsurface conditions. Earth Solutions NW, LLC TEST PIT NUMBER TP-1 15365 N.E. 90th Street, Suite 100 Redmond, Washington 98052 PAGE 1 OF 1 Telephone: 425-449-4704 Fax: 425-499-4711 PROJECT NUMBER ES-9558 PROJECT NAME 10429 — 240th Place S.W. DATE STARTED 11/16/24 COMPLETED 11/16/24 GROUND ELEVATION EXCAVATION CONTRACTOR Client Provided LATITUDE 47.78129 LONGITUDE-122.37340 LOGGED BY SES CHECKED BY HTW GROUND WATER LEVEL: NOTES SZ AT TIME OF EXCAVATION SURFACE CONDITIONS Grass AFTER EXCAVATION w H w 2 ww CO 0- TESTS J MATERIAL DESCRIPTION o Q z j c7 U) 0.0 TPSL Ta• : Dark brown TOPSOIL, roots intrusions to 3' 0.5 Brown poorly graded SAND with silt and gravel, medium dense, damp GB MC = 5.7 SP- .: SM 2.5 IT 3.0 Gray poorly graded SAND with gravel, medium dense, damp SP GB MC = 2.4 [USDA Classification: extremely gravelly coarse SAND] 5.0 Fines = 0.4 GB MC = 5.7 5 5 Test pit terminated at 5.5 feet below existing grade. No groundwater encountered during excavation. No caving observed. LIMITATIONS: Ground elevation (if listed) is approximate; the test location was not surveyed. Coordinates are approximate and based on the WGS84 datum. Do not rely on this test log as a standalone document. Refer to the text of the geotechnical report for a complete understanding of subsurface conditions. Earth Solutions NW, LLC 15365 N.E. 90th Street, Suite 100 Redmond, Washington 98052 Telephone: 425-449-4704 Fax: 425-499-4711 TEST PIT NUMBER TP-2 PAGE 1 OF 1 PROJECT NUMBER ES-9558 PROJECT NAME 10429 — 240th Place S.W. DATE STARTED 11/16/24 COMPLETED 11/16/24 GROUND ELEVATION EXCAVATION CONTRACTOR Client Provided LATITUDE 47.78130 LONGITUDE-122.37325 LOGGED BY SES CHECKED BY HTW GROUND WATER LEVEL: NOTES SZ AT TIME OF EXCAVATION SURFACE CONDITIONS Grass AFTER EXCAVATION w ww H w CO TESTS 2 J 0- o Q z c7 U) 0.5 SID SD 2.5 0110 GB MC = 4.0 o p Fines = 2.3 GP O o (�R M('=5d o D MATERIAL DESCRIPTION Dark brown TOPSOIL, minimal root intrusions -probed 6" Brown poorly graded SAND with silt and gravel, medium dense, damp Gray poorly graded GRAVEL with sand, medium dense, damp [USDA Classification: extremely gravelly coarse SAND] -probed 2" -becomes wet post test Gray poorly graded SAND with gravel, medium dense, damp -light groundwater seepage at 6.5' [USDA Classification: very gravelly coarse SAND] Test pit terminated at 6.5 feet below existing grade. Light groundwater seepage encountered at 6.5 feet during excavation. No caving observed. LIMITATIONS: Ground elevation (if listed) is approximate; the test location was not surveyed. Coordinates are approximate and based on the WGS84 datum. Do not rely on this test log as a standalone document. Refer to the text of the geotechnical report for a complete understanding of subsurface conditions. r Earth Solutions NW, LLC 15365 NE 90th Street, Suite 100 Redmond, WA 98052 Telephone: (425) 449-4704 GRAIN SIZE DISTRIBUTION PROJECT NUMBER ES-9558 PROJECT NAME 10429 — 240th Place S.W. U.S. SIEVE OPENING IN INCHES U.S. SIEVE NUMBERS I HYDROMETER 100 95 90 85 80 75 70 65 H c3 60 w m 55 tY w 50 z LL 1-- 45 z w ry 40 w a 35 30 25 20 15 10 5 0 III■■■■����■■off■III■11■■■■■■�■■111■■■■�■■��III■1 100 10 1 0.1 0.01 0.001 GRAIN SIZE IN MILLIMETERS COBBLES GRAVEL I SAND SILT OR CLAY coarse fine coarse medium fine ,ecimen Identification Classification Cc CU HA-01 2.50ft. USDA: Brown Very Gravelly Loamy Coarse Sand. USCS: SP-SM with Gravel. 0.75 32.92 TP-01 4.50ft. USDA: Gray Extremely Gravelly Coarse Sand. USCS: SP with Gravel. 0.92 10.48 TP-02 2.50ft. USDA: Gray Extremely Gravelly Coarse Sand. USCS: GP with Sand. 0.87 38.57 TP-02 6.50ft. USDA: Grav Very Gravelly Coarse Sand. USCS: SP with Gravel. 0.64 8.03 Specimen Identification D100 D60 D30 D10 LL I PL PI %Silt I %Clay • HA-01 2.5ft. 37.5 3.493 0.529 0.106 9.2 m TP-01 4.5ft. 37.5 5.152 1.522 0.491 0.4 A TP-02 2.5ft. 37.5 12.968 1.948 0.336 2.3 * TP-02 6.5ft. 19 2.793 0.791 0.348 0.3 E. CONSTRUCTION SWPPP REQUIREMENTS: The project will require grading to construct the proposed building and utilities (including the stormwater control facilities). Standard erosion control measures are proposed to be used during construction. The primary erosion and sediment control BMP during construction will be proper soil stabilization methods. Exposed soils shall be stabilized by application of effective BMPs that protect the soil from the erosive forces of raindrops, flowing water, and wind. Applicable practices include, but not limited to, temporary and permanent seeding, sodding, mulching, plastic covering, erosion control fabrics, matting, the early application of gravel base on areas to be paved, and dust control. The contractor shall select a soil stabilization method best suited for the particular situation. Stockpiles must be stabilized and protected with sediment trapping measures. In addition, site containment of exposed soils shall be sustained by using silt fence barriers along the down -slope boundaries of the site's disturbance areas. See the site development plan for details. Construction Stormwater Pollution Prevention Plan (SWPPP): The following is a summary of the site's erosion control measures that evaluates the typical DOE 13 elements of a SWPPP: Element 1: Mark Clearing Limits: Clearing limits have been delineated on the engineering site development plans. BMP Recommended: Utilized: BMP C233: Silt Fence Element 2: Establish Construction Access: A construction access has been delineated on the engineering site development plans. BMP Recommended: BMP C105: Stabilized Construction Access Element 3: Control Flow Rates: Due to the relatively small size of the site's disturbance areas (less than 0.5 ac); it is recommended to maintain sheet flow dispersion (through downslope perimeter silt fencing) and not install collect swales and a sediment trap that would concentrate runoff flows. During construction silt fencing will provide attenuation of site runoff and upon project completion and stabilization (established lawns and landscape of exposed soils). BMP Recommended: No site specific BMP prescribed. Element 4: Install Sediment Controls: Filter fabric fence has been delineated and detailed on the engineering site development plans. At a minimum, silt fence will be installed along the down gradient perimeter of the disturbed area that will receive sediment -laden runoff. BMP Recommended: BMP C233: Silt Fence Element 5: Stabilize Soils: Soils will be stabilized per the TESC notes listed on the engineering site development plans. BMP Recommended: BMP C120: Temporary and Permanent Seeding and BMP C123: Plastic Covering Element 6: Protect Slopes: Exposed slopes shall be stabilized per the TESC notes listed on the engineering site development plans. RAMEngineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page E-1 BMP Recommended: BMP C120: Temporary and Permanent Seeding and BMP C123: Plastic Covering Element 7: Protect Drain Inlets: Drain inlet protection will be installed on all catch basins that will receive sediment -laden runoff. See the engineering site development plans for locations and detail. BMP Recommended: BMP C220: Inlet Protection Element 8: Stabilize Channels and Outlets: This element is not applicable since there are no temporary channels or outlets proposed. BMP Recommended: BMP C209: Outlet Protection Element 9: Control Pollutants: Pollutants shall be managed as described in the TESC notes listed on the engineering site development plans. BMP Recommended: BMP C151: Concrete Handling Element 10: Control De -Watering: Highly turbid or contaminated de -watering water shall be handled separately from stormwater. The water from all de -watering systems for trenches and foundations shall be treated or disposed of prior to discharging from the site. BMP Recommended: No site specific BMP prescribed. Element 11: Maintain BMPs: BMPs shall be maintained and removed at the end of the project as follows: i. All temporary and permanent erosion and sediment control BMPs shall be inspected, maintained and repaired in accordance with the Drainage Manual or as approved or required by the City to assure continued performance of their intended function in accordance with BMP specifications. ii. The applicant may remove temporary BMPs when they are no longer needed. iii. All temporary erosion and sediment control BMPs shall be removed within 30 days after construction is completed and the City has determined that the site is stabilized. BMP Recommended: BMP C150: Materials on Hand Element 12: Manage the Project: The owner of the site is responsible for managing the installation and maintenance of the site BMPs. BMP Recommended: BMP C150: Materials on Hand and BMP C162: Scheduling. Element 13. Protect Low Impact Development BMPs: Compaction (i.e. vehicle and equipment traffic or storage; and/or placement of stockpiles) to the soils in the area of the stormwater BMPs (Post - Construction Soil Quality and Depth BMP T5.13 and Perforated Stub -out Connections BMP T5.10C) shall be avoided during construction. BMP Recommended: BMP C233: Silt/Protection Fence Conclusion: The total site disturbance area (0.263 ac.) of the project is less than one acre, thus a formal Department of Ecology Notice of Intent application for NPDES Construction Stormwater Permit coverage is not required. The final site development construction plans include specific grading and drainage improvement notes and details. With proper installation, maintenance, and inspections of the proposed construction the project should have minimal impact on the surrounding environment. RAMEngineering, Inc. RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page E-2 F. OPERATION AND MAINTENANCE GUIDELINES: These guidelines are intended to provide operation and maintenance instructions for the project's storm drainage control facilities. The owner is responsible for maintenance of storm drainage facilities within the property (private property owner system); the owner is not responsible for maintenance within the public right-of-way (City system). The private property owner is responsible for properly maintaining the stormwater infrastructure on their property to ensure it operates as designed. The City has developed an inspection program to ensure private property owners are properly maintaining their stormwater systems. This manual is not comprehensive; although it explains the intended operation of the various components of the drainage system, and suggests a routine of inspection and maintenance, it cannot anticipate every problem. Once a historical record of maintenance is established, it may be prudent to alter the routine. It is recommended that maintenance records be kept, and that the records be reviewed periodically. The private on -site infiltration trench system consists of excavated trench filled with drain rock. The infiltration trench system has been designed to infiltrate most storm event; if an extraordinary event was to occur or multiple back to back large storm events occurred the connected catch -basins may overtop and overflow into the street system. If regular overtopping of the catch basin is experienced the system shall be thoroughly cleaned and inspected. Over a period of time siltation of the infiltration bed can occur (especially if the system and upstream catch basin are not inspected and cleaned regularly) and replacement of the rock in the infiltration system may be required. Regular inspection and maintenance of the infiltration system should occur according to the attached maintenance tables from the Washington State Department of Ecology Stormwater Manual (2019- Volume V). Semi-annual inspections shall be conducted to ensure proper operations of the drainage system. The inspections should occur prior to the winter rain season (Oct/Nov), leaving sufficient time to correct any detected maintenance problems, and at the end of the season (April/May) to determine the effect of the season's runoff. Once a historical basis is developed the frequency of inspection may be modified as necessary. Sediment can build up inside control structures and catch basins, blocking or restricting flow to the inlet. To prevent this problem, these structures should be routinely cleaned. Regular inspections of control structures should be conducted to detect the need for non -routine cleanout. MAINTENANCE REQUIREMENTS ECDC Section 18.30.090 requires privately -owned stormwater management facilities, such as LID BMPs be properly maintained. The owner of the property is the responsible party for such maintenance. The system must be kept in good working order. The entire system should be inspected once per year. An improperly maintained BMP may cause private property or street flooding. RAMEngineering, Inc. RAM No. 23-035 Contact the City Engineering Division for maintenance information. The City may make periodic inspections of BMPs to ensure they are operating properly. ECDC Section 18.30.100 contains the enforcement provisions the City can use to ensure the system is properly maintained. 10429 240th P1 S W SFR Stormwater Site Plan Report Page F-1 Washington State Department of Ecology 2019 Stormwater Management Manual for Western Washington (2019 SWMMWW) Publication No.19-10-021 Appendix V-A: BMP Maintenance Tables Ecology intends the facility -specific maintenance standards contained in this section to be conditions for determining if maintenance actions are required as identified through inspection. Recognizing that Permittees have limited maintenance funds and time, Ecology does not require that a Permittee perform all these maintenance activities on all their stormwater BMPs. We leave the determination of importance of each maintenance activity and its priority within the stormwater program to the Permittee. We do expect, however, that sufficient maintenance will occur to ensure that the BMPs continue to operate as designed to protect ground and surface waters. Ecology doesn't intend that these measures identify the facility's required condition at all times between inspections. In other words, exceedance of these conditions at any time between inspections and/or maintenance does not automatically constitute a violation of these standards. However, based upon inspection observations, the Permittee shall adjust inspection and maintenance schedules to minimize the length of time that a facility is in a condition that requires a maintenance action. Table V-A.1: Maintenance Standards - Detention Ponds Maintenance Defect Conditions When Results Expected When Component Maintenance Is Needed Maintenance Is Performed Any trash and debris which exceed 1 cubic feet per 1,000 square feet. In general, there should be no visual evidence of Trash &Debris dumping. Trash and debris cleared from site If less than threshold all trash General and debris will be removed as part of next scheduled maintenance. Any poisonous or nuisance No danger of poisonous Poisonous vegetation which may constitute vegetation where maintenance Vegetation and a hazard to maintenance personnel or the public might noxious weeds personnel or the public. normally be. (Coordinate with local health department) RAM-7inaarinq, Inc, RAM No. 23-035 10429 240th PI SW SFR Stormwater Site Plan Report Page F-2 Table V-A.1: Maintenance Standards - Detention Ponds Maintenance Defect Conditions When Results Expected When Component Maintenance Is Needed Maintenance Is Performed Any evidence of noxious weeds Complete eradication of noxious as defined by State or local weeds may not be possible. regulations. Compliance with State or local eradication policies required (Apply requirements of adopted IPM policies for the use of herbicides). Any evidence of oil, gasoline, contaminants or other pollutants Contaminants and No contaminants or pollutants Pollution present. (Coordinate removal/cleanup with local water quality response agency). Any evidence of rodent holes if Rodents destroyed and dam or facility is acting as a dam or berm repaired. (Coordinate with Rodent Holes berm, or any evidence of water local health department; piping through dam or berm via coordinate with Ecology Dam rodent holes. Safety Office if pond exceeds 10 acre-feet.) Facility is returned to design function. Beaver Dams Dam results in change or function of the facility. (Coordinate trapping of beavers and removal of dams with appropriate permitting agencies) Insects destroyed or removed When insects such as wasps from site. Insects and hornets interfere with maintenance activities. Apply insecticides in compliance with adopted IPM policies Tree growth does not allow Trees do not hinder maintenance and inspection maintenance activities. Tree Growth and access or interferes with Harvested trees should be Hazard Trees maintenance activity (i.e., slope recycled into mulch or other mowing, silt removal, vactoring, beneficial uses (e.g., alders for or equipment movements). If firewood). trees are not interfering with RAMEngineering, Inc. RAM No. 23-035 10429 240th P/ S W SFR Stormwater Site Plan Report Page F-3 Table V-A.1: Maintenance Standards - Detention Ponds Maintenance Defect Conditions When Results Expected When Component Maintenance Is Needed Maintenance Is Performed access or maintenance, do not remove Remove hazard Trees If dead, diseased, or dying trees are identified (Use a certified Arborist to determine health of tree or removal requirements) Slopes should be stabilized using appropriate erosion Eroded damage over 2 inches control measure(s); e.g.,rock deep where cause of damage is reinforcement, planting of grass, still present or where there is compaction. Side Slopes of Pond Erosion potential for continued erosion. If erosion is occurring on Any erosion observed on a compacted berms a licensed compacted berm embankment. engineer in the state of Washington should be consulted to resolve source of erosion. Accumulated sediment that exceeds 10% of the designed Sediment cleaned out to Sediment pond depth unless otherwise designed pond shape and specified or affects inletting or depth; pond reseeded if Storage Area outletting condition of the necessary to control erosion. facility. Liner (if Applicable) Liner is visible and has more Liner repaired or replaced. Liner than three 1/4-inch holes in it. is fully covered. Any part of berm which has settled 4 inches lower than the design elevation If settlement is apparent, Ponds Berms Settlements measure berm to determine Dike is built back to the design (Dikes) amount of settlement elevation. Settling can be an indication of more severe problems with the berm or outlet works. A licensed engineer in the state of Washington should be RAMEngineering, Inc. RAM No. 23-035 10429 240th P/ S W SFR Stormwater Site Plan Report Page F-4 Table V-A.1: Maintenance Standards - Detention Ponds Maintenance Defect Conditions When Results Expected When Component Maintenance Is Needed Maintenance Is Performed consulted to determine the source of the settlement. Discernable water flow through pond berm. Ongoing erosion with potential for erosion to continue. Piping Piping eliminated. Erosion potential resolved. (Recommend a Goethechnical engineer be called in to inspect and evaluate condition and recommend repair of condition. Tree growth on emergency Trees should be removed. If spillways creates blockage root system is small (base less problems and may cause failure than 4 inches) the root system of the berm due to uncontrolled may be left in place. Otherwise Tree Growth overtopping. the roots should be removed and the berm restored. A Tree growth on berms over 4 licensed engineer in the state of feet in height may lead to piping Washington should be Emergency through the berm which could consulted for proper berm/spillway restoration. Overflow/ Spillway lead to failure of the berm. and Berms over 4 feet in height Discernable water flow through pond berm. Ongoing erosion with potential for erosion to continue. Piping Piping eliminated. Erosion potential resolved. (Recommend a Geotechnical engineer be called in to inspect and evaluate condition and recommend repair of condition. Only one layer of rock exists above native soil in area five square feet or larger, or any Emergency Emergency exposure of native soil at the Rocks and pad depth are Overflow/Spillway Overflow/Spillway top of out flow path of spillway. restored to design standards. (Rip -rap on inside slopes need not be replaced.) Erosion See "Side Slopes of Pond" RAMEngineering, Inc. RAM No. 23-035 10429 240th P/ S W SFR Stormwater Site Plan Report Page F-5 Table V-A.2: Maintenance Standards - Infiltration Maintenance Conditions When Maintenance Is Results Expected Component Defect Needed When Maintenance Is Performed See Table V-A.1: Trash & Debris See Table V-A.1: Maintenance Maintenance Standards - Detention Ponds Standards - Detention Ponds See Table V-A.1: Poisonous/Noxious See Table V-A.1: Maintenance Maintenance Vegetation Standards - Detention Ponds Standards - Detention Ponds General See Table V-A.1: Contaminants and See Table V-A.1: Maintenance Maintenance Pollution Standards - Detention Ponds Standards - Detention Ponds See Table V-A.1: Rodent Holes See Table V-A.1: Maintenance Maintenance Standards - Detention Ponds Standards - Detention Ponds Water ponding in infiltration pond after rainfall ceases and appropriate time allowed for infiltration. Treatment basins should infiltrate Water Quality Design Storm Volume within 48 hours, Sediment is removed and empty within 24 hours after and/or facility is Storage Area Sediment cessation of most rain events. cleaned so that infiltration system works according to (A percolation test pit or test of facility design. indicates facility is only working at 90% of its designed capabilities. Test every 2 to 5 years. If two inches or more sediment is present, remove). Filter Bags (if Filled with Sediment Sediment and debris fill bag more than Filter bag is replaced applicable) and Debris 1/2 full. or system is redesigned. By visual inspection, little or no water Gravel in rock filter is Rock Filters Sediment and Debris flows through filter during heavy rain replaced. storms. Side Slopes of Erosion See Table V-A.1: Maintenance See Table V-A.1: Pond Standards - Detention Ponds Maintenance RAMEngineering, Inc. RAM No. 23-035 10429 240th P/ S W SFR Stormwater Site Plan Report Page F-6 Table V-A.2: Maintenance Standards - Infiltration Maintenance Conditions When Maintenance Is Results Expected Component Defect Needed When Maintenance Is Performed Standards - Detention Ponds See Table V-A.1: Tree Growth See Table V-A.1: Maintenance Maintenance Standards - Detention Ponds Standards - Detention Ponds Emergency Overflow Spillway and Berms over 4 feet in height. See Table V-A.1: Piping See Table V-A.1: Maintenance Maintenance Standards - Detention Ponds Standards - Detention Ponds See Table V-A.1: Rock Missing See Table V-A.1: Maintenance Maintenance Standards - Detention Ponds Standards - Detention Ponds Emergency Overflow Spillway See Table V-A.1: Erosion See Table V-A.1: Maintenance Maintenance Standards - Detention Ponds Standards - Detention Ponds Pre -settling Ponds Facility or sump filled 6" or designed sediment trap depth of and Vaults with Sediment and/or sediment. Sediment is removed. debris Table V-A.S: Maintenance Standards - Catch Basins Maintenance Results Expected When Component Defect Conditions When Maintenance is Needed Maintenance is performed Trash or debris which is located immediately in front of the catch basin opening or is blocking inletting capacity No Trash or debris of the basin by more than 10%. located immediately in front of catch basin or on Trash or debris (in the basin) that exceeds 60 percent of grate opening. the sump depth as measured from the bottom of basin General to invert of the lowest pipe into or out of the basin, but in No trash or debris in the Trash & Debris no case less than a minimum of six inches clearance catch basin. from the debris surface to the invert of the lowest pipe. Inlet and outlet pipes free Trash or debris in any inlet or outlet pipe blocking more of trash or debris. than 1/3 of its height. No dead animals or Dead animals or vegetation that could generate odors vegetation present within that could cause complaints or dangerous gases (e.g., the catch basin. methane). RAM E, . RAM No. 23-035 10429 240th P/ S W SFR Stormwater Site Plan Report Page F-7 Table V-A.S: Maintenance Standards - Catch Basins Maintenance Results Expected When Component Defect Conditions When Maintenance is Needed Maintenance is performed Sediment (in the basin) that exceeds 60 percent of the sump depth as measured from the bottom of basin to invert of the lowest pipe into or out of the basin, but in No sediment in the catch Sediment no case less than a minimum of 6 inches clearance from basin the sediment surface to the invert of the lowest pipe. Top slab has holes larger than 2 square inches or Top slab is free of holes cracks wider than 1/4 inch. (Intent is to make sure no and cracks. Structure Damage material is running into basin). to Frame and/or Top Slab Frame not sitting flush on top slab, i.e., separation of Frame is sitting flush on more than 3/4 inch of the frame from the top slab. the riser rings or top slab and firmly attached. Frame not securely attached Maintenance person judges that structure is unsound. Basin replaced or Fractures or Grout fillet has separated or cracked wider than 1/2 inch repaired to design standards. Cracks in Basin and longer than 1 foot at the joint of any inlet/outlet pipe Walls/ Bottom or any evidence of soil particles entering catch basin Pipe is regrouted and through cracks. secure at basin wall. Settlement/ If failure of basin has created a safety, function, or Basin replaced or repaired to design Misalignment design problem. standards. Vegetation growing across and blocking more than 10% No vegetation blocking of the basin opening. opening to basin. Vegetation Vegetation growing in inlet/outlet pipe joints that is more No vegetation or root than six inches tall and less than six inches apart. growth present. Contamination and See Table V-A.1: Maintenance Standards - Detention No pollution present. Ponds Pollution Cover Not in Place Cover is missing or only partially in place. Any open Cover/grate is in place, meets design standards, catch basin requires maintenance. and is secured Locking Mechanism cannot be opened by one maintenance Mechanism opens with Catch Basin Mechanism Not person with proper tools. Bolts into frame have less than proper tools. Cover Working 1/2 inch of thread. One maintenance person cannot remove lid after Cover Difficult to applying normal lifting pressure. Cover can be removed by Remove (Intent is keep cover from sealing off access to one maintenance person. maintenance.) Ladder Rungs Ladder is unsafe due to missing rungs, not securely Ladder meets design standards and allows Ladder Unsafe attached to basin wall, misalignment, rust, cracks, or maintenance person safe sharp edges. access. Grate opening Grate with opening wider than 7/8 inch. Grate opening meets Unsafe design standards. Trash and Debris Trash and debris that is blocking more than 20% of Grate free of trash and Metal Grates (If grate surface inletting capacity. debris. Applicable) Grate is in place, meets Damaged or Grate missing or broken member(s) of the grate. the design standards, and Missing. is installed and aligned with the flow path. RAMEngineering, Inc. RAM No. 23-035 10429 240th P/ S W SFR Stormwater Site Plan Report Page F-8 ENGINEERING, INC. Civil Engineering /Land Planning