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Geotech Report Revised 3-21-18.pdfLIU & ASSOCIATES, INC. Geotechnical Engineering Engineering Geology Earth Science August 4, 2016 (Revised 3/21/2018) Mr. Mike Mietzner Mietzner Home Builders, LLC_. C41F^�Y COPY 11611 Airport Road, Suite B-1 Everett, WA 98204 Dear Mr. Mietzner: RFSUB Subject: Geotechnical Investigation and Infiltration Tests AUG Z 9 ?.018 Mietzner Plat v'LDING DLpAR CITY Op FONDS N f 8609/8611/8615 - 244th Street SW Edmonds, Washington L&A Job No. 16-117 INTRODUCTION We understand that the development a 16-lot plat residential project is proposed for the subject property located at the above addresses in Edmonds, Washington. At your request, we have completed a preliminary geotechnical investigation for the subject project. The purpose of this investigation is to explore and characterize subsurface (soil and groundwater) conditions of the project site and evaluate feasibility of onsite stormwater disposal. Presented in this report are our findings of subsurface conditions and recommendations for onsite stormwater disposal. PROJECT DESCRIPTION A three-story, above -grade, wood -framed, single-family residence is to be constructed on each of the lots. The residence structures are to be supported on perimeter concrete stemwalls, interior load -bearing walls, beams, and columns. The lots are to be accessed 19213 Kenlake Place NE - Kenmore, Washington 98028 Phone (425) 483-9134 - Fax (425) 486-2746 August 4, 2016 (Revised 3/21/2018) Mietzncr Plat L&A Job No. 16-117 Page 2 from 244th Street SW via a paved driveway entering the south side of and traversing northward into the interior of the site, with a hammerhead at the north end of this driveway. SITE CONDITIONS SURFACE CONDITION The general location of the project site is shown on Plate 1 — Vicinity Map, attached hereto. The site is situated on a gentle, southerly -declining slope. Within the site, the ground is very gently sloped. It is bounded by 2440' Street SW to the south and adjoined by residential development to the north, east, and west. The project site is a rectangle - shaped land elongated in the north -south direction. The townhomes are to be accessed via an access road with porous pavement. GEOLOGIC SETTING The Geologic Map of the Edmonds East and Part of the Edmonds West Quadrangles Washin ton, by James P. Minard, published by U. S. Geological Survey in 1983, was referenced for the geologic and soil conditions at the project site. According to this publication, the surficial soil unit at and in the vicinity of the site is mapped as Vashon Till (Qvt) deposits. The geology of the Puget Sound Lowland has been modified by the advance and retreat of several glaciers in the past one million years or so and the subsequent deposits and erosions. The latest glacier advanced to the Puget Sound Lowland is referred to as the LIU & ASSOCIATES, INC. August 4, 2016 (Revised 3/21/2018) Mietzner Plat L&A Job No. 16-117 Page 3 Vashon Stade of the Fraser Glaciation which had occurred during the later stages of the Pleistocene Epoch, and retreated from the region some 12,500 years ago. The deposits of the Vashon till soil unit were plowed directly under glacial ice during the most recent glacial period as the glacier advanced over an eroded, irregular surface of older formations and sediments. This soil unit is composed of a mixture of unsorted clay, silt, sand, gravel, and scattered cobbles and boulders. The Vashon till soil over the top two to four feet is normally weathered to a medium -dense state, and is moderately permeable and compressible. The underlying fresh till soil, commonly referred to as "hard pan", is very -dense and weakly -cemented. The fresh till soil possesses a compressive strength comparable to that of low-grade concrete and can remain stable on steep natural slopes or man -make cuts for a long period. The fresh till deposits can provide excellent foundation support with little or no settlement, but are of extremely low permeability and would hardly allow stormwater to seep through. SOIL CONDITION Subsurface conditions of the project site were explored with three backhoe test pits excavated on August 1, 2016, with a tire -mounted backhoe to depths of 7.5 and 9.0 feet. The approximate locations of the test pits are shown on Plate 2 - Site and Exploration Location Plan. The test pits, designated as TP-1, TP-2 and TP-3, were located with either a tape measure or by visual reference to existing topographic features in the field and on the topographic survey map, and their locations should be considered as only accurate to the measuring method used. LIU & ASSOCIATES, INC. August 4, 2016 (Revised 3/21/2018) Mietzncr Plat L&A Job No. 16-117 Page 4 A geotechnical engineer from our office was present during subsurface exploration, examined the soil and geologic conditions encountered, and completed logs of test pits. Soil samples obtained from each soil layer in the test pits were visually classified in general accordance with United Soil Classification System, a copy of which is presented on Plate 3. Detailed descriptions of soils encountered during site exploration are presented in test pit logs on Plates 4 and 5. The test pits encountered a layer of topsoil, about 8 to 12 inches thick, mantling the site. The topsoil is underlain by a layer of weathered soil of light -brown to brown, medium - dense, silty fine sand with trace to some gravel, about 2.3 to 3.5 feet thick. Underlying the weathered soil is underlain to the depths explored by a glacial till deposit of light -gray, very -dense, cemented, gravelly, silty, fine sand with occasional cobble. GROUNDWATER CONDITION Groundwater was not encountered in any of the three test pits excavated on the site. The very -dense, cemented, glacial till deposit underlying the site at shallow depth is of extremely low permeability and would hardly allow stormwater to seep through. This till deposit would perch stormwater infiltrating into the more permeable surficial soils. The amount of and the depth to the near -surface perched groundwater would fluctuate seasonally, depending on precipitation, surface runoff, ground vegetation cover, site utilization, and other factors. The perched groundwater would accumulate and rise in the wet winter months and may dry up completely during the dryer summer months. The project is in a local highland with a relatively small drainage basin. Therefore, groundwater under the site would be limited. LIU & ASSOCIATES, INC. August 4, 2016 (Revised 3/21/2018) Mictmer Plat L&A Job No. 16-117 Page 5 ONSITE STORMWATER DISPOSAL RECOMMENDATIONS General Low Impact Development (LID) methods for onsite stormwater disposal, include storage and reuse, splash blocks, surface dispersion, infiltration trenches, rain gardens (bio- retention cells), porous pavement may be considered for onsite stormwater disposal. These methods are discussed below. Storage and Reuse Roof runoff may be stored in cisterns or barrels during rainstorms. Water stored may be used later for watering plants and irrigating lawns. Splash Blocks The proposed residences are of limited total impervious area. Therefore, using splash blocks under roof downspouts to spread roof runoff onto grass covered yards would be sufficient to dispose roof runoff. Downspouts should be extended to at least 6 feet away from the structures where splash blocks are placed to create sheet flow onto the yards. The yards should be re -graded as necessary to allow disposed stormwater to flow away from the townhomes. Infiltration Trenches The project site is underlain at shallow depth by a very -dense, cemented, glacial till deposit of extremely low permeability. Therefore, using infiltration trenches or rain gardens to dispose stormwater solely by infiltration would require a large infiltration bottom area, will be inefficient and may not work well. If used, infiltration trenches LIU & ASSOCIATES, INC. August 4, 2016 (Revised 3/21/2018) Mietzner Plat L&A Job No. 16-117 Page 6 installed into till soil should be sized based on a design infiltration rate of 0.15 iph (inches per hour). Infiltration trenches should be located on the downhill side of adjacent structures, and should be set back at least 5 feet from property lines and 10 feet from nearby structure foundations or utility trenches. Also, the trench bottom should be at least 12 inches lower than the adjacent footing foundations and utility trenches. The tightlines conveying stormwater into infiltration trenches should have sufficient grade (1% minimum) to generate flow by gravity. Tightlines conveying stormwater into infiltration trenches should have sufficient gradient (1% minimum) to generate flow by gravity. A clay or lean concrete dam should be constructed in the tightline trenches to form an impermeable barrier to keep water in infiltration trenches from flowing backward to adjacent structures or utility trenches. The side walls (but not the bottom) of the infiltration trenches should be lined by a layer of non -woven filter fabric (Mirafi 140NS). The trenches are then filled with clean, 3/4 to 1-1/2 inch washed gravel to within about 12 inches of the finish grade. The dispersing pipes, consisting of 4-inch, perforated PVC pipes, spaced at no more than 4 feet on centers, should be embedded in the gravel fill at about 2 feet below top of trenches. The top of the gravel fill should then be covered with the same filter fabric and the remaining trenches filled with onsite clean sandy soil. Infiltration trenches, if installed under access road should have gravel fill placed in 10-inch lifts with each lift densified to a non - yielding state with a vibratory mechanical compactor. LIU & ASSOCIATES, INC. August 4, 2016 (Revised 3/21/2018) Mietzner Plat L&A Job No. 16-117 Page 7 Rain Gardens (Bio-retention Cells) In addition to infiltration, rain gardens may also rely on evaporation into the air and absorption by vegetation roots for stormwater disposal. Rain gardens should be about 3 feet deep with their bottom cut into weathered soil. If used, rain gardens installed into glacial till soil should be sized based on a design infiltration rate of 0.15 iph (inches per hour). Rain gardens should be located on the downhill side of adjacent structures and should be set back at least 5 feet from property lines and 10 feet from adjacent structure foundations and utility trenches. Tightlines conveying stormwater into rain gardens should have sufficient gradient (1% minimum) to generate flow by gravity. A clay or lean concrete dam should be constructed in the tightline trenches to form an impermeable barrier to keep water from flowing backward to adjacent structures. Soil samples should be obtained from the soil stratum into which stormwater is to be disposed for cation exchange rate to determine whether the soil stratum has sufficient rate to purify pollutant. If not, rain garden ponds (and infiltration trenches) should be lined with a layer of amended soil at least 18 inches thick. The amended soil should consist of adequate compost mixed with clean medium to coarse sand to achieve an organic content of at least 10% by dry weight. Rain garden ponds should be vegetated for erosion control and the vegetation should be fully established before the ponds can be put in use for stormwater disposal. Planted vegetation should be tolerant of ponding water and saturated soil conditions in the winter months and drought in the summer months. In general, the predominant plants should be of facultative species adapted to stresses associated with wet and dry conditions. LIU & ASSOCIATES, INC. August 4, 2016 (Revised 3/21 /2018) Mietzner Plat L&A Job No. 16-117 Page 8 Typically, the plants may comprise of red twig dogwood, rushes, sedges, salmonberry and twinberry and ornamentals such as royal ferns, big -leaved ligularias or various primroses. Surface Dispersion Runoff over roofs and paved driveways may be disposed onsite by surface dispersion. A surface dispersion system should consist of a distribution trench and a vegetated flowpath on the downhill side of the houses to be constructed on the lots. This method will work well only if there is sufficient open space to install this surface dispersion system on each lot. Porous Pavement General Porous pavement may be used for driveways of the proposed development to allow runoff to infiltrate into the ground. Two in -situ infiltration tests had been conducted within the footprint of the proposed access road of the project site, with the test results presented in a report titled "Infiltration tests, Mietzner Plat, 8609/8611/8615 — 244' Street SW, Edmonds, Washington," dated August 3, 2017. These tests were conducted in summer on July 3, 2017, and City of Edmonds requires that one additional infiltration test be conducted in winter. Therefore, we completed one more infiltration test on February 7, 2018, to meet city's requirement. The results of this additional infiltration test are presented in this report. This test was for the access road with porous pavement of the over which runoff is to be disposed by seeping through porous pavement and infiltrating into the subgrade soils underlying the road bed materials. LIU & ASSOCIATES, INC. August 4, 2016 (Revised 3/21/2018) Mietzner Plat L&A Job No. 16-117 Page 9 In -situ Infiltration Test The location of the additional infiltration test, designated as IT-3, is shown on Plate 2 attached hereto. The infiltration test pit was located inside the footprint of the proposed access road. The bottom of the infiltration test pit was excavated to about 19 inches deep, approximately the level of subgrade soils under the proposed access road, and was excavated into a weathered deposit of brown, silty fine sand with trace gravel. Dimensions of the infiltration test pit and the soil condition at bottom of the pits are presented in the table below: TEST PIT SIZE AND SOIL CONDITION Test Pit Description of Soil No. Size at Bottom of Test Pit IT-3 3.58' x 3.67' Brown, silty fine SAND, X 1.58' deep trace gravel The in -situ infiltration tests were conducted in accordance with the Small Pilot Test procedure outlined in Edmonds 2014 Stormwater Code. The infiltration test pit was first filled with water to about 12 inches deep for six hours to soak the soils beneath the pit. Clear tap water was used in the test. The infiltration test was then conducted in the pit in accordance with the test procedure of the stormwater code. The test results were presented in the APPENDIX attached to this report. The initial infiltration rate of the infiltration test, Isat initial, is to be corrected according to the following equation to get the design infiltration rate, KSat. Ksat = C FT x Ksat initial , where C FT = C Fv x C Ft x C Fm LIU & ASSOCIATES, INC. August 4, 2016 (Revised 3/21/2018) Mietziicr Plat L&A Job No. 16-117 Page 10 where, CF„ = factor of variability and number of locations tested, = 0.33 to 1.0 CFt = factor of uncertainty of test method, = 0.5 for small scale test, and CFm — 0.9. Use a middle value 0.65 for CFI,, thus, CFT = (0.65) (0.5) (0.9) = 0.29. The design Ksat values, shown in attached APPENDIX, were thus determined to be 0.87 iph (inch per hour) for Test IT-3. We recommend that an infiltration rate of 0.75 iph be used in design of storm runoff disposal over permeable pavement of the access road. Recommendations of Porous Pavement Road A design infiltration rate of 0.75 iph (inch per hour) may be used for design of porous pavement. A 10-inch thick layer of railroad ballast rocks (3/4 to 2-1/2 inch crushed rock) is to be placed over prepared subgrade soils and compacted to a firm condition with a vibratory compactor. The railroad road ballast rocks should be covered with a layer of non -woven filter fabric (Mirafi 140NS) and topped with a 4-inch layer of 5/8-inch crushed rock. This crushed rock base should also be compacted to a non -yielding state. The porous pavement with a minimum thickness of 4 inches should then be constructed over the crushed 5/8-inch crush rock base. LIMITATIONS This report has been prepared for the specific application to the subject project for the exclusive use by Mietzner Homes, and its associates, representatives, consultants and contractors. We recommend that this report, in its entirety, be included in the project contract documents for the information of the prospective contractors for their estimating and bidding purposes and for compliance to the recommendations in this report during LIU & ASSOCIATES, INC. August 4, 2016 (Revised 3/21/2018) Mietner Plat L&A Job No. 16-117 Page I construction. The conclusions and interpretations in this report, however, should not be construed as a warranty of the subsurface conditions. The scope of this report does not include services related to construction safety precautions and our recommendations are not intended to direct the contractor's methods, techniques, sequences or procedures, except as specifically described in this report for design considerations. Our recommendations and conclusions are based on subsurface conditions encountered in the infiltration test pit, our engineering analyses, and our experience and engineering judgment. The conclusions and recommendations are professional opinions derived in a manner consistent with the level of care and skill ordinarily exercised by other members of the profession currently practicing under similar conditions in this area. No warranty, expressed or implied, is made. The actual subsurface conditions encountered during construction may vary from those encountered in the test pits. The nature and extent of such variations may not become evident until construction starts. If variations occur then, we should be retained to re- evaluate the recommendations of this report, and to verify or modify them in writing prior to proceeding further with the construction work. LIMITATIONS This report has been prepared for the specific application to this project for the exclusive use by Mietzner Home Builders, LLC, and its associates, representatives, consultants and contractors. The conclusions and interpretations in this report, however, should not be construed as a warranty of subsurface conditions of the site. The scope of this investigation does not include services related to construction safety precautions and our LIU & ASSOCIATES, INC. August 4, 2016 (Revised 3/21/2018) Mietzner Plat L&A Job No. 16-117 Page 12 recommendations are not intended to direct the contractor's methods, techniques, sequences or procedures, except as specifically described in this report for design comWeratioris. All geotcchnical construction Wrk should be monitored by a geotechnical engineer during construction. CLOSURE We are pleased to be of service to you on this project. Please feel free to contact us if you have questions regarding this report or need further consultation. Five plates attached Yours very truly, LIU & ASSOCIATES, INC. J. S. (Julian) Liu, Ph.D., P.E. Principal LIU & ASSOCIATES, INC. 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MIETZNER PLAT 8615 - 24TH STREET SW G_ eotechnical Engineering _Engineering Geology • Earth Science EDMONDS, WASHINGTON JOB NO. 16-117 1 DATE 8/3/2016 1 PLATE s,`eQ,2, s�fLt�k �-r YP-) 0 TP 1-1 P 15+� �'{58' Dr"Ve .4i'sic I'-"' -5 1 11 11 I Pk � DIc� p K9 N A ,5 F 39' Itu Ic - 861s zN`I�" SF. Sw EA► -ids , u1�, R$ o'i c, dab POvG2l N,,x,�� , - o0�if,33o3looso3 -oowla33o5 too 105 oo` 1 s3o%%ool Oy 7D+dt = 3R, 00a sF 16 un;+s Sole s6 6L k 3 e, 4-Hn9 S)rtgbe f i"17 cFfoo` h.ov,,,s on ?rap" 1' 3` Slarj SFI`s -,A( �Wd,,n uH'.ts. =16 g,� U.'n Tj� of Cm-0,uJi&\ Per NBC - as. fro„r ,tetlp�K Koft N07- TO SCALE-CIIIIVKA1au,,j w IDT}}l LIU & ASSOCIATES. INC. Geotechnical Engineering • Engineering Geology • Earth Science SITE AND EXPLORATION LOCATION PLAN MIETZNER PLAT 8615 - 24TH STREET SW EDMONDS, WASHINGTON OB NO. 16-117 1 DATE 8/3/2016 I PLATE . UNIFIED SOIL CLASSIFICATION SYSTEM MAJOR DIVISIONS GROUP GROUP NAME SYMBOL GRAVEL CLEAN GW WELL -GRADED GRAVEL, FINE TO COARSE GRAVEL COARSE- MORE THAN 50% OF GRAVEL GP POORLY -GRADED GRAVEL GRAINED COARSE FRACTION GRAVEL WITH GM SILTY GRAVEL SOILS RETAINED ON NO.4 SIEVE FINES GC CLAYEY GRAVEL SAND CLEAN SW WELL -GRADED SAND, FINE TO COARSE SAND MORE THAN 50% MORE THAN 50% OF SAND SP POORLY -GRADED SAND SAND WITH SM SILTY SAND RETAINED ON THE COARSE FRACTION NO. 200 SIEVE PASSING NO.4 SIEVE FINES SC CLAYEY SAND FINE- SILT AND CLAY INORGANIC ML SILT GRAINED LIQUID LIMIT CL CLAY SOILS LESS THAN 50% ORGANIC OL ORGANIC SILT, ORGANIC CLAY MORE THAN 50% SILTY AND CLAY INORGANIC MH SILT OF HIGH PLASTICITY, ELASTIC SILT PASSING ON THE LIQUID LIMIT CH CLAY OF HIGH PLASTICITY, FAT CLAY NO. 200 SIEVE 50% OR MORE ORGANIC OH ORGANIC SILT, ORGANIC SILT HIGHLY ORGANIC SOILS PT PEAT AND OTHER HIGHLY ORGANIC SOILS NOTES: SOIL MOISTURE MODIFIERS: 1. FIELD CLASSIFICATION IS BASED ON VISUAL EXAMINATION DRY - ABSENCE OF MOISTURE, DUSTY, DRY TO OF SOIL IN GENERAL ACCORDANCE WITH ASTM D2488-83. THE TOUCH 2. SOIL CLASSIFICATION USING LABORATORY TESTS IS BASED SLIGHTLY MOIST - TRACE MOISTURE, NOT DUSTY ON ASTM D2487-83. MOIST - DAMP, BUT NO VISIBLE WATER 3. DESCRIPTIONS OF SOIL DENSITY OR CONSISTENCY ARE VERY MOIST - VERY DAMP, MOISTURE FELT TO THE TOUCH BASED ON INTERPRETATION OF BLOW -COUNT DATA, VISUAL WET - VISIBLE FREE WATER OR SATURATED, APPEARANCE OF SOILS, AND/OR TEST DATA. USUALLY SOIL IS OBTAINED FROM BELOW WATER TABLE LIU & ASSOCIATES, INC. UNIFIED SOIL CLASSIFICATION SYSTEM Geotechnical Engineering Engineering Geology • Earth Science PLATE 3 Logged By: JSL TEST PIT NO. Date: 8/1 /2016 1 Ground El. # Depth ft USCS CLASS. Soil Description Sample No. IN % Other Test _ OL Dark -brown, loose, organic, silty fine SAND, some roots, moist 1 -------- (T(iPSOI9------- _ SM Light -brown, medium -dense, silty fine SAND, some gravel, dry 2 3 SM Light -gray, very -dense, gravelly, silty, fine SAND, occasional 5 cobble, cemented, slightly -moist (VASHON TILL) 6 7 B 9 _ Test pit terminated at 9.0 ft; groundwater not encountered. 10 Logged By: JSL TEST PIT NO. Date: 8/1 /2016 OA, Ground El. t Depth ft USCS CLASS. Soil Description Sample No. w % Other Test OL Dark -brown, loose, organic, silty fine SAND, some roots, moist 1 (TOPSOIL) 2 SM Brown, medium -dense, silty fine SAND, trace gravel, moist to wet 3 4 SM Light -gray, very -dense, gravelly, silty, fine SAND, occasional s cobble, cemented, very -moist to moist (VASHON TILL) 7 8 9 10 LIU & ASSOCIATES, INC. Geotechnical Engineering - Engineering Geology • Earth Science TEST PIT LOGS MIETZNER PLAT 8615 - 24TH STREET SW EDMONDS, WASHINGTON JOB NO. 16-117 1 DATE 8/11/2016 1 PLATE 4 Logged By: JSL TEST PIT NO. Date: 8/1 /2016 3 Ground El. ± Depth ft USCS CLASS. SOII Description Sample No W % Other Test _ OL Dark -brown, loose, organic, silty fine SAND, dry 1 SM __(TOPSOIL/FILLI___ ___ __ ___ ____ Light -brown, loose, silty fine SAND, some gravel, with gravel and 2 cobble size angular rocks, glass bottles, brick fragments, dry 3 4 SM Light -gray, very -dense, gravelly, silty, fine SAND, occasional _ cobble, cemented, slightly -moist (VASHON TILL) 5 6 7 8 9 Test pit terminated at 7.5 ft; groundwater not encountered. 10 Logged By: TEST PIT NO. Date: Ground El. ± Depth ft. USCS CLASS. Soil Description Sample No. w % Other Test 1 2 3 4 5 6 7 8 9 10 LIU & ASSOCIATES, INC. Geotechnical Engineering • Engineering Geology • Earth Science TEST PIT LOGS MIETZNER PLAT 8615 - 24TH STREET SW EDMONDS, WASHINGTON JOB NO. 16-117 DATE 8/11/2016 1 PLATE 5