APPROVED STM_BLD2023-0433+Storm_Drainage_Report+4.6.2023_2.59.21_PM+3468243840 Daley Street
Single Family Residence
840 Daley Street
Edmonds, WA 98020
BLD 2023 -
Stormwater Site Plan Report
Prepared for:
Peter and Jia Tang
Date: April 4, 2023
OF AS l�
�Q \36508W�
IONn1.
-4-/3/202S
Prepared by: Rob Long, PE
RAM Fnginininring, Inr,
19109 3611 Ave W, Suite 103, Lynnwood WA 98036
(425) 678-6960 RAMengineeringinc.com
Job No. 23-002
840 Daley Street
Single Family Residence
Introduction: This summary report provides site design information for a single-family residence
at 840 Daley Street. This report includes stormwater analysis to support permit review and
approval. The property is located on the south side of Daley Street (west of 9t" Ave W), in the
southwest 1/4 of Section 24, Township 27N, Range 3E, W.M.
Site Address:
840 Daley Street
Edmonds, WA 98020
Tax Parcel Number:
00450700300002
Applicant:
Peter and Jia Tang
648 Bell Street
Edmonds, WA 98020
Phone: 206-372-2584
TABLE OF CONTENTS
SECTION PAGES
A. Project Overview.............................................................................................................................. 5
B. Existing Conditions Summary........................................................................................................... 1
C. Developed Site Hydrology................................................................................................................ 5
D. Soils Reports................................................................................................................................... 20
E. Construction SWPPPP Requirements................................................................................................ 2
F. Operation and Maintenance Guidelines............................................................................................ 5
R.4MEngineering, Inc.
RAM No. 23-002
840 Daley Street 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 0.19 acre parcel; the project is located on the south side of Daley Street (west of 91h Ave W) in the
City of Edmonds. The applicant, Peter and Jia Tang proposes to remove the existing residence and all
existing hard surface to construct a new single family residence with an attached accessory dwelling unit
(ADU) on the project 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 the entire 0.19 acres site with the removal of all existing improvements onsite. The
project will create/replace about 4,244 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 projects 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 (0.19 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. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page A-1
Minimum Requirement #4 —Preservation of Natural Drainage Systems and Outfalls. The natural flow
path and outfall of the site that generally slopes northerly is to the municipal separate storm sewer system
(MS4) within Daley Street. Daley Street is full sloped to the north and stormwater is collected along the
north gutter line and the stormwater pipe and catch basin along the north side of Daley Street. The
project will discharge to the existing MS4 within Daley Street and therefore maintain the site's natural
outfall. Additional discussion of the downstream path is included in Section C below.
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 soils and nearby slope areas (offsite to the
west) demonstrates that infiltration is a not a viable option for stormwater management onsite. The
project geotechnical evaluation recommends infiltration not be used due to reasonable concerns about
erosion and slope failure of nearby slopes. Existing slopes about 75 feet west of the subject site have been
classified as "erosion hazard" slopes.
Additionally, adequately flow length paths are not available for any dispersion type BMP. Only post
construction soil amendment and BMP detention pipe are proposed for onsite stormwater BMP. A
summary table of the project Stormwater Management BMPs are provided below.
RAMEngineering, Inc.
RAM No. 23-002
840 Daley Street 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
Limitation: Considered infeasible on slopes greater than 33
(Volume V, Chapter 11)
Yes
percent are present., BMP T5.13 shall be applied to the site
post construction.
Roofs:
BMP T5.30: Full Dispersion
Infeasibility: A viable vegetated flow path 50 or 100 feet
(Volume V, Chapter 3)
No
and less than 20% is not achievable onsite.
Infeasibility: The project geotechnical evaluation
BMP T5.10A: Downspout Full Infiltration Systems
recommends infiltration not be used due to reasonable
(Volume V, Chapter 4)
No
concerns about erosion and slope failure of nearby slopes.
Existing slopes about 75 feet west of the subject site have
been classified as "erosion hazard" slopes.
Infeasibility: The project geotechnical evaluation
BMP T5.14 Rain Gardens
recommends infiltration not be used due to reasonable
(Volume V, Chapter 11) or
No
concerns about erosion and slope failure of nearby slopes.
BMP Bioretention
Existing slopes about 75 feet west of the subject site have
(Vollumeame V, Chapter 7)
been classified as "erosion hazard" slopes.
BMP T5.106: Downspout Dispersion Systems
Infeasibility: A viable vegetated flow path 50 or 100 feet
(Volume V, Chapter 4)
No
and less than 20% is not achievable onsite.
Detention Vaults or Pipes
A detention vault/pipe is viable and proposed to meet
(Edmonds Stormwater Addendum)
Yes
Minimum Requirement No. 5.
Infeasibility: The project geotechnical evaluation
BMP T5.10C: Perforated Stub -out
recommends infiltration not be used due to reasonable
(Volume V, Chapter 4)
No
concerns about erosion and slope failure of nearby slopes.
Existing slopes about 75 feet west of the subject site have
been classified as "erosion hazard" slopes.
Other Hard Surfaces:
BMP T5.30: Full Dispersion
Infeasibility: A viable vegetated flow path 50 or 100 feet
(Volume V, Chapter 3)
No
and less than 20% is not achievable onsite.
BMP T5.10A: Full Infiltration
Infeasibility: The project geotechnical evaluation
(Volume V, Chapter 4)
recommends infiltration not be used due to reasonable
BMP T5.15: Permeable Pavement
No
concerns about erosion and slope failure of nearby slopes.
(Volume V, Chapter 5)
Existing slopes about 75 feet west of the subject site have
been classified as "erosion hazard" slopes.
BMP T5.14 Rain Gardens
Infeasibility: The project geotechnical evaluation
(Volume V, Chapter 11) or
recommends infiltration not be used due to reasonable
No
concerns about erosion and slope failure of nearby slopes.
BMP T7.30: Bioretention
Existing slopes about 75 feet west of the subject site have
(Volume V, Chapter 7)
been classified as "erosion hazard" slopes.
BMP T5.12: Sheet Flow Dispersion
Infeasibility: A viable vegetated flow path 50 or 100 feet
(Volume V, Chapter 3)
No
and less than 20% is not achievable onsite.
Detention Vaults or Pipes
A detention vault/pipe is viable and proposed to meet
(Edmonds Stormwater Addendum)
Yes
Minimum Requirement No. 5.
RAMEngineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page A-3
Parcel (Vicinity) Map:
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RAN Engineering, Inc.
RAM No. 23-002
NW-25-27-03
-----.---- WAU
840 Daley Street SFR
Stormwater Site Plan Report
Page A-4
Site Plan:
CS 1
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CITY OF EDMbNOS BLK 81
LOT 30 LOT 29 VOL. 2, IPG. 39 LOT 28
RAN Engineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page A-5
B. EXISTING CONDITIONS SUMMARY
Existing Conditions. The total site consists of 8,201 sf (0.19 acres) and is currently occupied by an existing
single-family residence, in -ground pool, and detached garage. The site's existing garage is access via an
alley along the south 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 west, south and east; and Daley
Street along the north boundary of the site (see aerial photo below).
The site generally slopes in the northerly direction at a relatively flat to moderate slopes with only 4 feet
of drop across the site (from south to north). No define drainage courses are found on -site and
stormwater runoff would sheet flow northerly. No stream or wetlands are located onsite; Shell Creek is
located about 250 feet southwest of 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 poorly graded sand with and without silt (USCS: SP-SM and SP) advance
outwash deposits. The subject site are generally consistent with Alderwood-Everett series soil. Full soils
description is included in the project's site specific geotechnical engineering study by Earth Solutions NW, LLC.
Aerial Photo (City of Edmonds GIS, 2020 photo)
RAMEngineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page B-1
C. DEVELOPED SITE HYDROLOGY:
Developed Conditions. The proposed project includes the construction of a single family residence with
an attached accessory dwelling unit, and associated driveway and utilities. All existing structures and
impervious (hard) surface onsite will be removed/replaced with the site development; landscaping and
grass lawn around the new residence will stabilize the site upon building construction.
The project proposes to create and/or replace 4,244 sf of hard surface with the complete site
development, all existing hard surface will be removed with the project site development. The following is
a summary of the proposed new/replaced hard surface areas:
Total Hard Surface to Mitigated = 4,244 sf (0.0974 ac)
Roof Area = 3,160 sf
Walkway/Patio Area = 271 sf
Driveway Area = 813 sf
Total Pervious Surface (Lawn/Landscape) = 4,077 sf (0.0936 ac)
Lot Lawn/Landscape Area = 4,077 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, and individual lot stormwater BMP
detention pipe (Edmonds Storm water Addendum Section 6.3) will be utilized to manage the project's
new/replaced hard surfaces. BMP T5.13: Post -Construction Soil Quality and Depth will be applied to the
disturbed pervious areas of the site development.
The total proposed new replaced hard surface of 4,244 sf will be mitigated with an individual lot detention
pipe systems. The onsite detention pipe systems have been sized in accordance with the Edmonds
Storm water Addendum simplified sizing approach, below is a summary of the system:
Detention Pipe Sizing Calculations:
■ Hard Surface = 4,244 sf
■ Required 36" Detention Pipe = 33.95 ft (0.008 x 4,244 sf)l
■ Provided 36" Detention Pipe = 34 ft
1. Per Edmonds Stormwater Addendum simplified sizing approach Section 6.3.1.
RAMEngineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page C-1
OLI
SOLID LOCKING LID EL.1 LOCKING
4+LID
EL. 175.30f
EMERGENCY
OVERFLOW 1 i
6" PVC
8" IE 171.72 FDE
36CPEP R£S7RICTOR
01 Aft
TEN7/ON
TANK
6" PVC
lE 169.20
2'-8" CPEP S7UB
CONNEC7ION ® 0.5%
3'-8" CPEP S7UB 2
CB TYPE I CONNECTION ® 0.5% PVC CAP ON BOTTOM
"+ WITH 0.5" ORIFICE
(SEE FLOW CONTROL
STRUCTURE DETAIL
SD-301 ON 7HIS SHEET)
CB 48" - TYPE 1I
DETENTION SYSTEM DETAIL
DETENTION SYSTEM SIZING
36" DETENTION PIPE REQUIRED
4,244 X 0.008 = 33.95 LF REO D (34 LF 36" PIPE PROPOSED)
(PER EDMONDS STORMWA7ER ADDENDUM 6.3.1)
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.
RAMEngineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page C-2
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
(SEE NOTE 1)
UNDISTURBED TURF (LAWN)
AREAS (SEE NOTE 1)
m
OPTION 1 — NO DISTURBANCE
PLANTING BEDS TURF (LAWN) AREAS
11�LflJ�fl�I�fl�IIfl�Lh�I�fl��fl�I�fl�
m
8"
UNDISTURBED
TURF/LAWN/LANDSCAPE
UNDISTURBED NATIVE SOIL
STEEP SLOPE NOTE:
AMENDED SOILS SHOULD NOT BE
INSTALLED ON FINISHED SLOPES
EXCEEDING 33%. AREAS EXCEEDING
33% SHALL BE STABILIZED PER THE
ENGINEER/GEOTECH OF RECORD.
3RASS: SEED OR SOD
1.75" OF COMPOST INCORPORATED
INTO 6.25" OF SITE SOIL (TOTAL
4MENDED DEPTH OF 9.5", FOR A
SETTLED DEPTH OF 8")
SUBSOIL SCARIFIED 4" BELOW
COMPOST AMENDED LAYER
,12" BELOW SOIL SURFACE)
OPTION 2 — AMEND IN PLACE OR STOCKPILE AND AMEND
GENERAL NOTES:
PLANTING BEDS TURF (LAWN) AREAS
1. AREAS OF NO DISTURBANCE
SHALL BE FENCED AND EXISTING
GRASS: SEED VEGETATION AND SOIL SHALL BE
OR SOD PROTECTED FROM CONSTRUCTION
1 I'1f1 �I1-1 I1 11-1 11 I IMPACTS.
I L 11L 1 I 1=1 III I I I M III 11=1 11=1 11=1 11=1 I I
I —I —I 1=1 I=1 I I—III=1 1=1 I IEl 11=1 11=1 11=1 11=1 I I
III-1I I� �I I I —I �I I1=1 III —I I I� I1=1I I� I1=1I1=1I 2. TO MEASURE SETTLED DEPTH,
II=11FI1 11=III—III—III—III II —III —III —III —III 6" IMPORTED WATER SOIL SUFFICIENTLY TO
, TOPSOIL MIX FULLY SATURATE WITHOUT
III II II —III —III II III II —
III—;ITE
III II COMPACTED CAUSING EROSION.
III= �- I— �TEI III
111=1 I —I I I I I I III-1I DEPTH)
III-III-II=III-11F111=1 6" III=111 I -11 =11 3. COMPOST SHALL MEET SPEC.
III, _I- _� =1� VA'�-1-�
II- 11 'm1 1=fj�j -I \ REQUIREMENTS IN THE 2017
IIFj�\�j_IIN '1-' SUBSOIL IS EDMONDS STORMWATER
\j II SCARIFIED 6" ADDENDUM (CHECKLIST 7).
BELOW 4. COMPACTION OF TOPSOIL (WHERE
IMPORTED REQUIRED) TO BE TO 85% (MAX)
12' \ \/\ TOPSOIL MIX OF THE MAXIMUM DRY DENSITY
OPTION 3 — IMPORT TOPSOIL PER MODIFIED PROCTOR TEST
(ASTM D 1557).
OF
EDMONDS POST CONSTRUCTION SOIL
QUALITY AND DEPTH
REVISION DATE
APRIL 2021
T PUBLIC WORKS STANDARD
DEPARTMENT DETAIL
Fs t �g9� APPROVED BY: R. ENGLISH S D - 642
R.4MEngineering, Inc. 840 Daley Street SFR
RAM No. 23-002 Stormwater Site Plan Report
Page C-3
Offsite Basin Analysis. The site is located in the Shell Creek watershed basin. The Shell Creek basin is an
urban basin that collects stormwater runoff from primarily residential areas in the City Edmonds and
ultimately discharges flows north/northwesterly to Puget Sound via the Shell Creek/Shell Creek By-pass (see
attached watershed map).
The subject site slopes north and sheet flows site runoff to the municipal separate storm sewer system
(MS4) within Daley Street. Daley Street is full sloped to the north and stormwater is collected along the
north gutter line and the stormwater pipe and catch basin (MS4) along the north side of Daley Street. The
MS4 flows westerly down Daley Street right-of-way to the base of the adjacent sloped area and then turns
north up 8t" Ave N, about 350 feet from the site. The MS4 stormwater pipe system does not discharge
directly into the Shell Creek stream; the stormwater runoff stays within a piped system that by-passes
Shell Creek. The Shell Creek By-pass system was installed in 1990 to reduce stream bank erosion and
provide additional conveyance capacity for the Shell Creek basin.
The Shell Creek By-pass system travels in a north/northwesterly direction until it eventually discharges
into the Puget Sound about 0.87 miles from the site. See the Downstream Drainage Facility Map and
Watershed Basin Map, delineating the downstream path to the discharge point to Shell Creek By-pass,
attached below.
Downstream Drainage Facility Map (City of Edmonds GIS)
PUGET SOUND -
DISCHARGE
0.87 MILES
FROM THE SITE 9 n 9
•���'� 4 na tea, ��
:m �o
•
Cep / • e b ��
J Pa i
/ - o SITE
a -
g o
O 0 L
RAMEngineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page C-4
Watershed Basin Map
FIGURE B - 1 N
CITY OF EDMONDS ,
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____-_______,N zostn'st/zoom stsw---
RAN Engineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page C-5
D. SOILS REPORTS:
1. Geotechnical Evaluation Letter
Prepared by: Earth Solutions NW, LLC
Date: March 28, 2023
Pages: 19
MAN =ngineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page D-1
March 28, 2023
ES-9040
PNT Group, LLC
5603 — 230t" Street Southwest
Mountlake Terrace, Washington 98043
Attention: Mr. Peter Tang
Subject: Geotechnical Evaluation
Proposed Single -Family Residence
840 Daley Street
Edmonds, Washington
Reference: Pacific Coast Surveys, Inc.
Topographic Survey, dated January 31, 2023
Tang Residence Option "B"
Earth
Solutions
NW«C
Earth Solutions NW LLC
Geotechnical Engineering, Construction
Observation/Testing and Environmental Services
James P. Minard
Geologic Map of the Edmonds East and Part of the Edmonds West Quadrangles
Washington, 1983
United States Department of Agriculture (USDA)
Web Soil Survey (WSS)
Department of Ecology
Stormwater Management Manual for Western Washington
Amended December 2014
City of Edmonds
Edmonds Stormwater Addendum, dated June 30, 2022
Edmonds City Code
Chapter 18.30 (Stormwater Management)
Chapter 23.80 (Geologically Hazard Areas)
Dear Mr. Tang:
As requested, Earth Solutions NW, LLC (ESNW) has prepared this geotechnical evaluation for
the proposed single-family residence. As part of our scope of services, we completed a
subsurface exploration, laboratory and engineering analyses, and prepared this written report
with our findings and recommendations for the proposed project. Based on our evaluation, the
proposed project is feasible from a geotechnical standpoint.
15365 N.E. 90th Street, Suite 100 • Redmond, WA 98052 • (425) 449-4704 0 FAX (425) 449-4711
PNT Group, LLC
March 28, 2023
Protect Description
ES-9040
Page 2
The subject site is at 840 Daley Street in Edmonds, Washington, as illustrated on the attached
Vicinity Map (Plate 1). The site consists of one tax parcel (Snohomish County parcel number
00434208101000). The site is currently developed with a single-family residence and associated
improvements. The site topography gently descends to the west; a steep slope area is located
approximately 50 to 75 feet west of the subject site.
We understand the subject site will be redeveloped with a new single-family residence and
associated improvements. Grading activities will likely include cuts of up to about four feet to
establish the planned building alignments. Site improvements will also include underground utility
installations.
We understand the proposed residential structure will consist of relatively lightly loaded wood
framing supported on conventional foundations. Based on experience with similar projects, we
anticipate wall loads will be on the order of 1 to 2 kips per linear foot, isolated footing loads will
be less than 20 kips, and we anticipate slab -on -grade loading of 150 pounds per square foot
(psf).
If the above design assumptions are incorrect or change, ESNW should be contacted to review
the recommendations in this report. ESNW should review the final design to verify the
geotechnical recommendations provided in this report have been incorporated into the plans.
Subsurface Conditions
As part of this geotechnical evaluation, an ESNW representative observed, logged, and sampled
three hand auger borings on January 31, 2023, advanced at accessible locations within the
proposed development area, using hand tools and a half -inch diameter steel T-probe to probe
the subgrade of the test holes. The approximate locations of the hand auger borings are depicted
on the Hand Auger Boring Location Plan (Plate 2). Please refer to the hand auger boring logs
provided as an attachment to this report for a more detailed description of subsurface conditions.
Representative soil samples collected at the test pit locations were analyzed in general
accordance with the Unified Soil Classification System (USCS) and USDA methods and
procedures.
Topsoil
Topsoil was observed extending to depths of approximately four to six inches below the existing
ground surface (bgs). The topsoil was characterized by dark brown color and fine organic
material.
Native Soil
Underlying the topsoil, native soil at the test pit locations was observed to consist of poorly graded
sand with and without silt (USCS: SP-SM and SP, respectively). Overall soil relative density
generally increased with depth, becoming medium dense to dense at about one to two and one-
half feet bgs.
Earth Solutions NW. LLC
PNT Group, LLC
March 28, 2023
Geologic Setting
ES-9040
Page 3
The referenced geologic map resource identifies Vashon advance outwash deposits (Qva)
across the site and transitional bed deposits (Qtb) downslope of the site to the west, near the toe
of the adjacent steep slope area. As reported on the geologic map resource, advance outwash
is characterized as mostly clean and well -stratified sand with some pebbles. Transitional bed
deposits are glacial and nonglacial deposits that occur beneath the Vashon advance outwash
and consist mostly of clay, silt, and fine to very fine sand.
The referenced WSS identifies Alderwood-urban land complex as the primary soil unit underlying
the subject site with Alderwood-Everett gravelly sandy loam mapped to the southwest of the site.
Based on our field observations, native soils on the subject site are generally consistent with
Alderwood-Everett series soil.
Groundwater
Groundwater seepage was not observed at the hand auger boring locations during the fieldwork
(January 2023). However, zones of groundwater seepage may be present deeper, particularly
near the contact with the deeper transitional bed deposits. Groundwater seepage rates and
elevations fluctuate depending on many factors, including precipitation duration and intensity, the
time of year, and soil conditions.
Geologically Hazardous Areas Assessment
As part of this geotechnical evaluation, the referenced chapter of the ECC was reviewed. Based
on our investigation and review, the following topics related to development plans and site
conditions are addressed:
Erosion Hazard Areas — ECC 23.80.020.A.
With respect to erosion hazard areas, section 23.80.020 of the ECC defines erosion hazards as
"at least those areas identified by the U.S. Department of Agriculture's Natural Resources
Conservation Service as having a `moderate to severe', `severe', or `very severe' rill and inter -rill
erosion hazard. Erosion hazard areas are also those areas impacted by shoreland and/or stream
bank erosion. Within the city of Edmonds, erosion hazard areas include:
1. Those areas of the city of Edmonds containing soils that may experience severe to very
severe erosion hazard. This group of soils includes, but is not limited to, the following
when they occur on slopes of 15 percent or greater:
a. Alderwood soils (15 to 25 percent slopes);
b. Alderwood/Everett series (25 to 70 percent slopes), and;
c. Everett series (15 to 25 percent slopes).
Earth Solutions NW. LLC
PNT Group, LLC
March 28, 2023
ES-9040
Page 4
2. Coastal and stream erosion areas which are subject to the impacts from lateral erosion
related to moving water such as stream channel migration and shoreline retreat;
3. Any area with slopes of 15 percent or greater and impermeable soils interbedded with
granular soils and springs or ground water seepage, and;
4. Areas with significant visible evidence of ground water seepage, and which also include
existing landslide deposits regardless of slope."
Based on the ECC definition, the site does not contain any erosion hazard areas; the steep slope
area approximately 50 to 75 feet west of the subject site would classify as an erosion hazard.
Landslide Hazard Areas — ECC 23.80.020.113.
With respect to landslide hazard areas, section 23.80.020 of the ECC defines landslide hazard
areas as areas potentially subject to landslides based on a combination of geologic, topographic,
and hydrologic factors. They include areas susceptible because of any combination of soil, slope
gradient, slope aspect, structure, hydrology, or other factors. Within the city of Edmonds,
landslide hazard areas specifically include:
1. Areas of ancient or historic failures in Edmonds which include all areas within the earth
subsidence and landslide hazard area as identified in the 1979 report of Robert Lowe
Associates and amended by the 1985 report of GeoEngineers, Inc., and further discussed
in the 2007 report by Landau Associates;
2. Coastal areas mapped as class U (unstable), UOS (unstable old slides) and URS
(unstable recent slides) in the Department of Ecology Washington coastal atlas;
3. Areas designated as quaternary slumps, earthflows, mudflows, or landslides on maps
published by the United States Geological Survey or Washington State Department of
Natural Resources;
4. Any slope of 40 percent or steeper that exceeds a vertical height of 10 feet over a 25-foot
horizontal run. Except for rockeries that have been engineered and approved by the
engineer as having been built according to the engineered design, all other modified
slopes (including slopes where there are breaks in slopes) meeting overall average
steepness and height criteria should be considered potential landslide hazard areas;
5. Any slope with all three of the following characteristics:
a. Slopes steeper than 15 percent;
b. Hillsides intersecting geologic contacts with relatively permeable sediment overlying a
relatively impermeable sediment, and;
c. Springs or ground water seepage.
Earth Solutions NW. LLC
PNT Group, LLC
March 28, 2023
ES-9040
Page 5
6. Any area potentially unstable as a result of rapid stream incision or stream bank erosion;
7. Any area located on an alluvial fan, presently subject to, or potentially subject to,
inundation by debris flow or deposition of stream -transported sediments, and;
8. Any slopes that have been modified by past development activity that still meet the slope
criteria.
Based on the ECC definition, the site does not contain any landslide hazard areas; the steep
slope area approximately 50 to 75 feet west of the subject site appears to classify as landslide
hazard area.
Temporary Excavations
For temporary cuts taller than four feet, we recommend sloping or benching the cuts with a 1 H:1 V
gradient. Steeper inclinations can be evaluated by ESNW during construction based on exposed
soil conditions.
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
• Loose lift thickness (maximum)
Granular soil*
At or slightly above optimum**
95 percent (Modified Proctor)
12 inches
Existing soil may not be suitable for use as structural fill unless 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.
With respect to underground utility installations and backfill, local jurisdictions may dictate the soil
type(s) and compaction requirements. Unsuitable material or debris must be removed from
structural areas if encountered.
Earth Solutions NW. LLC
PNT Group, LLC ES-9040
March 28, 2023 Page 6
Foundations
The proposed structure can be supported on conventional spread and continuous footings
bearing on undisturbed, competent native soil, compacted native soil, or new structural fill.
Competent native soils, suitable for support of the foundation, should be encountered beginning
at depths of approximately one to two and one-half feet bgs. Where loose or unsuitable soil
conditions are encountered at foundation subgrade elevations during site preparation activities,
compaction of the soils to the specifications of structural fill, or overexcavation and replacement
with granular structural fill will be necessary. Compaction of the soil to the levels necessary for
use as structural fill may be difficult during wet weather conditions. Organic material exposed at
foundation subgrade elevations must be removed and grades restored with structural fill.
Provided the structure will be supported as described above, the following parameters can be
used for design of the new foundations:
• Allowable soil bearing capacity 2,500 psf
• Passive earth pressure 300 pcf (equivalent fluid)
• Coefficient of friction 0.40
The passive earth pressure and coefficient of friction values include a safety factor of 1.5. A one-
third increase in the allowable soil bearing capacity can be assumed for short-term wind and
seismic loading conditions.
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 residential structure 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 construction of the slab.
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
PNT Group, LLC
March 28, 2023
Retaining Walls
ES-9040
Page 7
Retaining walls must be designed to resist earth pressures and applicable surcharge loads. The
following parameters may be used for 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 applicable.
** Where H equals the retained height (in feet).
35 pcf (equivalent fluid)
55 pcf
70 psf (rectangular distribution)*
300 pcf (equivalent fluid)
M1
8H psf**
A factor -of -safety of 1.5 has been applied to the passive earth pressure and coefficient of friction
values provided in this section. The above design parameters are based on a level backfill
condition and level grade at the wall toe. Revised design values will be necessary if sloping
grades are to be used above or below retaining walls. Additional surcharge loading from adjacent
foundations, sloped backfill, or other relevant loads should be included in the retaining wall
design.
Retaining walls should be backfilled with free -draining material that extends along the height of
the wall and a distance of at least 18 inches behind the wall. In lieu of 18 inches of a free draining
material, a drainage mat can be considered. ESNW should evaluate the suitability of drainage
mat application during construction. The upper 12 inches of the wall backfill may consist of a
less permeable soil, if desired. A perforated drainpipe should be placed along the base of the
wall and connected to an approved discharge location. A typical retaining wall drainage detail is
provided on Plate 3. If drainage is not provided, hydrostatic pressures should be included in the
wall design.
Seismic Design
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 with respect to earthquake loads. Based on the soil conditions encountered
at the test locations, the Site Class D is recommended for seismic design per the 2018 IBC.
Earth Solutions NW. LLC
PNT Group, LLC
March 28, 2023
Liquefaction
ES-9040
Page 8
Liquefaction is a phenomenon where saturated and loose cohesionless soil suddenly loses
internal strength and behaves as a fluid. This behavior is in response to increased pore water
pressures resulting from an earthquake or another intense ground shaking. In our opinion, site
susceptibility to liquefaction may be considered low. The depth of the regional groundwater table
and the relative density of the native soil were the primary bases for this opinion.
Drainage
Zones of perched groundwater seepage should be anticipated in site excavations depending on
the time of year grading operations take place. 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 should be designed to direct surface water away from structures and slopes.
Grades adjacent to structures and slopes should be sloped away at a gradient of at least 2
percent for a horizontal distance of up to 10 feet or the maximum allowed by adjacent structures.
In our opinion, foundation drains should be installed along building perimeter footings. A typical
footing drain detail is provided on Plate 4.
Infiltration and LID Evaluation
As indicated in the Subsurface Conditions section, native soils encountered during our fieldwork
were characterized primarily as sand. While native sand soil may exhibit a moderate to good
infiltration capacity, we do not recommend infiltrating site runoff due to the proximity to the steep
slope area to the west of the site. Based on topography and geologic mapping, attempted
infiltration would move laterally along the deeper fine-grained and pose a risk to stability of the
nearby steep slope area.
Pursuant to City of Edmonds stormwater management requirements, implementation of on -site
stormwater BMPs are required for proposed developments in accordance with specified
thresholds, standards, and lists. The intent of BMP implementation is to infiltrate, disperse, and
retain stormwater runoff on site to the extent feasible. The table below summarizes our
evaluation of low impact development methods, as outlined in the referenced stormwater manual,
from a geotechnical standpoint. It is instructed in the referenced stormwater manual that BMPs
are to be considered in the order listed (from top to bottom) for each surface type, and the first
BMP that is determined to be viable should be used. For completeness, however, we have
evaluated each listed BMP for the proposed surface types.
Earth Solutions NW. LLC
PNT Group, LLC
March 28, 2023
ES-9040
Page 9
BMP
Viable?
Limitations or
Infeasibility Criteria
Lawns and Landscaped Areas
T5.13: Post -construction soil quality
Yes
None.
and depth (Volume V, Chapter 5)
Roofs
T5.30: Full dispersion (Volume V,
Maybe*
Limitation: Adequate vegetative flow paths may not be
Chapter 5)
available.
T5.10A: Downspout full infiltration
NO
Infeasibility: Not recommended due to adjacent steep slope
systems (Volume III, Chapter 3)
area and risk of causing instability.
Roofs
Bioretention (Volume V, Chapter 7)
No
Infeasibility: Not recommended due to adjacent steep slope
area and risk of causing instability.
T5.10B: Downspout dispersion
Maybe*
Limitation: Adequate vegetative flow paths may not be
systems (Volume III, Chapter 3)
available.
T5.10C: Perforated stub -out
NO
Infeasibility: Not recommended due to adjacent steep slope
connections (Volume III, Chapter 3)
area and risk of causing instability.
T5.30: Full dispersion (Volume V,
Maybe*
Limitation: Adequate vegetative flow paths may not be
Chapter 5)
available.
T5.15: Permeable pavement
NO
Infeasibility: Not recommended due to adjacent steep slope
(Volume V, Chapter 5)
area and risk of causing instability.
Bioretention (Volume V, Chapter 7)
No
Infeasibility: Not recommended due to adjacent steep slope
area and risk of causing instability.
T5.12: Sheet flow dispersion
Limitation: Adequate vegetative flow paths may not be
T5.11: Concentrated flow dispersion
Maybe*
available.
(Volume V, Chapter 5)
* Viability to be determined by storm designer.
Limitations
This geotechnical evaluation report has been prepared for the exclusive use of Mr. Peter Tang
and his 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.
Earth Solutions NW. LLC
PNT Group, LLC
March 28, 2023
Additional Services
ES-9040
Page 10
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.
We trust this letter meets your current needs. Should you have questions, or if any additional
information is required, please call.
Sincerely,
EARTH SOLUTIONS NW, LLC
03/28/2023
Henry T. Wright, P.E.
Associate Principal Engineer
Attachments: Plate 1 — Vicinity Map
Plate 2 — Hand Auger Boring Location Plan
Plate 3 — Retaining Wall Drainage Detail
Plate 4 — Footing Drain Detail
Hand Auger Boring Logs
Grain Size Distribution
cc: RAM Engineering, Inc.
Attention: Mr. Rob Long, P.E. (Email only)
Earth Solutions NW. LLC
192nd Street Southwes
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Reference: NORTH
Earth 1
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C
Snohomish County, Washington
Observation/Testing00!
Open StreetMap.org
40
Vicinity Map
Tang Residence
Edmonds, Washington
Drawn MRS
Date 02/23/2023
Proj. No. 9040
NOTE: This plate may contain areas of color. ESNW cannot be
responsible for any subsequent misinterpretation of the information
Checked KTK
Date Feb. 2023
Plate 1
resulting from black & white reproductions of this plate.
DALEY STREET
174
r----- — cc , HA 1--��176
--�-- 17a1— • — — • IHAl2
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176
E
SPRAGUE
LEGEND
HA-1I Approximate Location of
• — ESNW Hand Auger Boring,
Proj. No. ES-9040, Jan. 2023
Subject Site
Existing Building
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.
NORTH
0 50 100 200
1 "=100' � �
Scale in Feet
Hand Auger Boring Location Plan
Tang Residence
Edmonds, Washington
NOTE: This plate may contain areas of color. ESNW cannot be Drawn MRS Date 02/23/2023 Pro' No. 9040
responsible for any subsequent misinterpretation of the information 1
resulting from black & white reproductions of this plate. Checked KTK Date Feb. 2023 Plate 2
18" Min.
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NOTES:
• Free -draining Backfill should consist
of soil having less than 5 percent fines.
Percent passing No. 4 sieve should be
25 to 75 percent.
• Sheet Drain may be feasible in lieu
of Free -draining Backfill, per ESNW
recommendations.
• Drain Pipe should consist of perforated,
rigid PVC Pipe surrounded with 1-inch
Drain Rock.
LEGEND:
ffiFree -draining Structural Backfill
o
1-inch Drain Rock
Structural
Fill
Perforated Rigid Drain Pipe
(Surround in Drain Rock)
SCHEMATIC ONLY - NOT TO SCALE
NOT A CONSTRUCTION DRAWING
Retaining Wall Drainage Detail
Tang Residence
Edmonds, Washington
Drawn MRS Date 02/23/2023 Proj. No. 9040
Checked KTK Date Feb.2023 Plate 3
Perforated Rigid Drain Pipe
(Surround in Drain Rock)
NOTES:
• Do NOT tie roof downspouts
to Footing Drain.
• Surface Seal to consist of
12" of less permeable, suitable
soil. Slope away from building.
LEGEND:
Surface Seal: native soil or
other low -permeability material
B.* - _- - - _... " - "
1-inch Drain Rock
SCHEMATIC ONLY - NOT TO SCALE
NOT A CONSTRUCTION DRAWING
Earth
Solutions
NW uc
Footing Drain Detail
Tang Residence
Edmonds, Washington
Drawn MRS Date 02/23/2023 Proj. No. 9040
Checked KTK Date Feb.2023 Plate 4
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
r Earth Solutions NW, LLC
15365 N.E. 90th Street, Suite 100
Redmond, Washington 98052
Telephone: 425-449-4704
Fax: 425-449-4711
BORING NUMBER HA-1
PAGE 1 OF 1
PROJECT NUMBER ES-9040 PROJECT NAME Tang Residence
DATE STARTED 1/31/23 COMPLETED 1/31/23 GROUND ELEVATION
DRILLING CONTRACTOR ESNW Rep LATITUDE 47.81363 LONGITUDE-122.36824
LOGGED BY KTK CHECKED BY HTW GROUND WATER LEVEL:
NOTES S7 AT TIME OF DRILLING
SURFACE CONDITIONS Grass AFTER DRILLING
_
wJ
p
0.0
w
~Lu
CO
d7
Q Z
TESTS
_
0_ O
fy
0
MATERIAL DESCRIPTION
TPSL
.`=: `. 0.3
Dark brown TOPSOIL
-
Dark brown poorly graded SAND with silt, medium dense, moist to wet
-becomes brown
SP_
-probed 8"
MC = 11.5
_
Fines = 8.9
SM
[USDA Classification: gravelly SAND]
2.5
-becomes tan, medium dense to dense, moist
-probed 4"
MC = 7.1
3.5
Hand auger boring terminated at 3.5 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.
r Earth Solutions NW, LLC
15365 N.E. 90th Street, Suite 100
Redmond, Washington 98052
Telephone: 425-449-4704
Fax: 425-449-4711
BORING NUMBER HA-2
PAGE 1 OF 1
PROJECT NUMBER ES-9040 PROJECT NAME Tang Residence
DATE STARTED 1/31/23 COMPLETED 1/31/23 GROUND ELEVATION
DRILLING CONTRACTOR ESNW Rep LATITUDE 47.8136 LONGITUDE-122.36802
LOGGED BY KTK CHECKED BY HTW GROUND WATER LEVEL:
NOTES S7 AT TIME OF DRILLING
SURFACE CONDITIONS Grass AFTER DRILLING
w
_
w
~Lu
Uj CO
TESTS
_
O
J
Q
Q z
0
0.5
SM
MC = 7.2
SP
2.5 SM
MC = 7.0 3.5
MATERIAL DESCRIPTION
Dark brown TOPSOIL (Fill)
Dark brown poorly graded SAND with silt, loose, moist
Brown poorly graded SAND with silt, medium dense, moist
-probed 8"
Test pit terminated at 3.5 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.
r Earth Solutions NW, LLC
15365 N.E. 90th Street, Suite 100
Redmond, Washington 98052
Telephone: 425-449-4704
Fax: 425-449-4711
BORING NUMBER HA-3
PAGE 1 OF 1
PROJECT NUMBER ES-9040 PROJECT NAME Tang Residence
DATE STARTED 1/31/23 COMPLETED 1/31/23 GROUND ELEVATION
DRILLING CONTRACTOR ESNW Rep LATITUDE 47.81344 LONGITUDE-122.36808
LOGGED BY KTK CHECKED BY HTW GROUND WATER LEVEL:
NOTES S7 AT TIME OF DRILLING
SURFACE CONDITIONS Grass AFTER DRILLING
_
wJ
p
0.0
w
~Lu
CO
d7
Q Z
TESTS
_
Q O
fy
0
MATERIAL DESCRIPTION
TPSL
.'—.
Dark brown TOPSOIL
0.5
Brown poorly graded SAND with silt, loose, moist
SP-
_
SM
-probed 4"
2.5
MC = 6.3
2 5
Tan poorly graded SAND, medium dense to dense, moist
SP
[USDA Classification: gravelly SAND]
MC = 5.9
3.5
Fines = 1.9
Hand auger boring terminated at 3.5 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 GRAIN SIZE DISTRIBUTION
15365 N.E. 90th Street, Suite 100
WWI Redmond, Washington 98052
Telephone: 425-449-4704
Fax: 425-449-4711
PROJECT NUMBER ES-9040 PROJECT NAME Tang Residence
U.S. SIEVE OPENING IN INCHES U.S. SIEVE NUMBERS I HYDROMETER
6 4 3 2 1 1 /23/8 3 4 6 810 1416 20 30 40 50 60 100140 200
100
95
90
85
80
75
70
65
H
cD
60
w
� 55
m
w 50
z
LL
45
z
w
40
w
a
35
30
25
20
15
10
5
0
100 10 1 0.1 0.01 0.001
GRAIN SIZE IN MILLIMETERS
COBBLES
GRAVEL
SAND
SILT OR CLAY
coarse fine
coarse medium fine
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.
Element 2: Establish Construction Access: A construction access has been delineated on the engineering
site development plans.
Element 3: Control Flow Rates: During construction silt fencing will provide attenuation of site runoff and
upon project completion and stabilization (established lawns and landscape of exposed soils).
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.
Element 5: Stabilize Soils: Soils will be stabilized per the TESC notes listed on the engineering site
development plans.
Element 6: Protect Slopes: Exposed slopes shall be stabilized per the TESC notes listed on the engineering
site development plans.
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.
Element 8: Stabilize Channels and Outlets: This element is not applicable since there are no temporary
channels or outlets proposed.
Element 9: Control Pollutants: Pollutants shall be managed as described in the TESC notes listed on the
engineering site development plans.
RAMEngineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page E-1
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 prior to discharging from the site.
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.
Element 12: Manage the Project: The owner of the site is responsible for managing the installation and
maintenance of the site BMPs.
Element 13. Protect Low Impact Development BMPs: No LID stormwater BMPs are proposed.
Conclusion: The total site disturbance area (0.19 ac.) of the project is less than one acre, thus a formal
Notice of Intent application for NPDES coverage will not be made to the Department of Ecology. 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 to the surrounding environment.
RAMEngineering, Inc.
RAM No. 23-002
840 Daley Street 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).
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 onsite detention tank system, control structure, junction catch basins, and onsite conveyance pipes
are to be privately maintained by the project residence. Maintenance shall include the removal of
sediment from the detention tank system, using a vactor truck or equally effective method. Regular
inspections of the control structure within the catch basin shall be conducted to detect if non -routine
maintenance is required due to sediment or debris blocking or clogging the fixed orifice or standpipe
inlet. Regular sediment removal from the catch basins with a vactor truck or equally effective method
shall be conducted as determined by regular inspections. Regular inspection and maintenance of the
storm filter 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. 23-002
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.
840 Daley Street SFR
Stormwater Site Plan Report
Page F-1
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.3: Maintenance Standards - Closed Detention Systems (Tanks/Vaults)
Maintenance
Results Expected
Component
Defect
Conditions When Maintenance is Needed
When Maintenance is
Performed
Plugged Air Vents
One-half of the cross section of a vent is blocked at
Vents open and
any point or the vent is damaged.
functioning.
Accumulated sediment depth exceeds 10% of the
diameter of the storage area for 1/2 length of
storage vault or any point depth exceeds 15% of
All sediment and debris
Debris and Sediment
diameter.
removed from storage
(Example: 72-inch storage tank would require
area.
cleaning when sediment reaches depth of 7 inches
for more than 1/2 length of tank.)
Storage Area
Any openings or voids allowing material to be
Joints Between
transported into facility.
All joint between
Tank/Pipe Section
(Will require engineering analysis to determine
tank/pipe sections are
sealed.
structural stability).
Tank Pipe Bent Out of
Any part of tank/pipe is bent out of shape more than
Tank/pipe repaired or
Shape
10% of its design shape. (Review required by
replaced to design.
engineer to determine structural stability).
Cracks wider than 1/2-inch and any evidence of soil
Vault replaced or
particles entering the structure through the cracks,
repaired to design
Vault Structure Includes
or maintenance/inspection personnel determines
specifications and is
Cracks in Wall, Bottom,
that the vault is not structurally sound.
structurally sound.
Damage to Frame
and/or Top Slab
Cracks wider than 1/2-inch at the joint of any
No cracks more than
inlet/outlet pipe or any evidence of soil particles
1/4-inch wide at the joint
entering the vault through the walls.
of the inlet/outlet pipe.
RAMEngineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page F-2
Table V-A.3: Maintenance Standards - Closed Detention Systems (Tanks/Vaults)
Maintenance
Results Expected
Component
Defect
Conditions When Maintenance is Needed
When Maintenance is
Performed
Cover Not in Place
Cover is missing or only partially in place. Any open
Manhole is closed.
manhole requires maintenance.
Mechanism cannot be opened by one maintenance
Locking Mechanism Not
person with proper tools. Bolts into frame have less
Mechanism opens with
Manhole
Working
than 1/2 inch of thread (may not apply to self-locking
proper tools.
lids).
Cover Difficult to
One maintenance person cannot remove lid after
Cover can be removed
Remove
applying normal lifting pressure. Intent is to keep
and reinstalled by one
cover from sealing off access to maintenance.
maintenance person.
Ladder is unsafe due to missing rungs,
Ladder meets design
Ladder Rungs Unsafe
misalignment, not securely attached to structure
standards. Allows
maintenance person
wall, rust, or cracks.
safe access.
See Table V-A.5:
See Table V-A.5: Maintenance Standards -Catch
See Table V-A.5:
Catch Basins
Maintenance Standards
Basins
Maintenance Standards
Catch Basins
Catch Basins
Table V-A.4: Maintenance Standards - Control Structure/Flow Restrictor
Maintenance
Defect
Condition When Maintenance
Results Expected When
Component
is Needed
Maintenance is Performed
Trash and Debris (Includes
Material exceeds 25% of sump
Control structure orifice is not
Sediment)
depth or 1 foot below orifice
blocked. All trash and debris
plate.
removed.
Structure is not securely
attached to manhole wall.
Structure securely attached to wall
and outlet pipe.
General
Structure is not in upright
position (allow up to 10% from
Structure in correct position.
plumb).
Structural Damage
Connections to outlet pipe are
Connections to outlet pipe are
watertight; structure repaired or
not watertight and show signs of
replaced and works as designed.
rust.
Structure has no holes other than
Any holes - other than designed
designed holes.
holes - in the structure.
Cleanout gate is not watertight
Gate is watertight and works as
or is missing.
designed.
Gate cannot be moved up and
Gate moves up and down easily
down by one maintenance
and is watertight.
Cleanout Gate
Damaged or Missing
person.
Chain/rod leading to gate is
Chain is in place and works as
missing or damaged.
designed.
Gate is rusted over 50% of its
Gate is repaired or replaced to
surface area.
meet design standards.
Control device is not working
Plate is in place and works as
Orifice Plate
Damaged or Missing
properly due to missing, out of
designed.
place, or bent orifice plate.
Obstructions
Any trash, debris, sediment, or
Plate is free of all obstructions and
vegetation blocking the plate.
works as designed.
RAMEngineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page F-3
Table V-A.4: Maintenance Standards - Control Structure/Flow Restrictor
Maintenance
Defect
Condition When Maintenance
Results Expected When
Component
is Needed
Maintenance is Performed
Any trash or debris blocking (or
Pipe is free of all obstructions and
Overflow Pipe
Obstructions
having the potential of blocking)
the overflow pipe.
works as designed.
See Table V-A.3: Maintenance
See Table V-A.3: Maintenance
See Table V-A.3: Maintenance
Manhole
Standards - Closed Detention
Standards - Closed Detention
Standards - Closed Detention
Systems (Tanks/Vaults)
Systems (Tanks/Vaults)
Systems (Tanks/Vaults)
Catch Basin
See Table V-A.5: Maintenance
See Table V-A.5: Maintenance
See Table V-A.5: Maintenance
Standards - Catch Basins
Standards - Catch Basins
Standards - Catch Basins
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
of the basin by more than 10%.
No Trash or debris
located immediately in
Trash or debris (in the basin) that exceeds 60 percent of
front of catch basin or on
the sump depth as measured from the bottom of basin
grate opening.
to invert of the lowest pipe into or out of the basin, but in
no case less than a minimum of six inches clearance
No trash or debris in the
Trash & Debris
from the debris surface to the invert of the lowest pipe.
catch basin.
Trash or debris in any inlet or outlet pipe blocking more
Inlet and outlet pipes free
than 1/3 of its height.
of trash or debris.
Dead animals or vegetation that could generate odors
No dead animals or
that could cause complaints or dangerous gases (e.g.,
vegetation present within
methane).
the catch basin.
General
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
No sediment in the catch
Sediment
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. Frame
the riser rings or top slab
and firmly attached.
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.
RAMEngineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page F-4
Table V-A.S: Maintenance Standards - Catch Basins
Maintenance
Results Expected When
Component
Defect
Conditions When Maintenance is Needed
Maintenance is
performed
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.
Washington State Department of Ecology
2019 Stormwater Management Manual for Western Washington (2019 SWMMWW)
Publication No.19-10-021
RAMEngineering, Inc.
RAM No. 23-002
840 Daley Street SFR
Stormwater Site Plan Report
Page F-5
ENGINEERING, INC.
Civil Engineering /Land Planning