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HomeMy WebLinkAboutEx_11_RS_Drainage_Report_210804_v1
Prepared for:
Zarnoor Associates, LLC
Nazim Karmali
19515 North Creek Parkway
Suite 314
Bothell, WA 98011
Prepared by:
CPH Consultants
11321-B NE 120th Street
Kirkland, WA 98034
Jamie Schroeder, PE
Adrian Smith, EIT
June 25, 2021
Technical Information Report
Harrington Redevelopment
CPH Project No. 0192-20-002
Renton, WA
EXHIBIT 11
RECEIVED
08/30/2021 jding
PLANNING DIVISION
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Harrington Redevelopment Preliminary Technical Information Report
CPH Project No. 0192-20-002 June 25, 2021
C|P|H CONSULTANTS Page 1
Preliminary Technical Information Report
FOR
HARRINGTON REDEVELOPMENT
RENTON, WA
TABLE OF CONTENTS
SECTION 1 – PROJECT OVERVIEW 2
FIGURE 1 – VICINITY MAP
FIGURE 2 – DRAINAGE INFORMATION SUMMARY FORM
SECTION 2 – CONDITIONS AND REQUIREMENTS SUMMARY 5
SECTION 3 – EXISTING SITE CONDITIONS 6
SECTION 4 – UPSTREAM SITE CONDITIONS 7
SECTION 5 – SWPPP 8
SECTION 6 – DEVELOPED SITE CONDITIONS 10
SECTION 7 – DOWNSTREAM ANALYSIS 13
SECTION 8 – OPERATIONS AND MAINTENANCE MANUAL 15
SECTION 9 – BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT 20
FIGURES
FIGURE 3 – EXISTING SITE CONDITIONS
FIGURE 4 – DEVELOPED SITE CONDITIONS
FIGURE 5 – EXISTING DRAINAGE BASINS
FIGURE 6 – DEVELOPED DRAINAGE BASINS
APPENDICES
APPENDIX A – NRCS SOILS DATA & GEOTECHNICAL REPORT
APPENDIX B – ARBORIST REPORT
APPENDIX C – WWHM REPORTS
APPENDIX D – DOWNSTREAM ANALYSIS & OFFSITE PHOTOS
APPENDIX E – PRELIMINARY WATER QUALITY DATA
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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SECTION 1 – PROJECT OVERVIEW
This Technical Information Report (TIR) is provided to describe the stormwater conditions and proposed
drainage improvements for the Harrington Redevelopment project. The project proposes to redevelop one
existing property into a five-story building with 54 residential units with retail, parking, and infrastructure
improvements within Renton, Washington. This report is provided to identify the applicable storm drainage
standards and to summarize the analyses and design provisions proposed for the project to comply with City
of Renton surface water standards. The information provided within this TIR represents the basis of design for
the storm drainage systems and surface water conditions for the project.
The vicinity map provided below as Figure 1 illustrates the general location of the project site. The site is
located at 960 Harrington Ave NE, Renton, WA 98056 in King County (KC tax parcel no. 7227801025).
More generally the site is located in a portion of the NW ¼, Section 9, Township 23 North, Range 5 East,
King County, Washington. (See Vicinity Map below).
Figure 1 – Vicinity Map
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The project site is comprised of one parcel with an area of approximately 0.67 acres. It currently consists of 2
one-story restaurants, several small structures, and parking. Several trees of varying type, age, and health
conditions exist on site. The site and surrounding parcels are zoned CV (Center Village). Figure 3 displays the
existing site conditions.
The proposed development will create a five-story building with 54 residential units along with retail and
parking. In addition, the project will construct half street frontage improvements along NE Sunset Blvd and
Harrington Ave NE including pavement narrowing, concrete curb, gutter, and sidewalk. The project will create
and/or replace a total of approximately 0.67 acres of impervious surfaces. Total site impervious coverage
for proposed individual lots is limited to 75% by the zoning designation. The proposed site plan is shown in
Figure 4.
The developed site is required to provide Enhanced Basic Water Quality treatment in addition to meeting the
Peak Rate Flow Control Standard (May 1979 Conditions) per current City of Renton surface water standards.
Water quality storm volumes are proposed to be treated with a biofilter prior to entering the city’s storm
drainage mains.
A series of catch basin inlets and underground pipes will collect and convey surface water runoff from the
rooftop and pervious and impervious surfaces to the existing stormwater system. Existing catch basins exist on
the north side of the site on NE Sunset Blvd and on the south side of the site on Harrington Ave NE.
Storm drainage controls for this project are proposed in accordance with the 2017 City of Renton Surface
Water Design Manual (CORSWDM), which is based on the 2016 King County Surface Water Design Manual
(KCSWDM) with some modifications to reflect City of Renton specific requirements.
On-site Soil Conditions
The soils of the area are characterized generally by the Natural Resource Conservation Services (NRCS) as
Ragnar-Indianola (RdC) with slopes ranging from 2% to 15%. A site-specific investigation of the existing site
geotechnical conditions was performed by Earth Solutions NW, LLC. A copy of the NRCS report is provided in
Appendix A for reference.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Figure 2 – Technical Information Report (TIR) Worksheet, 2017 Surface Water Design Manual
Part 1 PROJECT OWNER AND
PROJECT ENGINEER
Part 2 PROJECT LOCATION AND
DESCRIPTION
Project Owner: Zarnoor Associates Project Name: Harrington Redevelopment
Phone: 206-788-5644 DDES Permit #: ______________________
Address: 19515 North Creek Parkway
Suite 314
Location: Township: 23 N
Bellevue, WA 98005 Range: 5 E
Project Engineer:
Company:
Jamie Schroeder, PE
CPH Consultants
Section: 9
Phone: (425) 285-2390 Site Address: 960 Harrington Ave NE
Renton, WA 98056
Part 3 TYPE OF PERMIT APPLICATION
Part 4 OTHER REVIEWS AND PERMITS
◼ Landuse Services DFW HPA Shoreline
Subdivision / Short Subd. / UPD COE 404 Management
Building Services DOE Dam Safety Structural
M/F / Commercial / SFR FEMA Floodplain Rockery/Vault/ ____
Clearing and Grading COE Wetlands ESA Section 7
Right-of-Way Use Other _______________________________
Other:
Part 5 PLAN AND REPORT INFORMATION
Technical Information Report Site Improvement Plan (Engr. Plans)
Type of Drainage Full / Targeted / Type (circle one): Full / Modified /
Review (circle): Simplified / Large Project Simplified
Directed
Date (include revision Date (include revision
dates): 6/14/2021 dates): 6/14/2021
Date of Final: Date of Final:
Part 6 ADJUSTMENT APPROVALS
Type (circle one): Standard / Complex / Preapplication / Experimental / Blanket
Description: (include conditions in TIR Section 2)
Date of Approval: _____________________________
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Figure 2 – Technical Information Report (TIR) Worksheet, 2017 Surface Water Design Manual (cont’d.)
Part 7 MONITORING REQUIREMENTS
Monitoring Required: Yes / No Describe:
Start Date:
Completion Date:
Part 8 SITE COMMUNITY AND DRAINAGE BASIN
Community Plan: Highlands
Special District Overlays:
Drainage Basin: East Lake Washington – Renton Drainage Basin
Stormwater Requirements: Enhanced Basic Water Quality, Peak Rate Flow Control
Part 9 ONSITE AND ADJACENT SENSITIVE AREAS
River/Stream Steep Slope
Lake Erosion Hazard
Wetlands Landslide Hazard
Closed Depression Coal Mine Hazard
Floodplain Seismic Hazard
Other Habitat Protection
Part 10 SOILS
Soil Type Slopes Erosion Potential
RdC 2% - 15%
Ur 2% - 15%
High Groundwater Table (within 5 feet) Sole Source Aquifer
Other __________________ Seeps/Springs
Additional Sheets Attached
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Figure 2 – Technical Information Report (TIR) Worksheet, 2017 Surface Water Design Manual (cont’d.)
Part 11 DRAINAGE DESIGN LIMITATIONS
REFERENCE LIMITATION / SITE CONSTRAINT
Core 2 – Off-site Analysis
Sensitive/Critical Areas
LID Infeasibility
SEPA
Additional Sheets Attached
Part 12 TIR SUMMARY SHEET (provide one TIR Summary Sheet per Threshold Discharge Area)
Threshold Discharge Area:
(name or description)
24-in Surface Water Main, No. 126578
Core Requirements (all 8 apply)
Discharge at Natural Location Number of Natural Discharge Locations: 2
Offsite Analysis Level: 1 / 2 / 3 Dated: June 8, 2021
Flow Control Level: 1 / 2 / 3 or Exemption Number:
(include a facility summary sheet) Small Site BMP’s: _____________________
Conveyance System Spill containment located at:
Erosion and Sediment Control ESC Site Supervisor: TBD
Contact Phone:
After Hours Phone:
Maintenance and Operation Responsibility: Private / Public
If Private, Maintenance Log Required: Yes / No
Financial Guarantees and Liability Provided: Yes / No
Water Quality Type: Basic / Sens. Lake / Enhanced Basic / Bog
(include facility summary sheet) or Exemption No.
Landscape Management Plan: Yes / No
Special Requirements (as applicable)
Area Specific Drainage Type: CDA / SDO / MDP / BP / LMP / Shared Fac / None
Requirements Name: ________________________________
Floodplain/Floodway Delineation Type: Major / Minor / Exemption / None
100-year Base Flood Elevation (or range): _______________
Datum:
Flood Protection Facilities Description: N/A
Source Control Describe landuse: Commercial Mixed Use
(comm./industrial landuse) Describe any structural controls: N/A
Oil Control High-use Site: Yes / No
Treatment BMP: __________________________________
Maintenance Agreement: Yes / No
with whom?:
Other Drainage Structures
Describe:
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Figure 2 – Technical Information Report (TIR) Worksheet, 2017 Surface Water Design Manual (cont’d.)
Part 13 EROSION AND SEDIMNET CONTROL REQUIREMENTS
MINIMUM ESC REQUIREMENTS
DURING CONSTRUCTION
MINIMUM ESC REQUIREMENTS
AFTER CONSTRUCTION
■ Clearing Limits ■ Stabilize Exposed Surfaces
■ Cover Measures ■ Remove and restore Temporary ESC facilities
■ Perimeter Protection
■ Traffic Area Stabilization ■ Clean and remove all silt and debris, ensure
■ Sediment Retention operation of permanent facilities, restore operation
of Flow Control BMP Facilities as necessary
■ Surface Water Collection ■ Flag Limits of SAO and open space
■
■
■
Dewatering Control
Dust Control
Flow Control
preservation areas
■
■
Protection of Flow Control BMP Facilities
(existing and proposed)
Maintain BMPs/Manage Project
Other _____________________________
Part 14 STORMWATER FACILITY DESCRIPTIONS (Note: Include Facility Summary and Sketch)
Flow Control Type/Description Water Quality Type/Description
Detention ◼ Biofiltration Biofilter Vault
Infiltration Wetpool
Regional Facility Media Filtration
Shared Facility ◼ Oil Control Oil/water Separator
Small Site BMP’s Spill Control
Other Small Site BMP’s
Other
Part 15 EASEMENTS / TRACTS
Part 16 STRUCTURAL ANALYSIS
◼ Drainage Easement Cast in Place Vault
Access Easement Retaining Wall
◼ Native Growth Protection Covenant Rockery > 4’ High
Tract Structural on Steep Slope
Other Other
Part 17 SIGNATURE OF PROFESSIONAL ENGINEER
I, or a civil engineer under my supervision, have visited the site. Actual site conditions as observed were incorporated into this
worksheet and the attached technical Information Report. To the best of my knowledge the information provided here is accurate.
June 14, 2021
Signed Date
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SECTION 2 – CONDITIONS AND REQUIREMENTS SUMMARY
Compliance with Project Drainage Requirements
The storm drainage and temporary erosion control standards for the project are established by the 2017 City
of Renton Surface Water Design Manual (CORSWDM). The project must comply with all minimum requirements
1 through 9 as it proposes more than 5,000 square feet of new impervious surface coverage. The CORSWDM
specifies nine minimum requirements that are to be met for this project. Compliance and/or applicability of
each of these design standards are summarized below:
CORSWDM Core Requirements
1. Discharge at Natural Location: The project site currently slopes and drains to two different
discharge points at catch basins whose flows converge within ¼ mile downstream. On-site stormwater
will maintain this existing drainage pattern and ultimate downstream discharge in accordance with
current flow control standards.
2. Off-site Analysis: Summarized in Section 3 – Off-Site Analysis.
3. Flow Control: The project requires Peak Rate Flow Control. This standard will be achieved by
comparing the proposed and existing site conditions. Descriptions of the proposed flow control
facilities are provided in Section 4 – Flow Control and Water Quality Facility Analysis and Design.
4. Conveyance System: The project proposes to collect stormwater runoff and convey it to existing
catch basins and storm pipes. These improvements are shown in Figure 4 and described further in
Section 5 – Conveyance System Analysis and Design.
5. Erosion and Sediment Control: Temporary erosion and sediment controls are as described in Section
8 – CSWPPP Analysis and Design.
6. Maintenance and Operations: The on-site storm drainage facilities are proposed to be privately
maintained and have been designed in accordance with city of Renton surface water standards. As
such, Operations and Maintenance Manual will be provided with final engineering.
7. Financial Guarantees and Liability: A Bond Quantity Worksheet will be prepared and provided for
review and approval prior to issuance of any site work permits with the final Technical Information
Report (TIR). Approval and all financial guarantees will be provided by the developer.
8. Water Quality: Enhanced Basic Water Quality treatment is required for the proposed project. This
treatment level will be achieved by means of one biofiltration vault as shown on Figure 4 and as
described in Section 4 – Flow Control and Water Quality Facility Analysis and Design.
9. On-site BMPs: On-site BMPs are required for the proposed project. This is described further in
Section 4.
CORSWDM Special Requirements
1. Other Adopted Area-Specific Requirements: No area-specific requirements apply to this project
site.
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2. Flood Hazard Area Delineation: The limits of this project are not located within or in proximity to a
100-year floodplain.
3. Flood Protection Facilities: N/A.
4. Source Control: No additional source control is proposed or expected to be necessary.
5. Oil Control: The project is considered a high-use area and proposes an oil/water separator for the
parking garage. The water separated will then flow to the sanitary sewer system.
6. Aquifer Protection Area: The limits of this project are not located within an Aquifer Protection Area
(AFA).
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SECTION 3 – OFF-SITE ANALYSIS
Task 1: Study Area Definition and Maps
The proposed project site is located at 960 Harrington Ave NE in Renton, WA and is currently developed with
two one-story restaurants, utility structures, and a parking lot. Existing ground cover consists mostly of grass
with several trees of varying age and health. The existing site topography consists of slopes ranging from 0%
to 15%. The existing site conditions are shown in Figure 3.
Task 2: Resource Review
King County iMAP and the City of Renton (COR) Maps and GIS Data were reviewed to identify any potential
sensitive areas in the proximity of the project site.
• Wetlands: iMap does not identify any wetlands on the project site.
• Streams and 100-year Floodplain: The project site is not located in the 100-year floodplain.
• Erosion Hazard Areas: COR Maps identifies no erosion hazard areas on the project site.
• Seismic Hazard Areas: COR Maps identifies no seismic hazard areas on the project site.
• Landslide Hazard Areas: COR Maps identifies no landslide hazard area on the project site.
• Coal Mine Hazard Areas: COR Maps identifies no coal mine hazard area on the project site.
• Critical Aquifer Recharge Area: The project site is not located within a critical aquifer recharge area
per iMAP records.
• Basin Condition: iMap does not indicate any basin conditions.
• Areas Susceptible to Groundwater Contamination: iMap does not show the project site as being
susceptible to groundwater contamination.
King County iMAP was also reviewed for downstream drainage complaints. No relevant complaints were
identified.
Task 3: Field Inspection
A field inspection was performed on June 8, 2021, on a sunny day with a temperature of approximately 65
degrees.
Onsite Drainage Basin
The existing topography of the site has slopes ranging from 0% to 15%. The project site is comprised of a
single drainage basin with surface runoff traveling primarily as sheet flow over impervious areas towards the
northwest and southwest corner. The project site currently drains to two different discharge points at catch
basins whose flows converge within ¼ mile downstream. The drainage basin is comprised mostly of impervious
building and parking area, along with a small area of grass and trees. Based on visual inspection during the
site visit and survey contour data there are low points where runoff can collect on site. Low points will remain
similar to the existing low points to ensure proposed drainage patterns remain similar to existing drainage
patterns.
Task 4: Drainage System Description
Downstream Basin
Runoff from the project site sheet flows northwesterly and southwesterly before entering existing stormwater
infrastructures via off-site catch basins. The northwestern catch basin connects to the storm main located on the
south side of NE Sunset Blvd and flows west. Approximately 480 feet downstream, the main turns southwest,
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runs 397 feet under 3 properties and NE 9th Place until it reaches Ferndale Circle NE. The southwestern catch
basin connects to the storm main located on the east side of Harrington Avenue NE and flows south.
Approximately 470 feet downstream of the site at the intersection of Harrington Ave NE and NE 9th St, the
main turns to the west and runs 900 feet down NE 9th St, turns north, and runs 293 feet up Ferndale Cir NE
where it reunites with the flow from the northwest catch basin. The outlet pipe flows 233 feet west through two
properties to Edmonds Ave NE, where it joins with another surface water main. The outlet pipe runs 212 feet
west under two properties to Dayton Ave NE, past the quarter mile mark. The collected runoff generally
continues to flow northwest to Lake Washington. A downstream map and photos are attached in Appendix D.
Upstream Basin
The project site is bordered by a large grocery store to the east, apartment buildings to the south, NE Sunset
Blvd to the north, and Harrington Ave Ne to the west. Surface flow from NE Sunset Blvd and the grocery store
flow southwest along the edge of the road towards the site, entering the storm system on the south side of NE
Sunset Blvd. A portion of the east property slopes towards the site. This upstream flow-through basin has been
accounted for in the design.
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SECTION 4 – FLOW CONTROL AND WATER QUALITY FACILITY
ANALYSIS AND DESIGN
The hydrologic analysis of the runoff conditions for this project is based on drainage characteristics such as
basin area, soil type, and land use (i.e., pervious vs. impervious) in accordance with the City of Renton Surface
Water Design Manual. The Western Washington Hydraulic Model (WWHM) software was used to evaluate
the storm water runoff conditions for the project site and to design the on-site flow control facilities. The
following is a summary of the results of the analysis and the proposed drainage facility improvements for this
project.
Existing Site Hydrology
The existing site conditions are shown in Figure 3 and summarized in Table 4.1 below.
Table 4.1 – Land Use Cover, Existing Site Conditions (prior to development)
Basin ID Total Area
(AC)
Land Cover (AC)
Impervious Till Forest Pasture
North Basin 0.27 0.22 0.00 0.05
North Frontage 0.07 0.03 0.00 0.03
South Basin 0.40 0.38 0.00 0.02
South Frontage 0.12 0.11 0.00 0.01
Upstream Flow-Through 0.09 0.09 0.00 0.00
Project Basin 0.95 0.83 0.00 0.12
The Western Washington Hydraulic Model (WWHM) software was used to model the existing site hydrology
and calculate runoff peak rates. The results of the existing site runoff analysis are provided in Appendix C.
Existing site conditions were modeled as historic site (i.e., fully forested) conditions in the analysis of the pre-
developed conditions for all on-site targeted developed surfaces in accordance with CORSWDM standards
for Flow Control.
The project basin area totals 0.95 acres and consists of 0.67 acres of on-site improvements and 0.19 acres of
frontage improvements. The northern portion of the site flows to a catch basin on NE Sunset Blvd, while the
southern portion flows to a catch basin on Harrington Ave NE. For more information regarding basin areas see
Figure 5. The site’s runoff flows will need to match its existing conditions since there will be no detention for
this project. The overall flow control model was modeled in WWHM. Input and output parameters for this
model are provided in Appendix C of this report.
Developed Site Hydrology
The site is planned to be improved with roadway, storm drainage, and utility infrastructure in support of the
mixed-use development. Frontage improvements on NE Sunset Blvd and Harrington Ave NE will be completed
in accordance with city road standards as conditions with the preliminary plat approval. These improvements
include road narrowing for side parking, 8-foot planter strip, and 5-foot sidewalk.
The developed site drainage is contained within one threshold basin that contains two natural discharge
areas. These two discharges converge within ¼ mile. The offsite drainage map can be seen in Appendix D.
The developed conditions of the site were modeled using the WWHM modeling software. All the roadway,
on-site paved surfaces, and landscape areas on the site are collected and directed to the city stormwater
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system, with the exception of the parking garage. The parking garage will be treated with an oil/water
separator and discharged to the sewer system.
Fully developed conditions were modeled assuming coverage as shown on the current plans. The impervious
and pervious areas for all other areas were calculated directly by measuring the new rooftops, roadways,
and sidewalks as impervious, and grass areas as pervious. The results of the developed site runoff analysis for
the project site are summarized in Table 4.2 and more detailed land use summaries are provided in Figure 5.
Table 4.2 – Land Use Cover, Developed Site Conditions
Basin ID Total Area
(AC)
Land Cover (AC)
Impervious Till Forest Till Grass
North Basin 0.27 0.23 0.00 0.05
North Frontage 0.07 0.04 0.00 0.03
South Basin 0.40 0.34 0.00 0.06
South Frontage 0.12 0.06 0.00 0.06
Upstream Flow-Through 0.09 0.09 0.00 0.00
Project Basin 0.95 0.76 0.00 0.19
Flow Control
Compliance with the Peak Rate Control Duration Standard (Existing Conditions) is proposed for this project.
The site has been designed to have release durations match the peak flows from the 2-year and 10-year,
and 100-year event as required by Section 1.2.3 of Chapter 1 of the CORSWDM. Table 4.3 shows the pre-
developed and developed peak flows for 2-year, 10-year, and 100-year storm events.
Table 4.3 – Peak Flow Summary
Structure Land-Use
Condition
Peak Flow Rates (cfs)
2-year 10-year 100-year
Project Runoff
Pre-
Developed 0.3208 0.4637 0.6554
Developed 0.2982 0.4318 0.6111
The full WWHM results are provided in the WWHM Total Basin Peak Flows Report. Because the developed
peak flows are less than the existing peak flows, an on-site flow control facility is not required to meet the
Peak Rate Control Duration Standard.
Water Quality Design
The CORSWDM requires that all proposed projects assess the requirement to provide water quality facilities
to treat runoff of pollution-generating impervious surfaces. Storm drainage runoff from pollution generating
impervious surfaces (PGIS) will require Enhanced Water Quality treatment prior to discharge to the
downstream, off-site system. This treatment level is proposed to be achieved with a BioPod Biofilter located in
the southeast corner of the site, upstream of the off-site stormwater system.
Runoff from the pollution-generating parking area and a portion of the roof runoff will be collected and
treated using the BioPod Biofilter. Given these parameters the off-line water quality facility flow rate was
determined to be 0.0229 cfs. Table 4.8 below shows the land use conditions used for determining the water
quality flowrate for the Biopod Biofilter and the WWHM results are provided in Appendix E of this report.
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Table 4.8 – Land Use Cover, Developed Conditions for Determining the Water Quality Flowrate
Basin ID Total Area
(AC)
Land Cover (AC)
Impervious Till Forest Till Grass
WQ Basin
(Total) 0.27 0.25 0.00 0.02
The BioPod Biofilter consists of an inlet chamber for high-flow bypass and removal of gross pollutants, a
treatment chamber for filtration through StormMix engineered media, and an outlet chamber for flow
collection and discharge. A standard detail has been provided by OldCastle and can be found in Appendix
E.
On-Site BMPs
Core requirement #9 requires that all proposed projects provide on-site BMPs to mitigate the hydrologic
impacts generated by new impervious and pervious surface, existing impervious surfaces, and replaced
impervious surface. The on-site BMPs are methods to disperse, infiltrate, or otherwise reduce or prevent
development related increases in runoff at or near the sources of those increases. On-site BMPs shall be
incorporated to the maximum extent feasible per the CORSWDM.
The feasibility and applicability of full dispersion must be evaluated for all target impervious surfaces. Full
dispersion has been determined to be infeasible due to insufficient flow paths on-site.
Where full dispersion of target impervious areas is not feasible or applicable, or will cause flooding or
erosion impacts, the feasibility and applicability of full infiltration must be evaluated. Full infiltration has been
determined to be infeasible, due to the infiltration rate of 0.5, given by the geotechnical report.
All target impervious surfaces not mitigated by full dispersion or full infiltration must be mitigated to the
maximum extent feasible using one or more BMPs from the following: limited infiltration, rain gardens,
bioretention, and permeable pavement. Limited infiltration facilities, rain gardens, and bioretention do not
appear to be feasible at this time due to the available areas to place the systems and meet required
setbacks.
Permeable pavement has been determined to be feasible. Permeable pavement can be used for sidewalks. A
Geotech shall complete testing to confirm if subgrade meets minimum organic matter content and minimum
cation exchange capacity requirements or a 6” sand layer may be included in the design beneath the
permeable pavement in areas of pollution generating impervious.
All target impervious surfaces not mitigated by an aforementioned BMP must be mitigated to the maximum
extent feasible using the Basic Dispersion BMP. Basic dispersion has been determined to be infeasible due to
the available areas to place systems and meet required setbacks.
For an impervious area greater than 65% on the buildable portion of the site/lot, on-site BMPs must be
applied to 20% of the target impervious surfaces or to an impervious area equal to at least 10% of the
site/lot, whichever is less.
BMPs must be implemented, at minimum, for an impervious area equal to at least 10% of the lot for lot sizes
up to 11,000 square feet and at least 20% of the lot for lot sizes between 11,000 and 22,000 square feet.
If these minimum areas are not mitigated using feasible BMPs from above, one or more BMPs from the
following list are required to be implemented to achieve compliance: Reduced Impervious Surface Credit,
Native Growth Retention Credit and Tree Retention Credit. Native Growth Retention Credit has been
determined to be infeasible for the project due to existing site topography and lack of potential donor areas.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Harrington Redevelopment Preliminary Technical Information Report
CPH Project No. 0192-20-002 June 25, 2021
C|P|H CONSULTANTS Page 15
Tree Retention Credit has been determined to be infeasible for the project due to no trees meeting the
minimum design requirements.
The soil moisture holding capacity of new pervious surfaces shall be protected in accordance with the soil
amendment standards as detailed in Section C.2.13 of the CORSWDM. Any proposed connection of roof
downspouts to the local drainage system shall be via a perforated pipe connection as detailed in Section
C.2.11 of the CORSWDM. Both of these BMPs will be implemented with the final construction plans for the
project.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Harrington Redevelopment Preliminary Technical Information Report
CPH Project No. 0192-20-002 June 25, 2021
C|P|H CONSULTANTS Page 16
SECTION 5 – CONVEYANCE SYSTEM AND ANALYSIS AND DESIGN
Surface water collection and conveyance for the project is proposed by means of grading, grated inlets, and
below grade pipes. Building roof drains, on-site paved surfaces and landscape areas on the site are collected
and directed to the existing public stormwater system.
Conveyance analysis for the project will be performed in accordance with Chapter 4 of the CORSWDM which
requires that new and existing pipe systems be designed with sufficient capacity to convey and contain at
minimum the 25-year peak flow. The design flow rate for conveyance/backwater analysis is based on peak
100-year peak flow rates using the rational method. Developed conditions for improved tributary areas and
existing conditions for any off-site tributary areas were used for input parameters.
The storm drainage conveyance systems are illustrated in Figure 4. Conveyance backwater analysis will be
provided with final engineering.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Harrington Redevelopment Preliminary Technical Information Report
CPH Project No. 0192-20-002 June 25, 2021
C|P|H CONSULTANTS Page 17
SECTION 6 – SPECIAL REPORTS AND STUDIES
Geotechnical Engineering Study – Draft, by Earth Solutions NW, LLC, March 31, 2021
Arborist Report, by Layton Tree Consulting, LLC, April 19, 2021
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Harrington Redevelopment Preliminary Technical Information Report
CPH Project No. 0192-20-002 June 25, 2021
C|P|H CONSULTANTS Page 18
SECTION 7 – OTHER PERMITS
Construction and Grading Permits will be obtained from the City of Renton for roadway, storm drainage, and
utility improvements proposed for the infrastructure serving the development.
Design Review Approval will be obtained from the City of Renton to establish the layout of the site plan and
to ensure the proposed plat is in accordance with COR adopted standards. A Construction Permit will be
required to construct the access and utility infrastructure to serve the development.
A general Stormwater Permit from Department of Ecology is not required since the disturbed area is less than
1 acre.
The individual building permit will be required for the building structure.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Harrington Redevelopment Preliminary Technical Information Report
CPH Project No. 0192-20-002 June 25, 2021
C|P|H CONSULTANTS Page 19
SECTION 8 – CSWPPP ANALYSIS AND DESIGN
Site specific details and provisions for the temporary erosion and sediment control (ESC) facilities are
provided with the improvement plans that accompany this TIR. The proposed facilities have been selected
and sized in accordance with the recommendations provided in the CORSWDM standards. In addition to the
site-specific ESC measures, the following general Best Management Practices (BMPs) for sediment control shall
also be implemented in accordance with the provisions of the CORSWDM:
1. Clearing Limits
Construction clearing limits fence or silt fence will be installed by the contractor along the entire
project corridor to prevent disturbance of project areas not designated for construction. These
fences will be installed prior to clearing and grading activities where appropriate.
2. Cover Measures
Temporary and permanent cover measures will be provided by the contractor to protect
disturbed areas. Disturbed areas will be seeded and mulched to provide permanent cover
measure and to reduce erosion within seven days if those areas not scheduled for immediate
work.
3. Perimeter Protection
The contractor will install silt fences as indicated on the drawings prior to any up-slope clearing,
grading and trenching activities in order to reduce the transport of sediment offsite.
4. Traffic Area Stabilization
Stabilized pads of quarry spalls will be installed by the contractor at all egress points from the
project site as required to reduce the amount of sediment transported onto paved roads or other
offsite areas by motor vehicles.
5. Sediment Retention
Sediment retention will be provided by silt fencing and catch basin inlet protection at the
locations and dimensions shown on the project drawings.
6. Surface Water Control
Surface water control will include ditches, temporary culverts, check dams, and/or other inlet and
outlet protection at the locations and dimensions shown on the drawings.
7. Dust Control
Water and/or street sweeping equipment will be used by the contractor to control dust emissions
during construction operations.
8. Wet Season Requirements
If soils are exposed during the period of October 1 to March 31, the contractor will mulch and
seed or otherwise cover as much disturbed area as possible by the first week of October, in
order to provide protective ground cover for the wet season. The contractor will also conform to
the following wet season special provisions:
A. Apply cover measures to disturbed areas that are to remain unworked for more than two
days.
B. Protect stockpiles that are to remain unworked for more than 12 hours. No area is to be
left uncovered/denuded longer than 12 hours during the winter months.
C. Provide onsite stockpiles of cover materials sufficient to cover all disturbed areas.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Harrington Redevelopment Preliminary Technical Information Report
CPH Project No. 0192-20-002 June 25, 2021
C|P|H CONSULTANTS Page 20
D. Seed all areas that are to be unworked during the wet season by the end of the first
week of October.
E. Apply mulch to all seeded areas for protection.
F. Provide onsite storage of 50 linear feet of silt fence (and the necessary stakes) for every
acre of disturbed area. Straw bales are to be stockpiled onsite for use in an emergency.
G. Provide construction road and parking lot stabilization areas for all sites.
H. Provide additional sediment retention as required by the City of Renton Engineer.
I. Provide additional surface water controls as required by the City of Renton Engineer.
J. Implement construction phasing and more conservative BMPs for construction activity near
surface waters (to be evaluated).
K. Review and maintain TESC measures on a weekly basis and within 24-hours after any
runoff-producing event.
9. Sensitive Areas Restrictions
No sensitive areas are located on-site.
10. Maintenance Requirements
All ESC measures will be maintained and reviewed on a regular basis following the standard
maintenance requirements identified in the project drawings. An ESC supervisor will be
designated by the contractor and the name, address and phone number of the ESC supervisor will
be given to the City prior to the start of construction. A sign will be posted at the primary
entrance to the project site identifying the ESC supervisor and his/her phone number.
The ESC supervisor will inspect the site at least once a month during the dry season, weekly during
the wet season, and within 24 hours of each runoff-producing storm. A standard ESC maintenance
report will be used as a written record of all maintenance.
The contractor will be responsible for phasing of erosion and sediment controls during construction
so that they are coordinated with construction activities. The contractor will also be responsible for
maintenance of temporary controls during construction, including removal of accumulated
sediment, and for the removal of the controls and remaining accumulated sediment at the
completion of construction.
11. Final Stabilization
Prior to obtaining final construction approval, the site shall be stabilized, the structural ESC
measures removed, and drainage facilities cleaned. To obtain final construction approval, the
following conditions must be met:
• All disturbed areas of the site should be vegetated or otherwise permanently stabilized
in accordance with project BMPs. At a minimum, disturbed areas should be seeded and
mulched to provide a high likelihood that sufficient cover will develop shortly after final
approval. The plans include erosion control notes and specifications for hydro-seeding
and mulching disturbed areas.
• Structural measures such as silt fences, pipe slope drains, storm drain inlet protection and
sediment traps and ponds shall be removed once the proposed improvements are
complete and vegetated areas are stabilized. All permanent surface water facilities shall
be cleaned completely and restored to working order prior to removal of ESC facilities.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Harrington Redevelopment Preliminary Technical Information Report
CPH Project No. 0192-20-002 June 25, 2021
C|P|H CONSULTANTS Page 21
SECTION 9 – BOND QUANTITIES, FACILITY SUMMARIES, AND
DECLARATION OF COVENANT
All required bonds, facility summaries, and covenants will be provided prior to final approval.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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CPH Project No. 0192-20-002 June 25, 2021
C|P|H CONSULTANTS Page 22
SECTION 10 – OPERATIONS AND MAINTENANCE MANUAL
The on-site storm drainage conveyance facilities for this project will be privately maintained by the property
owner. The required BMP facilities will be privately maintained and designed in accordance with
CORSWDM. A site-specific maintenance manual for the private BMPs will be completed prior to final
recording.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Site Planning
Civil Engineering
Landscape Architecture
Project Management
Land Use Consulting
FIGURES
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
NE SUNSET BLVDHARRINGTON AVE NEΔFIGURE 3 - EXISTING SITE CONDITIONS
IN FEETPLAN
0
N
50 100101 South Wenatchee Avenue, Suite C3
Wenatchee, WA 98801 • (509) 293-7731
Site Planning • Civil Engineering
Landscape Architecture • Land Use Consulting
11321-B NE 120th Street
Kirkland, WA 98034 • (425) 285-2390
www.cphconsultants.com
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
NE SUNSET BLVDHARRINGTON AVE NEΔFIGURE 4 - DEVELOPED SITE CONDITIONS
IN FEETPLAN
0
N
50 100101 South Wenatchee Avenue, Suite C3
Wenatchee, WA 98801 • (509) 293-7731
Site Planning • Civil Engineering
Landscape Architecture • Land Use Consulting
11321-B NE 120th Street
Kirkland, WA 98034 • (425) 285-2390
www.cphconsultants.com
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
NE SUNSET BLVDHARRINGTON AVE NEΔUPSTREAM FLOW-THROUGH
0.09 AC IMP.
NORTH FRONTAGE
0.03 AC IMP
0.03 AC LAWN
SOUTH FRONTAGE
0.11 AC IMP.
0.01 AC LAWN
NORTH BASIN
0.22 AC IMP.
0.05 AC LAWN
SOUTH BASIN
0.38 AC IMP.
0.02 AC LAWN
FIGURE 5 - EXISTING DRAINAGE BASINS
IN FEETPLAN
0
N
50 100101 South Wenatchee Avenue, Suite C3
Wenatchee, WA 98801 • (509) 293-7731
Site Planning • Civil Engineering
Landscape Architecture • Land Use Consulting
11321-B NE 120th Street
Kirkland, WA 98034 • (425) 285-2390
www.cphconsultants.com
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
NE SUNSET BLVDHARRINGTON AVE NEΔUPSTREAM FLOW-THROUGH
0.09 AC IMP.
NORTH FRONTAGE
0.04 AC IMP.
0.03 AC LAWN
SOUTH FRONTAGE
0.06 AC IMP.
0.06 AC LAWN
SOUTH BASIN
0.35 AC IMP.
0.05 AC LAWN
NORTH BASIN
0.23 AC IMP.
0.05 AC LAWN
FIGURE 6 - DEVELOPED DRAINAGE BASINS
IN FEETPLAN
0
N
50 100101 South Wenatchee Avenue, Suite C3
Wenatchee, WA 98801 • (509) 293-7731
Site Planning • Civil Engineering
Landscape Architecture • Land Use Consulting
11321-B NE 120th Street
Kirkland, WA 98034 • (425) 285-2390
www.cphconsultants.com
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Site Planning
Civil Engineering
Landscape Architecture
Project Management
Land Use Consulting
APPENDIX A
GEOTECHNICAL REPORT, NRCS SOILS REPORT
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
PREPARED FOR
ZARNOOR ASSOCIATES, LLC
C/O MR. KARIM KARMALI
March 31, 2021
_________________________
Chase G. Halsen, L.G.
Project Geologist
_________________________
Keven D. Hoffmann, P.E.
Senior Project Manager
GEOTECHNICAL ENGINEERING STUDY
HARRINGTON REDEVELOPMENT
960 HARRINGTON AVENUE NORTHEAST
RENTON, WASHINGTON
ES-7282
Earth Solutions NW, LLC
15365 Northeast 90th Street, Suite 100
Redmond, Washington 98052
Phone: 425-449-4704 | Fax: 425-449-4711
www.earthsolutionsnw.comDRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
March 31, 2021
ES-7282
Zarnoor Associates, LLC
c/o Mr. Karim Karmali
19515 North Creek Parkway, Suite 314
Bothell, Washington 98011
Attention: Mr. Nazim Karmali
Dear Mr. Karmali:
Earth Solutions NW, LLC (ESNW) is pleased to present this geotechnical report to support the
design and construction of the proposed mixed-use development, currently known as the
Harrington Redevelopment. Based on the results of our investigation, the proposed
redevelopment is feasible from a geotechnical standpoint. Our study indicates the site is
underlain primarily by dense to very dense glacial till.
Based on our findings, the proposed mixed-use structure may be constructed on a conventional
continuous and spread footing foundations bearing upon competent native soil, recompacted
native soil, or new structural fill placed directly on competent native soil. Competent native soil
suitable for support of the proposed building will likely be encountered beginning at depths of
about two-and-one-half to five feet below existing grades across most of the site. Soil in the
northwest site corner was characterized as loose to medium dense during the field exploration;
accordingly, areas of native soil may need to be either mechanically recompacted or
overexcavated and replaced with suitable structural fill to establish competent and uniform soil
bearing conditions. In general, where loose or unsuitable soil conditions are exposed at
foundation subgrade elevations, compaction of the soil to the specifications of structural fill or
overexcavation and replacement with suitable structural fill will be necessary.
Full infiltration is not recommended from a geotechnical standpoint given the predominance of
dense silty sand encountered across most of the site. Sandier soils encountered near the
northwest site corner may prove feasible for limited, targeted infiltration. However, any design
would need to incorporate provisions for overflow. If infiltration is pursued, ESNW should be
contacted to provide supplementary consulting and testing services.
Pertinent geotechnical recommendations are provided in this study. We appreciate the
opportunity to be of service to you on this project. If you have any questions regarding the content
of this geotechnical engineering study, please call.
Sincerely,
EARTH SOLUTIONS NW, LLC
Chase G. Halsen, L.G.
Project Geologist DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Earth Solutions NW, LLC
Table of Contents
ES-7282
PAGE
INTRODUCTION ................................................................................. 1
General .................................................................................... 1
Project Description ................................................................. 2
SITE CONDITIONS ............................................................................. 2
Surface ..................................................................................... 2
Subsurface .............................................................................. 2
Topsoil and Fill ............................................................. 3
Native Soil ..................................................................... 3
Geologic Setting ........................................................... 3
Groundwater ................................................................. 3
Critical Areas Review ............................................................. 4
DISCUSSION AND RECOMMENDATIONS ....................................... 4
General .................................................................................... 4
Site Preparation and Earthwork ............................................. 4
Temporary Erosion Control ......................................... 4
Excavations and Slopes .............................................. 5
In-situ and Imported Soil ............................................. 5
Subgrade Preparation .................................................. 6
Wet Season Grading…………………………………...... 6
Structural Fill ................................................................ 6
Foundations ............................................................................ 7
Seismic Design ....................................................................... 7
Slab-on-Grade Floors ............................................................. 8
Retaining Walls ....................................................................... 8
Drainage................................................................................... 9
Preliminary Infiltration Feasibility ............................... 9
Utility Support and Trench Backfill ....................................... 9
LIMITATIONS ...................................................................................... 10
Additional Services ................................................................. 10 DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Earth Solutions NW, LLC
Table of Contents
Cont’d
ES-7282
GRAPHICS
Plate 1 Vicinity Map
Plate 2 Boring Location Plan
Plate 3 Retaining Wall Drainage Detail
Plate 4 Footing Drain Detail
APPENDICES
Appendix A Subsurface Exploration
Boring Logs
Appendix B Laboratory Test Results DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Earth Solutions NW, LLC
GEOTECHNICAL ENGINEERING STUDY
HARRINGTON REDEVELOPMENT
960 HARRINGTON AVENUE NORTHEAST
RENTON, WASHINGTON
ES-7282
INTRODUCTION
General
This geotechnical engineering study (study) was prepared for the proposed mixed-use project
(currently referred to as the Harrington Redevelopment), to be constructed directly southeast of
the intersection between Northeast Sunset Boulevard and Harrington Avenue Northeast, in
Renton, Washington. This study was prepared to provide geotechnical recommendations for
currently proposed development plans and included the following geotechnical services:
Borings to characterize soil and groundwater conditions.
Laboratory testing of representative soil samples collected at the boring locations.
Engineering analyses.
The following documents and maps were reviewed as part of our study preparation:
Feasibility Study for Revised Options – Surface Parking, prepared by Grouparchitect,
dated August 10, 2020.
Conceptual Site Plan for 25% Schematic Design, prepared by Grouparchitect, dated
February 4, 2021.
ALTA/NSPS Land Title Survey, prepared by Axis Survey & Mapping, Inc., dated January
7, 2020.
Online Web Soil Survey (WSS) resource, maintained by the Natural Resources
Conservation Service (NRCS) under the United States Department of Agriculture (USDA).
Geologic Map of the Renton Quadrangle, Washington, prepared by D.R. Mullineaux, 1965.
Chapter 3, Title IV of the Renton Municipal Code.DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Earth Solutions NW, LLC
Project Description
We understand the project is pursing construction of a six-story, mixed-use structure and
associated site improvements. The at-grade level will include a parking garage, retail space, and
residential accessories, and levels two through six will be apartments. Site ingress and egress
will be provided by Northeast Sunset Boulevard.
At the time of report submission, specific building load plans were not available for review. Based
on our experience with similar developments, the proposed structure will utilize a concrete
podium for at-grade level construction, with lightly loaded wood farming above. Perimeter footing
loads will likely be about 5 to 6 kips per lineal foot. Slab-on-grade loading is anticipated to be
approximately 150 pounds per square foot (psf). We anticipate grade modifications (cuts or fills)
of less than five feet will be necessary to establish design elevations.
If the above design assumptions either change or are incorrect, ESNW should be contacted to
review the recommendations provided in this report. ESNW should review final designs to
confirm that appropriate geotechnical recommendations have been incorporated into the plans.
SITE CONDITIONS
Surface
The subject site is located at the southeast corner of the Northeast Sunset Boulevard and
Harrington Avenue Northeast intersection, in Renton, Washington. The approximate site location
is depicted on Plate 1 (Vicinity Map). The irregularly shaped site consists of King County Parcel
No. 722780-1025, totaling about 0.67 acres.
The site is bordered to the north by Northeast Sunset Boulevard, to the east by a Safeway grocery
store and parking lot, to the south by an apartment building, and to the west by Harrington Avenue
Northeast. The existing topography descends to the southwest, with about six to eight feet of
elevation change across the subject site. The site is currently developed with two restaurants
(Subway and Pizza Hut) and associated improvements. Most of the site is surfaced with asphalt.
Subsurface
An ESNW representative observed, logged, and sampled the advancement of three soil borings
on February 12, 2021. The borings were completed within accessible areas of the property using
a drill rig and operators retained by our firm. The approximate locations of the borings are
depicted on Plate 2 (Boring Location Plan). Please refer to the boring logs provided in Appendix
A for a more detailed description of subsurface conditions. Representative soil samples collected
at the boring locations were analyzed in general accordance with both Unified Soil Classification
System (USCS) and USDA methods and procedures. DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Topsoil and Fill
Topsoil was not encountered at the boring locations. Given the existing level of development,
significant amount of topsoil are not expected across the site.
Silty sand fill was encountered at B-2, extending to a depth of about four-and-one-half feet below
the existing ground surface (bgs). The fill was characterized as very loose and moist. As stated
above, asphalt covers most of the ground surface across the site. Asphalt thicknesses were
about one to two inches at the boring locations.
Native Soil
Native site soil encountered at the boring locations consisted primarily of silty sand (USCS: SM).
Localized areas of poorly graded sand with silt and well-graded sand with silt (USCS: SP-SM and
SW-SM) were encountered at B-3. Native soils were primarily observed in a medium dense to
very dense and moist condition and generally exhibited an increasingly dense condition with
depth. However, the approximate upper 10 feet of soil encountered at B-3 was characterized as
loose to medium dense. Each boring location was terminated in very dense native soil and
extended to a maximum exploration depth of about 26.5 feet bgs.
Geologic Setting
The referenced geologic map resource identifies ground moraine deposits (Qgt) as underlying
the site and adjacent areas. Ground moraine deposits, otherwise known as glacial till, are
considered an unsorted mixture of sand, silt, clay, and gravel. The referenced WSS resource
identifies soils of the Ragnar-Indianola association and Urban land designations across the site
and immediately adjacent areas. The Ragnar-Indianola associations is representative of kame,
terrace, and eskers landforms, while designations of Urban land suggest historic earthwork
activities and grade modifications in the area. Based on the encountered conditions, native soils
are generally considered representative of ground moraine (glacial till) deposits in accordance
with local geologic mapping.
Groundwater
Minor perched groundwater seepage was exposed at a depth of about 10 feet bgs within B-1.
Zones of perched groundwater seepage should be expected during general earthwork activities
and will likely develop within the soil substratum depending on the time of year. Seepage rates
and elevations fluctuate depending on many factors, including precipitation duration and intensity,
the time of year, and soil conditions. In general, groundwater flow rates are higher during the
winter, spring, and early summer months.
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Earth Solutions NW, LLC
Critical Areas Review
The City of Renton GIS mapping application and Chapter 3, Title IV of the Renton Municipal Code
were reviewed to evaluate the presence of jurisdictionally recognized geologic hazards on site or
on immediately adjacent parcels. Review of these applications did not indicate the presence of
any jurisdictionally recognized geologic hazards in the area. In addition, we did not observe any
obvious indication of the presence of these hazards at surface grades or within the boring
locations.
DISCUSSION AND RECOMMENDATIONS
General
Based on the results of our investigation, construction of the proposed residential development
is feasible from a geotechnical standpoint. The primary geotechnical considerations for the
proposal are in reference to structural fill placement and compaction, established a suitable
subgrade to support the proposed mixed-use structure, foundation design, and stormwater
management recommendations.
Site Preparation and Earthwork
Initial site preparation activities will consist of installing temporary erosion control measures,
establishing grading limits, and demolishing existing improvements. Subsequent earthwork
activities will involve site grading activities, foundation preparation, and installation of
infrastructure improvements.
Temporary Erosion Control
The following temporary erosion and sediment control (TESC) Best Management Practices
(BMPs) are offered:
Temporary construction entrances and drive lanes should be constructed with at least six
inches of quarry spalls to both minimize off-site soil tracking and provide a stable access
entrance surface. A woven geotextile fabric can be placed beneath the quarry spalls to
provide greater stability, if needed.
Silt fencing should be placed around the site perimeter.
When not in use, soil stockpiles should be covered or otherwise protected. Stockpiles
should never be placed at the top of slopes, whether the slopes are native or created
through grading.
Temporary measures for controlling surface water runoff, such as interceptor trenches,
sumps, or interceptor swales, should be installed prior to beginning earthwork activities.
Dry soils disturbed during construction should be wetted to reduce dust.
When appropriate, permanent planting or hydroseeding will help to stabilize site soils.DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Additional TESC BMPs, as specified by the project civil engineer and/or as indicated on the TESC
plans, should be incorporated into construction activities. TESC measures must be upkept and
may require modification during construction to ensure proper function.
Excavations and Slopes
Based on the soil conditions observed at the boring locations, the following allowable temporary
slope inclinations, as a function of horizontal to vertical (H:V) inclination, may be used. The
applicable Federal Occupation Safety and Health Administration (OSHA) and Washington
Industrial Safety and Health Act (WISHA) soil classifications are also provided:
Loose to medium dense soil 1.5H:1V (Type C)
Areas exposing groundwater seepage 1.5H:1V (Type C)
Dense to very dense, undisturbed native soil 0.75H:1V (Type A)
Steeper temporary slope inclinations within undisturbed, very dense native soil may be feasible
based on the soil and groundwater conditions exposed within the excavations. ESNW can
evaluate the feasibility of utilizing steeper temporary slopes at the time of construction, on a case-
by-case basis. In any event, an ESNW representative should observe temporary slopes to
confirm inclinations are suitable for the exposed soil conditions and to provide additional
excavation and slope stability recommendations, as necessary.
If the recommended temporary slope inclinations cannot be achieved, temporary shoring may be
necessary to support excavations. Permanent slopes should be graded to 2H:1V (or flatter) and
planted with vegetation to enhance stability and minimize erosion potential. Permanent slopes
should be observed by ESNW prior to vegetation and landscaping.
In-situ and Imported Soil
Successful use of the on-site soil as structural fill will largely be dictated by the moisture content
at the time of placement and compaction. Based on the conditions observed during our
subsurface exploration, the on-site soil is highly moisture sensitive. Depending on the time of
year construction occurs, remedial measures (such as soil aeration) may be necessary as part
of site grading and earthwork activities. If the on-site soil cannot be successfully compacted, the
use of an imported soil may be necessary.
In our opinion, a contingency should be provided in the project budget for export of soil that cannot
be successfully compacted as structural fill, particularly if grading activities take place during
periods of extended rainfall activity. In general, soils with fines contents greater than 5 percent
typically degrade rapidly when exposed to periods of rainfall.
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Earth Solutions NW, LLC
Imported structural fill soil should consist of a well-graded, granular soil that can achieve a
suitable working moisture content. During wet weather conditions, imported soil intended for use
as structural fill should consist of a well-graded, granular soil with 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).
Subgrade Preparation
Foundation and slab subgrade surfaces should consist of competent, undisturbed native soil or
structural fill placed and compacted atop competent native soil. ESNW should observe subgrade
areas prior to placing formwork. Supplementary recommendations for subgrade improvement
may be provided at the time of construction; such recommendations would likely include further
mechanical compaction effort or overexcavation and replacement with suitable structural fill.
Wet Season Grading
Earthwork activities that occur during wet weather conditions may require additional measures to
protect structural subgrades and soils intended for use as structural fill. Site-specific
recommendations can be provided at the time of construction and may include leaving cut areas
several inches above design elevations, covering working surfaces with crushed rock, protecting
structural fill soils from adverse moisture conditions, and additional TESC recommendations.
ESNW can assist in obtaining a wet season grading permit or extension, where appropriate, if
required by the governing jurisdiction.
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. The following recommendations
are provided for soils intended for use as structural fill:
Moisture content At or slightly above optimum
Relative compaction (minimum)95 percent (per ASTM D1557)
Loose lift thickness (maximum)12 inches
Existing site soil may only be considered suitable for use as structural fill if it can achieve a
suitable moisture content at the time of placement and compaction. If the on-site soil cannot
meet the above specifications, use of an imported structural fill material will likely be necessary.
With respect to underground utility installations and backfill, local jurisdictions will likely dictate
soil type(s) and compaction requirements. DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Zarnoor Associates, LLC ES-7282
c/o Mr. Karim Karmali Page 7
March 31, 2021
Earth Solutions NW, LLC
Foundations
In our opinion, the proposed mixed-use structure may be constructed on a conventional
continuous and spread footing foundations bearing upon competent native soil, recompacted
native soil, or new structural fill placed directly on competent native soil. Competent native soil
suitable for support of the proposed building will likely be encountered beginning at depths of
about two-and-one-half to five feet bgs across most of the site. Soils encountered at B-3
(northwest corner) were characterized as loose to medium dense to a depth of about 10 feet bgs.
Loose native soil will likely need to be either mechanically recompacted or overexcavated and
replaced with suitable structural fill to establish competent and uniform soil bearing conditions.
ESNW should be on site during foundation preparation activities to further delineate areas
requiring remediation and provide additional recommendations. In general, where loose or
unsuitable soil conditions are exposed at foundation subgrade elevations, compaction of the soil
to the specifications of structural fill or overexcavation and replacement with suitable structural
fill will be necessary.
Provided the foundations will be supported as suggested, the following parameters may be used
for design:
Allowable soil bearing capacity 3,000 psf
Passive earth pressure 300 pcf (equivalent fluid)
Coefficient of friction 0.40
The above passive pressure and friction values include a factor-of-safety (FOS) of 1.5. A one-
third increase in the allowable soil bearing capacity may be assumed for short-term wind and
seismic loading conditions. With structural loading as expected, total settlement in the range of
one inch and differential settlement of about one-half inch is anticipated. Most settlement should
occur during construction when dead loads are applied.
Seismic Design
We presume the project will be vested under the 2015 International Building Code (2015 IBC),
which recognizes the American Society of Civil Engineers (ASCE) for seismic site class
definitions. Based on our exploration and evaluation, Site Class C should be used for design. If
the project will be designed under the 2018 IBC, ESNW can provide further evaluation and
coordination with the project structural engineer to determine appropriate seismic design
parameters, which may include additional geotechnical and geophysical investigation on site.
In our opinion, site susceptibility to liquefaction may be considered low. The in-situ density and
gradation of the native soil and the absence of a uniformly established, shallow groundwater table
were the primary bases for this opinion. DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Zarnoor Associates, LLC ES-7282
c/o Mr. Karim Karmali Page 8
March 31, 2021
Earth Solutions NW, LLC
Slab-on-Grade Floors
Slab-on-grade floors for the proposed mixed-use structure should be supported on competent,
firm, and unyielding subgrades. Unstable or yielding subgrade areas should be recompacted or
overexcavated and replaced with suitable structural fill prior to slab construction. A capillary
break consisting of at least four inches of free-draining crushed rock or gravel should be placed
below each 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. Vapor barriers should be made from material
specifically designed for use as a vapor barrier and should be installed in accordance with the
manufacturer’s recommendations.
Retaining Walls
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) 35 pcf (equivalent fluid)
At-rest earth pressure (restrained condition) 55 pcf
Traffic surcharge* (passenger vehicles)70 psf (rectangular distribution)
Passive earth pressure 300 pcf (equivalent fluid)
Coefficient of friction 0.40
Seismic loading condition 8H psf**
* Where applicable
** Where H equals the retained height (in feet)
The above passive pressure and friction values include a FOS of 1.5 and 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. The upper 12 inches of the wall
backfill may consist of a less permeable soil, if desired. A sheet drain may be considered in lieu
of free-draining backfill. 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. DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Zarnoor Associates, LLC ES-7282
c/o Mr. Karim Karmali Page 9
March 31, 2021
Earth Solutions NW, LLC
Drainage
Discrete zones of perched groundwater seepage should be anticipated in site excavations
depending on the time of year grading operations take place, particularly within deeper
excavations for utilities. Temporary measures to control surface water runoff and groundwater
during construction would likely involve interceptor trenches, interceptor swales, and sumps.
ESNW should be consulted during preliminary grading to both identify areas of seepage and
provide recommendations to reduce the potential for seepage-related instability.
Finish grades must be designed to direct surface drain water away from structures and slopes.
Water must not be allowed to pond adjacent to structures or slopes. In our opinion, foundation
drains should be installed along building perimeter footings. A typical foundation drain detail is
provided on Plate 4.
Preliminary Infiltration Feasibility
Full infiltration is not recommended from a geotechnical standpoint given the predominance of
dense silty sand encountered across most of the site. Sandier soils encountered near the
northwest site corner may prove feasible for limited, targeted infiltration. However, any design
would need to incorporate provisions for overflow. For feasibility and sizing considerations only,
a preliminary infiltration rate of 0.5 inches per hour may be considered for infiltration facilities
proposed near the northwest site corner.
If infiltration is pursued, ESNW should be contacted to provide supplementary consulting and
testing services. Additional services concerning infiltration feasibility would likely include in-situ
testing and soil suitability verification.
Utility Support and Trench Backfill
In our opinion, the native soil will generally be suitable for support of utilities. Remedial measures
may be necessary in some areas to provide support for utilities, such as overexcavation and
replacement with structural fill and/or placement of geotextile fabric. Groundwater seepage may
be encountered within utility excavations, and caving of trench walls may occur where
groundwater is encountered. Depending on the time of year and conditions encountered,
dewatering or temporary trench shoring may be necessary during utility excavation and
installation.
The on-site soil may only be suitable for use as structural backfill throughout the utility trench
excavations if the soil is at (or slightly above) the optimum moisture content at the time of
placement and compaction. Moisture conditioning of the soil may be necessary at some locations
prior to use as structural fill. Each section of the utility lines must be adequately supported in the
bedding material. Utility trench backfill should be placed and compacted to the structural fill
specifications previously detailed in this report or to the applicable specifications of the presiding
jurisdiction. DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Zarnoor Associates, LLC ES-7282
c/o Mr. Karim Karmali Page 10
March 31, 2021
Earth Solutions NW, LLC
LIMITATIONS
This study has been prepared for the exclusive use of Zarnoor Associates, LLC, and its
representatives. The recommendations and conclusions provided in this study 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. No warranty, express or
implied, is made. Variations in the soil and groundwater conditions observed at the boring
locations may exist and may not become evident until construction. ESNW should reevaluate
the conclusions provided in this study if variations are encountered.
Additional Services
ESNW should have an opportunity to review final project plans with respect to the geotechnical
recommendations provided in this report. ESNW should also be retained to provide testing and
consultation services during construction. DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Drwn. MRS
Checked CGH Date Mar. 2021
Date 03/29/2021 Proj. No. 7282
Plate 1
Earth Solutions NWLLC
Geotechnical Engineering,Construction
EarthSolutionsNWLLC
EarthSolutions
NW LLC Observation/Testing and Environmental Services
Vicinity Map
Harrington Redevelopment
Renton, Washington
NORTHReference:
King County, Washington
OpenStreetMap.org
NOTE: This plate may contain areas of color. ESNW cannot be
responsible for any subsequent misinterpretation of the information
resulting from black & white reproductions of this plate.
SITE
Renton
DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Plate
Proj. No.
Date
Checked By
Drwn. ByEarth Solutions NWLLCGeotechnical Engineering,ConstructionObservation/Testing and Environmental ServicesEarthSolutionsNWLLCEarthSolutionsNWLLCMRS
CGH
03/29/2021
7282
2Boring Location PlanHarrington RedevelopmentRenton, Washington
LEGEND
Approximate Location of
ESNW Test Pit, Proj. No.
ES-7282, Feb. 2021
Subject Site
Existing Building
NORTH
0 20 40 80
Scale in Feet
1"=40'
NOTE: This plate may contain areas of color. ESNW cannot be
responsible for any subsequent misinterpretation of the information
resulting from black & white reproductions of this plate.
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.
B-1
B-1
B-2
B-3
N.E. SU N SET BOULEVARDHARRI
NGTON AVENUE S.E.
340
334
340
334 DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Drwn. MRS
Checked CGH Date Mar. 2021
Date 03/29/2021 Proj. No. 7282
Plate 3
Earth Solutions NWLLCEarthSolutionsNWLLC
EarthSolutions
NW LLC Geotechnical Engineering,Construction
Observation/Testing and Environmental Services
Retaining Wall Drainage Detail
Harrington Redevelopment
Renton, Washington
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:
Free-draining Structural Backfill
1-inch Drain Rock
18" Min.
Structural
Fill
Perforated Rigid Drain Pipe
(Surround in Drain Rock)
SCHEMATIC ONLY - NOT TO SCALE
NOT A CONSTRUCTION DRAWINGDRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Drwn. MRS
Checked CGH Date Mar. 2021
Date 03/29/2021 Proj. No. 7282
Plate 4
Earth Solutions NWLLC
Geotechnical Engineering,Construction
Observation/Testing and Environmental Services
EarthSolutionsNWLLC
EarthSolutions
NW LLC
Footing Drain Detail
Harrington Redevelopment
Renton, Washington
Slope
Perforated Rigid Drain Pipe
(Surround in Drain Rock)
18" Min.
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.
1-inch Drain Rock
SCHEMATIC ONLY - NOT TO SCALE
NOT A CONSTRUCTION DRAWINGDRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Earth Solutions NW, LLC
Appendix A
Subsurface Exploration
Boring Logs
ES-7282
Subsurface conditions at the subject site were explored on February 12, 2021, by advancing
three borings using a drill rig and operators retained by our firm. The approximate locations of
the borings are illustrated on Plate 2 of this study. The boring logs are provided in this Appendix.
The borings were advanced to a maximum depth of approximately 26.5 feet bgs.
The final logs represent the interpretations of the field logs and the results of laboratory analyses.
The stratification lines on the logs represent the approximate boundaries between soil types. In
actuality, the transitions may be more gradual. DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
316.0
SS
SS
SS
SS
SS
67
67
67
100
0
22-24-31
(55)
17-28-28
(56)
14-15-20
(35)
19-26-28
(54)
50/5"
MC = 9.3%
Fines = 23.9%
MC = 6.5%
MC = 13.2%
MC = 5.3%
MC = 8.4%
SM
20.0
Brown silty SAND, medium dense, moist
-becomes gray, very dense
[USDA Classification: slightly gravelly SAND]
-becomes dense
-minor perched groundwater seepage
-increased sand content
-becomes very dense
NOTES Surface Conditions: asphalt ~1.5" to 2"
GROUND ELEVATION 336 ft
LOGGED BY CGH
DRILLING METHOD HSA
HOLE SIZE
DRILLING CONTRACTOR Geologic Drill Partners GROUND WATER LEVELS:
CHECKED BY KDH
DATE STARTED 2/12/21 COMPLETED 2/12/21
AT TIME OF DRILLING ---
AT END OF DRILLING ---
AFTER DRILLING ---
(Continued Next Page)SAMPLE TYPENUMBERDEPTH(ft)0
5
10
15
20
PAGE 1 OF 2
BORING NUMBER B-1
PROJECT NUMBER ES-7282 PROJECT NAME Harrington Redevelopment
GENERAL BH / TP / WELL - 7282.GPJ - GINT STD US.GDT - 3/31/21Earth Solutions NW, LLC
15365 N.E. 90th Street, Suite 100
Redmond, Washington 98052
Telephone: 425-449-4704
Fax: 425-449-4711
RECOVERY %BLOWCOUNTS(N VALUE)TESTS
U.S.C.S.MATERIAL DESCRIPTION
GRAPHICLOGDRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
SS 100 50/6"MC = 9.0%
Boring terminated at 20.5 feet below existing grade. Groundwater
seepage encountered at 10.0 feet during drilling. Boring backfilled with
bentonite.SAMPLE TYPENUMBERDEPTH(ft)20
PAGE 2 OF 2
BORING NUMBER B-1
PROJECT NUMBER ES-7282 PROJECT NAME Harrington Redevelopment
GENERAL BH / TP / WELL - 7282.GPJ - GINT STD US.GDT - 3/31/21Earth Solutions NW, LLC
15365 N.E. 90th Street, Suite 100
Redmond, Washington 98052
Telephone: 425-449-4704
Fax: 425-449-4711
RECOVERY %BLOWCOUNTS(N VALUE)TESTS
U.S.C.S.MATERIAL DESCRIPTION
GRAPHICLOGDRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
331.5
316.0
SS
SS
SS
SS
SS
100
100
100
100
50
1-1-1
(2)
4-14-19
(33)
50/5"
11-14-18
(32)
50/4"
MC = 14.2%
MC = 13.9%
Fines = 26.6%
MC = 8.7%
MC = 11.0%
MC = 10.7%
SM
SM
4.5
20.0
Brown silty SAND, very loose, moist (Fill)
-trace organic material
Brown silty SAND, loose, moist
[USDA Classification: slightly gravelly sandy LOAM]
-becomes gray, dense
-minor iron oxide staining
-becomes very dense
-becomes dense
-possible obstruction
-no recovery due to obstruction. Sample taken from spoils.
NOTES Surface Conditions: asphalt ~1"
GROUND ELEVATION 336 ft
LOGGED BY CGH
DRILLING METHOD HSA
HOLE SIZE
DRILLING CONTRACTOR Geologic Drill Partners GROUND WATER LEVELS:
CHECKED BY KDH
DATE STARTED 2/12/21 COMPLETED 2/12/21
AT TIME OF DRILLING ---
AT END OF DRILLING ---
AFTER DRILLING ---SAMPLE TYPENUMBERDEPTH(ft)0
5
10
15
20
PAGE 1 OF 1
BORING NUMBER B-2
PROJECT NUMBER ES-7282 PROJECT NAME Harrington Redevelopment
GENERAL BH / TP / WELL - 7282.GPJ - GINT STD US.GDT - 3/31/21Earth Solutions NW, LLC
15365 N.E. 90th Street, Suite 100
Redmond, Washington 98052
Telephone: 425-449-4704
Fax: 425-449-4711
RECOVERY %BLOWCOUNTS(N VALUE)TESTS
U.S.C.S.MATERIAL DESCRIPTION
GRAPHICLOGBoring terminated at 20.0 feet below existing grade. No groundwater
encountered during drilling. Boring backfilled with bentonite.
SS 50/5"DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
SS
SS
SS
SS
SS
67
67
67
100
55
5-5-6
(11)
4-4-6
(10)
5-3-2
(5)
2-3-13
(16)
13-50/5"
MC = 8.4%
MC = 6.8%
Fines = 9.5%
MC = 9.6%
MC = 11.0%
Fines = 29.9%
MC = 7.5%
SP-
SM
SM
7.5
20.0
Brown poorly graded SAND with silt and gravel, medium dense, moist
[USDA Classification: very gravelly loamy coarse SAND]
Brown silty SAND, loose, moist
[USDA Classification: gravelly fine sandy LOAM]
-becomes gray, medium dense
-becomes very dense
NOTES Surface Conditions: asphalt ~1"
GROUND ELEVATION
LOGGED BY CGH
DRILLING METHOD HSA
HOLE SIZE
DRILLING CONTRACTOR Geologic Drill Partners GROUND WATER LEVELS:
CHECKED BY KDH
DATE STARTED 2/12/21 COMPLETED 2/12/21
AT TIME OF DRILLING ---
AT END OF DRILLING ---
AFTER DRILLING ---
(Continued Next Page)SAMPLE TYPENUMBERDEPTH(ft)0
5
10
15
20
PAGE 1 OF 2
BORING NUMBER B-3
PROJECT NUMBER ES-7282 PROJECT NAME Harrington Redevelopment
GENERAL BH / TP / WELL - 7282.GPJ - GINT STD US.GDT - 3/31/21Earth Solutions NW, LLC
15365 N.E. 90th Street, Suite 100
Redmond, Washington 98052
Telephone: 425-449-4704
Fax: 425-449-4711
RECOVERY %BLOWCOUNTS(N VALUE)TESTS
U.S.C.S.MATERIAL DESCRIPTION
GRAPHICLOGDRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
SS
SS
100
100
25-30-38
(68)
26-26-42
(68)
MC = 7.4%
Fines = 10.3%
MC = 5.0%
SM
SW-
SM
21.0
26.5
Gray silty SAND, very dense, moist
[USDA Classification: slightly gravelly coarse SAND]
Gray well-graded SAND with silt, very dense, moist
-4" silty sand lens
Boring terminated at 26.5 feet below existing grade. No groundwater
encountered during drilling. Boring backfilled with bentonite.SAMPLE TYPENUMBERDEPTH(ft)20
25
PAGE 2 OF 2
BORING NUMBER B-3
PROJECT NUMBER ES-7282 PROJECT NAME Harrington Redevelopment
GENERAL BH / TP / WELL - 7282.GPJ - GINT STD US.GDT - 3/31/21Earth Solutions NW, LLC
15365 N.E. 90th Street, Suite 100
Redmond, Washington 98052
Telephone: 425-449-4704
Fax: 425-449-4711
RECOVERY %BLOWCOUNTS(N VALUE)TESTS
U.S.C.S.MATERIAL DESCRIPTION
GRAPHICLOGDRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Earth Solutions NW, LLC
Appendix B
Laboratory Test Results
ES-7282 DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
0
5
10
15
20
25
30
35
40
45
50
55
60
65
70
75
80
85
90
95
100
0.0010.010.1110100
3
D100
140
Specimen Identification
1
fine
6
HYDROMETER
304
23.9
26.6
9.5
29.9
10.3
101/2
COBBLES
Specimen Identification
4
coarse
20 401.5 8 14
USDA: Gray Slightly Gravelly Loamy Sand. USCS: SM.
USDA: Gray Slightly Gravelly Sandy Loam. USCS: SM.
USDA: Brown Very Gravelly Loamy Coarse Sand. USCS: SP-SM with Gravel.
USDA: Gray Gravelly Fine Sandy Loam. USCS: SM.
USDA: Gray Slightly Gravelly Coarse Sand. USCS: SW-SM.
6 60
PERCENT FINER BY WEIGHTD10
0.115
0.096
0.345
0.075
0.232
0.376
0.371
2.788
0.214
0.599
GRAIN SIZE DISTRIBUTION
100
35.00
8.22
LL
B-01
B-02
B-03
B-03
B-03
0.08
3/4
U.S. SIEVE OPENING IN INCHES U.S. SIEVE NUMBERS
GRAVEL SAND
19
19
37.5
37.5
9.5
%Silt
0.54
1.24
B-01
B-02
B-03
B-03
B-03
2 2003
Cc CuClassification
%Clay
16
PID60 D30
coarse SILT OR CLAYfinemedium
GRAIN SIZE IN MILLIMETERS
3/8 50
2.5ft.
5.0ft.
5.0ft.
10.0ft.
20.0ft.
2.50ft.
5.00ft.
5.00ft.
10.00ft.
20.00ft.
PL
PROJECT NUMBER ES-7282 PROJECT NAME Harrington Redevelopment
GRAIN SIZE USDA ES-7282 HARRINGTON REDEVELOPMENT.GPJ GINT US LAB.GDT 2/24/21Earth Solutions NW, LLC
15365 N.E. 90th Street, Suite 100
Redmond, Washington 98052
Telephone: 425-449-4704
Fax: 425-449-4711
DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Earth Solutions NW, LLC
Report Distribution
ES-7282
EMAIL ONLY Zarnoor Associates, LLC
c/o Mr. Karim Karmali
19515 North Creek Parkway, Suite 314
Bothell, Washington 98011
Attention: Mr. Nazim Karmali
EMAIL ONLY Grouparchitect
1735 Westlake Avenue North, Suite 200
Seattle, Washington 98109
Attention: Mr. Kyle Stevens DRAFTDocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
United States
Department of
Agriculture
A product of the National
Cooperative Soil Survey,
a joint effort of the United
States Department of
Agriculture and other
Federal agencies, State
agencies including the
Agricultural Experiment
Stations, and local
participants
Custom Soil Resource
Report for
King County
Area,
Washington
Natural
Resources
Conservation
Service
May 17, 2021
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Preface
Soil surveys contain information that affects land use planning in survey areas.
They highlight soil limitations that affect various land uses and provide information
about the properties of the soils in the survey areas. Soil surveys are designed for
many different users, including farmers, ranchers, foresters, agronomists, urban
planners, community officials, engineers, developers, builders, and home buyers.
Also, conservationists, teachers, students, and specialists in recreation, waste
disposal, and pollution control can use the surveys to help them understand,
protect, or enhance the environment.
Various land use regulations of Federal, State, and local governments may impose
special restrictions on land use or land treatment. Soil surveys identify soil
properties that are used in making various land use or land treatment decisions.
The information is intended to help the land users identify and reduce the effects of
soil limitations on various land uses. The landowner or user is responsible for
identifying and complying with existing laws and regulations.
Although soil survey information can be used for general farm, local, and wider area
planning, onsite investigation is needed to supplement this information in some
cases. Examples include soil quality assessments (http://www.nrcs.usda.gov/wps/
portal/nrcs/main/soils/health/) and certain conservation and engineering
applications. For more detailed information, contact your local USDA Service Center
(https://offices.sc.egov.usda.gov/locator/app?agency=nrcs) or your NRCS State Soil
Scientist (http://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/contactus/?
cid=nrcs142p2_053951).
Great differences in soil properties can occur within short distances. Some soils are
seasonally wet or subject to flooding. Some are too unstable to be used as a
foundation for buildings or roads. Clayey or wet soils are poorly suited to use as
septic tank absorption fields. A high water table makes a soil poorly suited to
basements or underground installations.
The National Cooperative Soil Survey is a joint effort of the United States
Department of Agriculture and other Federal agencies, State agencies including the
Agricultural Experiment Stations, and local agencies. The Natural Resources
Conservation Service (NRCS) has leadership for the Federal part of the National
Cooperative Soil Survey.
Information about soils is updated periodically. Updated information is available
through the NRCS Web Soil Survey, the site for official soil survey information.
The U.S. Department of Agriculture (USDA) prohibits discrimination in all its
programs and activities on the basis of race, color, national origin, age, disability,
and where applicable, sex, marital status, familial status, parental status, religion,
sexual orientation, genetic information, political beliefs, reprisal, or because all or a
part of an individual's income is derived from any public assistance program. (Not
all prohibited bases apply to all programs.) Persons with disabilities who require
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alternative means for communication of program information (Braille, large print,
audiotape, etc.) should contact USDA's TARGET Center at (202) 720-2600 (voice
and TDD). To file a complaint of discrimination, write to USDA, Director, Office of
Civil Rights, 1400 Independence Avenue, S.W., Washington, D.C. 20250-9410 or
call (800) 795-3272 (voice) or (202) 720-6382 (TDD). USDA is an equal opportunity
provider and employer.
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Contents
Preface....................................................................................................................2
How Soil Surveys Are Made..................................................................................5
Soil Map..................................................................................................................8
Soil Map................................................................................................................9
Legend................................................................................................................10
Map Unit Legend................................................................................................11
Map Unit Descriptions.........................................................................................11
King County Area, Washington.......................................................................13
RdC—Ragnar-Indianola association, sloping..............................................13
Ur—Urban land...........................................................................................14
References............................................................................................................15
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How Soil Surveys Are Made
Soil surveys are made to provide information about the soils and miscellaneous
areas in a specific area. They include a description of the soils and miscellaneous
areas and their location on the landscape and tables that show soil properties and
limitations affecting various uses. Soil scientists observed the steepness, length,
and shape of the slopes; the general pattern of drainage; the kinds of crops and
native plants; and the kinds of bedrock. They observed and described many soil
profiles. A soil profile is the sequence of natural layers, or horizons, in a soil. The
profile extends from the surface down into the unconsolidated material in which the
soil formed or from the surface down to bedrock. The unconsolidated material is
devoid of roots and other living organisms and has not been changed by other
biological activity.
Currently, soils are mapped according to the boundaries of major land resource
areas (MLRAs). MLRAs are geographically associated land resource units that
share common characteristics related to physiography, geology, climate, water
resources, soils, biological resources, and land uses (USDA, 2006). Soil survey
areas typically consist of parts of one or more MLRA.
The soils and miscellaneous areas in a survey area occur in an orderly pattern that
is related to the geology, landforms, relief, climate, and natural vegetation of the
area. Each kind of soil and miscellaneous area is associated with a particular kind
of landform or with a segment of the landform. By observing the soils and
miscellaneous areas in the survey area and relating their position to specific
segments of the landform, a soil scientist develops a concept, or model, of how they
were formed. Thus, during mapping, this model enables the soil scientist to predict
with a considerable degree of accuracy the kind of soil or miscellaneous area at a
specific location on the landscape.
Commonly, individual soils on the landscape merge into one another as their
characteristics gradually change. To construct an accurate soil map, however, soil
scientists must determine the boundaries between the soils. They can observe only
a limited number of soil profiles. Nevertheless, these observations, supplemented
by an understanding of the soil-vegetation-landscape relationship, are sufficient to
verify predictions of the kinds of soil in an area and to determine the boundaries.
Soil scientists recorded the characteristics of the soil profiles that they studied. They
noted soil color, texture, size and shape of soil aggregates, kind and amount of rock
fragments, distribution of plant roots, reaction, and other features that enable them
to identify soils. After describing the soils in the survey area and determining their
properties, the soil scientists assigned the soils to taxonomic classes (units).
Taxonomic classes are concepts. Each taxonomic class has a set of soil
characteristics with precisely defined limits. The classes are used as a basis for
comparison to classify soils systematically. Soil taxonomy, the system of taxonomic
classification used in the United States, is based mainly on the kind and character
of soil properties and the arrangement of horizons within the profile. After the soil
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scientists classified and named the soils in the survey area, they compared the
individual soils with similar soils in the same taxonomic class in other areas so that
they could confirm data and assemble additional data based on experience and
research.
The objective of soil mapping is not to delineate pure map unit components; the
objective is to separate the landscape into landforms or landform segments that
have similar use and management requirements. Each map unit is defined by a
unique combination of soil components and/or miscellaneous areas in predictable
proportions. Some components may be highly contrasting to the other components
of the map unit. The presence of minor components in a map unit in no way
diminishes the usefulness or accuracy of the data. The delineation of such
landforms and landform segments on the map provides sufficient information for the
development of resource plans. If intensive use of small areas is planned, onsite
investigation is needed to define and locate the soils and miscellaneous areas.
Soil scientists make many field observations in the process of producing a soil map.
The frequency of observation is dependent upon several factors, including scale of
mapping, intensity of mapping, design of map units, complexity of the landscape,
and experience of the soil scientist. Observations are made to test and refine the
soil-landscape model and predictions and to verify the classification of the soils at
specific locations. Once the soil-landscape model is refined, a significantly smaller
number of measurements of individual soil properties are made and recorded.
These measurements may include field measurements, such as those for color,
depth to bedrock, and texture, and laboratory measurements, such as those for
content of sand, silt, clay, salt, and other components. Properties of each soil
typically vary from one point to another across the landscape.
Observations for map unit components are aggregated to develop ranges of
characteristics for the components. The aggregated values are presented. Direct
measurements do not exist for every property presented for every map unit
component. Values for some properties are estimated from combinations of other
properties.
While a soil survey is in progress, samples of some of the soils in the area generally
are collected for laboratory analyses and for engineering tests. Soil scientists
interpret the data from these analyses and tests as well as the field-observed
characteristics and the soil properties to determine the expected behavior of the
soils under different uses. Interpretations for all of the soils are field tested through
observation of the soils in different uses and under different levels of management.
Some interpretations are modified to fit local conditions, and some new
interpretations are developed to meet local needs. Data are assembled from other
sources, such as research information, production records, and field experience of
specialists. For example, data on crop yields under defined levels of management
are assembled from farm records and from field or plot experiments on the same
kinds of soil.
Predictions about soil behavior are based not only on soil properties but also on
such variables as climate and biological activity. Soil conditions are predictable over
long periods of time, but they are not predictable from year to year. For example,
soil scientists can predict with a fairly high degree of accuracy that a given soil will
have a high water table within certain depths in most years, but they cannot predict
that a high water table will always be at a specific level in the soil on a specific date.
After soil scientists located and identified the significant natural bodies of soil in the
survey area, they drew the boundaries of these bodies on aerial photographs and
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identified each as a specific map unit. Aerial photographs show trees, buildings,
fields, roads, and rivers, all of which help in locating boundaries accurately.
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Soil Map
The soil map section includes the soil map for the defined area of interest, a list of
soil map units on the map and extent of each map unit, and cartographic symbols
displayed on the map. Also presented are various metadata about data used to
produce the map, and a description of each soil map unit.
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Custom Soil Resource Report
Soil Map
5260860526087052608805260890526090052609105260920526093052609405260950526096052608605260870526088052608905260900526091052609205260930526094052609505260960561620 561630 561640 561650 561660 561670 561680 561690
561620 561630 561640 561650 561660 561670 561680 561690 561700
47° 29' 57'' N 122° 10' 54'' W47° 29' 57'' N122° 10' 50'' W47° 29' 53'' N
122° 10' 54'' W47° 29' 53'' N
122° 10' 50'' WN
Map projection: Web Mercator Corner coordinates: WGS84 Edge tics: UTM Zone 10N WGS84
0 25 50 100 150
Feet
0 5 10 20 30
Meters
Map Scale: 1:559 if printed on A portrait (8.5" x 11") sheet.
Soil Map may not be valid at this scale.
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MAP LEGEND MAP INFORMATION
Area of Interest (AOI)
Area of Interest (AOI)
Soils
Soil Map Unit Polygons
Soil Map Unit Lines
Soil Map Unit Points
Special Point Features
Blowout
Borrow Pit
Clay Spot
Closed Depression
Gravel Pit
Gravelly Spot
Landfill
Lava Flow
Marsh or swamp
Mine or Quarry
Miscellaneous Water
Perennial Water
Rock Outcrop
Saline Spot
Sandy Spot
Severely Eroded Spot
Sinkhole
Slide or Slip
Sodic Spot
Spoil Area
Stony Spot
Very Stony Spot
Wet Spot
Other
Special Line Features
Water Features
Streams and Canals
Transportation
Rails
Interstate Highways
US Routes
Major Roads
Local Roads
Background
Aerial Photography
The soil surveys that comprise your AOI were mapped at
1:24,000.
Warning: Soil Map may not be valid at this scale.
Enlargement of maps beyond the scale of mapping can cause
misunderstanding of the detail of mapping and accuracy of soil
line placement. The maps do not show the small areas of
contrasting soils that could have been shown at a more detailed
scale.
Please rely on the bar scale on each map sheet for map
measurements.
Source of Map: Natural Resources Conservation Service
Web Soil Survey URL:
Coordinate System: Web Mercator (EPSG:3857)
Maps from the Web Soil Survey are based on the Web Mercator
projection, which preserves direction and shape but distorts
distance and area. A projection that preserves area, such as the
Albers equal-area conic projection, should be used if more
accurate calculations of distance or area are required.
This product is generated from the USDA-NRCS certified data as
of the version date(s) listed below.
Soil Survey Area: King County Area, Washington
Survey Area Data: Version 16, Jun 4, 2020
Soil map units are labeled (as space allows) for map scales
1:50,000 or larger.
Date(s) aerial images were photographed: Jul 25, 2020—Jul 27,
2020
The orthophoto or other base map on which the soil lines were
compiled and digitized probably differs from the background
imagery displayed on these maps. As a result, some minor
shifting of map unit boundaries may be evident.
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Map Unit Legend
Map Unit Symbol Map Unit Name Acres in AOI Percent of AOI
RdC Ragnar-Indianola association,
sloping
0.3 40.7%
Ur Urban land 0.4 59.3%
Totals for Area of Interest 0.7 100.0%
Map Unit Descriptions
The map units delineated on the detailed soil maps in a soil survey represent the
soils or miscellaneous areas in the survey area. The map unit descriptions, along
with the maps, can be used to determine the composition and properties of a unit.
A map unit delineation on a soil map represents an area dominated by one or more
major kinds of soil or miscellaneous areas. A map unit is identified and named
according to the taxonomic classification of the dominant soils. Within a taxonomic
class there are precisely defined limits for the properties of the soils. On the
landscape, however, the soils are natural phenomena, and they have the
characteristic variability of all natural phenomena. Thus, the range of some
observed properties may extend beyond the limits defined for a taxonomic class.
Areas of soils of a single taxonomic class rarely, if ever, can be mapped without
including areas of other taxonomic classes. Consequently, every map unit is made
up of the soils or miscellaneous areas for which it is named and some minor
components that belong to taxonomic classes other than those of the major soils.
Most minor soils have properties similar to those of the dominant soil or soils in the
map unit, and thus they do not affect use and management. These are called
noncontrasting, or similar, components. They may or may not be mentioned in a
particular map unit description. Other minor components, however, have properties
and behavioral characteristics divergent enough to affect use or to require different
management. These are called contrasting, or dissimilar, components. They
generally are in small areas and could not be mapped separately because of the
scale used. Some small areas of strongly contrasting soils or miscellaneous areas
are identified by a special symbol on the maps. If included in the database for a
given area, the contrasting minor components are identified in the map unit
descriptions along with some characteristics of each. A few areas of minor
components may not have been observed, and consequently they are not
mentioned in the descriptions, especially where the pattern was so complex that it
was impractical to make enough observations to identify all the soils and
miscellaneous areas on the landscape.
The presence of minor components in a map unit in no way diminishes the
usefulness or accuracy of the data. The objective of mapping is not to delineate
pure taxonomic classes but rather to separate the landscape into landforms or
landform segments that have similar use and management requirements. The
delineation of such segments on the map provides sufficient information for the
development of resource plans. If intensive use of small areas is planned, however,
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onsite investigation is needed to define and locate the soils and miscellaneous
areas.
An identifying symbol precedes the map unit name in the map unit descriptions.
Each description includes general facts about the unit and gives important soil
properties and qualities.
Soils that have profiles that are almost alike make up a soil series. Except for
differences in texture of the surface layer, all the soils of a series have major
horizons that are similar in composition, thickness, and arrangement.
Soils of one series can differ in texture of the surface layer, slope, stoniness,
salinity, degree of erosion, and other characteristics that affect their use. On the
basis of such differences, a soil series is divided into soil phases. Most of the areas
shown on the detailed soil maps are phases of soil series. The name of a soil phase
commonly indicates a feature that affects use or management. For example, Alpha
silt loam, 0 to 2 percent slopes, is a phase of the Alpha series.
Some map units are made up of two or more major soils or miscellaneous areas.
These map units are complexes, associations, or undifferentiated groups.
A complex consists of two or more soils or miscellaneous areas in such an intricate
pattern or in such small areas that they cannot be shown separately on the maps.
The pattern and proportion of the soils or miscellaneous areas are somewhat similar
in all areas. Alpha-Beta complex, 0 to 6 percent slopes, is an example.
An association is made up of two or more geographically associated soils or
miscellaneous areas that are shown as one unit on the maps. Because of present
or anticipated uses of the map units in the survey area, it was not considered
practical or necessary to map the soils or miscellaneous areas separately. The
pattern and relative proportion of the soils or miscellaneous areas are somewhat
similar. Alpha-Beta association, 0 to 2 percent slopes, is an example.
An undifferentiated group is made up of two or more soils or miscellaneous areas
that could be mapped individually but are mapped as one unit because similar
interpretations can be made for use and management. The pattern and proportion
of the soils or miscellaneous areas in a mapped area are not uniform. An area can
be made up of only one of the major soils or miscellaneous areas, or it can be made
up of all of them. Alpha and Beta soils, 0 to 2 percent slopes, is an example.
Some surveys include miscellaneous areas. Such areas have little or no soil
material and support little or no vegetation. Rock outcrop is an example.
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King County Area, Washington
RdC—Ragnar-Indianola association, sloping
Map Unit Setting
National map unit symbol: 1hmty
Elevation: 0 to 1,000 feet
Mean annual precipitation: 30 to 65 inches
Mean annual air temperature: 48 to 54 degrees F
Frost-free period: 150 to 210 days
Farmland classification: Farmland of statewide importance
Map Unit Composition
Ragnar and similar soils:45 percent
Indianola and similar soils:40 percent
Estimates are based on observations, descriptions, and transects of the mapunit.
Description of Ragnar
Setting
Landform:Kames, terraces, eskers
Parent material:Glacial outwash
Typical profile
H1 - 0 to 4 inches: ashy fine sandy loam
H2 - 4 to 27 inches: ashy fine sandy loam
H3 - 27 to 60 inches: loamy sand
Properties and qualities
Slope:2 to 15 percent
Depth to restrictive feature:20 to 40 inches to strongly contrasting textural
stratification
Drainage class:Well drained
Capacity of the most limiting layer to transmit water (Ksat):High (1.98 to 5.95
in/hr)
Depth to water table:More than 80 inches
Frequency of flooding:None
Frequency of ponding:None
Available water capacity:Low (about 3.7 inches)
Interpretive groups
Land capability classification (irrigated): None specified
Land capability classification (nonirrigated): 3e
Hydrologic Soil Group: A
Forage suitability group: Droughty Soils (G002XN402WA)
Other vegetative classification: Droughty Soils (G002XN402WA)
Hydric soil rating: No
Description of Indianola
Setting
Landform:Terraces
Parent material:Glacial drift
Typical profile
H1 - 0 to 6 inches: loamy fine sand
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H2 - 6 to 30 inches: loamy fine sand
H3 - 30 to 60 inches: sand
Properties and qualities
Slope:2 to 15 percent
Depth to restrictive feature:More than 80 inches
Drainage class:Somewhat excessively drained
Capacity of the most limiting layer to transmit water (Ksat):High (1.98 to 5.95
in/hr)
Depth to water table:More than 80 inches
Frequency of flooding:None
Frequency of ponding:None
Available water capacity:Low (about 5.0 inches)
Interpretive groups
Land capability classification (irrigated): None specified
Land capability classification (nonirrigated): 3e
Hydrologic Soil Group: A
Forage suitability group: Droughty Soils (G002XN402WA)
Other vegetative classification: Droughty Soils (G002XN402WA)
Hydric soil rating: No
Ur—Urban land
Map Unit Composition
Urban land:100 percent
Estimates are based on observations, descriptions, and transects of the mapunit.
Description of Urban Land
Interpretive groups
Land capability classification (irrigated): None specified
Land capability classification (nonirrigated): 8
Hydric soil rating: No
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References
American Association of State Highway and Transportation Officials (AASHTO).
2004. Standard specifications for transportation materials and methods of sampling
and testing. 24th edition.
American Society for Testing and Materials (ASTM). 2005. Standard classification of
soils for engineering purposes. ASTM Standard D2487-00.
Cowardin, L.M., V. Carter, F.C. Golet, and E.T. LaRoe. 1979. Classification of
wetlands and deep-water habitats of the United States. U.S. Fish and Wildlife
Service FWS/OBS-79/31.
Federal Register. July 13, 1994. Changes in hydric soils of the United States.
Federal Register. September 18, 2002. Hydric soils of the United States.
Hurt, G.W., and L.M. Vasilas, editors. Version 6.0, 2006. Field indicators of hydric
soils in the United States.
National Research Council. 1995. Wetlands: Characteristics and boundaries.
Soil Survey Division Staff. 1993. Soil survey manual. Soil Conservation Service.
U.S. Department of Agriculture Handbook 18. http://www.nrcs.usda.gov/wps/portal/
nrcs/detail/national/soils/?cid=nrcs142p2_054262
Soil Survey Staff. 1999. Soil taxonomy: A basic system of soil classification for
making and interpreting soil surveys. 2nd edition. Natural Resources Conservation
Service, U.S. Department of Agriculture Handbook 436. http://
www.nrcs.usda.gov/wps/portal/nrcs/detail/national/soils/?cid=nrcs142p2_053577
Soil Survey Staff. 2010. Keys to soil taxonomy. 11th edition. U.S. Department of
Agriculture, Natural Resources Conservation Service. http://
www.nrcs.usda.gov/wps/portal/nrcs/detail/national/soils/?cid=nrcs142p2_053580
Tiner, R.W., Jr. 1985. Wetlands of Delaware. U.S. Fish and Wildlife Service and
Delaware Department of Natural Resources and Environmental Control, Wetlands
Section.
United States Army Corps of Engineers, Environmental Laboratory. 1987. Corps of
Engineers wetlands delineation manual. Waterways Experiment Station Technical
Report Y-87-1.
United States Department of Agriculture, Natural Resources Conservation Service.
National forestry manual. http://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/
home/?cid=nrcs142p2_053374
United States Department of Agriculture, Natural Resources Conservation Service.
National range and pasture handbook. http://www.nrcs.usda.gov/wps/portal/nrcs/
detail/national/landuse/rangepasture/?cid=stelprdb1043084
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United States Department of Agriculture, Natural Resources Conservation Service.
National soil survey handbook, title 430-VI. http://www.nrcs.usda.gov/wps/portal/
nrcs/detail/soils/scientists/?cid=nrcs142p2_054242
United States Department of Agriculture, Natural Resources Conservation Service.
2006. Land resource regions and major land resource areas of the United States,
the Caribbean, and the Pacific Basin. U.S. Department of Agriculture Handbook
296. http://www.nrcs.usda.gov/wps/portal/nrcs/detail/national/soils/?
cid=nrcs142p2_053624
United States Department of Agriculture, Soil Conservation Service. 1961. Land
capability classification. U.S. Department of Agriculture Handbook 210. http://
www.nrcs.usda.gov/Internet/FSE_DOCUMENTS/nrcs142p2_052290.pdf
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Site Planning
Civil Engineering
Landscape Architecture
Project Management
Land Use Consulting
APPENDIX B
ARBORIST REPORT
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LAYTON TREE CONSULTING, LLC
It’s all about trees……
PO BOX 572, SNOHOMISH, WA 98291-0572 * 425-220-5711 * bob@laytontreeconsulting.com
ARBORIST REPORT/TREE PLAN
960 Harrington Avenue NE
Renton, WA
Report Prepared by:
Bob Layton
Registered Consulting Arborist #670
Certified Arborist #PN-2714A
April 19, 2021
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Page 2 Layton Tree Consulting LLC April 19, 2021
Table of Contents
Assignment.................................................................................................................................................... 3
Description .................................................................................................................................................... 3
Methodology ................................................................................................................................................. 3
Judging Condition...................................................................................................................................... 3
Observations ................................................................................................................................................. 4
Discussion/Recommendations ...................................................................................................................... 4
Tree Density-Tree Replacement ................................................................................................................... 5
Arborist Disclosure Statement ...................................................................................................................... 6
Attachments
Photos, pages 7 - 13
Tree Summary Table
Tree Plan Map
City of Renton – Approved Tree List
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Page 3 Layton Tree Consulting LLC April 19, 2021
Assignment
Layton Tree Consulting, LLC was asked to compile an Arborist Report for one parcel in Renton. The
subject property is located at 960 Harrington AVE NE. The purpose of the report is to satisfy City
requirements regarding tree retention regulations associated with the proposed redevelopment of the
property.
My assignment is to prepare a written report on present tree conditions, and to provide appropriate
recommendations for the protection of retained or protected trees during development.
This report covers all of the criteria set forth under the City of Renton’s tree regulations, Municipal Code
Section 4-4-130 - Tree Retention and Land Clearing Regulations.
Date of Field Examination: April 13, 2021
Description
Three significant trees were identified on the property. A significant tree is any tree with a caliper of at least
6-inches or alder or cottonwood tree at least 8-inches. A numbered aluminum tag was attached to the
lower trunk of the subject trees. These tag numbers correspond with the numbers on the attached Tree
Summary Table and attached Tree Plan Map.
An additional three off-site trees were also assessed. These exist within the right-of-way of NE Sunset Blvd.
These are all mature London plane trees.
Methodology
Each tree in this report was visited. Tree diameters were measured by tape. The tree heights were
measured using a Spiegel Relaskop. Each tree was visually examined for defects and vigor. The tree
assessment procedure involves the examination of many factors:
• The crown or canopy of the tree is examined for current vigor/health by examining the foliage for
appropriate color and density, the vegetative buds for color and size, and the branches for structural
form and annual shoot growth; and the overall presence of limb dieback and/or any disease issues.
• The trunk or main stem of the tree is inspected for decay, which includes cavities, wounds, fruiting
bodies of decay (conks or mushrooms), seams, insect pests, bleeding or exudation of sap, callus
development, broken or dead tops, structural defects and unnatural leans. Structural defects can
include but are not limited to excessive or unnatural leans, crooks, forks with V-shaped crotches,
multiple attachments.
• The root collar and exposed surface roots are inspected for the presence of decay, insect damage, as
well as if they have been injured or wounded, undermined or exposed, or the original grade has
been altered.
Judging Condition
The three condition categories are described as follows:
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Page 4 Layton Tree Consulting LLC April 19, 2021
Good – free of significant structural defects, no disease concerns, minor pest issues, no significant root
issues, good structure/form with uniform crown or canopy, foliage of normal color and density, average or
normal vigor, will be wind firm if isolated or left as part of a grouping or grove of trees, suitable for its
location
Fair – minor to moderate structural defects not expected to contribute to a failure in near future, no disease
concerns, moderate pest issues, no significant root issues, asymmetric or unbalanced crown or canopy,
average or normal vigor, foliage of normal color, moderate foliage density, will be wind firm if left as part of
a grouping or grove of trees, cannot be isolated, suitable for its location
Poor – major structural defects expected to cause fail in near future, disease or significant pest concerns,
decline due to old age, significant root issues, asymmetric or unbalanced crown or canopy, sparse or
abnormally small foliage, poor vigor, not suitable for its location
The attached Tree Summary Table provides specific information on tree sizes and dripline measurements.
Observations
The subject trees are described as follows:
Tree #1 is a semi-mature to mature Austrian pine. It has developed an asymmetric crown and lean to
the south away from Tree #2. The root crown and ground around the tree are covered with a dense
matt of English ivy. Vigor is good. Foliage is of normal color and density. The lower trunk appears
sound. Root growth has cracked surrounding pavement and lifted curb sections. Condition is ‘fair’.
Tree #2 is a mature London plane. It is surrounded by pavement and a sidewalk. There is obvious root
growth beneath the pavement that extends up to 20-feet from the trunk to the east. The tree has
developed good structural form. Vigor appears good. No concerning conditions were observed.
Condition is rated as ‘good’.
Tree #3 is a young to semi-mature Austrian pine, comprised of two stems or trunks. It also has an
asymmetric crown and lean to the south away from the larger plane trees. Condition is ‘fair’.
Right-of-way Trees
Trees #4, #5 and #6 are mature London plane trees within the right-of-way of Sunset Blvd. NE. Trees #4
and #5 have developed good structural form with no concerning issues. Lower trunks are sound with no
outward indicators of any internal decay issues. Vigor appears good. Condition is rated as ‘good’.
The lower trunk of Tree #6 forks into two main stems or trunks, which are codominant (equal diameter).
There is a moderate buildup of included or embedded bark between the forked stems. Vigor appears
good. Condition is rated as ‘fair’.
Discussion/Recommendations
It is my understanding the City would like to see Trees #4, #5 and #6 preserved. Tree #6 is well away
from the subject property and not likely to be impacted. London plane is actually quite hardy and
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tolerable of construction impacts, so long as those impacts are kept to acceptable levels. It is also my
understanding that Trees #1, #2 and #3 are being proposed for removal.
Whether or not Trees #4 and #5 can be retained will depend on the required street frontage
improvements. Relocating the sidewalk to the opposite sides of Trees #4 and #5 will create major
disturbances and have consequential impacts on long-term health. The existing grades are not
conducive to relocating the sidewalk as it slopes down from the elevation of the existing sidewalk. If the
existing sidewalk can be left as-is, the odds of successful retention are much higher.
Tree locations are shown on the attached Tree Plan Map. The driplines of trees have been delineated
on the map, as well as the recommended location of the critical root zone boundary. The critical root
zone boundary is based on species, age, condition, dripline, prior improvements, proposed impacts and
the anticipated cumulative impacts to the entire root zone. Encroachment beyond this limit is likely to
compromise long-term health or longevity.
Pavement or sidewalk sections within the critical root zone boundary shall be removed using primarily
hand-labor. Pavement/concrete can be broken up with a manual jack-hammer and removed by hand
from the tree protection zone. Keep equipment off of the critical root zone boundary to protect soils
and surface roots.
A tree protection barrier shall be placed around any retained or protected trees to the largest extent
possible and fully protect the critical root zone. Cover tree protection areas with a protective +/- 6-inch
layer of coarse arborist wood chip mulch or hog fuel. Thoroughly irrigate any newly exposed areas from
pavement/concrete removal prior to covering with wood chips.
Any roots encountered during work outside of the tree protection areas shall be pruned clean at sound
tissue prior to backfilling or finishing areas. Sound tissue is where the root is undamaged and the bark is
completely intact with the root. Any authorized work within dripline of retained and/or protected trees
shall be supervised by the project arborist in an effort to ensure impacts are kept as minimal as possible
or to acceptable levels.
Some pruning may be needed to provide adequate construction clearance. The amount of anticipated
pruning or removal of branches is not significant and not expected to have any adverse impacts on tree
health or stability. All clearance pruning will conform to ANSI A-300 Pruning Standards.
Simply finish the landscape within the driplines of any retained/protected trees by cutting/hand-pulling
any unwanted vegetation, raking off half of the protective wood chips and applying a more attractive 2
to 4-inch covering of organic mulch/beauty bark. Keep large plantings, irrigation/dispersion trenches
and construction of hardscapes outside of the dripline where possible.
Tree Density-Tree Replacement
Consult with your City planner on tree replacement/landscape requirements.
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Replacement trees shall be at least 2-inch caliper for deciduous species and 6-feet in height for
evergreen species. The City’s approved tree list is attached. Replacement tree species shall be chosen
from this list. Plant new trees in areas where they can fully mature without conflicting with new
improvements.
Arborist Disclosure Statement
Arborists are tree specialists who use their education, knowledge, training and experience to examine
and assess trees, recommend measures to enhance the beauty and health of trees, and attempt to
reduce the risks associated with living near trees. Clients may choose to accept or disregard the
recommendations of the arborist, or to seek additional advice.
Arborists cannot detect every condition that could possibly lead to the structural failure of a tree. Trees
are living organisms that grow, respond to their environment, mature, decline and sometimes fail in
ways we do not fully understand. Conditions are often hidden within trees and below ground.
Arborists cannot guarantee that a tree will be healthy and/or safe under all circumstances, or for a
specified period of time. Likewise, remedial treatments, like any medicine, cannot be guaranteed.
Treatment, pruning and removal of trees may involve considerations beyond the scope of the arborist’s
services such as property boundaries, property ownership, site lines, disputes between neighbors, and
other issues. Arborists cannot take such considerations into account unless complete and accurate
information is disclosed to the arborist. An arborist should then be expected to reasonably rely upon
the completeness and accuracy of the information provided.
Trees can be managed, but they cannot be controlled. To live near trees is to accept some degree of
risk. The only way to eliminate all risk associated with trees is to eliminate all trees.
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Photo Documentation
Tree #1 – lower trunk
Tree #1 – lower trunk, obvious root growth beneath pavement
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Trees #1 and #2, looking north up Harrington Ave NE
Tree #2 – lower trunk
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Tree #2 – mid crown
Tree #2 – lower trunk, sidewalk has lifted and been repaired in the past
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Tree #3 on right, #4 on left, #5 in background
Tree #4 – lower trunk, large surface roots extending several feet to the south
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Trees #4 and #5 within proximity to sidewalk
Tree #5 in foreground, #4 in background
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Tree #5 in foreground, #4 in background
Tree #6 – lower trunk
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Tree #6 – lower trunk
Tree #6
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Layton Tree Consulting LLC
For:Zarnoor Associates
Site:960 Harrington AVE NE - Renton
Tree Summary Table
Date:
Tree/DBH Height
Tag #Species (inches)(feet)Condition Comments Proposal
N S E W
1 Austrian pine 23 45 6 15 12 8 Fair asymmetric crown/lean south, root crown covered with ivy Remove
2 London plane 42 83 30 32 36 24 Good trunk sound ,sound stem attachments Remove
3 Austrian pine 9,5 (10)24 6 14 10 4 Fair leans south, natural lean Remove
OFF-SITE TREES
4 London plane 34 67 22 26 20 36 Good sound trunk, large exposed surface roots to south TBD
5 London plane 29 70 18 28 22 21 Good sound trunk, large exposed surface roots to south TBD
6 London plane 46 85 28 30 NA 30 Fair trunk forks at 5 feet, noteworthy included bark Protect
Drip-Line measurements from face of trunk
TBD - to be determined
Drip-Line / Limits of Disturbance
(feet)
4/13/2021
Calculated DBH: the DBH is parenthesis is the square root of the sum of the dbh for each individual
stem squared (example with 3 stems: dbh = square root [(stem1)2 +(stem2)2 +(stem3)2 ]).
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APPROVED TREE LIST – Small, Medium, and Large
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In the City of Renton there is an overabundance of maple and cherry species. According to the most recent street tree inventory, maples
currently comprise 35% and cherry 24% of all species. To reduce a catastrophic loss of species, experts agree that 10% o r less of any species
or cultivar exist within a street tree population. Because of this, planting maple or cherry trees within the right -of-way is discouraged.
SMALL TREES:
30 feet in height or less
Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Acer buergeranum / Trident Maple 20 20
yellow
orange
and red
Adaptable to urban environments. Decidiuous: prefers moist, well-drained soils:
tolerates infertile sites. Drought tolerant.
Acer campestre / Hedge Maple 30 30 yellow
Deciduous; prefers moist, rich soils; slow growing tree tolerant of air pollution
and soil compaction; yellow fall color; cultivars available including Queen
Elizabeth maple (‘Evelyn’) with dark green, glossy foliage.
Acer circinatum / Vine Maple 20-25 10
orange
and red
Deciduous; prefers moist, well-drained soils; tolerates seasonal saturation and
varying soil types; drought tolerant once established; bushy shrub or small tree;
most often multi-trunked and does well in small groups; white flowers April-
June.
Acer ginnala 'Flame' / Amur Maple 20 20 red
Deciduous; prefers moist, well-drained soils, but is tolerant of drought; is often
multi-trunked, but can be pruned to a single stem; rounded form; fragrant,
yellowish-white flowers in spring; cultivars are available such as ‘Flame’ and
‘Embers’ with differing fall colors. Select or prune for single stem; can be multi-
trunked.
Acer grandidentatum 'Schmidt' / Rocky Mt.
Glow Maple 25+ 15 intense
Acer griseum / Paperback Maple 25 20 scarlet
Deciduous; prefers moist, well-drained soils, but is moderately drought tolerant;
bronze peeling bark provides year-round visual interest; often multitrunked, but
can be trained to a single stem; slow growing; disease and pest resistant.
Smooth, peeling, cinnamon colored bark.
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Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Acer palmatum / Japanese Maple 20 24
yellow,
orange,
red
Prefers moist, well-drained soils; deciduous; slow to moderate growth rate;
multi-trunked with spreading branches; intolerant of inundation but moderately
drought resistant; vibrant fall colors; many cultivars available including ‘Emperor
I’, ‘Katsura’, and ‘Osakazuki’. Hundreds of varied cultivars. Can be slow growing.
Acer saccharum 'Apollo' 25 10
yellow,
orange Prefers well drained soils, but grows in varying soils; hearty.
Acer platanoides 'Globosum' / Globe
Norway Maple 20 18 yellow
Moist soils preferred, but tolerates drought and seasonal inundation; tolerant of
urban pollution; dense, compact, round form; slow-growing deciduous tree with
brilliant fall color; shallow root system may make mowing under the tree slightly
difficult; good selection for locations under power lines; another cultivar well
suited for such a location is A. platanoides ‘Almira,’ reaching only 20-25 ft.
Rounded top, and compact growth.
Acer truncatum / Purpleblow maple 20-25 20-25
Prefers moist, well-drained soil, but drought tolerant; very cold hardy deciduous
tree; moderate growth rate; yellow flowers in spring; an additional maple
cultivar of interest is 'Pacific sunset'.
Acer truncatum x A. platanoides 'Warren's
Red' / Pacific Sunset 30 25
yellow-
orange/
red
Acer Triflorum - Roughbark maple 25-30 20-25
apricot,
gold
Deciduous; prefers moist soils, but somewhat drought tolerant once established;
rough, knobby trunk provides interest in winter; disease and pest resistant; non-
aggressive roots do not damage sidewalks or driveways.
Amelanchier grandiflora 'Princess Diana' 20 15 bright red Good for limited space.
Amelanchier x grandiflora 'Autumn
Brilliance' Serviceberry 20 15
red or
yellow
Moist to dry, well-drained soils; small tree; drought tolerant; white clustered
flowers in spring; also try 'Princess Diana' for bright red fall color and the slightly
taller 'Robin Hill' (20-30 feet). Reliable bloom.
Amelanchier laevis ' lustre' / Luster
Serviceberry 25 25
red or
yellow
Moist to dry, well-drained soils; small tree; drought tolerant; white clustered
flowers in spring.
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Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Arbutus 'Marina' 25 15 evergreen
Good substitute for Pacific Madrone. May exceed 25' height under some site
conditions.
Carpinus caroliniana / American hornbeam 20-30 20-20
Deciduous; prefers moist, rich soils; grows near saturated areas but is only
weakly tolerant of saturation; blooms March-May; slow growing; deep coarse
laterally spreading roots; medium life span; also consider Carpinus japonica
(Japanese hornbeam).
Cercis canadensis / Eastern Redbud 25 30 yellow
Deciduous; prefers moist, rich soils; tolerant of shade; somewhat drought
resistant, but not in full sun; purple-lavender flowers; medium longevity; often
multi-trunked; shallow, fibrous roots become deeper on drier sites; fairly short-
lived; blooms March-May. Blooms before leaves are out.
Cornus kousa 'Chinensis' / Chinese Kousa
Dogwood 20 20
reddish to
scarlet
Prefers moist soils; tolerant of varying soil types; moderate growth rate;
deciduous; white flowers in June and large red fruits that resemble a raspberry
in September; red to maroon fall color; more disease resistant than other
dogwoods; many additional cultivars available. Most resistant to disease of the
dogwoods.
Crataegus crus-galli 'Inermis' / Thornless
Cockspur Hawthorn 25 30
orange to
scarlet Red persistent fruit.
Crataegus x lavalii / Lavalle Hawthorne 28 20
bronze,
coppery
red
Deciduous; prefers moist, well-drained soil, but tolerant of varying soil types;
white flowers in spring; fruit can be a bit messy. Thorns on younger trees.
Crataegus phaenopyrum / Washington
Hawthorn 25 20 scarlet Thorny.
Fraxinus pennsylvanica 'Johnson' /
Leprechaun Ash 18 16 yellow
Prefers moist, well-drained soils; deciduous: slow to moderate growth rate;
tolerant of inundation but moderately drought resistant. A miniature in every
way.
Magnolia x loebneri 20 20 yellow Several cultivars.
Magnolia grandiflora 'Little Gem' 15 10 evergreen Useful where larger varieties are inappropriate.
Magnolia grandiflora 'Victoria' 25 20 evergreen
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Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Malus spp. / Flowering crabapple 15-25 6-15
Selection should be based on disease resistance to apple scab and fireblight.
Tolerant of prolonged soil saturation; short lived; tolerant of drought and
seasonally saturated soils; deciduous; white or faintly pink flowers in spring;
numerous Malus species and cultivars provide a variety of foliage and flower
colors, forms and fruit.
Malus 'Adirondack' 18 8 yellow Red fruit. Excellent scab resistance.
Malus 'Red Barron' 18 8 yellow Good for narrow spaces. Red berries.
Malus 'Golden Raindrops' 18 13 yellow Abundant yellow fruit.
Malus 'Tschonoskii' 28 14 scarlet Sparse green fruit, pyramidal.
Parrotia persica / Persian Parrotia 30 20
yellow-
orange
red
Moist to dry soils; drought tolerant when established, deciduous tree with
moderate growth rate; brilliant fall color; often multi-trunked, but can be
trained to have just one; tolerates urban pollution and soil compaction; surface
roots do not generally cause problems; virtually disease and pest-free.
Pranus 'Frankthrees' / Mt. St. Helens Plum 20 20 Purple foliage.
Prunus 'Newport' / Newport Plum 20 20
reddish to
scarlet Purple red foliage.
Prunus cerasifera 'Krauter Vesuvius' /
Flowering Plum 30 15 Upright growth, darkest foliage of the plums.
Prunus cerasifera 'Thundercloud' / Plum 20 20 Dark purple foliage.
Prunus x hillieri 'Spire' 30 10
orange
red
Prunus 'Snowgoose' / Snow Goose Cherry 20 20 Upright when young, spreading when older.
Prunus serrulata 'Amanogawa' / Flowering
Cherry 20 6 bronze Particularly useful for very narrow planting strips.
Prunus serrulata 'Shirofugen' / Japanese
flowering cherry 25 25
Deciduous flowering tree; moist, well-drained soils; double pink to white blooms
in spring; vigorous grower; additional desirable choices include P. serrulata
‘Snowgoose’, ‘Kwanzan’, and ‘Shirotae’.
Prunus x yedoensis 'Akebono' / Flowering
Cherry 25 25 yellow
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Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Quercus Ilex / Holly Oak 20 20
Prefers moist soils, but grows in varying soils; hearty, slow-growing evergreen
tree; light pink flowers May-June; pruning will keep tree small for a hedge,
without pruning may grow considerably larger – not appropriate under utility
lines; tolerates salt water spray. Prune to keep small, leave it alone to grow
large.
Styrax japonica / Japanese Snowbell 25 25 yellow Plentiful, green 1/2 inch seeds.
Styrax obassia / Fragrant Snowbell 30 25
Prefers moist, well-drained soil but tolerates wide variations; fragrant with
flowers; twisting bark. Try other Styrax species.
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MEDIUM TREES:
30 to 50 feet in height
Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Acer campestre 'Evelyn' / Queen Elizabeth
Maple 35 30 yellow More upright branching than the species.
Acer platanoides 'Columnar' / Columnar
Norway maple 40 15 yellow
Deciduous; adapts to varying soils; upright or columnar in form making this
cultivar a better choice for narrow locations; tolerant of drought and seasonal
inundation; tolerates urban pollution and displays brilliant fall color; shallow
rooting necessitates locating at least 4-6 feet from sidewalks and driveways to
prevent heaving of pavement. Good close to buildings.
Acer truncatum x A. platanoides
'Klethsform' / Norwegian Sunset 35 25
yellow-
orange/
red
Acer rubrum 'Bowhall' / Bowhall Maple 40 15
yellow
orange
Acer rubrum 'Karpick' / Karpick Maple 35-40 20
yellow to
orange May work under very high powerlines with arborist's approval.
Acer rubrum 'Scarsen' / Scarlet Sentinel
Maple 40 20
yellow
orange
Acer rubrum / Red Maple 35-50 15-40
Deciduous tree known for fall color; prefer wet or moist soils; fast growing with
roots that may heave sidewalks or interfere with mowing; many cultivars of
varying heights available including: A. rubrum, 'Armstrong', 'Bowhall', 'Karpick',
'Scarsen', and 'Red Sunset'.
Betula jacquemontii / Jacquemontii Birch 40 30 yellow White bark makes for good winter interest.
Carpinus betulus 'Fastigiati' / Pyramidal
European Hornbeam 35 25 yellow
Fagus sylvatica 'Dawyck Purple' / Dawyck
Purple Beech 40 12
Purple foliage.
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Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Fraxinus americana 'Autumn Applause' /
Ash 40 25 purple
Deciduous; prefers moist, well-drained soils; dense, wide spreading canopy;
long-lived; purple fall color; moderate growth rate; also try F. Americana
'Junginger'.
Fraxinus oxycarpa 'Raywood' / Raywood
Ash 35 25
reddish
purple
Pyrus calleryana 'Aristocrat' / Pear 40 45 red
Pyrus calleryana 'Chanticleer' / Flowring
Pear 40 15
Deciduous tree that grows well in a variety of soil types; orange to reddish fall
color; white flowers in spring; additional cultivars of interest include P.
calleryana 'Redspire' and 'Aristocrat'.
Pyrus calleryana 'Redspire' / Pear 40 45 red
Pyrus calleryana 'Autumn Blaze' / Pear 30 25 scarlet Vigorous.
Ginko biloba 'Autumn Gold' / Maidenhair
tree 45 35 yellow
Moist soils; deciduous ornamental tree; fast growing and long-lived; tolerant of
urban pollution, summer drought and winter inundation; showy fall color; grows
in soils of varying quality; provides dense canopy; additional cultivars available.
Ginko biloba 'Princeton Sentry' 40 15 yellow Very narrow growth.
Gleditsia triacanthos inermis 'Shademaster'
/ Shademaster Thornless Honeylocust 45 35 yellow
Deciduous; prefers moist, rich soils, but will grow in varying soil types; a
thornless cultivar tolerant of drought and seasonal inundation; adapts to urban
pollution and displays vigorous growth; deciduous tree with showy yellow fall
color; additional cultivars available such as ‘Imperial,’ which grows 30-35 feet,
‘Moraine,’ and ‘Rubylace’. Do not confuse with 'Sunburst'.
Koelreuteria paniculata / Goldenrain Tree 20-35 10-30 yellow
Deciduous; prefers moist well-drained soils, but is tolerant of poor soils; medium
rate of growth and longevity; tolerant of periods of drought and seasonal
inundation; tolerates urban pollution; provides a dense, wide-spreading canopy.
Midsummer blooming.
Oxydendron arboreum / Sourwood 35 12
reddish
purple Consistent and brilliant fall color.
Prunus sargentii 'Columnarus' 35 15
orange to
orange
red The cherry with the best fall color.
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Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Quercus 'Crimschmidt' / Crimson Spire Oak 45 15 Hard to find.
Robinia x ambigua 'Idahoensis' / Pink Idaho
Locust 35 25 yellow Fragrant flowers.
Tilia americana 'Redmond' 35 20 yellow Pyramidal, needs water.
Tilia cordata 'Chancole' / Chancelor Linden 35 20 yellow Pyramidal.
Tilia cordata 'De Groot' / Linden 30-50 20 yellow Compact, suckers less than other Lindens.
Tilia cordata 'Greenspire' / Greenspire
Linden 40 30 yellowish Symmetrical pyramidal form.
Tilia cordata 'Littleleaf' / Littleleaf Linden 30-50 30
Deciduous; prefers moist, well-drained soils, but tolerant of a variety of soil
types; tolerant of wind and urban pollution; fast growing and long-lived;
tolerates summer drought and seasonal inundation; provides a dense canopy; C.
cordata is the hardiest Linden; many forms available including, T. cordata
‘Chancellor’, ‘Corzam’, and ’Greenspire’.
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LARGE TREES:
50 feet in height or taller
Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Acer freemanli / Autumn Blaze Maple 50 40 orange
Abies grandis / Grand Fir 100 40
Evergreen; tolerant of fluctuating water tables and floods; medium rate of
growth; root structure depends on site conditions – shallow in moist areas, deep
taproot in drier conditions.
Acer nigrum 'Green Colunm' / Green
Column Maple 50 20
yellow to
orange Good close to buildings.
Acer platanoides 'Emerald Queen' 50 40 yellow
Deciduous; fast growing with an erect, spreading form; prefers moist soils, but is
tolerant of summer drought and seasonal inundation; tolerates urban pollution;
avoid locating near structures due to shallow, vigorous rooting; additional
cultivars available including A. platanoids ‘Parkway’.
Acer pseudoplatanus / Sycamore maple 40-60 25-40
Deciduous; prefers moist, well-drained soils but is adaptable to may soil types;
tolerates summer drought and seasonal inundation; tolerant of urban pollution
with a moderate growth rate; sturdy, resistant to wind and salt spray; a number
of cultivars are available including: A. pseudoplatanus ‘Atropurpureum,’ ‘
Brilliantissimum,’ ‘Cox’ (Lustre), and ‘Puget Pink’.
Acer saccharum 'Bonfire' 50 40
bright
orange
red Fastest growing sugar maple.
Acer saccharum 'Commemoration' 50 35
orange to
orange-
red Resistant to leaf tatter.
Acer saccharum 'Green Mountain' 45 35
red to
orange
Acer saccharum / Sugar maple 60-75 35
yellow,
orange
Deciduous; prefers moderately moist, well-drained soils; long-lived and tolerant
of urban pollutants; slow to medium growth rate; needs large planting area; a
variety of cultivars available including Acer saccharum ‘Legacy’.
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Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Calocedrus decurrens / Incense cedar 75-90 10-20
Evergreen; tolerant of poor soils; drought tolerant after established; tolerant of
wind and urban conditions; narrow growth habit makes this a good choice for
smaller spaces and ideal for screening, fragrant tree; slow growing and long-
lived.
Carpinus betulus / European Hornbeam 40-60 30-40
Deciduous tree: tolerant of urban pollution and poor soils; cultivars available
and suggested include 'Fasigiata' (30-40 ft height) and 'Franz Fontaine' (30-35 ft
height).
Cedrus deodara / Deodar cedar 40-60 20-40
Evergreen; prefers moist, well-drained soils, but drought tolerant when
established; fairly fast growing and long lived; dense, wide spreading canopy;
attractive cultivars available.
Cercidiphyllum japonicum / Katsura Tree 40-60 20-40
apricot,
orange
Deciduous; requires moist soil and does not do well on hot dry sites. Leaves are
heart-shaped.
Cercidiphyllum japonicum / Katsura Tree 40 40
yellow to
orange
Fagus sylvatica / Green Beech 50 40 bronze Silvery-grey bark.
Fraxinus american 'Autumn Purple' /
Autumn Purple White Ash 60-80 50-70
to a dark
purple
Deciduous; prefers moist well-drained soils but tolerates a range of soil types;
Also try 'Rosehill'.
Fraxinus latifolia / Oregon Ash 40-80 30
Deciduous; saturated, ponded or moist soils; flood tolerant; small green-white
flowers; tolerant of poor soils.
Fraxinus pennsylvanica / Green Ash 50 40
Deciduous; prefers moist soils; fast growth rate; salt, seasonal drought and
urban pollution; numerous cultivars including'Patmore' (50-60 ft. height),
'Summit' (to 45 ft. height), and 'Urbanite' (to 50 ft. height).
Fraxinus pennsylvanica 'Patmore' /
Patmore Ash 45 35 yellow Extremely hardy, may be seedless.
Fraxinus pennsylvanica 'Urbanite' / Ash 50 40
deep
bronze
Gleditsia triacanthos inermis 'Skyline' /
Skyline Thornless Honeylocust 60-70 40 yellow
Deciduous; prefers moist soils, but will grow in poor soils; tolerant of drought,
seasonal inundation, and urban pollution; occasionally fruit pods can create
litter during winter months; thornless. Do not confuse with 'Sunburst'.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
APPROVED TREE LIST – Small, Medium, and Large
H:\CED\Data\Forms-Templates\Self-Help Handouts\Planning\treeslist_march2010.doc P. 11
Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Gymnocladus dioicus espresso / Espresso
Kentucky Coffeetree 50 35 yellow Deciduous; drought and variable soil tolerant; seedless.
Liquidamber styraci fleia / American
sweetgum 60-75 40
Deciduous; prefers moist well-drained soils but tolerant of poor soils; drought
tolerant after established; avoid major roadways and restricted sites. Many
cultivars available.
Liriodendron tulipifera / Tulip Tree 60-80 30-60 yellow
Deciduous; prefers moist, deep, well-drained soils, but tolerates poor soils; fast
growing; needs large growing area, lower growing cultivars available such as
'Columnar'. Fast-growing tree.
Metasequoia glyptostoboides / Dawn
redwood 70-100 25
Deciduous; prefers moist, deep, well-drained soils, but tolerates compacted and
poor soils; long-lived, fast growing conifer; tolerant of seasonal inundation and
drought; can grow in standing water; needles turn russet in the fall; needs large
growing area; lower growing cultivars available such as M. glyptostroboides
‘Gold Rush’ and ‘Sheridan Spire’.
Nothofagus antartica / Southern Beech 50 35 none Rugged twisted branching and petite foliage.
Nyssa sylvatica / Tupelo 70+ 20
apricot to
bright red Handsomely chunky bark.
Picca omorika / Serbian spruce 50-60 20-25
Slow growing; tolerant of varying soils and urban pollution; moderately drought
tolerant once established; elegant evergreen spruce, good for narrow locations;
lower growing cultivars available.
Pseudotsuga menziesii / Douglas fir 75-120 40
Evergreen conifer; moist to dry soils; long-lived with a medium to fast rate of
growth; tolerant of summer drought, winter inundation, and poor soils;
withstands wind and urban pollution; provides a nice canopy, but potential
height will restrict placement.
Quercus coccinea / Scarlet oak 50-60 45
brilliant
scarlet to
red
Deciduous; grows in a variety of soil types; long-lived with a moderate growth
rate; tolerant of summer drought and urban pollution; does not tolerate
saturated soils or shade.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
APPROVED TREE LIST – Small, Medium, and Large
H:\CED\Data\Forms-Templates\Self-Help Handouts\Planning\treeslist_march2010.doc P. 12
Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Quercus macrocarpa / Burr oak 70-80 30-40
Prefers moist soils, but is adaptable to varying soils; slow growing and long-lived;
rugged looking deciduous tree; tolerant of seasonal drought and inundation;
tolerates urban pollution and city conditions; provides a wide-spreading, dense
canopy.
Quercus phellos / Willow oak 60-70 50
Deciduous; prefers moist, well-drained soils, but grows in a wide range of soils
types; long-lived tree with moderate growth rate and fibrous root system;
tolerant of seasonal drought and inundation, as well as urban pollution; provides
a wide-spreading, dense canopy; small delicate leaves.
Quercus palustris 'Crownright' 80 40 More upright form of Pin Oak.
Quercus robar / English oak 40-60+ 40
Prefers well-drained soil; slow to moderate growth rate; long-lived deciduous
tree; tolerant of seasonal drought and inundation; tolerates urban pollution,
poor soils and constrained root space; susceptible to powdery mildew; many
varieties and cultivars available including: ‘Concordia,’ ‘Fastigiata,’ ‘Foliis
Variegatis, and ’Westminster Globe.’
Quercus rubra / Northern red oak 60-75 50
Prefers moist, well-drained soils, but drought tolerant when established;
tolerates seasonal inundation, urban pollution and salt spray; moderate rate of
growth and longevity; provides a dense, wide-spreading canopy; susceptible to
oak wilt fungus.
Quercus shumardii / Shumard's oak to 70 50
Prefers moist, well-drained soils; deciduous, long-lived tree; tolerant of seasonal
drought and inundation, urban pollution and poor soils.
Taxodium distichum / Bald cypress to 75 40
Deciduous conifer; wet, mucky soils; tolerant of summer drought and seasonal
flooding; will grow in poor soils; slow growing; long-lived with a wide-spreading
canopy; roots do not appear to lift sidewalks as readily as other species; prune
lower branches for sight-lines; cultivars include T. distichum ‘Shawnee Brave’.
Thuja plicata / Western red cedar 200+ 60
Moist to swampy soils; evergreen tree tolerant of seasonal flooding and
saturated soils; a good tree for screening; long-lived; cultivars ‘Pumilio’ and
‘Cuprea’ are shorter versions, ‘Aurea’ and ‘Atrovirens’ have distinctive foliage.
Tilia americana x euchlora 'Redmond' /
Redmond Linden 50 35 yellow
Prefers moist, rich soils, but tolerant of a variety of soils; tolerant of seasonal
drought and inundation, urban pollution and poor soils; deciduous tree
resistant; also try 'Sentry' and 'Boulevard'.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
APPROVED TREE LIST – Small, Medium, and Large
H:\CED\Data\Forms-Templates\Self-Help Handouts\Planning\treeslist_march2010.doc P. 13
Botanical name / Common Name
Mature
Height
in Feet
Mature
Spread
in Feet Fall Color Comments
Tilia plalyphyllos / Bigleaf linden 60-80 60
Prefers moist, well-drained soils, but grows in a variety of soil types; deciduous
tree with medium growth rate; long-lived; tolerant of seasonal drought and
inundation; tolerates urban pollutants; provides a wide-spreading, dense
canopy; yellowish-white flowers attract bees.
Tilia tomentosa / Silver Linden 40-75 25-45
Deciduous; prefers moist, well-drained soils, but drought tolerant when
established; urban tolerant. Cultivars include 'sterlay' and 'Green Mountain'.
Ulmus ssp. / Elm hybrids 50-60 35-50 yellow
Deciduous; prefers moist, well-drained soils, but drought tolerant; rapid grower;
a hybrid elm resistant to Dutch elm disease; suggested hybrids include
‘Accolade’, ‘Homestead’ and ‘Pioneer’.
Ulmus 'Homestead' / Homestead Elm 60 35 yellow
Ulmus parvifolia / Lace Bark Elm 50 40
Deciduous; prefers moist, well drained soils but tolerant of soil types and hot dry
conditions. Flaking bark of orange, gray, green and brown color. Several cultivars
including 'Allee' and 'Bosque'.
Ulmus 'Pioneer' / Pioneer Elm 60 50 yellow Resistant to Dutch elm disease.
Umbellularia californica / Oregon myrtle 40-75+ to 50
Prefers moist, well-drained soils; slow growing evergreen tree with aromatic
leaves; tolerates seasonal drought and inundation; tolerant of urban pollution;
provides a wide spreading, dense canopy; resistant to pests and disease; good
for tall hedges or, when trunks are thinned, as a street tree; requires summer
watering until established.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Site Planning
Civil Engineering
Landscape Architecture
Project Management
Land Use Consulting
APPENDIX C
WWHM REPORTS
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
WWHM2012
PROJECT REPORT
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:32:21 AM Page 2
General Model Information
Project Name:Total Basin peak flows
Site Name:Harrington Redevelopment
Site Address:960 Harrington Ave NE
City:Renton
Report Date:6/10/2021
Gage:Seatac
Data Start:1948/10/01
Data End:2009/09/30
Timestep:15 Minute
Precip Scale:1.000
Version Date:2019/09/13
Version:4.2.17
POC Thresholds
Low Flow Threshold for POC1:50 Percent of the 2 Year
High Flow Threshold for POC1:50 Year
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Landuse Basin Data
Predeveloped Land Use
North Basin
Bypass:No
GroundWater:No
Pervious Land Use acre
A B, Lawn, Mod 0.05
Pervious Total 0.05
Impervious Land Use acre
ROADS FLAT 0.22
Impervious Total 0.22
Basin Total 0.27
Element Flows To:
Surface Interflow Groundwater
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:32:21 AM Page 4
Upstream Flow-Through
Bypass:No
GroundWater:No
Pervious Land Use acre
Pervious Total 0
Impervious Land Use acre
DRIVEWAYS MOD 0.087
Impervious Total 0.087
Basin Total 0.087
Element Flows To:
Surface Interflow Groundwater
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:32:21 AM Page 5
South Basin
Bypass:No
GroundWater:No
Pervious Land Use acre
A B, Lawn, Mod 0.02
Pervious Total 0.02
Impervious Land Use acre
ROADS FLAT 0.38
Impervious Total 0.38
Basin Total 0.4
Element Flows To:
Surface Interflow Groundwater
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:32:21 AM Page 6
North Frontage
Bypass:No
GroundWater:No
Pervious Land Use acre
A B, Lawn, Mod 0.03
Pervious Total 0.03
Impervious Land Use acre
ROADS FLAT 0.03
Impervious Total 0.03
Basin Total 0.06
Element Flows To:
Surface Interflow Groundwater
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:32:21 AM Page 7
South Frontage
Bypass:No
GroundWater:No
Pervious Land Use acre
A B, Lawn, Mod 0.01
Pervious Total 0.01
Impervious Land Use acre
ROADS FLAT 0.11
Impervious Total 0.11
Basin Total 0.12
Element Flows To:
Surface Interflow Groundwater
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:32:21 AM Page 8
Mitigated Land Use
North Basin
Bypass:No
GroundWater:No
Pervious Land Use acre
A B, Lawn, Flat 0.05
Pervious Total 0.05
Impervious Land Use acre
ROADS FLAT 0.23
Impervious Total 0.23
Basin Total 0.28
Element Flows To:
Surface Interflow Groundwater
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:32:21 AM Page 9
Upstream Flow-Through
Bypass:No
GroundWater:No
Pervious Land Use acre
Pervious Total 0
Impervious Land Use acre
DRIVEWAYS MOD 0.087
Impervious Total 0.087
Basin Total 0.087
Element Flows To:
Surface Interflow Groundwater
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:32:21 AM Page 10
South Basin
Bypass:No
GroundWater:No
Pervious Land Use acre
A B, Lawn, Flat 0.05
Pervious Total 0.05
Impervious Land Use acre
ROADS FLAT 0.35
Impervious Total 0.35
Basin Total 0.4
Element Flows To:
Surface Interflow Groundwater
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:32:21 AM Page 11
North Frontage
Bypass:No
GroundWater:No
Pervious Land Use acre
A B, Lawn, Flat 0.03
Pervious Total 0.03
Impervious Land Use acre
ROADS FLAT 0.04
Impervious Total 0.04
Basin Total 0.07
Element Flows To:
Surface Interflow Groundwater
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:32:21 AM Page 12
South Frontage
Bypass:No
GroundWater:No
Pervious Land Use acre
A B, Lawn, Flat 0.06
Pervious Total 0.06
Impervious Land Use acre
ROADS FLAT 0.06
Impervious Total 0.06
Basin Total 0.12
Element Flows To:
Surface Interflow Groundwater
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:32:21 AM Page 13
Routing Elements
Predeveloped Routing
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Mitigated Routing
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Analysis Results
POC 1
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #1
Total Pervious Area:0.11
Total Impervious Area:0.827
Mitigated Landuse Totals for POC #1
Total Pervious Area:0.19
Total Impervious Area:0.767
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #1
Return Period Flow(cfs)
2 year 0.320762
5 year 0.405842
10 year 0.463723
25 year 0.538879
50 year 0.596453
100 year 0.655467
Flow Frequency Return Periods for Mitigated. POC #1
Return Period Flow(cfs)
2 year 0.298238
5 year 0.377691
10 year 0.431783
25 year 0.502057
50 year 0.555918
100 year 0.611147
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #1
Year Predeveloped Mitigated
1949 0.415 0.386
1950 0.446 0.414
1951 0.262 0.244
1952 0.227 0.211
1953 0.249 0.232
1954 0.262 0.243
1955 0.297 0.276
1956 0.287 0.267
1957 0.327 0.303
1958 0.266 0.247
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:33:06 AM Page 16
1959 0.274 0.254
1960 0.268 0.249
1961 0.277 0.257
1962 0.244 0.226
1963 0.274 0.255
1964 0.269 0.250
1965 0.337 0.313
1966 0.224 0.208
1967 0.389 0.361
1968 0.451 0.419
1969 0.306 0.284
1970 0.298 0.277
1971 0.356 0.331
1972 0.371 0.348
1973 0.224 0.208
1974 0.326 0.303
1975 0.372 0.345
1976 0.254 0.236
1977 0.272 0.253
1978 0.341 0.317
1979 0.459 0.426
1980 0.405 0.377
1981 0.332 0.308
1982 0.469 0.435
1983 0.382 0.355
1984 0.239 0.222
1985 0.329 0.305
1986 0.287 0.266
1987 0.443 0.411
1988 0.269 0.250
1989 0.351 0.326
1990 0.589 0.561
1991 0.464 0.433
1992 0.238 0.221
1993 0.211 0.197
1994 0.229 0.212
1995 0.295 0.274
1996 0.329 0.308
1997 0.308 0.287
1998 0.310 0.288
1999 0.637 0.592
2000 0.315 0.292
2001 0.351 0.326
2002 0.400 0.371
2003 0.324 0.302
2004 0.599 0.557
2005 0.268 0.249
2006 0.242 0.226
2007 0.561 0.521
2008 0.449 0.418
2009 0.412 0.383
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #1
Rank Predeveloped Mitigated
1 0.6375 0.5920
2 0.5992 0.5615
3 0.5895 0.5568
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:33:06 AM Page 17
4 0.5606 0.5209
5 0.4687 0.4350
6 0.4637 0.4333
7 0.4588 0.4263
8 0.4512 0.4195
9 0.4486 0.4177
10 0.4459 0.4138
11 0.4432 0.4113
12 0.4150 0.3855
13 0.4119 0.3830
14 0.4049 0.3770
15 0.4000 0.3711
16 0.3891 0.3612
17 0.3823 0.3549
18 0.3720 0.3485
19 0.3711 0.3452
20 0.3563 0.3309
21 0.3510 0.3265
22 0.3507 0.3262
23 0.3409 0.3171
24 0.3370 0.3131
25 0.3318 0.3084
26 0.3293 0.3079
27 0.3288 0.3055
28 0.3266 0.3031
29 0.3259 0.3027
30 0.3245 0.3022
31 0.3147 0.2921
32 0.3099 0.2877
33 0.3077 0.2866
34 0.3063 0.2842
35 0.2980 0.2767
36 0.2971 0.2760
37 0.2950 0.2738
38 0.2874 0.2667
39 0.2867 0.2661
40 0.2772 0.2570
41 0.2743 0.2550
42 0.2738 0.2544
43 0.2720 0.2525
44 0.2695 0.2502
45 0.2689 0.2498
46 0.2684 0.2490
47 0.2679 0.2490
48 0.2658 0.2468
49 0.2617 0.2444
50 0.2616 0.2433
51 0.2540 0.2361
52 0.2495 0.2317
53 0.2439 0.2264
54 0.2420 0.2260
55 0.2393 0.2220
56 0.2377 0.2206
57 0.2285 0.2124
58 0.2270 0.2106
59 0.2243 0.2081
60 0.2240 0.2081
61 0.2108 0.1966
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Duration Flows
The Facility PASSED
Flow(cfs)Predev Mit Percentage Pass/Fail
0.1604 1756 1341 76 Pass
0.1648 1609 1213 75 Pass
0.1692 1428 1078 75 Pass
0.1736 1319 983 74 Pass
0.1780 1173 882 75 Pass
0.1824 1077 825 76 Pass
0.1868 991 752 75 Pass
0.1912 895 679 75 Pass
0.1956 836 629 75 Pass
0.2000 755 572 75 Pass
0.2044 705 530 75 Pass
0.2088 647 487 75 Pass
0.2132 600 440 73 Pass
0.2176 556 411 73 Pass
0.2220 510 384 75 Pass
0.2265 471 361 76 Pass
0.2309 433 336 77 Pass
0.2353 407 303 74 Pass
0.2397 383 289 75 Pass
0.2441 354 259 73 Pass
0.2485 333 245 73 Pass
0.2529 306 228 74 Pass
0.2573 288 210 72 Pass
0.2617 264 200 75 Pass
0.2661 246 181 73 Pass
0.2705 233 172 73 Pass
0.2749 218 164 75 Pass
0.2793 202 148 73 Pass
0.2837 187 142 75 Pass
0.2881 177 128 72 Pass
0.2925 166 121 72 Pass
0.2969 159 113 71 Pass
0.3013 146 109 74 Pass
0.3057 138 101 73 Pass
0.3101 128 92 71 Pass
0.3145 120 90 75 Pass
0.3190 112 87 77 Pass
0.3234 110 78 70 Pass
0.3278 102 74 72 Pass
0.3322 92 68 73 Pass
0.3366 91 63 69 Pass
0.3410 88 61 69 Pass
0.3454 81 57 70 Pass
0.3498 78 53 67 Pass
0.3542 71 52 73 Pass
0.3586 66 48 72 Pass
0.3630 61 46 75 Pass
0.3674 59 44 74 Pass
0.3718 57 41 71 Pass
0.3762 53 38 71 Pass
0.3806 52 33 63 Pass
0.3850 49 31 63 Pass
0.3894 48 29 60 Pass
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
Total Basin peak flows 6/10/2021 8:33:06 AM Page 20
0.3938 46 27 58 Pass
0.3982 42 23 54 Pass
0.4026 39 22 56 Pass
0.4070 36 20 55 Pass
0.4115 31 20 64 Pass
0.4159 30 17 56 Pass
0.4203 27 14 51 Pass
0.4247 25 14 56 Pass
0.4291 23 13 56 Pass
0.4335 22 13 59 Pass
0.4379 20 10 50 Pass
0.4423 20 8 40 Pass
0.4467 17 8 47 Pass
0.4511 15 8 53 Pass
0.4555 14 8 57 Pass
0.4599 13 8 61 Pass
0.4643 11 8 72 Pass
0.4687 9 8 88 Pass
0.4731 8 8 100 Pass
0.4775 8 8 100 Pass
0.4819 8 8 100 Pass
0.4863 8 8 100 Pass
0.4907 8 7 87 Pass
0.4951 8 7 87 Pass
0.4995 8 7 87 Pass
0.5040 8 7 87 Pass
0.5084 8 7 87 Pass
0.5128 8 6 75 Pass
0.5172 8 5 62 Pass
0.5216 8 4 50 Pass
0.5260 8 4 50 Pass
0.5304 7 3 42 Pass
0.5348 6 3 50 Pass
0.5392 6 3 50 Pass
0.5436 6 3 50 Pass
0.5480 6 3 50 Pass
0.5524 6 3 50 Pass
0.5568 5 3 60 Pass
0.5612 4 2 50 Pass
0.5656 4 1 25 Pass
0.5700 3 1 33 Pass
0.5744 3 1 33 Pass
0.5788 3 1 33 Pass
0.5832 3 1 33 Pass
0.5876 3 1 33 Pass
0.5920 2 1 50 Pass
0.5965 2 0 0 Pass
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Water Quality
Water Quality BMP Flow and Volume for POC #1
On-line facility volume:0 acre-feet
On-line facility target flow:0 cfs.
Adjusted for 15 min:0 cfs.
Off-line facility target flow:0 cfs.
Adjusted for 15 min:0 cfs.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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LID Report
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Model Default Modifications
Total of 0 changes have been made.
PERLND Changes
No PERLND changes have been made.
IMPLND Changes
No IMPLND changes have been made.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Appendix
Predeveloped Schematic
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Mitigated Schematic
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Predeveloped UCI File
RUN
GLOBAL
WWHM4 model simulation
START 1948 10 01 END 2009 09 30
RUN INTERP OUTPUT LEVEL 3 0
RESUME 0 RUN 1 UNIT SYSTEM 1
END GLOBAL
FILES
<File> <Un#> <-----------File Name------------------------------>***
<-ID-> ***
WDM 26 Total Basin peak flows.wdm
MESSU 25 PreTotal Basin peak flows.MES
27 PreTotal Basin peak flows.L61
28 PreTotal Basin peak flows.L62
30 POCTotal Basin peak flows1.dat
END FILES
OPN SEQUENCE
INGRP INDELT 00:15
PERLND 8
IMPLND 1
IMPLND 6
COPY 501
DISPLY 1
END INGRP
END OPN SEQUENCE
DISPLY
DISPLY-INFO1
# - #<----------Title----------->***TRAN PIVL DIG1 FIL1 PYR DIG2 FIL2 YRND
1 North Basin MAX 1 2 30 9
END DISPLY-INFO1
END DISPLY
COPY
TIMESERIES
# - # NPT NMN ***
1 1 1
501 1 1
END TIMESERIES
END COPY
GENER
OPCODE
# # OPCD ***
END OPCODE
PARM
# # K ***
END PARM
END GENER
PERLND
GEN-INFO
<PLS ><-------Name------->NBLKS Unit-systems Printer ***
# - # User t-series Engl Metr ***
in out ***
8 A/B, Lawn, Mod 1 1 1 1 27 0
END GEN-INFO
*** Section PWATER***
ACTIVITY
<PLS > ************* Active Sections *****************************
# - # ATMP SNOW PWAT SED PST PWG PQAL MSTL PEST NITR PHOS TRAC ***
8 0 0 1 0 0 0 0 0 0 0 0 0
END ACTIVITY
PRINT-INFO
<PLS > ***************** Print-flags ***************************** PIVL PYR
# - # ATMP SNOW PWAT SED PST PWG PQAL MSTL PEST NITR PHOS TRAC *********
8 0 0 4 0 0 0 0 0 0 0 0 0 1 9
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END PRINT-INFO
PWAT-PARM1
<PLS > PWATER variable monthly parameter value flags ***
# - # CSNO RTOP UZFG VCS VUZ VNN VIFW VIRC VLE INFC HWT ***
8 0 0 0 0 0 0 0 0 0 0 0
END PWAT-PARM1
PWAT-PARM2
<PLS > PWATER input info: Part 2 ***
# - # ***FOREST LZSN INFILT LSUR SLSUR KVARY AGWRC
8 0 5 0.8 400 0.1 0.3 0.996
END PWAT-PARM2
PWAT-PARM3
<PLS > PWATER input info: Part 3 ***
# - # ***PETMAX PETMIN INFEXP INFILD DEEPFR BASETP AGWETP
8 0 0 2 2 0 0 0
END PWAT-PARM3
PWAT-PARM4
<PLS > PWATER input info: Part 4 ***
# - # CEPSC UZSN NSUR INTFW IRC LZETP ***
8 0.1 0.5 0.25 0 0.7 0.25
END PWAT-PARM4
PWAT-STATE1
<PLS > *** Initial conditions at start of simulation
ran from 1990 to end of 1992 (pat 1-11-95) RUN 21 ***
# - # *** CEPS SURS UZS IFWS LZS AGWS GWVS
8 0 0 0 0 3 1 0
END PWAT-STATE1
END PERLND
IMPLND
GEN-INFO
<PLS ><-------Name-------> Unit-systems Printer ***
# - # User t-series Engl Metr ***
in out ***
1 ROADS/FLAT 1 1 1 27 0
6 DRIVEWAYS/MOD 1 1 1 27 0
END GEN-INFO
*** Section IWATER***
ACTIVITY
<PLS > ************* Active Sections *****************************
# - # ATMP SNOW IWAT SLD IWG IQAL ***
1 0 0 1 0 0 0
6 0 0 1 0 0 0
END ACTIVITY
PRINT-INFO
<ILS > ******** Print-flags ******** PIVL PYR
# - # ATMP SNOW IWAT SLD IWG IQAL *********
1 0 0 4 0 0 0 1 9
6 0 0 4 0 0 0 1 9
END PRINT-INFO
IWAT-PARM1
<PLS > IWATER variable monthly parameter value flags ***
# - # CSNO RTOP VRS VNN RTLI ***
1 0 0 0 0 0
6 0 0 0 0 0
END IWAT-PARM1
IWAT-PARM2
<PLS > IWATER input info: Part 2 ***
# - # *** LSUR SLSUR NSUR RETSC
1 400 0.01 0.1 0.1
6 400 0.05 0.1 0.08
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END IWAT-PARM2
IWAT-PARM3
<PLS > IWATER input info: Part 3 ***
# - # ***PETMAX PETMIN
1 0 0
6 0 0
END IWAT-PARM3
IWAT-STATE1
<PLS > *** Initial conditions at start of simulation
# - # *** RETS SURS
1 0 0
6 0 0
END IWAT-STATE1
END IMPLND
SCHEMATIC
<-Source-> <--Area--> <-Target-> MBLK ***
<Name> # <-factor-> <Name> # Tbl# ***
North Basin***
PERLND 8 0.05 COPY 501 12
PERLND 8 0.05 COPY 501 13
IMPLND 1 0.22 COPY 501 15
Upstream Flow-Through***
IMPLND 6 0.087 COPY 501 15
South Basin***
PERLND 8 0.02 COPY 501 12
PERLND 8 0.02 COPY 501 13
IMPLND 1 0.38 COPY 501 15
North Frontage***
PERLND 8 0.03 COPY 501 12
PERLND 8 0.03 COPY 501 13
IMPLND 1 0.03 COPY 501 15
South Frontage***
PERLND 8 0.01 COPY 501 12
PERLND 8 0.01 COPY 501 13
IMPLND 1 0.11 COPY 501 15
******Routing******
END SCHEMATIC
NETWORK
<-Volume-> <-Grp> <-Member-><--Mult-->Tran <-Target vols> <-Grp> <-Member-> ***
<Name> # <Name> # #<-factor->strg <Name> # # <Name> # # ***
COPY 501 OUTPUT MEAN 1 1 48.4 DISPLY 1 INPUT TIMSER 1
<-Volume-> <-Grp> <-Member-><--Mult-->Tran <-Target vols> <-Grp> <-Member-> ***
<Name> # <Name> # #<-factor->strg <Name> # # <Name> # # ***
END NETWORK
RCHRES
GEN-INFO
RCHRES Name Nexits Unit Systems Printer ***
# - #<------------------><---> User T-series Engl Metr LKFG ***
in out ***
END GEN-INFO
*** Section RCHRES***
ACTIVITY
<PLS > ************* Active Sections *****************************
# - # HYFG ADFG CNFG HTFG SDFG GQFG OXFG NUFG PKFG PHFG ***
END ACTIVITY
PRINT-INFO
<PLS > ***************** Print-flags ******************* PIVL PYR
# - # HYDR ADCA CONS HEAT SED GQL OXRX NUTR PLNK PHCB PIVL PYR *********
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END PRINT-INFO
HYDR-PARM1
RCHRES Flags for each HYDR Section ***
# - # VC A1 A2 A3 ODFVFG for each *** ODGTFG for each FUNCT for each
FG FG FG FG possible exit *** possible exit possible exit
* * * * * * * * * * * * * * ***
END HYDR-PARM1
HYDR-PARM2
# - # FTABNO LEN DELTH STCOR KS DB50 ***
<------><--------><--------><--------><--------><--------><--------> ***
END HYDR-PARM2
HYDR-INIT
RCHRES Initial conditions for each HYDR section ***
# - # *** VOL Initial value of COLIND Initial value of OUTDGT
*** ac-ft for each possible exit for each possible exit
<------><--------> <---><---><---><---><---> *** <---><---><---><---><--->
END HYDR-INIT
END RCHRES
SPEC-ACTIONS
END SPEC-ACTIONS
FTABLES
END FTABLES
EXT SOURCES
<-Volume-> <Member> SsysSgap<--Mult-->Tran <-Target vols> <-Grp> <-Member-> ***
<Name> # <Name> # tem strg<-factor->strg <Name> # # <Name> # # ***
WDM 2 PREC ENGL 1 PERLND 1 999 EXTNL PREC
WDM 2 PREC ENGL 1 IMPLND 1 999 EXTNL PREC
WDM 1 EVAP ENGL 0.76 PERLND 1 999 EXTNL PETINP
WDM 1 EVAP ENGL 0.76 IMPLND 1 999 EXTNL PETINP
END EXT SOURCES
EXT TARGETS
<-Volume-> <-Grp> <-Member-><--Mult-->Tran <-Volume-> <Member> Tsys Tgap Amd ***
<Name> # <Name> # #<-factor->strg <Name> # <Name> tem strg strg***
COPY 501 OUTPUT MEAN 1 1 48.4 WDM 501 FLOW ENGL REPL
END EXT TARGETS
MASS-LINK
<Volume> <-Grp> <-Member-><--Mult--> <Target> <-Grp> <-Member->***
<Name> <Name> # #<-factor-> <Name> <Name> # #***
MASS-LINK 12
PERLND PWATER SURO 0.083333 COPY INPUT MEAN
END MASS-LINK 12
MASS-LINK 13
PERLND PWATER IFWO 0.083333 COPY INPUT MEAN
END MASS-LINK 13
MASS-LINK 15
IMPLND IWATER SURO 0.083333 COPY INPUT MEAN
END MASS-LINK 15
END MASS-LINK
END RUN
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Mitigated UCI File
RUN
GLOBAL
WWHM4 model simulation
START 1948 10 01 END 2009 09 30
RUN INTERP OUTPUT LEVEL 3 0
RESUME 0 RUN 1 UNIT SYSTEM 1
END GLOBAL
FILES
<File> <Un#> <-----------File Name------------------------------>***
<-ID-> ***
WDM 26 Total Basin peak flows.wdm
MESSU 25 MitTotal Basin peak flows.MES
27 MitTotal Basin peak flows.L61
28 MitTotal Basin peak flows.L62
30 POCTotal Basin peak flows1.dat
END FILES
OPN SEQUENCE
INGRP INDELT 00:15
PERLND 7
IMPLND 1
IMPLND 6
COPY 501
DISPLY 1
END INGRP
END OPN SEQUENCE
DISPLY
DISPLY-INFO1
# - #<----------Title----------->***TRAN PIVL DIG1 FIL1 PYR DIG2 FIL2 YRND
1 North Basin MAX 1 2 30 9
END DISPLY-INFO1
END DISPLY
COPY
TIMESERIES
# - # NPT NMN ***
1 1 1
501 1 1
END TIMESERIES
END COPY
GENER
OPCODE
# # OPCD ***
END OPCODE
PARM
# # K ***
END PARM
END GENER
PERLND
GEN-INFO
<PLS ><-------Name------->NBLKS Unit-systems Printer ***
# - # User t-series Engl Metr ***
in out ***
7 A/B, Lawn, Flat 1 1 1 1 27 0
END GEN-INFO
*** Section PWATER***
ACTIVITY
<PLS > ************* Active Sections *****************************
# - # ATMP SNOW PWAT SED PST PWG PQAL MSTL PEST NITR PHOS TRAC ***
7 0 0 1 0 0 0 0 0 0 0 0 0
END ACTIVITY
PRINT-INFO
<PLS > ***************** Print-flags ***************************** PIVL PYR
# - # ATMP SNOW PWAT SED PST PWG PQAL MSTL PEST NITR PHOS TRAC *********
7 0 0 4 0 0 0 0 0 0 0 0 0 1 9
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END PRINT-INFO
PWAT-PARM1
<PLS > PWATER variable monthly parameter value flags ***
# - # CSNO RTOP UZFG VCS VUZ VNN VIFW VIRC VLE INFC HWT ***
7 0 0 0 0 0 0 0 0 0 0 0
END PWAT-PARM1
PWAT-PARM2
<PLS > PWATER input info: Part 2 ***
# - # ***FOREST LZSN INFILT LSUR SLSUR KVARY AGWRC
7 0 5 0.8 400 0.05 0.3 0.996
END PWAT-PARM2
PWAT-PARM3
<PLS > PWATER input info: Part 3 ***
# - # ***PETMAX PETMIN INFEXP INFILD DEEPFR BASETP AGWETP
7 0 0 2 2 0 0 0
END PWAT-PARM3
PWAT-PARM4
<PLS > PWATER input info: Part 4 ***
# - # CEPSC UZSN NSUR INTFW IRC LZETP ***
7 0.1 0.5 0.25 0 0.7 0.25
END PWAT-PARM4
PWAT-STATE1
<PLS > *** Initial conditions at start of simulation
ran from 1990 to end of 1992 (pat 1-11-95) RUN 21 ***
# - # *** CEPS SURS UZS IFWS LZS AGWS GWVS
7 0 0 0 0 3 1 0
END PWAT-STATE1
END PERLND
IMPLND
GEN-INFO
<PLS ><-------Name-------> Unit-systems Printer ***
# - # User t-series Engl Metr ***
in out ***
1 ROADS/FLAT 1 1 1 27 0
6 DRIVEWAYS/MOD 1 1 1 27 0
END GEN-INFO
*** Section IWATER***
ACTIVITY
<PLS > ************* Active Sections *****************************
# - # ATMP SNOW IWAT SLD IWG IQAL ***
1 0 0 1 0 0 0
6 0 0 1 0 0 0
END ACTIVITY
PRINT-INFO
<ILS > ******** Print-flags ******** PIVL PYR
# - # ATMP SNOW IWAT SLD IWG IQAL *********
1 0 0 4 0 0 0 1 9
6 0 0 4 0 0 0 1 9
END PRINT-INFO
IWAT-PARM1
<PLS > IWATER variable monthly parameter value flags ***
# - # CSNO RTOP VRS VNN RTLI ***
1 0 0 0 0 0
6 0 0 0 0 0
END IWAT-PARM1
IWAT-PARM2
<PLS > IWATER input info: Part 2 ***
# - # *** LSUR SLSUR NSUR RETSC
1 400 0.01 0.1 0.1
6 400 0.05 0.1 0.08
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END IWAT-PARM2
IWAT-PARM3
<PLS > IWATER input info: Part 3 ***
# - # ***PETMAX PETMIN
1 0 0
6 0 0
END IWAT-PARM3
IWAT-STATE1
<PLS > *** Initial conditions at start of simulation
# - # *** RETS SURS
1 0 0
6 0 0
END IWAT-STATE1
END IMPLND
SCHEMATIC
<-Source-> <--Area--> <-Target-> MBLK ***
<Name> # <-factor-> <Name> # Tbl# ***
North Basin***
PERLND 7 0.05 COPY 501 12
PERLND 7 0.05 COPY 501 13
IMPLND 1 0.23 COPY 501 15
Upstream Flow-Through***
IMPLND 6 0.087 COPY 501 15
South Basin***
PERLND 7 0.05 COPY 501 12
PERLND 7 0.05 COPY 501 13
IMPLND 1 0.35 COPY 501 15
North Frontage***
PERLND 7 0.03 COPY 501 12
PERLND 7 0.03 COPY 501 13
IMPLND 1 0.04 COPY 501 15
South Frontage***
PERLND 7 0.06 COPY 501 12
PERLND 7 0.06 COPY 501 13
IMPLND 1 0.06 COPY 501 15
******Routing******
END SCHEMATIC
NETWORK
<-Volume-> <-Grp> <-Member-><--Mult-->Tran <-Target vols> <-Grp> <-Member-> ***
<Name> # <Name> # #<-factor->strg <Name> # # <Name> # # ***
COPY 501 OUTPUT MEAN 1 1 48.4 DISPLY 1 INPUT TIMSER 1
<-Volume-> <-Grp> <-Member-><--Mult-->Tran <-Target vols> <-Grp> <-Member-> ***
<Name> # <Name> # #<-factor->strg <Name> # # <Name> # # ***
END NETWORK
RCHRES
GEN-INFO
RCHRES Name Nexits Unit Systems Printer ***
# - #<------------------><---> User T-series Engl Metr LKFG ***
in out ***
END GEN-INFO
*** Section RCHRES***
ACTIVITY
<PLS > ************* Active Sections *****************************
# - # HYFG ADFG CNFG HTFG SDFG GQFG OXFG NUFG PKFG PHFG ***
END ACTIVITY
PRINT-INFO
<PLS > ***************** Print-flags ******************* PIVL PYR
# - # HYDR ADCA CONS HEAT SED GQL OXRX NUTR PLNK PHCB PIVL PYR *********
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END PRINT-INFO
HYDR-PARM1
RCHRES Flags for each HYDR Section ***
# - # VC A1 A2 A3 ODFVFG for each *** ODGTFG for each FUNCT for each
FG FG FG FG possible exit *** possible exit possible exit
* * * * * * * * * * * * * * ***
END HYDR-PARM1
HYDR-PARM2
# - # FTABNO LEN DELTH STCOR KS DB50 ***
<------><--------><--------><--------><--------><--------><--------> ***
END HYDR-PARM2
HYDR-INIT
RCHRES Initial conditions for each HYDR section ***
# - # *** VOL Initial value of COLIND Initial value of OUTDGT
*** ac-ft for each possible exit for each possible exit
<------><--------> <---><---><---><---><---> *** <---><---><---><---><--->
END HYDR-INIT
END RCHRES
SPEC-ACTIONS
END SPEC-ACTIONS
FTABLES
END FTABLES
EXT SOURCES
<-Volume-> <Member> SsysSgap<--Mult-->Tran <-Target vols> <-Grp> <-Member-> ***
<Name> # <Name> # tem strg<-factor->strg <Name> # # <Name> # # ***
WDM 2 PREC ENGL 1 PERLND 1 999 EXTNL PREC
WDM 2 PREC ENGL 1 IMPLND 1 999 EXTNL PREC
WDM 1 EVAP ENGL 0.76 PERLND 1 999 EXTNL PETINP
WDM 1 EVAP ENGL 0.76 IMPLND 1 999 EXTNL PETINP
END EXT SOURCES
EXT TARGETS
<-Volume-> <-Grp> <-Member-><--Mult-->Tran <-Volume-> <Member> Tsys Tgap Amd ***
<Name> # <Name> # #<-factor->strg <Name> # <Name> tem strg strg***
COPY 1 OUTPUT MEAN 1 1 48.4 WDM 701 FLOW ENGL REPL
COPY 501 OUTPUT MEAN 1 1 48.4 WDM 801 FLOW ENGL REPL
END EXT TARGETS
MASS-LINK
<Volume> <-Grp> <-Member-><--Mult--> <Target> <-Grp> <-Member->***
<Name> <Name> # #<-factor-> <Name> <Name> # #***
MASS-LINK 12
PERLND PWATER SURO 0.083333 COPY INPUT MEAN
END MASS-LINK 12
MASS-LINK 13
PERLND PWATER IFWO 0.083333 COPY INPUT MEAN
END MASS-LINK 13
MASS-LINK 15
IMPLND IWATER SURO 0.083333 COPY INPUT MEAN
END MASS-LINK 15
END MASS-LINK
END RUN
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Predeveloped HSPF Message File
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Mitigated HSPF Message File
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Disclaimer
Legal Notice
This program and accompanying documentation are provided 'as-is' without warranty of any kind. The
entire risk regarding the performance and results of this program is assumed by End User. Clear
Creek Solutions Inc. and the governmental licensee or sublicensees disclaim all warranties, either
expressed or implied, including but not limited to implied warranties of program and accompanying
documentation. In no event shall Clear Creek Solutions Inc. be liable for any damages whatsoever
(including without limitation to damages for loss of business profits, loss of business information,
business interruption, and the like) arising out of the use of, or inability to use this program even
if Clear Creek Solutions Inc. or their authorized representatives have been advised of the
possibility of such damages. Software Copyright © by : Clear Creek Solutions, Inc. 2005-2021; All
Rights Reserved.
Clear Creek Solutions, Inc.
6200 Capitol Blvd. Ste F
Olympia, WA. 98501
Toll Free 1(866)943-0304
Local (360)943-0304
www.clearcreeksolutions.com
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APPENDIX D
DOWNSTREAM ANALYSIS & OFF-SITE PHOTOS
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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Offsite Drainage Map
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
OFF-SITE ANALYSIS DRAINAGE SYSTEM TABLE
SURFACE WATER DESIGN MANUAL, CORE REQUIREMENT #2
Basin: East Lake Washington - Renton Subbasin Name: North Renton Basin Subbasin Number:
Symbol Drainage
Component Type,
Name, and Size
Drainage
Component
Description
Slope Distance
from site
discharge
Existing
Problems
Potential
Problems
Observations of field
inspector, resource
reviewer, or resident
see map Type: sheet flow, swale,
stream, channel, pipe,
pond; Size: diameter,
surface area
drainage basin, vegetation,
cover, depth, type of sensitive
area, volume
% ¼ ml = 1,320 ft. constrictions, under capacity, ponding,
overtopping, flooding, habitat or organism
destruction, scouring, bank sloughing,
sedimentation, incision, other erosion
tributary area, likelihood of problem,
overflow pathways, potential impacts
A 24” Conc. Pipe Existing SD System 2.18% 0’-59’ None Observed None Observed -
B 12” Conc. Pipe Existing SD System 2.90% 59’-249’ None Observed None Observed -
C 12” Conc. Pipe Existing SD System 3.74% 249’-344’ None Observed None Observed -
D 12” Conc. Pipe Existing SD System 6.63% 344’-482’ None Observed None Observed -
E 20” Conc. Pipe Existing SD System - 482’-879’ None Observed None Observed No more pipe data available.
F 24” Conc. Pipe Existing SD System 0.67% 879’-1093’ None Observed None Observed -
G 24” Conc. Pipe Existing SD System 0.26% 1093’-1112’ None Observed None Observed -
H 24” Conc. Pipe Existing SD System 0.79% 1112’-1324’ None Observed None Observed -
I 20” Conc. Pipe Existing SD System 0.71% 1324’-1440’ None Observed None Observed -
J 20” Conc. Pipe Existing SD System 1.41% 1440’- None Observed None Observed -
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
OFF-SITE ANALYSIS DRAINAGE SYSTEM TABLE
SURFACE WATER DESIGN MANUAL, CORE REQUIREMENT #2
Basin: East Lake Washington - Renton Subbasin Name: North Renton Basin Subbasin Number:
Symbol Drainage
Component Type,
Name, and Size
Drainage
Component
Description
Slope Distance
from site
discharge
Existing
Problems
Potential
Problems
Observations of field
inspector, resource
reviewer, or resident
see map Type: sheet flow, swale,
stream, channel, pipe,
pond; Size: diameter,
surface area
drainage basin, vegetation,
cover, depth, type of sensitive
area, volume
% ¼ ml = 1,320 ft. constrictions, under capacity, ponding,
overtopping, flooding, habitat or organism
destruction, scouring, bank sloughing,
sedimentation, incision, other erosion
tributary area, likelihood of problem,
overflow pathways, potential impacts
L 12” Pipe Existing SD System 3.97% 0’-92’ None Observed None Observed -
M 12” Pipe Existing SD System 1.53% 92’-210’ None Observed None Observed -
N 12” Pipe Existing SD System 2.59% 210’-341’ None Observed None Observed -
O 12” Pipe Existing SD System 2.29% 341’-455’ None Observed None Observed -
P 12” PE Pipe Existing SD System 0.59% 455’-470’ None Observed None Observed -
Q 12” Conc. Pipe Existing SD System 2.56% 470’-580’ None Observed None Observed -
R 12” Conc. Pipe Existing SD System 11.44% 580’-677’ None Observed None Observed -
S 12” Conc. Pipe Existing SD System 11.84% 677’-741’ None Observed None Observed -
T 12” Conc. Pipe Existing SD System 9.55% 741’-954’ None Observed None Observed -
U 15” Conc. Pipe Existing SD System 0.92% 954’-1124’ None Observed None Observed -
V 18” Conc. Pipe Existing SD System 1.07% 1124’-1257’ None Observed None Observed -
W 20” Conc. Pipe Existing SD System 5.53% 1257’-1550’ None Observed None Observed -
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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PHOTO #1: LOOKING NORTHEAST FROM HARRINGTON AVE NE WHERE THE SITE CONVEYANCE SYSTEM CONNECTS TO
THE EXISTING PUBLIC STORM DRAINAGE SYSTEM.
PHOTO #2: LOOKING SOUTH WHERE THE UNDERGROUND STORM MAIN RUNS ALONG THE EAST SIDE OF HARRINGTON
AVE NE.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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PHOTO #3: LOOKING EAST DOWN NE 9TH ST WHERE IT INTERSECTS HARRINGTON AVE NE. THE STORM MAIN
REDIRECTS TOWARDS THE WEST AT THIS INTERSECTION.
PHOTO #4 & 5: LOOKING WEST WHERE THE STORM MAIN FROM FERNDALE CIRCLE NE CROSSES UNDER TWO
PROPERTIES TO EDMONDS AVE NE. AT THIS CATCH BASIN, THE DISCHARGE FROM THE NORTH PORTION OF THE SITE
UNITE WITH THE DISCHARGE OF THE SOUTH PORTION OF THE SITE.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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PHOTO #6 & 7: THE STORM MAIN COMING FROM FERNDALE CIR NE ENDS AT THE CATCH BASIN IN PHOTO #6. IT
CONNECTS TO THE CATCH BASIN IN PHOTO # 5. FROM HERE IT RUNS UNDER TWO PROPERTIES TO DAYTON AVE NE
AND CONTINUES GENERALLY TOWARDS THE WEST.
PHOTO #8 & 9: LOOKING EAST DOWN NE SUNSET BLVD WHERE THE STORM MAIN RUNS UNTIL IT REDIRECTS SOUTH
THROUGH THE PROPERTY SHOWN IN PHOTO #9 AND ENDS IN THE CATCH BASIN SHOWN IN PHOTO #4.
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
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APPENDIX E
PRELIMINARY WATER QUALITY DATA
WATER QUALITY FLOWS:
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
ISOMETRIC VIEW
BPU-IB C
US Patents Pending
THIS DOCUMENT IS THE PROPERTY OF OLDCASTLE INFRASTRUCTURE, INC. IT IS SUBMITTED FOR REFERENCE PURPOSES ONLY AND SHALL NOT BE
USED IN ANY WAY INJURIOUS TO THE INTERESTS OF SAID COMPANY. COPYRIGHT © 2020 OLDCASTLE INFRASTRUCTURE, INC. ALL RIGHTS RESERVED.
BioPod f Biofilter
Underground
Vault with Internal Bypass dOldcastle
dOldcastle
dOldcastle
Bioretention/
Biofiltration
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB
A
PLAN VIEW
A
SECTION A-A
BPU-IB C
US Patents PendingSAUDFI1325-0510USAXXXXTHIS DOCUMENT IS THE PROPERTY OF OLDCASTLE INFRASTRUCTURE, INC. IT IS SUBMITTED FOR REFERENCE PURPOSES ONLY AND SHALL NOT BE
USED IN ANY WAY INJURIOUS TO THE INTERESTS OF SAID COMPANY. COPYRIGHT © 2020 OLDCASTLE INFRASTRUCTURE, INC. ALL RIGHTS RESERVED.
MODEL
VAULT SIZE 1
(ID)
VAULT
FOOTPRINT 1
(OD)
TREATMENT FLOW
CAPACITY (GPM/CFS)
A DIM B DIM C DIM A1 DIM B1 DIM 1.6 GPM/SF
(WA GULD2)
1.8 GPM/SF
(NJCAT3)
BPU-46IB 4'6'1.5'5'7'25.6 / 0.057 28.8 / 0.064
BPU-48IB 4'8'1.5'5'9'38.4 / 0.086 43.2 / 0.096
BPU-412IB 4'12'1.5'5'13'64.0 / 0.143 72.0 / 0.160
BPU-66IB 6'6'1.5'7'7'38.4 / 0.086 43.2 / 0.096
BPU-68IB 6'8'1.5'7'9'57.6 / 0.128 64.8 / 0.144
BPU-612IB 6'12'2'7'13'91.2 / 0.203 102.6 / 0.229
BPU-812IB 8'12'2'9'13'121.6 / 0.271 136.9 / 0.305
BPU-816IB 8'16'2'9'17'172.8 / 0.385 194.4 / 0.433
BioPod f Biofilter
Underground
Vault with Internal Bypass
fFIDSAUXXXXUSADFI11540010FIDSAUXXXXUSADFI11540010
SITE SPECIFIC DATA
Structure ID
Model Size
Orientation (Left or Right)
Treatment Flow Rate (cfs)
Peak Flow Rate (cfs)
Rim Elevation
Pipe Data Pipe Location
(Front or Side)Pipe Size Pipe Type Invert
Elevation
Inlet
Outlet
Notes:
1 All Dimensions are nominal, ID=Inside Dimension, OD=Outside Dimension.
2 Treartment flow capacity at 1.6 gpm/sf media surface area based on an WA Ecology GULD
Approval for Basic, Enhanced & Phosphorus.
3 Treatment flow capacity at 1.8 gpm/sf media surface area based on an NJCAT Verification &
NJ DEP Certification.
Bioretention/
Biofiltration
DocuSign Envelope ID: 9A2B0C09-72D8-490B-A60E-EAD24B2FAACB