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HomeMy WebLinkAboutW3310951 (FULL DRAINAGEREVIEW)
PARCEL #: 0723059001
DD. 73 7 L OGA N A vE N, RENToN, WA 9i /
PROJECT# W3310951
February 29, 2016
Owner:
The Boeing Company
Attn: Sergio Echerivel
737 Logan Ave N
Renton, WA 98057
Phone: (480) 993-7784
DC ' G
For Submittal to DAVIDO CONSULTING GROUP, INC .
City of Renton
15029 Bothell Way NE, Ste 600
Lake Forest Park, WA 98155
Phone: 206.523.0024
Fax: 206.523.1012 CITY OF RENTON
RECEI\/FD
MAR 2 2016
DEVELOPMENT
SERVICE,5
Technical Information Report—Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
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Technical Information Report— Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29,2016
CERTIFICATE OF ENGINEER
The technical material and data contained within this report has been prepared by or under the
direction of the following registered professional engineer(s), licensed in accordance with the
laws of the State of Washington to practice in the State of Washington.
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TIR_Boeing Renton Site Logistics Project_04-086 Steam Utilidor_Final_Revision I
Technical Information Report—Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
QUICK REFERENCE PROJECT INFORMATION
General Project Information
Project Description Construction of an at-grade concrete utilidor spanning between
the 04-089 Building and 04-086 Building, as well as a spur to
the 04-017 Building, which will house a new steam line and two
condensate lines to supplement the existing steam line when the
new paint booths within Building 04-086 become operational.
Parcel# 0723059001
Site Address 737 Logan Ave N, Renton, WA iL
Parcel Size 6,680,504 SF 153.36 Acres
Project Size 84,347 SF (1.94 Acres
Owner/Developer The Boeing Company
Attn: Sergio Echerivel
737 Logan Ave N
Renton, WA 98057
Phone: 480 993-7784
Consulting Engineer Tim Gabelein, P.E.—Davido Consulting Group, Inc.
15029 Bothell Way NE, Suite 600
Lake Forest Park, WA 98155
Phone: 206 523-0024
Drainage
Study Area The study area is the project site itself including the larger
drainage basins that the project site lies within and the
downstream drainage system to its discharge location to Lake
Washington (within t/4 of a mile downstream).
Drainage Full Drainage Review Requirements per the 2009 King County
Requirements Surface Water Design Manual(KCSWDM) and City of Renton
Amendments to the KCSWDM (combination of which is
hereafter referred to as The Manual).
Tributary Drainage Predeveloped Conditions: Redeveloped Conditions:
Area & Land Cover Impervious= 13,408 SF Impervious=28,244 SF
Summary PGIS = 13,408 SF PGIS = 13,940 SF
Pervious Surface =70,939 SF Pervious Surface=56,103 SF
Total=84,347 SF Total=84,347 SF
Soils Geotechnical analysis and report completed by Soil &
Environmental Engineers, Inc. S&EE attached herein
Drainage Flow Control Best Management Practices(FCBMPs)are
Improvements proposed including basic dispersion via sheet flow. -
ESC Measures ESC measures per Full Drainage Requirements
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Technical Information Report-Revision 1
Boeing Renton Site Logistics Project-04-086 Steam Utilidor February 29, 2016
TABLE OF CONTENTS
1. Project Overview..........................................................................................................5
1.1 General Description of Proposal ...................................................................................8
1.2 Existing Site Conditions ...............................................................................................8
1.3 Developed Site Conditions............................................................................................8
1.4 Site Area and Size of Improvements.............................................................................9
1.5 Disposition of Stormwater before Project......................................................................9
1.6 Disposition of Stormwater after Project......................................................................10
1.7 Soils ...........................................................................................................................10
2. Conditions and Requirements Summary .....................................................................16
2.1 Core Requirement#1: Discharge at Natural Location .................................................16
2.2 Core Requirement#2: Offsite Analysis.......................................................................16
2.3 Core Requirement#3: Flow Control...........................................................................16
2.4 Core Requirement#4: Conveyance System.................................................................16
2.5 Core Requirement#5: Erosion and Sediment Control.................................................17
2.6 Core Requirement #6: Maintenance and Operations....................................................17
2.7 Core Requirement#7: Financial Guarantees and Liability...........................................17
2.8 Core Requirement#8: Water Quality..........................................................................17
2.9 Special Requirement#1: Other Adopted Area-Specific Requirements ........................17
2.10 Special Requirement #2: Flood Hazard Area Delineation............................................17
2.11 Special Requirement #3: Flood Protection Facilities...................................................17
2.12 Special Requirement #4: Source Control.....................................................................17
2.13 Special Requirement #5: Oil Control ..........................................................................18
2.14 Special Requirement 96: Aquifer Protection Area.......................................................18
3. Offsite Analysis..........................................................................................................18
4. Flow Control and Water Quality Facility Analysis and Design....................................18
4.1 Existing Site Hydrology..............................................................................................18
4.2 Developed Site Hydrology..........................................................................................18
4.3 Performance Standards...............................................................................................19
4.4 Flow Control ..............................................................................................................19
4.5 Water Quality.............................................................................................................21
5. Conveyance System Analysis and Design...................................................................21
5.1 Existing Conveyance..................................................................................................21
5.2 Proposed Conveyance.................................................................................................21
6. Special Reports and Studies........................................................................................22
7. Other Permits..............................................................................................................22
8. Construction SWPPP Analysis and Design .................................................................22
8.1 ESC Plan Analysis and Design ...................................................................................22
8.2 Stormwater Pollution Prevention and Spill Plan Design..............................................23
9. Bond Quantities, Facility Summaries, and Declaration of Covenants..........................24
10. Operations and Maintenance Manual..........................................................................24
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Technical Information Report—Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
APPENDICES
APPENDIX A Figure 1 - Technical Information Report (TIR) Worksheet
APPENDIX B Geotechnical Report
APPENDIX C Drainage Plans
APPENDIX D Temporary Erosion and Sediment Control Plan
APPENDIX E Bond Quantity Worksheet
APPENDIX F Stormwater Facility Summary Sheet
APPENDIX G KCRTS Modeling Results
APPENDIX H Site Logistics TIR
LIST OF TABLES
TABLE 1 Site Area and Size of Improvements.....................................................................9
TABLE 2 Proposed ESC Measures and Construction Sequencing.......................................23
LIST OF FIGURES
FIGURE 1 TIR Worksheet................................................................APPENDIX A
FIGURE2 Vicinity Map ........................................................................................................5
FIGURE3 Project Limits.......................................................................................................7
FIGURE 4 Drainage Basins, Subbasins, and Site Characteristics..........................................I I
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Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
1. PROJECT OVERVIEW
The project is located at The Boeing Commercial Airplane 737 Airplane Production Plant which
is located at 737 Logan Ave N (the "Site") in Renton, WA (the"City"). A vicinity map is
provided below in FIGURE 2. The Site is bounded to the north by Lake Washington, to the west
by the Cedar River, to the east by Logan Ave N, and to the south by the City of Renton Stadium.
This project is part of the Boeing Renton Site Logistics Project, which is a large project that
encompasses multiple smaller projects aimed to modify the site layout, materials movement, and
infrastructure improvements for increased production rates of the 737 aircraft at the Boeing
Renton Site. A Technical Information Report dated March, 2014 was created by BergerABAM
for tasks 1 through 7 of the Boeing Renton Site Logistics Project (hereafter referred to as the
"Site Logistics TIR") and a copy of the Site Logistics TIR is included as APPENDIX H of this
report. This Technical Information Report will serve as a stand-alone document for the purpose
of the 04-086 Building Steam Utilidor Improvements.
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Technical Information Report—Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
The project involves the construction of a new steam line and two new condensate lines spanning
from the 04-089 Building (steam plant)to the 04-086 Building(paint hanger building)to
supplement and add redundancy to the existing steam line currently serving the 04-086 Building.
The additional steam and condensate lines are being constructed in anticipation of additional
paint operations within the 04-086 Building becoming operational in 2017. The new steam and
condensate lines will be housed in an at-grade precast and cast-in-place concrete utilidor which
varies in size throughout the alignment. In addition, a spur utilidor(hereafter referred to as the
"04-017 Spur")to connect the new steam and condensate lines to existing steam and condensate
lines near the 04-017 Building is included in this project. The total length of utilidor is
approximately 1,880 LF with the lid width varying between 64 inches and 79 inches (exterior
dimensions). Throughout this report,the project area will be referred to in three sections: Linear
Park, 04-017 Spur, and North Span. The Linear Park represents the project area between the 04-
089 Building and the main line BNSF railroad crossing and the majority of the area is
landscaping and grass. The 04-017 Spur represents the project area from the main line BNSF
crossing to the steam connection just east of the 04-017 Building, which lies entirely within
existing pavement. The North Span represents the project area from the main line BNSF railroad
crossing to the steam connection just west of the 04-086 Building and is comprised of a
combination of pavement and landscaping. FIGURE 3 shows the anticipated project limits as
well as the sections of the proposed utilidor mentioned above.
The project will adhere to the 2009 King County Surface Water Design Manual(KCSWDM) as
well as the 2010 City of Renton Amendments to the KCSWDM, the combination of which is
hereafter known as "The Manual". This report follows the Technical Information Report(TIR)
requirements for Full Drainage Review per Section 1.1 of The Manual. The TIR worksheet is
attached as FIGURE 1 in APPENDIX A.
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i
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Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
1.1 General Description of Proposal
The project involves the construction of an at-grade concrete utilidor spanning between the 04-
089 Building and 04-086 Building, as well as a spur to the 04-017 Building, which will house a
new steam line and two condensate lines to supplement and add redundancy to the existing steam
line when the new paint booths within the 04-086 Building become operational in 2017.No
changes to vehicular or pedestrian access to the site will occur during this project. However,the
project does include the realignment of approximately 5,893 SF of asphalt walkway for
pedestrian circulation within the Linear Park.
1.2 Existing Site Conditions
The overall Boeing Renton Production Plant is comprised mainly of production facilities,
roadways, parking area, and walkways. Over 99%of the site is covered in impervious surfaces.
The storm drainage systems at the Boeing Renton Production Plant are distributed into more than
25 basins with 21 separate closed conveyance outfalls to Lake Washington. Additional
information on the existing site conditions of the overall Boeing Renton Production Plant can be
found in the Site Logistics TIR in APPENDIX H (prepared by others).
The project site, for use in this report, is defined as the area of anticipated disturbance associated
with 04-086 steam improvements, and is shown in FIGURE 3. The Linear Park is mostly
landscaping and grass but also includes two Boeing-owned railroad spurs as well as an asphalt
pedestrian walkway. Originally, the Linear Park was scheduled to be landscaped as part of the
Duct Bank Project (Task 6 of the Renton Site Logistics Project) which was completed in 2015.
However, the Linear Park landscaping was postponed due to this project utilizing the same area
in an effort to not landscape the same park twice within a year. Therefore, portions of the Linear
Park are currently exposed dirt. The topography of the Linear Park differs throughout as it
includes landscape berms and railroad tracks which are elevated above surrounding areas. In
general, the Linear Park moderately slopes westerly towards the interior of the site. The Linear
Park lies within Drainage Basin 27 which discharges to Lake Washington via Outfall 004 as
shown in Appendix B of the Site Logistics TIR. However, it is unlikely any stormwater
generated within the Linear Park will contribute to the piped storm systems in Drainage Basin 27
as stormwater will either disperse via sheet flow or infiltrate within the landscaped areas.
The 04-017 Spur and North Span areas are almost entirely covered in paved surfaces comprised
of interior roadways, parking areas, and pedestrian walkways. Both areas lie within Drainage
Basin 25C and discharge stormwater to Lake Washington via Outfall 002 as shown in Appendix
B of the Site Logistics TIR. TABLE 1 summarizes the existing land cover of the project site.
1.3 Developed Site Conditions
The developed site conditions, shown in the project plans submitted under separate cover, will
include approximately 8,411 SF of concrete surface utilidor lid within existing pervious areas as
well as approximately 5,893 SF of new and replaced asphalt walkway within the Linear Park. In
addition, a concrete interior roadway just south of the 04-086 Building will be expanded by
approximately 532 SF. The remainder of utilidor improvements will result in the replacement of
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Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
existing paved surfaces and will not change the runoff characteristics of the existing pavement
surfaces being replaced. The existing sheet flow paths and grades will not be altered.
Approximately 52,300 SF of the Linear Park and an additional 3,800 SF of pervious area in the
North Span will be improved with new landscaping and is shown on the Landscape Plans
submitted under separate cover. Runoff from the new utilidor and new walkway areas within the
Linear Park will either disperse via sheet flow or infiltrate within the top 7 feet of fill soils
present in that area(see Section 1.7 for information on the existing site soils). It is not anticipated
that any stormwater runoff generated from the Linear Park improvements will enter the existing
drainage system within Drainage Basin 27. TABLE 1 summarizes the developed site conditions
and land cover. FIGURE 4 shows the developed project site drainage basin maps.
1.4 Site Area and Size of Improvements
The pre-developed and developed site areas and size of improvements are shown in FIGURE 4
and summarized in TABLE 1.
TABLE 1 Site Area and Size of Improvements
Project Site Areas
Existing Developed
SF Acres SF Acres
Impervious Areas:
Parking, Interior Roads, 13,408 0.31 13,940 0.32
Walkways
New Concrete Surface Utilidor 8,411 0.19
New/Replaced Asphalt Walkway 5,893 0.14
Total Impervious Surface 13,408 0.31 28,244 0.65
Total New/Replaced 14,836 0.34
Impervious Surface:
Total Pollution Generating 13,408 0.31 13,940 0.32
Impervious Surface:
Total New/Replaced Pollution
Generating Impervious 771 0.02
Surface:
Pervious Areas:
Landscaping/Grass 70,939 1.63 56,103 1.29
Total Pervious Surface 70,939 1.63 56,103 1.29
Total Project Site Area 84,347 1.94 84,347 1.94
The land cover areas in TABLE 1 were determined by area measurements in AutoCAD from a
topographic survey completed in September, 2015 by DHA. As shown by TABLE 1, the project
is adding 14,836 SF of new impervious surface comprised mainly of the new concrete surface
utilidor and asphalt walkways and very minimal new pollution generating impervious surface
(771 SF).
1.5 Disposition of Stormwater before Project
Existing drainage basins and outfalls located within the overall Boeing Renton Production Plant
are shown and described in detail in the Site Logistics TIR attached as APPENDIX H of this
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Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
report. Stormwater runoff from the Linear Park currently disperses via sheet flow or infiltrates
into the ground. Runoff generated in the 04-017 Spur and North Span areas are captured in a
series of inlets and trench drains located within the paved surfaces of Drainage Basin 25C before
discharging to Lake Washington.
1.6 Disposition of Stormwater after Project
Runoff from the developed site will mimic the runoff from the predeveloped site. In the Linear
Park, new impervious surfaces will disperse via sheet flow into the new landscaped areas or
infiltrate into the top 7 feet of fill soils present in that area. Runoff from the 04-017 Spur and
North Span areas will be captured in a series of inlets and trench drains located within the paved
surfaces of Drainage Basin 25C before discharging to Lake Washington. Refer to the project
plans and Section 4 of this report for more details about the proposed stormwater mitigation
methods. See FIGURE 4 for drainage basin maps of the developed project site.
1.7 Soils
A geotechnical investigation was completed by Soils and Environmental Engineers, Inc. (S&EE)
and the results of this investigation are summarized in a report dated December 17, 2015. The
S&EE report summarizes the site history& geology, surface and subsurface conditions,
groundwater conditions, and anticipated design and construction considerations. S&EE explains
in their report that the subsurface soils at the site include fill over native soils. The fill in the
Linear Park includes 1 to 3 feet thick topsoil over 3 to 7 feet thick sand and silty sand. In the
pavement areas, the fill includes between 3.5 to 6 feet thick of medium dense to dense sand and
medium stiff to soft silt. Through the Linear Park, the groundwater is approximated 7 to 10 feet
in depth, while the groundwater within the 04-017 Spur and North Span are shallowed and vary
between 3 to 6 feet in depth. A copy of the final S&EE report is attached in APPENDIX B.
; I
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2. CONDITIONS AND REQUIREMENTS SUMMARY
The project conditions and requirements were stipulated in the KCSWDM and by the City of
Renton Amendments to the KCSWDM. The project is subject to Full Drainage Review
requirements specified in Section 1.1.2 of The Manual and thus must comply with Core
Requirements 1-8 and Special Requirements 1-6.
The following sections address The Manual's core and special requirements.
2.1 Core Requirement#1: Discharge at Natural Location
Runoff from the proposed improvements will emulate the natural pre-developed conditions of
the site as much as possible as all runoff will either disperse via sheet flow, infiltrate in the
vegetated areas, or discharge to Lake Washington.No storm conveyance systems will be altered
or constructed as a part of this project,thus keeping intact the natural drainage course from the
site and satisfying Core Requirement#1 of The Manual (see Sections 1.5 and 1.6).
2.2 Core Requirement#2: Offsite Analysis
A detailed qualitative offsite analysis for Drainage Basin 25 beginning from the southwestern
extents of the basin and ending at the outfall to Lake Washington (Outfall 002) was completed as
a part of the Site Logistics TIR. Likewise, a qualitative offsite analysis for the entire existing
storm system within Drainage Basin 27 was completed as a part of the Site Logistics TIR, which
is included as APPENDIX H. See Section 3 for additional information on the offsite analysis.
2.3 Core Requirement#3: Flow Control
Although the project is adding more than 2,000 SF of new plus replaced impervious surface, the
project is not subject to the flow control facility requirement since the project meets the
requirements of the Direct Discharge exemption per Section 1.2.3 of the City of Renton
Amendments to the KCSWDM. However, the project is subject to the Large Lot High
Impervious BMP Requirement stipulated in Section 5.2.1.3 of the KCSWDM. The project will
satisfy the Large Lot High Impervious BMP Requirement through the use of basic dispersion via
sheet flow in accordance with Appendix C, Section C.2.4 of the KCSWDM. See Section 4.4 for
additional information on the proposed flow control BMP.
2.4 Core Requirement#4: Conveyance System
The project does not propose to construct any new conveyance systems or modify any existing
conveyance systems other than a reroute of one existing storm drain in the Linear Park to avoid
conflict with the utilidor alignment. The rerouted storm drain will connect to the same location it
is currently connected to thus not changing any flow patterns. Instead, the project will be
utilizing the existing conveyance systems within Drainage Basin 25 for a very minimal amount
of additional flow. The existing conveyance systems are required to have sufficient capacity to
convey and contain the 25-year peak flow for the entire contributing drainage area, assuming
build-out conditions. See Section 5 for additional information on the existing conveyance
systems.
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2.5 Core Requirement#5: Erosion and Sediment Control
Erosion and sediment control(ESC) measures have been designed for the project in accordance
with Section 1.2.5 of The Manual to prevent the transport of sediment from the site to adjacent
properties and downstream drainage facilities during construction. Temporary measures include
a stabilized construction entrance, perimeter protection(e.g. sift fencing, straw wattles, or
compost socks), chain link fencing, and inlet protection at impacted catch basins. A Temporary
Erosion and Sediment Control Plan has been prepared for construction of this project and is
included in APPENDIX D. See Section 8.1 for additional information on the proposed erosion
and sediment control measures.
2.6 Core Requirement#6: Maintenance and Operations
Maintenance and operation for stormwater facilities for The Boeing Company Renton Plant are
conducted in accordance with the plant's Industrial Stormwater Permit, WAR-000232. No.
stormwater facilities are proposed as a part of this project.
2.7 Core Requirement#7: Financial Guarantees and Liability
A bond quantities worksheet has been completed and attached as APPENDIX E (see Section 9).
The Boeing Company will be responsible for all stormwater drainage guarantees and liabilities
for this project.
2.8 Core Requirement#8: Water Quality
The project is exempt from water quality requirements since it is adding less than 5,000 SF of
new plus replaced pollution generating impervious surface as stated in Section 1.2.8 of the City
of Renton Amendments to the KCS WDM.
2.9 Special Requirement#1: Other Adopted Area-Specific Requirements
The project is located within the Cedar River Basin and there are no special drainage
requirements that apply to this project.
2.10 Special Requirement#2: Flood Hazard Area Delineation
The project is exempt from Special Requirement#2 because it does not contain and is not
adjacent to a flood zone as designated by FEMA panel, which is provided in Appendix D of the
Site Logistics TIR(attached as APPENDIX H of this report).
2.11 Special Requirement#3: Flood Protection Facilities
The project is exempt from Special Requirement#3 because it will not rely on an existing flood
protection facility(such as a levee or revetment) for protection against hazards posed by erosion
or inundation and will not modify or construct a new flood protection facility.
2.12 Special Requirement#4: Source Control
The project will comply with the source control requirements stipulated in Section 1.3.4 of the
City of Renton Amendments to the KCSWDM. See the SWPPP for this project, submitted under
separate cover, as well as Section 8.2 of this report for details on proposed source control
measures.
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2.13 Special Requirement#5: Oil Control
The project site is exempt from Special Requirement#5 because it does not trigger oil control
requirements since the project site is under the high-use site thresholds.
2.14 Special Requirement#6: Aquifer Protection Area
The project is exempt from Special Requirement#6 because it is not located in Zone 1 or Zone 2
of the Aquifer Protection Areas identified in Reference 1 I-B of the City of Renton Amendments
to the KCSWDM.
3. OFFSITE ANALYSIS
A detailed qualitative offsite analysis for Drainage Basin 25 beginning from the southwestern
extents of the basin and ending at the outfall to Lake Washington (Outfall 002) was completed as
a part of the Site Logistics TIR. Likewise, a qualitative offsite analysis for the entire existing
storm system within Drainage Basin 27 was completed as a part of the Site Logistics TIR, which
is included as APPENDIX H. Both of these qualitative analysis were reviewed by DCG to assess
the condition of the downstream system. There were no apparent problems noted within the
analysis and nothing that would prohibit its continued use by the proposed project. As with any
conveyance system, routine maintenance is recommended.
4. FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND DESIGN
The following sections summarize the stormwater flow control and water quality facility analysis
and design.
4.1 Existing Site Hydrology
The existing Linear Park consists mainly of landscaping but also includes railroad tracks, a
pedestrian walkway, benches, lighting, and numerous access lids for existing utilities. In general,
the Linear Park moderately slopes westerly towards the interior of the site. Stormwater runoff
generated in the Linear Park either disperses via sheet flow in the existing landscaping or
infiltrates into the 7 feet of fill soils present in the park area. See section 1.7 and APPENDIX B
for more information on the site soils. The 04-017 Spur and North Span areas consist mainly of
impervious surfaces. Both areas lie within Drainage Basin 25C and runoff is captured by
numerous existing inlets within the drainage basin and is piped to Outfall 002 where the basin
discharges to Lake Washington.
4.2 Developed Site Hydrology
The developed project site hydrology will mimic the existing project site hydrology as
stormwater generated in the Linear Park will disperse via sheet flow in the newly configured
landscaping or infiltrate into the 7 feet of fill soils present in the park area. Stormwater generated
in the 04-017 Spur and North Span areas will mimic the existing conditions as runoff will get
collected by existing inlets within the Drainage Basin 25C and piped to Outfall 002 where the
basin discharges to Lake Washington. See FIGURE 4 for the developed site drainage basin
maps and APPENDIX B for offite soils information.
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4.3 Performance Standards
• The project is exempt from flow control requirements per the Direct Discharge
Exemption.
• The project is subject to Large Lot High Impervious BMP Requirements since the project
lies within a lot that is greater than 22,000 SF and will result in an impervious surface
coverage of more than 45% (current impervious surface coverage on the site is greater
than 99%). Basic dispersion will be used to satisfy this requirement.
• The project is exempt from water quality requirements since it will be creating less than
5,000 SF of new plus replaced pollution generating impervious surface.
4.4 Flow Control
As discussed in Section 2.3 and 4.3,the project is exempt from flow control requirements since
the project qualifies for the Direct Discharge Exemption as the site discharges directly to lake
Washington.
The Large Lot High Impervious BMP Requirement will be satisfied through the use of basic
dispersion via sheet flow. As stated in Section 5.2.1.3 of the KCSWDM, the feasibility of full
dispersion must be evaluated for all target impervious surface prior to evaluating other flow
control BMPs. However, full dispersion is not feasible as the required native vegetated flowpath
is not obtainable onsite. Since full dispersion is not feasible and the project will result in an
impervious surface coverage of more than 65%, flow control BMPs must be applied to an
impervious area equal to at least 10%of the site/lot or 20% of the target impervious surface,
whichever is less.
For this project, a majority of the improvements will replace existing impervious surfaces for the
sole purpose of installing utilities(steam and condensate lines). Per the definition of"replaced
impervious surface"on Page 1-4 of the City of Renton Amendments to the KCSWDM,
"replaced impervious surface means any existing impervious surface on the project site
that is proposed to be removed and re-established as impervious surface, excluding
impervious surface removed for the sole purpose of installing utilities. "
Therefore,the target impervious surface total for the project is 14,836 SF, as shown in TABLE
1, and does not include impervious surfaces replacing existing impervious surfaces. Since 20%
of the target impervious surface is less than 10%of the entire site/lot,the project must apply a
flow control BMP to 2,968 SF of target impervious surface area. The project will satisfy this
requirement through the use of basic dispersion via sheet flow which will be applied to slightly
over 3,000 SF of target impervious surface area comprised of portions of the new utilidor and
walkway areas in the Linear Park. The dispersion and flowpath areas (10' minimum flowpath)
are shown on the Drainage Plan included as APPENDIX C. The proposed dispersion area and
flowpaths meet the following requirements stipulated in Section C.2.4.5 of the KCSWDM,
Design Specifications for Impervious Surface Sheet Flow (Basic Dispersion)
1. The strip of impervious surface maybe either roof(with no gutter) or pavement. The edge
of the target impervious strip and the ground adjacent to or immediately below the edge
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must be either level or sloped such that the direction of sheet flow is perpendicular to the
edge or no more than 45 degrees from perpendicular.
The strip of impervious surface being dispersed will be either concrete (utilidor lid) or
asphalt (new walkway). The edge of the impervious surface being dispersed will be level in
the case of the utilidor lid and sloped no more than 2%for the asphalt walkway. The
impervious strip being dispersed will allow for the direction of sheet flow to be
perpendicular, or very close to perpendicular, to the edge of the impervious surface strip. See
the proposed dispersion and flowpath areas on the Drainage Plan included as APPENDIX C.
2. A 2-foot-wide, 4-to-6 inch-deep, strip of crushed rock or the extended base course of a
road or driveway must be provided at or below the edge of the impervious strip to
facilitate dispersal of runoff. This requirement may be waived for use of reverse slope
sidewalks and other impervious strips that are 10 feet wide or less.
Since the proposed impervious areas being dispersed are less than 10-feet wide, the project is
eligible for exemption from Design Specification#2. Nevertheless, adding a strip of crushed
rock along the utilidor was evaluated, but since the utilidor lids are removable (for
maintenance purposes)there is a big concern of the crushed rock falling into the utilidor each
time a lid is removed, thus causing a significant void area that will prevent proper dispersion
once lids are replaced. Crushed rock falling into the utilidor has potential to become a
significant maintenance problem for Boeing if the maintenance crew consistently has to
replace rock falling into the utilidor each time it is opened and remove the rock from the
utilidor to prevent the potential for clogging in the drain/pump system. Sheet flow will be
adequately dispersed through the vegetation based on the design grading and an even
dispersion from the lid (i.e. no concentration of stormwater). Because of these reasons, it is
our recommendation that this project is granted an exemption from Design Specification #2.
3. A "vegetated flowpath segment"of at least 10 feet in length must be available along the
flowpath that runoff would follow upon discharge from the strip of crushed rock.
A vegetated flowpath of at least 10 feet in length is available along the flowpath that runoff
will follow upon discharge from the concrete and asphalt strips. In most proposed sheet flow
dispersion areas, greater than 10 feet of vegetated flowpath is available. The vegetated
flowpaths are shown on the Drainage Plans included as APPENDIX C.
4. No more than a 20 foot-wide strip of impervious surface may be sheet flowed in this
manner unless the length of vegetated flowpath segment is increased 10 feet for each
additional 20 feet of impervious surface width or fraction thereof.
This project does not propose to sheet flow a 20-foot wide or greater strip of impervious
surface. Therefore, 10 feet of vegetated flowpath is sufficient for the impervious surface
areas proposed to be dispersed via basic sheet flow dispersion.
S. For purposes of maintaining adequate separation of flows discharged from adjacent
dispersion devices, the outer edge of the vegetated flowpath segment for the strip of
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impervious surface must not overlap with other flowpath segments, except those
associated with sheet flow from a non-native pervious surface.
The outer edge of the proposed vegetated flowpath segments do not overlap with other
flowpath segments. The proposed flowpath segments can be seen on the Drainage Plans
included as APPENDIX C.
4.5 Water Quality
The project is exempt from water quality requirements since it will be creating less than 5,000
SF of new plus replaced pollution generating impervious surface. Again, impervious surface
replaced as part of a utility installation is exempt.
5. CONVEYANCE SYSTEM ANALYSIS AND DESIGN
The existing and proposed conveyance systems are required to have sufficient capacity to convey
and contain the 25-year peak flow for the entire contributing drainage area, assuming build-out
conditions. The existing and proposed conveyance systems are discussed in the following
sections.
5.1 Existing Conveyance
The project lies within Drainage Basin 25 and 27. The Linear Park lies within Drainage Basin 27
while the remainder of the project (North Span and 04-017 Spur) is within Drainage Basin 25.
All proposed impervious surfaces within the Linear Park will either be dispersed via sheet flow
or will infiltrate within the top 7 feet of fill soils present in that area. Therefore, no additional
runoff from the Linear Park will be contributing to the existing conveyance system within
Drainage Basin 27. In addition, no modifications to the existing drainage system within Drainage
Basin 27 are proposed as a part of this project.
Drainage Basin 25, which is detailed in Section 3.5 of the Site Logistics TIR, is a piped system
which discharges to Lake Washington via outfall 002. This project proposes to add 2,767 SF of
new impervious surface (or 0.058 CFS from a 25-year peak flow),to Drainage Basin 25, which
currently contains 908,174 SF of impervious surface. Therefore,the impervious surface total -�
within Drainage Basin 25 will increase by approximately 0.3%. The additional flow added to
Drainage Basin 25 was modeled in the King County Runoff Time Series(KCRTS) using a 15-
minute time step in accordance with Table 3.2.2.A of the KCSWDM. See APPENDIX G for
more information on the KCRTS model.
5.2 Proposed Conveyance
This project does not propose to add a new conveyance system or modify an existing conveyance
system. Based on the qualitative downstream analysis performed as part of the Site Logistics
Project TIR and reviewed by DCG, the project does not warrant additional conveyance capacity
analysis. The minimal impervious surface added will add only 0.058 CFS to an existing
conveyance system that was constructed to handle the peak runoff from a 900,000+ SF basin.
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6. SPECIAL REPORTS AND STUDIES
Special reports and studies include:
• A geotechnical report completed by Soil & Environmental Engineers, Inc. (S&EE)on
December 17, 2015. See APPENDIX B for the report in its entirety.
• A TIR for the Site Logistics Project completed by BergerABAM on March 3, 2014. See
APPENDIX H for the full TIR.
7. OTHER PERMITS
Other permits required for this project include:
• Building Permit and Special Inspection (through City of Renton).
• National Pollution Discharge Elimination System—Construction Stormwater General
Permit (this permit has been issued by the Department of Ecology for the Site Logistics
project).
8. CONSTRUCTION SWPPP ANALYSIS AND DESIGN
A detailed construction stormwater pollution prevention plan(SWPPP) has been prepared for the
project for Submittal to the Department of Ecology by Boeing and will serve as an Appendix to
the SWPPP prepared for the Site Logistics project. A copy of the SWPPP document shall be
maintained on the site at all times during construction and will be made available to the City of
Renton staff upon request.
This section summarizes the Construction SWPPP analysis and design. The two components of
the SWPPP are the erosion and sediment control(ESC) and the stormwater pollution prevention
and spill (SWPPS) plans. Both the ESC Plan and SWPPS serve as guides as the contractor is
required to design a working SWPPP for the site. The analysis and design of these plans are
discussed in the following sections.
8.1 ESC Plan Analysis and Design
The ESC design follows the guidelines provided in Appendix D of The Manual and is intended
to satisfy Core Requirement #5 Erosion and Sediment Control.
A stabilized construction entrance will be maintained throughout construction of the site
improvements. Silt fencing will be installed downslope of the improvements. Chain link fencing
will be used to protect all trees that are to be preserved onsite and to mark project limits. Street
cleaning on the surrounding interior roads as well as Logan Ave N will occur daily or as needed
to remove any sediment tracked from the site. Site surface drainage will be maintained to prevent
any ponding and inlet protection will be provided at all existing catch basins that may receive
runoff during construction. All disturbed areas that will not be paved will be stabilized by
planting and mulching immediately after construction. The proposed ESC measures are shown
on the Temporary Erosion and Sediment Control Plan in APPENDIX D.
An ESC supervisor will be designated for the project and must be a Certified Professional in
Erosion and Sediment Control or a Certified Erosion and Sediment Control Lead, as recognized
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by King County. The ESC supervisor will be responsible for the'performance, maintenance, and
review of all ESC measures, as well as the compliance with all permit conditions relating to ESC
as described in The Manual.
TABLE 2 Proposed ESC Measures and Construction Sequencing
(ESC Measures Shall Comply with the KCSWDM Appendix D)
ESC Measure Comment
1 Identify Project Limits Mark by fencing or other means to contain the
grubbing and grading activities. This includes
installing temporary chain link fencing around
trees that are to remain.
2 Install temporary silt fence Install fence down-slope of the improvements. l
3 Construct stabilized Use existing gravel driveway for construction --}
construction entrance entrance or construct new temporary entrance if
necessary i.e., sediment tracked onto road).
4 Install inlet protection as Ensure that sediment cannot enter the existing
required, based on drainage system.
construction sequencing
5 Maintain ESC measures Relocate or install new measures if necessary to
meet King County ESC standards(KCSWDM
Appendix D).
6 Street Cleaning Provide for periodic street cleaning to remove
and sediment that may have been tracked out.
Sediment should be removed by shoveling or
sweeping and carefully removed to a suitable
disposal area where it will not be re-eroded.
7 Inspect downstream Verify that all drainage system components free
drainage system, clean if of sediment. If sediment present then repair or
necessary during implement additional ESC measures.
construction.
8 Surfacing and Sod/Seed Construct pavement, sidewalks, etc. as soon as
Exposed Areas possible. Cleared areas will be sod/seeded as
soon as possible after grading completed.
9 Remove ESC measures After hard surfaces are constructed and cleared
after site stabilized and areas are stabilized, remove ESC measures and
cleans stem. clean any sediment/debris in drainage system.
8.2 Stormwater Pollution Prevention and Spill Plan Design
The SWPPS plan is intended to prevent pollutants from coming into contact with stormwater
runoff, surface waters, or groundwater, during construction. Vehicles, construction equipment,
materials, chemical storage, and sediment from clearing and grading all have the potential to
pollute stormwater during construction. The following 13MPs are required during the
construction of this project:
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• Maintain good housekeeping.
• Designate vehicle, equipment, and chemical storage areas.
• Inspect vehicle, equipment, and petroleum product storage and dispensing areas regularly
to detect any leaks or spills.
• Store and contain liquid materials in such a manner that if the tank leaks,the contents
will not discharge into the storm drainage system, surface waters, or groundwater.
• Provide maintenance and cleaning of the storm drainage system regularly by removing
sediment and debris.
• All spills will be cleaned up immediately and disposed of correctly. Do not hose down
spill areas to a storm drainage system.
• All toxic materials will be stored under cover when not in use or during a rain event.
• Use storm drain covers or other similarly effective runoff control measures to prevent
sediment and other pollutants from entering catch basins.
All ESC and SWPPS BMPs will be inspected routinely by the ESC supervisor. All ESC
measures will be removed, the site stabilized, and the drainage system cleaned once construction
is completed.
9. BOND QUANTITIES,FACILITY SUMMARIES,AND DECLARATION OF
COVENANTS
The bond quantities, facility summaries, and declaration of covenants/agreements are addressed
in the following sections.
• Bond Quantities—The bond quantities for the project are calculated in King County's
Bond Quantity Worksheet attached in APPENDIX E.
• Facility Summaries—The stormwater facilities are summarized in the Stormwater
Facility Summary Sheet attached in APPENDIX F.
• Declaration of Covenants/Agreements—A declaration of covenant for the basic
dispersion flow path areas will be provided under separate cover at a later date.
10. OPERATIONS AND MAINTENANCE MANUAL
Although no stormwater facilities are proposed as a part of this project, the landscaped areas and
dispersion flowpaths shall be maintained in accordance with the landscape architects
recommendations, which will be submitted to Boeing under separate cover later.
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APPENDIX A Figure 1 - Technical Information Report (TIR)
Worksheet
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KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Part 1 PROJECT OWNER AND Part 2 PROJECT LOCATION AND
PROJECT ENGINEER DESCRIPTION
Project Owner The Boeing Company Project NameBoeing Renton Site Logistics Project
Phone 480-993-7784 DDES Permit# 04-086 Steam Utilidor
Address 737 Logan Ave N Location Township 23N
Renton,WA 98057 Range 5E
Project Engineer Tim Gabelem, P.E. Section 7
Company Davido Consulting Group,Inc. Site Address 737 Logan Ave N
Phone 206-523-0024 Renton, WA 98057
Part 3 TYPE OF PERMIT APPLICATION Part 4 OTHER REVIEWS AND PERMITS
❑ Landuse Services ❑ DFW HPA ❑ Shoreline
Subdivison / Short Subd. / UPD ❑ COE 404 Management
® Building Services ❑ DOE Dam Safety ® Structural
M/F/Commerical / SFR Rockery/Vault/
❑ Clearing and Grading
El FEMA Floodplain �❑ 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 Review (iD Targeted / Type (circle one): Full Modified /
(circle): Large Site Small Site
Date (include revision January 29, 2016 Date (include revision January 29, 2016
dates): February 29, 2016 dates): February 29, 2016
' i
Date of Final: February 29, 2016 Date of Final: February 29,2016
Part 6 ADJUSTMENT APPROVALS
Type (circle one): Standard / Complex / Preapplication / Experimental/ Blanket
Description: (include conditions in TIR Section 2)
N/A
Date of Approval:
2009 Surface Water Design Manual 1/9/2009
1
KING COUNTY, WASHINGTON, SURFACE, WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Part 7 MONITORING REQUIREMENTS
Describe:
Monitoring Required: Yes No
Start Date:
Completion Date:
I
Part 8 SITE COMMUNITY AND DRAINAGE BASIN
Community Plan :
Special District Overlays:
Drainage Basin: Cedar River Drainage Basin
Stormwater Requirements: Flow Control and Water Quality Exempt
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
See Geotech Report 0-2% Average Low
® High Groundwater Table (within 5 feet) ❑ Sole Source Aquifer
❑ Other ❑ Seeps/Springs
❑ Additional Sheets Attached
2009 Surface Water Design Manual 2 1/9/2009
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Part 11 DRAINAGE DESIGN LIMITATIONS
REFERENCE LIMITATION/SITE CONSTRAINT
❑ Core 2—Offsite Analysis
❑ Sensitive/Critical Areas
❑ SEPA
❑ Other
❑ Additional Sheets Attached
Part 12 TIR SUMMARY SHEET provide one TIR Summary Sheet per Threshold Discharge Area
Threshold Discharge Area:
name or description) Project Site and Drainage Bains 25 and 27
Core Requirements (all 8 apply)
Discharge at Natural Location Number of atural Discharge Locations: 1
Offsite Analysis Level: 1 / 2 / 3 dated:
Flow Control Level: 1 / 2 / 3 or Exemption Number Direct Discharge E emption
incl. facility summary sheet Small Site BMPs
Conveyance System Spill containment located at: NA
Erosion and Sediment Control ESC Site Supervisor: TBD
Contact Phone:
After Hours Phone:
Maintenance and Operation Responsibility: Privat / Public
If Private, Maintenance Log Required: es /No
Financial Guarantees and Provided: Yes No
Liability
Water Quality Type: Basic / Sens. Lake / Enhanced Basicm / Bog
(include facility summary sheet) or Exemption No. 1
Landscape Management Plan: es / 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 Describe: NA
Source Control Describe landuse: Commercial
(comm./industrial landuse) Describe any structural controls: See SWPPP
2009 Surface Water Design Manual 1/9/2009
3
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Oil Control High-use Site: Yes / No
Treatment BMP:
Maintenance Agreement: Yes / No
with whom?
Other Drainage Structures
Describe:
Part 13 EROSION AND SEDIMENT CONTROL REQUIREMENTS
MINIMUM ESC REQUIREMENTS MINIMUM ESC REQUIREMENTS
DURING CONSTRUCTION AFTER CONSTRUCTION
® Clearing Limits 0 Stabilize Exposed Surfaces
0 Cover Measures 0 Remove and Restore Temporary ESC Facilities
X❑ Perimeter Protection 0 Clean and Remove All Silt and Debris, Ensure
X❑ Traffic Area Stabilization Operation of Permanent Facilities
® Sediment Retention 0 Flag Limits of SAO and open space
preservation areas
© Surface Water Collection ❑ Other
® Dewatering Control
0 Dust Control
® Flow Control
Part 14 STORMWATER FACILITY DESCRIPTIONS Note: Include Facility Su mary and Sketch
Flow Control Type/Description Water Quality Type/Description
❑ Detention ❑ Biofiltration
❑ Infiltration ❑ Wetpool
❑ Regional Facility ❑ Media Filtration
❑ Shared Facility ❑ Oil Control
® Flow Control Basic Dispersion ❑ Spill Control
BMPs (sheet flow)
❑ Flow Control BMPs
❑ Other
❑ Other
2009 Surface Water Design Manual 4 l/9/2009
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Part 15 EASEMENTS/TRACTS Part 16 STRUCTURAL ANALYSIS
❑ Drainage Easement ® Cast in Place Vault
© Covenant ® 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. Digitally signed by Tim W
Gabelein
Date:2016.01.28 17:23:40-08'00'
Signed/Date
2009 Surface Water Design Manual 1/9/2009
5
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S&EE
GEOTECHNICAL REPORT
4-86 STEAM UTILIDOR
BOEING RENTON PLANT
S&EE JOB NO. 1512
DECEMBER 17,2015
S
Job No.1512 S&EE
SOIL& ENVIRONMENTAL ENGINEERS,INC.
16625 Redmond Way Suite M 124 Redmond,Washington 98052,w,%,A.SoiI Env ironmencal.com (425)868-5868 '
December 17. 2015
Mr.Sergio Echerivel
The Boeing Company
Project Construction Management
CC: Mr.Tim Gabelein,PE
Geotechnical Report
4-86 Steam Utilidor
Boeing Renton Plant
Dear Sergio:
We are pleased to present here our Geotechnical Report for the referenced project. Our services were
authorized via work order number 2211201#150227, and have been performed in accordance with our '
proposal dated October 2, 2015. We appreciate the opportunity to provide our services. Should you have
any questions regarding the contents of this report or require additional information, please let me know
anytime.
Very truly yours, ,
G SOIL&ENVIRONMENTAL ENGINEERS,INC.
II- C.J. Shin,Ph.D., P.E.
{3NAL President
i
1512rpt see EE
1
' TABLE OF CONTENTS
Section Page
' 1.0 INTRODUCTION.................................................................................................................................................1
2.0 SCOPE OF WORK...............................................................................................................................................1
' 3.0 SITE CONDITIONS.............................................................................................................................................2
3.1 SITE HISTORY&GEOLOGY...........................................................................................................................2
3.2 SURFACE CONDITIONS...................................................................................................................................3
' 3.3 SUBSURFACE CONDITIONS...........................................................................................................................4
3.4 GROUNDWATER CONDITIONS....................................................................................................................4
3.5 PREVIOUS DUCTBANK CONSTRUCTION EXPERIENCE..........................................................................5
' 3.5.1 Excavation and shoring................................................................................................................................5
3.5.2 Subgrade Stabilization.................................................................................................................................6
3.5.3 Backfill.........................................................................................................................................................6
3.5.4 Dewatering....................................................................................................................................................7
' 4.0 ENGINEERING EVALUATIONS AND RECOMMENDATIONS..................................................................8
4.1 GENERAL...........................................................................................................................................................8
4.2 EXCAVATION AND SHORING.......................................................................................................................9
' 4.2.1 Shoring Design In General...........................................................................................................................9
4.2.2 Shoring Design for Excavation near Railroad Tracks...............................................................................10
4.2.3 Open-Cut.....................................................................................................................................................10
' 4.2.4 Subgrade Preparation................................................................................................................................10
4.2.5 Bearing Capacity and Subgrade Modulus..................................................................................................II
4.2.6 Backfill.......................................................................................................................................................11
4.3 LATERAL EARTH PRESSURES ON UNDERGROUND WALLS...............................................................12
' 4.4 BUOYANCY RESISTANCE............................................................................................................................13
4.5 PAVEMENTS............................................................................................................................ ...................14
4.5.1 Pavement Design.......................................................................................................................................14
4.5.2 Subgrade Preparation................................................................................................................................14
4.6 SEISMIC DESIGN PARAMETERS.................................................................................................................15
4.7 ADDITIONAL SERVICES...............................................................................................................................16
5.0 CLOSURE.............................................................................................................................................................16
FIGURE 1: SITE LOCATION MAP
FIGURE 2: SITE AND EXPLORATION PLAN
' FIGURE 3: SITE HISTORY MAP
FIGURE 4: LIQUIFACTION MAP
FIGURE 5: SOIL PROFILE—SECTION A-A
FIGURE 6: SOIL PROFILE—SECTION B-B
' FIGURE 7: SOIL PROFILE—SECTION C-C
FIGURE 8: SURCHARGE LOAD ON SUBSURFACE WALL
APPENDIX A: LOG OF PREVIOUS EXPLORATIONS
' APPENDIX B: LATERAL PRESSURES ON SHORING WALLS NEAR RAILROAD
t
' 1512rpc S&EE
t
REPORT OF GEOTECHNICAL INVESTIGATION
4-86 STEAM UTILIDOR '
For
The Boeing Company
1.0 INTRODUCTION '
The project site is located in the eastern portion of the Boeing Renton Plant. A Site Location Map is shown '
in Figure 1 and a Site and Exploration Plan is shown in Figure 2,both are included at the end this report. '
The project scope includes the construction of an underground steam utilidor from Building 4-89 to
Buildings 4-17 and 4-86. The utilidors will have high pressure steam and condensate lines inside. From
the east side of Building 4-89 the proposed utilidor will run eastward and cross under the railroad tracks. '
The utilidor will then extend for approximately 1000 feet in a northeasterly direction in Boeing's Linear
Park. At the location about 200 feet north of the flagpole,the utilidor will turn west and cross under the ,
railroad. The utilidor will then split with one running westward for about 350 feet and connect to
Building 4-17, and the other running northeast for about 800 feet and connect to Building 4-86. The '
utilidors will be a precast concrete structure about 5 feet in width, and will be installed to depths ranging
from about 4 to 7 feet. Pre-casted underground vaults will also be installed along the utilidor route. The '
plan dimensions of the vaults will range from 8 feet x 23 feet to 15 feet x 16 feet, and the bottom of the
vaults will be about 11 to 16 feet below the ground surface.
2.0 SCOPE OF WORK '
The purpose of our investigation is to provide geotechnical parameters and recommendations for design '
and construction. Specifically,the scope of our services have included the following: '
1. Review of available geotechnical information and provide the followings:
- Site History and Geology '
- Surface Conditions
- Subsurface Soil Conditions
- Groundwater Conditions '
2. Engineering evaluations and recommendation regarding the following:
- Dewatering Recommendations ,
- Shoring Recommendations
- Open-Cut Feasibility '
- Allowable Bearing Pressures and Subgrade Modules Values
- Buoyancy Resistance
Job No. 1512 S&EE '
- Footing Drain Recommendations vs Designing for Hydrostatic Pressure
- Lateral Earth Pressures and Surcharge Forces on Underground Walls
- Lateral Earth Pressures for Shoring(If Different)
- Backfill Recommendations
- Structural Fill
- CDF and Pea Gravel Backfill Feasibility
- Seismic Considerations and Seismic Surcharges
- Subgrade Preparation for Structures
- Utilidor Subgrade Preparation
- Subgrade Preparation for Pavement Replacement
3. Construction Support and Monitoring including:
- Trench and Vault Excavation Inspection
- Dewatering Monitoring
- Shoring Installation Inspection
- Inspection of Structural Fill/Backfill Materials
- Compaction Requirements
- Respond to Contractor RFIs
- Once per Month Construction Meetings
4. Preparation of this geotechnical report.
3.0 SITE CONDITIONS
3.1 SITE HISTORY& GEOLOGY
Boeing Renton Plant is located at the south end of Lake Washington. Figure 3 shows that the northern
portion of the plant was once under the lake. The Black River used to run out of the lake, flowed south
through the site vicinity and then veered west. In 1911, Cedar River flooded Renton. In the following year
the town dug a 2000-foot-long, 80-foot-wide canal to reroute the course of the Cedar to the north so that it
flowed directly into Lake Washington, in the hope of avoiding floods in the future. From July to October
1916, the construction of the Lake Washington Ship Canal lowered Lake Washington 8.8 feet. In the
process,the Black River dried up, and the outfall from Lake Washington became the ship canal (reference:
Suzanne Larson, History of the Lake Washington Ship Canal, King County Arts Commission, 1975,
Introduction, 23.)
During WW II, the Boeing Renton Plant was leveled by 3 to 5 feet thick of fill. The native soils
immediately under the fill include alluvial deposits that are over 100 feet in thickness. These soils are
typically soft and unconsolidated in the upper 50 feet and become compact thereafter. Published geologic
Job No.1512 2 S&EE
information (Geologic Map of The Renton Quadrangle, King County, Washington by D.R. Mullineaux,
1965) indicates that the alluvial soils are underlain by Arkosic sandstone. S&EE performed a few soil test
borings in 2012—2013 at North Bridge site located at the north end of Cedar River(see Figure 3). These
borings found glacially deposited and consolidated soil(hard silt)at depths of about 150 to 170 feet. Boring
data from our previous projects at the south side of Renton Airport show that the hard silt is underlain by
sandstone.
Seismic Hazards The project area is under the threat of two types of earthquakes—crustal and subduction
zone events. The former will result from the movement of the Seattle Fault. This fault is a collective
term for a series of four or more east-west-trending, south-dipping fault strands underlying the Seattle
area. This thrust fault zone is approximately 2 to 4 miles wide(north-south) and extends from the Kitsap
Peninsula near Bremerton on the west to the Sammamish Plateau east of Lake Sammamish on the east.
The four fault strands have been interpolated from over-water geophysical surveys (Johnson, et al., 1999)
and, consequently, the exact locations on land have yet to be determined or verified. Recent geologic
evidence suggests that movement on this fault zone occurred about 1,100 years ago, and the earthquake it
produced was on the order of a magnitude 7.5.
The Cascadia subduction zone(also referred to as the Cascadia fault) is a convergent plate boundary that
stretches from northern Vancouver Island to northern California. It is a very long sloping subduction
zone fault that separates the Juan de Fuca and North America plates. This fault can generate mega
earthquakes having a magnitude of 9 or above. Our previous studies at Boeing Renton Plant have shown
that due to its long period/duration, subduction zone earthquakes would cause more severe liquefaction
hazard than earthquakes generated by the nearby Seattle fault.
A liquefaction map (Figure 4: Preliminary Liquefaction Susceptibility Map of the Renton Quadrangle,
Washington by Stephen Palmer)indicates that the project area has high liquefaction susceptibility.
3.2 SURFACE CONDITIONS
Except at the railroad crossings, most of the southern portion of the proposed utilidor will be installed in
Linear Park whereas most of the northern portion of the utilidor will be installed in the plant. The ground
surface in the park is mainly covered with landscaping materials,whereas the ground surfaces in the plant
include asphalt and concrete pavements. The ground surface in the plant is relatively flat and is about 4
feet lower than that of the park. As shown in Figure 2, the proposed utilidor is relatively close to the
existing electrical ductbank, which was constructed from December 2013 to July 2015. The width of the
Job No.1512 3 S&EE
ductbank is about 5 feet. The depths of excavation for the ductbank ranged from about 7 to 12 feet and
the depths for ductbank vaults ranged from about 12 to 16 feet.
3.3 SUBSURFACE CONDITIONS
A few previous borings were drilled near the proposed steam utilidor. The locations of these borings
are shown on Figures 2 - Site and Boring Location Plan, and the logs of these borings are included in
Appendix A of this report.
The boring data show that the subsoils at the site include fill over native soils. In the park area the
fill includes about 1 to 3 feet thick of topsoil over 3 to 7 feet thick of sand and silty sand. The latter is
loose to medium dense. In the pavement areas, the fill includes about 3.5 to 6 feet thick of medium
dense to very dense sand, and medium stiff to soft silt. These soils appear to be placed with some
compaction effort.
The native soils below the fill include very loose to medium dense sand and very soft to medium stiff
silt. The two deep borings, B-1-2015(4-89) and B-2-2015(4-86) show that these unconsolidated,
younger alluvial deposits extend to a depth of about 100 feet, and they are underlain by compact,
older alluvial deposits. Our previous borings at the North Bridge site show that the older alluvial
soils are in turn underlain by glacial soils.
3.4 GROUNDWATER CONDITIONS
There were several groundwater-monitoring wells along the ductbank route. These wells were installed
for the purposes of ductbank construction and had been decommissioned during the construction.
S&EE took groundwater level readings at these monitoring wells from April 2014 to February 2015.
The collected data show that the depths of groundwater fluctuated between 6.5 to 12 feet below the
ground surface in the Linear Park; and the depths of groundwater fluctuated between 3 to 6 feet below
the top of pavements in the plant. We believe that the groundwater level is affected by precipitation
and the lake level.
Job No. 1512 4 S&EE
3.5 PREVIOUS DUCTBANK CONSTRUCTION EXPERIENCE
3.5.1 EXCA"TION AND SHORING
As mentioned previously, electrical ductbank was recently constructed at Boeing Renton Plant. The
ductbank is relatively close to the proposed steam utilidor. S&EE performed a geotechnical investigation
for the design of the ductbank project, and provided monitoring services during construction. Due to the
similarity of the two projects, we believe that our experience with the ductbank project would benefit the
proposed steam utilidor project.
For the ductbank excavation,the contractor first excavated a trench about 5 feet wide and to a depth of about
3 to 4 feet below the ground surface. Then trench boxes or steel sheets were installed inside the trench as
shoring. The crew would then excavate inside the boxes. In case of steel sheet shoring, the excavation
would begin after the sheets were driven to the desired embedment. A vibratory hammer,APE 50,was used
for driving the steel sheets. Each sheet was over-lapped about 6 inches along the length of the excavation.
18-inch-wide sheet piles were also used for narrow locations. As the excavation progressed,the crew would
install pumped jacks(horizontal bracing)in both horizontal and vertical directions. The maximum depth of
excavation ranged from about 7 to 12 feet, including a maximum of 18 inches over-excavation for subgrade
stabilization.
For vault excavation the contractor first excavated a hole,about 5 to 8 feet in depth. Then steel sheets were
driven at 4 sides of the hole. A trench box was installed inside the enclosure as bracing, and then the
excavation was performed inside the trench box. The maximum depth of excavation was about 16 feet,
including 18 inches of over-excavation for subgrade stabilization.
When the ductbank crossed under existing utilities, the installation of steel sheets or a trench box could
damage the lines. As such, the contractor would install 3" x 12" treated timber lagging as shoring. As
each piece of lagging was installed the crew would fill the void behind the lagging with 1-'/4-inch crushed
rock or pea gravel. A sledge hammer was used to tamp the lagging and shovel handle was used to prod
the rock to remove any void.
Job No. 1512 5 S&EE
3.5.2 SUBGRADE STABILIZATION
Depending on the subgrade condition three methods were used for subgrade preparation and stabilization:
1) If the subgrade soil was not wet, soft or organic and was stable enough to receive compaction, a
1,000-pound vibratory plate compactor would be used to compact the subgrade to a firm and
unyielding condition. Then a 6-inch-thick of 1-'/4-inch minus crushed rock base course would be
placed over the compacted subgrade. The same compactor would be used to compact the base
course to a firm and unyielding condition.
2) If the subgrade was not organic, but the soil was soft and not stable enough to receive
compaction, the loose soil cuttings over the excavated subgrade would be removed by machine
and hand shovels. A non-woven geotextile with a minimum 200-pound grab tensile strength
would be placed over the subgrade. The geotextile was installed flat with all wrinkles removed
and edges overlapped by one foot. Then a 6-inch-thick of 1-'/4-inch minus crushed rock base
course would be placed over the geotextile and the same compactor was used to compact the
crushed rock to a firm and unyielding condition.
3) If the subgrade was very soft/loose and wet, the subgrade would be over-excavated 18 inches.
After all loose cuttings from the excavation process were removed from the subgrade, a one-foot-
thick of quarry spalls would be placed over the entire subgrade. The contractor would then
compact the spalls with the back of the trackhoe bucket until the subgrade became stable. If the
compaction caused the spalls to sink into the subgrade, a second lift of quarry spalls would be
placed and compacted until the subgrade became stabilized by the quarry spalls. The crew would
then placed a 6-inch-thick lift of 5/8" x 1-'/4" crushed rock (choker stone) over the spalls. The
crushed rock was then compacted to a firm and non-yielding condition using the same compactor.
3.5.3 BACKFILL
Backfill was performed using one of the following methods.
l) In areas of no space restraint, the contractor would excavated a 1 H:1 V slope at both sides of the
poured ductbank. The bottom of the slopes would extend to aboutl8 inches below the top of the
duct bank. The purpose of these slopes was to remove the loosened/disturbed sidewalls. The
excavation would then be backfilled with structural fill. The material was placed in 12-inch-thick
lifts and each lift was compacted to a firm and non-yielding condition by a trackhoe-mounted
Job No.1512 6 S&EE
hoepac. During the process, the contractor would bench the side slopes to allow the backfill to
key into the slopes.
2) In areas of space restraint, the contractor would use CDF for backfill. The CDF was poured into
the excavation until reaching 2 feet below the top of the ground surface. Then a vibratory
hammer was used to remove the steel sheets that were used for shoring. The sheets were
removed while the CDF was still fluid so it would the flow evenly as the sheets were extracted.
The level of CDF would drop in a correlating manner when the shoring was removed indicating
that the CDF was filling the voids left by the sheets. After the last of the shoring was removed, a
vibrator would be used to assist the CDF filling all cracks and voids. This procedure had
prevented sidewall caving or ground settlement.
3.5.4 DEWATERING
For excavation close groundwater table, dewatering was successful using pumping from sump holes. For
excavation below groundwater table and in areas where subgrade soils had moderate to high hydraulic 1
conductivities, wellpoints were used. The wells were installed in a single row, parallel to the duct bank, J
or surrounding the vault excavation. The wells were installed and began to function one to two weeks
before the excavation. Typically, the wellpoints were spaced at 5 to 7 feet on center, depending on the
subsurface conditions. The wells were 20-foot long PVC pipes that consisted of 3-foot-long, 2-inch-
diameter slotted pipes at the tips and 17-foot-long, 1.5-inch-diameter risers. The drilling crew used a 5-
inch hollow stem auger to drill a 20-foot borehole. The pipe was installed through the hollow stem of the
auger. Once the pipe was in place the crew poured 3 bags of Colorado Silica Sand (10-20 particle size)
around the pipe to pack the slotted screen, and poured bentonite chips for the remainder of the borehole.
Each individual well was connected to an 8-inch-diameter PVC manifold leading to a vacuum pump. The
removed groundwater was retained in nearby baker tanks.
' I
I�
Job No. 1512 7 S&EE
4.0 ENGINEERING EVALUATIONS AND RECOMMENDATIONS
4.1 GENERAL
1. The subgrade conditions at the proposed steam utilidors and vaults include existing fill and native
soils. Both include loose to medium dense, sand, silty sand and silt. Since the construction will
result in essentially no increase in overburden pressure, we expect no new compression of the
subsoils, and thus no new ground settlement under static condition. On the other hand, the
subsoils below groundwater table and to a depth of about 100 feet are prone to liquefaction during
strong earthquakes. Liquefaction is a condition when vibration or shaking of the ground results in
the excess pore pressures in saturated soils and subsequent loss of strength. Liquefaction can
result in ground settlement or heaving. Our evaluation shows that liquefaction can results in a
maximum ground settlement on the order of 13 inches.
2. Soft and wet silty soils should be anticipated for excavation deeper than 5 to 6 feet in the Linear
Park, and deeper than 4 feet in the plant. Soft and unstable subgrade would require stabilization
so that a stable work base can be created and re-compression of the disturbed subgrade soils can
be avoided. Previous experience at the plant has shown that soft and wet subgrade can be
stabilized using quarry spalls,and soft and dry subgrade can be stabilized using geotextile.
3. Excavation shoring will be required at locations where open cut is not feasible. Previous
ductbank construction had utilized shoring system including speedshore, steel sheets, trenches
boxes, and sheet piles. Timber lagging was also used at crossing of existing utilities. We
recommend that the contractor review the soil conditions carefully and be flexible in the system
they select. The contractor should pay special attention to excavations along the existing
railroad tracks. Any gaps between soil cut and shoring walls should be filled with CDF the
same day of the excavation. Any ground cracks near the tracks, if found, should be filled
with CDF immediately.
The contractor should also be aware of possible sidewall caving when trench boxes or speed-
shore are retreated. The caving will leave loose sloughing at the bottom of the excavation. This
loose soil must be removed or compacted in place so that future ground settlement can be
avoided. Compaction of such loose sloughing is not always feasible due to the proximity of
groundwater table and possible sidewall disturbance by vibration. When cleaning by excavators
and hand shovels are not possible,the contractor should be prepared to remove the loose soil by a
Job No.1512 8 S&EE
vac truck. Also, backfill with CDF is necessary when compaction is not feasible, such as at the
locations of utility crossing. Backfill with pea gravel should be avoided as it may create
difficulties in future excavation.
4. Shallow groundwater table is present at the site. Previous construction at the plant had utilized
sumping and wellpoints. The contractor should note that: a) Boeing Renton Plant has limited
allowance for daily discharge of water from all construction activities onsite. Currently, Metro
King County allows for 25,000 gallon per day discharge to the storm/sewer system. The county
may suspend discharge temporarily for a day or two during heavy rainstorm events. The above
restrictions may affect construction sequence; the contractor should thus plan accordingly. The
person retains the discharge permit for Boeing is Ms.Doris Turner<doris.s.turner@boeing.com>;
b) Pre-discharge treatment may be required for water quality control. Again, Ms. Doris Turner
should be contacted for such issue.
5. With the presence of shallow groundwater and soft subsoils, installation of underground utilities
requires adequate equipment, manpower and experience. Similar projects were completed
successfully at the plant. We recommend that the earthwork contractor review the project
information carefully and formulate a work plan prior to excavation.
4.2 EXCAVATION AND SHORING
4.2.1 SHORING DESIGN IN GENERAL
Since the soil conditions changes throughout the utilidor route,one set of soil pressure diagrams for shoring
design may not be adequate. As a starting point, we recommend the following soil parameters for the
design. We should review the design and provide recommendations for necessary adjustments.
Soil's total unit weight: 115 to 130 pcf(pounds per cubic feet)
Soil's buoyant unit weight: 45 to 70 pcf
Active soil pressure:45 pcf,equivalent fluid density,above groundwater table
Active soil pressure:20 pcf,equivalent fluid density,below groundwater table
Passive soil pressure:240 pcf,equivalent fluid density,above groundwater table(include 1.5 safety factor)
Passive soil pressure: 80 to 100 pcf, equivalent fluid density, below groundwater table (include 1.5 safety
factor)
Job No.1512 9 S&EE
Imbalanced hydrostatic pressure should be added to the active side. The pressure will depend on the type
of dewatering method. A 2 feet over-excavation at the passive side should be considered in the design.
4.2.2 SHORING DESIGN FOR EXCAVATION NEAR RAILROAD TRACKS
We have developed lateral pressure diagrams for excavation shoring near the existing railroad. These
diagrams are included in our November 23, 2015 technical memorandum. A copy of this memorandum is
included in Appendix B of this report.
4.Z3 OPEN-CUT
Open cuts above groundwater table may be sloped at I H:IV. Open cuts below groundwater table may
need to be 1.5H:1 V or flatter. For a combination of open cut and shoring, benching in the upper 2 to 4
feet works well in the past as it lessens the overburden pressure and facilitates backfill. The benches
should have a 1:1 ratio between height and horizontal run, and the height of each bench should be limited
to 2 feet.
4.2.4 SUBGRADE PREPARATION
All loose soil cuttings should be removed prior to the placement of bedding materials. Wet and loose
subgrades should be anticipated. The contractor should make efforts to minimize subgrade disturbance,
especially during the last foot of excavation. Note that subgrade disturbance in wet and loose soil is
inevitable, and subgrade stabilization is necessary in order to avoid re-compression of the disturbed zone.
Depending on the degrees of disturbance, the stabilization may require a layer of quarry spalls (2 to 4
inches or 4 to 6 inches size crushed rock). Based on our experience at the plant, when compacted by a
hoepac or the dynamic force of the excavator's bucket, a 12 to 18 inches thick layer of spalls would sink
into the loose and soft soils, interlock and eventually form a stable subbase. A chocker stone such as 5/8"x
1-1/4" clean crushed rock should be installed over the quarry spalls. This stone should be at least 6 inches
in thickness and should be compacted to a firm and non-yielding condition by a mechanical compactor that
weighs at least 1,000 pounds.
In the event that soft silty soils above groundwater table are encountered at subgrades, the subgrade should
be over-excavated for a minimum of 6 inches. A non-woven geotextile having a minimum grab tensile
strength of 200 pounds should be installed at the bottom of the over-excavation and the over-excavation
Job No.1512 10 S&EE
backfilled with 1-1/4" minus crushed rock. The material should have adequate moisture and be compacted
to a firm a non-yielding condition using the same compactor.
4.2.5 BEARING CAPACITYAND SUBGRADE MODULUS
Subgrade so prepared should have an allowable bearing capacity of 1,500 psf(pounds per square feet),
and a subgrade modulus of 50 pci (pounds per cubic inches). The bearing capacity includes a safety
factor of 3, and can be increased by 1/3 for transient loads. Total settlement under these loads should be
on the order of 1/4 to 1/2 inch.
4.2.6 BACKFILL
Structural fill materials should be used for all backfill. Structural fill materials should meet the following
material and compaction requirements.
Material Requirements: Structural fill should be free of organic and frozen material and should
consist of hard durable particles, such as sand, gravel, or quarry-processed stone. The onsite
granular fill soil is suitable for structural fill on a selected basis, and the native soils below the fill
are not suitable. Suitable imported structural fill materials include silty sand,sand,mixture of sand
and gravel (pitrun), recycled concrete and crushed rock. All structural fill material should be
approved by an engineer from our office prior to use.
Please note that: 1) Flowable CDF (Control Density Fill) is considered an acceptable structural fill.
The material should have a minimum compressive strength of 150 psi; 2) Recycled concrete often
has a fines content exceeding 20%,making the material sensitive to moisture. As such,the material
may be difficult to use in wet winter months.
Placement and Compaction Requirements: Structural fill should be placed in loose horizontal
lifts not exceeding a thickness of 6 to 12 inches, depending on the material type, compaction
equipment,and number of passes made by the equipment. Structural fill should be compacted to
a firm and non-yielding condition or at least 95% of the maximum dry density as determined
using the ASTM D-1557 test procedures.
Job No.1512 11 S&EE
4.3 LATERAL EARTH PRESSURES ON UNDERGROUND WALLS
Lateral earth pressures on permanent retaining walls, underground vaults or utility trenches/pits, and
resistance to lateral loads may be estimated using the recommended soil parameters presented in the
following table.
Coefficient
Equivalent Fluid Unit Weight(PCF) of
Friction
at Base
Active At-rest Passive
Structural fill and 40 50 200 0.5
native soils
Note: Footing drains are not recommended and thus hydrostatic pressures should be added to the
above lateral earth pressures.
The at-rest case applies to unyielding walls, and would be appropriate for walls that are structurally
restrained from lateral deflection such as basement walls,utility trenches and vaults. The active case applies
to walls that are permitted to rotate or translate away from the retained soil by approximately 0.002H to
0.004H, where H is the height of the wall. The passive earth pressure and coefficient of friction include a
safety factor of 1.5.
SURCHARGE INDUCED LATERAL LOADS
Additional lateral earth pressures will result from surcharge loads from floor slabs or pavements for
parking that are located immediately adjacent to the walls. The surcharge-induced lateral earth pressures
are uniform over the depth of the wall. Surcharge-induced lateral pressures for the "active" case may be
calculated by multiplying the applied vertical pressure (in psf) by the active earth pressure coefficient
(Ka). The value of Ka may be taken as 0.36. The surcharge-induced lateral pressures for the "at-rest" case
are similarly calculated using an at-rest earth pressure coefficient (Ko) of 0.5. For surcharge loads that
are not adjacent to the wall, the induced lateral earth pressure will depend on the magnitude of the
surcharge and the distance from the wall. Such induced lateral load can be estimated using the equations
shown on Figure 8.
Job No.1512 12 S&EE
The slope-induced lateral earth pressure can be accounted for by increasing the effective height of the
wall by one-half the slope height. The traffic-induced lateral earth pressure can be accounted for by
increasing the effective wall height by 2 feet.
SEISMIC INDUCED LATERAL LOADS
For imbalanced, seismic induced lateral loads, the dynamic force can be assumed to act at 0.6 H above the
wall base and the magnitude can be calculated using the following equation.
Pe =10H
Where Pe = uniform pressure in psf
H = wall height in feet
BACKFILL BEHIND WALLS
Structural fill materials should be used for backfill. The material and compaction requirements are
presented in Section 4.2.6.
4.4 BUOYANCY RESISTANCE
The subsoils below groundwater table will liquefy during strong earthquakes. As such, buoyancy force
should be considered in the design. If the self-weight of the structure and equipment is insufficient to
resist the buoyancy force, an extended base can be considered for additional resistance. In this case, the
resistance can be calculated using the weight of the soil above groundwater table and above the extended
base. A soil's unit weight of 120 pounds per cubic feet (pcf) can be used for this purpose. Sidewall
friction should be ignored.
i
Job No.1512 13 S&EE
4.5 PAVEMENTS
4.5.1 PA VEMENT DESIGN
Asphalt pavements constructed over prepared subgrades can be designed with a CBR(California Bearing
Ratio) value of 8; concrete pavement can be designed with a subgrade reaction modulus of 100 pci
(pounds per cubic inches). Top course and base courses under pavements should consist of well-graded
crushed rock conforming to WSDOT specifications for Crushed Surfacing, Specification 9-03.9(3). The
material should be compacted to at least 95 percent of the maximum dry density, as determined by the
modified Proctor compaction test(ASTM D 1557)or to meet standards dictated by project specifications.
Please note that recycled concrete has been used as base course at the plant. As the material often has a
fines content exceeding 20%,the material is moisture-sensitive and may become problematic (pumping and
unstable)in wet winter months.
4.5.2 SUBGRADE PREPARATION
We recommend that all pavement subgrades be proof-rolled to identify areas of soft, wet, organic, or
unstable soils. Proof-rolling should be accomplished with a heavy (12-ton) vibratory roller, front-end-
loader, or loaded dump truck making systematic passes over the subgrade while being observed by a site
inspector from our office. After proof-rolling, the top 12 inches of the entire subgrade should be
thoroughly compacted to a firm and non-yielding condition or at least 95 percent of the maximum dry
density, as determined by the modified Proctor compaction test (ASTM D 1557). The subgrade soil
should have adequate moisture content(within+/-2%from optimum)at the time of compaction.
In areas where unstable and/or unsuitable subgrade soils are detected during proof-rolling, these soils
should be over-excavated a minimum 12 inches. Additional over-excavation depth may be required to
remove buried debris, organic or very soft soil. Non-woven geotextile having a minimum 200 pounds
- grab tensile strength may be necessary for additional subgrade stabilization. The geotextile should be
placed with 12-inch overlaps and all wrinkles removed. The over-excavation should then be backfilled
with 1-1/4"minus crushed rock. The material should have adequate moisture content, and be compacted
to a firm and non-yielding condition by a compactor approved by our site inspector.
Job No.1512 14 S&EE
4.6 SEISMIC DESIGN PARAMETERS
The geotechnical-related parameters to be used for seismic design in accordance with 2012 IBC
provisions are evaluated as described in Section 1613.3 of the 2012 IBC Code. The spectral response
USGS website using a latitude of 47.49 degrees and a longitude of 122.21 degrees. The values for Site
Class B(rock)are:
Ss= 1.455 g (short period,or 0.2 second spectral response)
S, =0.545 g (long period,or 1.0 second spectral response)
The Site Class is selected using the definitions in Chapter 20 of ASCE 7-10 considering the average
properties of soils in the upper 100 feet of the soil profile at the site.Using the boring data,we determined
that the subsoils correspond to Site Class E("Soft Clay Soil")in Table 20.3-1 (ASCE 7-10).
The site coefficient values, obtained from Section 1613.3.3 of the 2012 IBC, are used to adjust the
mapped spectral response acceleration values to get the adjusted spectral response acceleration values for
the site. The recommended Site Coefficient values for Site Class E are:
Fa= 0.9 (short period,or 0.2 second spectral response)
F„= 2.4 (1.0 second spectral response)
The most recent USGS Earthquake Hazards Map (U.S. Geologic Survey web site, 2008 data) has
indicated that a horizontal peak acceleration (PGA)of 0.61 g is appropriate for a 4,275-year return period
event,i.e.an event having a 2 percent chance of being exceeded in 50 years.
Based on our evaluation, the subsoils below the groundwater table and to a depth of about 100 feet are
liquefaction prone during the subduction zone earthquakes. The evaluation of liquefaction potential is
complex and is dependent on many parameters including soil grain size,density, surface loading, level of
ground acceleration, and duration of shaking. Our evaluation shows that liquefaction can results in a
maximum ground settlement on the order of 13 inches.
Job No.1512 15 S&EE
4.7 ADDITIONAL SERVICES
We have been retained by the owner to perform additional services during the construction of the project.
Our scope will include the following:
1. Monitor trench and vault excavations.
2. Monitor dewatering and shoring installation.
3. Monitor the placement and compaction of structural fill. We will confirm the suitability of the fill
materials, perform field density tests, and assist the contractor in meeting the compaction
requirements.
4. Response to contractors' RFI.
5. Attendance of construction progress meeting when necessary.
6. Other geotechnical issues deemed necessary.
5.0 CLOSURE
The recommendations presented in this report are provided for design purposes and are based on soil
conditions disclosed by the available geotechnical boring data. Subsurface information presented herein
does not constitute a direct or implied warranty that the soil conditions between exploration locations can be
directly interpolated or extrapolated or that subsurface conditions and soil variations different from those
disclosed by the explorations will not be revealed. The recommendations outlined in this report are based
on the assumption that the development plan is consistent with the description provided in this report. If the
development plan is changed or subsurface conditions different from those disclosed by the exploration are
observed during construction, we should be advised at once so that we can review these conditions, and if
necessary,reconsider our design recommendations.
Job No. 1512 16 S&EE
Washington — Renton
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Revised03-09 Figure 1 - Site Location Map Copyright 2009®The Boeing Company.All rights reserved. -
4-86 Building
N T 8-5-D
100 50 0 100 200
SCALE IN FEET B-2-2015(4-86)
LEGEND:
STEAM UTILIDOR PREVIOUS BORING r
B•-4-D
B-9-2012
low—
DUCTBANK
PREVIOUS CONE t.
PENETRATION
TEST HCP-1 . � X #
'B-2-1965(4-17)
-•" \ ,
❑a B-3-D ,. . . . , .. x
4-17 Building
PREVIOUS BORING -
%PREVIOUS1
B-1 (CC128) BORING 3
y
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Figure 2 - Site and Exploration Plan
F• ,•.� �+* Bryn Mawr £� s�`` EXPLANATION
�1� Facility Boundary
Current ;, ., •
'• Cedar River --- '` r Former Lake Washington Shoreline
t Waterway
4 ,:• Renton A '" • I ��I I ® Ancestral Black River
Facility ,� -• - � 7
[ - ® Ancestral Cedar River
..' . •. .--t Boundary •.`` �,�
�i •i North Bridge ,--
,�., Current Cedar River Waterway
' •.. �:!VIA
d �F' +; .MENI � `; i ® Wetland
-4. +;\ r -- } 0 Forested Uplands
- 1 Geologic Cross Section (see figure 2-8)
Former Lake
Washington .�
Shoreline` [ ; Approximate
r, + .
Location of
. Project Site
..
.� . . +3
{
+ J - •
•, Ancestral
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--- •� '. . Renton Airport Forme
` .. Y; .�.. �• . . • .;, s Lake Washingto
Shoreline, Black an
,,,�{ ` ' • • f•�� Cedar River Channel
_• �mow.'"#-'�' . . • 'r. . r' ' � B
.� r• ll � , - Figure 3
01-0183 Fig2-9.ai
_ I
Il7TI I 'i I'.nl N Inra,\n II .
- ' " �I wA9HINGTON gWfgN O AND[AR N RR[OURC[f
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� 1•-•1�.I �tI L j ' t
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PRELIMIN RY LIQUEFACTION E TIOIN SUSCEPT1811_ITY MAP O
�• �\ rI �. ��1C IV c �.., RE ITON QUADRANGLE, WASHINGTON
��•',�. 1 h' '�.:�'}'I x I II r. �•I I II'
7 IV II by
IV IV STEPHEN P. PALMER
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26'.
I I
I I "� ....... maD unity,derived Irem M.Illne,u.,1965a i j��y\ ��r„ / �I I f �: �: mo' " \ !
3 1 in,P..U': \ r1y4/n
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� I I ,ions n,port.non roWr,r,l and poFt v.non JluNum
A N PTluui.IIILN L F Ciro r9VSCF Y
II ! I �` It �\ CATEGORY 11 Include,past-V„nen I,<uarrine dep.lt,anJ<ollurlum-
�1 ✓ `)`•/ \� ` 1. `,. '\, { 1 ' LlglhFKTION 9usc[PTI[ILITr LOW TO NIGH
% '� - III GATEWRY IN Inclutl..,II PIM,mc.ne ilacr,l and nanela9l,l
✓ l \ 13� `./rJ depe,IN and the OI<eel,Mudlbw
7 dr? I 1 d�- 0_i'll\7 LIQUI-11"9u5C11-ILT1.LOW
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1 +l � I. I}\e• ! ' .\ ,II j..-- II 1.14 '� LIQUEFACTION slncenlulnr:Low To NIL
1
` x :lI --- e. .bin—.,tee.e,a WN..
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I
`,1 i - , I ;I 'r\ I > ✓ \\\ • i o 5 NHtprlcmlTeuel,cN^n,IIe Id.n--11 he c rre,pan reference vet,t u bar enNbw.e nJ 9cnuner, Sul i,nk y�o^ut.the 9
.^a<a M.n•.n iar Lh.m.In L,nle x of cni:ber tl and 9chunaL IR90.
4
f - I - '1 cof lea .e.. en bar Ieseb D,e n^swb•.lyk.e.n.l c ur.aa
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9 1� NT I:. - - yw I w,tont o.h•na<r m,e,ne.or L,L.w„.melon.
Abantl;netl<hannNa o/the Green It—that db n appear to contain
nerm lt<nl,cream..r pp t .aria..see n.
II\
III I,
✓ b'' ' r• - },' "' I '. —.__._ Oral.ee.and atraa tn,t aDDear ro be abandoned channel,
\ tl of the Cr.n Rlvr.m•
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! _ (I_r 1..�� r..: .� -r+'•4'—`4'X4,�� I.I. �__ _ .- _____ � - -.. .. .._
r _ -- — \
r -— - -
q �.
;, `� .Ietn. l -•:-• dA" ^I. _ ., I \ this ma—reart only as a genera.guide to dcl.noa:e areas orone,to Lquefaction.This
i' e•�i \ map is rot d substitute for a srspecho inveslganon m:to assess the poteal for
f - ,,' I ~(,\ `11 �— m+r..4 n liquelacllon forary development project.BCceuse of the-egiona nature or this map and
becauselhedsta used:nthe iquefaclionsusreptibllhyaasnssmeN havebren subdivided
•�'.!"_ {FI. 1 4' zd 'l \ u \ III '!% on the be$i$of regional geological mapping,!his map cannot be used to determine the
IF.21L presence or absence of'q le uefiable sa beneath any speci!ic locality,To make this
t 11 ) •f i '/• '.a ) determination!requires site-specHk geotechnica:!nve5tigatbns performed by qual"ied
II I" practitioners.'
r ,,. •e ,.,.r W e ,
_ Figure 4
I Iry
I
i
t
I
Technical Information Report—Revision l
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29,2016
THIS PAGE INTENTIONALLY LEFT BLANK it
Davido Consulting Group,Inc.
TIR_Boeing Renton Site Logistics Project_04086 Steam Utilidor_Final_Revision I
B-1-2015(4-89) B-1-D B-2-D B-3-D
0 Rail Road — 0
ark brown silty sand
4"Asphalt (Topsoil)
Fli_l_ Brown and gray, sand and silty sand
5 with gravel (medium dense to loose) 5
---------------- Q------------- ----------------------------------------------- - - - - ----------- �
10 10
H
NATIVE: Gray silt and silty sand W
W -layer of gavel at 10 feet to 12
(medium stiff to very soft) W
LL feet below the top of ground (medium dense to loose) _
15 -15 a
= W
F- 0
a
W
13
20 20
NATIVE: Brown and gray sand and gravel
{loose to medium dense}
25 25
i—30 - 30
4-86 Steam Utilidor Fiqure 5
S&EE 1512 Generalized Soil Profile,Section A A
(No Horizontal Scale) See Figure 2 for location
B-3-D
Dark brown silty sand(Top Soil)
— 0 — --0
(Offset 115 feet to the South) Rail Read
(12"concrete at the ground surface)
B-2-1965 (Bldg. 4-17) B-4-D �(/
FILL: Brown sand and silty
-5 FILL:Brown silt and sand with gravel FILL: Silt(mediu stiff) sand with gravel (loose) —5
(medium dense)
--------------------------------------------------V------------------------ -- �J
--- ----- --•---- ---- - -------.-------•-----------•-----------..
NATIVE: Gray silt and silty sand
10 _f— (soft and loose) 10
t—
W
W
W
W =
15 15 a
= I NATIVE: Sand, silt and silty sand
a (loose to medium dense with W
s�
W occasional dense pockets)
20 20
25 25
—30 30
4-86 Steam Utilidor Fiqure 6
S&EE 1512 Generalized Soil Profile,Section B-B
(No Horizontal Scale) See Figure 2for location
B-4-D B-2-2015 (Bldg. 4-86)
(12"Concrete at ground surface) (8"Concrete at ground surface)
0 —0
4 FILL: Gray silt(medium stiff) FILL: Sand and silty sand
(medium dense to dense)
----- -- -----
5 5
NATIVE: Silt, silty sand and sand
10 (soft and loose with occasional medium dense pockets) L 10
H
W
W
W
W =
UL 15 15 a
= W
a
W
0
20 -20
C25 —25
30 30
S EE 1512 4o Horizam UScalr Generalized Soil Profile,Section C-C
(No Horiz�ntalSCale) See F i ure2 forlocation
0 0
m=0.1
0.2 \ Q2 m=0.6
m=0.5 Z.1 �
m=O.
O4 04
m=0.3
= m=0.4
NP17C /
LL.0.6 0.6
o m R m P� R
� J
J 0.1 .60H 0.2 .78 .59 H
>OB / / 0.3 .60H 0.4 .78 .59H
0s
0.5 .56H 0.6 45 .48H
0.7 .48H j
1
1.0 10.2 .4 .6 .8 1.0
0 0 .5 1.0 2 1.5
VALUE OF (TH (TL) VALUE OF 0-H (�P)
I
POINT LOAD Op op
P
LINE LOAD QL Z=nH pH
FOR m < 0.4
X=1i1 H
vH(UL (0 i�n2)2 H LL �H R FOR m 0.4
Z=nH PH= 0.55QL I 'H(H-)= 0.28n� 3
P (Q16+-n )
PH
� FOR m>0.4: FOR m )0.4_
H �H ( Ham)_ 1.28m2n (H2 )= 1.77m2n2
R L (m2+n2)2 H Op (fn2+-n2)3
I tt 4RESULTANT P - 0.64 QL aH =�N�2(1.18)1 H (m2+1 )
PRESSURES FROM LINE LOAD QL 9�
(BOUSSINESQ EQUATION MODIFIED BY EXPERIMENT) 3 C.
TxzH
SECTION A-A
PRESSURES FROM POINT LOAD Op
(BOUSS(NESQ EQUATION
MODIFIED BY EXPERIMENT)
Reference: Foundations and Earth Structures,
Design Manua! 7.2, Department of the Navy, May 1982 Calculation of Surcharge Loads
on Subsurface Walls
APPENDIX A
LOGS OF PREVIOUS BORINGS
U� �
° Q
BORING B-1
z L' 8-1-2015 (4-89)
O iL 8 ii m -Si_Si in co Surface condition: Asphalt
0
A 4 inches thick asphalt
sots 5 sP Gray fine to medium sand with fine to medium gravel
s (dense)(fill)
17 18
17 11
15
sM Grayish brown silty fine sand with some fine gravel
(medium dense to loose)
5 s 18
7 9
7
3 18
2 5
1
10 6 18
s ::i :::'GP Gray fine to medium gravel with silty sand
10 (medium dense)
s 13 Svc/ Gray fine to coarse sand,with little fine to medium gravel
9 (medium dense)
15 7 18
8 8
9
9 18
12 0
13
20
(Boring log continued on Figure A-1b)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: August 17-18,2015
Drilling Contractor: Holocene Drilling
Figure A-1 a
S&EE Job No.1508 Boeing 4-89 Building
a
U N h
a� �0
75
BORING B-1
�o ;o Q
Q�
(Continued)
N G O Nco
O U U U
Q U_ m C/)
20—
i9 iz }.��:svv Gray fine to coarse sand with some fine to medium gravel
11 X.■ (medium dense to dense)
'� -at 20 feet driller drove casing to prevent caving
■OX
casing installed from 0 to 30 feet
18 18
12 0 In
10
' ti
.ti
25 20 18
25 12
zz
P7ML
0%
10 18 Gray silt with lenses of fine sand
a s 1 a (medium stiff)
30 1 18 ML
1 18 Gray silt with trace organics
1 (very soft)
35 1 18
1 15
2
40
(Boring log continued on Figure A-1 c)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: August 17-18,2015
Drilling Contractor: Holocene Drilling Figure A-1 b
S&EE Boeing4-89 Building
Job No.1508 g
U N �
BORING B-1
(Continued)
a m ° �, 3 X:-°c E v
40
1 16 wv PT Brown peat with trace wood chips
z 3 `01
`� (medium stiff)
4 wv
vw
wv
wv
..w
wv
wv
wv
w..
wv
wv
w�
w..
wv
wv
wv
45 2 18 sP Gray silty fine sand with trace organics
6 15 (loose)
sw Gray fine to coarse sand with some fine gravel
(medium dense)
50 11 18 ■
10 6
13 ■} ■
■
i■f
' X
tiff
r■."
■Y.■:
■■%%
Vx%
55 s 18 ■
10 5 nEz 0
10 '
:■
r■
.Y
60
(Boring log continued on Figure A-1d)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-I1b auto hammer
Drilling Date: August 17-18,2015
Drilling Contractor: Holocene Drilling Figure A-1 c
S&EE Boeing 4-89 Building
Job No.1508 9 g
BORING B-1
°
°
11 co (Continued)
N O O N O U U coU
60—
12 18 sP Gray fine to medium sand
12 12 (medium dense)
14
65 10 18 X -trace fine gravel at 65 feet
13 7
14
70 10 18
11 5
12
XT
75 1s 18 -trace coarse sand and fine gravel at 75 feet
17 s
13
80
(Boring log continued on Figure A-1e)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: August 17-18,2015
Drilling Contractor: Holocene Drilling Figure A-1 d
SUE Boeing4-89 Building
Job No.1508 g
i
BORING B-1
>°
(Continued)
C O O U U U
iL p� M ;= Cl)
80
12 ,$ sP Gray fine sand
s s (medium dense)
7
85 2 18
4 5
7
ML Gray silt with sandy silt
(medium stiff)
90 0 18
2 17
3
95 11 18 SP Gray fine sand with trace wood chips
10 s Y P
9 (medium dense)
10
(Boring log continued on Figure A-1f)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: August 17-18,2015
Drilling Contractor: Holocene Drilling Figure A-1 e
S&EE Boeing 4-89 Building
Job No.t5os 9 9
BORING B-1
of (Continued)
o� a
N C O CU U U CU U
O p ap co co
100 5 18 sm Gray silty fine sand with trace wood chips and lenses of fine sand
s 11
7 (medium dense)
105 7 18 sM Gray silty sand(loose)
4 13
6
MH Light brown silt with organics(stiff)
110
1 18 \7
3 9
7
MH Gray silt(stiff)
115 3 1s
4 12
5
120
(Boring log continued on Figure A-1g)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: August 17-18,2015
Drilling Contractor: Holocene Drilling
Figure A-1 f
S&EE Boeing4-89 Building
Job No.1508 9
U° BORING B-1
Q� ��
(Continued)
co
N G a O U U co
U
V, iY1 C C C/)
120 25 18 sP Gray fine sand
21 12 (dense)
125 13 18 sP Gray medium sand trace fine gravel
1s 1s 15 (dense)
130 17 18
21 13 sP Gray fine sand
2' (dense)
I
135 20 18
22 16 ERHE
26
140
(Boring log continued on Figure A-1h)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: August 17-18,2015
Drilling Contractor: Holocene Drilling Figure A-1 g
S&EE
Job No.1508 Boeing 4-89 Building
U N �� �
BORING B-1
t U Z °'5 B
o� ° (Continued)
Q)i c V o c= B U
140 24 18 SP Gray fine sand
zz 14 (dense to very dense)
23
145 28 1s
29 13
34
150 25 18
21 16
28
-trace silt below 145 feet, very dense
To
X.
155
160
(Boring log continued on Figure A-1 i)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: August 17-18,2015
Drilling Contractor: Holocene Drilling Figure A-1 h
S&E Boeing4-89 Building
Job No.1508 g
U
g �0
BORING B-1
a ��j ? co
0 N
o� ° (Continued)
w co � a cn
N G 0 O U U U
O � Z C) oo cc v> j
160 22 1e SP Gray fine to medium sand with some coarse sand
za 14 (very dense)
32
165
170 2 18 CH Grayinorganic clay with high plasticity
s 18 9 Y 9 P Y
14 (very stiff)
175
8 18
180 10 10 -lenses of fine sand at 180 feet
Boring aborted at a depth of 180 feet on August 18,2015
due to sloughing gravels causing drill shaft collapse.
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: August 17-18,2015
Drilling Contractor: Holocene Drilling
Figure A-1 i
S&E
Job No.1508 Boeing 4-89 Building
' a
BORING B-1-D
o� k
p m Si c h j Surface condidon: Grass Lawn
0
2 16 SM Dark brown silty fine sand,trace fine to medium gravel,trace organics
12 i (loose to medium dense)(moist)(fill)
I
SM Brown silty fine sand,trace fine to medium gravel(fill)(medium dense)(moist)
5 1e -gray sift at 2.5 to 3 feet
7 I I -soil temperature measured to be 65.2 degrees F
1 1 ff
6 II I!
; 2 ; ts i
2 114 i
I i I
1 1 8 110 � (I
_ 1
I ' 1
10; 4 "a sP Brown fine to medium sand, trace fine to medium gravel(medium dense)(wet)
4 :18
12 I
1 ' I
1
I
1 ,
4 18
5 9
7 sP Brown fine to coarse sand,trace fine to medium gravel(medium dense)(wet)
1
I
-
1 I '
15
' 7 116 '
7 ' 18 I
1 I
I 1 '
i
I 1 1
1 18 I
8 1 _
1 I
1 1 I -
I
20 --I-
I_ '
(boring log continue on Figure A-1b)
Client: The Boeing Company
Drilling Method: Hollow-Stem Auger by a track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 12,2013
Drilling Contractor: Holocene Drilling Figure A-1 a
S&EE Job No.1309-D- Proposed Ductbank
"O
� w
o Q BORING B-1-D
�0 ° (Continued)
ga o )
20 7 18
10 12 / SP Gray fine to medium sand, some fine to medium gravel
12: lense of gray silt(medium dense)(wet)
12 18
11 12
11
26
7 ; 18
r ' 9 , 12
13
r ' ,
-Gray silt at 28.5 to 29 feet
30,
-Gray silt at 31 feet
Boring completed at a depth of 31.5 feet on October 12, 2013.
One groundwater monitoring well installed. The well consists of 2"slotted
PVC pipe from depths of 15 to 20 feet, and solid pipe from 0 to 15 feet.
Groundwater depth measured at 7'-7" on October 19, 2013.
35; '
40,--
Client, The Boeing Company
Drilling Method: Hollow-Stem Auger by a track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 12,2013
Drilling Contractor: Holocene Drilling J
Figure A-1 b
S&E9- Pro osed Ductbank
Job No.1309-D p
I
mo a 8 BORING B-2-D
' 41 1 U
a z c�
'n'0 a y
o Surface condition: Grass Lawn
0 s 1a
6 14 sM. Dark brown silty fine to coarse sand(medium dense)(moist)(fill)
s l
7 18
12
, , I
s 18 I sP Light brown fine to coarse sand,trace fine to medium gravel (fill)(medium dense)(moist)
, ' I
I I
' S 2 18
' 3 , 18
6 ML Gray and brown silt,trace organics and fine sand lenses
I 1 (soft to medium stiff)(moist to wet)
-soil temperature measured to be 62.4 degrees F
1
1 ,18
1 '18 -lens of fine gravel at 8 feet
2
, i 1
i
10, 3 '18
2 i18
I � 3 ,
I I
I
, , I
I
,
1 � 2 118
4 118
2 ,
1 ' ,
15, o i 18 '
0 18 ;
a
SM Gray silty fine sand with lenses of organics(very loose)(wet)
1 1 ,
I I
' 2 1s
1 I '
ML Brown silt,trace organics and wood debris(very soft)(wet)
1 i ,
(boring log continue on Figure A-2b)
' Client: The Boeing Company
Drilling Method: Hollow-Stem Auger by a track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 12,2013
Drilling Contractor: Holocene Drilling
Figure A-2a
S&EE Job No.1309-D• Proposed Ductbank
1
a
�o
BORING B-2-D a � t S' (Continued)
U U (n
20
o ; 18 ML Gray silt,trace very fine sand, trace organics (very soft)(wet)
' -wood debris at 20 feet
' Sp i Gray fine to medium sand(medium dense to loose)(wet)
1 I
4 1 18
8 18
12 '
I '
I '
I '
I ' I
r
26; s 1s
8 I 10
1 ' 7 I
I ' I
1 ' I
I ' 1
7 ,18
I ' 6 11e
2 I
I ' I
I ' I
1 � 1
I
I ' I
30 18
2
4 J;18 -- I
' a M�. Brownish gray silt, trace organics (medium stiff)(wet)
I ; I
I 1
I ' 1
Boring completed at a depth of 31.5 feet on October 12, 2013.
35;
1 �
I I
, I I
401 _
Client: The Boeing Company '
Drilling Method: Hollow-Stem Auger by a track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 12,2013
Drilling Contractor: Holocene Drilling
Figure A-2b
S&EE ,
Jonr4o.1309_p Proposed Ductbank
BORING B-3-D
ayi aNi a V
c c y j Surface condition: Grass Lawn
' 0 2 18 , sM
4 18 , Dark brown silty sand(topsoil)
14
I sm/ Brown silty fine sand and fine sand with trace silt,trace fine to medium gravel
SP (f+ll)(loose)(moist)
3 i 18
2 4
' 3
i
5
e ; 18
2 i 2
,
i
4 :18
1 i 12
2 i ML Gray silt with lenses of gray fine sand (soft to medium stiff)(mcist)
10' _
18
4
3 i 18
3 �
sP Brownish gray fine sand (loose to medium dense)(wet)
s 1a
4 10
s
15, 18 5 '5 18 �
3 ' 18 ,
' S 18 � iI
7 ,
20
(boring log continue on Figure A-3b)
Client: The Boeing Company
Drilling Method: Hollow-Stem Auger by a track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 12,2013
Drilling Contractor: Holocene Drilling
Figure A-3a
' S&E9-Job No.1309-0- Proposed Ductbank
BORING B-3-D
° (Continued) 1
UvUc E U
Co �= 0 j
20,
10� 18 ; sP Gray fine sand with lenses of peaty silt(medium dense to dense)(wet)
13
' I �
I I
� I
1 '
, 1
7 18
7 12
7 -fine to coarse sand,trace fine gravel at 23 to 24 feet ,
I � �
I � i
I I '
26 1 '
5 18
I 7 1 ,s
I g I
I i
I ' I
I '
I
1 ' I
1
16 18
12
I i I i I I
I I I
I I
I I, , 1
30 i
1 5 :18
7 18IVI
2 1
, , I Boring completed at a depth of 31.5 feet on October 12, 2013.
t One groundwater monitoring well installed. The well consists of 2"slotted
PVC pipe from depths of 15 to 20 feet, and solid pipe from 0 to 15 feet.
Groundwater depth measured at 9'-9'I on October 19, 2013.
I f
I I I
■1 ' I ' 1 '
' I
I
I , I
I , I
40:
_
-- - - --
Client: The Boeing Company
Drilling Method: Hollow-Stem Auger by a track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 12,2013
Drilling Contractor: Holocene Drilling Figure A-3b
S&E9-yob No.1309-D p Pro osed Ductbank ,
a
BORING B-4-D
ayi a�i a Cl)
c j Surface condition: Driveway
0
C 12 inches thick concrete
3 18 a a I ML Bluish gray silt, trace very fine sand,trace organics (medium stiff to very soft)(moist)
2X
i
0 18
Q 0 12
6 ' ' 1 18
z 1e
sM Gray silty fine sand (loose)(wet)
I (I
2 12 III
' z
10, o
o ,18IVI -lens of fine to medium gravel at 10.5 feet
o ML Brownish gray silt with trace wood chips, lenses of peat and fine sand.
i (soft to medium stiff)(wet)
z ,a
' z
15
3
4 i 18
_ 1 4 iIvl
i
o ;o ' SM Gray silty fine sand with trace wood chips and lenses of brown peaty silt.(very loose)(wet)
III
20
--I - —
Client: The Boeing Company
Drilling Method: Hollow-Stem Auger by a truck-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 10,2013
Drilling Contractor: Holocene Drilling Figure A-4a
S&EE Proposed Ductbank Pro
Job No.13o5-0- p
w BORING B-4-D
(Continued)
co
m Surface condition: Driveway
20 1 1 1al 1
z 1a ML Brownish gray silt,trace organics (grass), lenses of gray fine sand
3 : (loose to very loose)(wet)
I I
I � I
I I I
I I '
I o I ,s
0 18
of
I I
I I I
I I I
I I '
I
I I I
26 1 1s t
1 18
' I 1
I I
I I I
1
I I
I
I I
' 1 118
2 10
2 1
I ' I
sM Gray silty fine sand with silt lenses (loose to medium dense)(wet)
I I I
I
II
30, 3 ,18
18 illl
I ' 4
I ' I
I I
5 '18 I II
5 '18
8
1 I 1
I ' i
Boring completed at a depth of 33 feet.
I I I I I
One vibrating wire piezometer(VWP)installed at a depth 32 feet. '
One foot of sand pack installed below and above piezometer.
35 Groundwater depth measured at 3'-10"on October 19, 2013.
I , 1
1 1 I I
1 1 '
One groundwater monitoring well installed. The well consists of 2" slotted
PVC pipe from depths of 13 to 18 feet, and solid pipe from 0 to 13 feet.
Groundwater depth measured at 3'-1" on October 19, 2013-
1 '
1 1
1 ' 1
401
Client: The Boeing Company
Drilling Method: Hollow-Stem Auger by a truck-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 10,2013
Drilling Contractor: Holocene Drilling Figure A-4b
S&EE Job No.1309-D-4-81 p ose Prod Ductbank at South of 4-81 Building
In
N
BORING B-5-D
n
a m a
m c c in j Surface condition Driveway
0
Ac 4"asphalt over 4" recycled concrete
' SP Brown fine sand, trace silt, trace fine to medium gravel(fill)(medium dense)
14 18 , -fine to coarse sand,trace silt,trace fine gravel at 2.5 feet, slightly cemented
19 9
,
11
6 2 18
10 4
10
z
„ -2" lens organics at 7.8 feet
5 /j ML -8"grayish brown peaty silt at 8 feet
Gray sift,trace very fine sand, trace organics(very soft)
Q ;
10 _ F ; ( -depth of groundwater measured at 9'-g"on February 5, 2014
0 to
2
5 18 1 SM • -no sample recovery, likely silty sand(loose)
3 0
i
15 a 19 ! Brownish gray silty fine sand with lenses of peaty silt and organics(very loose)
2 8
2 )1
l
0 18 , �I
0 18 1I i
2 1
Y�
20
(boring log continue on Figure A-5b)
Client: The Boeing Company
Drilling Method: Hollow-Stem Auger by a truck-mount rig
Sampling Method SPT sampler driven by 140-lb auto hammer
Drilling Date: January 28,2014
Drilling Contractor: Holocene Drilling Figure A-5a
SUE Proposed Ductbank
,lob No 1W9D p
n
C O 4 -0 BORING B-S-D
(Continued)
O U U ry W
20
s 18 ML Gray silt with lenses of organics(medium stiff)
s sP Gray fine sand,trace organics(medium dense to very dense)
11 18 '... r
a 1 ,
26 14 1$ -very dense at 25 to 29 feet
21 18
25
I to F
17 18
2s
30 to F71 -wood debris at 30 feet
C
36 0 18
18
2 ;` Mt_: Light brown peaty silt(soft)
40 G_ _18 Boring completed at a depth of 41 5 feet on January 28, 2014
0 18 A groundwater monitoring well installed. The well consists of a slotted, 2"PVC pipe from
n
depths of 25 to 30 feet,and solid pipe from 25 feet to ground surface. Aflash-mounted
monument installed.
Client: The Boeing Company
Drilling Method: Hollow-Stem Auger by a truck-mount rig
Sampling Method SPT sampler driven by 1404b auto hammer
Drilling Date January 28,2014 Figure A-5b
Drilling Contractor Holocene Drilling
S&EE Proposed Ductbank
Job No 1309D
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I
Technical Information Report— Revision I
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
THIS PAGE INTENTIONALLY LEFT BLANK
� l
Davido Consulting Group,Inc.
TIR_Boeing Renton Site Logistics Project_04-086 Steam Utilidor_Final_Revision I 1
a
a�
U C y O
cU U BORING B-2-2015
o °�
t 5 co Q) n co B-2-2015 (4-86)
n a> O y 3 ct E U
O U_ 0 Z m c c c j Surface condition: Concrete slab
0
C 8 inches thick concrete
sP Brown and gray fine to medium sand with trace fine gravel
24 18
27 14 (very dense)(fill)
21
18 18
28 14
35
5 8 18
8 10
8 SM Gray silty sand
(medium dense to very loose)
1 18
2 14
3
10 o 18 -some brown peat from 10 feet to 13 feet,very soft
0 14
1
1 18
1 18
2
sl= Gray fine to medium sand with trace silt
(medium dense)
15 4 18
s s
7
7 18
10 9
a
20
(Boring log continued on Figure A-2b)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: July 30-31,2015
Drilling Contractor: Holocene Drilling Figure A-2a
S&EE Job No.1507 BoeingPaint Booth PB5/6
o � a
m
a--
BORING B-2-2015
c,
o� (Continued)
O
co
O pZ m Ec c
20
s 18 SP Gray fine to medium sand with trace silt
6 2 (medium dense)
s 18
11 s
13
25 s 18
10 14
12
8 18
10 10
10
30 10 18 -loose below 30 feet
s 12
3
MH Brown silt with trace fine sand and trace peat
(very soft)
1 18
1 4
1
35 0 18 -wood particles at 35 feet
0 12
1
0 18
1 18
1
PT Dark brown peat
„W (very soft)
wv
40 �
(Boring log continued on Figure A-2c)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: July 30-31,2015
Drilling Contractor: Holocene Drilling Figure A-2b
S&EE Job Na.1507 Boeing Paint Booth PB5/6
Uco
BORING B-2-2015
(Continued)
Q) N Q
U co
O ii co
ao
0 18 MH Gray silt with trace fine sand and lenses of brown peat
0 18 (very soft to soft)
1
2 18
2 16
2
45 2 18
1 14
1
vwv PT Brown peat
(very soft)
wv
wv
6 18 sP Gray fine to medium sand with trace coarse sand
8 s (medium dense)
GP Gray fine to medium gravel
(medium dense)
50 12 18
15 9 *:
15
f:
55 7 18
9 14
15 sP Gray fine sand
(medium dense)
60
(Boring log continued on Figure A-2d)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: July 30-31,2015
Drilling Contractor: Holocene Drilling Figure A-2c
S&E Bin Paint Booth PB5/6
Job No.1507 Boeing
a
BORING B-2-2015
U
oZ (Continued)
o
r � � �� a
N O O N O U U co
O� z E�S� co Z)
60
18 ;P Gray fine to medium gravel (medium dense)
9 12 ::�:
SP Gray fine sand with trace silt
(medium dense)
EEFE
65 s io SM Gray silty sand with trace organics
7 (medium dense)
MH Gray fine sandy silt
(very soft)
70 0 18
1 18
1
7$ 61.6 0 18
0 0
0
80
(Boring log continued on Figure A-2e)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-I1b auto hammer
Drilling Date: July 30-31,2015
Drilling Contractor: Holocene Drilling Figure A-2d
S&E Bin Paint Booth PB5/6
Job No.1507 Boeing
a
BORING B-2-2015
(Continued)
co
80
1 18 'MH Gray fine sandy silt
2 14 (soft)
' sM Gray silty fine sand
(loose)
' 85 1 18
z 10
4
' 90 6 4 MH Brownish gray silt
9 (stiff to soft)
95 5 18
' 3 0
1
' l 0 50.8
(Boring log continued on Figure A-2f)
tClient: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: July 30-31,2015
Drilling Contractor: Holocene Drilling
Figure A-2e
S&EE
Job No.1507 BoeingPaint Booth PB5/6
U N �
BORING B-2-2015
: ° (Continued)
N 0 ° � O U U co
° IL C) 0
1 _=
100 5 18 Mt_ Gray silt with some fine sand '
5 14 (stiff)
7
105 '
110 1 1s
2 18 MH Brownish gray silt with trace fine sand
5 (medium stiff)
115
120 '
(Boring log continued on Figure A-2g)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: July 30-31,2015
Drilling Contractor: Holocene Drilling Figure A-2f
S&E Bin Paint Booth PB5/6 '
Job No.1507 Boeing
t BORING B-2-2015
?Q) E
° (Continued)
U co
U
120 3 18 MH Geenish brown silt trace fine sand
a
s s (stiff)
' sM Gray silty sand with little medium sand
(medium dense)
' 125
GP Gray gravel
:.. (very dense)
130 31 18 -
' 36 12 ==oL Gray silt with fine sand and organics few fine gravel and trace coarse sand
39 (hard)
135 —
' 140
(Boring log continued on Figure A-2h)
' Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: July 30-31,2015
Drilling Contractor: Holocene Drilling Figure A-2g
S&EE Job No.1507 Boeing Paint Booth PB5/6
T T BORING B-2-2015
a�
Q
3 -) ° (Continued)
co
N G O N O U: U
U_ m U) Z)
140 30 18 sP Gray fine sand
38 ao 15 (very dense)
sM Gray silty fine sand '
(very dense)
145 '
150 18 40 ,
40 14
40
-wood particles at 151 feet
155
160 '
(Boring log continued on Figure A-2i)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: July 30-31,2015
Drilling Contractor: Holocene Drilling Figure A-2h
SUEBoeingPaint Booth PB5/6 '
Job No.1507
To
U N N
BORING B-2-2015
(Continued)
O p Il � Z)
160 30 11 SP Gray fine sand with little silty sand
33 14 (very dense)
34
165
170 20 1s
27 16
32
MI
i.„■SW Gray fine to coarse sand with many fine to medium gravel
(medium dense to very dense)
175
'.X
:'
f..
7 16
180 47 12 -4:
Boring aborted at a depth of 180 feet on July 31, 2015
due to sloughing gravels causing drill shaft collapse.
Client: The Boeing Company
Drilling Method: Mud rotary advanced by truck-mount drill rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: July 30-31,2015
Drilling Contractor: Holocene Drilling Figure A-2i
S&EE Job No.1501 BoeingPaint Booth PB5/6
APPENDIX B
LATERAL PRESSURES ON SHORING WALLS NEAR RAILROAD
S&EE
SOIL& ENVIRONMENTAL ENGINEERS,INC.
16625 Redmond Way,Suite M 124.Redmond.Washington 98052,www,SoilEnvimnmeMaLoom,425.868.5868
DESIGN MEMORANDUM
AM Aft
G E1VG
To: Mr.Tim Gabelein, PE
Cc: Sergio Echerivel ;
Date: November 23,2015 28ie9
From: C.J.Shin, PhD, PE .c� C.lt 7.3
Re: 4-86 Steam Utilidor,Boeing Renton Plant OxAt, `
Temporary excavations are proposed near BNSF tracks. Attached Plate I shows the plan view and cross-
sections of the proposed excavations. You have indicated that Sections 2 and 8 are most critical in terms of
excavation shoring. Their sectional views are shown in Plates 1 and 2,respectively. Per your request,I
have evaluated the lateral pressures on these critical sections. The results are shown in Plates 3 to 6.
Please note that ductbank construction parallel to the tracks was performed in May,2015. At the closest
location,the edge of the trench excavation was about 10 feet from the edge of the track. The contractor
(Gary Merlino)first excavated a 3-foot deep trench. Then, 15-foot deep steel sheets were driven at both
sides of the trench(using a vibratory hammer). Each sheet was over-lapped about 6 inches along the length
of the excavation. The contractor then excavated the soil inside the steel sheets. As the excavation
progressed,they installed pumped jacks(horizontal bracing)in both horizontal and vertical directions. The
maximum depth of excavation was about 12 feet,including 18 inches of over-excavation for subgrade
stabilization. At the closest location,the edge of the vault excavation was about 8 feet from the edge of the
track. The contractor first excavated a 5-foot deep hole. Then,20-foot deep steel sheets were driven at 4
sides of the hole. A trench box was installed inside the enclosure as bracing,and then the excavation was
performed inside the trench box.The maximum depth of excavation was about 15 feet,including 18 inches
of over-excavation for subgrade stabilization. Groundwater was controlled using well points.
Based on my experience with the ductbank construction,I believe that the proposed excavation for the
steam utilidor can be performed with similar shoring system as long as they are designed to resist the lateral
loads. If trench boxes are used,the gap between the excavation sidewal Is and the trench box should be
filled with CDF or pea gravel the same day of the excavation. I further believe that soldier piles are
unnecessary.
I believe that this memo will serve the current needs. If there is any question,please let me know anytime.
Attachments:
Plate 1:Critical location and Section 2
Plate 2: Section 8
Plate 3:Lateral pressure on shoring wall(1.5:1 excavation or Zone A shoring at Section 2)
Plate 4:Lateral pressure on shoring wall(2:1 excavation or Zone B shoring at Section 2)
Plate 5:Lateral pressure on shoring wall(1.5:1 excavation or Zone A shoring at Section 8)
Plate 6:Lateral pressure on shoring wall(2:1 excavation or Zone B shoring at Section 8)
Technical Information Report— Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29,2016
TfUS PAGE INTENTIONALLY LEFT BLANK
Davido Consulting Group,Inc.
TIR_Boeing Renton Site Logistics Project_04-086 Steam Utilidor_Final_Revision 1
0+00 D+10 0+20 0+30 0+40
C12F C12G30 6 3D
7'-9'
25 25
--_ __ — __ _ _—ate — _ _ _ _— —— — —----_ --- _ 51
--- --
I
I I
20 I I v 20
i II
'4$.
2 Critical
1 12'-63'
Locations
15
10
- 1rjR 0+00 D+10 0+20 0+30 0+40
PSE SPUR TRACK - SECTION 1
SCALE: 1"=5'
r r
-,_ 0+00 0+10 0+20 0+30 0+40
3 30
0
va
7'-9"
] 25 __ n _ r 25
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zolx a sglertc uc
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15. 1 15
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PSE SPUR TRACK - SECTION 2 Critical Locations
SCALE: , -5 and Section 2�
Y 0+00 0+10 0+20 0+30 0+40 0+50 0+60
J --... 30
39_W
Z ` 12'-6'
4 & 7 9.
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PSE SPUR TRACK - SECTION 3
SCALE: 1 =5
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RENTON SITE '°a MD' W3310951
CNIL MASTER RENTON arc"D RTN-YD-05XX-XADWG
0+00 0+10 0+20 0+30 0+40 0+50 0+00 0+10 0+20 0+30 0+40 0+00 0+10 0+20 0+30 0+40
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SCALE: I =5 SCALE: 1 =5 SCALE: 1 =5
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10 -_ -_ - 10 10
s
0+00 0+10 0+20 0+30 0+35 0+00 0+10 0+20 0+30
5 PSE SPUR TRACK — SECTION 5 BNSF MAIN LINE — SECTION 8
SCALE: I =5 SCALE: 1 =5
0+00 0+10 0+20 0+30 0+40 0+00 0+10 0+20 0+30 0+40
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CIS
PSE SPUR TRACK - SECTION 6 BNSF MAIN LINE - SECTION 9
SCALE: 1"=5'
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60% SUBMITTAL
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0+00 0+10 0+20 0+30 0+40
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25 25
i
5. Active Soil Pressure
i
Surcharge-Induced Hydrostatic
ZO 20
� 48"
29 !
____ ___._ -- 15
12'-21YI10 90 H F62
Max. depth of over-excavation (Latera Pressure in psf)
10
10
I p
i
0+00 0+10 0+20 0+30 0+40
PSE SPUR TRAC K -- SECTION 2
SCALE: 1 =5 Plate 3
Lateral Pressures on Shoring Wall
0+00 0+10 0+20 0+30 0+40
30 t6'- d 30
25 a 25
ZONE a 94M uOE C
20 _ -- __� 20
5
i2/0 boy 624,
(Latera Pressure in,psf)
10 —
0+00 0+10 0+20 0+30 0+40
PSE SPUR TRACK -- SECTION 2
SCALE: 1 =5
Plate 4
Lateral Pressures on Shoring Wall
i
0+00 0+10 0+20 0+30
I
30 - 30
7'-90
25 - 25
20
w 20
cv 48
i k
15 - - � + -f-- H
IF15
IL x
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j (Lateral Fressure in psf)
i
10 - ' _ _ _ _ 10
0+00 0+10 0+20 0+30
BNSF MAIN LIN E - SE("NTION 8
SCALE: 1"=5' Plate 5
Lateral Pressures on Shoring Wall
0+00 0+10 0+20 0+30
a o, S'
-- - - -- — — -- - 25
. -
20 ,. 20
I N 48"
•t ._
2'
15 ----� - - - - - 15
4 4 4 41,fw —�
2.40 6a H 62 k, C
(Lateral Pressure in psf)
10 - _ �_.______ _ ________ __ ___ __ __ ___.. 10
i
0+00 0+10 0+20 0+30
BNSI- MAIN LINE - S E�k-1; 8TION
SCALE: 1"=5' Plate 6
Lateral Pressures on Shoring Wall
Technical Information Report — Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
APPENDIX C Drainage Plans
i
Davido Consulting Group,Inc.
TIR_Boeing Renton Site Logistics Project_04-086 Steam Utilidor_Final_Revision I
Technical Information Report—Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
THIS PAGE INTENTIONALLY LEFT BLANK
Davido Consulting Group,Inc.
TIR_Boeing Renton Site Logistics Project_04-086 Steam Utilidor_Final_Revision 1
i
M TCHLI E - 0 0 TI ION SEE SHEET C12G
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t, FFC = t9.5 � COL 3.5-28
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2.0 ) 1 7 IN \ cj
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W SV - 1L36 48 DA STRUCTURE -TYPE 2 �` �--
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WATER FVEI. = 14 59 l7
SUMP - ,59 1 t GENERAL NOTES
- J
(` RIMH 4935 1 J 1,t 1 iF ,R' f `��7 /JG J~ LE> FOR PUMP STATION SEE PLAN&PROFILE
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rr- X1 26`DA LID- r37222 \�-� 1 fl J_'> 1 FW!"Is. SIGN LID j d? a EXISTING PAVEMENT FLOWPATHS MA COLLECTIDN/
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(' r 15 CPP(SW)1E. = 15,W -T1 t, ` {+SOO WATER SUPFv / ,,tt'' C513G S1&C5130 3B FOR DETAILED GRADING
DIP(5);.E 16.25 1 a ,/ G B.5'SECURITY 7.V� = 15. /Sy 1D"
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CPP ISx) 74,59 _ �' L� M 15.67 WIN-YD-C13G-R,FOR REMOVAL PLAN
ORAIH %- ''.STEAM VA L. �� / 15 RC F( .E. = 14.69 { S / 2,15'x 1,80 INNER I) CNSIO R7N-YD-C73G-TESL,FOR TEMPORARY EROSION t
CHANN� uC 4 1 y� WATER L ' id. r203242 SEDIMENT CONTROL PLAN
iZ (NE)E = 9.7719 RIM-YO-CX13G-,?A.FOR UTILIOOR PLAN&PROFILE
,e \ ✓ / + R - _ ♦ PVC(NW)I.E.. = 19.77
n OI `\ t5 5[5 / "'y `ji // MPi /� S ♦/ =2� / 8 TER LEVEL I t6.47 RTN-YO-Ci1IG-2A FOR UTILIDO PLAN&PROFILE
P(SW)LE 19.15
i
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EACH SUMP= 17S2
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P=22.14 SLS� RTN-YD-0513G-X FOR GRADING&PAVING PUN
DOUBLE TURN SEE FIELD BOOK NOTES /�"
/$IS 11 RTN-YO-G X I/i- FOR GRADING 8 PANIC PLAN
'COMM VAULT / ENZpN
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_ R
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1 i + S W, 35'X 35'INNER DIMENSION- W
) GP I CABLES RUNNING(S 'rNO V)
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° IE LD ROOK NOTES r
X �J 8'WROUGHT IRDN 3.5'X 3.5'INNER DIMENSION Q
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I
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WATERER SEE FIELD BO NOTES
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MATCHLINE - FOR CONTINUATION SEE SHEET C14G
0 AO' P:206 523 0024 C29
a� DRAINAGE PLAN 2.29.2016 KEY PLAN
N SCALE: 1 =20 N F_dc52geng Com C30 NOT TO w4E
SCALE IN FEET
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of"�W D THIS DEWN AND/OR D15 0229.2016 DRAINAGE PLAN W3310951 A 02.29.2016
A W-OB8 STEAM UTIDOR W3310951 OCG TG 02.29.T016 �.'�, 0g
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W3310951
4 s�,�"AL CIVIL MASTER RENTON°�ND R7N-YD-CI3G-STS,DWG
MATCHLINE - FOR CONTINUATION SEE SHEET C13F 77
_ _ _ EGEND
_
� s =
A' 4' c INLI (s I E 1 0 �'- r,•T; �, .P LL t,1'
\
PwR
9T A � STEAM VAULT
' DI OLIG to-.
c 5 .Sk m MENSION`
, 5
ti T. \, 7 E LEv �11a.Y U 1�11 !\lT
MP
127 , S
WTR PI E E +1 h.F6 \M PIP E
/�
5T L gat, MENSO .rn + / - .� 6�
4a� WA ER LEVEL 75-77' _ �-' 4. FF'DI _
Su P = 4 V "[ - 189A U�Jt #14677 '�/ SURFACE UiILIDOR
�` AT
t -rr
JD
�Y
0 5 LACK COAT STEEL UTILITY CASING 9.98 1 �•T RIM 189 - #1 1 • -;� ER DIME SIGN
W �$ 2.0 u0 277 V - i-""� �. 1V ` A\ '2 m� " '+� :�A v, q;ar�6 � W - � EXISTING CONTOUR
• Y 1 O N �C NE) E = 16 20
,, 1,,WATER VEL
PROPOSED CONTOUR
, SUMP
��pp,,1 1D
OUN VEGETATED FLOMPATH
/1 C. BANK 1 IM P WATER VAT - J _ , 1
I WATE LE - \ 8' z • A9. �.,.---�'" i-!� IC = 9. 2 ,� - FW" N
L
tK ` ' bl FWf 1 7 � ' wATFP
W TE EYE P = 1
-
GENERAL NOTES
I,�c i:2N ! ti ✓, v ` ,%}'! \+ FW ;p AN / B f IrGP EXISTING PAVEMENT FLOWPATHS AND COLLECTION/
If v SN'k �J WATER AM VLT I \ i-� ���yy"-•'"\Sr.N -�f CONVEYANCE SYSTEM TO BE MAINTAINED.SEE SHEETS
•• J.i-7"' '� LI 40 p */�. .\�LL6�•. C514F-3A C514F-39 k C514F-3C FOR DETAILED
C J/ 279 11 5p _ }
� �- H 4�r; i ti �
CPMaNG
B., SiU HUT % T
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= 12"RCP(S)I,E. 17.71 2.0 k 1.7'I NER DIMENSION ` � > 5%
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WATER = 17.86 f CONSTRUCTION NOTES
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o/c 0 6"a x I �DIA STD 92477 RT3B.FOR GRADING&PAVING PLAN
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y TYPE 2 49474
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SCALE IN FEET SCALE: 1"=20' µw aEger,9 co c3D
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` TO 0229.2016 SHEET r
BDi���• bel,n APPROVED DEFT. DATE TO 0229.2016'° 04-086 STEAM UTILIDOR C16F-STS C36 0'
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0229.2016 RENTON SITE
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Technical Information Report— Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29,2016
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Davido Consuding Group,Inc.
TIR_Boeing Renton Site Logistics Project_04086 Steam Utilidor_Final_Revision I
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Technical Information Report — Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29,2016
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1
1
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1
APPENDIX D Temporary Erosion and Sediment Control Plan
1
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rDavido Consulting Group,Inc.
TIR_Boeing Renton Site Logistics Project_04-086 Steam Utilidor_Final_Revision I
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Technical Information Report—Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
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Davido Consulting Group,Inc. '
T[R_Boeing Renton Site Logistics Project_04-086 Steam Utilidor_Final_Revision 1
MATCH - FOR C NTIN ATI N SEE SHEET C12G
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I i' MNCP DIMFNt��` _ G 1 $ H-irL la-BEi, RIM=253 \ , .'�
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I r fNUENSICN. ( 1 Sty_�SEf IELD DOOK NOTES CONSTRUCTION—
li 1.451 / J( "" ' ENTRANCE i
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AICRNETER BOX
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(W) L- 14.08 a nn �' 2 75'X 1.80'INNER
RN= 9 40 134-62 rl E W4:. _' _ LION.,
OF 1'CALr = 765 23007 1,
2fi DIA uG ( ..:L 1 / 4EWE-CLEANOUT II"CPP(NE - -- 8.83
8"UIP 'ERICA,PILI
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, � j,, ,Y WATER V' OVERHEAD WIRE WATER 18767� is TBpES CL FOR PROJECT
WATER 19 t=- a^` V / UD i 9 /
I UD 929 _�� /t C / , \ 4 40 1 6- ER DI ON ELEVATION=5b 40 S+ db
4.0 x 6.0 INNCR DIMENSION l It 1 / 38'CIA _ 13.
3E'Ou LID- 131220 �-'• s NO I = a.55 EWER
W2*TOA7RF OF DIP o 15.39.RUNS(L-W) 't,.� \ , '� 4W UMP �� �+ LID�p�� * ��� GENERAL NOTES
wA`1R EVE = 1459
SUMP ,.59 t / 14' 1 CONTRACTOR TO DESIGN G
SDMM ea8 /(Ubyy ` M / / GQ PUMA BASED ON PRELIMINARY PLAN PROVIDED BY
a e
1� RIM 19,35 m / �\ � Jt� AND IMPLEMENT DEWATERIN
4 / OEVMTERING CONSULTANT
48 DU 57RLICTURE TYPt 4 1 r/✓� SCWE�R,�rF/yN /
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15'CPP(NE)I E 4 BE x t (^' ) FW! � > 'STOP' /�" OEYMTERINC IS THE ONSUE STORM SYSTEM.
15 CPR(SW)LE 'S°;: �` 1 1+50 WATER SUPPN
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WA ER EJEt 4.n` Q/ / / T \ ETER ih TRAFFIC IF RATED VAULT FOR p N /" /J" J�� 4 EXCAVATED
SOILS ST� RESTRICTED.
BE DISPOSED.AN AN
FUSED
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IT'S x X 1. J CW� 5. EXCAVATED SOILS SHALL BE STORED AT THE APPROVED
U _ T ,t [ D-9 GATE STORAGE FACILITY ONLY AND MUST INCLUDE
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STEEL PIPELE. -231S
235
I
I ' I 116i�° I GENERAL NOTES
1. CONTRACTOR 70 DESIGN AND IMPLEMENT pEIMTERWIG
GP PLAN BASED ON PRELNpNARY PUN PROVIDED D1'
DENAT OF DISCHARGE CONSII FOR
POINT THE
i
STRUCTON
"RI I F'WROUGHT IRON I NT
2. DENATERWG IS THE ONSITE STORM NSYSTEM.
1 6 ICE 3. REFER TO THE EROSION CONTROL NOTES ON C2-IA.
b 9 s I I IALL 4. REUSED ONT$RES M _UST BE 116POSEII OF AT IµNpT
LLJI I APPROVED LOCATION
to
t 5. EXCAVATED SOILS SWILL BE STORED AT THE APPROVED
u / 9 II *� fC I 0-9 GATE STORAGE FACILITY ONLY AND MUST INCLUDE
SECONDARY CONTAINMENT AND STORMWATER TREATMENT
CONTAINMENT METHODS.N TO BE REUSED AS BACKFILL.
W I C z- ��I I AS NECESSARY.MATCH EXISTING STORAGE FACILITY
= I
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Vl I, I � 1 1 CONTESOILS NT AS DESCRIBED INKEPT I7HE£PROJEC�CEEOTMEC�TIYNCAL
W I uD TO U7ILIDOR �. $ 'tA REPORT
(� )- .�_ _ -. , V ^� j: 5. I �INSTALL TEMPORARY CB INLET
N UD IA LID
c,a 1 ""'" PROTECTION TYPE 1 C516-1H
O I (2)512'PIPIES TOP 097 PIPE 23.17 $ 1 I1 / l I CHAINISTING TEMPORAW
Z URLRWGHIZE XPARK.N$T PEIBMETER LINK FENCEH SUMP=21.17 IyI
c 1'( \ �C"o' I I I AT BASE O!FENCE SUCH AS SILT FENCE, C516�1F
- Z W@COMPOST SOCK OR
N. .RB M1h�rfi \\ ~ m I I I 1 ACCORDANCE WRH APPENDIXMD"OF 11 2009
O W I LL7� \ \P �-y KING COUNTY STORMMATER DESIGN MAMA- C516-1F
V EXISTING I. e`J I B N , I I6 I I I�UTILIZE EXISTING CONSTRLX]TIDN ENTRANCE OR
III 1 I INSTALL NEW TEMPORARY STABILIZED
u- B L D G 1 ' 00 1 111�I I I I I I SDMH CONSTRUCTION ENTRANCE C51 -1
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a' 1x 1I / 'OVERFIE��11 W E I (924B 6[..
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TYPE 2-J49247
$ U' LID T LOOR y 2 J "BIKE E t2'CPP(5)LE 21.26
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fi ITOF UNKNOWN MH UNQ OPEN �/ SIGN
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LuN" I 7 CI IYHNAT4 'r )$( = A N SADDER ON UM IT / L .' TYPE 2- 149246 O C15
ECURRY FCNCE j$( - 24'DIP(E)I.C. = 11.37 C16
X I IA Al ( ) C. 2.9 c 24'DP DIP(W)1LE. =680 W C16
'T n� LADDER ON" I= C19
O
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19 48'DA STRUC111i Cgs
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MATCHLINE FOR CONTINUATION SEE
1 - - - - - - _ _ ISSUED FOR CONSTRUCTION G27
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RDN TE
LADDER ON Lake Forest PaTK WA 9815E
` 20' 10' 0 N. 40' SEE SHEET C17F DICIP 206523,0024 C29 KEY PLAN
TESC PLAN 02.29.2016
SCALE IN FEET SCALE: 1 =20 N F 206523,1012 wYw.dOgangr oon C30 NOT To Suu
g SYM REIGN BY AwroRIO IA1E SYM PEV6ON 91 APPAO E5 DUE y w c ACCEPTABILITY DPA 0I.29.2016 04 DATEweTTnE clATnam AXYISINN 5xAE0. pATT
A D4-086 STEAM UTLIDDR W3310951 DOG TG 02.29.2016 �N /Ot W3310951 A 02.29.2016
�`o TH5 0ESIGN AND TO 02.29.2016 TESC PLAN ry
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BOE/A/G' ��Q��g� DEP. DATE TG D229.2D,6 T C16F-TESC C41tp
P - 02 TO 0229MI5 RENTON SITE NO. W331D951 Cow NO,
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L 74 _
(12n)
I1 �\.
alnrTNaHr TAet 1-�//' FILL PPE IX CONCRETE JOINT CONCRETE OR ASPHALT SEE
ON CONCRETE PAVING PUNS AND DETAILS)
I WIDTH VARIES
NIa�I DI111I111W � rF'/ A01AeNX HaXa elrX r ORllEO DOWEL BAR I�B 3 —�{ EX CONCRETE JaNTS PER P°iNT
AYNG PLAIN
wNM+IIId
UTIUDOR 4'SCR.40 STEEL PPE o P
PER PUN PART TRAFFIC YELLOW ,
I 425 SO.
\ �[ ] E PAVING
BASE COURSE SE
FN.FL
l
STEAK PIPE 12[ilTS]50. ., (UNLESS6OTHERWISE PUNS AND DETAILS)
ELEVA7pN PER I WP.NI
6'MN MECHANICAL2'3 E%CAVATION WIDTH NOTE°ON PLANS)[152] OR AS NECESSARY FOR STRUCTURN.FIE.ON6rtE GRANULAR FILL
INSTALLATION OF 2x - SUTAE1L FOR STRUCTURAL FILL ON
=21SeeVaeet erg. III &J NNrE �ANDOF1NCr ELECT BS95.SAND.PITRUURAL FILL OPTIONS
P_______ CONCRETE [216] v[�---4'YIN ROCK.OR GE (150 RIRMIN)CRUSHED
captured eeninu We roll. BASE 30OD P51IC�OTECHNICAL REPORTPSFOR DETAILS
e?e D►YSZURN HEAVY-DUTYSTR11ClUT" UTILIOOR RISE,Usll k LID
PRODUCT NUMBER Z535 THICKNESSES PER PRECAST
AEND VERTICAL 2•MIN
I OR APPROVEp EQUAL MANUFACTURER OR STRUCTURAL
BENDS Sa OVEREXCAVADON VARIES BETWEEN; PLANS IF CAST-IN-PLACE
REQUIRED TO NOR-N-SEAL PPE SLOPE AS 6'M 18'DEPENDNO ON '.:--
3'-5'1�-125—) 1 1
/ --
ACHIEVE I�RT INDICATED ON AIBCRAOE CQNOIiIONS CEOTECH
I/ �I` I ELEVATIONS NOTED KOR-N-SEAL PUNS TO DETERMINE EXTENTS OF SEE STRUCTURAL PLANS .. NATIVE MATERIAL
1 _R•-1C DIA ON PLANS DMDKXCAVAIDN NO SUBORDE FOR UTLOM CONNECTIONPRECAST-(tOO400rrIm1 OIA(4-) PREPARATION.SEE GEOTEOINICAL DETAILS(HELD PLATES) WA FACTURER CONCRETE BE GRANTED
_ _ REPORT FOR DETAILS PRECAST OR APPROVED EQUAL
LIDOR DRAIN
Live Stake .� STORM DRAIN 48„Wx42„D TUNNEL
CROSSING SECTION BOLLARD SCALE:
NOT TO SCALE C513G-2A, C513c-2B,C574F-2B&C5I4F-2C SCALE: HORIZONTAL 1`-5' - VERTICAL 1°-5' C513G-2A,C513G-2B,C516F-2A
' " "1 X1 Stake � TYPICAL CROSS SECTION
odor (25,25mm) SCALE:NOT TO SCALE C516F-2A & C16F-STS SCALE: NOT TO SCALE C513G-2A,C513G-2!LCC514F-3A&C516-IN
`i
NOTE.
1.Saev roll mNel4tioo regoiaa the plecaowK dad ewac ereldag of[he mll in a aeac6,3'-5"(75-125mm)
deep.duA ov coeNw.rwoflvma mt be WovW b rm order or anwnd rofi.
CLFINOUL CASING AND ACCESS LID CONCRETE OR ASPHALT(SEE
TO BE RATED FOR LOADING AS PAVING PLANS AND BETALS)
STRAW WATTLE SPECIFIED STRUCTURAL SSILTEP EX CONCRETE AR WIDTH1 RpE�
SCALE: NOT TO SCALE C14F-TESC, C15F� C16F-TESL FIG PER PLAIN AREA CLEANWT(CO) GRILLED DOWEL BAR\ E%CONCRETE PANT
JOINTS PER PAVING PLAN
STAPLE OR 2,4 DOUGLAS y` l
SIE E OR 5A 2K2x14 C0.WELDED FIR OR EQUAL S _J � ¢a
C
(TYp,) WIRE FABRIC OR EOUIL - ^y43i.-:_. BASE COURSE(SEE PAVING
C516-IC FILTER FABRIC MAT'L - ,,.
PUNS AND DETAILS)
1 j "(UN
WITH
2.14 GAL
0Q /F1 I M.W.FZaOR EQUAL --�) L TH OR3AS%NECESSARY'CAVATION DFOR
I'TO 1-1/2' an INSTALLATION OF STRUCTURAL FLL.ONSITE GRAN"FILL
HASHED GRAVELUiL100RAND
SUITABLEFOR STRUCTURAL FLL ON
OR PEA GRAVEL WATERPROOFlNG SELECT BASIS.STRUCTURAL FILL OPTIONS
NEWLY GRADED OR PIPE MATERIAL CON 1Y D
LADE SILTY SAM.PITRUN,RECYCLE
• a GANGRENE,CRUSHED ROCK OR COT
fe IIA
DISTURBED SIDE a" ," PER PLANS OVEREXCAVATION VARIES BETWEEN ( D
SLOPE ' .// - r 150 PSI MN SEE(GEOlECHWCAL
SLOPE 6'TO 18'DEPENDING ON REPORT FOR DETAILS
I
.GEOTECH
.• �.I � T.r �T,�,�n -. �,f �1 I�'I ,'�l r __ — /_—_ _—_—_—�— SUBGRO DETEOMMANEE EXTENTS
OF UTIIDOR EASEL A LID
OVER CA ION AND
I I I i ___ _ PREPARATION.SEE DE
GEOTECHNICAI ,' ," ". ::. IN T
J— Id(NESSES PRECIS
N REPORT FOR OETAILS MANUFACTURER OR STRUCTURAL
,j �RITIAE SEE SIRUCTINNIL PUNS PLANS F CAST-IN-PLACE
II i II II
I I I AMINE MATERIAL
1 CONNECTION
I I 1 FOR lI1IDOR
I L ��_.__ _- -- ____._. DETAILS(WELD RATES)
LJ LJ e' VERT
e0 EEND OF NODUT�IR�E rr rr IM FACTURE CONCRETE
BEEGGRIW�TEE
2e4 DOUGLAS FIR/ FILTER FABRIC MATERIAL BURY BOTTOM OF FILTER y 63 Wx48 D TUNNEL PRECAST OER APPROVED
EOUAI
DR EQUAL•`'- D.C. LIRMR Ib OR AppppyEp FABRIC RENC MAYL IN 6a1
TRENCH TYPICAL SILT FENCE SECTION 5A TYPICAL CLEANOUT INSTALL TYPICAL CROSS SECTION
SCALE: N07 TO SCALE C2—IA SCALE: NOT TO SCALE C514F-213 SCALE: NOT TO SCALE C514F-2C,C515F-2A`5515F-28 &C516F-2A
SILT FENCE ELEVATION r5-'�
SCALE:NOT TO SCALE C14F-TESC,C15F-TESC&C16F-TESL TRENCH BMWLL MATERIAL
M WSDOT SM.SPEC.9.03.19
g N LOOSE LAYERS OF NOT MORE THAN 10'DEPTH AND
rNOTE uEQULS H LFNOTN COMPER ACTEo 15 a R CD 9WH OF MAXSHOWN
DENSITY
EQUALS HALF OF ad �;- PER ASN D1557 OR CDT WHERE SHOWN ON aMNNcs
UNFIAADED LENGTH WALL TFMCOESS 'E'.. OR AS APPROVED OR DIRECTED BY CONSTRUCTION MANAGER
EQUALS HALF OF STEEL SPLIT SLEEVE CASING
WALL THICKNESS THERE SHALL BE NO EXPOSED GALVANIZED MATERIALS OR ZINC CASING SPACERS s
APPLIED SURFACE TREATMENTS ON ANY EXTERIOR OR UNDERGROUND
COMPACTED LOADING WSDOT STD.SPEC.9-03.12(3)
'e BOLTED FLANGE MATERIALS OR SURFACES(EXCLUDING INTERIORS OF UTILIDORS AND RUBBER GASKET OR CDT AS DIRECTED BY CONSTRUCTION MANAGER
VAULTS).ALL GALVANIZED OR ZINC APPLIED MATERIALS OR COATINGS
SHALL BE PERMANENTLY PAINTED OR COATED TO PREVENT EXPOSURE
E%UTILITY r0 OF THE GALVANIZEDIZINC MATERIALS PRIOR TO INSTALLATION OR STEEL SPLIT SLEEVE CASING
REMAIN N PLACE COMPLETION OF CONSTRUCTION. END SEA
END SEAL = �' PoBK HAUNCHES
UNDER
RIPE HAUNCHES
C516-IF `s
END SEAL BOLT AND
SPACING MANUFACTURER DTll TYPEAER EX UTILITY TO UNUISILA RED NEW PPE DA. TOP OF E OR TOP O
END SEAL FOUNDATION
OR TOP OF
ROIW N PUCE SUBGRAOE 30' NHENR/t D« 12 FOlXDA1lON MATERIAL
BOLT SPACING&TYPE
I,SD H 18'(WNEN D>� 14' WSOOT STANDARD
PER MANUFACTURER RUBBER GASKET 71
� SPEC.9-03.1-03.17 AND 9-OJ.IB
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CASING SPACERS FLANGE FIRE (F) & WATER (CW) LINE $
g CROSS SECTION B sB TYPICAL TRENCH SECTION �_ 3
STEEL SPLIT SLEEVE SCALE. 1'=4'
$A W/SPACERS, C516�-1F SCALE: NOT TO SCALE
C513G-2A C513`13-213 k C516-1G
C516-I F s t.600 ell Way NE 3
—1/ ISSUED FOR CONSTRUCTION Lake Forest Park WA 98155
SPLIT—SLEEVE DETAIL—PLAN VIEW CROSS SECTION A tiA 5 A SCALE: 1�=4 C51�2C SCALE: NOT TO SCALE C516--1F 02.29.2016 P.206523.1012
F:206.523.012
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A 04-086 STEAM URDOR W3310951 DOG TG 02.29.2016 ` � DNS 2 SPECf1CATION 6 APPRD1m 1G 02.29.2016 seA:LT n
M",FZA/Ge a+ fNNI In APPROEDof I DEW.I DA TG 02.291016 mx 04-086 STEAM UTBJDOR C51 6-1 F C47
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CIVIL WESTER RENTON RTN-YD-0516-1F_.DWG
ASPHALT AC PAVEMENT REMOVAL NOTES: NOTES:
LENGTH PER THE OPT) AC PAVEMENT. 1NCH TO
1, AC PAVEMENT SMALL BE SAVED FOR FULL DEPTH OF AC _OSHA _
SLOPES STEEPER THAN,�.;, EXCEPT FOR ROCK)L SORT AS RE(
REVENTS
SIDE DEVELOPMENT RETRIEVAL OURED
fPSI NO
INSPECTOR SYSTE 2. OVERSAMNG OF ADJACENT AC PAVEMENT SHALL BE ACCEPTABLE FOR TO PROTECT EXISTING STRUCTURES.
DRAINAGE GRATE 5 MIN 1.FOR AC PAVEMENT REMOVAL.C515`--1H THE AB50LUIE MNANN DISTANCE REWIRED TO SAN FULL DEPTH
DRAINAGE OF THE EXISTNG AC PAVEMENT TO DE REMOVED. 2. VERTICAL TRENCH WALLS W/SHORING(IF OVER 41 TO CONFORM TO
GRATE FRA1� 7PoM GRATE 7 OSHA REGUAIDIS.
R=25'LAIN, RECTANWIAR 2.FOR CONCRETE REMOVAL
UIATE SHOWN C516-1H 3. THE CONTRACTCR STALL TAKE EXTREME CAUTION TO AVOID ANY
}, SAWCUT FOR EXCAVATION SHALL BE NEAT VERTICAL CUT VINO FINAL.
DAMAGE 10 ADJACENT EXISTING PAVEMENT WHICH 6 TO REMAIN. SMCUT FOR PAVEMENT PATCH SHALL BE WITH SAWCUT MACHINE.
SEDIMENT MO OVERFLOW SAMEIIT EXISTING pANAI',E WHICH OCCURS MAY RESULT IN THE COMPLETE
BYPASS ASPHALT PAVEMENT MEET EXISTING BASE AND REPLACEMENT CF THE DAMAGED PAVEMENT AT THE DISCRETION OF
EBRIIS
PAVEMENT THICKNESS, THE ENGINEER.ALL COSTS ASSOCAIED WITH THE REPAIRS AS A 4. SEE BASF TO BMSG GUIDELINES FOR SHORING AND EXCAVATION IN
BELOW INLET L EXISTING SURFACE COURSE "-• EXCEPT NOT LESS THAN RESULT OF DAMAGE SMALL BE INCURRED BY THE CONTRACTOR AT PROXIMITY TO BASF TRACKS,SEE PROJECT SPECIFIC APPROVED
GRATE DEVICE OVERFLOW'BYPASS TACK COAT FACE OF D SECTIDN NO COST TO THE OWNER. VARIANCES TO BNSF STANDARDS,SHEET C2-IC
(TYP.) CUT AND EACH COARSE 5, SEE GEOTECMNIGAL REPORT FOR SHORING RECOMMENDATIONS.
FIEIERED
C-8'OUARRY SPALLS WATER —_ 1=�
6. SEE STRUCTURAL%INS FOR SHORING DESIGN DE7NL5
1. RIE THE BELOW INLET GRATE DEVICE(BIGD) EXISTING BASE COURSE S506-4D
CEO-iE%TILE FABRIC FOR THE STORM WATER STRUCTURE IT WILL
PROVIDE FULL WIDTH SERVICE. EX671G AGGREGATE BtSE
EXG1.AC PAVEMENT TO BE REMOVED [MST.AC PAVEMENT TO RE"
2. THE BGO SHALL HAVE A BUILT-IN
12'MIN.THICKNESS AREA INGRESS/EGRESS • HIGH-ROW RELIEF SYSTEM(OVERFLOW . H II PAVEMENT PATCH WIDTH VARIES
I I BYPASS). I I '�. i II
NOTE: 3 THE RETRIEVAL SYSTEM MUST ALLOW SAW CUT COMPLETELY 12%
SIABUZED ACCESS SMALL BE USED N ALL AREAS OF THE STE WITH VEHICLE REMOVAL EC THE ABIGDTER WITHOUT SPICING NEW CRUSHED SURFACING THROUGH PAVEMENT SA�UI FOR 12'3
THE COLLECTED WTERNL. EXCAVATION WIDTH VARIES
TRAFFIC AMID PAINED,ACCESS
WILL
KNOW CO SIPS.CIDER MEANS OF ,OP COURSE901 3
PROVIDING STABUZED ACCESS WILL BE CONSIDERED. 4, PERFORM STANDARD
SPECIE N ACCORDANCE SPEC 9-03. 3 P/AIEMEMI PATpf SAWCUT SAWCUT SAWCUT FOR
WITH 305)ARD SPEGFOGTION WSDOT / /// FOR FOR PAVEMENT EXCAVATION
B-0I,}(15). / � "AC'. r EXCAVATION EXCAVATION
STABILIZED CONSTRUCTION CB INLET PROTECTION TYPICAL TIE—IN TO EXISTING
ENTRANCE o TYPE 1 SEC NOTE I
� � PAVEMENT SECTION � ACCREq,E � J � SEE NOTE 2
C16F-TESC 'IDT'D SCALE C13G-TESC, C14F-TESCCC115F-TESC &Ci6F-TESC ALE:1'-4' C516-1H BASE/Rem 4.DI r
MAX MAX
Z3 21
MINIMUM CLASHED SURFACING BASE
COMPACTED ND PG w-22 COURSE Ws°oT SPEC 9-0},9(3) PAVEMENT REMOVAL D,IEIDOR/WIIA,PER
pAPRK C516-1HTACK AND SEAL EDGES A COMPACTED 1p AT LEAST 96,1 OF STRUCTURAL PLAN
MAX DENSITY PER ASTM D1557 NOTE
,�— THERE SHALL BE NO EXPOSED GALVANIZED MATERIALS OR ZINC AC PAVEMENT SECTION TYPICAL TRENCH EXCAVATION
APPLIED SURFACE TREATMENTS ON ANY EXTERIOR OR UNDERGROUND NOT TO SCALE C13G-R, C14F-R, C14G-R, C15F-RE & C16F-R NOT TO SCALE C513G-2A, C513G-2B, C514F-2A 4F-2B
MATERIALS OR SURFACES(EXCLUDING INTERIORS OF UTILIDORS AND C13G-TESC,C14F-TESC,C14G-TESC, C15F-TESC &C16F-TESC C514F-2C, C515F-2A,C515F-2B& 16F-2A
r++ , VAULTS).ALL GALVANIZED OR ZINC APPLIED MATERIALS OR COATINGS
SHALL BE PERMANENTLY PAINTED OR COATED TO PREVENT EXPOSURE DRIFT
OF THE GALVANIZEDIZINC MATERIALS PRIOR TO INSTALLATION OR PIN SUPPORT BEAMS PROTECT PIPE WITH
COMPACTED EXISTING COMPLETION OF CONSTRUCTION. 3' MIN
SUBGRADE PER W/ B"x24'MIN SLEEVE AT EACH CHAIN
i H I T 9 �A36STEEL HOIST. SEE NOTES TYP
CEO EC N CAL RE
PORT AND
H
'
CONSTRUCTION NOTES.
GEO EC LAICAL ENGINEER'
S
_ RECOMMENDATIONS �>,i r� ,� r i CS1`/1 EX PAVEMENT
UNLESS NOTED OTHERWISE.
TEMPORARY PPE SUPPORT CONSTRUCTION NOTES
1jLPORTLAND CEMENT CONCRETE (PCC) o g ' ;��,��,�� ;,�;\;;\> ALL FIRE LINES SHALL W SHUT OCIN WHEN
TYPICAL ASPHALT SECTION PAVEMENT REMOVAL NOTES: FIRE LINES. N CROSSES SHUTDOWN
Is WITHIN WITH
20 FEET a
` x � 5' MAX SHORING.lYP FIRE LINES COORDINATE SHUTDOWII WITH
SCALE:1'=4' C13G, C1417, C14G, C15F, C16F I. ALL EXISTING DOWELS AND DEFORMED BARS SMALL BE SAWED TYP CONSTRUCTION MANAGER AND BOEING FIRE,
OFF AT THE INTERFACE OF THE REMOVAL LIMITS PAVEMENT w EX WATER WIN 2. NOTIFY THE CONSTRUCTION MANAGER OF ESTIMATED
C513G-3A,C513G-3B, C514F-X SMALL BE SAWED FOR FULL DEPTH OF CONCRETE SUB.AC BASE START DATE.CONTRACTOR SMALL NOTIFY THE
C514F-3B,C514F-3C, C515F-SALT AND AC SUB BASE. CONSTRUCTION MANAGER 2 BUSINESS DAYS BEFORE
C515F-3B,C516F-3A&C516-1H 2, OVERSAWNG OF ADJACENT AS WELL AS ANY EXISTING CONCRETE a CONTRACTOTIONR
BEGINS
3. CONTRACTOR SHALT SUBMIT A WATER MAIN SUPPORT
SLABS AW SHALL BE ACCEPTABLE FOR THE ABSOLUTE NW4 DISTANCE PLAN FOR ALL PIPES 4-INCHES MID LARGER
- REWIRED ICI S FULL DEPTH OF THE EXISTING COONCRETE STAB, 4. PROVIDE PROTECTIVE'GAIN SLEEVE'AT EACH
AC BASE AND AC SUBBASE TO BE REMOVED. i ITEMPORARY RESTRAINT < SUPPORT POINT.
400D P51 3. THE CONTRACTOR BALL TAKE EXTREME CAUTON TO AVOID ANY ; EX JOINT OR SLEEVE OR PRESSURE PIPE 5. RECOMMEND USING SALVAGED FIRE HOSE FOR CHI UN
CONCRETE DAMAGE TO ADJACENT EXISTING CONCRETE PANELS WHICH ARE TO AS DIRECTED SLEEVES'
MINIMUM REMAIN(THE EDGES ARE OF PARTICULAR IMPORTANCE.)DAMAGE 6. PROVIDE SUPPORT AT EACH JOINT.VALVE,AND FITTING
DEPTHS a. TIFOR'�NECHDAI°A10EDS MAY PANEL AS ULT IN THE THE DSCRE7aIVPOF COMPLETE REPLACEMENT
ENDNEER ALL j /.\/ \/.\ \�/.\/.\ \� �% (CONE-ALONE)SHALL BE I,Spp LgS.ALL PIPES.MINIMUM CAPACITY OF CHAIN HOISTS
14 M 18'O.0(ROTA PAYS) COSTS ASSOCIATED WITH THE REPAIRS AS A RESULT OF DAMAGE 7. SUPPORT BEAUS AND CHAIN HOISTS ARE TO BE
SMALL BC INCURRED BY THE CONTRACTOR AT NO COST TO THE �/�i j j INSTALLED ALONG THE FULL LENGTH OF THE POPE
OWNER. TRENCH WIDTH WITH SUFFICIENT FORCE APPLIED 10 SUPPORT THE
�' • " • " 4. IN PARTICULAR THE CONTRACTOR SMALL NOT UNDERMINE EXISTING PIPE BEFORE EXCAVATING BELOW THE SPRING LINE.
4! < B. ANY DAMAGE TO PPE OR APPURTENANCES SHALL[#
PROVIDE 2'
C ,< C C YIN PCC PAVEMENT TO REMAIN.
��r COVER �� REPORTED TO THE CONSTRUCTION MANAGER
- TEMP PIPE SUPPORT / TS IMMEDIATELY SO REPAIRS CAN BE MADE.
J - CRUISED SURFACING BASE COURSE PER EXIST.PCC PAVEMENT TO BE REMOVED EXIST,PCC PAVEMENT TO RE MAN 1=� 9. NOTIFY THE CONSTRUCTION MANAGER IMMEDIATELY IF A
WSDOT STD SPEC 9-03.9(3)COMPACTED SCALE: NOT TO SCALE C514F-2A & C516-1G BELL RJ INT.AT ANY WATER MAN,IS EXPOSED
? COMPACTED EXISTING 70 AT LEAST 98%OF VAX DENSITY PER SM CUT COMPLETELY EXIST. PCC JOINT `i
,o SUBGRADE PER ASTM D1557 THROUGH PAVEMENT 'D. BACK�WITH CONNTROL DENSITY FILL STATION SHALL BE
GEOTECHNICAL REPORT AND BOND WRES
GEOTECHIIFCAL ENGINEER'S CONTRACTOR SHALL INSTALL TESTED BY ENGINEERING PERSONNEL TO INSURE
RECOMMENDATIONS ��i�r�X�r�i` r r r`r r `r r ,ry j A DRIFT PIN IN PAVEMENT AT PROPER OPERATION BEFORE BACHFILLWG OF WATER
MAN.
-, ,�\,\`iT`� ••\ T PCC .'_o P PREVENT MOVEMENT.NMO EMENTMTYP 12. FAF SMALL BE DESIGNED TO HAVE MAXIMUM 28-DAr
STRENGTH OF 1DA PSI AND A MAXIMUM 20-DAY
m STRENGTH NOT TO EXCEED 300 PSI,UNIT WEIGHT
P a- EX PAVEMENT 11
TEOP PIPE SILL BE SUPPORT
U KO PLY MDETAI NOT TO BE USED FOR
{ TYPICAL CONCRETE SECTION AGGREGATE Re - CONIC DUCT BANKOROTHER UTILITY CROSSINGS IN
- ..../ EXCESS OF 12"DIAMETER CONTRACTOR TO PROVIDE
G SCALE:1'-4'
C13G, C14F, C14G, C15F & C16F i PIPE SUPPORT DESIGN FOR PIPES OR DUCT BANKS
Y �i EXCEEDING THIS SQE.
C513G-3A, C513G-36, C514F-3A,
C514F-36, C514F-3C, C515F-3A, L►
PAVEMENT GENERAL NOTES:
C515F-3B & C516F-3A PAVEMENT REMOVAL DETAIL DRIFT PIN
a
1. SEE PAVEMENT/GRADING NOTES ON C2-18 FOR PAVEMENT RECONSTRUCTION AND JOINT PCC PAVEMENT REMOVAL SCALE: NOT TO SCALE c516-1H
TREATMENT SPECIFICATIONS NOT TO SCALE C13G-R, C14F-R, C14G-R, C15F-R, & C16F-R
2. SEE SPECIFICATION SECTION 312000 AND GEDTECHNCAL REPORT FOR ADDITIONAL SUBGRADE
PREPARATION REOURE1ENTS C13G TESC, C14F TESC, C14C TESC, C15F TESC&C16F TESC $
YSsu0t 600 III Way NE a
3. DREAMS SKIN ARE MINIMUM COMPACTED DEPTHS.INHERE EXISTING PAVEMENT DEPTHS ARE ISSUED FOR CONSTRUCTION
GREATER THIN SHOWN,MATCH EXISTINGHNI DEPTHS. Lake Forest Park WA 98155
4. CONTRACTOR SHALL FOLLOW CEO7ECHNFIIL REPORT AMID GEO7ECHHCA ENGINEERS FEUD
EXCAVATION EDN WORK ORED O CONCRETE
02.29.2016 P:2D6 523 0024
A
� 5. STEEL EDGES REgARED ON CONCRETE PAVEMENT ADACENT TO UfIDOR REMOVABLE LID DICIG
F'.20&23,1012
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SYM ID6A1 N APPIXIWD DATE SIM 110%XF1 or APPADYED DATEDATE
v w_c ACCEPTABILITY VAS 02292016 sunau cuIrlQHrt nLv�voa s.raoi DArz
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A (A-DBE STEAM UTIIDOR W33,095, OCG IS 022920,E v w+ rHAs DFSCH AHD/oR C516-1 H CT9
BITE//VG aoel'n APPKOIED 10 DEPT. DATE(
iG 0229201E
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V ,PQ„�eF •t6: TG 02292016 RENTON SITE JOB M0' W3310951
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B
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Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29,2016
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Technical Information Report—Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
APPENDIX E Bond Quantity Worksheet
Davido Consulting Group,Inc.
I IR_Boeing Renton Site Logistics Project_04-086 Steam Utilidor_Final_Revision 1
Technical Information Report—Revision 1
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Site Improvement Bond Quantity Worksheet S15 Webdate 02/22/2013
LN King County
Department of Permitting & Environmental Review
35030 SE Douglas Street, Suite 210
Snoqualmie, Washington 98065-9266 For alternate formats, call 206-296-6600.
206-296-6600 TTY Relay 711
Project Name: Boeing Renton Site Logistics Project - 04-086 Steam Utilidor Date: 1/29/2016
Location: 737 Logan Ave N, Renton Project No.:
Activity No.:
Note: All prices include labor, equipment, materials, overhead and
Clearing greater than or equal to 5,000 board feet of timber? profit. Prices are from IRS Means data adjusted for the Seattle area
or from local sources if not included in the IRS Means database.
yes X no
If yes,
Forest Practice Permit Number:
(RCW 76.09)
Page 1 of 9
Unit prices updated: 02/12/02
Version: 11/26/2008
Bond Quantity Worksheet_Version 20081126.xls Report Date: 1/28/2016
Site Improvement Bond Quantity Worksheet S15 Web date: 02/22/2013
Unit #of
Reference# Price Unit Quantity Applications Cost
EROSION/SEDIMENT CONTROL Number
Backfill &compaction-embankment ESC-1 $ 5.62 CY
Check dams, 4" minus rock ESC-2 SWDM 5.4.6.3 $ 67.51 Each
Crushed surfacing 1 1/4"minus ESC-3 WSDOT 9-03.9(3) $ 85.45 CY
Ditching ESC-4 $ 8.08 CY
Excavation-bulk ESC-5 $ 1.50 CY
Fence, silt ESC-6 SWDM 5.4.3.1 $ 1.38 LF 5000 1 6900
Fence, Temporary (NGPE) ESC-7 $ 1.38 LF
Hydroseeding ESC-8 SWDM 5.4.2.4 $ 0.59 SY
Jute Mesh ESC-9 SWDM 5.4.2.2 $ 1.45 SY
Mulch, by hand, straw, 3'' deep ESC-10 SWDM 5.4.2.1 $ 201 SY 5964 1 11988
Mulch, by machine, straw. 2''deep ESCA1 SWDM 5.4.2.1 $ 0,53 SY
Piping, temporary, CPP, 6'' ESC-12 $ 10,70 LF
Piping, temporary, CPP, 8" ESCA3 $ 16.10 LF
Piping, temporary, CPP, 12'' ESC-14 $ 20.70 LF
Plastic covering, 6mm thick, sandbagged ESCA5 SWDM 5.4.2.3 $ 2.30 SY
Rip Rap, machine placed, slopes ESC-16 WSDOT 9-13.1(2) $ 39.08 CY
Rock Construction Entrance, 50'x15'x1' ESC-17 SWDM 5.4.4.1 $ 1,464.34 Each
Rock Construction Entrance, 100'x15'x1' ESC-18 SWDM 5.4.4.1 $ 2,928.68 Each 1 2 5857
Sediment pond riser assembly ESC-19 SWDM 5.4.5.2 $ 1,949.38 Each
Sediment trap, 5' high berm ESC-20 SWDM 5.4.5.1 $ 17.91 LF
Sed.trap,5'high,riprapped spillway berm section ESC-21 SWDM 5A.5.1 $ 68.54 LF
Seeding, by hand ESC-22 SWDM 5.4.2.4 $ 0.51 SY
Sodding, 1''deep, level ground ESC-23 SWDM 5.4.2.5 $ 6.03 SY
Sodding, 1''deep, sloped ground ESC-24 SWDM 5.4.2.5 $ 7.45 SY
TESC Supervisor ESC-25 $ 74.75 HR 8 1 598
Water truck, dust control ESC-26 SWDM 5.4.7 $ 97.75 HR 2 1 196
WRITE-IN-ITEMS **** (see page 91
Temporary Inlet Protection $ 60.00 Each 20 1 1200
Truck Wash $ 6,060.00 9 1 54540
Truck Wash Maintenance $ 20,200.00 1 1 20200
ESC SUBTOTAL: $ 101,47&50
30% CONTINGENCY&MOBILIZATION: $ 30,443.55
ESC TOTAL: $ 131,922.05
COLUMN: A
Page 2 of 9
Unit prices updated: 02/12/02
Version: 11/26/2008
Bond Quantity Worksheet Version 20081126.xls Report Date: 1/28/2016
Site Improvement Bond Quantity Worksheet Web date: 12/02/2008
Existing Future Public Private Quantity Completed
Right-of-Way Right of Way Improvements (Bond Reduction)*
&Drainage Facilities Quant.
Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Complete Cost
GENERAL ITEMS No.
Backfill&Compaction-embankment GI-1 $ 5.62 CY
Backfill&Compaction-trench GI-2 $ 8.53 CY 2211 18,859.83
Clear/Remove Brush,by hand GI-3 $ 0.36 SY
Clearin /Grubbin /Tree Removal GI-4 $ 8,876.16 Acre 2.15 19,083.74
Excavation-bulk GI-5 $ 1.50 CY
Excavation-Trench GI-6 $ 4.06 CY 72751 29,536.50
Fencing,cedar,6'hi h GI-7 $ 18.55 LF
Fencing,chain link,vinyl coated, 6'high GI-8 $ 13.44 LF 312 4,193.28
Fencing,chain link,gate,vinyl coated, 2 GI-9 $ 1,271.81 Each
Fencing,split rail,3'high GI-10 $ 12.12 LF
Fill&compact-common barrow GI-11 $ 22.57 CY
Fill&compact-gravel base GI-12 $ 25.48 CY
Fill&compact-screened topsoil GI-13 $ 37.85 CY
Gabion,12"deep,stone filled mesh GI-14 $ 54.31 SY
Gabion,18"deep,stone filled mesh GI-15 $ 74.85 SY
Gabion,36"deep,stone filled mesh GI-16 $ 132.48 SY
Grading,fine,by hand GI-17 $ 2.02 SY
Grading,fine,with grader GI-18 $ 0.95 SY 50001 4,750.00
Monuments,T Ion GI-19 $ 135.13 Each
Sensitive Areas Sin GI-20 $ 2.88 Each
Sodding,1"deep,sloped ground GI-21 $ 7.46 SY
Surveying,line&grade GI-22 $ 788.26 Da
Surveying,lot location/lines GI-23 $ 1,556.64 Acre
Traffic control crew(2 flaggers) GI-24 $ 85.18 HR
Trail,4"chipped wood GI-25 $ 7.59 SY
Trail,4"crushed cinder GI-26 $ 8.33 SY
Trail,4"top course GI-27 $ 8.19 SY
Wall,retaining,concrete GI-28 $ 44.16 SF
Wall,rockery GI-29 $ 9.49 1 SF
Page 3 of 9 SUBTOTAL 76,423.35
Unit prices updated: 02/12/02
*KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantity Worksheet_Version 20081126.)ds Report Date: 1/28/2016
Site Improvement Bond Quantity Worksheet Web date: 12/02/2008
Existing Future Public Private Bond Reduction*
Right-of-way Right of Way Improvements
&Drainage Facilities Quant.
Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Complete Cost
ROADIMPROVEMENT No.
AC Grinding,4'wide machine<1000s RI-1 $ 28.00 SY
AC Grinding,4'wide machine 1000-200 RI-2 $ 15.00 SY
AC Grinding,4'wide machine>2000s RI-3 $ 7.00 SY
AC Removal/Dis osal/Re air RI-4 $ 67.50 SY
Barricade,type I RI-5 $ 30.03 LF
Barricade,type III Permanent RI-6 $ 45.05 LF
Curb&Gutter,rolled RI-7 $ 17.00 LF
Curb&Gutter,vertical RI-8 $ 12.50 LF 2611 3,262.50
Curb and Gutter,demolition and disposal RI-9 $ 18.00 LF
Curb,extruded asphalt RI-10 $ 5.50 LF
Curb,extruded concrete RI-11 $ 7.00 LF
Sawcut,asphalt,3"depth RI-12 $ 1.85 LF 515 952.75
Sawcut,concrete,per 1"depth RI-13 $ 1.69 LF 10600 17,914.00
Sealant,asphalt RI-14 $ 1.25 LF
Shoulder,AC, see AC road unit price RI-15 $ - SY
Shoulder,gravel,4"thick RI-16 $ 15.00 SY 60 900.00
Sidewalk,4"thick RI-17 $ 35.00 SY
Sidewalk,4"thick,demolition and dis os RI-18 $ 29.50 SY
Sidewalk,5"thick RI-19 $ 38.50 SY
Sidewalk,5"thick,demolition and dispos RI-20 $ 37.50 SY
Sign,handicap RI-21 $ 85.28 Each
Striping,per stall RI-22 $ 5.82 Each
Striping,thermoplastic, for crosswalk RI-23 $ 2.38 SF
Striping,4"reflectorized line RI-24 $ 0.25 LF
Page 4 of 9 SUBTOTAL 23,029.25
Unit prices updated: 02/12/02
*KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantity Worksheet_Version 20081126.x1s Report Date: 1/28/2016
Site Improvement Bond Quantity Worksheet Web date: 12/02/2008
Existing Future Public Private Bond Reduction*
Right-of-way Right of Way Improvements
&Drainage Facilities Quant.
Unit Price I Unit Quant. Cost Quant. Cost Quant. Cost Com fete Cost
ROAD SURFACING (4"Rock=2.5 base&1.5"top course) For'93 KCRS(6.5"Rock=5"base&1.5"top course)
For KCRS'93, additional 2.5"base add RS-1 $ 3.60 SY
AC Overlay,1.5"AC RS-2 $ 11.25 SY
AC Overlay,2"AC RS-3 $ 15.00 SY
AC Road,2",4"rock,First 2500 SY RS-4 $ 21.00 SY
AC Road,2",4"rock,Qty.over 2500SY RS-5 $ 19.00 SY
AC Road,3",4"rock,First 2500 SY RS-6 $ 23.30 SY 7001 16,310.00
AC Road,3",4"rock,Qty.over 2500 SY RS-7 $ 21.00 SY
AC Road,5",First 2500 SY RS-8 $ 27.60 SY
AC Road,5",Qty.Over 2500 SY RS-9 $ 25.00 SY
AC Road,6",First 2500 SY S-1 $ 33.10 SY
AC Road,6",Qty.Over 2500 SY RS-11 $ 30.00 SY
Asphalt Treated Base,4"thick RS-1 $ 20.00 SY
Gravel Road,4"rock,First 2500 SY S-1 $ 15.00 SY
Gravel Road,4"rock,Qty.over 2500 SY RS-1 $ 8.50 1 SY
PCC Road,5",no base,over 2500 SY RS-1 $ 27.00 SY
PCC Road, 6",no base,over 2500 SY RS-1 $ 25.50 SY
Thickened Edge RS-1 $ 8.60 LF
Page 5 of 9 SUBTOTAL 16,310.00
Unit prices updated: 02/12/02
*KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantity Worksheet_Version 20081126.xls Report Date: 1/28/2016
Site Improvement Bond Quantity Worksheet Web date: 12/02/2008
Existing Future Public Private Bond Reduction*
Right-of-way Right of Way Improvements
&Drainage Facilities Quant.
Unit Price Unit I Quant. Cost Quant. I Cost Quant. Cost Complete Cost
DRAINAGE (CPP=Corrugated Plastic Pipe,N12 or Equivalent) For Culvert prices, Average of 4'cover was assumed.Assume perforated PVC is same price as solid pipe.
Access Road,R/D ID-1 $ 21.00 1 SY
Bollards-fixed D-2 $ 240.74 Each
Bollards-removable D-3 $ 452.34 Each
*(CBs include frame and lid
CB Type l D-4 $ 1,257.64 Each
CB Type IL D-5 $ 1,433.59 Each
CB Type II,48"diameter D-6 $ 2,033.57 Each
for additional depth over 4' D-7 $ 436.52 FT
CB Type Il,54"diameter D-8 $ 2,192.54 Each
for additional depth over 4' D-9 $ 486.53 FT
CB Type II,60"diameter D-10 $ 2,351.52 Each
for additional depth over 4' D-11 $ 536.54 FT
CB Type II,72"diameter D-12 $ 3,212.64 Each
for additional depth over 4' D-13 $ 692.21 FT
Through-curb Inlet Framework Add D-14 $ 366.09 Each
Cleanout,PVC,4" D-15 $ 130.55 Each
Cleanout,PVC,6" D-16 $ 174.90 Each
Cleanout,PVC,8" D-17 $ 224.19 Each
Culvert,PVC,4" D-18 $ 8.64 LF
Culvert,PVC,6" D-19 $ 12.60 LF
Culvert,PVC, 8" D-20 $ 13.33 LF
Culvert,PVC, 12" D-21 $ 21.77 LF
Culvert,CMP,8" D-22 $ 17.25 LF
Culvert,CMP, 12" D-23 $ 26.45 LF
Culvert,CMP, 15" D-24 $ 32.73 LF
Culvert,CMP,18" D-25 $ 37.74 LF
Culvert,CMP,24" D-26 $ 53.33 LF
Culvert,CMP,30" D-27 $ 71.45 LF
Culvert,CMP,36" 1 D-28 $ 112.11 LF
Culvert,CMP,48" 1 D-29 $ 140.83 LF
Culvert,CMP,60" 1 D-30 $ 235.45 1 LF
Culvert,CMP,72" 1 D-31 $ 302.58 1 LF
Page 6 of 9 SUBTOTAL
Unit prices updated: 02/12/02
*KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantity Worksheet_Version 20081126.)ds Report Date: 1/28/2016
Site Improvement Bond Quantity Worksheet Web date 12/02/2008
Existing Future Public Private Bond Reduction'
Right-of-way Right of Way Improvements
DRAINAGE CONTINUED &Drainage Facilities Quant.
No. Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Complete Cost
Culvert,Concrete,8" D-32 $ 21.02 LF
Culvert,Concrete,12" D-33 $ 30.05 LF
Culvert,Concrete,15" D-34 $ 37.34 LF
Culvert,Concrete, 18" D-35 $ 44.51 LF
Culvert,Concrete,24" D-36 $ 61.07 LF
Culvert,Concrete,30" D-37 $ 104.18 LF
Culvert,Concrete,36" D-38 $ 137.63 LF
Culvert,Concrete,42" D-39 $ 158.42 LF
Culvert,Concrete,48" D-40 $ 175.94 LF
Culvert,CPP,6" D-41 $ 10.70 LF
Culvert,CPP,8" D-42 $ 16.10 LF
Culvert,CPP, 12" D-43 $ 20.70 LF
Culvert,CPP, 15" D-44 $ 23.00 LF
Culvert,CPP, 18" D-45 $ 27.60 LF
Culvert,CPP,24" D-46 $ 36.80 LF
Culvert,CPP,30" D-47 $ 48.30 LF
Culvert,CPP,36" D-48 $ 55.20 LF
Ditching D-49 $ 8.08 CY
Flow Dispersal Trench (1,436 base+) D-50 $ 25.99 LF
French Drain 3'depth) D-51 $ 22.60 LF
Geotextile,laid in trench,polypropylene D-52 $ 2.40 SY
Infiltration pond testing D-53 $ 74.75 HR
Mid-tank Access Riser,48"dia, 6'deep D-54 $ 1,605.40 Each
Pond Overflow Spillway D-55 $ 14.01 SY
Restrictor/Oil Separator,12" D-56 $ 1,045.19 Each
Restrictor/Oil Separator,15" D-57 $ 1,095.56 Each
Restrictor/Oil Separator,18" D-58 $ 1,146.16 Each
Riprap,placed D-59 $ 39.08 CY
Tank End Reducer 36"diameter D-60 $ 1,000.50 Each
Trash Rack, 12" D-61 $ 211.97 Each
Trash Rack, 15" D-62 $ 237.27 Each
Trash Rack, 18" 1 D-63 $ 268.89 1 Each
Trash Rack,21 1 D-64 $ 306.84 1 Each
Page 7 of 9 SUBTOTAL
Unit prices updated: 02/12/02
'KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantity Worksheet_Version 20081126.xls Report Date: 1/28/2016
Site Improvement Bond Quantity Worksheet Web date: 12/02/2008
Existing Future Public Private Bond Reduction'
Right-of-way Right of Way Improvements
&Drain a a Facilities Quant.
Unit Price Unit Quant. I Price Quant. Cost Quant. Cost complete Cost
PARKING LOT SURFACING
No.
2"AC,2"top course rock&4"borrow PL-1 $ 21.00 SY
2"AC, 1.5" top course&2.5"base cour PL-2 $ 28.00 SY
4"select borrow PL-3 $ 4.55 SY
1.5"top course rock&2.5"base course PL-4 $ 11.41 SY
UTILITY POLES&STREET LIGHTING Utility pole relocation costs must be accompanied by Franchise Utility's Cost Statement
Utility Poles Relocation UP-1 Lump Sum
Street Light Poles w/Luminaires UP-2 Each
WRITE-IN-ITEMS
Such as detention/water quality vaults. No.
AC Pave.Vehicle Rated,12"rock base WI-1 $ 39.50 TN 157 6,201.50
AC Pave.Vehicle Rated,4.5"Asphalt W I-2 $ 96.00 TN 59 5,664.00
Heavy Duty Conc Pavein ,10"Thick WI-3 $ 16.55 SF 8578 141,965.90
12"Rock Base at Conc Paving W I-4 $ 39.50 TN 643 25,398.50
Demo Ex Asphalt Pavement W I-5 $ 3.05 SF 2953 9,006.65
Demo Ex Conc Pavement W I-6 $ 5.05 SF 11697 59,069.85
Demo Ex 6"Conc Curb WI-7 $ 5.20 LF 342 1,778.40
Demo Ex Chain Link Fence W I-8 $ 10.35 LF 198 2,049.30
WI-9
wi-10
SUBTOTAL 251,134.10
SUBTOTAL(SUM ALL PAGES): 366,896.70
30%CONTINGENCY&MOBILIZATION: 110,069.01
GRANDTOTAL: 476,965.72
COLUMN: B C D E
Page 8 of 9
Unit prices updated: 02/12/02
'KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantity Works heet_Version 20081126.x1s Report Date: 1/28/2016
Site Improvement Bond Quantity Worksheet Web date: 12/02/2008
Original bond computations prepared by:
Name: Tim Gabelein, PE Date: 1/29/2016
PE Registration Number: 47652 Tel.#: (206) 523-0024
Firm Name: Davido Consulting Group, Inc.
,address: 15029 Bothell Way NE Suite 600, Lake Forest Park, WA 98155 Project No:
ROAD IMPROVEMENTS&DRAINAGE FACILITIES FINANCIAL GUARANTEE REQUIREMENTS
PERFORMANCE BOND* PUBLIC ROAD&DRAINAGE
AMOUNT BOND*AMOUNT MAINTENANCE/DEFECT BOND*
REQUIRED AT RECORDING OR
Stabilization/Erosion Sediment Control(ESC) (A) $ 131,922.1 TEMPORARY OCCUPANCY***
Existing Right-of-Way Improvements (B) $ -
Future Public Right of Way& Drainage Facilities (C) $ -
Private Improvements (D) $ 476,965.7
Calculated Quantity Completed (E) $ -
Total Right-of Way and/or Site Restoration Bond*/** (A+B) $ 131,922.1
(First$7,500 of bond*shall be cash.)
Performance Bond*Amount (A+B+C+D) = TOTAL (T) $ 608,887.8 T x 0.30 $ 182,666.3 OR
Minimum bond*amount is$2000.
Reduced Performance Bond*Total*** (T-E) $ 608,887.8
Use larger of Tx30/o or(T-E)
(B+C)x
Maintenance/Defect Bond*Total 0.25= $ -
NAME OF PERSON PREPARING BOND*REDUCTION: Date:
*NOTE: The word'bond"as used in this document means a financial guarantee acceptable to King County.
**NOTE: KCC 27A authorizes right of way and site restoration bonds to be combined when both are required.
The restoration requirement shall include the total cost for all TESC as a minimum,not a maximum. In addition,corrective work,both on-and off-site needs to be included.
Quantities shall reflect worse case scenarios not just minimum requirements. For example,if a salmonid stream may be damaged,some estimated costs for restoration
needs to be reflected in this amount. The 30%contingency and mobilization costs are computed in this quantity.
***NOTE: Per KCC 27A,total bond amounts remaining after reduction shall not be less than 30%of the original amount(T)or as revised by major design changes.
REQUIRED BOND*AMOUNTS ARE SUBJECT TO REVIEW AND MODIFICATION BY DDES
Page 9 of 9 Unit prices updated: 02/12/02
Check out the DDES Web site at www.kingcounty.gov/permits Version: 11/26/08
Bond Quantity Worksheet_Version 20081126.xls Report Date: 1/28/2016
Technical Information Report—Revision I
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
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Technical Information Report — Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
APPENDIX F Stormwater Facility Summary Sheet
Davido Consulting Group,Inc.
TIR_Boeing Renton Site Logistics Project_04-086 Steam Utilidor_Final_Revision 1
Technical Information Report—Revision 1
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KING COUNTY, WASHINGTON, SURFACE, WATER DESIGN MANUAL
STORMWATER FACILITY SUMMARY SHEET DDES Permit
Number
(provide one Stormwater Facility Summary Sheet per Natural Discharge Location)
The project is exempt from flow control requirements per the Direct
Overview: Discharge Exemption
Project Name
Boeing Renton Site Logistics Project- 04-086 Steam Utilidor Date January 29, 2016
Downstream Drainage Basins
Major Basin Name Cedar River
Immediate Basin Name Basin 27
Flow Control: None
Flow Control Facility Name/Number
Facility
Location
If none,
Flow control provided in regional/shared facility(give
location)
No flow control required X Exemption number
Direct Discharge Exemption
General Facility Information:
Type/Number of detention facilities: Type/Number of infiltration facilities:
ponds ponds
vaults tanks
tanks trenches
Control Structure Location
Type of Control Structure Number of Orifices/Restrictions
Size of Orifice/Restriction: No. l
No. 2
No. 3
No. 4
Flow Control Performance Standard
_. 2009 Surface Water Design Manual 1/9/2009
1
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
Live Storage Volume Depth Volume Factor of Safety
Number of Acres Served
Number of Lots
Dam Safety Regulations(Washington State Department of Ecology)
Reservoir Volume above natural grade N/A
Depth of Reservoir above natural grade N/A
Facility Summary Sheet Sketch
All detention, infiltration and water quality facilities must include a detailed sketch.
(11"x 17" reduced size plan sheets maybe used) N/A
2009 Surface Water Design Manual 1/9/2009
2
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
Water Quality: The project is exempt from water quality requirements as the project is adding
less than 5,000 SF of new plus replaced pullution generating impervious surface
1
Type/Number of water quality facilities/BMPs:
biofiltration Swale sand filter(basic or large)
(regular/wet/or continuous inflow) sand filter, linear(basic or
large)
combined detention/wetpond sand filter vault(basic or
targc)
(wetpond portion basic or large) sand bed depth (inches)
combined detention/wetvault stormwater wetland
filter strip storm filter
X flow dispersion wetpond (basic or large)
Basic dispersion via sheet flow
farm management plan wetvault
landscape management plan Is facility Lined?
oil/water separator If so,what marker is used
above
(baffle or coalescing plate)
Liner?
catch basin inserts:
Manufacturer
pre-settling pond
pre-settling structure:
Manufacturer
high flow bypass structure(e.g., flow-splitter catch basin)
source controls
Design Information
Water Quality design flow
Water Quality treated volume(sandfilter)
Water Quality storage volume(wetpool)
Facility Summary Sheet Sketch
2009 Surface Water Design Manual 1/9/2009
3
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
All detention, infiltration and water quality facilities must include a detailed sketch.
(11"x17" reduced size plan sheets may be used) N/A
2009 Surface Water Design Manual 1/9/2009
4
Technical Information Report—Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
APPENDIX G KCRTS Modeling Results
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Boeing Renton Site Logistics Project — 04-086 Steam Utilidor
KCRTS Screenshot—Additional Flow to Drainage Basin 25
ro uct— o o Time ries -
Project Location . Sea-Tac
Computing Series Basin 25 Additional Flow.tsf
ional Scale Factor 1.00 - �KC RTS Analysis Took Data Type Reduced -- J
resting IS-minute Time Series File Compute PEAKS and Flow Frequencies ?�
Loading Time Series File:C:\KC-SWDM\KC-DATA\STEI1SR.rnf 8 --
Impervious 0.06 acres Scaling Yr: 8 RotFIowFREOUENCIES
Total Area : 0.06 acres
Peak Discharge: 0.07S CFS at 6:30 on Jan 9 in Year 8 Compute Flow DURATION and Exceedence
Storing Time Series File:Basin 25 Additional Flow.tsf 8
Rot Probability E7(CEEDENCE Curves
--- Time Series Computed
---- ----------------------_ COMPARE Flow Durations
KCRTS Command
Enter the Analysis TOOLS Module Extract a HYDROGRAPH
--------------------------
----------------------------------------------------------------- Rot a Hydro(Q,RARt
Analysis Tools Command Compute VOLUME Discharge
Compute PEAKS and Flow Frequencies
--------------------------
Loading Stage/Discharge curve:basin 25 additional flov.tsf BETURN to Previous Menu J
Flow Frequency Analysis
Compute a flow Frequency Curve
-------------- ----
T... Series File:basin 25 additional flov.tsf _-
Project Location:Sea-Tac
Frequencies & Peaks saved to File:Basin 25 Additional Flov.pks
W77-
rolect ocatlon: a- ac — --_.._- _..___. ___- ----------------
---Annual Peak Flow Rates--- --Flow Frequency Analysis------
FlowRate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.030 6 8/27/01 18:00 0.07S 1 100.00 0.990
0.021 8 9/17/02 17:45 10.0S8 2 25.00 0.960
0.058 2 12/08/02 17:15 0.041 3 10.00 0.900
0.024 7 8/23/04 14:30 0.034 4 5.00 0.800
0.032 5 10/28/04 16:00 0.032 5 3.00 0.667
0.034 4 10/27/05 10:45 0.030 6 2.00 0.500
0.041 3 10/25/06 22:45 0.024 7 1.30 0.231
0.075 1 1/09/08 6.30 0.021 8 1.10 0.091
puted Peaks 0.069 50.00 0.980
i
Boeing Renton Site Logistics Project — 04-086 Steam Utilidor
(Peak flow results from KCRTS for additional flow to Drainage Basin 25)
Flow Frequency Analysis
Time Series File:basin 25 additional flow.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis------
FlowRate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.030 6 8/27/01 18:00 0.075 1 100.00
0. 990
0.021 8 9/17/02 17:45 0.058 2 25.00
0. 960
0.058 2 12/08/02 17:15 0.041 3 10. 00
0. 900
0.024 7 8/23/04 14:30 0.034 4 5.00
0.800
0.032 5 10/28/04 16:00 0.032 5 3.00
0.667
0.034 4 10/27/05 10: 45 0.030 6 2.00
0.500
0.041 3 10/25/06 22:45 0.024 7 1. 30
0.231
0.075 1 1/09/08 6:30 0. 021 8 1. 10
0.091
Computed Peaks 0. 069 50. 00
0. 980
Technical Information Report—Revision I
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
APPENDIX H Site Logistics TIR
*Calculations and water quality information associated with Appendix B of the Site Logistics
TIR is not included in this report as the information does not pertain to the 04-086 Steam
Utilidor Project.
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BergerABAM Building Permit Submittal (Revised)
Technical Information Report
X`
i,'f1
j 7A #
04-68 Yards and Grounds, Southwest Marshaling Yard
Renton Site, Building 04-051
Project No.W1829787
Submitted to
The Boeing Company
Renton,Washington
A13.0362,03 3 March 2014
Technical Information Report '
Boeing Commercial Airplanes ,
Renton Site Logistics Project - SW Marshaling Yard
Renton, Washington '
Submitted to
The Boeing Company
800 North Sixth Street '
Renton, Washington 98055
3 March 2014
Prepared by:
BergerABAM
33301 Ninth Avenue South,Suite 300
Federal Way,Washington 98003-2600
Job No.A13.0362.03
TECHNICAL INFORMATION REPORT
Renton Site Logistics Project — SW Marshaling Yard
Renton, Washington
TABLE OF CONTENTS
SECTION PAGE
PROJECT ENGINEER'S CERTIFICATE....................................................................................................1
Section 1: Project Overview..................................................................................................................2
Boeing Renton Site Overall Existing Conditions....................................................................................3
ProposedConditions.............................................................................................................................3
SoilsConditions.....................................................................................................................................4
Section 1.1: Project Tasks Overview....................................................................................................5
1.1.1a SW Marshaling Yard...................................................................................................................5
1.1.1b Truck Inspection.........................................................................................................................7
1.1.2 Task 2- Parts Movement Road Improvement...........................................................................10
1.1.3 Task 3-Gate D-35 and Badge Office Relocation and Perimeter Fence Relocation...................12
1.1.4 Task 4-Spine Road, Parking Improvements and Perimeter Fence Relocation.........................15
1.1.5 Task 5- Lot 1 Marshaling Yard...................................................................................................17
1.1.6 Task 6—Duct Banks....................................................................................................................19
1.1.7a Task 7a-Air Compressor Building............................................................................................19
1.1.7b Task 7b-Existing Truck Inspection Reconfiguration ...............................................................21
Section 2: Conditions and Requirements Summary........................................................................21
Requirements Summary:Stormwater Management Guidelines......................................................22
Core Requirement 1- Discharge at the Natural Location...................................................................22
Core Requirement 2-Off-site Analysis...............................................................................................22
Core Requirement 3- Flow Control....................................................................................................22
Core Requirement 4-Conveyance System.........................................................................................22
Core Requirement 5- Erosion and Sediment Control ........................................................................22
Core Requirement 6- Maintenance and Operations .........................................................................22
Core Requirement 7- Financial Guarantees and Liability ..................................................................23
Core Requirement 8-Water Quality..................................................................................................23
Technical Information Report BergerABAM,A13.0362.03
Renton Site Logistics Project—SW Marshaling Yard March 3,2014
Renton,Washington Page ii of iii
Special Requirement 1-Other Adopted Area-Specific Requirements...............................................23
Special Requirement 2- Flood Hazard Delineation............................................................................23
Special Requirement 3- Flood Protection Facilities...........................................................................23
Special Requirement 4-Source Control.............................................................................................23
Special Requirement 5-Oil Control....................................................................................................24
Special Requirement#6—Aquifer protection Area............................................................................24
Section3: Off-site Analysis................................................................................................................24
3.0 Nishiwaki Lane Trunkline—Outfall 021.........................................................................................24
3.1 Basin 31-Outfall 021.....................................................................................................................26
3.2 Basin 32—Outfall 021...................................................................................................................30
3.3 Basin 34—Outfall 021...................................................................................................................34
3.4 Basin 21—Outfall 001...................................................................................................................37
3.5 Basin 25—Outfall 002...................................................................................................................38
3.6 Basin 27—Outfall 004...................................................................................................................40
Section 4: Flow Control and Water Quality Facility Analysis and Design.......................................44
4.1 Water Quality Treatment..............................................................................................................44
4.2 Water Quantity Detention............................................................................................................45
Section 5: Conveyance System Analysis and Design.......................................................................45
Section 6:Special Reports and Studies............................................................................................45
Section7: Other Permits....................................................................................................................46
Section8: Not Used ...........................................................................................................................46
Section 9: Construction SWPPP Analysis and Design .....................................................................46
Section 10: Bond Quantities, Facility Summaries,and Declaration of Covenant..........................46
Section 11: Operations and Maintenance Manual ..........................................................................46
LIST OF APPENDICES
Appendix A Site Maps
Appendix B Drainage Maps and Calculations(under separate cover)
Appendix C City of Renton Maps
Appendix D Flood Zone Maps
Appendix E Geotechnical Report
Appendix F Stormwater Pollution Prevention Plan (under separate cover)
Appendix G Forms
Appendix H Maintenance Manual
Appendix I Water Quality General Use Level Designations
Technical Information Report BergerABAM,A13.0362.03
Renton Site Logistics Project—SW Marshaling Yard March 3,2014
Renton,Washington Page iii of iii
TECHNICAL INFORMATION REPORT
RENTON SITE LOGISTICS PROJECT - SW MARSHALING YARD
RENTON, WASHINGTON
PROJECT ENGINEER'S CERTIFICATE
I hereby certify that this Technical Information Report for the Renton Site Logistics Project—
SW Marshaling Yard has been prepared by me or under my direct supervision and meets
minimum standards of care and expertise,which is usual and customary in this community for
professional engineers.I understand that the City of Renton does not and will not assume
liability for the sufficiency,suitability, or performance of drainage facilities designed by me.
Reviewed by
Connie Linden,PE
Project Manager
�lE E.L
O� OF WASH
4 3 y -
SSA AL
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 1 of 47
i
I
SECTION 1: PROJECT OVERVIEW
The proposed project is located at The Boeing Commercial Airplane 737 Airplane Production
Renton Plant located on the southern shore of Lake Washington,within the City limits of the
City of Renton,Washington.The facility is bordered by the Cedar River to the west and Logan
Ave to the east.The City of Renton Stadium is located directly south of the Boeing Renton
Production Plant.Surrounding land use is predominantly commercial,industrial, and retail.
The City of Renton Municipal Airport is located adjacent to the project site on the western bank
of the Cedar River.The Landing,a mixed-use development, and an outdoor storage yard are
located just west of the site.A site vicinity map is provided in Appendix A.
The Renton Site Logistics Project encompasses modifications to site layout,materials movement
and infrastructure improvements necessary for increased production of the 737 aircraft and
planned future growth of the Boeing Renton Facilities.
The project objectives include
• Optimizing efficiency by improving material management flow;
• Reducing congestion by revising and repurposing site layout and minimizing the number of
personnel vehicles within the secured perimeter area;and
• Improving site safety by providing better separation of parts,equipment,and people.
The project will be sequenced to maintain operations during all phases of construction and to
minimize impacts to the movement of people,parts, and equipment. The project consists of
seven tasks.
Task 1: Southwest Marshaling Yard and Truck Inspection
Task 2: Parts Movement Road Improvement
Task 3:Gate D-35 and Badge Office Relocation and Perimeter Fence Relocation(portion)
Task 4:Spine Road,Parking Improvements and Perimeter Fence Relocation(portion)
Task 5:Lot 1 Marshaling Yard j
Task 6: Duct Banks
Task 7: Air Compressor Building and Existing Truck Inspection Reconfiguration
These improvements will affect that portion of the site which lies north of N. 61h Street and
south of Lake Washington.The western limit of the proposed improvements will be the 200-
foot shoreline setback of the Cedar River and the eastern extent of the proposed improvements
will be Logan Ave. These limits define the "project site" as addressed in this TIR. See the Project
Site and Task Identification Maps provided in Appendix A.
It is the intent of this Technical Information Report to address the site improvements of each
individual project task and the applicable conditions and requirements as they pertain to each
task as well as to address hydrologic impacts to the entire project site as a whole. All project
tasks are covered by this TIR;however,this TIR will be updated as the design of each of the
project tasks is furthered and submitted for building/construction permits. This TIR is being
submitted with the Building Permit submittal for Task 1a: Southwest Marshaling Yard,Task 1b:
Truck Inspection and Task 3: Gate D-35 and Badge Office Relocation.
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 2 of 47
Boeing Renton Site Overall Existing Conditions
The topography of the entire project site is relatively flat, with slopes generally ranging from
less than 1 to approximately 2 percent.The Boeing Renton Production Plant is predominantly
covered by production facilities and supporting interior roadways and parking areas.Less than
1-percent of the surface cover is pervious in the existing site condition. Runoff from the project
- site is collected by closed(pipe)conveyance systems which outfall either directly or indirectly to
Lake Washington.Due to the flat topography of the site and surrounding area,the storm
drainage outfalls are partially or fully submerged at all times.
The Boeing Commercial Airplane 737 Airplane Production Renton Plant operates 24-hours a
day,365-days of the year.The industrial activities which occur at the project site require the
Boeing Renton facilities to participate in a statewide Industrial Stormwater General Permit
(ISWGP) and maintain a Stormwater Pollution Prevention Plan (SWPPP)meeting the
requirements of the Washington State Department of Ecology.
The storm drainage systems at the Boeing Renton Facilities are divided into over 25 basins for
reference in the above mentioned SWPPP. The closed conveyance system has 21 separate
outfalls which, directly or indirectly, drain north to Lake Washington.The Drainage Basin and
Outfall definitions and naming conventions used in this Report will follow the existing SWPPP
conventions for continuity. A total of six Basins(21,25,27,31,32, and 34) and four Outfalls
(John's Creek-001,002, 004, and 021)will be affected by the proposed improvements.Each of
these drainage elements will be discussed further in Section 3,Offsite Analysis.
Proposed Conditions
Surface cover,topography and hydrology at the project site will be essentially unchanged by
the proposed improvements.The proposed improvements will affect vehicular and pedestrian
traffic patterns, changes to materials handling(delivery routes and temporary storage
locations),and infrastructure improvements to upgrade outdated and insufficient facility
support systems.Table 1.0 below summarizes existing and proposed surface coverage for the
overall project site.
Technical Information Report BergerABAM,A13.0362203
Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 3 of 47
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,� I
TABLE 1.0-Site Surface Cover
Surface Cover Existing Developed
Condition Condition
1
46.199 acres
Total Site Area
(2,012,421 sfl
Pervious(Landscape) 2.941 acres 3.536 acres -
(128,094s (154,046 s
Impervious(Pavement,buildings,etc.) 43.258 acres 42.662 acres
(1,884,327 s (1,858,375 s
Total New Impervious Area 1.873 acres
(81,630 s
Total New Pollution-Generating Impervious
1.154 acres
(50,277 s
6.871 acres
Total Replaced Impervious Area (299,324 sf)
Total Replaced Pollution-Generating Impervious 6.146 acres
(267,733 s
The existing conditions and improvements proposed by each task are described in Section 1.1,
Project Tasks Overview.
Soils Conditions
The City of Renton Stormwater Management Design Manual (2009)Amendment,Reference 11C,
shows site soils as Urban Land.A copy of the aforementioned soils map is provided in
Appendix C of this report. Urban land is generally soil that has been significantly modified by
urbanization and disturbance of the natural soil layers.The probable erosion hazard is slight to
moderate.
A memo addressing Geotechnical Considerations for the Boeing Renton Logistics Site prepared
by Soil&Environmental Engineers,Inc. is included as Appendix E of this Report.This memo
summarizes the site history, general sub-surface,soils, and groundwater conditions at the site,
and anticipated design and construction considerations.Project task specific site soils
investigations will be performed prior to final design and a geotechnical soils investigation for
each task will be included as a part of the final TIR. This TIR includes the final geotechnical
soils reports for the Southwest Marshaling Yard of Task 1 and a portion of the duct bank work,
located south of Building 04-81.
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 4 of 47
Section 1.1: Project Tasks Overview
- 1.1.1a SW Marshaling Yard
This task includes improvements for the proposed Southwest(SW)Marshaling Yard,located at
the existing parking Lot 16 north of Building 04-68,south of Building 04-21,and east of
Nishiwaki Lane.The yard will receive semi-truck vehicles from the proposed Truck Inspection
Area to the south, and will serve as an offloading and temporary storage area for materials and
equipment prior to distribution within the facility.
Existing Conditions
The site currently serves as a privately owned vehicle(POV)parking lot.A number of existing
utilities are located within the proposed yard,including a sanitary sewer pump station(4A-07),
an oil/water separator for stormwater(OWS-043),and a manually actuated sluice gate(Vault
No.591)that can isolate the on-site stormwater conveyance system,in the event of an accidental
spill.Other utilities present within the site include yard lighting,underground power, storm
drains,sanitary sewer, potable water, compressed air, and fire water. Fire hydrants are located
on the east and south perimeter of the site.A covered pedestrian canopy extends along the east
side of the existing POV parking lot. A fueling station is located in the northeastern corner of
the yard site;however,no work will take place within the fueling station area. This fueling
station is outside the work limits.
Stormwater runoff within the site is managed with a system of catch basins located throughout
the parking area.The entire site sits within stormwater drainage Basin 32.Basin 32 ultimately
drains to Lake Washington.Drainage from the site is directed through an oil/water separator
(OWS-043) and passes through the above mentioned sluice gate (No.591)prior to being
conveyed to a storm trunk line in Nishiwaki Lane.This trunk line ranges in diameter from a 30-
inch-diameter pipe near Apron D located south of 61h Ave, and increases in size as the trunk
routes to the north through 42-,48-, and 54-inch lines,before finally discharging to Lake
Washington at Outfall 021 via a 60-inch pipe.All existing surfaces within the project site are
impervious and considered to be pollution generating.A summary area table is provided
below.
Proposed Improvements
The proposed improvements will be limited to that necessary for converting the existing POV
- parking lot into a truck marshaling yard, along with minor repair and overlay work to existing
pavement in the northern portion of the site.An existing propane tank will also be relocated in
the northern portion of the site under separate permit. Major improvements will include
construction of a new office building, storage canopy,truck ramp,utility relocation,utility
service to the new building and canopy,signage,and pavement reconstruction and restriping.
A portion of the existing stormwater collection and conveyance system located centrally within
the proposed SW Marshaling Yard site is undersized and contains pipe segments with negative
slopes. These conditions create nuisance flooding problems upstream and adjacent to the new
SW Marshaling Yard site.This existing 10-inch conveyance pipe that lies at a negative slope will
be replaced with 12-inch and 18-inch HDPE and ductile iron pipe. This new 12-and 18-inch
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 5 of 47
storm conveyance system will accommodate the new buildings, discussed below,roof drains.A
further discussion of conveyance system improvements can be found in Section 5 of this report.
In addition to the project task improvements above, a water quality treatment facility will also
be constructed within the limits of the SW Marshaling Yard project Task.The stormwater
treatment facility will provide water quality treatment for the entire Basin 32 area as a treatment
trade for the target surface areas created by the entire project.The system will consist of a flow
splitter,pre-treatment system,a filter vault, and stormwater pump. A further discussion of the
Water Quality Treatment requirements for the entire project site and the proposed stormwater
treatment system can be found in Section 2,Conditions and Requirements Summary,and in
Section 4,Flow Control and Water Quality Facility Analysis and Design.
Buildings
The building components of the project include the construction of a steel canopy and adjacent
office building.The steel canopy,approximately measuring 102 feet by 102 feet,will have a
minimum clearance height of 18 feet within the canopy.The canopy will be enclosed with
siding on the south and west sides. The one-story office building,measuring approximately 22
feet wide by 84 feet long,will provide space for a material handling dispatch office,break area,
restroom,kitchenette, and electrical/communication closet.
Paving Replacement
The existing POV parking area asphalt concrete pavement(ACP)will be demolished and
replaced with a heavy-duty ACP section suitable for truck traffic and material and equipment
storage. Pavement repair will take place along the northern drive aisle and at the location of the
existing propane tank,which is above ground,which will be relocated (relocation under
separate permit).
Utility Improvements
New potable water,building fire service line,sanitary sewer,power, and communication lines
will be extended to the new office building. Compressed air lines will be extended to the new
truck canopy.A new duct bank will be constructed in the drive located along the east side of the
project, and continue north to connect to Building 04-21 near the southwest comer of the
building. Existing utilities will be protected and preserved to the extent possible, aside from
underground power to yard light,which will be relocated with the yard lights.
Stormwater Improvements
In general, stormwater runoff patterns from the new site will mimic existing.All surface runoff
from within the improved site will drain to catch basins within the Project Task area.An
existing 10-inch conveyance pipe,which is centrally located within the SW Marshaling Yard site
and is laid at a negative slope,will be replaced with a new 12-and 18-inch line. The new
building roof drain system will be connected to this new 12-inch line. Some minor changes to
flow paths may occur, due to re-grading of the replacement pavement.This may alter flow rates
within individual catchment areas. Existing and proposed surface coverage areas are
summarized in the table below:
Technical Information Report BergerABAM,A13.0362203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 6 of 47
Table 1.1.1a SW Marshaling Yard Surface Cover
Surface Cover Existing Developed
Condition Condition
2.035 acres
Total Site Area (88,659 sfl
Pervious(Landscape) 0.013 acres 0.004 acres
(554 sf) (177 sj)_
Impervious(Pavement, buildings,etc.) 2.02 acres 2.031 acres
(88,015 s) (88,482 s
New Impervious 0.301 acres
(13,132 s
New Pollution-Generating Impervious 0.016 acres
(712 s
Replaced Impervious 1.695 acres
(73,851 sfi
Replaced Pollution-Generating Impervious 1.410 acres
(61,426 sfi
Stormwater Facilities
A water quality treatment facility will be constructed within the limits of the SW Marshaling
Yard Project Task Area.This stormwater treatment facility will provide water quality treatment
for the entire Basin 32 area,which totals 10.536 acres, as a treatment trade for the target surface
areas created by the entire project.A further discussion of the Water Quality Treatment
requirements for the entire project site and the proposed stormwater treatment system can be
found in Section 2, Conditions and Requirements Summary,and in Section 4,Flow Control and
Water Quality Facility Analysis and Design.
1.1.1b Truck Inspection
The Truck Inspection Relocation project will relocate the existing truck inspection area from
Park and Logan Avenues to a new location in the southwestern portion of the site with access
from North 6th Street. The relocated truck inspection area will be located in the southwestern
parking lot area on the Renton site, to the east of Gate D-30 at Nishiwaki Lane, and south of
- Building 04-68. This new site will accommodate additional vehicles,and is sited to provide
more direct access to the proposed SW Marshaling Yard,located to the north of Gate D-30 and
the Building 04-68.Once completed,delivery semi-trucks will enter the new truck inspection
area from westbound North 61h Street, and exit the inspection area south of the D-30 gate at
Nishiwaki Lane and the flight line access road. The majority of truck traffic will continue
northbound along the flight line access road to the new SW Marshaling Yard.The existing
security fence will be relocated to the north and east sides of the site so the relocated inspection
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 7 of 47
area remains outside the secure perimeter.The existing truck inspection area will be
demolished and the site repurposed as a new vehicle parking area as a part of Task 7.
Existing Conditions
The proposed site will occupy the southwestern corner of a POV parking lot. Approximately
two-thirds of the site is paved. There are small interior landscaped islands and a larger
landscape island in the southwestern comer of the site. There is a 30-foot-wide landscaped strip
on the south side of the project area,bordering the north side of the North 61h Street right-of-
way.The southern area of the site is used for temporary storage and trailer parking. Existing
utilities within the site include storm,sanitary,fire water, potable water, communication,
underground power, and compressed air lines.Most of these utilities are concentrated within a
20-foot-wide corridor running east to west along the north edge of the landscaped strip.Most of
the existing site lies within the secured area behind the security fence on the west and south
sides.
Proposed Improvements
The proposed improvements include construction of a single-truck inspection bay,truck staging
area,inspection bay canopy,office building,utilities,landscaping,and pavement striping and
signage.Each element is described in detail below. A portion of the asphalt paved surface will
be demolished in the southwestern comer and converted from asphalt to landscaped areas. The
building and canopy will be located outside and to the east of the 200-foot Cedar River setback.
Buildings
The building component of the project includes the construction of a truck inspection canopy
and inspection office.The steel truck inspection canopy,measuring approximately 32 feet wide
by 80 feet long,will provide protection for vehicles and inspectors from the elements during
inspections.The canopy will be enclosed on the two longitudinal faces.The inspection office,
measuring approximately 12 feet by 32 feet,will provide office space and restroom facility for
inspection personnel.
Staging Area
A truck staging area will be constructed behind the inspection bay and sized to allow a
minimum of eight trucks to park and maneuver without encroaching on to North 6th Street.
Given the length constraints between the flight line access road to the west and proposed Spine
Road to the east, the staging area will contain two to three adjacent staging bays.A through-
lane will be constructed east of the staging area to allow vehicles to bypass the inspection bay
and return to North 61h Street via the flight line access road.
utilities
New utilities will include domestic and fire water services, sanitary sewer, power, and -
communication service to the new inspection office.Impacts to existing utilities will be avoided
to the extent possible, although at a minimum,four yard lights will be relocated with this
project.
Paving Replacement
The existing POV parking area ACP(asphalt-concrete pavement)within the truck staging area,
entrance and exit drives will be demolished and replaced with a heavy-duty ACP section
suitable for truck traffic. Paved areas within the 200-foot setback will be repaired and overlaid.
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 8 of 47
ACP in the southwestern comer and an area in the northwestern corner along the western
boundary of the site will be removed and replaced with landscaping.
Stormwater Management
The project task site lies within storm drainage Basin 34.Stormwater runoff within this basin is
managed by a system of catch basins.Collected runoff is conveyed west to an oil/water
separator which provides oil control treatment for the entirety of Basin 34.From this point,it is
conveyed north via the trunkline located within Nishiwaki Lane to Outfall OF-021,which
discharges to Lake Washington. Stormwater run-off from North 61h Street and its adjoining
landscape buffer are collected via a roadside Swale and several catch basins. Stormwater run-off
from North 61h Street is combined at the southwestern corner of the Truck Inspection site and is
then directed to the above mention trunkline which lies directly west of the site.
Stormwater patterns will remain largely unchanged by this project. An existing 18-inch
conveyance main will be re-routed around the new truck inspection office building.Additional
catchment basins will be added as a part of this project task.Stormwater runoff will decrease in
this area due to the decrease of impervious coverage,since a portion of the existing pavement
will be converted to landscape. Existing and proposed surface coverage are summarized in the
table below.
Table 1.1.1b Truck Inspection Surface Cover
Surface Cover Existing Developed
Condition Condition
1.679 acres
Total Site Area (73,152 sp
0.379 acres 0.612 acres
Pervious(Landscape) (16,533 sp (26,684 s�
Impervious(Pavement, buildings,etc.) 1.3 acres 1.050 acres
(56,619 s (45,772 s
New Impervious 0.276 acres
(12,050 sfi
New Pollution-Generating Impervious 0.197 acres
(8,617 sfi
-- Replaced Impervious 0.711 acres
(31,004 s
Replaced Pollution-Generating Impervious 0.632 acres
(27,571 s
Stormwater Facilities
The site, as indicated above, drains to Lake Washington,which is a flow control exempt
receiving water. A water quality treatment facility will be constructed within the limits of the
SW Marshaling Yard Project Task Area.This stormwater treatment facility will provide water
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Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 9 of 47
quality treatment for the entire Basin 32 area as a treatment trade for the target surface areas
created by the entire project.A further discussion of the Water Quality Treatment requirements
for the entire project site and the proposed stormwater treatment system can be found in
Section 2,Conditions and Requirements Summary, and in Section 4,Flow Control and Water
Quality Facility Analysis and Design.
1.1.2 Task 2-Parts Movement Road Improvement
The Parts Movement Road is used to transport materials and equipment between the various
fabrication buildings.This roadway will be widened to the north from two lanes to three lanes
to accommodate larger and more frequent movement of parts. The existing parking stalls
striping along the north will be removed. The road improvements will follow the existing parts -
road alignment along the south side of Buildings 04-21 and 04-17.The proposed Parts
Movement Road will then run parallel to the existing rail spur adjacent to Logan Ave east of
Building 04-17.The road will then intersect an existing drive along the south side of Buildings
04-81 and 04-82.From this intersection, the Parts Movement Road then follows the southern and
eastern face of Building 04-82 east and north to terminate at the southwest corner of Building
04-86.
The proposed Parts Movement Road will provide a route for transporting wing parts from
Building 04-86 to Building 04-21.Wing parts will be transported by cart with a required
minimum width of 24 feet.To allow parts transport while allowing vehicular movement to the
east,the existing two-lane roadway is proposed to be expanded to three lanes consisting of two
12-foot lanes and a 13-foot striped lane for parts movement.
This work includes the removal of a center landscape median and new asphalt paving between
Buildings 04-17 and 04-21 and re-striping throughout the site.
Existing Conditions
In the existing condition,the western segment of the proposed Parts Movement Road alignment
is currently a two-lane interior roadway,bordered by parking lots, transportation area,and
buildings.The eastern segment alignment consists of an interior drive and parking lot drive
aisle, and is bordered to the south by a landscaped boulevard park area.
The Parts Movement Road project lies within three drainage basins,Basin 31 for the western
portion of the project task,Basins 27 for the central portion of the project task, and Basin 25 for
the eastern portion of this project task. The storm systems within this project task area are
closed conveyance systems.
Other utilities that are present within the project area are light standards,underground power,
private potable and fire water mains,post indicator valves and fire hydrant, and water vaults
and water vaults. Fire hydrants and post indicator valves are located on the north side of the
Parts Movement Road and will be relocated and/or adjusted as required to accommodate these
improvements.
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Proposed Improvements
The two existing lanes of the parts movement road will be retained and restriped,as well as
removing parallel parking striping along the north side of the existing roadway to allow
roadway widening to the north.The corridor between buildings 04-20 and 04-21,will also be re-
striped as a part of this project. Existing landscape medians will be demolished and removed as
a part of this project and this area patch with concrete and asphalt pavement.
Utility Improvements
Existing utilities will be protected and preserved to the extent possible.Light standards within
the project area will be relocated. Fire hydrants and post indicator valves along the north side
of the Part Road and between Buildings 04-21 and 04-04 will be relocated and/or adjusted as
needed to accommodate the northern widening.
Stormwater Improvements
In general, stormwater runoff patterns from the new site will mimic existing. The existing
drainage pattern within the separate Basins will be retained with some modification to the size
of Basin 27. Surface runoff will be directed to existing catch basin locations in the northern
pavement section to remain within the western and central portion of the project task site,
Basins 31 and 27.Stormwater run-off within Basin 25 will continue to sheet flow north to
channel drains located just south of Buildings 04-81 and 04-82.
Existing flat pavement grades create nuisance flooding problems at the western end of the parts
road within Basin 31.Additional catch basins in ponding areas are proposed as a part of this
project to resolve some of these nuisance flooding occurrences. Run-off collected from the
western portion of the Parts Movement Road in Basin 31 is conveyed north via 16-, 18-and 24-
inch closed conveyance pipes where it is combined with run-off from paved areas and roof
drainage adjacent to Buildings 04-45,04-44,04-42, and 04-41.North of Building 04-41,
stormwater run-off from the majority of Basin 31 is routed through an oil/water separator prior
to entering the trunkline which conveys stormwater run-off from the south to Outfall 021.
South of the central portion of the Parts Movement Road, re-grading and conveyance system
changes that will occur as a part of Task 3 Badge Office Relocation and Task 4 Spine Road will
re-direct a portion of Basin 27 to Basin 32.In the existing condition, stormwater run-off sheet
flowed from the existing parking areas and Transportation Yard to catch basins located within
the existing road.The amount of area sheet flowing to these catch basins will be reduced in the
proposed condition as described in Task 3 and Task 4.Run-off collected from the central portion
of the Parts Movement Road in Basin 27 is conveyed north via 4-, 6-, and 8-inch pipes to two
oil/water separators located at the south edge of Building 04-21.From these oil/water
separators,pump stations direct run-off north via 12-and 18-inch pipes to north edge of
Building 04-20 where stormwater run-off is combined with the remainder of run-off from Basin
27 prior to discharging into Lake Washington at Outfall 004.
In the eastern portion of the project site area,some minor changes to flow paths may occur.
Flow rates within individual catchment areas may be altered;however,overall basin flow
patterns will remain the same as the existing condition. Run-off from the Parts Movement Road
within Basin 25 is conveyed north via 15-,24-, and 36-inch pipes and is discharged to Lake
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Washington at Outfall 002. Existing and proposed surface coverage within the project Task Area
are summarized in the table below.
Table 1.1.2 Parts Movement Road
Surface Cover Existing Developed
Condition Condition
5.280 acres
Total Site Area (229,959 sfl
Pervious(Landscape) 0.155 acres 0.136 acres
(6,779 s (5,926 s
Impervious(Pavement,buildings,etc.) 5.124 acres 5.144 acres
(223,180 s (224,073 s
0.021 acres
New Impervious
(925 s
New Pollution-Generating Impervious 0.021 acres
(925 s
0.637 acres
Replaced Impervious (27,791 s
Replaced Pollution-Generating Impervious 0.637 acres
(27,791 s
Stormwater Facilities
The site, as indicated above, drains to Lake Washington,which is a flow control exempt
receiving water. A water quality treatment facility will be constructed within the limits of the
SW Marshaling Yard Project Task Area.This stormwater treatment facility will provide water
quality treatment for the entire Basin 32 area as a treatment trade for the target surface areas
created by the entire project. A further discussion of the Water Quality Treatment requirements
for the entire project site and the proposed stormwater treatment system can be found in
Section 2,Conditions and Requirements Summary, and in Section 4, Flow Control and Water
Quality Facility Analysis and Design.
1.1.3 Task 3-Gate D-35 and Badge Office Relocation and Perimeter Fence Relocation
Existing Gate D-35 (including the Gatehouse) and the Badge Office,currently located near the
intersection of North 81h Street and Logan Avenue,are proposed to be relocated from their
current location to the intersection of the new Spine Road and North 81h Street.The Gatehouse,
which is equipped with lift rings,will be moved to the new Spine Road northern segment,
south of Building 04-21.The Badge Office, a module structure,will be relocated to the east of
the new Gatehouse,west of Building 04-89.The perimeter security fence will also be
reconstructed to interface with the Gatehouse. The Badge Office and reconfigured parking lot
located on the south side of the new Badge Office building site will be set outside the perimeter
security fence.Work at this location includes removal of existing asphalt and landscape
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installation,new private roadway and parking,vehicle control bollards, striping,and signage.
Utility work includes relocation of impacted underground utilities,building domestic water
and fire services,sanitary sewer building connection,power, communications, and stormwater
conveyance improvements.
Existing Conditions
The relocation site for the Gatehouse,Gate D-35,is currently an interior roadway drive.Utilities
within the immediate area include storm and sanitary sewer lines,underground power, and
telephone lines.The relocation site for the Badging Office is currently developed with a parking
lot for service vehicles,modular buildings, and truck ramps.Utilities on this site include storm
lines in the southern and northern portions of the site;underground power and gas along the
southern boundary of the project site;telephone along the northern site boundary;and private
domestic and fire line mains located along the south and east side of the site.The nearest
sanitary sewer manhole,which is a privately maintained sewer system,is approximately 165
feet to the northwest of the project site.
Stormwater runoff within the Badge Office site is managed with a system of catch basins
located along the northern and southern sides of the existing parking area.For the Gatehouse
site, storm lines are primarily located along the west side of the site.The Gatehouse and Badge
Office proposed sites are located in stormwater drainage Basin 32.Basin 32 ultimately drains to
Lake Washington,which is a flow control exempt receiving water.
Proposed Improvements
Proposed improvements for the Gatehouse site include demolition of existing pavement at the
Gatehouse footprint and at a vehicle "turn-out" area directly northeast of the Gatehouse;
relocating 12-and 15-inch storm lines to construct the Gatehouse foundation;new power and
communication lines to serve the Gatehouse;new turnstile gates for pedestrian employee
access;perimeter security fencing relocation to interface the Gatehouse and turnstile gate;
perimeter/security lighting;new covered pedestrian walkways along the north-leg of the new
Spine Road at the Gatehouse location;pavement grinding and overlay;and pavement striping
and signage.
Improvements for the Badge Office site include demolition of existing pavement at the building
foundation and building ramps;demolition of a section of existing covered pedestrian walkway
to install a new drive entrance for the site;relocation and reconstruction of 12-inch storm lines
and catch basins;new sanitary side sewer,domestic water,and fire services for the building;
new communication and power services;new perimeter security fencing constructed along the
north and east sides of the site;new site/parking lot lighting;new landscaped islands and
signage;and pavement grinding,overlay and striping.
Buildings
The buildings component of the project includes the relocation of the existing Gatehouse and
modular Badge Office currently located near the intersection of North 8th Street and Logan
Avenue.The Gatehouse,measuring approximately 11 feet 4 inches wide by 19 feet long,will
provide a restroom and office space for security personnel.The Badge Office,measuring
approximately 60 feet wide by 85 feet long,will serve to provide badge and identification
functions for visitors to the Boeing Renton site.
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Utility Improvements
Existing utilities will be protected and preserved to the extent possible. The existing stormwater
collection and conveyance system within the project task site will be reconstructed to
accommodate the proposed improvements. Light standards within the project area will be
relocated or replaced.Water main valve lids,catch basin rims,and underground utilities vault
lids will be adjusted to finish overlay pavement elevations.A portion of the duct bank will be
installed in the western leg of the North 8th Street roadway template,from west of the
intersection of North 81h Street and Logan Avenue and continuing west to Building 04-75.See
Task 6 for further description of the duct bank alignment.
Stormwater Improvements
In general, stormwater runoff patterns for the new Gatehouse and Badge Office sites will mimic
existing. Stormwater run-off collected east of the project site within Basin 32 will continue to be
directed west through the re-constructed conveyance system. Catch basins will be added within
the northern leg of the Spine Road and the repurposed parking area north of the Badge office
will collect runoff from PGIS that previously drained to the Parts Movement Road within Basin
27, and redirect it to Basin 32.Drainage from Basin 32 currently flows west to an oil/water
separator and sluice gate within the SW Marshaling Yard. Stormwater runoff from the entirety
of Basin 32 will receive water quality treatment via the stormwater treatment system that will
be constructed as a part of the SW Marshaling Yard in Task 1. Runoff then enters the storm line
trunk in Nishiwaki Lane,which then discharges to Lake Washington at Outfall No. OF-021 via a
60-inch pipe.A summary area table is provided below.
Table 1.1.3 Gate D-35 and Badge Office Relocation
Surface Cover Existing Developed
Condition Condition
2.795 acres
Total Site Area
(121,712 sf)
Pervious(Landscape) 0 acres 0.154 acres
(0 s (6,722 s
Impervious(Pavement,buildings,etc.) 2.977 acres 2.639 acres
(129,671 s (114,990 s
0.325 acres
New Impervious
(14,189 s
New Pollution-Generating Impervious 0.088 acres
(3,864 s
Replaced Impervious 1.579 acres
(68,800 s
Replaced Pollution-Generating Impervious (58,4 acres
(58,475 s
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Stormwater Facilities
The site, as indicated above, drains to Lake Washington,which is a flow control exempt
receiving water. A water quality treatment facility will be constructed within the limits of the
SW Marshaling Yard Project Task Area.This Stormwater treatment facility will provide water
quality treatment for the entire Basin 32 area as a treatment trade for the target surface areas
created by the entire project. A further discussion of the Water Quality Treatment requirements
for the entire project site and the proposed stormwater treatment system can be found in
Section 2,Conditions and Requirements Summary,and in Section 4, Flow Control and Water
Quality Facility Analysis and Design.
1.1.4 Task 4-Spine Road, Parking Improvements and Perimeter Fence Relocation
1.14a-Perimeter Fence Relocation
The existing perimeter fencing will be reconfigured at the Renton facility to improve the flow of
personal vehicles to the site and to reduce pedestrian-vehicle conflicts.The new secured
perimeter will be created inboard of the main personal vehicle parking areas,providing
streamlined entry and exit to the site during shift changes.Sections of existing fencing will be
removed and new ornamental fencing will be installed along with new employee turnstiles as
part of this work.
1.1.1b-Spine Road and Parking Improvements
A central interior roadway, the Spine Road,is proposed from North 61h Street to Gate D-35.The
Spine Road will provide Boeing employee access to POV parking lots located in the southern
portion of the Boeing plant site from North 6th Street.The perimeter security fence will be
reconstructed such that POV areas are outside the perimeter security fence.The southern
parking lots will be reconfigured to interface the new Spine Road.A covered walkway will be
provided along the western edge of the new Spine Road.Additional parking is also planned at
the existing transportation area,with the demolition of a total of 8-bays of the existing
transportation/auto shop canopy at Building 04-90.
Existing Conditions
In the existing condition,land cover along the proposed Spine Road alignment is nearly entirely
pollution generating impervious surface.The existing parking areas are nearly all impervious
area,with the exception of small landscaped end islands at the terminus of the parking row
aisles.There are also landscaped areas along the existing covered walkway on the eastern side
of the southern parking area,along the Logan Avenue frontage.
The proposed Spine Road and southern parking lots lay within three site drainage basins,
namely Basin 34 in the southern portion of the project and Basins 27 and 32 in the northern
portion of the project.These drainage basins ultimately drain to Lake Washington, a flow
control exempt receiving water.
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Proposed Improvements
Proposed improvements include restriping along the proposed Spine Road alignment. Covered
pedestrian walkways will be relocated to align the Spine Road.The southern parking areas will
be reconfigured to interface the new Spine Road.Existing landscape islands will remain at their
current locations to the maximum extent feasible and new landscaped islands will be
constructed.Signaled four-way stop controlled intersection is proposed at the intersection of the
new Spine Road and North 61h Street.Parking lot improvements include covered pedestrian
walkways,parking lot lighting,and landscaping.
Buildings
Structures associated with this task include the installation and relocation of 10-foot-wide
covered pedestrian walkways.These structures provide weather protections for employees as
they move from parking areas to work areas.
Utility Improvements
The existing storm system within the project area is a closed conveyance system with primarily
12-and 18-inch pipes and Type 1 and Type 2 catch basins. Other utilities that are present within
the project area are light standards,underground power and power vaults,private potable and
fire water mains,post indicator valves and fire hydrant,water vaults,utilidors,compressed air
lines,underground communication lines and vaults, gas line(along the southern boundary),
and sanitary sewer lines(in the northern portion of the project site). Existing utilities will be
protected and preserved to the extent possible.Light standards within the project area will be
relocated and/or new parking lot standards installed.
Stormwater Improvements
In general, stormwater runoff patterns for the Spine Road and parking lots will mimic existing.
No changes to catch basin locations or conveyance system is anticipated as a part of this project
task.
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Table 1.1.4 Spine Road and Parking Improvements
Surface Cover Existing Developed
Condition Condition
27.039 acres
Total Site Area (1,177,808 sp
Pervious(Landscape) 2.065 acres 1.961 acres
(89,939 s (85,461 s
Impervious(Pavement,buildings,etc.) 24.974 acres 25.076 acres
(1,087,869 s (1,092,347 s
0.853 acres
New Impervious (37,164 s
acres
New Pollution-Generating Impervious 0.737.737 9 s
Replaced Impervious 0.124 acres
(5,408 s
i
Replaced Pollution-Generating 0 acres
Impervious 1 (0 s
Stormwater Facilities
The site,as indicated above, drains to Lake Washington,which is a flow control exempt
receiving water. A water quality treatment facility will be constructed within the limits of the
SW Marshaling Yard Project Task Area.This stormwater treatment facility will provide water
quality treatment for the entire Basin 32 and the additional 19,000 sf Basin 27 area as a treatment
trade for the target surface areas created by the entire project.A further discussion of the Water
Quality Treatment requirements for the entire project site and the proposed stormwater
treatment system can be found in Section 2, Conditions and Requirements Summary, and in
Section 4,Flow Control and Water Quality Facility Analysis and Design.
1.1.5 Task 5-Lot 1 Marshaling Yard
The existing Lot 1 Marshaling Yard,located at the northeast corner of the Renton facility,will be
retained and reconfigured with this project.The site is situated between the existing Buildings
04-81 and 04-20 and includes a POV parking lot and a temporary materials staging area.
Modifications to this area will be limited to replacing the existing asphalt pavement at the
relocated material storage area with heavy duty cement concrete and restriping for the parking
stalls,interior vehicle circulation routes,and aircraft parking.Minor utility modifications will
also be necessary to accommodate the modified site layout.These will mostly be limited to
relocating yard lighting,underground power, and fire hydrants.
Existing Conditions
The existing Lot 1 Marshaling Yard is located at the north end of the facility and is bounded on
the north side by Lake Washington,to the west by Building 04-20,to the east by 04-81 Building,
and on the south side by Building 04-17.The existing marshaling yard and storage area is at the
northern end of the site with POV parking situated at the south end. Existing utilities within the
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Renton,Washington Page 17 of 47
Marshaling area include yard/area lighting,fire hydrants,and storm drains.Underground
power,sanitary sewer, potable water,compressed air, and fire protection lines all route through
the site. A sanitary sewer lift station(4A-06)is located at the west side of the site,east of the by
Building04-20. A large stormwater vault(No.487)is situated at the north end of the site.
Existing stormwater within the Marshaling Yard area is managed by a system of catch basins
and storm drains that drain to a water quality wet vault that provides basic treatment and oil
control prior to discharging to Lake Washington.All of the existing area is paved with a mix of
impervious concrete and asphalt surfacing and is considered to be pollution generating.The
project site lies within drainage Basin 27 which discharges to a water quality wet vault prior to
discharging to Lake Washington, a flow control exempt receiving water,via 32-inch pipe at
Outfall No.OF-004.
Proposed Improvements
The proposed improvements will reconfigure the site to relocate the existing marshaling yard
and POV parking and expand the existing Apron R area for aircraft parking.Apron R will be
expanded into the existing marshaling area and the existing marshaling area will be relocated to
the south to between Buildings 04-20 and 04-81. POV parking will be relocated and expanded
south of the relocated marshaling yard.Physical improvements will be limited to pavement
overlay and repair,restriping,relocating four yard lights and associated electrical panels and
underground power, and relocating two fire hydrants. Existing stormwater management will
be unchanged by this project as there will be no net increase or reduction in pollution
generating impervious surfaces. Existing drainage patterns and volumes will mimic existing.
The table below summarizes existing and proposed surface coverage at the project task site.
Table 1.1.5 Lot 1 Marshaling Yard
Surface Cover Existing Developed
Condition Condition
Total Site Area 5.392 acres
(234,870 sfl
Pervious(Landscape) 0 acre 0 acre
(0 s (0 s
Impervious(Pavement, buildings,etc.) 5.392 acres 5.392 acres ;
(234,870 s (234,870 s
New Impervious 0 acre
(0 s
New Pollution-Generating Impervious 0 acre
(0 s
Replaced Impervious 0.951 acre
(41,418 s
Replaced Pollution-Generating Impervious 0.951 acre
(41,418 s
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Renton,Washington Page 18 of 47
Stormwater Faclilties
Because this project site only proposes restriping and pavement replacement(overlay and
repair)for the proposed Marshaling Yard,water quality facilities are not proposed for this
project area.
1.1.6 Task 6 - Duct Banks
The Duct Bank component of the project consists of comprehensive upgrade of the
underground electrical feeders, primarily routing the electrical feeders from the main
substations and unit substations to individual manufacturing and office buildings while
developing a functional grid system.
The system of electrical duct banks will be installed throughout the Renton facility.This work is
the first phase of an overall upgrade to site electrical utilities;power and wiring will be
provided in later phases.The current site service consists of two receiving substations
connected to the Puget Sound Energy transmission grid,with feeders from each substation
routed to unit substations located in the various buildings.The feeders from either receiving
substation are not fully isolated from those out of the opposite substation.This upgrade will
provide two isolated and independent routes from each receiving substation to the buildings
for full electrical redundancy. Certain alignments will have parallel duct banks to maintain that
isolation.
The duct banks shall consist of nonmetallic conduits encased in reinforced concrete,except at
short sections of metallic conduit at building entries.Underground utility vaults will be
provided at junctions,critical locations and distributed along extended routes to facilitate future
electrical cable installation. Duct banks will terminate only in utility vaults and receiving
substation cable galleries or above ground and inside of building shells.Duct banks will be
installed at varying depths but not less than 24 inches from top of encasement to the top surface
of any finished grade,with deeper routes selected as needed to avoid existing buried utilities.
Duct bank construction will be coordinated such that installation will be concurrent with the
other site logistics projects where possible.The table below summarizes the existing and
proposed surface coverage for those portions of the Duct Bank installation that will not occur
within the boundaries of the other tasks proposed by this project.See Appendix A for the duct
bank alignment location.
Drainage Design
Sump pumps will be provided at each utility vault to remove condensation and/or groundwater
- and will be discharged into the storm system.
1.1.7a Task 7a -Air Compressor Building
The Air Compressor Building project task site encompasses an area at the north end of the
facility and is located adjacent to Building 04-20.The existing area at the Air Compressor
Building site is currently an asphalt drive aisle. Existing utilities include storm drains,fire
protection lines, and domestic water lines.Run-off from this area is collected via a closed
system and discharge to a water quality wet vault prior to discharging to Lake Washington,a
flow control exempt receiving water,via 32-inch pipe at Outfall No. OF-004.
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Proposed Improvements
Physical improvements will be limited to constructing the proposed Air Compressor Building
and associated structures and relocating existing utilities as required.Existing stormwater
management will be unchanged by this project as there will be no net increase or reduction in
pollution generating impervious surfaces. Existing drainage patterns and volumes will mimic
existing.The table below summarizes existing and proposed surface coverage at the project task
site. This project will be constructed under separate permit.
Table 1.1.7a Air Compressor Building
Surface Cover Existing Developed
Condition Condition
0.282 acre
Total Site Area (12,305 sJ)
Pervious(Landscape) 0 acre 0 acre
(0 s (0 s
Impervious(Pavement, buildings, etc.) 0.282 acre 0.282 acre
(12,305 s (12,305 s
0 acre
New Impervious (0 s
New Pollution-Generating Impervious 0 acre
(0 s
Replaced Impervious 0.092 acre
(4,100 s
Replaced Pollution-Generating Impervious 0.092 acre
(4,100 s
, J
Buildings
Structures associated with the task include the installation of an air compressor building,with a
building footprint of approximately 4,100 SF,and associated cooling towers (three towers for a
total footprint of 600 SF),electrical vault(approximately 1,100-SF footprint),and air storage
tanks(two 10,000-gallon tanks)in support of manufacturing production at the Renton plant. As
noted above, this project will be constructed under separate building permit.Final area
calculations will be provided with the Compressed Air Building Permit submittal.
Stormwater Facilities
Water quality treatment will not be required because this project site only proposes constructing
the Air Compressor Building and replacing PGIS with NPGIS.Roof drains from the compressor
building will be connected to the existing storm drainage system in the area that drains to the
water quality wet vault,mimicking the existing drainage pattern.
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1.1.7b Task 7b-Existing Truck Inspection Reconfiguration
The existing Truck Inspection located at the intersection of Park and Logan Avenues will be
reconfigured and repurposed as a parking facility.The existing structures will be removed and
replaced with ACP.The site lies entirely within Basin 21.A separate TIR will be prepared and
submitted for this work.The table below summarizes existing and proposed surface coverage at
the project task site.
Table 1.1.7b Existing Truck Inspection Reconfiguration
Surface Cover Existing Developed
Condition Condition
Total Site Area 1.331 acres
(57,976 sp
0.086 acre 0.060 acre
Pervious(Landscape) (3,736 s (2,598 s
Impervious(Pavement, buildings,etc.) 1.245 acres 1.271 acres
(54,240 s (55,378 s
New Impervious 0.026 acre
(1,138 s
New Pollution-Generating Impervious 0.096 acre
(4,170 s
Replaced Impervious 0.070 acre
(3,032 s
Replaced Pollution-Generating Impervious 0 acre(0 s
SECTION 2: CONDITIONS AND REQUIREMENTS SUMMARY
The following are the design standards that are applicable to this project.
• City of Renton Municipal Code
• City of Renton Development Standards
• City of Renton Amendments to the King County Surface Water Design Manual,2010
• King County Surface Water Design Manual,2009(KCSWDM)
• State Environmental Policy Act(RCW 43.21C)
The following publications and manuals are applicable to this project when a specific subject is
not covered or discussed in the above listed documents.
• Manual on Uniform Traffic Control Devices(2009)
• AASHTO"Policy on Geometric Design of Highways and Streets" (2004)
• WSDOT Design Manual
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 21 of 47
a
Requirements Summary:Stormwater Management Guidelines
The project site and Threshold Discharge Areas are subject to the following minimum
requirements.
Core Requirement 1-Discharge at the Natural Location
This project will re-route existing storm pipe conveyance systems.The project will also make
modifications to the size of tributary drainage basins,Basin 34,32,31 and Basin 27.These
changes will be made to redirect stormwater run-off to proposed water quality treatment
facilities located within Basin 32 and to reduce the tributary area for the existing water quality
treatment facility in Basin 27.All four basins discharge from the Project Site at the southern
shore Lake Washington,combining within 1/4 mile downstream of the project site.
Core Requirement 2-Off-site Analysis
A qualitative off-site analysis is included within Section 3 of this report.A quantitative analysis
of the onsite conveyance systems for Basin 32 and 34 was performed to determine that no
negative impacts will result from re-directing portions of Basin 27 to Basin 32 and 31.
Core Requirement 3-Flow Control
The project site meets the requirements of the Direct Discharge Exemption per Section 1.2.3 of
the City of Renton Amendments to the KCSWDM.Projects that are exempt from flow control
requirements are not required to implement Flow control BMPs detailed in Section 1.2.3.3 of the
City of Renton Amendments to the KCSWDM.
Core Requirement 4-Conveyance System
The existing conveyance systems for this project are required to have capacity to convey and
contain the 25-yr,24-hr storm event from the project site to its discharge into Lake Washington
in accordance with the requirements of the Direct Discharge Exemption per Section 1.2.3 of the
City of Renton Amendments to the KCSWDM.The modifications to the existing conveyance
system with the project site are required to convey and contain the 25-yr,24-hr storm event.The l
conveyance systems for the project site will be modeled using SBUH in accordance with the l
requirements of the City of Renton Amendments to the KCSWDM and the 2009 KCSWDM. See
Section 5 for additional information regarding the design of the conveyance system for this
project.
Core Requirement 5- Erosion and Sediment Control
A Temporary Erosion and Sediment Control Plan has been prepared for construction of this
project, and was previously submitted with the foundation permit for the SW Marshaling Yard.
A copy of the SWPPP will be maintained on the site and will be made available to city staff and
city inspectors as requested.
Core Requirement 6-Maintenance and Operations
Stormwater facilities maintenance and operation for The Boeing Company Renton plant are
conducted in accordance with the plant's Industrial Stormwater Permit,WAR-000232.
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Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 22 of 47
Core Requirement 7-Financial Guarantees and Liability
The Boeing Company is responsible for all storm drainage guarantees and liabilities for this
project.
Core Requirement 8- Water Quality
Enhanced Water Quality Treatment is required for project sites with predominate commercial,
industrial, or multi-family land uses.The Renton Site Logistics Project is exempt from providing
Enhanced Water Quality Treatment per the City of Renton Amendments to the KCSWDM,
Section 1.2.8.1.A Basic WQ Treatment Areas, sub-heading Intent,on page 1-64;which states:
"However,projects that drain entirely by pipe to the major receiving waters listed on page 1-33
are excused from this increased treatment and may revert to the Basic WQ menu because
concentration effects are of less concern as the overall flow volume increases."
Water Quality Treatment Target Surface areas for the project site include New PGIS that is not
fully dispersed.Because the valuation of the proposed site improvements does not exceed 50%
of the assessed value of the existing site improvements,replaced PGIS is not included in the
target surface area per criteria item#4 on page 1-64 of the City of Renton Amendments to the
KCSWDM,Section 1.2.8.1.A Basic WQ Treatment Areas.
Basic Water Quality Treatment will be provided for the project site by a water quality treatment
facility will be constructed within the limits of the SW Marshaling Yard Project Task Area.This
stormwater treatment facility will provide water quality treatment for the entire Basin 32 area as
a treatment trade for the target surface areas created by the entire project.
A further discussion of the proposed Water Quality Treatment System can be found in Section
4,Flow Control and Water Quality Facility Analysis and Design.
Special Requirement 1-Other Adopted Area-Specific Requirements
This project is located within the Cedar River Basin.There are currently no special drainage
requirements that apply to this project.
Special Requirement 2-Flood Hazard Delineation
This project is not located within a flood zone as designated by FEMA panel.Refer to the flood
zone maps provided in Appendix D.
Special Requirement 3-Flood Protection Facilities
There are currently no flood protection facilities for the site.
Special Requirement 4-Source Control
This project will comply with all"Required BMPs for All Commercial Properties" as described
in the 2009 King County Stormwater Design Manual(KCSWDM). The City of Renton Stormwater
Management Design Manual (2009)Amendment,which this project must comply, refers to the
KCSWDM, Section III for source control requirements. The basic requirements for source control
- Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 23 of 47
for all commercial properties include "Clean Your Storm Drainage System," "Eliminate Illicit
Connections to the Storm Drainage System,"and "Stencil Your Storm Drains."
Special Requirement 5-Oil Control
Oil control for Basins 27,31, 32, and 34 is provided by existing oil/water separators.
Improvements within Basin 25 are limited to the Parts Movement Road.Traffic on this portion
of the Parts Movement Road will be limited to non-motorized part transport carts and
occasional delivery vehicles and does not trigger oil control treatment. Improvements within
Basin 21 will be limited to the removal of the existing Truck Inspection buildings and the re-
configuration of this area to an all-day parking area for private vehicles.All day parking areas
are not within the thresholds which define high use sites.No additional oil control facilities will
be provided as a part of this project.
Special Requirement#6 -Aquifer protection Area
The proposed project site is not located within an Aquifer Protection Area based on the
Groundwater protection Areas in the City of Renton Map included in the City of Renton
Amendments to the KCSWDM.
SECTION 3: OFF-SITE ANALYSIS
Stormwater run-off from the project site generally discharges directly to Lake Washington and
does not enter an off-site conveyance system.Because the stormwater outfalls are submerged,
no bank sloughing or evidence of erosion was observed.The following downstream and
upstream analysis documents the Boeing Renton Production Plant onsite conveyance systems -
that will be affected by the proposed project improvements. The storm drainage systems at the
Boeing Renton Facilities are divided into over 25 basins.The closed conveyance system has 21
separate outfalls which, directly or indirectly,drain north to Lake Washington.A total of six
Basins(21,25,27,31,32,and 34) and four Outfalls(John's Creek 001,002,004, and 021)will be
affected by the proposed improvements. A qualitative upstream and downstream analysis will
be provided for Basins 21,25 and 27 which discharge to lake Washington via Outfall 001,
Outfall 002, and Outfall 004 respectively.No net increase in stormwater run-off will occur in
these basins and no negative impacts to the existing onsite private conveyance systems will
occur as a result of the proposed improvements in these basins.A qualitative and quantitative
analysis will be performed for Basins 31,32, and 34 and the associated Outfall 021 to determine
if this existing system has adequate capacity to convey and contain the 25-yr 24-hr storm event
with the minor increase in the sizes of Basins 32 and 34 and to determine the backwater
hydraulic grade line elevation at the proposed water quality treatment facilities within the new
SW Marshaling Yard.
3.0 Nishiwaki Lane Trunkline - Outfall 021
The Nishiwaki Lane trunkline is a privately maintained storm conveyance system which serves
as the main point of discharge for stormwater run-of within the western and southern portions
of the project site.Basins 31,32, 34,37, and 38 as well as stormwater run-off from the North 61h
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 24 of 47
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Street area are all collected within this trunkline and discharged to Lake Washington at Outfall
021.
The trunkline begins north of the South Aircraft Bridge,west of Apron D and within the Cedar
River Trail corridor. Run-off generated by the paved surface of Apron D (Basins 38)enters the
trunkline at CB I-01 via a 24-inch main and is directed north via a of 30-inch reinforced concrete
pipe to CB 1-02.At CB I-02, run-off generated by the paved surface of Lot 8 (Basin 37) and a
portion of the North 6th Street right-of-way enters the trunkline via a 24-inch pipe.The 30-inch
- trunkline continues north to CB I-05, a junction point located near the inter section of Nishiwaki
Lane and North 61h Street. (Approx.505 LF of 30-inch pipe with an average slope of 0.29
Stormwater run-off collected in open swales along North 61h Street and Nishiwaki Lane and
catch basins located within North 6th Street and the southwest entrance to Lot 15 enters CB I-05
via a 12-inch pipe.This tributary area consists of the northern half of North 6th Street extending
west from its intersection with Logan Ave to the southwest entrance to Lot 15,the southeast
entrance to Lot 15, a portion of the south half of North 61h Street and a small portion of the
Cedar River Trail Park and Nishiwaki Lane.
From CB I-05 the trunkline increases in size to 36-inch diameter reinforced concrete pipes and
continues north along the eastern edge of Nishiwaki Lane to a junction point at CB I-07 where
run-off generated within Basin 34 enters the trunkline via a 30-inch pipe. (Approx. 318 LF of 36-
inch pipe with an average slope of 0.11 %.)The conveyance system within Basin 34 is described
separately.
A 42-inch reinforced concrete pipe continues north from CB 1-07 to CB I-08,where the trunkline
increases in size to a 48-inch reinforced concrete pipe prior to continuing north to the junction
point at CB 1-09. (Approx.323 LF of 42-inch pipe lay at a flat slope and approx.332 LF of 48-inch pipe
lay at a negative slope.)
Run-off from Basin 32 enters CB I-09 via a 24-inch pipe. From this point the trunkline continues
north along the eastern edge of Nishiwaki Lane to the next junction point at CB I-15 through a
series of 60-inch diameter reinforced concrete pipes. The conveyance system within Basin 32 is
described separately. (Approx. 2,080 LF of 60-inch pipe with an average slope of less than 0.1 %J
Stormwater run-off from a portion of the Cedar River Trail Park and Nishiwaki Lane as well as
the landscaped area along the western Boeing Renton Site perimeter totaling 290,907 sf is
collected in a drainage swale with varying side-slopes,bottom width, and depth.This swale
conveys run-off north from a point adjacent to the Existing Gate D-30 to the northern extent of
Nishiwaki Lane. It is collected by a catch basin and enters the trunkline at CB I-15.The trunkline
turns northeast and enters Boeing Renton Plant perimeter north of Building 04-41.
The 60-inch reaches a junction point at CB I-16 where run-off from Basin 31 enters the main via
12-inch and 24-inch pipes.The conveyance system within Basin 31 is described separately. The
trunkline continues northeast from CB I-16 via 60-inch pipes to its discharge point to Lake
Washington at Outfall 021. (Approx. 318 LF of 60-inch pipe with an average slope 3.22 %.)
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 25 of 47
Exlsting Conditions Summary
No evidence of nuisance flooding or erosion was observed within this catchment area.No
incidents of flooding along this trunkline were documented in the Boeing Renton Site's
maintenance records. Nuisance flooding occurs within Basin 31 and 32,upstream of the
trunkline.A conveyance analysis of the existing trunkline indicates that some surcharging
occurs in both the 25-and 100-yr design storm events;however,no overtopping occurs within
the model for either storm event.
Proposed Improvements
The tributary area to the Nishiwaki trunkline will increase by approximately 32,000 square feet.
A backwater analysis of the existing trunkline was performed using StormShed 3G,an SBUH
methodology software program,to determine if the system can contain and covey the 25-yr,
24hr storm event and the effects that this project will have on the privately maintained Boeing
Renton Site conveyance systems upstream of the trunkline.
An increase of 0.363 cfs(less than 0.5%)occurs during the 25-yr,24-hr design storm event due to
the total increase of tributary area in Basin 32 resulting from the proposed project
improvements.The velocity of discharge at Outfall 021 will increase by 0.04 feet per second. A
maximum 0.102' (less than 1.5 inches) increase in the hydraulic grade line occurs at the farthest
upstream junction point,CB I-01,where Basin 38 discharges into the trunkline.
No additional surcharge conditions or overtopping occurs in either the 25-and 100-yr design
storm events.The impacts to the system are anticipated to be minimal. Conveyance system
improvements to minimize onsite nuisance flooding within Basin 31 and 32 are proposed as a
part of this project and are discussed below.Basin and reach maps and backwater analysis
calculation summaries are included in Appendix B of this report.
3.1 Basin 31-Outfall 021
Basin 31 is located at the northwestern corner of the Boeing Renton Production Plant extending
from just south of Buildings 04-79 and 04-21 north to the southern shore of Lake Washington
along the western edge of the site, adjacent to Nishiwaki Ave. The table below summarizes the
existing and proposed surface coverage for the project site within Basin 31. -
I
l
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 26 of 47
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TABLE 3.1 Basin 31- Outfall 021: Project Site Surface Cover
Basin 31-Surface Cover Existing Developed
Condition Condition
23.000 acres 22.745 acres
Total Basin Area (1,001,899 sp (990,801 sp
Total Project Site Area within Basin 31 2.620 acres 1.078 acres
(Western Extent of Task 2—Parts Movement Road) (114,143 sJ) (46,984 s0
Pervious(Landscape) 0.083 acres 0.072 acres
(3,623 s (3,178 s
Impervious(Pavement,buildings,etc.) 22.926 acres 22.672 acres
(998,695 s (987,623 s
Total New Impervious Area 0 acre
(0 s
Total New Pollution-Generating Impervious-PGIS 0 acre
(Target Surface Area for Water Quality treatment) (0 s
Total Replaced Impervious Area 0.251 acres
(10,955 sfi
Total Replaced Pollution-Generating Impervious 0.251 acres
(10,955 s
Reach 31D-1
Stormwater run-off from the paved area north of Buildings 04-77 and 04-78,the majority of roof
runoff from these buildings, and run-off from the western portion of the Parts Movement Road
is collected via sheet flow to catch basins with 4-,6-and 8-inch lateral connections and
conveyed west via 12-inch pipes(approx. 292 LF 12-inch pipe with an average slope of 0.44%).
Ponding within the Parts Movements has been observed during rainfall events due to flat
pavement slopes and undersized lateral connection.
Drainage is directed north from the Parts Movement Road through a 16-inch collection and
conveyance system which collects run-off from the paved drive aisle between Buildings 04-45
and 04-21 and roof run-off from the eastern half of Building 04-45(approx. 408 LF 16-inch pipe
with an average slope of less than 0.M.At the northern extent of Building 04-45 the 16-inch main
turns west and collects run-off from the paved area between Buildings 04-44 and 04-45 as well
as run-off from the southern portion of the Building 04-44 roof. This 16-inch pipe continues west
to the drive aisle west of Buildings 04-45 and 04-44 to a connection point adjacent to Building
04-40(approx. 148 LF 16-inch pipe with an average slope of less than 0.1%).
Reach 31C
Stormwater run-off from the paved area south of Building 04-79 and roof run-off from Building
04-79 are collected via a system of catch basins and 6-, 10-and 12-inch pipes.This system directs
drainage north and west through the paved drive aisle west of Building 04-45 via a 12-inch
diameter main. Catch basins with lateral connections and roof drain connections collect run-off
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 27 of 47
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from this drive aisle and the western portion of Building 04-45 and convey it to north to
combine with the 16-inch pipe at the end of Reach 3113-1 adjacent to Building 04-40(approx. 386
LF 12-inch pipe with an average slope of 0.3%).
Drainage from the 16-inch conveyance pipe for Reach 31D-land 12-inch conveyance pipe
combine and continue north via a 24-inch diameter pipe within the drive aisle west of Buildings
04-44 and 04-42. Surface run-off from the paved drive aisle and roof run-off from Buildings 04-
44 and 04-42 is collected via catch basins with laterals and roof drainage connections within this
24-inch diameter mainline as its continues north beyond Building 04-42 to a connection point at
the southwest corner of Building 04-41 (approx. 936 LF 24-inch pipe with an average slope of 0.3%).
See Reach 31C continued below.
Reach 31D-2
Roof run-off from the western portion of Building 04-20 is collected and conveyed via 4-and 10-
inch pipes to a pump system located within the southwestern corner of Building 04-21.This
pump system directs stormwater north through a 12-inch force main located within the limits of
Building 04-21 to a point just north of the southern extent of Building 04-44 where it turns
northwest and enters the paved drive aisle between Buildings 04-44, 0442, and 04-20.The 12-
inch force main ends at an 18-inch collection and conveyance system located centrally in the
drive aisle.As this conveyance system continues north,the pipe size increases from 18-to 24-
inch prior to turning west just south of Building 04-41.Roof drain connections collect runoff
from western portion of Building 04-41 as the 24-inch mains turns north within the drive aisle
west of Building 04-41 and conveys the collected roof run-off to bypass a flow splitter and
oil water separator systems ROWS-031 ROWS-041 and ROWS-042 located just north of the
/ p Y ( � � ) 1
northwest corner of Building 04-41(approx. 596 LF 18-inch pipe with an average slope of 0.22%and
600 LF 24-inch pipe with an average slope of 0.38%). J
Reach 31D-3
A collection and conveyance system runs south to north parallel and directly adjacent to the
Reach 3113-2 storm main located centrally in the drive aisle between Buildings 04-44, 04-42,and
04-20.This system is comprised of catch basins and 12-inch diameter pipes up to Building 04-41
and increases to an 18-inch system as it turns west and continues parallel to and north of the _
previously described 24-inch conveyance main(approx. 776 LF of 12-inch pipe with an average slope
of less than 0.1%and 150 LF 18-inch pipe with an average slope of 0.84%).This reach collects run-off
from the paved drive aisle between Buildings 04-44,04-42, and 04-20.At the southwest corner
of Building 04-41, this 18-inch collection and conveyance main is intercepted by the Reach 31C
storm line heading north from the drive aisle located west of Buildings 04-44 and 04-42.
Reach 31C(continued)
From this connection point, a 24-inch diameter conveyance main directs drainage north within
the drive aisle to the previously described flow splitter and oil/water separator system
(ROW-041 and ROWS-042).Catch basins and lateral connections collect storm water run-off
from the paved drive aisle prior to the flow splitter connection.Discharge from the Oil/Water
Separator system and bypass flows combined with roof fun-off from Reach 31D-2.
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 28 of 47
Reach 31B
Storm water run-off from the paved area north and east of Building 04-41 sheet flows to a
system of catch basins and 12-and 18-inch pipes which direct this run-off to the flow splitter
and oil/water separator near the northwest corner of Building 04-41(ROWS-031).A system of 4-,
6-,8-and 18-inch pipes collect roof drainage from Building 04-41 and direct it to bypass the oil
water separator system to combine with discharge from both oil/water separator systems and
bypass flows combined with roof fun-off from Reach 31D-2.
Reach 31A
Stormwater run-off from the paved area north and east of Building 04-41 is collected and
conveyed via a catch basin and lateral connection to the trunkline at CB I-16.Stormwater run-
off from the remainder of Basin 31 which is discharged from the oil/water separator systems
and bypass systems located north of Building 04-41 also enters the trunkline at CB I-16.
Existing Conditions Summary
Existing undersized storm laterals with negative slopes and flat pavement grades create
nuisance flooding problems at the western end of the Parts Movement Road within Basin 31
(Reach 3113-1) south of Building 04-21.
- A backwater analysis of the existing conveyance system indicates that additional surcharging
and overtopping occurs within the model occurs during both the 25-and 100-yr design storm
I
events.No records of flooding incidents have been found to confirm the modeled result.Field
survey of the existing conditions will be performed to confirm the structure elevations and pipe
sizes obtained from as-builts.
The existing oil/water separator system located at the end of Reach 31C;ROWS-041 &ROWS-
042 consists two Coalescing Plate Interceptor(CPI)oil/water separator modules(Model No.
814-10-SA&712-SA respectively)with a combined oil control treatment capacity of 1,750
gallons per minute.
The existing oil/water separator located at the end of Reach 31A;ROWS-031,consists of a CPI
oil/water separator module (Model Unknown)with an oil control treatment capacity that is
currently unknown.
Proposed Improvements
Existing undersized storm laterals with negative slopes and flat pavement grades create
nuisance flooding problems at the western end of the Parts Movement Road within Basin 31
(Reach 3113-1) south of Building 4-21.Replacement of inadequate storm lateral pipes and the
addition of new catch basins in flat areas are recommended to resolve some of these nuisance
flooding occurrences.
No new PGIS or NPGIS will be added within Basin 31 as a part of this project and no net
increase in runoff volumes will result from the improvements proposed by this project within
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 29 of 47
Basin 31. Approximately 12,800 square feet of impervious pavement will be replaced and
regarded north of the SW Marshaling Yard transferring the area to Basin 32.
A quantitative analysis of the conveyance system within Basin 32,Basin 34 and the trunkline
located within Nishiwaki Lane was performed due to the anticipated increase in peaks flow and
volume within Basin 32.The change in the Hydraulic Grade elevation was calculated to be -
0.01 foot during the 100-year,24-hour design storm event at CB I-16,where Basin 31 enters the
trunkline. The proposed increase in the size of Basin 32 will not negatively affect the
conveyance system within Basin 31.
3.2 Basin 32 - Outfall 021
Basin 32 is located centrally on the project site and extends east from Nishiwaki Lane to just
west of Building 04-89,near Logan Ave.Site use within this Basin includes production support
and maintenance operations,including two onsite fueling stations,with a POV parking area
located at the western edge of the Basin near Nishiwaki Lane.The table below summarizes the
existing and proposed surface coverage for the project site within Basin 32.
TABLE 3.2 Basin 32-Outfall 021:Project Site Surface Cover
Basin 32-Surface Cover Existing Developed
Condition Condition
9.844 acres 10.536 acres
Total Basin Area (428,823 sfl (458,940 sfl
Total Project Site Area within Basin 32 4.531 acres 5.116 acres
(Task 1b—SW Marshaling Yard, Task 3—Gate D-35 and (197,383 sf) (222,890 sfl
Badge Office Relocation, &Task 4—Parking Im rovements)
Pervious(Landscape) 0.083 acres 0.126 acres
(3,623 s (5,527 s
Impervious(Pavement,buildings,etc.) 9.043 acres 10.408 acres
(393,952 s (453,412 s
Total New Impervious Area 0.585 acre
(25,505 s
Total New Pollution-Generating Impervious 0.065 acre
(Target Surface Area for Water Quality treatment) (2,855 sfi
Total Replaced Impervious Area 3.164 acres
(137,866 s
Total Replaced Pollution-Generating Impervious 2.655 acres
(115,693 s
Reach 32Q
Reach 320 begins just west of Building 04-89 where a system of catch basin and 6-and 8-inch
pipes collect run-off from the paved surface.The paved area immediately adjacent to the fueling
station directs drainage to a 475 gallon spill control vault prior to connecting to this branch
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 30 of 47
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system with a 4-inch pipe.Runoff is then conveyed west via a 12-inch pipe to Reach 32L.
(Approx.295 LF of pipe with an average slope of 0.24%J
Reach 32L
Surface runoff from the northeast paved transportation yard is collected via a catch basin and is
conveyed south to the connection point with Reach 340. From this connection point run-off is
conveyed west via a 12-inch pipe to a junction point with Reaches 32N and 32P. See Reach 32L
continued below. (Approx. 248 LF 12-inch pipe with an average slope of 0.27
Reach 32N
The northeastern portion of the North 8th Street entrance to the Boeing Renton Site drains to
catch basins located adjacent to the covered walkway.These catch basins are connected via 8-
and 12-inch laterals to a collection and conveyance system located within the transportation
yard.This system, consisting of catch basins and 12-inch pipes,begins just north of the covered
walkway at the North 81h Street entrance and generally follows the walkway west and then
north to terminate at its connection to Reaches 32P and 32L. (Approx.370 LF 12-inch pipe with an
average slope of 0.20%J
Reach 32P
Reach 32P collects drainage via catch basins from the northwest corner of the transportation
yard,near the existing truck ramps.Run-off is conveyed south in 12-inch pipes south to the
point of connection with Reaches 32N and 32L. (Approx. 151 LF 12-inch pipe with an average slope
of 0.33 %.)
Reach 32L(Continued)
From its connection to Reaches 32N and 32P,Reach 32L conveys stormwater run-off west and
then southwest via 19-inch pipes to catch basin centrally located in the parking area just east of
the transportation yard and west of Buildings 04-71 and 04-69. (Approx. 97 LF 19-inch pipe with
an average slope of 0.64%.)Reach 32L continues west via a 24-inch pipe to a point just north of
Building 04-71. (Approx. 161 LF 24-inch pipe with an average slope of 0.22 %.)A channel drain
which collects run-off from a concrete pad located at the northwest corner of Building 04-71
connects to the system via a 4-inch lateral.The 24-inch collection and conveyance system
continues southwest and west beyond Building 04-71 where it collects additional surface runoff
prior to connecting to a 22x13 arch pipe. (Approx. 98 LF 12-inch pipe with an average slope of less
than 0.1 %.)This arch pipe conveys drainage southwest to the paved area just east of Building
04-70 where the conveyance main reverts back to 24-inch circular pipe prior to continuing
southwest. (Approx. 128 LF 22x 13 arch pipes lay at a negative slope)Roof runoff from Building 04-
70 is directed to the surrounding paved area via sheet flow. Roof and surface water run-off is
collected between Buildings 04-70,04-71,and 04-75 via catch basins connected to the 24-inch
main by 6-and 8-inch laterals. South of Building 04-70, the 24-inch main turns west and
continues to collect run-off within the drive aisle north of Building 04-75 until it reaches the
southern flow splitter associated with the oil/water separator system (ROWS-043) located at the
southeast corner of the POV parking area west of Building 04-70. (Approx.216 LF 24-inch pipe
with an average negative slope.)
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 31 of 47
Reach 32J
8-inch roof laterals collect drainage from a portion of Building 04-75 and convey it north to the
southern edge of the paved drive aisle between Building 04-75 and the POV parking lot.A
collection and conveyance system of catch basins and 18-inch pipes collects runoff from a
portion of the drive and conveys this surface run-off combined with roof run-off from Building
04-75 to the southern flow splitter associated with the oil/water separator system(ROWS-043)
located at the southeast corner of the POV parking area west of Building 04-70 where it is
combined with Reach 32L. (Approx. 100 LF 18-inch pipe with an average slope of 2.5%J
Reach 32K
Reach 32K begins in the paved area between Buildings 04-77 and 04-71.Run-off generated on
the roofs of these buildings sheet flows to the surrounding pavement where combines with
surface run-off.Catch basins collect the combined run-off and convey it south and southwest
via 12-inch pipes to a point within the eastern extent of the POV parking lot where it connects to
Reach 32A-2. Ponding within this paved area has been documented in Boeing's maintenance
records. (Approx. 163 LF 12-inch pipe with an average slope of 0.1 %J
Reach 32A-1
Run-off generated in the western extent of the POV parking area and the western perimeter
drive aisle is collected and conveyed south and then southeast via 12-inch pipe to the northern
flow splitter associated with the oil/water separator system(ROWS-043)located at the southeast
corner of the POV parking area west of Building 04-70 where it is combined with Reach 32A-2.
(Approx.354 LF 12-inch pipe with an average slope of 0.25
Reach 32A-2
Reach 32A-2 begins just south of the second covered fueling station located at the northeast
comer of the POV parking area.Run-off from the paved surface is collected and conveyed south
via a 10-inch pipe to a connection point with the 12-inch pipe at the terminus of Reach 32K just
south and east of the sanitary sewer lift station located within the POV parking area. The 10-
inch collection and conveyance line continues south as it collects run-off from the eastern
portion of the POV parking area.Reach 32A-2 ends at the northern flow splitter associated with
the oil/water separator system(ROWS-043)located at the southeast corner of the POV parking
area west of Building 04-70 where it is combined with Reach 32A-1. (Approx. 175 LF 12-inch pipe
with an average slope of 0.94 %J
Reach 32A -
Treatment flows from both flow splitters are directed to the oil/water separator(ROWS-043).
Bypass flows and treated discharge from the separator combine and are directed west via a 24-
inch pipe.This 24-inch conveyance main is route through a manually actuated sluice gate (Vault
No.591)that can be closed in the event of a fuel spill upstream.The discharge from Basin 32
continues west and connects to the Nishiwaki Lane trunkline via a 24-inch pipe at CB I-09.
(Approx.206 LF 24-inch pipe with an average slope of 1.27
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Renton,Washington Page 32 of 47
Existing Conditions Summary
Existing undersized conveyance pipes with negative create nuisance flooding problems just
south of Building 04-69 within Reach 32L and between Buildings 04-77 and 04-70 within
Reach K.
The existing oil/water separator system located at the southeast corner of the POV parking area
west of Building 04-70;ROWS-043,consists of a Coalescing Plate Interceptor(CPI)oil/water
separator module(Model No.818-2-CPS)with a maximum oil control treatment capacity of
- more than 875 gallons per minute.
Spill containment is provided for this basin at the manually actuated sluice gate(Vault No.591)
that can be closed in the event of a fuel spill upstream.
Proposed Improvements
This project proposes to redirect an equivalent 19,000 sf area of PGIS from the southern extent
of Basin 27, Sub-Basin 27E as a part of Task 3 and 4 to Basin 32.The project includes
replacement of inadequate conveyance pipe to alleviate existing nuisance flooding within Basin
32.The storm conveyance facilities will be re-routed to accommodate the structure
improvements included as a part of Task 1,SW Marshaling Yard and Task 3,Badge Office.
A backwater analysis of conveyance system was performed using StormShed 3G, an SBUH
methodology software program,to determine if the system can contain and covey the 25-yr,
24hr storm event and the effects that this project will have on the privately maintained Boeing
Renton Site conveyance systems that connect to the trunkline upstream of Basin 32.
When modeled with the improvements proposed to the existing conveyance system;no
additional surcharge conditions or overtopping occurs in either the 25-and 100-yr design storm
events.The overall function of the system will be improved as a result of this project.Basin and
reach maps and backwater analysis calculation summaries are included in Appendix B of this
report.
A water quality treatment facility will be constructed within the limits of the SW Marshaling
Yard Project Task Area. .The system will consist of a flow splitter, pre-treatment system,a filter
vault,and stormwater pump station.This stormwater treatment facility will provide water
quality treatment for the entire Basin 32 area as a treatment trade for the target surface areas
created by the entire project.A further discussion of the Water Quality Treatment requirements
for the entire project site and the proposed stormwater treatment system can be found in
Section 2,Conditions and Requirements Summary, and in Section 4,Flow Control and Water
Quality Facility Analysis and Design.
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Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 33 of 47
3.3 Basin 34 - Outfall 021
Basin 34 is located just north of North 6th Street and extending north to include Buildings 04-68
and 04-75 to the west, Building 04-71, and the North 8th Street Entrance at Gate D-40 to the east.
This Basin reaches from Logan Ave North on its eastern perimeter to Nishiwaki Lane at its
western perimeter.The table below summarizes the existing and proposed surface coverage for
Basin 34.
TABLE 3.3 Basin 34 - Outfall 021:Project Site Surface Cover
Basin 34-Surface Cover Existing Developed
Condition Condition
30.385 acres 30.310 acres
Total Basin Area (1,323,590 sp (1,320,335 sp
Total Project Site Area within Basin 34 23.832 acres 23.754 acres
(Task 1-SW Marshaling Yard and Truck Inspection, Task 3 (1,038,162 sJ) (1,034,745 sfi
-Gate D-35 and Badge Office Relocation,and Task 4-
Parking Improvements)
Pervious(Landscape) 2.184 acres 2.481 acres
(95,150 sp (108,076 s
Impervious(Pavement,buildings,etc.) 28.201 acres 27.829 acres
(1,228,436 s (1,212,259 s
Total New Impervious Area 0.979 acre
(42,685 s
Total New Pollution-Generating Impervious 0.783 acre
(Target Surface Area for Water Quality treatment) (34,111 s
Total Replaced Impervious Area 0.908 acres
(39,567 s
acres
Total Replaced Pollution-Generating Impervious 0.703.703 0 s
Reach 34A-1
The run-off generated at northwestern corner of Basin 34 at the existing North 8th Street
entrance is collected via a system of catch basins and 12-inch diameter pipes and conveyed
south in a collection and conveyance system of 12-inch pipes and catch basins which collects
run-off from the north western portion of Basin 34 including the existing Badge Office. (Approx.
560 LF 12-inch pipe with an average slope of 0.1 %.)just south of the Badge Office,the conveyance
pipes increase in size to 18-inch diameter pipes and continue south and south west,collecting
stormwater run-off to a connection point with Reaches 34A-2 and 34A located just east of
Substation 2. (Approx. 344 LF 18-inch pipe with an average slope of 0.23
Reach 34A-2
Surface run-off from the paved area surrounding the Substation 2 is collected via a system of 8-
and 12-inch pipes and catch basins. This system conveys stormwater run-off north to a
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Renton,Washington Page 34 of 47
connection point with Reaches 34A-1 and 34A just east of the Substation. (Approx. 190 LF of pipe
with an average slope of 1.05%J
Reach 34A
Combined run-off is conveyed west via an 18-inch main. Catch basins with 6-and 12-inch
lateral connections collect drainage as this 18-inch main continues west to a connection point
south and east of Building 04-75. (Approx. 441 LF 18-inch pipe with an average slope of 0.42
Reach 34B-1
A collection and conveyance system comprised of 8-and 15-inch pipes and catch basins is
- centrally located within the paved area between Reach 34B-2 and Building 04-75.This system
collects surface run-off from the surrounding pavement and conveys it south and west to a
point adjacent to the southern extent of Building 04-75 where drainage enters a 22"x13" arch
pipe.This 22x13 arch pipe directs run-off south and southwest to a point of connection. (Approx.
452 LF of pipe with an average slope of 0.11
Reach 34B-2
The roof run-off from Building 04-71 is collected via 6-inch pipe and connects to an 8-inch
collection and conveyance system which directs runs to the northeast corner of Building 04-75.
The collection and conveyance system's pipe size increases to 15-inch diameter as it the system
continues south along the eastern face of Building 04-75 and then turns east and decreases in
size to 12-inch diameter pipe.Run-off from the paved surface directly east of the northern two-
thirds of Building 04-75 and roof drainage from the northeastern portion of Building 04-75 is
collected via catch basins with lateral connections and roof drain connection.This 12-inch
diameter pipe and catch basin system continues east and south to connect to the 22x13 arch pipe
described in Reach 34B-1. Run-off continues southwest to a point of connection near the
southeast corner of Building 04-75. (Approx. 633 LF of pipe with an average slope of 0.2 %J
Reach 34B4
Roof drainage run-off from the southeastern portion of Building 04-75 and surface run-off from
the paved area directly east of the southern third of Building 04-75 area collected in a system 6-
and 15-inch pipes and catch basins which roof drainage connections.This system connects to
the 22x13 arch pipe at the southeast corner of Building 04-75.From this connection point,run-
off is directed south via an 18-inch pipe to connect to the 18-inch mainline described in Reach
34A. (Approx. 220 LF of pipe with an average slope of 0.29
Reach34B
Run-off is directed west within the mainline via a series of 24-and 30-inch pipes and catch
basins to the western extent of Building 04-75.Roof run-off from portions Buildings 04-75 and
04-68 as well as run-off from the landscaped area at the southeast comer of Building 04-68 are
collected via 8-and 12-inch lateral connections.Run-off from a portion of the paved area south
of Building 04-68 is collected within catch basin on the mainline as it continues west via a 24-
inch pipe to the paved drive aisle located along the Boeing Renton Production Plant western
perimeter. (Approx. 506 LF of pipe with an average slope of 0.49%J
-- Technical Information Report BergerABAM,A13.0362.203
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Renton,Washington Page 35 of 47
Reach 34E
Stormwater run-off from drive aisle and paved truck maneuvering area west of building
receives water quality treatment via Filterra units located at the western edge of the paved drive
aisle.A conveyance system of catch basins and 12-inch pipe collects drainage from the truck
well at Building 04-68 and connects to the 12-inch pipe and conveyance system which collects
treated run-off and overflow bypass run-off from the Filterra units.This system directs the
combined run-off south to a point of connection with the 24-inch mainline described in Reach
34B. (Approx. 310 LF of pipe with an average slope of 0.4%.)The storm main turns south and
continues to collect and convey run-off within the west perimeter drive aisle via a system of
catch basins and 24-inch pipes to a junction point with Reach 34D and 34C, located near the
center of Lot 15 within the western-most drive aisle. (Approx.278 LF of pipe with an average slope
of 0.9%J
Reach 34D
Storm water run-off along the eastern perimeter of Lot 15 south of Sub-Station 2 sheet flows
south and west to a catch basin in the southeast corner of the parking lot.From this collection
point, a collection and conveyance system consisting of 18-inch pipes and catch basins collects
additional run-off from a narrow portion of paved surface area along the southern perimeter of
Lot 15 to the southwest comer of the parking area. From this point the 18-inch conveyance pipe
turns northwest and then increases in diameter to a 24-inch pipe which directs drainage north
to the junction point with Reach 34ABE and Reach 34C. (Approx. 1,215 LF of pipe with an average
slope of 0.61 %J
Reach 34C
The surface run-off generated in the eastern central portion of Lot 15 is collected via two branch
systems of catch basins and conveyance pipes ranging in size from 6-to 12-inch diameter.
(Approx. 856 LF of pipe with an average slope of 1.03 %.)These branch collection systems converge
at n 18-inch collection and conveyance system which collects surface run-off from the majority
of Lot 15. Catch basins located along the main and catch basins with 12-inch lateral connections
spaced at approximately 175-foot intervals collect and convey run-off from east to the junction
with Reach 34ABE and Reach 34D. (Approx. 706 LF 18-inch pipe with an average slope of 0.35%J
From this junction point,run-off enters a flow splitter which directs water quality flows to a
system of oil/water separators(ROWS-49 and ROWS-50).Discharge from the oil/water
separator system and bypass flows combined at a junction point within the landscaped
perimeter.A 30-inch pipe discharges run-off from Basin 34 into the trunkline located within
Nishiwaki Lane at CB I-07 where this trunkline which conveys stormwater run-off north to
discharge to Lake Washington at Outfall 021. (Approx.20 LF 30-inch pipe with a slope of 0.5%J
Existing Conditions Summary
No evidence of nuisance flooding or erosion was observed within this catchment area.No
incidents of flooding were documented in the Boeing Renton Site's maintenance records.
Technical Information Report BergerABAM,A13.0362.203 -
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Renton,Washington Page 36 of 47
The existing oil/water separator system located at the end of Reach 34C;ROWS-49 and ROWS-
50, consists of two 8x16 CPI oil/water separator modules(Model Unknown)with an oil control
treatment capacity that is currently unknown.
Proposed Improvements
The impacts to the system are anticipated to be minimal. Additional catch basins may be added
to the existing conveyance system as required to facilitate positive drainage. An 18-inch
conveyance pipe will be re-routed to accommodate the new truck inspection facilities. Basin and
reach maps are included in Appendix B of this report.
3.4 Basin 21 - OutfaH 001
Basin 021 is a mainly impervious area located north of Park Ave N,just east of its intersection
with 7571h Ave which encompasses the existing Truck Inspection Facilities to be removed and
Substation#2. Drainage is collected via catch basins and routed northeast through a closed
conveyance system of 8-inch and 12-inch diameter pipes to connect to a 48-inch diameter pipe
system which enters Basin 021 from the south.This 48-inch diameter pipe system continues
northeast where it discharges to John's Creek east of Lake Washington Boulevard.
The table below summarizes the existing and proposed surface coverage for the project site
within Basin 21.
TABLE 3.4 Basin 21-Outfa11001:Project Site Surface Cover
Existing Developed
Basin 21- Surface Cover
Condition Condition
3.958 acres
Total Basin Area (172,451 sfi
Total Project Site Area within Basin 21 1.318 acres
(Task 7b-Existing Truck Inspection Reconfiguration) (57,417 sJ)
Pervious(Landscape) 0.648 acres 0.601 acres
(28,235 s (26,200 s
Impervious(Pavement,buildings,etc.) 3.31 acres 3.341 acres
(144,184 s (145,547 s
Total New Impervious Area 0.095 acre
(4,170 s
Total New Pollution-Generating Impervious 0.095 acre
(Target Surface Area for Water Quality treatment) (4,170 s
Total Replaced Impervious Area 1.159 acres
(50,525 s
Total Replaced Pollution-Generating Impervious 1.159 acres
(50,525 s
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 37 of 47
Existing Conditions Summary
No evidence of nuisance flooding or erosion was observed within this catchment area. No
incidents of flooding were documented in the Boeing Renton Site's maintenance records. The
existing land use is considered high use due to the percentage of diesel powered vehicles
entering and queuing in this area. Currently oil control is not provided in this basin.
Proposed Improvements
Improvements within this Basin will be detailed under a separate TIR
3.5 Basin 25 - Outfa11002
Basin 25 is located just north of Logan Ave, directly east of Building 04-17 and extends from
Building 04-17 north and east to the eastern edge of the project site and the southern shore of
Lake Washington.This Basin includes roof run-off from Building 04-86 and a portion of the roof
run-off from Building 04-81. The table below summarizes the existing and proposed surface
coverage for the project site within Basin 27.
TABLE 3.5 Basin 25 - Outfall 002: Project Site Surface Cover
Existing Developed
Basin 25-Surface Cover
Condition Condition
22.727 acres
Total Basin Area (990,004 sf)
Total Project Site Area within Basin 25 1.356 acres
(Task 2-Parts Movement Road fdTask 6-Duct Banks) (59,075 s,0
Pervious(Landscape) 1.878 acres 1.878 acres
(81,830 s (81,830 s
Impervious(Pavement,buildings,etc.) 20.848 acres 20.848 acres
(908,174 s (908,174 s
Total New Impervious Area 0 acre
(0 s
Total New Pollution-Generating Impervious 0 acre
(Target Surface Area for Water Quality treatment) (0 s
Total Replaced Impervious Area 0 acres
(0 s
Total Replaced Pollution-Generating Impervious 0 acres
(0 s
Reach 25C
Drainage from the southwestern extent of the basin sheet flows north to channel drains located
just south of Building 04-81 and 04-82.From these channel drains it is conveyed west and north
through a series of 12-inch and 15-inch conveyance pipes to a collection and conveyance system
consisting of 24-inch diameter pipes with catch basin laterals between Buildings 04-82 and 04-17
(approx. 443 LF 12-inch pipe with an average slope of 0.36%and 158 LF 15-inch pipe with an average
slope of 0.5%). Catch basin laterals and roof drainage connections along this 24-inch main collect
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 38 of 47
surface run-off from the paved drive aisle between the two building and run-off from the
western portions of the Building 04-17 roof(approx. 747 LF 24-inch pipe with an average slope of less
than 0.1%).
Reach 25A
A separate collection and conveyance line is routed around the southern,eastern, and northern
perimeter of Building 04-17 consisting of 8-, 12-, 18-, and 21-inch pipes. Catch basin laterals and
roof drainage connections along this main collect surface run-off from the paved areas south,
east and north of the building and the southern,eastern, and northern portions of the roof
(approx. 93 LF 8-inch pipe with an average slope of 1.25%, 170 LF 12-inch pipe with an average slope of
0.65%,390 LF 18-inch pipe with an average slope of 0.33%,and 422 LF 21-inch pipe with an average
slope of 0.32%). Reach 25A and Reach 25C combine at the northwestern corner of Building 04-17
and continue north in a 36-inch pipe.Run-off from the roof of Building 04-83 enters the 36-inch
mainline as it continues to a point adjacent to the northern extent of Building 04-82(approx.259
LF 36-inch pipe with an average slope of 0.34%).
Reach 25B
Run-off from the eastern portion of the Building 04-82 roof is collected in an 8-inch pipe which
directs this run-off north to the northeastern corner of Building 04-82 where it connects to the
previously described 36-inch storm collection and conveyance main.Run-off from the paved
area north of Buildings 04-82 and 04-83 is collected by a catch basin on this 36-inch main where
it is directed further north and east to discharge directly to Lake Washington via a 27-inch pipe
at Outfall 002 (approx. 155 LF 36-inch pipe with an average slope of 0.71%and 30 LF 27-inch pipe with
an average slope of 0.33%).
Existing Conditions Summary
No evidence of nuisance flooding or erosion was observed within this catchment area. No
incidents of flooding were documented in the Boeing Renton Site's maintenance records.
Proposed Improvements
A portion of the Parts Movement Road improvements lies within the southern extent of Basin
25. No changes to surface cover or conveyance systems will occur as a part of this project.
Existing onsite traffic patterns will be revised as a result of this project.Trucks entering the site
from the existing Truck Inspection Facilities were routed onto the Boeing Site at 757th Ave
south of Buildings 04-80 and 04-81.This high use traffic will be rerouted southwest to Basins 32
and 34 where oil control facilities are already in place due to the relocation of the truck
inspection facilities.Traffic on this portion of the Parts Movement Road will be limited to non-
motorized part transport carts and occasional delivery vehicles and does not facilitate high use
traffic patterns;therefore, oil control will not be provided.
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Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 39 of 47
3.6 Basin 27 - Outfall 004
Basin 27 is located just west of Logan and extending north between Buildings 04-21,04-20, and
04-81 to the south shore of Lake Washington.The table below summarizes the existing and
proposed surface coverage for the project site within Basin 27.
TABLE 3.6 Basin 27 - Outfall 004:Project Site Surface Cover
Basin 27-Surface Cover Existing Developed
Condition Condition
31.840 acres 31.403 acres
Total Basin Area (1,386,989 sfl (1,367,943 sf)
Total Project Site Area within Basin 27 13.198 acres 12.762 acres
(Task 2—Parts Movement Road, Task 3—Gate D-35 and (574,907 sp (555,934 sp
Badge Office Relocation,and Task 4—Parking Improvements,
Task 5—Lot 1 Marshaling Yard, Task 6—Duct Banks, Task 7
—Air Compressor Building)
Pervious(Landscape) 2.151 acres 2.162 acres
(93,740 s (94,192 sfi
Impervious(Pavement,buildings,etc.) 29.965 acres 29.241 acres
(1,305,301 s (1,273,751 sfi
Total New Impervious Area 0.605 acre
(26,388 sfi
Total New Pollution-Generating Impervious 0.419 acre
(Target Surface Area for Water Quality treatment) (18,278 s
Total Replaced Impervious Area 1.690 acres
(73,659 sfi
504 acres
Total Replaced Pollution-Generating Impervious 1.5,549 s
Reach 27C-H
Stormwater run-off from a narrow area adjacent to and west of Logan Ave beginning at the
intersection of Logan and North 61h Street and extending north to the southeastern corner of
Building 04-17(Sub-basin 27 C)is collected and conveyed north via a closed network of catch
basins and 12-inch diameter pipe.Catch basins with 4-, 6-,8-,and 12-inch lateral pipe
connections collect drainage from the narrow parking between the existing covered
walkway/utilidor east of Lot 7 and Logan Ave (approx.. 1,335 LF of 12-inch pipe with average slope
of 0.2%).The 12-inch conveyance main with lateral connections continues north beyond the
existing North 81h Street entrance collects surface run-off from landscaped areas and the existing
rail spurs located north of North 811,Street and east of Building 04-90 until it reaches the
southeast corner of Building 04-17(approx. 705 LF 12-inch pipe with an average slope of 0.25%).A
roof drainage connection at Building 04-89 adds roof drainage run-off from the entirety of this
building(sub-basin 27H)to the conveyance system.The conveyance pipe increases to a 15-inch
diameter pipe at Building 04-17 and continues north along the east face of the building(approx.
402 LF 15-inch pipe with an average slope of 0.5%). Beyond Building 04-17,the conveyance main
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 40 of 47
turns northwest.Catch basins with 6-inch lateral connections collect some surface run-off from
the paved area just north of Building 04-17(approx. 444 LF 15-inch pipe with an average slope of
0.47%).The conveyance system turns north and no further surface run-off is collected prior to
its connection to a flow splitter(No.465)located between Buildings 04-21 and Building 04-81
(approx. 518 LF of 15-inch pipe with an average slope of less than 0.M.
Reach 27B-J
j Surface run-off from the paved area north of Buildings 04-04 and 04-17 between Buildings 04-21
and 04-81 is collected and conveyed north to the flow splitter described above(No.465)via
three collection and conveyance systems consisting of 12-inch diameter pipes conveyance,8-
inch laterals and catch basins.
The eastern collection system collects and conveys drainage from south to north adjacent to
Building 04-20 and will be revised to accommodate the VPAL improvements being constructed
under a separate permit.As-builts from these improvements are not available at this time as
this project is still being constructed. The existing conveyance pipe generally follows the
eastern face of Building 04-20 to a point adjacent to the flow splitter and makes a 90-degree turn
east to its point of connection(approx. 950 LF of pipe with an average slope of 0.5%).
The central collection system collects and conveys drainage from south to north from the paved
area just north of Building 04-17 to and extends directly north to the flow splitter(No.465).
(Approx. 847 LF 12-inch pipe with an average slope of 0.5%.)
The western collection system conveys drainage from south to north,following the western
edge of the striped drive aisle adjacent to Building 04-81 to a point adjacent to the flow splitter
and makes a 90-degree turn west to its point of connection (approx. 650 LF 12-inch pipe with an
average slope of 0.6%).
- Run-off from Reach 27B-J and 27C-H combine at the flow splitter (No.465)and receive water
quality treatment at the wet vault with flows above the designed water quality treatment
volume being bypassed. The bypass flow and discharge from the wet vault continue north via a
27-inch diameter pipe(approx. 175 LF 27-inch pipe with an average slope of 1.6%).
Reach 27E
Run-off from the western portion paved area south of Building 04-20and the western portion
the rail spur area south of Building 04-20 which lies within Sub-Basin 27E is collected via catch
basins with 4-,6-,and 8-inch lateral connections to 8-and 10-inch conveyance pipes. Run-off
from this western portion of Basin 27 is directed to oil/water separator(ROWS-047).Drainage is
then directed to the southeast corner of Building 04-21 from an adjacent pump system(No.
516B)via a 6-inch force main.
The southwestern portion of Sub-Basin 27E,including roof drainage run-off from building 04-
90, the western portion of the rail spur area south of Building 04-20, and the existing and
proposed Parts Movement Road(Basin 27E);is collected and conveyed to a second separate
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Renton,Washington Page 41 of 47
oil/water separator(ROWS-048)via a system of catch basins with 4-,6-, and 8-inch lateral
connections to 12-inch conveyance pipes. Run-off is directed from the oil/water separator to an
adjacent pump system(No.510A).The 6-inch force main from pump No.516B connects to the
force main exiting pump No.510A at the southeast building corner.Discharge from both
pumps is directed north from the southeastern corner of Building 4-21 via a 12-inch force main
between Buildings 04-21 and 04-04 to a connection point near the interface of Buildings 04-21
and 04-20.
Reach 27F
Run-off from the paved drive aisle between Buildings 04-21 and 04-04 is collected via a system
of 6-inch lateral pipes and catch basins and is conveyed north via a variety of pipes including 6-
and 12-inch circular pipes and 17x13 arch pipe to a connection point adjacent to Building 04-21
and 04-20 line.
Roof drain run-off from Building 04-04 is collected and conveyed via a variety of 6-, 8-, 12-and
18-inch circular pipes as well as a 21x15 arch pipe to combine with surface run-off and
discharge from the force main Reach 27E at a connection point adjacent to Building 04-21 and
04-20 line.
Reach 27G
From the interface of Buildings 04-21 and 04-20,run-off is then tight-lined via an 18-inch and 24-
inch diameter gravity pipe system north adjacent to Building 04-20 and will be revised to
accommodate the VPAL improvements being constructed under a separate permit.As-builts
from these improvements are not available at this time as this project is still being constructed.
The conveyance continues north beyond Building 04-20 to a storm vault where it combines with
run-off from the southeastern portion the roof of Building 04-20(approx. 1,000 LF of pipe at an
average slope of 0.36%). From this vault, run-off is directed east via a 27inch diameter pipe to
combine with the wet vault discharge and bypass flows and continues north via a 30-inch pipe
(approx. 200 LF of 27-inch pipe with an average slope of 0.75% and 55 LF of 30-inch pipe with an
average slope of 1.09%).
Reach 27A
Stormwater run-off from the western portion of the Building 04-81 roof is collected and
conveyed north via a 10-inch diameter pipe to the northwest corner of Building 04-81.Drainage
is then directed northwest via a 12-inch pipe to connect to the 30-inch pipe conveying drainage
from the remainder of Basin 27 and a portion of Basin 58 (approx. 112 LF 12-inch pipe with An
average slope of 3.06%). From this final combination point drainage is conveyed north via a 36-
inch diameter pipe to the Lake Washington at Outfall 004(approx. 182 LF 36-inch pipe with an
average slope of less than 0.15%).
Existing Conditions Summary
Water Quality flow from a total tributary basin area of 678,285 SF including Sub-Basins 27C,
27B, 27H, and 27J is directed from the flow splitter(No.465)to a combination wet-vault and
oil/water separator(No.487/ROWS-030).The design water quality treatment volume and oil
Technical Information Report BergerABAM,A13.0362.203 -
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 42 of 47
control treatment capacity of the Coalescing Plate Separator located within the wet vault are
currently unknown.
ROWS-047 is a Coalescing Plate oil/water separator module(Model No.612-2-CPS)which
accepts run-off from an 84,140 sf portion of Sub-basin 27E and has maximum oil control
treatment capacity of 438 gpm.The required design flow for this separator was 260 gpm.
ROWS-048 is a Coalescing Plate oil/water separator module(Model No. 816-2-CPS)which
accepts run-off from a 175,180 sf portion of Sub-basin 27E and has maximum oil control
treatment capacity of 585 gpm.The required design flow for this separator was 516 gpm.
Proposed Condition
New PGIS will be created within sub-basin 27E by the demolition of a portion of Building 04-90
and replacement with asphalt pavement for parking areas just south of the Parts Movement
Road as a part of Task 4-Spine Road.Additional new PGIS will be created by the removal of the
landscape islands between Buildings 04-21 and 04-04 that will occur as a part of Task 2—Parts
Movement Road.This new PGIS located within Sub-Basin 27E receives oil control treatment at
ROWS-047 and ROWS-48. This 18,500 sf target surface area cannot reasonably be treated within
Basin 27 due to the existing site conditions downstream of the existing oil/water separators;
namely the underground utility infrastructure which is located between Buildings 04-20 and 04-
81 consisting of fire protection,steamline utilidors,power, telecommunications,forced air,etc.
This utility infrastructure is essential to the industrial operations and safety of operations within
the Boeing Renton Production Plant and cannot be reasonably relocated to facilitate a new
water quality treatment system within Basin 27.
This project proposes to redirect an equivalent 19,000 sf area of PGIS from the southern extent
of Basin 27,Sub-Basin 27E as a part of Task 3 and 4 to Basin 32.A water quality treatment
system located downstream of the existing oil/water separator at the western edge Basin 32 will
be constructed as a part of Task 1 to provide treatment for the entirety of Basin 32 and this
additional 19,000 sf of Basin 27.
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 43 of 47
i
SECTION 4: FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND DESIGN
4.1 Water Quality Treatment
Water Quality Treatment Target Surface areas for the project site include New PGIS that is not
fully dispersed.Because the valuation of the proposed site improvements does not exceed 50%
of the assessed value of the existing site improvements,replaced PGIS is not included in the
target surface area per criteria item#4 on page 1-64 of the City of Renton Amendments to the
KCSWDM, Section 1.2.8.1.A Basic WQ Treatment Areas.
Basic Water Quality Treatment will be provided for the project site by a water quality treatment f
facility will be constructed within the limits of the SW Marshaling Yard Project Task Area. This
stormwater treatment facility will provide water quality treatment for the entire Basin 32 area as
a treatment trade for the target surface areas created by the entire project.
Required: New PGIS for the Renton Site Logistics Project=1.154 acres (50,277 s))
Provided: WQ Treatment Area (Basin 32=10.536 acres(458,940 sf)modeled as entirely
impervious surface coverage.
The Water Quality treatment flow rate was determined by using 35%of the 2-yr peak flow rate
for the 100%impervious 10.536 acres tributary basin modeled in KCRTS using 15-minute time -
steps.
2yr peak flow= 5.02 cfs
WQ design Flow=35%of 5.02=1.757
Flow Splitter,CDS unit and Filter Vault Sizing based on 1.8 cfs l
Treatment will be provided by a Contech Stormfilter Vault using seventy-three 27-inch
cartridges proceeded by a CDS hydrodynamic separator to provide pre-treatment.Water
quality treatment will be preceded by a flow splitter device to bypass run-off from storm events
larger than the design storm.This flow splitter installed upstream of the treatment vault
ensures pollutants collected in the hydrodynamic separator and filter media are not flushed
back into the conveyance system during larger design storm events due to the backwater
conditions within the conveyance system. -
The CDS hydrodynamic separator model selected for the site has been approved to treat flows
up to 2.0 cfs.
Mass loading calculations have been provided for the filter system;however,because a
pretreatment system is provided upstream of the filter cartridge unit, the hydraulic sizing
governs.
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 44 of 47
Both systems have been designed in accordance with the requirements of the 2009 KCSWDM.
Sizing calculations and system component details for the proposed storm filter vault and pre-
treatment system are included in Appendix B of this Report.
4.2 Water Quantity Detention
The project site meets the requirements of the Direct Discharge Exemption per Section 1.2.3 of
the City of Renton Amendments to the KCSWDM.
Flow Control BMPs are not required per discussions with the City of Renton.
SECTION 5:CONVEYANCE SYSTEM ANALYSIS AND DESIGN
The existing conveyance systems for this project are required to have capacity to convey and
contain the 25-year,24-hour storm event from the project site to its discharge into Lake
Washington in accordance with the requirements of the Direct Discharge Exemption per
Section 1.2.3 of the City of Renton Amendments to the KCSWDM. The modifications to the
existing conveyance system with the project site are required to convey and contain the
25-year,24-hour storm event. The conveyance systems for the project site have been modeled
using SBUH in accordance with the requirements of the City of Renton Amendments to the
KCSWDM and the 2009 KCSWDM.
As a part of the upstream and downstream analysis included Section 3;a backwater analysis of
the existing trunkline was performed using StormShed 3G, an SBUH methodology software
program,to determine if the system can contain and covey the 25-year,24-hour storm event
and the effects that this project will have on the privately maintained Boeing Renton Site
conveyance systems.
Proposed storm improvements planned to correct existing nuisance flooding problems were
also modeled as a part of this analysis. Basin and reach maps and backwater analysis
calculation summaries are included in Appendix B of this report.
Conveyance improvements proposed in each project task have been modeled individually and
are included in Appendix B.
SECTION 6:SPECIAL REPORTS AND STUDIES
A memo addressing Geotechnical Considerations for the Boeing Renton Logistics Site prepared
by Soil& Environmental Engineers,Inc.is included as Appendix E of this Report.This memo
summarizes the site history, general sub-surface,soils, and groundwater conditions at the site,
and anticipated design and construction considerations.Project task specific site soils
investigations will be performed for each of the tasks and a geotechnical soils investigation
report prepared and submitted with the building permit for each of the tasks.With this TIR
publication(March 3,2014), the geotedmical reports for the SW Marshaling Yard(part of Task
1)is included in Appendix E. This TIR will be updated as Geotechnical Reports are prepared
for subsequent tasks.
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 45 of 47
l
SECTION 7: OTHER PERMITS
The following is a list of the actions and permits that will be required as part of this project.
• State Environmental Policy Act
• National Pollution Discharge Elimination System—Construction Stormwater General Permit
(this permit has been issued by Ecology for the Logistics projects)
• Building,Grading, and Utility
• Shoreline Substantial Development
• Dewatering(see note below)
Note: The Boeing Company holds an Industrial Wastewater Permit with King County.
This Permit requires a separate dewatering permit application for dewatering
activity in excess of 25,000 gallons per day. Due to high groundwater conditions, de-
watering activity required for construct of foundations and for utility trenching is
anticipated to exceed this amount.Therefore, a dewatering permit application is
needed through King County.The anticipated dewatering volume will be
determined by a qualified hydrologist prior to permit application.
SECTION 8: NOT USED
SECTION 9: CONSTRUCTION SWPPP ANALYSIS AND DESIGN
A construction SWPPP has been prepared for the project was provided as a part of the
Foundation permit submittal.Per discussions with the City of Renton review staff, an updated
copy of this SWPP document will be maintained on the site at all times throughout construction
and will be made available to city staff upon request.A Notice of Intent application has been
submitted by the owner,The Boeing Company, to the Washington State Department of Ecology
and a NPDES construction permit has been issued for this project. 1
SECTION 10: BOND QUANTITIES, FACILITY SUMMARIES,AND DECLARATION OF
COVENANT
The project facilities will be constructed, owned, and maintained by The Boeing Company. The
Bond Quantities and Facility Summaries forms are included in Appendix G.
SECTION 11: OPERATIONS AND MAINTENANCE MANUAL
The stormwater facilities for this project include catch basins for collection of stormwater runoff
and pipe system mains,ranging between 12-and 30-inch high-density polyethylene pipe
(HDPE) and ductile iron,Class 52.Roof and footing drains range from 4-to 6-inch HDPE and
ductile iron,Class 52.The proposed conveyance systems will connect to existing pipe
conveyance systems.
Existing stormwater facilities on the site include oil/water separators,water quality wet vault,
catch basins, and stormwater conveyance pipes.The existing stormwater system maintenance
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project-SW Marshaling Yard-Foundation Permit March 3,2014
Renton,Washington Page 46 of 47
program,currently in place for the site, will be used for the new conveyance system catch
basins and pipes. Stormwater facilities maintenance and operation at the Boeing Renton plant
are m accordance with the plant's Industrial Stormwater Permit,WAR-000232.
A water quality treatment system consisting of a flow splitter,pre-treatment system, a
stormfilter vault, and stormwater pump will be installed as a part of this project within the SW
Marshaling Yard.Operations and maintenance manuals for each component of this Water
Quality Treatment system are included for reference in Appendix H.
i
Technical Information Report BergerABAM,A13.0362.203
Renton Site Logistics Project—SW Marshaling Yard—Foundation Permit March 3,2014
Renton,Washington Page 47 of 47
Technical Information Report
Renton Site Logistics Project
Renton, Washington
Appendix A
Site Maps
SECONDARY AIR �; �' ` x`\
COMPRESSOR PLANT
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Technical Information Report—Revision 1
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THIS PAGE INTENTIONALLY LEFT BLANK
Davido Consulting Group,Inc.
TIR Boeing Renton Site Logistics Project_04-086 Steam Utilidor Final Revision 1
Technical Information Report— Re-ision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
THIS PAGE INTENTIONALLY LEFT BLANK
Davido Consulting Group,Inc.
TIR_Boeing Renton Site Logistics Project_04-086 Steam Utilidor_Final_Revision 1
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Technical Information Report
Renton Site Logistics Project
Renton, Washington
Appendix B
Drainage Maps and Calculations
Technical Information Report—Revision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
THIS PAGE INTENTIONALLY LEFT BLANK
Davido Consulting Group,Inc.
T[R_Boeing Renton Site Logistics Project_04-086 Steam Utilidor Final Revision 1
Appendix B
BergerABAM Drainage Maps and Calculations
Building Permit Submittal (Revised)
Technical Information Report
7 1-
04-68 Yards and Grounds, Southwest Marshaling Yard
Renton Site, Building 04-051
Project No.W1829787
Submitted to
The Boeing Company
Renton,Washington
A13.0362.03 3 March 2014
Technical Information Report
Appendix B, Drainage Maps and Calculations
Boeing Commercial Airplanes
Renton Site Logistics Project - SW Marshaling Yard
Renton, Washington
Submitted to
The Boeing Company
800 North Sixth Street
Renton, Washington 98055
3 March 2014
Prepared by:
BergerABAM
33301 Ninth Avenue South,Suite 300
Federal Way,Washington 98003-2600
Job No.A13.0362.03
TECHNICAL INFORMATION REPORT
APPENDIX B, DRAINAGE MAPS AND CALCULATIONS
Renton Site Logistics Project - SW Marshaling Yard
Renton, Washington
TABLE OF CONTENTS
1) Qualitative/Quantitative Analysis
a) Qualitative/Quantitative Analysis Basin Maps
i) Existing Nishiwaki Lane Trunkline-Outfall 021
ii) Developed Nishiwaki Lane Trunkline-Outfall 021
iii) Existing Basin 31 -Outfall 021
iv) Developed Basin 31-Outfall 021
v) Existing Basin 32-Outfall 021
vi) Developed Basin 32-Outfall 021
vii) Existing Basin 34-Outfall 021
viii) Developed Basin 34-Outfall 021
ix) Existing Basin 21 -Outfall 001
x) Developed Basin 21-Outfall 001
xi) Existing Basin 25-Outfall 025
xii) Developed Basin 25-Outfall 025
xiii) Existing Basin 27-Outfall 004
xiv) Developed Basin 27-Outfall 004
xv) Ex Overall-36x48
xvi) Dev Overall-36x48
b) Quantitative Analysis Calculations-25 yr&100 yr - 11x17
i) Existing Nishiwaki Lane Trunkline-Outfall 021
ii) Developed Nishiwaki Lane Trunkline-Outfall 021
iii) Existing Basin 31-Outfall 021
iv) Existing Basin 32-Outfall 021
v) Developed Basin 32-Outfall 021
vi) Existing Basin 34-Outfall 021
vii) Developed Basin 34-Outfall 021
2) Water Quality Facility Design
a) Water Quality Tributary Basin Map(Basin 32)
b) Water Quality Facility Design Summary and calculations
Technical Information Report-Appendix B BergerABAM,A13.0362.03
Renton Site Logistics Project-SW Marshaling Yard March 3,2014
Renton,Washington Page ii of iii
i) KCRTS Developed Basin Peak Flows
ii) Manufacturer Supplied Sizing Calculations
iii) Flow Splitter Calculations
iv) Structure Details—Plan Sheets-24x36
3) Conveyance System Analysis
a) Basin 32—Task 1A SW Marshaling Yard
i) Overall Basin Map
ii) SW Marshaling Yard Basin Map
iii) Conveyance calculations
b) Basin 32—Task 3 Gate D-35 and Badge Office Relocation
i) Overall Basin Map
ii) Gate D-35 and Badge Office Relocation Basin Map
iii) Conveyance calculations
c) Basin 34—Task 1B Truck Inspection
i) Overall Basin Map
ii) Truck Inspection Basin Map
iii) Conveyance calculations
Technical Information Report—Appendix B BergerABAM,A13.0362.03
Renton Site Logistics Project—SW Marshaling Yard March 3,2014
Renton,Washington Page iii of iii
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Technical Information Report
Renton Site Logistics Project
Renton, Washington
Appendix C
City of Renton Maps
Reference 11-A
1,
p
> s Flow Control Standards
a 6 si f r
Peak Rate Flow Control Standard(Existing Site Conditions)
9
# �P•t SS.rs.a�� _ d 3r 721,, -Flow Control Duration Standard(Existing Site Conditions)
k
Flow Control Duration Standard(Forested Conditions)
-
�, Ramon City Limits
Potential Annexation Area
Project Site sF m
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Technical Information Report BergerABAM,A13.0362.03
Renton Site Logistics Project—SW Marshaling Yard March 3,2014
Renton,Washington Appendix C-City of Renton Maps Page C-1 of C-3
Reference 11-B
N.,
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Groundwater Protection Areas in the City of Renton
• Prod-bon Well Weli field Capture Zones
• Spnngbrook Springs O one Year Capture Zone N
-_� Gry L�mrcs 0 Five Year Caplple Zone
Public Works Department, Cedar Valley Sole Source O Ten Year Capture Zone
Water Utility-. Aquifer Project Review Area Aquifer Protection Area Zones
J.Wilson,
Mrk,C. Streamnow Sw Area
J.W ilwn,D.Ellis,C.eoalsman � Zone 1
—'M�. City n� I - Cedar'✓alley Sde sour—Ia., i�Zone 1 Moddied '
Qmne2 ._
Technical Information Report BergerABAM,A13.0362.03
Renton Site Logistics Project—SW Marshaling Yard March 3,2014
Renton,Washington Appendix C-City of Renton Maps Page C-2 of C-3
Reference 11-C
Project Site 8..
�o
,
r_
City of Renton Soil Survey Map wa�a,ttom« �,aa .
Public Works .... - re,Ro,acrron aaa zm.,naan.a
Surface Water Utilityu�
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G.Del Rasarw ' ^r�e�city L-mrs
1 212 2/2 0 09
Technical Information Report BergerABAM,A13.0362.03
Renton Site Logistics Project—SW Marshaling Yard March 3,2014
Renton,Washington Appendix C-City of Renton Maps Page C-3 of C-3
Technical Information Report
Renton Site Logistics
Renton, Washington
Appendix D
Flood Zone Maps
(DM
7 7 n�
� � n
Fo Lake Washington
boa
Er
N' 0• APPROXIMATE SCALE IN FEET
�y 500 0 500
O
I .nr
NOTE: MAP AREA SHOWN ON THIS PANEL IS
LOCATED WITHIN TOWNSHIP 24 NORTH,RANGE 'I NATIONAL FLOOD INSURANCE PROGRAM
5 EAST. - —
m F
FIRM
FLOOD INSURANCE RATE MAP
v
KING COUNTY,
7 WASHINGTON AND
INCORPORATED AREAS
1 PANEL 664 OF 1725
Q ;SEF MAP tNCEx FOR PANELS NOT PRI —,
a
N \ c
/ / a�orr ur � "fiEab xu r
/ ( AP NUMB
53I033C0 64EF
II
MAP REVISED:
MAY 16,1995 �
LIMIT OF
DETAILED
Y sTuov CORPORATE LIMITSrx %
ao M327 ZONw---\A, � 7 rderal Emergency Management Agency
9 / This is an o1Aci�copy of a potion oT the alww"*need Ilootldmap tt
extracted using F-MIT On-line lies map does not,.nett changes
w 15 ZONE X or amen anon s which may hate been made subsequent to the data on t»
O - --------- — - - title Mock. For the latest product irdormanon about Nations Flootl insurance
0 W U3 - 0977 Program Good maps check the FEMA Flood Map Store M www.met Tema gov
N N
O O
N tP W
� ( �
� � n
N 0
wkE
APPROXIMATE SCALE IN FEET
O91
v;., 500 0 500
9
MNATIONAL FLDOO INSURANCE PROGRAM
m
oa
K FIRM
FLOOD INSURANCE RATE MAP
b x
KING COU
RM328' - NTY,WASHINGTON AND
X NORTH s INCORPORATED AREAS
C7
PANEL 9710F 1725
0
y -ZONE X r�E-IN-FUR PANELS NOT PRINTED,
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AREAS ..: �
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ZONE AE"7'; MAP NUMBER
1f NORTH 6Tw 5303360971 F
�I �t MAP REVISED
MAY 16,1995
Y ZONE X
W O 0 O ¢
-- Z Z Z o
a
Federal Emergency Alanagemenr Agency}
n 9 ZONE NORTH STH T^ of
an omcial co of a porton of the aoo a referenced flood map. x
x was tracted using F MIT On-Line. This map dcos not reflect charges
N r o dmenla which may have been made autsequent to the date on the
0
W W " - -/ title dock. For the latest product information about National Flood Insurance
dN N - - program good maps check the FEMA Flood Map Store at wvAv.msc fema.gov
0 CD
N r~P W
Technical Information Report
Renton Site Logistics
Renton, Washington
Appendix E
Geotechnical Report
=OPP
i
S&EE
� 1
GEOTECHNICAL REPORT
PROPOSED SW MARSHALING YARD
BOEING RENTON PLANT
S&EE JOB NO. 1309M
DECEMBER 8,2013
Job No. 1309M S&EE
SOIL&ENVIRONMENTAL ENGINEERS,INC.
16625 Redmond Way,Suite M 124,Redmond,Washington 98052,(425)868-5868
December 8,2013
Sieu Quail, PE, LEED AP l
BergerABAM
33301 Ninth Avenue South, Suite 300
Federal Way, Washington 98003-2600
Geotechnical Report
Proposed SW Marshaling Yard
Boeing Renton Plant
Dear Sieu:
We are pleased to present herewith our Geotechnical Report for the referenced project. Our services were
authorized via BergerABAM's General Agreement dated July 23, 2013. We appreciate the opportunity to
provide our services. Should you have any questions regarding the contents of this report or require
additional information,please contact the undersigned.
Very truly yours,
G SOIL&ENVIRONMENTAL ENGINEERS,INC.
K
C.J. Shin,Ph.D.,P.E.
�OIVAL�'
President
ek _jV 7 o 74-1
Job No.1309M Sck EE
I
TABLE OF CONTENTS
Section Page
1.0 INTRODUCTION................................................................................................................................................l
2.0 SCOPE OF WORK..............................................................................................................................................2
3.0 SITE CONDITIONS............................................................................................................................................2
3.1 SITE HISTORY&GEOLOGY..........................................................................................................................2
3.2 SURFACE AND SUB-SURFACE CONDITIONS.............................................................................................3
3.3 GROUNDWATER CONDITIONS...................................................................................................................4
4.0 LABORATORY TESTS......................................................................................................................................4
5.0 ENGINEERING EVALUATIONS AND RECOMMENDATIONS.................................................................5
5.1 SEISMIC CONSIDERATION AND HAZARD.................................................................................................5
5.2 SETTLEMENT ANALYSES.............................................................................................................................5
5.3 FOUNDATION...................................................................................................................................................5
5.3.1 GENERAL...................................................................................................................................................5
5.3.2 AUGERCAST PILE.....................................................................................................................................6
5.3.3 MAT FOUNDATIONAND SLAB-ON-GRADE..........................................................................................8
5.4 LATERAL EARTH PRESSURES ON UNDERGROUND WALLS.................................................................9
I 5.5 UNDERGROUND UTILITY CONSTRUCTION............................................................................................10
5.5.1 SHORING AND OPEN-CUT....................................................................................................................I I
5.5.2 SUBGRADE PREPARATION....................................................................................................................I 1
5.5.3 BEARING CAPACITYAND BACKFILL...................................................................................................12
5.5.4 BUOYANCY RESISTANCE........................................................................................................................12
5.5.5 GROUNDWATER CONTROL...................................................................................................................12
5.6 STRUCTURAL FILL.......................................................................................................................................13
5.7 PAVEMENT DESIGN CONSIDERATIONS..................................................................................................13
5.8 ADDITIONAL SERVICES..............................................................................................................................15
6.0 CLOSURE............................................................................................................................................................15
FIGURE 1: SITE LOCATION MAP
FIGURE 2: SITE&BORING LOCATION PLAN
FIGURE 3: LIQUEFACTIN ANALYSES
FIGURE 4: SOIL PROFILE AND PARAMETERS
FIGURE 5: PILE RESPONSES UNDER LATERAL LOAD—FREE HEAD
FIGURE 6: PILE RESPONSES UNDER LATERAL LOAD—FIXED HEAD
FIGURE 7: LATERAL LOADS ON SUBSURFACE WALLS
FIGURE 8: LATERAL EARTHE PRESSURES ON CANTILEVERED SHORING WALLS
FIGURE 9: LATERAL EARTHE PRESSURES ON BRACED SHORING WALLS
APPENDIX A: LOG OF EXPLORATIONS
APPENDIX B: LABORATORY TEST RESULTS
Job No. 1309M S&EE
GEOTECHNICAL REPORT
PROPOSED SW MARSHALING YARD
BOEING RENTON PLANT
For
The Boeing Company
1.0 INTRODUCTION
We present in this report the results of our geotechnical investigation for the proposed SW Marshaling Yard
project at Boeing's Renton plant. This project is a part of the Boeing Renton Logistics projects which
include additional components such as new electrical ductbanks, spine road, badge office, truck
inspection, etc. At the time of this report, these additional components are at the preliminary design
stage. An overall view of the logistic projects is shown in Figure 1 which is included at the end of this
report.
The site for SW Marshaling Yard is located in the southwestern portion of Renton Plant. A Site&Boring
Location Plan is shown in Figures 2. We understand that the yard will be used to store airplane parts.
Proposed structures in the yard will include a canopy that has a footprint of about 100 feet by 100 feet,
and an office building that has a footprint of about 20 feet by 75 feet. The former will be a steel-framed
structure with maximum column loads on the order of 85 kips, 15 kips, and 30 kips for downward, uplift,
and lateral, respectively. These values are un-factored, working-stress loads. Asphalt pavement is
proposed at the canopy floor.
Many new underground utilities are proposed for the project. We understand that an underground storm
water pump station is proposed at the southeastern portion of the site. This pump station will have a
diameter of about 10 feet and a depth of about 16 feet. An underground storm water quality control vault
is proposed at the southwestern portion of the site. This vault will have a footprint of about 12 feet by 20
feet and a depth of about 12 feet. Other utilities include new storm drain and sewer lines.
' I
Job No.1309M S&EE
2.0 SCOPE OF WORK
S&EE performed geotechnical engineering evaluations for the project. The scopes of our services have
included the followings:
i
1. Exploration of the subsurface soil and groundwater conditions.
2. Performance of laboratory testing.
3. Evaluation and determination of the subsurface soil profile.
4. Engineering evaluations and recommendation regarding foundation and slab supports.
5. Recommendations regarding earthwork.
6. Preparation of this geotechnical report.
3.0 SITE CONDITIONS
3.1 SITE HISTORY&GEOLOGY
Boeing Renton Plant is located at the south end of Lake Washington. During WW II,the plant area was
leveled by about 2 to 5 feet thick of fill. The native soils immediately under the fill include alluvial
deposits that are over 100 feet in thickness. These soils are typically soft and unconsolidated in the upper
50 feet and become compact thereafter. Published geologic information (Geologic Map of The Renton
Quadrangle, King County, Washington by D.R. Mullineaux, 1965) indicates that the alluvial soils are
underlain by Arkosic sandstone. We performed two soil test borings in January 2012 at North Bridge site
near the northwestern corner of the plant. These borings found glacially deposited and consolidated soil
(hard silt)at a depth of 160 feet and the soil extends to the maximum boring depth of 180 feet. Boring data
from our previous projects at the south side of Renton Airport show that the hard silt is underlain by
sandstone.
Seattle Fault Seattle Fault is the prominent active fault closest to the site. The fault is a collective term
for a series of four or more east-west-trending, south-dipping fault strands underlying the Seattle area.
This thrust fault zone is approximately 2 to 4 miles wide (north-south) and extends from the Kitsap
Peninsula near Bremerton on the west to the Sammamish Plateau east of Lake Sammamish on the east.
The four fault strands have been interpolated from over-water geophysical surveys(Johnson, et al., 1999)
Job No. 1309M 2 S&EE
i
and, consequently, the exact locations on land have yet to be determined or verified. Recent geologic
evidence suggests that movement on this fault zone occurred about 1,100 years ago, and the earthquake it
produced was on the order of a magnitude 7.0. A liquefaction map (Preliminary Liquefaction
Susceptibility Map of the Renton Quadrangle, Washington by Stephen Palmer) indicates that the project
area has high liquefaction susceptibility.
3.2 SURFACE AND SUB-SURFACE CONDITIONS
The SW Marshaling Yard is located in a parking lot that was constructed in 2004. The site surface is
relatively flat and the pavement is in good working conditions with no visible cracks or signs of distress. -
We explored the subsurface soil and groundwater conditions at the sites by the drilling of 2 soil test
borings, B-I-M and B-2-M. The boring locations are shown in Figure 2 and the boring logs are included
in Appendix A. Our knowledge of the subsurface conditions is augmented by a previous boring, B-3,
that is location at the south side of the site.
The boring data indicate that the asphalt pavement at the project site is 2.5 inches in thicknesses. The
pavement is underlain by about 10 inches thick of recycle concrete. The material is very dense and is
underlain by a surficial fill layer. This layer is about 3 to 4 feet thick and consists of a mixture of sand
and gravel (typical pitrun fill). This pitrun fill is medium dense to very dense.
The soils below the fill are alluvial in origin. These soils include inter-bedded silt, silty sand, sand and
gravel. In general,the soils are soft and loose to depths of 50 to 60 feet, except for the pockets of medium
dense layers that are present in this upper alluvium between the depths of about 15 to 32 feet. A medium
dense layer is present at the depths of 60 to 80 feet. Most of the pile foundations at the plant are embedded
in this layer. Details of the subsurface conditions can be found in the boring logs.
i
Job No. 1309M 3 S&EE
3.3 GROUNDWATER CONDITIONS
During our field exploration program, we installed the following vibrating wire piezometers (VWP) in
boring B-2-M. We later measured the piezometers' frequency and calculated the groundwater depths.
The results are tabulated below.
Boring Number VWP Depth Date Date Groundwater
(feet) Installed Measured Depth(feet)
B-2-M* 15 Oct 4,2013 Oct 10,2013 6.6
Oct 19,2013 6.6
B-2-M* 50 Oct 4,2013 Oct 10,2013 6.3
Oct 19,2013 6.4
*VWP installed in same borehole, separated aquifers.
Our experience with the construction of the nearby Building 4-68 indicates that the groundwater table
may rise to a depth of about 5 feet during wet winter months.
4.0 LABORATORY TESTS
Disturbed soil samples were retrieved from boreholes during our field explorations. Selected samples were
transported to our sub-contracted soil laboratory, AAR in Redmond, WA for testing. The tests included
gradation,moisture content and Atterberg Limits tests. The test results are included in Appendix B.
Job No.1309M 4 S&EE
I
I
5.0 ENGINEERING EVALUATIONS AND RECOMMENDATIONS
5.1 SEISMIC CONSIDERATION AND HAZARD
We recommend that Site Class E as defined in the 2012 IBC (or ASCE 7-10) be considered for the
seismic design. We have performed liquefaction analyses and the results are shown in Figure 3. The
results show that the layer of loose subsoils below the groundwater table and to a depth of about 57 feet
are liquefaction prone during strong earthquakes (M = 7.0). Also, liquefaction can result in ground
settlement on the order of 7 inches.
5.2 SETTLEMENT ANALYSES
We have performed settlement analyses for shallow foundation supports of the proposed canopy and
office building. Using the un-factored column loads and a ground pressure of 250 pounds per square feet,
the results show a maximum settlement of 1.5 inches if the canopy is support on spread footings. The
majority of the settlements are results from the consolidation of the compressible silt layers at the depths
of about 5 to 10 feet and 30 to 50 feet. Assuming that the office building is supported on a mat
foundation, the analyses show a maximum settlement of about one inch and a maximum differential
settlement of about 1/2 inches in 10 feet span. -
5.3 FOUNDATION
5.3.1 GENERAL
1. The subsurface soils at SW Marshaling Yard sites include soft and loose soils near the ground
surface and liquefiable soils extending to a depth of about 57 feet. Based on our discussion with
Mr. Sieu Quan, PE of BergerABAM,we both believe that the foundation settlement at the canopy
is excessive if the building is supported on spread footings. On the other hand, we believe that
the mat foundation is suitable for the support of the office building.
2. We recommend augercast piles for the support of SW Marshaling Yard canopy. The piles
should extend below the liquefaction zone and to a depth of 70 feet measuring from the current
ground surface.
Details of our recommendations are presented in the following sections.
Job No. 1309M 5 S&EE
5.3.2 AUGERCAST PILE
The augercast piles should be 18-inch in diameter and the pile tip should be embedded at a minimum
depth of 70 feet, measured from the top of the existing ground surface. The minimum pile spacing
should be 5 feet on center.
Pile Capacities: The pile will develop an allowable downward capacity of 85 kips and upward capacity of
30 kips. These values include a safety factor of about 2.5 and have considered the effect of liquefaction.
Figure 4 shows the soil parameters used in our evaluations. Please note that the top of pile is assumed at
a depth of 3 feet below the ground surface,approximately the depth to the bottom of pile caps.
Response to Lateral Load: Figures 5 and 6 show the results when the pile is subjected to a lateral working
load of 10 kips. The former assumes a free/pin head connection and the latter assumes a fix head condition.
We believe that the actual condition will fall somewhere in between, and will depends on the degree of
reinforcements at the joint of pile and pile cap.
Figures 5 and 6 also show that the point of reflection is located at about 18 feet below the top of pile(about
21 feet below the ground surface). Based on this, we recommend that the pile be designed with a point of
fixity at a depth of 30 feet below the ground surface. The anticipated lateral load on pile is relatively
light. We therefore recommend that the reduction of lateral capacity due to group effect be ignored.
Additional Lateral Resistance: Additional resistance to lateral loads will be provided by passive soil
pressure against the pile caps and grade beams. Assuming that structural fill is used for the backfill, an
equivalent fluid density of 200 pounds per cubic foot (pcf) may be used for design. The criteria for the
structural fill are presented in Section 5.6 of this report.
Pile Settlements: Pile settlement will result from elastic compression of the piles and the supporting soils.
The settlement is estimated to be about 1/2 inches, and will occur rapidly, essentially as the loads are
applied.
Pile Installation: Cement grout must be pumped continuously during withdrawal of the auger, the rate of
which should not exceed about 5 to 8 feet per minute. Also, at least 10 feet of grout head must be
maintained during the entire withdrawal. We anticipate that the grout volume discharged from the pump
to be about 1.2 to 1.5 times the theoretical volume of the drilled hole. The grout volume is usually
obtained by counting the number of pump strokes. The grout pressure at the pump should be maintained
in the range of 150 to 350 psi, depending on the length of the feeder hose used. The drilling contractor
Job No. 1309M 6 S&EE
should provide pressure gages and stroke counters at the pump prior to drilling.
Quality Control: The piling contractor must implement the following quality control measures.
1. Prior to pile installation, the contractor should provide historical data regarding the volume
of grout output per stroke of their pump. If this is not available, the contractor should
calibrate the grout pump by filling a 55-gallon drum. This calibration should be performed a
minimum of two times and approved by our onsite inspector.
2. Prior to casting, the operator should lift auger 6 to 12 inches at start of grout pumping to
facilitate tip plug removal, then return to previously established tip elevation. An initial grout
head of 10 feet should be developed before start of auger withdrawal and maintained
during extraction.
3. Volume of placed grout should be at least 120 percent of theoretical volume.
4. If grout pumping is interrupted during placement, the auger should be lowered a minimum
of 5 feet and restart withdrawal.
5. The rebar cage should be equipped with centralizers and the cage should be plumb before
inserting into the drilled-hole. Single cable hooked on one side of the cage, or any other
mean resulting in tilting of the cage is not allowed. The cage should sink to the design
depth by its own weight. Pushing the cage down by machine is not allowed. If grout de-
hydration or any other reason preventing smooth cage installation, the hole should be re-
drilled and re-grouted.
6. For adjacent piles that are less than 5 feet clear space, the minimum waiting period for
installation should be 12 hours.
7. Pile installation should be monitored by an inspector from our office. Our inspector will
evaluate the adequacy of the construction methods and procedures. Any problems which
might arise, or deviations from the specifications, will be considered during our evaluations
and approval of each pile installed.
Job No. 1309M 7 S&EE
5.3.3 MAT FOUNDATIONAND SLAB-ON-GRADE
We recommend that the mat foundation and slab-on-grade be designed with a subgrade reaction modulus of
100 pci (pounds per cubic inches) and an allowable bearing pressure of 1,500 psf(pounds per square
feet), exclusive of mat's self-weight. This value includes a safety factor of at least 2,and can be increased
by one-third for wind and seismic loads.
To promote uniform support and prevent loosened base, we recommend that a 6 inch thick base course be
installed below the bottom of mat and slab. The base course material should be 1-1/4" minus crushed rock.
The material should be placed in one lift and be compacted to a firm and non-yielding condition by a
mechanical compactor that weighs at least 1,000 pounds. We further recommend that the slope between the
slab and thickened edge(mat)be 2H:1 V or flatter.
As the groundwater table is at least 5 feet in depth and the soils above the groundwater table are granular in
nature, we believe the chance of capillary rise to slab level is remote. As such, we believe that a moisture
barrier is un-necessary.
Sub-grade Preparation: The subgrade soil should be moisture-conditioned to +/-2% from its optimum
moisture content. The subgrade should then be leveled and compacted to a firm and non-yielding condition
by at least 4 passes of a vibratory roller compactor that weighs at least 10 tons. In the event that soft,wet,or
organic soils are found during compaction, the soils should be removed by over-excavation. The over-
excavation should then be backfilled with structural fill. Subgrade preparation should be monitored by a site
inspector from our office.
Job No. 1309M 8 S&EE
5.4 LATERAL EARTH PRESSURES ON UNDERGROUND WALLS
Lateral earth pressures on permanent retaining walls, underground vaults or utility trenches/pits, and
resistance to lateral loads may be estimated using the recommended soil parameters presented in the
following table.
Coefficient
Equivalent Fluid Unit Weight(PCF) of
Friction
at Base
Active At-rest Passive
Structural fill and 40 50 200 0.5
native soils
Note: Hydrostatic pressures are not included in the above lateral earth pressures.
The at-rest case applies to unyielding walls, and would be appropriate for walls that are structurally
restrained from lateral deflection such as basement walls, utility trenches or pits. The active case applies to
walls that are permitted to rotate or translate away from the retained soil by approximately 0.002H to
0.004H, where H is the height of the wall. The passive earth pressure and coefficient of friction include a
safety factor of 1.5.
SURCHARGE INDUCED LATERAL LOADS
1
Additional lateral earth pressures will result from surcharge loads from floor slabs or pavements for
parking that are located immediately adjacent to the walls. The surcharge-induced lateral earth pressures
are uniform over the depth of the wall. Surcharge-induced lateral pressures for the "active" case may be
calculated by multiplying the applied vertical pressure (in psf) by the active earth pressure coefficient
(Ka). The value of Ka may be taken as 0.3. The surcharge-induced lateral pressures for the "at-rest" case
are similarly calculated using an at-rest earth pressure coefficient (Ko) of 0.5. For surcharge loads that
are not adjacent to the wall, the induced lateral earth pressure will depend on the magnitude of the
surcharge and the distance from the wall. Such induced lateral load can be estimated using the equations
shown on Figure 7.
i
Job No. 1309M 9 S&EE
The slope-induced lateral earth pressure can be accounted for by increasing the effective height of the
wall by one-half the slope height. The traffic-induced lateral earth pressure can be accounted for by
increasing the effective wall height by 2 feet.
SEISMIC INDUCED LATERAL LOADS
For imbalanced, seismic induced lateral loads, the dynamic force can be assumed to act at 0.6 H above the
wall base and the magnitude can be calculated using the following equation.
Pe =10H
Where Pe = uniform pressure in psf
H = wall height in feet
BACKFILL AND DRAINAGE BEHIND RETAINING WALLS
Unless the wall is designed to sustain hydrostatic pressures,granular soils with less than 5%fines should be
used for backfill behind walls. Care must be taken when compacting backfill adjacent to retaining walls,to
avoid creating excessive pressure on the wall. The density of the structural fill can be assumed to be 130
and 68 pounds per cubic feet above and below groundwater table,respectively.
Perforated drainpipes should be installed behind retaining walls to assist drainage. Drainpipes should be at
least 4 inches in diameter, covered by a layer of uniform size drain gravel of at least 12 inches in thickness,
and be connected to a suitable discharge location. An adequate number of cleanouts should be installed
along the drain line for future maintenance.
5.5 UNDERGROUND UTILITY CONSTRUCTION
As mentioned previously, new underground utilities will include a pump station, storm quality control
vault,and storm drain and sewer lines. The installation of these facilities will require excavations near or
below the groundwater table. With the presence of shallow groundwater table and soft subsoils, the
installation will require adequate equipment, manpower and experience. Similar projects were completed
successfully near the project site. We recommend that the earthwork contractor review the project
information carefully and formulate a work plan prior to excavation.
Job No. 1309M 10 S&EE
5.5.1 SHORING AND OPEN-CUT
The choice of excavation shoring or open cut will depend on factors such as depth and size of excavation,
depth of groundwater table and de-watering method, space restraint, and others. Shoring systems
including trench shield, trench box, sheetpile or freeze wall were utilized at the plant before. We have
evaluated the lateral soil pressures on shoring walls. Figures 8 and 9 show our recommended lateral earth
pressures for cantilevered and braced walls,respectively.
For open cut excavation, the contractor should prepare for I H:IV cut slope above the groundwater table
and 2HA V below. Construction safety is contractors' responsibility and they should make necessary
steps to ensure safety. Past experience shows that bench cut at the top of the excavation can lessen the
overburden pressure, reduced the tendency of sidewall sloughing, and facilitate backfill. The bench, if
used, should have a ]A ratio between the height and horizontal run. Trench boxes or speed-shore may be
necessary at the bottom portion of the excavation. The contractor should be aware of possible sidewall
caving when trench boxes or speed-shore are removed. The caving will leave loose sloughing at the
bottom of the excavation. This loose soil must be removed or compacted in-place so that future ground
settlement can be avoided. Compaction of such loose sloughing is not always feasible due to the
proximity of groundwater table and possible sidewall disturbance by vibration. When cleaning by -
excavators and hand shovels are not possible, the contractor should be prepared to remove the loose
sloughing using a vector truck. Also, backfill with CDF will be necessary when compaction is not
feasible, such as at the locations of utility crossing and tight spaces.
5.5.2 SUBGRADE PREPARATION
All loose soil cuttings should be removed prior to the placement of bedding materials. Wet and loose
subgrades should be anticipated. The contractor should make efforts to minimize subgrade disturbance,
especially during the last foot of excavation. Often time subgrade disturbance in wet and loose soil is
inevitable, and subgrade stabilization is necessary in order to avoid re-compression of the disturbed zone.
Depending on the degrees of subgrade disturbance, the stabilization may require a layer of quarry spalls
(2 to 4 inches or 4 to 8 inches size crushed rock). Based on our experience at the plant, when compacted
by a hoepac, a 12 to 18 inches thick layer of spalls would sink into the loose and soft soils, interlock and
eventually form a stable subbase. A chocker stone such as 1-1/4" clean crushed rock should be installed
over the quarry spalls. This stone should be at least 6 inches in thickness and should be compacted to a firm
and non-yielding condition by a mechanical compactor.
I
Job No. 1309M 1 1 S&EE
In the event that soft silty soils above groundwater table are encountered at subgrades,the subgrade should
be over-excavated a minimum of 6 inches. A non-woven geotextile having a minimum grab tensile
strength of 200 pounds should be installed at the bottom of the over-excavation and the over-excavation
backfilled with 1-1/4" minus crushed rock. The material should be compacted to a firm a non-yielding
condition using a mechanical compactor.
5.5.3 BEARING CAPACITYAND BACKFILL
Excavated subgrade so prepared should have an allowable bearing capacity of 1,500 psf(pounds per
square feet) for subgrades shallower than a depth of 5 feet; and 2,000 psf for subgrades deeper than 15
feet.
Structural fill materials should be used for backfill. The material and compaction requirements are
presented in Section 5.6.
5.5.4 BUOYANCY RESISTANCE
During strong earthquakes, the subsoils below the groundwater table may liquefy and lose the frictional
resistance against the walls of underground vaults. The remaining resistances include the structural
weight and the frictional resistance from the soil above the groundwater table. The frictional resistance
can be estimated using an equivalent fluid density of 50 pcf and a friction coefficient of 0.5. In the event
that additional uplift resistance is required, a few options can be considered: 1) increase the structural
weight by a thickened base; 2) extend the base to engage additional soil overburden, and 3) install soil
anchors. The type of anchor may include the augercast pile recommended for the canopy support,
micropiles,or helical piles.
5.5.5 GROUNDWATER CONTROL
We understand that Mr. Scott Bender of Bender Consulting, LLC(BCL)will provide a groundwater control
or de-watering plan. The contractor should note that:
1) Discharge to storm lines may be limited by the capacity of the existing pipes. Metro King
County only allows for 25,000 gallon per day discharge to the sewer system. The county may
_ even suspend discharge temporarily for a day or two during heavy rainstorm events. The above
restrictions may affect construction sequence and the contractor should thus plan accordingly.
Job No. 1309M 12 S&EE
The person retains the discharge permit for Boeing is Ms. Doris Turner
<doris.s.turner@boeing.com>.
2) Pre-discharge treatment may be required for water quality control. Again, Ms. Doris Turner
should be contacted for such issue.
5.6 STRUCTURAL FILL
Structural fill materials should meet both the material and compaction requirements presented below.
Material Requirements: Structural fill should be free of organic and frozen material and should consist of
hard durable particles, such as sand, gravel, or quarry-processed stone. The onsite granular fill above
groundwater table is suitable for structural fill. Suitable imported structural fill materials include silty
sand, sand, mixture of sand and gravel (pitrun), recycled concrete and crushed rock. All structural fill
material should be approved by a site inspector from our office prior to use.
Placement and Compaction Requirements: Structural fill should be placed in loose horizontal lifts not
exceeding a thickness of 6 to 12 inches, depending on the material type, compaction equipment, and
number of passes made by the equipment. Structural fill should be compacted to a firm and non-yielding
condition or at least 95% of the maximum dry density as determined using the ASTM D-1557 test
procedures.
5.7 PAVEMENT DESIGN CONSIDERATIONS
After the existing pavement is removed from the proposed pavement areas, the exposed subgrade soils
may include very dense recycled concrete and medium dense pitrun fill (a mixture of sand and gravel)
We recommend that the subgrade be proof-rolled to identify areas of soft, wet, organic, or unstable soils.
Proof-rolling should be accomplished with a heavy vibratory roller, front-end-loader, or loaded dump
truck(or equivalent)making systematic passes over the site while being observed by a site inspector from
our office. In areas where unstable and/or unsuitable subgrade soils are observed, these soils should be
overexcavated to approximately 12 inches and backfilled with densely compacted, structural fill.
Geotextile may be necessary at the overexcavated subgrade.
Job No. 1309M 13 S&EE
After proof-rolling, the subgrade should be thoroughly compacted by a vibratory roller compactor that
weighs at least 12 tons. The roller should make at least 6 passes. The subgrade soil should have adequate
moisture content(within+/-2%from optimum)at the time of compaction.
Asphalt pavements constructed over proof-rolled and compacted subgrades, as specified above, can be
designed with a California Bearing Ratio of 12. The pavements should also be designed for frost
protection consisting of at least 15 inches of pavement, base course, and/or granular subbase between the
subgrade soils and the top of the pavement. The base course and granular subbase should be non-frost-
susceptible and contain no more than 5 percent fines(material finer than a No. 200 U.S. standard sieve).
Crushed rock materials with less than 10 percent non-plastic fines are also regarded as non-frost-
susceptible. Subbase fills should meet the gradation requirements of WSDOT Standard Specification 9-
03.14(1), Gravel Borrow (WSDOT, 2010b). Subbase should be compacted to at least 95 percent of the
maximum dry density, as determined by the modified Proctor compaction test (ASTM D 1557). Base
course under pavements should consist of clean, pit-run sand and gravel; well-graded crushed rock; well-
graded recycle concrete; or a blend of commercial rock products conforming to WSDOT specifications
for Crushed Surfacing, Specification 9-03.9(3). The base course layer should be compacted to at least 98
percent of the maximum dry density, as determined by the modified Proctor compaction test (ASTM D
1557).
A typical standard-duty (lightweight) pavement section that we have used on similar projects consists of
2.5 inches of Class B asphalt concrete surfacing, 4 inches of base course, and 4 inches of subbase. A
heavy-duty pavement section could consist of 4.5 inches of Class B asphalt concrete surfacing, 6 inches
of base course, and 6 inches of subbase. Sidewalks could consist of 4 inches of Portland cement concrete
over 4 inches of base course. A concrete pavement section could consist of 6 inches of reinforced
concrete over 4 inches of base course. We recommend that these typical sections be considered for
planning purposes and that project-specific pavement design analyses be performed. These analyses will
require traffic load data such as vehicle axle loads and daily vehicle trips.
Job No. 1309M 14 S&EE
5.8 ADDITIONAL SERVICES
We recommend the following our additional services during the construction of the project.
I. Monitoring pile installation. We will approve contractors' equipment; observe the installation of
each pile;assess and approve the capacity of each pile;and provide recommendations when needed.
2. Monitoring earthwork. We will observe subgrade soil, and provide recommendations regarding
local over-excavation to remove soft, wet or organic soil; observe and approve structural fill
material;observe and approve fill placement and compaction.
3. Monitor mat and slab subgrade preparation. We will confirm the bearing capacity of the subgrade
soils,and will assist the contractor in evaluating the protection and over-excavation requirements, if
necessary.
4. Review and responses to contractors' submittals and RFI's.
5. Attendance of construction progress meetings.
6. Preparation and distribution of field reports.
7. Other geotechnical issues deemed necessary.
6.0 CLOSURE
The recommendations presented in this report are provided for design purposes and are based on soil
conditions disclosed by the available geotechnical boring data. Subsurface information presented herein
does not constitute a direct or implied warranty that the soil conditions between exploration locations can be
directly interpolated or extrapolated or that subsurface conditions and soil variations different from those
disclosed by the explorations will not be revealed. The recommendations outlined in this report are based
on the assumption that the development plan is consistent with the description provided in this report. If the
development plan is changed or subsurface conditions different from those disclosed by the exploration are
observed during construction, we should be advised at once so that we can review these conditions, and if
necessary,reconsider our design recommendations.
Job No.1309M 15 S&EE
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• PROPOSED STORM DRAIN MANHOLE
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SW MARSHALING YARD CANOPY ��
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LIQUEFACTION ANALYSIS
SW Marshaling Yard, Boeing Renton Plant
Hole No.=B-1-M Warer Depth=4 ft Magnlrude=7
Accelerarion=4.25g
Raw Unlit Fines Soil Description Shear Stress Ratio Factor of Safety Settlement
S PT 50 Weight 13 0 0 1 0 1 5 0(in.; 10
Dense fill
13 12E Loose to medium dense sand
f o 4 115
-I
23 125 2
i
Medium dense gravel
20 13 129 2
Loose, inter-bedded sand,silty sand and
sift
Loose to medium dense sand
30 21 122 10
Soft silt
3 102 NoLq
40 1 102 NoLq
3 102 NoLq
50 4 102 NaLq ----
7 120 75
Loose siltf sand
3
60 16 120 50 Medium dense sand
e
17 l
fs 1=1 S=6.98 in.
70 23 121 ` CRR — CSR fs1-- Saturated
Shaded Zone has Liquefaction Potential Unsaturat. —
Civiffech Corporation S&EE Job No. 1309-M Figure 3
ALL-PILE CivilTech Software www drviltech Wm Licensed to
Concrete poured into drilled hole
Diameter is limited to 24in(61 cm).
FOUNDATION PROFILE & SOIL CONDITIONS
Depth FOUNDATION PROPERTIES t� M SOIL PROPERTIES Depth
from P from
Ground-ft Re pp Iblf3 C-k /f2 k-Ib/i3 e50% Ns t Ground-ft
YYidtti in A'-in2 Per.in I'-in4 E- 2 W-kptf �__ __) _ -_--- P--- _ _ _P.
0.0 18 254.5 56.5 5153.0 3000 0.255 0.0 8.5 34.3 0.00 43.0 13
Concrete(rough) SarW/Gravel
8.5 9.5 37.0 000 76.1 23
Sand/Gravel
15 15
_.__ ...._._.._...
r - .5 7.5 31.1 0 00 20.4 7
Sand/Gravel
j 23.5 9.5 38.5 0.00 68.2 20
Sand/Gravel
30 28.5 45 VIA 0.18 35.9 1.96 3 30
Silt(Phi+C)
45 45
r
51.0-8.5 34.2 0.00 42.8 -- 13
Sand/Gravel _---._---
54.0 48.5 31.3 6.00 21.5 7
Sand/Gravel
-- - - -- -- 60-,
58.0 57.5 35.4 6.00 54.6 18
Sand/Gravel
82.5 70 38 0.00 84.4 19
Sand/Gravel
_.....__.._........._-._._._..-_...........
__.....____._-.
72.0
75 75
90 90 1
Batter Angle=0 (Pile diameter not to scale) Surface Angle=0
CivilTech SW Marshaling Yard, Boeing Renton Plant Figure 4
Software S&EE Job No. 1309-M (Liquefaction State)
M
PILE DEFLECTION & FORCE vs DEPTH
Single Pile,Khead=l, Kbc=l
DEFLECTION,yt-in MOMENT-kp-t SHEAR-kpDemap
-2 K-�b rs e5o% 'e TOP-11
.7 +20 C F" C4p
F-1 1 11 11 1 11 1 1 1 1 11,.fil j-'1111 ' I ' ll ' ",-11 1 1 1 1 1 1 ----FT_TT 1 1 1 1 1 1 1 a5 U3 000 430
7 Vt
,,-o at x 9-,t
TM*-1 22E-a Tot)y1-115E+0 Tcg)Wam"-o 0 TOO S1*3r-10
Mac-A-1 AM+() Mac Vxrrere-B0 0 Va(War-109 _W selglon E_WD-Zlom
TOO%-1 12E-2
Civiffech SW Marshaling Yard, Boeing Renton Plant
Software S&EE Job No. 1309-M (Liquefaction State) (Figure'!511 Free Head)
PILE DEFLECTION & FORCE vs DEPTH
Single Pile,Khead=5. Kbc=2
DEFLECRON.yt-in MOMENT -kp-f SHEAR-kpDew(ZO
anj C-Oa2 WDIZ Pfla Too_'
----
Savo ura+el
li
000 430
—30
Tip yo-4,05E-9 TCO Aw3 24z-1 Tap)e%D1*r9--69 Toe&"ear-100
M ,?-324E-1 Max 1omel-69 7 Var.Srear-100
Too St-3 laE-18 Last SFAW -rit-5153
Civiffech SW Marshaling Yard. Boeing Renton Plant
Software S&EE Job No. 1309-M (Liquefaction State) (FigureL2_[Fixed Head)
0 0 -
m=0.1
0.2 \ 0.2 m=0.6
m=0.5 2�
m=O.
04 04
m=0.3
m=0.4
N /C
00 0.6 0.6
W m R m P� R
u J
-' 0.I .60H 0.2 .78 .59 H
> / / 0.3 .60H 0.4 78 .59 H
0.8 / OB
0.5 .56 H 0.6 .45 .48 H
0.7 .48H
10 --)1 1 0 .2 .4 .6 .8 1.0 0 .5 1.0 1.5
VALUE OF C-H ( H VALUE OF vH ( 2
TL
POINT LOAD Qp Q
X=mH P
LINE LOAD QL Z=nH
FOR m < 0.4 A A
X=1n H - _}
0-H(�)_ (0 I H OH R FOR m�0.4
0.28n2
P = 0.55Q (H2)=
Z=nH H L H �p ( .In
FOR m)0.4: FOR m >0.4
H
vH( H�)= 1.28m2n ( H2 )= 1_77m2n2
4 R L (m2+-n2)2 H Qp (m2+.n2)3
RESULTANT P = 0.64 QL o-H =0-H COS (1.10)
H (m2+1 ) vH - Q�p
PRESSURES FROM LINE LOAD QL - 9
Q
(BOUSSINESQ EQUATION MODIFIED BY EXPERIMENT) 3 aH
X=mH
SECTION A-A
PRESSURES FROM POINT LOAD Qp
(BOUSSINESQ EQUATION
MODIFIED BY EXPERIMENT)
Reference: Foundations and Earth Structures,
Design Manual 7.2, Department of the Navy, May 1982 Calculation of Surcharge Loads
on Subsurface Wails
FIGURE 7
Surcharge Load = q (200 psf from construction equipment)
I
5 sa1
Sheet Pile Wall
H
(Ignore resistance at top one foot)
n
a)
0
D
spl sa2 0.3*q
Passive Soil Pressure: Active Soil Pressures: (Surcharge-Induced)
spl = 126*D sal = 175
sa2= 175+ 18*(H+D)
(NOT-TO-SCALE)
Notes:
1. All pressures in pounds per square feet(psf)
2. Passive earth pressure includes a safety factor of 1.5
3. Recommended minimum embedment D= 1.5*(5+H)
4. Hydrostatic pressure on wall will is not shown and will depend on de-watering method.
Figure 8
Lateral Earth Pressures on Cantilevered Sheet Pile Wall
S&EE SW Marshaling Yard, Boeing RentonPlant
Job no. ]309M
Surcharge Load = q(200 psf from construction equipment)
-T-1
5 -
------- ------ ------- ------------------
Sheet Pile Wall sal
H
sa2
a
m (Ignore resistance at top one foot)
S spl
n
a)
0
D
sp2 sa3 0.3*q
(Surcharge-Induced)
Passive Soil Pressures: Active Soil Pressures:
spl = 126*D sal = 114
sa2= 12*H
sa3= 12*H+ 18*D
(NOT-TO-SCALE)
Notes:
1. All pressures in pounds per square feet(psf)
2. Passive earth pressure includes a safety factor of 1.5
3. Hydrostatic pressure on wall is not shown and will depend on de-watering method
Figure 9
Lateral Earth Pressures on Braced Sheet Pile Wall
S&EE SY Marshaling Yard, Boeing RentonPlant
Job no. 1309M
APPENDIX A
FIELD EXPLORATION AND LOGS OF BORINGS
The subsurface conditions at the project site were explored with the drilling of 2 soil test borings, B-1-M
and B-2-M at SW Marshaling Yard. The test borings were advanced using a truck-mounted drill rig. A
representative from S&EE was present throughout the exploration to observe the drilling operations, log -
subsurface soil conditions, obtain soil samples, and to prepare descriptive geologic logs of the
exploration. Soil samples were taken at 2.5- and 5-foot intervals in general accordance with ASTM D-
1586, "Standard Method for Penetration Test and Split-Barrel Sampling of Soils" (1.4" I.D. sampler).
The penetration test involves driving the samplers 18 inches into the ground at the bottom of the borehole
with a 140 pounds hammer dropping 30 inches. The numbers of blows needed for the samplers to
penetrate each 6 inches are recorded and are presented on the boring logs. The sum of the number of
blows required for the second and third 6 inches of penetration is termed "standard penetration resistance"
or the "N-value". In cases where 50 blows are insufficient to advance it through a 6 inches interval the
penetration after 50 blows is recorded. The blow count provides an indication of the density of the
subsoil, and it is used in many empirical geotechnical engineering formulae. The table below provides a
general correlation of blow count with density and consistency. A chart showing the Unified Soil
Classification System is included at the end of this appendix.
DENSITY(GRANULAR SOILS) CONSISTENCY(FINE-GRAINED SOILS)
N-value <4 very loose N-value <2 very soft
5-10 loose 3-4 soft
1 1-30 medium dense 5-8 medium stiff
31-50 dense 9-15 stiff
>50 very dense 16-30 very stiff
>30 hard
Vibrating wire piezometers (VWP) were installed in the borehole of B-2-M shown in table below. The
borehole was backfilled with bentonite-cement grout per VWP manufacturer's instruction. A flush-
mount monument was installed at the ground surface. The borehole without VWP was backfilled with
bentonite chips,and the surface was patched with concrete.
Boring Number VWP Depth Date
(feet) Installed J
B-2-M 15 Oct 4,2013
B-2-M 50 Oct 4,2013
Job No.1309M S&I
a
BORING B-1-M
Surface condition: Parking lot
0
3o is p 18 GWF 2.5 inches thick asphalt pavement over(1-114" minus) recycled concrete
40 ' ; (very dense)(fill)
I
; O
sP Brown and gray, fine to coarse sand with fine to medium gravel
(very dense to medium dense)(moist to damp)(fill)
12 ' 18
20 8 !
20
'
I �
I
6 7 18
12 18 ,
10
5 18e o -sampler tube plugged with medium gravel(no sample collected)
! 5 ; I
10 18 '
1 12
3 ML Gray silt with trace fine sand(soft)
I
sP Gray fine sand(loose)
I �
� I I
I
2 ! 18
8 10 SP Gray fine to coarse sand, trace fine to medium gravel(medium dense to dense)
12
I ' I
' I
! ' I
, I 1
i ' I
I ! I
15! 8 18 1
15, 617,
;
I
' I
1 16 GP Gray fine to medium gravel with few coarse sand (medium dense)
14; 12 s
12
P, •
s
(Boring log continued on Figure A-5b)
' Client: The Boeing Company
Drilling Method: Mud rotary advanced by track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 3,2013
Drilling Contractor: Gregory Drilling Figure A-5a
' SUE
Job No.1309-M Proposed Marshaling Yard
1
„
r
T �
;o a BORING B-1-M '
CO
(Continued)
ti j Surface condition: Parking lot ,
20
a18 • GPi Gray fine to medium gravel with few coarse sand (medium dense)
14
7 ; SPi Inter-bedded, gray,fine sand, silty fine sand and sift,trace organics(loose)
SM
ML
1 18
3 0
31 r,
i
26 ' ; 2 18
4 ' 8
3 ;
3 8 SP Gray, fine to medium sand with lenses of silty fine sand. (medium dense to dense)
i30 i 30 18
18 12
; 14 ;
' ML Grayish brown silt with trace organics. (soft)
1
1'
35; 0 18 '
2 14
i1 1
i
r
1 I �
(Boring log continued on Figure A-5c)
Client: The Boeing Company r
Drilling Method: Mud rotary advanced by track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 3,2013
Drilling Contractor: Gregory Drilling Figure A-5b
SUE 'Job No.1309-M Proposed Marshaling Yard
__ 1
a
w BORING B-1-M
(Continued)
:D Surface condition: Parking lot
40
0 14 ML Gray silt with lenses of gray fine sand and brown peat. (very soft to soft)
o
46 ; 018
1 18
2 ;
50: 018 '
2 18 '2
55, 4 18 ' SM Gray silty fine sand and sandy silt, lenses of brown peat(loose and soft)
3 6
i
4
IT
t '
L so
' II
i
(Boring log continued on Figure A-5d)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 3,2013
Drilling Contractor: Gregory Drilling Figure A-5c
S&EE
Job No.1309-M Proposed Marshaling Yard
a
a�
w BORING B-1-M
(Continued)
CO
N V CO
U) , Surface condition: Parking lot
60
s i 8 i sP Gray fine sand,trace organics. (medum dense)
7
,
66 ; 3 18 -peat lens at 65 feet
s ; 10 , -silt lense at 65.5 feet
8 ,
�Sp Gray fine to coarse fine, trace fine to medium gravel(medium dense)
i
70 a 18 '
12 � 14 ;
-driller report loosing drill mud viscosity
;
75, ; 8 18
i
g 10
80 --1--'--
(Boring log continued on Figure A-5e)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 3,2013
Drilling Contractor: Gregory Drilling Figure A-5d
S&E9- Proposed Marshaling Yard
Job No.1309-M P 9
QT
ivo a a BORING B-1-M
(Continued)
C/)
a' oD " cn j Surface condition: Parking lot
' 80
3 18 sP Gray fine sand,trace organics. (loose)
, 1 3 � I
I 1 i fl
1 1 '
I i 1 I
1 t
� � 1
1 I
I ' I
I I I
I i I I
86; 1 z18
1 14 I
2
I i I
I ' i
ML Gray sandy silt and silty fine sand,trace organics. (medium stiff
I 1
1 1
' 1 1
i
i 1 i
go: 8 1 18
9 18
, g 1
1 1 I
1 I 1
t 1 '
85 t
3 1 18 '
4 18
' I i
I 1 i
I 1 I
1 i '
' I i
I � 1
I , I
I '
' I '
' I '
' I
100--= -'_--
3 18
4 18
3
Boring completed at a depth of 101.5 feet on October 3, 2013.
Client: The Boeing Company
Drilling Method: Mud rotary advanced by track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 3,2013 Figure A-5e
Drilling Contractor: Gregory Drilling
S&EE
Job No.1309-M Proposed Marshaling Yard
U
� w
BORING B-2-M
o� p
p q1 c c co , Surface condition: Parking lot
0
43 , 1s :Z Gw 2.5 inches thick asphalt pavement over(1-1/4" minus)recycled concrete (very dense)(fill)
sora 12 0
Q
sP Brown, fine to coarse sand with fine to medium gravel(medium dense)(moist)(fill)
a ' 18
14 , 18
15 ,
6 '
ML Gray silt with trace organics(soft)
1 19
' 1 19
2
o , 18
1 18 '
� 10
3 i 18 ;
3 ,
,
sP Gray fine sand(loose to medium dense)
s ; 1a '
5 , 0 '
5
15; e 19 ' sP Gray fine to coarse sand,trace fine to medium gravel(medium dense)
10,, a ;
a
s ' 18 GP Gray fine to medium gravel,few fine to coarse sand (medium dense)
j ; s ! SIP
-driller report loosing drill mud
20!--I--'---'
(Boring log continued on Figure A-6b)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date. October 4,2013
Drilling Contractor: Gregory Drilling Figure A-6a
S&E9- Proposed Marshaling Job rlo.l�os-M P g Yard
a BORING B-2-M
(Continued)
z Qco
O UU
m c; coj Surface condition: Parking lot
20 11 18 • GP/ Gray fine to medium gravel with few coarse sand (medium dense)
15 12 i SP
8 ' •
i
1
5 ' 18 ; ••
2 ' 18 2 Mt_ Brownish gray organic silt(soft to medium stiff)
�
25 18
s j a Sp Gray, fine sand with silt lenses, trace fine gravel(medium dense)
5
8 18 '
10 12 '
18
30; a 18
11 12 '
13
ML Grayish brown organic silt(soft)
35, 0 18 '
1 i 8 '
� I ,
40'------'---
----L
(Boring log continued on Figure A-6c)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by track-mount rig
Sampling Method: SPT sampler driven by 140-I1b auto hammer
Drilling Date. October 4,2013
Drilling Contractor: Gregory Drilling Figure A-6b
S&EE Proposed Marshaling Yard
Job No.1309-M p g
a
BORING B-2-M
(Continued)
o rU co
p ap c-Si a> > Surface condition: Parking lot
40
z 18 i ML Gray silt with lenses of gray fine sand and brown peat(soft to medium stiff)
2
:
:
46 1 18
1 18
2
;
;
;
;
;
:
'
50 1 18
3 18
, 9 ,
sP Gray fine sand(medium dense)
Boring completed at a depth of 51.5 feet.
Vibrating wire piezometers(VWP) installed at depths of 15 and 50 feet.
One foot of sand pack installed below and above piezometers.
;
Borehole backfilled with bentonite-cement grout per VWP manufacturer.
55
;
;
60�------'--- --
Client: The Boeing Company
Drilling Method: Mud rotary advanced by track-mount rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: October 4,2013
Drilling Contractor: Gregory Drilling Figure A-6c
S&E9- Proposed Marshaling Yard
Job No.1309-M P 9
'O
d
N
BORING B-3
i N
(O Q Q h
h%
c U) j Surface condition: Palling lot
0
GWI 3 inches thick asphalt pavement over recycled concrete(fill)(moist)(very dense)
41 t8 '
46 t 8
47
5 ' 18 ;
Os;
6 10
5 ML Gray silt with lenses of silty fine sand and fine sand (soft to very soft)
6 3 18SZ
'
i 1
0 i 18
18 '
10; ;
SM Gray silty fine sand with some fine gravel(loose)
0 118 Ills
4 6
7 ; 16 8
14 Sp/ Gray medium to coarse sand and fine to medium gravel(medium dense)
, ,
17 GP
15,
6 18 ;
7 6 ,
7
20:------'--
(Boring log continued on Figure 3b)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by track-mount Diedrich D-120 Drill Rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: February 28 and March 1,2011
Drilling Contractor: Holocene Drilling Figure 3a
S&EE Proposed g
Job No.1104 p sed 4-68 Building
a
m
s
�o a BORING B-3
(Continued)
o m =s c
20 s 18
• �P� Gray fine to medium gravel with few coarse sand (medium dense)
7 4 ,
7 , SID
3 1 18
3 0 ' ML Brown silt with trace very fine sand(medium stiff)
� ,
3
26'
sP Brown to gray to black fine to medium sand with lenses of grayish brown silt
(medium dense)
5 to ;
5 12 ,
7
30, 8 , 18
12 ' 16 ,
� , F
2 ; is ML Grayish brown silt with trace fine sand,trace peat(soft)
2
35
3 t8
s 1a
' sPi Inter-bedded fine to medium sand, silt, and silty fine sand, lenses of brown peat(loose)
'
7 ML/
SM
40:-----'--
(Boring log continued on Figure 3c)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by track-mount Diedrich D-120 Drill Rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: February 28 and March 1,2011
Drilling Contractor: Holocene Drilling Figure 3b
SUE
Job No.1104 Proposed 4$8 Building
a
m
c> t o
m
BORING B-3
a� (Continued)
U me C
40
0 18 ;18 sw Inter-bedded fine to medium sand, silt, and silty fine sand (loose)
7 ML/
SM
46 o 18 i ML Gray silt with trace fine sand, lenses of peat(very soft)
-vane shear reading=0.4 ksf
50
s o sP Gray fine to medium sand with trace silt(loose to medium dense)
s
55 11 18 -medium dense below 55 feet
13 18 ,
15
i
i
(Boring log continued on Figure 3d)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by track-mount Diedrich D-120 Drill Rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: February 28 and March 1,2011
Drilling Contractor: Holocene Drilling Figure 3c
S&E Proposed 4-68 Building
Job No.1104 p g
a
BORING B-3
oa
(Continued)
U
D Q Q. co
60
s 12 sP Gray fine to medium sand with lenses of soft silt(loose to medium dense)
66' 3 118
3 9 I
4
PT Brown non-fibrous peat(soft)
70' j 3 18 -vane shear reading =0.4 ksf
8 18 1
2 ,
I 1 '
ML Gray silt with trace fine to medium gravel(medium stiff
I 1 '
I 1 '
I I '
I I '
sP Gray fine to coarse sand with some fine to medium gravel,trace silt(dense)
I I '
I I '
I I I
I I '
1 1
75 I 18 1 18
'
18 1 12
20
I I '
I I '
1 1 '
I I '
I 1
(Boring log continued on Figure 3e)
Client: The Boeing Company
Drilling Method: Mud rotary advanced by track-mount Diedrich D-120 Drill Rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: February 28 and March 1,2011
Drilling Contractor: Holocene Drilling Figure 3d
S&EE
Job No.1104 Proposed 4-68 Building
b
N
m w
a s BORING B-3
(Continued)
o
&0E n co
U
ao
so.
1a ; ie SP Gray fine to medium sand with some fine to medium gravel,trace silt(dense)
1s +
86' 15 lense of peat at 85 feet
19 ; 1s
90' '
12 18 ; -lense of medium stiff silt at 90 feet
5 12
s
95; 0 18 '
19 ML Gray silt with trace fine sand(very soft to stiff)
-vane shear reading=0.5 ksf
__;-1_! -stiff below 100 feet
a 8 Boring completed at a depth of 100 feet on March 1,2011.
7 A groundwater monitoring well is installed with slotted PVC pipe from depths of
10 to 20 feet. Depth of groundwater measured at a depth of 6 feet 2 inches on
March 2, 2011.
Client: The Boeing Company
Drilling Method: Mud rotary advanced by track-mount Diedrich D-120 Drill Rig
Sampling Method: SPT sampler driven by 140-lb auto hammer
Drilling Date: February 28 and March 1,2011 Figure 3e
Drilling Contractor: Holocene Drilling
Job No.S&E4 Proposed 4-68 Building
UNIFIED SOIL CLASSIFICATION SYSTEM
p
g j DESCRIPTION MAJOR DIVISIONS
GW WELL-GRADED GRAVELS OR GRAVEL-SAND MIXTURES, CLEAN
LITTLE OR NO FINES GRAVELS
• GP POORLY GRADED GRAVELS OR GRAVEL-SAND MIXTURES, (LITTLE OR J a o z w > J
• LITTLE OR NO FINES NO FINES) W 4i o w w m w
�-•._ - -..__-_ -_.— _-. _ _— ._ _ _ > zdS� w> J_
GM ! SILTY GRAVELS,GRAVEL-SAND-SILT GRAVELS LL >
• MIXTURES w w ai v 0 I w
-- -- - - ---------- - ---- WITH FINES C7 I w Wz . W �
GC CLAYEY GRAVELS,GRAVEL-SAND-CLAY (APPRECIABLE U w ' Z
MIXTURES AMOUNT OF FINES) Q O
.----._..----- - --- -- ---- Z
WELL-GRADED SAND OR GRAVELLY SANDS,
SW LITTLE OR NO FINES — —_- CLEAN p Z o N- ' UL 1ZZ
= w w
— ---__-_ - SANDS
C OOR Y-GRADED SANDS OR GRAVELLY SANDS I p z y> of
of ~w �_w
SIP -- - - - --ISANDS I a < Q o" o Y
j SM I SILTY SANDS,SAND SILT MIXTURES Q w U.
w_ N o O ¢z
LITTLE OR NO FINES NO FINES) c� g
1 I 2> U N w
I---- _.._ WITH FINES ! N u' �� WUo
SC CLAYEY SANDS,SAND-CLAY MIXTURES (APPRECIABLE ° LLO p a J
AMOUNT OF FINES)
�— - zm
I
INORGANIC SILTS,VERY FINE SANDS,ROCK FLOUR,SILTY OR z>
°ML CLAYEY FINE SANDS OR CLAYEY SILTS WITH SLIGHT PLASTICITY .w U)
INORGANIC CLAYS OF LOW TO MEDIUM PLASTICITY,GRAVELLY — <y z
CL I CLAYS,SANDY CLAYS,SILTY CLAYS,LEAN CLAYS SILTS &CLAYS O aQ
LIQUID LIMIT LESS THAN 50 U)
ORGANIC SILTS AND ORGANIC SILT-CLAYS OF LOW d w
OL I PLASTICITY zoo ul
INORGANIC SILTS,MICACEOUS OR DIATOMACEOUS FINE Q �z
I MH SANDY OR SILTY SOILS,ELASTIC SILTS z=IMIFCH
INORGANIC CLAYS OF HIGH PLASTICITY,FAT LL1 w SILTS&CLAYS_ LIQUID LIMIT GREATER TITAN 50 p
1 OH ORGANIC CLAYS OF MEDIUM TO HIGH PLASTICITY, i 2.
ORGANIC SILTS
-- - --—
i PT 1 PEAT AND OTHER HIGHLY ORGANIC SOILS HIGHLY ORGANIC SOILS
Non-disturbed D&M Sampler
SPT(1.4"ID SAMPLER)
SHELBY TUBE SAMPLER
DEPTH OF GROUNDWATER DURING EXPLORATION SOIL CLASSIFICATION CHART
AND KEY TO EXPLORATION LOG
S&EE
APPENDIX B
LABORATORY TEST RESULTS
Job No. 1309M S&EL'
Particle Size Distribution Report
o 0 0
o 0 0 0 �0p
100
! i
90
80
70 ! ! I I I I I I I
Z 60
z 50
I 1 1 I I I
UwJ
� 40
I I I I l 1 1 I ! I I 1 !
30
I ! 1 I I I I ! I I I I I !
20
10
o 11 1 I ( I 1 f l ( I I I I I
100 10 1 0.1 0.01 OAol
GRAIN SIZE-mm.
%Gravel %Sand %Fines
Coarse I Medium Fine Silt Clay
0.0 0.0 1 0.1 1 0.2 1 4.9 i 76.7 18.1
SIEVE PERCENT SPEC.' PASS? Material Description
SIZE FINER PERCENT (X=NO) Gray Silty Sand
3/8 100.0
#4 99.9 Moisture:21.1%
#10 99.7
#40 94.8 Atterberg Limits
#60 72.4 PL= LL= PI=
9100 45.7 Coefficients
#200 18.1 D90= 0.3686 D85= 0.3255 D60= 0.1978
D50= 0.1636 030= 0.1039 D15=
D10= Cu= CC=
Classification
USCS= AASHTO=
Remarks
Received: 10115/2013;Tested:10/17/2013
Equipment:53 66 58 141
(no specification provided)
Source of Sample: 1309-M Depth: 10'-11.5'
Sample Number:B-1 Date: 10/18/2013
A.A.R. _ Client: Soil&Enviommental Engineers Inc.
Testing Project: S&EE Lab Misc.
Laboratory, Inc. Project No: 12-343 Figure 13-341
Tested By: Mike Jarbeau Checked By: J. Hoover
Particle Size Distribution Report
C C Q O O
s d \ 6 E. _ o C, e S � o
(p O1 N � =C t0 Vt it 3C iC it ik ik ik iG
"0
I i I I I I I l I I 11 1 1 1
9�
I I II I ! I I I I I I I I I I
80
I I I l i I I I I I I
70
Of
z 60 —
I
50 I I II I I I ( 1 I i I I II
W
� 40
I I ! I I 1 I I I I I I I
30
20 I ! I I I I I I l I I I I
� I
10 IL I
0 I 1 I I I I I I I I I ! I
100 10 1 0.1 0.01 0.001
GRAIN SIZE-mm.
+3" %Gravel %Sand %Fines
--
Coarse Fine Coarse Medium Fine Sik Clay
0.0 ! 2.4 34.9 12.7 29.8 15.0 5.2
SIEVE PERCENT SPEC.* PASS? Material Description
SIZE FINER PERCENT (X=NO) Gray Sand with Gravel
1 100.0
3/4" 97.6 Moisture:9.6%
1/2" 82.2
3/8" 76.8 Atterberg limits
#4 62.7 Pl= LL= P1=
410 50.0 Coefficients
#40 20.2 D90= 15.4953 D85= 13.7596 D80= 4.0636
#60 13.3 D50= 2.0039 D30= 0.7225 D15= 0.2898
4100 8.4 D10= 0.1810 Cu= 22.45 Cc= 0.71
#200 5.2
Classification
USCS= AASHTO=
Remarks
Received: 10/15/2013;Tested: 10/17/2013
Equipment:53 66 58 141
(no specification provided)
Source of Sample: 1309-M Depth: 12.5'-14'
Sample Number: B-1 Date: 1 011 8/20 1 3
Q.A.R. Client: Soil&Enviornmental Engineers Inc.
Testing Project: S&EE Lab Misc.
Laborato Inc. Pro ect No: 12-343 Figure 13-342
Tested By: Mike Jarbeau Checked By:J. Hoover
Particle Size Distribution Report
100
90 - --- --
I
I I I I I I I I I I I I I I I
80
I I I I I I I I t i l l l
70 i I I 11 1 I I I 1 1 1
Z 60 +
LL
z ao I I I I I I I I I I I I
w 1 ! I f ( I
LU 40 I I I I 'I l i I I II I I I . I
30
I I I I I I I 1 I l l i I
20—
I I f I t I I !
10
I I I I I I I I I
o I I ! I I I I I I I I 1 1
100 10 1 0.1 0.01 0.001
GRAIN SIZE-mm.
°b Gravel %Sand _ %Fines
°�+3' Coarse Fine Coarse Medium—�—Fine Silt Clay
0.0 1 33.4 1 38.7 10.6 8.7 4.6 4.0
SIEVE PERCENT SPEC.` PASS? Material Description
SIZE FINER PERCENT (X=Nd) Gray Silty Gravel and Sand
1 1/4 100.0
1 72.7 Moisture:8.7%
3/4 66.6
3/8 42.3 Atterberg Limits
#4 27.9 PL= LL= PI=
#10 17.3 Coefficients
#40 8.6 D90= 29.6145 D85= 28.5349 D60= 14.4639
#60 6.6 D50= 11.4510 D30= 5.5872 D15= 1.5432
#100 1 5.2 D10= 0.6081 Cu= 23.79 Cc= 3.55
#200 4.0 Classification
USCS= GP AASHTO=
Remarks
Received: 10/15/2013;Tested: 10/17/2013
Equipment:53 66 58 141
no specification provided)
Source of Sample: 1309-M Depth: 15'-16.5'
Sample Number:B-1 Date: 10/18/2013
A.A.R. Client: Soil&Enviommental Engineers Inc. ;
Testing Project: S&EE Lab Misc.
Laborator Inc. Project No: 12-343 Figure 13-343
Tested By: Mike Jarbeau Checked By: J. Hoover
Particle Size Distribution Report
100 !
90 �-
�
I I I i 1 1 Ii I I I I I
80
70
I I I I I ! I I I l l l l
zLL
so -
i
50
I I I 1 I
U i 1
o ao
30
i I
20 ( II I I I I I I I I I I I 1
10
I I I I I I I I I I I i l
o I I I I i l l II I I I I I I
100 10 1 0.1 0.01 0.001
GRAIN SIZE-mm.
%Gravel %Sand %Fines
%+3" Coarse Fine Coarse Medium Fine Silt Clay
0.0 0.0 1 0.9 1 8.1 48.4 35. 1 7.3
SIEVE PERCENT SPEC." PASS? Material Description
SIZE FINER PERCENT (X=NO) Gray-Brown Sand
3/8 100.0
#4 99.1 Moisture: 15.6%
#10 91.0
40 42.6 Atterberg_Limits
#
# 0 22. PL= LL= Pl=
#100 11.4 Coefficients
#200 7.3 090= L8861 D85= 1.4881 D60= 0.6603
D50= 0.5093 D30= 0.3132 D15= 0.1890
D10= 0.1307 Cu= 5.05 Cc= 1.14
Classification
uSCS= AASHTO=
Remarks
Received: 10/15/2013,Tested: 10/17/2013
Equipment:53 66 58 141
(no specification provided)
Source of Sample: 1309-M Depth: 30'-30.5'
Sample Number:B-1 Date: 10/18/2013
A.A.R. Client: Soil&Enviornmental Engineers Inc.
Testing Project: S&EE Lab Misc.
Laborato Inc. Project No: 12-343 Figure 13-344
Tested By: Mike Jarbeau Checked By: J. Hoover
LIQUID AND PLASTIC LIMITS TEST REPORT
Dashed line indicates the approximate
upper limit boundary for natural soils /
50
/
/
/
X40 —
w
o /
z /
U 30
H /
dJ /
/ O
a 20
/ OV
/
/
10
_ `' ML or OL N1H it OH
0 •
0 10 20 30 40 50 60 70 80 90 100 110
LIQUID LIMIT
33.9
33.7 f
i
33.5 - -
33.3
w 33.1
Z 832.9
32.7
32.5
32.3
32.1 I
31.9 Lr
5 6 7 8 9 10 20 25 30 40
NUMBER OF BLOWS
MATERIAL DESCRIPTION LL PL Pi %<#40 %<#200 USCS 1
Gray Silt
� 32 30 2
Moisture:31.7%
Project No. 12-343 Client: Soil&Enviommental Engineers Inc. Remarks:
Project: S&EE Lab Misc.
•Received:10/15/2013
Tested: 10/17/2013
Source of Sample: 1309-M Depth:45' Equipment:66 82-2 52 53
Sample Number:B-i
A.A.R. Testing Laboratory, incdl Figure 13.349
Tested By: J. Hoover— Checked By: J_Hoover _ _`
LIQUID AND PLASTIC LIMITS TEST REPORT
120
Dashed line indicates the approximate
upper limit boundary for natural soils
100
,
/
x 80 /
w
Q /
z � "
U 60 /
H �
g
� 40
/
,
/ 0-
OS
20
/ I
MLor OL 11 Hof OH •
0
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 160 170 180 190 200
LIQUID LIMIT
190
180 � - -_-
170
l� 160 i
H150
z
140
Cr
uJ
130
120
110
100
90
5 6 7 8 9 10 20 25 30 40
NUMBER OF BLOWS
MATERIAL DESCRIPTION LL PL PI %<#40 %0200 USCS
Gray Silty Clay
0 156 153 3
Moisture:63.2%
Project No. 12-343 Client: Soil&Enviommental Engineers Inc. Remarks:
Project: S&EE Lab Misc. 1•Received: 10/15/2013
Tested: 10/17/2013
Source of Sample: 1309-M Depth:95' Equipment:66$2-2 52 53
Sample Number:B-1
A.A.R. Testing Laboratory, I�C, Figure 13.350 >>
Tested By: J. Hoover Checked By:J.Hoover
Particle Size Distribution Report
�J N gig
�O M N •- .— � :Q t3 it ak A it it � � 7k iR
100
I I I I I I I I I I I I I I
90
I ! I I 1 I I I I I I I E
I I I I I I I I ( I I I I II
80
70 I I I I I I
( I I I ! I I I I I ( I I
w I I ( I I I f I I l l l
Z 60
z 60
I ! I I I I I I ! I I I ! I
�
v I E I i l l l I I I I I I
w 40
I I I I I I I I I I I I I
30
20
10
I I I I I I I I I
100 10 1 0.1 0.01 0.001
GRAIN SIZE-mm.
%+r %Gravel %Sand %Fines
Coarse Fine Coarse: Medium Fine Silt Clay
0.0 0.0! 38.1 14.7 28.5 I4.I 4.6
SIEVE PERCENT SPEC.` PASS? Material Description
SIZE FINER PERCENT (X=NO) Gray Sand and Gravel
3/4 100.0
3/8 80.5 Moisture:9.2%
#4 61.9 Atterberg Limits
#10 471 PL= LL= PI=
#40 18.7
#60 12.6 Coefficients
#100 7.4 D90= 13.3263 D85= 11.1632 D60= 4.3297 -
#200 4.6 D50= 2.3842 DgO= 0.8207 Q15= 0.3120
13 0= 0.1966 Cu= 22.02 Cc= 0.79
Classification
USCS= SP AASHTO=
1
Remarks
Received: 1 0/1 5120 1 3;Tested:10/17/2013 -
Equipment:53 66 58 141 I
(no specification provided)
Source of Sample: 1309-M Depth: 15'-16.5'
Sample Number:B-2 Date: 10/18/2013
A.A.R. Client: Soil&Enviornmental Engineers Inc.
Testing Project: S&EE Lab Misc.
Laboratory, Inc. Project No: 12-343 Figure 13-345
Tested By: We Jarbeau Checked By:J. Hoover
Particle Size Distribution Report
O O O
C,
N
cp M N � n � � it i[ ik ii iC it iR ik
100
90
I I C I I ! I ! ! ! I I I I I
80
70
Z 60 - —
,� I ! I ( I I I ( ! I ! II
Z 50
I I
d 40 I I� I I II I I I I I I I I I I II
30 .1
20
10
I ! I I I ! I I I I i i
o I l i I I I I I I i I I I I
T-1
100 10 1 0.1 0.01 0.001
GRAIN SIZE-mm.
°h Gravel %Sand %Fines
%+3" _ — — —
Coarse Fine Coarse Medium Fine Silt Clay
0.0 0.0 0.2 7.5 51.3 1 35.6 5.4
SIEVE PERCENT SPEC.` PASS? Material Description
SIZE FINER PERCENT (X=NQ) Gray Sand
3/8 100.0
#4 99.8 Moisture: 17.3%
#10 92.3
#40 41.0 Atterbem Limits
#60 24.4 PL= LL= PI=
#100 10.9 Coefficients
#200 5.4 D90= 1.7993 D86= 1.4802 D60= 0.7148
D60= 0.5470 D30= 0.3006 D15= 0.1801
D10= 0.1424 Cu= 5.02 Cc= 0.89
Classification
USCS= AASHTO=
Remarks
Received: 10/1512013,Tested: 10/17/2013
Equipment:53 66 58 141
(no specification provided)
Source of Sample: 1309-M Depth: 27.5'-29'
Sample Number: B-2 Date: 10/18/2013
-----
A.A.R. Client: Soil&Enviornmental Engineers Inc.
i
Testing Project: S&EE Lab Misc.
Laborato Inc. Project Na: 12-343 Figure 13-346
Tested By: Mike Jarbeau Checked By:J. Hoover
rza LIQUID AND PLASTIC LIMITS TEST REPORT
—�
Dashed line indicates the approximate
zapper limit boundary for natural soils
100 �
°c
X 80
w
Z � 1
60
CJ �
J i
d 40
'0
—
i
i
20
u° o�
ML or OL MH Or OH
0
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 160 170 180 190 200
LIQUID LIMIT
118 •
116
z
----
0 108
w
im
104
102
100 —
98
5 6 7 8 9 10 20 25 30 40
NUMBER OF BLOWS
MATERIAL DESCRIPTION LL PL PI %<940 %<#200 USCS
Gray Sandy Silt
• 115 102 13
Moisture:61.8%
Project No. 12-343 Client: Soil&Enviommental Engineers Inc. Remarks:
Project: S&EE Lab Misc.
•Received: 10/15/2013
Tested: 10/17/2013
Source of Sample: 1309-M Depth: 35' Equipment:66 82-2 52 53
Sample Number:B-2 +
A.A.R. Testing Laboratory, Inc. Figure 13-348
Tested By: J. Hoover Checked By: J. Hoover
Technical Information Report
Renton Site Logistics
Renton, Washington
Appendix F
Stormwater Pollution Prevention Plan
(was previously provided under separate cover; SWPPP shall
be maintained on construction site at all times)
Technical Information Report
Renton Site Logistics
Renton, Washington
Appendix G
Forms
Site Improvement Bond Quantity Worksheet S15 Webdate: �,_.z2/2013
King County
Department of Permitting & Environmental Review
35030 SE Douglas Street, Suite 210
Snoqualmie, Washington 98065-9266 For alternate formats, call 206-296-6600.
206-296-6600 M Relay 711
Project Name: SW Marshaling Yard Date: 3-Mar-14
Location: Boeing Company Renton Site Project No.:
Activity No.:
Note: All prices include labor, equipment, materials, overhead and
Clearing greater than or equal to 5,000 board feet of timber? profit. Prices are from RS Means data adjusted for the Seattle area
or from local sources if not included in the RS Means database.
yes _X no
If yes,
Forest Practice Permit Number:
(RCW 76.09)
Page 1 of 9
Unit prices updated: 02/12/02
Version: 11/26/2008
2014_0303_Bondgty.xls NPDES Permit has been issued directly by Ecology. Report Date: 3/5/2014
Site Improvement Bond Quantity Worksheet VV`'"`'ikl `212013
Unit #of
Reference#t Price Unit Quantity Applications Cost
EROSION/SEDIMENT CONTROL Number
Backfill &compaction-embankment ESC-1 $ 5.62 CY
Check dams,4"minus rock ESC-2 SWDM 5.4.6.3 $ 67.51 Each
Crushed surfacing 1 1/4"minus ESC-3 WSDOT 9-03.9(3) $ 85.45 CY
Ditching ESC-4 $ 8.08 CY
Excavation-bulk ESC-5 $ 1.50 CY
Fence, silt ESC-6 SWDM 5.4.3.1 $ 1.38 LF
Fence,Temporary(NGPE) ESC-7 $ 1.38 LF
Hydroseeding ESC-8 SWDM 5.4.2.4 $ 0.59 SY
Jute Mesh ESC-9 SWDM 5.4.2.2 $ 1.45 SY
Mulch, by hand, straw, 3"deep ESC-10 SWDM 5.4.2.1 $ 2.01 SY
Mulch, by machine, straw,2"deep ESC-11 SWDM 5.4.2.1 $ 0.53 SY
Piping, temporary, CPP,6" ESC-12 $ 10.70 LF
Piping,temporary, CPP,8" ESC-13 $ 16.10 LF
Piping, temporary, CPP, 12" ESC-14 $ 20.70 LF
Plastic covering, 6mm thick, sandbagged ESC-15 SWDM 5.4.2.3 $ 2.30 SY
Rip Rap, machine placed; slopes ESC-16 WSDOT 9-13.1(2) $ 39.08 CY
Rock Construction Entrance, 50'xl5'x1' ESC-17 SWDM 5.4.4.1 $ 1,464,34 Each
Rock Construction Entrance, 100'x15'x1' ESC-18 SWDM 5.4.4.1 $ 2,928.68 Each
Sediment pond riser assembly ESC-19 SWDM 5.4.5.2 $ 1,949.38 Each
Sediment trap, 5' high berm ESC-20 SWDM 5.4.5.1 $ 17.91 LF
Sed.trap.5'high,riprapped spillway berm section ESC-21 SWDM 5.4.5.1 $ 68.54 LF
Seeding,by hand ESC-22 SWDM 5.4.2.4 $ 0.51 SY
Sodding, 1"deep, level ground ESC-23 SWDM 5.4.2.5 $ 6.03 SY
Sodding, 1"deep, sloped ground ESC-24 SWDM 5.4.2.5 $ 7.45 SY
TESC Supervisor ESC-25 $ 74.75 FIR
Water truck, dust control ESC-26 SWDM 5.4.7 $ 97.75 HR
WRITE-IN-ITEMS **** (see page 9)
Each
ESC SUBTOTAL: $
30%CONTINGENCY& MOBILIZATION: $
ESC TOTAL: $ —
COLUMN: A
Page 2 of 9
Unit prices updated: 02/12/02
Version: 11/26/2008
2014_0303_Bondgty.xls NPDES Permit has been issued directly by Ecology. Report Date: 3/5/2014
Site Improvement Bo ' Quantity Worksheet Web date: '1102/2008
Existing Future Public Private Quantity Completed
Right-of-Way Right of Way Improvements (Bond Reduction)`
&Drainage Facilities Quant.
Unit Price Unit Quant. Cost Quant, Cost Quant. Cost Complete Cost
GENERAL ITEMS No.
Backfill&Compaction-embankment GI-1 $ 5.62 CY
Backfill&Compaction-trench GI-2 $ 8.53 CY 1400 11,942.00
Clear/Remove Brush,by hand GI-3 $ 0,36 SY
Clearin /Grubbin /Tree Removal GI-4 $ 8,876.16 Acre
Excavation-bulk GI-5 $ 1.50 CY 3000 4,500.00
Excavation-Trench GI-6 $ 4.06 CY 1400 5.684,00
Fencing,cedar.6'high GI-7 $ 18.55 LF
Fencing,chain link,vinyl coated, 6'hi h GI-8 $ 13.44 LF
Fencing,chain link,gate,vinyl coated, 2 GI-9 $ 1,271.81 Each
Fencing,split rail.Thigh GI-10 $ 12.12 LF
Fill&compact-common barrow GI-11 $ 22,57 CY
Fill&compact-gravel base GI-12 $ 25A8 CY 3021 76,975.08
Fill&compact-screened topsoil GI- 13 $ 37.85 CY
Gabion, 12"deep,stone filled mesh GI-14 $ 54,31 SY
Gabion. 18"deep,stone filled mesh GI-15 $ 74.85 SY
Gabion,36"deep,stone filled mesh GI-16 $ 132.48 SY
Grading,fine,by hand GI-17 $ 2.02 SY
Grading,fine,with grader GI-18 $ 0.95 SY 3000 2,850.00
Monuments,3'long GI-19 $ 135.13 Each
Sensitive Areas Sin GI-20 $ 2.88 Each
Sodding, 1"deep,sloped ground GI-21 $ 7.46 SY
Surveying,fine&grade GI-22 $ 788.26 Day 40 31,530.40
Surveying,lot location/lines GI-23 $ 1,556.64 Acre
Traffic control crew(2 fla gers) GI-24 $ 85.18 HR
Trail,4"chipped wood GI-25 $ 7.59 SY
Trail,4"crushed cinder GI-26 $ 8.33 SY
Trail,4"top course GI-27 $ 8.19 SY
Wall,retaining,concrete GI-28 $ 44.16 SF
Wall,rockery GI-29 $ 9.49 SF
Page 3 of 9 SUBTOTAL 133,481,48
Unit prices updated: 02/12/02
`KCC 27A authorizes only one bond reduction. Version: 11/26/08
2014 0303_Bondgty.xls Report Date: 3/5/2014
Site Improvement Bo ' Quantity Worksheet web date "102!2008
Existing Future Public Private Bond Reduction"
Right-of-way Right of Way Improvements
&Drainage Facilities Quant.
Unit Price Unit Quant. Cost Quant. Cost Quant Cost Completel Cost
ROAD IMPROVEMENT No.
AC Grinding.4'wide machine< 1000s RI-1 $ 28.00 SY
AC Grinding,4'wide machine 1000-200 RI-2 $ 15.00 SY 1910 28,650.00
AC Grinding,4'wide machine>2000sy RI-3 $ 7.00 SY
AC Removal/Disposal/Repair RI-4 $ 67.50 SY 50 3,375.00
Barricade,type I RI-5 $ 30.03 LF
Barricade,type III(Permanent) RI-6 $ 45,05 LF
Curb&Gutter,rolled RI-7 $ 17.00 LF
Curb&Gutter,vertical RI-8 $ 12,50 LF
Curb and Gutter,derolition and disposa RI-9 $ 18.00 LF
Curb,extruded asphalt RI-10 $ 5.50 LF
Curb.extruded concrete RI-11 $ 7.00 LF
SawCUt,asphalt,3"depth RI-12 $ 1.85 LF 1750 3,237.50
Sawcut,concrete,per 1"depth RI-13 $ 1,69 LF
Sealant,asphalt RI-14 $ 1,25 LF 1 1750 2,187.50
Shoulder,AC, (see AC road unit price) RI-15 $ - SY
Shoulder,gravel,4"thick RI- 16 $ 15.00 SY
Sidewalk,4"thick RI-17 $ 35,00 SY 30 1,050.00
Sidewalk,4"thick,demolition and dispos RI-18 $ 29.50 SY
Sidewalk,5"thick RI-19 $ 38.50 SY
Sidewalk,5"thick.demolition and dispos RI-20 $ 37.50 SY
Sign,handicap RI-21 $ 85.28 Each
Striping,per stall RI-22 $ 5.82 Each
Striping,thermoplastic,(for crosswalk) RI-23 $ 2,38 SF 700 1,666.00
Striping.4"reflectorized line RI-24 $ 0,25 LF 19401 485.00
Page 4 of 9 SUBTOTAL 40,651.00
Unit prices updated: 02/12/02
'KCC 27A authorizes only one bond reduction. Version: 11/26/08
2014 03o3_Bondgty.xls Report Date:3/5/2014
Site Improvement Bo ' Quantity Worksheet Web date: "'r0212008
Existing Future Public Private Bond Reduction'
Right-of-way Right of Way Improvements
&Drainage Facilities Quant.
Unit Price IUnit Quant. Cost Quant. I Cost Quant. Cost Complete Cost
ROAD SURFACING (4"Rock=2.5 base&1.5"top course) For'93 KCRS(6.5"Rock=5"base&1.5"top course)
For KCRS'93.(additional 2.5"base)add RS-1 $ 3.60 SY
AC Overlay.1.5"AC RS-2 $ 11.25 SY
AC Overrla ,2"AC RS-3 $ 15,00 SY 1283 19,245.00
AC Road,2",4"rock,First 2500 SY RS-4 $ 21.00 SY
AC Road,2",4"rock,Oty.over 2500SY RS-5 $ 19.00 SY
AC Road.3",4"rock,First 2500 SY RS-6 $ 23.30 SY
AC Road,3",4"rock,Qty.over 2500 SY RS-7 $ 21,00 SY
AC Road,5".First 2500 SY RS-8 $ 27.60 SY
AC Road,5",Oty.Over 2500 SY RS-9 $ 25.00 SY 7780 194,500.00
AC Road,6",First 2500 SY RS-1 $ 33.10 SY
AC Road,6".Oty.Over 2500 SY RS-11 $ 30.00 SY
Asphalt Treated Base,4"thick RS-12 $ 20.00 SY
Gravel Road,4"rock,First 2500 SY RS-1 $ 15.00 SY
Gravel Road,4"rock,Oty.over 2500 SY RS-1 $ 8.50 SY
PCC Road,5",no base,over 2500 SY RS-1 $ 27.00 SY
PCC Road, 6",no base,over 2500 SY RS-1 $ 25.50 SY
Thickened Edge RS-1 $ 8,60 LF
Page 5 of 9 SUBTOTAL 213,745.00
Unit prices updated: 02/12/02
`KCC 27A authorizes only one frond reduction. Version: 11/26/08
2014_0303_Bondgty.xis Report Date:3/5/2014
Site Improvement Bo Quantity Worksheet Web date: "f02/2008
Existing Future Public Private Bond Reduction'
Right-of-way Right of Way Improvements
&Drainage Facilities Quant.
Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Complete Cost
DRAINAGE (CPP=Corrugated Plastic Pipe,N12 or Equivalent) For Culvert prices, Average of 4'cover was assumed.Assume perforated PVC is same price as solid pipe.
Access Road,R/D D-1 $ 21.00 1 SY
Bollards-fixed D-2 $ 240.74 Each
Bollards-removable D-3 $ 452.34 Each 1 211 9,499.14
(CBs include frame and lid)
CB Type I D-4 $ 1,257.64 Each 10 12,576A0
CB Type IL D-5 $ 1.433.59 Each 1 1.433.59
CB Type 11,48"diameter D-6 $ 2,033.57 Each
for additional depth over 4' D-7 $ 436.52 FT
CB Type 11,54"diameter D-8 $ 2,192,54 Each
for additional depth over 4' D-9 $ 486.53 FT
CB Type 11,60"diameter D-10 $ 2,351.52 Each
for additional depth over 4' D- 11 $ 536.54 FT
CB Type 11,72"diameter D- 12 $ 3,212.64 Each 7 22,488.48
for additional depth over 4' D-13 $ 692.21 FT
Through-curb Inlet Framework(Add) D-14 $ 366.09 Each
Cleanout,PVC,4" D-15 $ 130.55 Each
Cleanout,PVC,6" D-16 $ 174.90 Each 6 1,049.40
Cleanout,PVC,8" D-17 $ 224,19 Each 2 448.38
Culvert,PVC,4" D-18 $ 8.64 LF
Culvert,PVC,6" D-19 $ 12,60 LF 314 3,956.40
Culvert,PVC, 8" D-20 $ 13.33 LF
Culvert.PVC,12" D-21 $ 21,77 LF
Culvert,CMP,8" D-22 $ 17.25 LF
Culvert,CMP,12" D-23 $ 26.45 LF
Culvert,CMP, 15' D-24 $ 32.73 LF
Culvert,CMP, 18" D-25 $ 37.74 LF
Culvert,CMP,24" D-26 $ 53.33 LF
Culvert,CMP,30" D-27 $ 71.45 LF
Culvert,CMP,36" D-28 $ 112.11 LF
Culvert,CMP,48" D-29 $ 140.83 LF
Culvert,CMP,60" D-30 $ 235.45 LF
Culvert.CMP,72" D-31 $ 302.58 LF
Page 6 of 9 SUBTOTAL 51,451.79
Unit prices updated: 02/12/02
'KCC 27A authorizes only one bond reduction. Version: 11/26/08
2014.0303__Bondgty.xls Report Date: 3/5/2014
Site Improvement Bo Quantity Worksheet Web date '110212008
Existing Future Public Private Bond Reduction*
Right-of-way Right of Way Improvements
DRAINAGE CONTINUED &Drainage Facilities Quant.
No. Unit Price Unit Quant. Cost Quant.7-Cost Quant. Cost Complete Cost
Culvert,Concrete,8" D-32 $ 21.02 LF
Culvert,Concrete, 12" D-33 $ 30.05 LF
Culvert,Concrete, 15" D-34 $ 37.34 LF
Culvert,Concrete, 18" D-35 $ 44.51 LF
Culvert,Concrete,24" D-36 $ 61.07 LF
Culvert,Concrete,30" D-371 $ 104.18 LF
Culvert.Concrete,36" D-38 $ 137.63 LF
Culvert,Concrete,42" D-39 $ 158.42 LF
Culvert,Concrete,48" D-40 $ 175.94 LF
Culvert,CPP,6" D-41 $ 10.70 LF
Culvert,CPP,8" D-42 $ 16.10 LF
Culvert,CPP, 12" D-431 $ 20.70 LF 619 128113
Culvert,CPP, 15" D-44 $ 2100 LF
Culvert,CPP, 18" D-45 $ 27.60 LF 102 2815.2
Culvert,CPP,24" D-46 $ 36.80 LF 13 478.4
Culvert,CPP,30" D-47 $ 48.30 LF
Culvert.CPP,36" D-48 $ 55.20 LF
Ditching D-491 $ 8.08 CY
Flow Dispersal Trench (1,436 base+) D-50 $ 25,99 LF
French Drain (3'depth) D-51 $ 22.60 LF
Geotextile,laid in trench,polypropylene D-52 $ 2.40 SY
Infiltration pond testing D-53 $ 74.75 HR
Mid-tank Access Riser,48"dia, 6'deep D-54 $ 1.605A0 Each
Pond Overflow Spillway D-551 $ 14.01 SY I
Restrictor/Oil Separator,12" D-561 $ 1,045.19 Each
Restrictor/Oil Separator.15" D-571 $ 1,095.56 Each
Restrictor/Oil Separator, 18" D-58 $ 1,146.16 Each
Riprap,placed D-59 $ 39.08 CY
Tank End Reducer(36"diameter) D-60 $ 1,000.50 Each
Trash Rack,12" D-61 $ 211.97 Each
Trash Rack,15" D-62 $ 237.27 Each
Trash Rack,18" D-63 $ 268,89 Each
Trash Rack,21" 1 D-641 $ 306.84 Each
Page 7 of 9 SUBTOTAL 16106.9
Unit prices updated: 02/12/02
*KCC 27A authorizes only one bond reduction Version: 11/26/08
2014110303-Bondqty.xis Report Date:3/5/2014
Site Improvement Bo ' Quantity Worksheet Web date: I`t0212008
Existing Future Public Private Bond Reduction"
Right-of-way Right of Way Improvements
&Drainage Facilities Quant.
Unit Price Unit Quant. Price Quant. Cost Quant. Cost Complete Cost
PARKING LOT SURFACING
No.
2"AC.2"tap course rock&4"borrow PL-1 $ 21.00 SY
2"AC, 1.5" top course&2.5"base cour PL-2 $ 28.00 SY
4"select borrow PL-3 $ 4.55 SY
1.5-top course rock&2.5"base course PL-4 $ 11.41 SY
UTILITY POLES & STREET LIGHTING Utility pole relocation costs must be accompanied by Franchise Utility's Cost Statement
Utility Pole(s)Relocation UP-1 Lurnp Sum
Street Light Poles w/Luminaires UP-2 Each
WRITE-IN-ITEMS
(Such as detention/water quality vaults.) No.
Water Quality Vault W I- 1 J ###f#F#### Each 1 150000
Pretreatment Manhole WI-2 $20,000.00 Each 1 20000
Flow Splitler WI-3 $16,000.00 Each 1 16000
Pump Station W I-41 #########t Each 1 130000
Oil/Water Separator W I-5 $12.000,00 Each 1 12000
WI-6
WI-7
WI-8
WI-9
Wi-10
SUBTOTAL 328,000.00
SUBTOTAL(SUM ALL PAGES): 783.436.17
30%CONTINGENCY&MOBILIZATION: 235,030.85
GRANDTOTAL: 1,018,467.02
COLUMN: B C D E
Page 8 of 9
Unit prices updated: 02/12/02
'KCC 27A authorizes only one bond reduction. Version: 1 1126/08
2014 0303 Bondgty.xls Report Date:3/5/2014
! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !
Site Improvement Bond Quantity Worksheet Web date: 12/02/2008
Original bond computations prepared by:
Name: Date:
PE Registration Number: Tel.#:
Firm Name:
Address: Project No:
ROAD IMPROVEMENTS&DRAINAGE FACILITIES FINANCIAL GUARANTEE REQUIREMENTS
PERFORMANCE BOND' PUBLIC ROAD&DRAINAGE
AMOUNT BOND'AMOUNT MAINTENANCE/DEFECT BOND'
REQUIRED AT RECORDING OR
Stabilization/Erosion Sediment Control(ESC) (A) $ - TEMPORARY OCCUPANCY""
Existing Right-of-Way Improvements (B) $ 1,018,467.0
Future Public Right of Way&Drainage Facilities (C) $
Private Improvements (D) $
Calculated Quantity Completed (E) $ -
Total Right-of Way and/or Site Restoration Bond'/" (A+B) $ 1,018,467.0
(First$7,500 of bond'shall be cash.)
Performance Bond`Amount (A+B+C+D) = TOTAL (T) $ 1,018,467.0 T x 0.30 $ 305,540.1 OR
Minimum on amount is$2000.
Reduced Performance Bond'Total"" (T-E) $ 1,018,467.0
Use larger of Tx30%or (B+C)x
Maintenance/Defect Bond"Total 0.25= $ 254,616.8
NAME OF PERSON PREPARING BOND'REDUCTION: •� L�n�dh Date: 313 ZZ01+ —
NOTE: The word"bond"as used in this document means a financial guarantee acceptable to King County.
*'NOTE: KCC 27A authorizes right of way and site restoration bonds to be combined when both are required.
The restoration requirement shall include the total cost for all TESC as a minimum,not a maximum. In addition,corrective work,both on-and off-site needs to be included.
Quantities shall reflect worse case scenarios not just minimum requirements. For example,if a salmonid stream may be damaged,some estimated costs for restoration
needs to be reflected in this amount. The 30%contingency and mobilization costs are computed in this quantity.
"*NOTE: Per KCC 27A,total bond amounts remaining after reduction shall not be less than 30%of the original amount(T)or as revised by major design changes.
REQUIRED BOND'AMOUNTS ARE SUBJECT TO REVIEW AND MODIFICATION BY DDES
Page 9 of 9 Unit prices updated: 02/12/02
Check out the DDES Web site at www.kingcounty.goy/permits Version: 11/26/08
2014_0303_Bondgty.xls Report Date: 3/5/2014
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
STORMWATER FACILITY SUMMARY SHEET DDES Permit
Number
(provide one Stormwater Facility Summary Sheet per Natural Discharge Location)
Overview:
Project Name
Date
r�
Downstream Drainage Basins '
Major Basin Name
Immediate Basin Name d OZ
Flow Control: NpA/1,- i
Flo Control Facility Name/Number
Facility
Location
If none,
Flow controvided in regional/shared f cility(give
location) pr
No flow contro required Exemption number
General Facility Information:
Type/Number of detention facilit s: Type/Number of infiltration facilities: i
ponds ponds
vaults tanks
tanks trenches
Control Structure Location
Type of Control Struc e _ Number of Orifices/Restrictions
Size of Orifice/R triction: No. 1
No.2
No. 3
No.4
Flow Co of Performance Standard
2009 Surface Water Design Manual 1/92009 t
1
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
Live Storag olume Depth Vo,tine Factor of Safety
Number of Acres Sery
Number of Lots
- Dam Safety Regulations(Washington tate De 4-tment of Ecology)
Reservoir Volume above natur 1 gr de
Depth of Reservoir above al gra
17
Facility Summary Sheet Skpt6h
All detention,infilt ion and water quality facil\musta detailed sketch.
(11"xl 7"reduc size plan sheets maybe used)
2009 Surface Water Design Manual 1/9/2009
2
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
Water Quality:
Type/Number of water quality facilitiesBMPs:
biofiltration swale sand filter(basic or large)
(regular/wet/or continuous inflow) sand filter,linear(basic or
large)
combined detention/wetpond sand filter vault(basic or
large)
(wetpond portion basic or large) sand bed depth (inches)
combined detention/wetvault stormwater wetland
filter strip _storm filter
flow dispersion wetpond(basic or large)
farm management plan wetvault
landscape management plan Is facility Lined?
oil/water separator If so,what marker is used
above
(baffle or coalescing plate)
Liner?
catch basin inserts:
Manufacturer 0,per t
pre-settling pond
pre-settling structure:
Manufacturer CaD-tW k
_<high flow bypass structure(e.g.,flow-splitter catch basin)
source controls
Design Information
Water Quality design flow A
Water Quality treated volume(sandfilter)
Water Quality storage volume(wetpool)
Facility Summary Sheet Sketch
2009 Surface Water Design Manual 1/9/2009
3
STORM LINE A LAT /.� -
I, 21. STORM UNE A � MATCH EX. LEGEND
__ :�. '� /� - ,P� ■ PROPOSED CATCH BASIN
SDMH 595A-14 F _ ISD,MH 595X CB TYPE W ( -�- PROPOSED STORM LINE NEW CB TYPE II-48 8 -A- PROPOSED COMPRESSED AIR UNE
W/SOLID LOCKING LID NEW CB TYPE 11-48
_ - W/SOLID LOCKING LID /
_ - N 183670.40 N 183673.77 - -CIA- PROPOSED DOMESTIC WATER LINE
E 7299580-17 / -
/� TOP 20.26 E 1299606.25
_ - -SAN- PROPOSED SANITARY SEWER UNE
IE NW 16.02 12'HOPE TOP 19.85 �*
a = - OWS _ IE E 16.02 `SYSS IE N 16.17 POLE MOUNTED LIGHT(SEE ELECTRICAL PLANS)
`- IE HE 16.17
_ - E 1299549.65 - IE w 15.89 .,
o - _ SURFACE MOUNTED LIGHT(SEE ELECTRICAL PLANS)
TOP 21.28 11V: i N IE,:5 15.90 r - T SE WJS
IE W 15.67 MATCH EX. IE E 15.67 -
9 N
' - _. .,
ter,
6 GENERAL L,IO c�
ELEVATIONS O S SHOWN ARE AT FINAL GRADE.SEE SHEET
3
SANITARY LINE A - C524-A NPROVDE SMOOTH TRANSITION TO EXISTING
_
PAVEMENT CONSTRUCTION.AND T NEWLY INSTALLED STRUCTURES
DURING
N�
N
c� \. 21.00 qNG ', r�- � SEE FOR THRUST BLOCKING DETAIL '
-- 24,1
N 1 J633.79 NII 2� SEE Es FOR SANITARY SEWER CLEANOUT
E 1299520.63 - -
'O TOP 20.34
Ca nPe-14 _ IE w 15.9s gpN �" � "/ CONSTRUCTION NOTES
yy - -
7 J - IE E 15.95 6. .�.'��
_ N 183610.60 - -- J --
el-',-' CB 4A-17 e ° CB 594A-14 -- 1 PROTECT EXISTING 24'RCP CONNECTION TO WEIR STRUCTURE.
�E 1299435.15 CB TYPE
-TOP 20.11 ,-'' ° REPLACE EX.CB TYPE SEE SHEET C524-C FOR PROFILE.
N 129947.3 - W NEW CB TYPE IL /
IE E 15.97(IX 12") E 1299472.35 TTARY UNE A - 21.00 N 183631 56 � SEE SHEET C524-C FOR STORM SEWER PROFILES.PROVIDE STORM
U ,
I�S 15.97 �`.. TOP 20.50 -,. `1 TE01299617.65
P298 65 5 �. SEWER PIPE MATERIAL AS SHOWN,
6
MATCH EX, IE E 16.45 6 b _ - ,-' _ �� 1
a, IE N 15,74 DD:_ SEE SHEET C524-0 FOR SANITARY SEWER PROFILES.PROVIDE
MATCH " ■ -'- e� j y IE S 15,74 /. SANITARY SEWER PIPE MATERIAL AS SHOWN.
.20.Ot '� ® REMOVE EXISTING PIPE PENETRATION FROM MANHOLE OR CATCH
(TYPE 'O �� RM BASIN AND CORE DRILL NEW PIPE PENETRATION.INSTALL
AEI j PPE-N-SEAL BOOT FOR WATERTIGHT CONNECTION TO PROPOSED
PLUG EXISTING STORM LINE AT CATCH BASIN
S
�C
EEE=21 .00
�q RECONNECT EXISTING STORMRA PROPOSED
P
6 . ' --' ,-' USE PIPE STUBOF SIMILAR MATERIAL AND STAINLESS STRUCTURE.
c
' SANITARY UNE B
i�
s i
i� FERNCO COUPUN WITHTSHFAR BANDS IF NECESSARY TO EXTEND
SDMH 594-14 AND MODIFY EXISTING 5
REPLACE IX CB TYPE I
NEW CB TYPE II-48 ----- ORAL DRAIN
PROVIDE SOLID LOCKING LID _ ,� PROVIDE TYPE I CATCH BASIN PER WS OT 51D LAN 520-01
\$ N 18359891 SDMH 5938 ADD FISH AN NOT DUMP STENCIL.WELD OR STAMP
E 1299627.28 -�• IE W 15 49 �.�i STRUCTURE ONTO LIDO
V 7 D P 8
f TOP 20.00 ya E CAC BASIN SOUD LID PE t, N T N 0.00 - '� i ® PROVIDE TYPE II CATCH IN WITHR WBDOT STD
2 sroRM uNE s RIM o, ,,' BUILDING 4-51 21.00 ,
I_f= �� �U �� STENCIL.WELD OR STAMP ISTRUCTURE AIDD ONTO NOT DUMP"
IE SE 15 59 y 4 �'� INSTALL NEW SIDE SEWER CONNECTION TO EXISTING MANHOLE.
2 _
CORE DRILL AND INSTALL KOR-N-SEAL BOOT FOR WATERTIGHT
-" - - r-- - CONNECTION TO PROPOSED PIPE
C'MN �9`m- TYT E z 20.9
200'S CK - - J° 7 Tc jl
_ FROM OR NARY 21.17 �'�� - -(. L S ' -� / _ - CUT CLEANLY AN REM NARY EWER STUB INSTALLED
- --� - __� _ - -- --_--- 203 DURING FOUNDATION WORK TO LOCATION NECESSARY TO INSTALL
HIGH WATER MARK ^'• _-- "_. --_ _ _.
'W11CHI IX 1
21.1 h r -� � .- � \ is-i i�t OIL/WATER SEPARATOR AT THE LOCATION SHOWN.
° I J� -"'7 PROVIDE 2"DOMESTIC POTABLE WATER UNE.TYPE K COPPER.
•` 'I > "
21.00 ;. \ \ INSTALL WITH MINIMUM 40"i COVER.POTHOLE EXISTING UTILITIES
° e I( 7 _ AHEAD OF CONSTRUCTION TO AVOID DIRECT CONFLICTS.PROTECT
EE-2 1 1 / 21.t7r " - 9 i IV`. 1 c PROVIDE SANITARY SEWER CLEAN-OUT PER DETAIL
_ y O iiEXISTING UI
MATCH IX. - / ,,,
SDMH 589H-14 20.63 i -' 1.00 ,,- ,, 1.11 M = _ -my
CB TYPE 11-48 21.00 " ( -- D�:> PROVIDE 90-DEGREE BEND WITH TYPE K COPPER SWEEPING BEND
W/SOLD _- - ^ 2 .`T _ A1C IN ACCORDANCE WITH MANUFACTURER RECOMMENDATIONS,OR
LOCKING 20.98 - SHEET - INSTALL LONG RADIUS 90-DEGREE ELL.
I
CON E TION
SEE T
., -' j R WATER G N C \
v ' TION '� 1 PROVIDE COMPRESSED AIR LINE PER MECHANICAL PUNS.
' \ N 183540.02 21.00 1 /
E 1299451.07 ,-. / ,- ..- 6 p,1C ,� *�- s. � � '.
TOP 20.80 e, - / __ ,
L '
DI
\IE N 15.61 CB 589J 14 /r ,- ' n '7`�� is Tr \ JO NTIDFITTINGS,CL 52 STORM DRAIN FRCEMAIN WITH RESTRAINED j
IE SE 15.61
CB TYPE I -' 3
c N 18353024 ,�� INSTALL 45-DEGREE DI STORM DRAIN FORCEMAIN FITTINGS(TYP.
• E 1299475.39 -,� \' i - 4).
- MATCH EX-
SDMH 5891-74 TOP 20.50 � a �' �
I
E W 16.24
CB TYPE II-48 1 - /� r '' pp at EX�� SUPPLIER TO PROVIDE ANTI-FLOATATION DESIGN/CALC W/
V" W/SOLD 2. _ - = C' c°• i / PRODUCT SUBMITTAL.DESIGN SHALL CONSIDER SOIL LIQUIFACTION
LOCKING UD y 1 8.OA FW a d i PER GEOTECHNICAL RECOMMENDATIONS
�;
N 183517.92
! E 1299455.61 p _. _ _U _ -SDMH 589C�t'4 2 �1� �'W ~�i 1� PROVIDE 8°FIRE WATER CONNECTION.PROVIDE 8"DI X 8"DI WET
! TOP 20.99 U` LIFT STATI0f1 TAPPING SLEEVE W/INTEGRAL TAPPING VALVE.POUR THRUST
IE E 14.62 _ 0 - �N 183' H N 183yf0.05 / - \ ,F BLOCKING IN ACCORDANCE WITH DETAILS ON SHEET C524-I.
;iE W 1442(24"EX) 9509.54 12 �, T Oz E), 9559.70 / C S
Tg S17.84 : `-+�� M�� ._t,l`. -- / PROVIDE 1"MR LINE CONNECTION TO EX6TIN 8"CA INCLUDING
- 2A.HOPE BTOR T 2 V / / \ �� �� ' WELDED TEE AND VALVE SEE MECHANICAL PLANS
� ka:-- INSTALL 90-DEGREE DI MJ BENDS WITH THRUST BLOCK.
,-
N 183 03.14 /_ �, 1 ` / � INSTALL LIFT STATION VALVE VAULT.SEE DETAIL ON SHEET
8 \ ORAOE BR MATCH IX. I E 2
--- 1 STORM LINE D ��� 1 I' C524-G.
E 1299482.34 2MATC _
SDMM 589E-14 12 - NORTHINGS AND FUSTINGS TO FLOATATION SLAB.
-LIFT STATION
VEIR STRUCNREt o NOPE \ v. ��'� a / VALVE VAULT
W/SOUD LO KING UD MATCH EX. ��ur���� 8 / 6 N 183520,08 MATCH EX.20.92 \
E 129941 t82 M4 HEX <: E 12 99553 74
ENW' 5Q148 8 21.MATCH EX, �� �,;h�I '�' 3 i ,M E
t n
I'
E.t 14.79(EX 2e) r
IE HE 16.12 _ MATCH EX. -. -
IE S 14.79 i _ 2 T RM UNE ��������
IE W 14.79 MATCH EX. BUILDING 4-68
BergerAIBAM IFC
Fedor 9M SM,Suite 1 o' O 03.03.14
FFederaleral war,y,WaS WasOUninBrnn 98003-26-26 00
(206)431-2300 F-:(206)431-2250
SCALE IN FEET
SYM REVISION BY APPROVED DATE SYM REVISION IW APPROVED DATEA. SUBMLE CURRENT REVISION ORI fir` 03.03.14
A71 ACCEPTABILITY TNP 0103.14
0 SW MARSHALING YARD-IFC W1829787 DRS ARAM 03.03.13 u.L SPETHIS CIFCA7EON 15MAPP OVED SA 0103.14 GRADING&UTILITY DETAIL PLAN W18zs787
BOE/A/G® nvvrzoveo BY DEPT. DATE DRS 03.03.14 SW MARSHALING YARDCHECKED
r 52/)_n r
JOB NO,V e7 /"l COMP NOv
° ,` RENTON SITE W1829787
CIVIL MASTER RENTON MG NO RTN-YD-0524-A
3/8'EXPANSION JOINT(lYP.)
SEE WSDOT STD PLAN F-30.10 LANDING 6^0" PEDESTRIAN CURB
SIDE WALK
2'WEARING COURSE HMA 2"WEARING COURSE HMA �
CL t/2-PG 70-22 TACK T
T
CL t/2"PG TACK AND SEAL EDGES AT INFLOW
AND SEAL EDGGESES AT b'
A INTERFACE WITH EXISTING INTERFACE WITH EXISTINGPAVEMENT CURB AND GUTTER
PAVEMENT MP CURB RAMP
2.5"HMA CL 1/2" 2.5°HMA CL CURB RA
1/2' � FACE OF CURB DETECTABLE WARNING SURFACE SEE STANDARD PLAN F-45.10
PC 64-22 jf ii. PG 64-22 LADDER PLAN DEPRESSED CURB&GUTTER
iV�
12"CRUSHED SURFACING 6'CRUSHED SURFACING
`✓:,`,�-� y��i„Z�! TOP COURSE WSDOT STD y TOP COURSE WSDOT STD
SPEC 9-03.9(3) \ - SPEC 9-03.9(3)
COMPACTED TO AT LEAST EXIST.COMPACTED COMPACTED TO AT LEAST 4'-0°MIN.
\\
95%OF MAX.DENSITY PER SUBGRADE 95%OF MAX.DENSITY PER 96'DIA PRECAST STRUCTURE SEE CONTRACT PLANS GRADE BREAK ASTM D1557(SEE NOTE 2), ASTM D1557(SEE NOTE 2).
EXIST.COMPACTED COUNTER SLOPE TOP OF
I
SUBGRADE
a 2.0%MAX. 5' _0 ROADWAY
FOR EXISTING SUBGRADE WITH FOR EXISTING SUBGRADE WITH HIGH FLOW BYPASS To _
CONVEYANCE SYSTEM _
GRANULAR MATERIAL LESS THAN 12" GRANULAR MATERIAL 12" AND \ - g DEPRESSED CURB&GU TER SEE STANDARD PLAN
CEMENT CONCRETE f-10.12&NOTE 6
GREATER \\v��// `` PEDESTRIAN CURB
NOTES: _ _ _ _ _ JL INFLOW
LANDING DETECTABLE WARNING SURFACE SEE STANDARD PLAN
1. SEE SHEET C2B PAVEMENT/GRADING NOTES FOR ADDITIONAL REQUIREMENTS. �� / I 30'TEE F-45.10
2. 6"OF PULVERIZED ASPHALT MAY BE USED OVER 6"CSTC. \ '` I SECTION 1
i
ASPHALT PAVEMENT SECTIONS I 12'TEE
SCALE: N/A C550, C551 /�
15'-0"MAX. 4'-0"MIN. 15'-0"MAX.
a ` SEE NOTE 7 SEE CONTRACT PLAN SEE NOTE 6
\\
SIDE WALK / GRADE BREAK-. GRADE BREAK SIDE WALK
8.3%MAX. 2.0%MAX. 8
c CURB RAMP CURB RAMP
CAP AND PLUG WATER QUALITY 3/8`EXPANSION JOINT(TYP.) LANDING
RIGID FLEXIBLE
TO WO FACILIIY� OUTLET DURING CONSTRUCTION SEE WSDOT STD PLAN F-30.10
SECTION 2
(DI,CONC) (CPEP,CMP,PVC)
J 1. PROVIDE A SEPARATE CURB RAMP FOR EACH MARKED OR UNMARKED CROSSWALK.CURB RAMP LOCATION SHALL BE PLACED
PROVIDE NEAT, WITHIN THE WIDTH OF THE ASSOCIATED CROSSWALK,OR AS SHOWN ON PLANS.
STRAIGHT SAWCUT WHERE"GRADE BREAK"IS CALLED OUT,THE ENTIRE LENGTH OF THE GRADE BREAK BETWEEN THE TWO ADJACENT SURFACE
LINE WHERE PAVEMENT,SEE A ROUND SOLID LID 2.PLANES SHALL BE FLUSH.
MATCHING EXIST. PAVEMENT SECTIONS _ RIM EL=20.82
PAVEMENT 3.00 NOT PLACE GRATINGS,JUNCTION BOXES,ACCESS COVERS,OR OTHER APPURTENANCES IN FRONT OF THE CURB RAMP OR ON
ANY PART OF THE CURB RAMP OR LANDING.
4.SEE STANDARD PUN F-10.12 FOR CURB,CURB AND GUTTER,DEPRESSED CURB AND GUTTER,AND PEDESTRIAN CURB DETAILS.
5.SEE STANDARD PLAN F-30.10 FOR CEMENT CONCRETE SIDEWALK DETAILS.SEE PLANS FOR WIDTH AND PLACEMENT OF SIDEWALK.
6„ FLOATABLE z l _ 6.THE CURB RAMP MAXIMUM RUNNING SLOPE SHALL NOT REQUIRE THE RAMP LENGTH TO EXCEED 15 FEET TO AVOID CHASING THE
CONTROL BAFRE 3 UDDER SLOPE INDEFINITELY WHEN CONNECTING TO STEEP GRADES.WHEN APPLYING THE 15-FOOT MAX.LENGTH,THE RUNNING SLOPE OF
+` �v_ ^ •� THE CURB RAMP SHALL BE AS FLAT AS FUSIBLE.
e
7.CURB RAMP,LANDING,AND FLARES SHALL RECEIVE BROOM FINISH.SEE STANDARD SPECIFICATIONS 8-14.
NEW TRENCH BACKFlLL MAT'L WSDOT - PROVIDE
OUT MAINTENANCE
EXIST.SUBGRADE✓^ STD SPEC.9 0 F N PULED IN _ -
LO06E LAYERS 3.NOT MORE THAN - TYPE PARALLEL A SIDEWALK RAMP r 10"DEPTH AND COMPACTED TO AT
yy�.,r�. L✓"'��i�. (.1..) �p55OF MAX.DENSITY PER _ _ SCALE: N/A -C524-A
4" s,��r..,� 6'MIN. 11 BYPASS OUTLET EL= 14.79 WO OUTLET EL= 14.79
✓'n
(MIN.) Y`
/ 36°TEE WITH SOLID CAP AND PLUG WATER QUALITY
BOTTOM,PROVIDE OUTLET DURING CONSTRUCTION
I MAINTENANCE CLEANOUT DOOR THRESHOLD THRESHOLD PER
ARCHITECTURAL DRAWINGS COORDINATE EMBED PER
6-3 4"m ORIFICE 18"MIN BUILDING ARCHITECTURAL DRAWINGS
/ 18'MIN BUILDING FIM91
�-! FLOOR,SEE -4"4,000 PSI CONCRETE
., ARCHRECTURN.
PIPE BEDDING PER WSDOT SUMP=10.80 6"MIN.DEPTH OF CRUSHED PUNS FOR DETAILS LANDING PAD SECTION
9-03.12(3)95%,.
5% 1 MIN SURFACING BASE COURSE
COMPACTION A MAX.155 PER WSDOT STD SPEC
DENSITY PER ASTM D 1557 PIPE O.D.+2 FEET PIPE AS 9-03.9(3)COMPACTED TO ! o
SPECIFIED MINIMUM OF 95%MAX
ON PLAN DENSITY PER ASTM D1557 12H IV N •• i
fl4TL CEOTECHNICAL FABRIC 'o •o •••o ° •••a °°a 'o °o a •o °• °°• - ADA LANDING PAD + 12HAV
1. ALL BACKFlLL SHALL BE COMPACTED TO AT LEAST 95%OF MAX.DRY DENSITY PER ASTM D-1557, ° p n a ° O a ° ° p n ° O a O n O n O MAX 6•CRUSHED
2, IF TRENCH SUBGRADE IS DETERMINED BY THE GEOTECHNICAL ENGINEER DURING CONSTRUCTION TO O n o O 2 5'GM SURFACING TOP
•o a o0 o R�O a °00 a a o0 o °�O •a ° O •o ° COURSE WSDOT STD
BE UNSUITABLE,PROVIDE GEOTEXTILE FABRIC FOR SUBGRADE STABILIZATION AS DIRECTED BY THE o o o o o a SPEC CTED T(3)
BOEING CONSTRUCTION MANAGER PER THE GEOTECHNICAL ENGINEER'S RECOMMENDATIONS. O o o O o O o O o O o O °o O COMPACTED TO AT
LEAST 95%OF MAX.
3. FOR ADDITIONAL REQUIREMENTS SEE THE GENERAL NOTES ON SHEET C28. a.O n °•p° ° O a °•O .p a °•p a °.O - I < NOTES: DENSITY PER ASTM
TY P. PIPE BEDDING SECTION a a II T MIN SEE SHEET ADD PAVEMENT/GRADINGEMEN 01557(SEE NOTE 2).
NOTE: GRA ACCORDANCE
E WITH
IN NOTES FOR ADDITIONAL RETIREMENTS.
SCALE. N A SUPPLIER TO PROVDE AMC-FLOTATION DESIGN&CALCULATIONS WITH M DESIG SUBMITTAL.ANTI- ACCORDANCE WITH 2. 6'OF PULVERIZED ASPHALT MAY BE
/ C52�-A FLOTATION DESIGN SHALL CONSIDER SOIL LIME CTIO RESULTING FROM DESIGN TSITE.EARTHQUAKE RECOMMENDATIONS
ENGINEER'S USED OVER 6'CSTC.
MAGNITUDES PER THE GEOTECHNICAL RECOMMENDATIONS SPECIFIC TO THE PROJECT SIZE. RECOMMENDATIONS
WEIR STRUCTURE DETAIL � CONCRETE LANDING PAD DETAILtr
O
SCALE: NTS - C524-A SCALE: N/A 24-B
BergerABAM
33301 9th Avenue South,Suite 300
Federal Way,Washington 98003-26M
(206)431-2300 Fax:(206)431-2250 0- DAR
SYM REVISION er APPROVED DATE sYM REVISION BY APPROVED DATE ACCEPTABILITY TNP 03.03.14�ts,I SumTntc CURREM RENSON SYMBOL DATE
03.03.14
7H
CIVIL SECTIONS AND DETAILS w1s2s7e7 ORI
0 SW MARSHALING YARD-IFC W1829787 DRS ARAM 03.03.14 THIS DESIGN AND/OR TRW 03.03.14 �EEr
/ ® -,' SPEGFl`ATKNI IS APPROVEDTIttF C524-E C 1 5
(`7/V//7CT`r- APPRrnw 3.14 SW MARSHALING YARD
Br DEFT, DATE MCH 03.0
JOB NO. COMP A<< N0.- RENTON SITE W1829787
__ >:fs yE.,Z•- •i CIVIL MASTER RENTON oNc RTN-YD-0524-E
SITE SPECIFIC TOP SLAB ACCESS INLET BAY
SEE FRAME AND 3'X6'ACCESS HATCH(SPRING AUTO-ASSISTED) CONCRETE WALL WIDTH TO BE TOP SLAB ACCESS
DATA REQUIREMENTS COVER DETAIL SEE FRAME AND COVER DETAIL
DESIGNED BY VAULT SUPPLIER
STRUCTURE ID RTU-8 ---- --------- ----'----- ---'--- --------- --------------------e— ------------------ ------
----- —�
A
WATER QUALITY FLOW RATE (cfs) 1.806 I - • , I
PEAK FLOW RATE (cfs) 12.76 i r • `` e •.
RETURN PERIOD OF PEAK FLOW (yrs) 1OOYR v / \ — — — —�— — �\--------------- — — — — HE — Q-- —I:—
IIrr-------------1 ——— ———— ——— --- ---
FIBERGLASS SEPARATION # OF CARTRIDGES REQUIRED 73 \
CYLINDER AND INLET LL-- - -------------s-- ——— --- --- ---- --
90' FIBERGLASS CARTRIDGE FLOW RATE 11.3 -------------------- —�-- — — --�-- — — --- i �I�
I" SEPARATION
r ` ———— ———
CYLINDER AND MEDIA TYPE (CSF, PERLITE, ZPG) ZPG I ° �/ - ,TTL------------ --- --- ---- --- I
- • INLET I 7—� r-------- — — — —�— — — — —
45' PIPE DATA: I.E. MATERIAL DIAMETER FLO — — —
_ / •-•— —S:Z— —C:7— —SZ %--------- o 0 o O O O
A INLET PIPE #1 14.67 HOPE 12" q jI-- -
INLET PIPE #2 - - - �INLEf INLET — —�-- — — — O �— —�-- —_ — — — — -- — — --�-- — — --- OUTLET BAY
I .. DISSIPATOR11 ----------=-- — I 1,
OUTLET PIPE 11.62 HOPE 12" 1_ J ,— " — --------- --- --- --- OUTLET
F II
Vit ♦ — — — —�— — I SZ— — -- — — — — —�— — — — 0-- — —
UPSTREAM RIM ELEVATION 21,12' I
i
I
FIBERGLASS INLET — CENTER RIM ELEVATION 21.12' i♦ _ _ _ _ _ _ __ __ _ _ _ _ _ __
AND CYLINDER — --
DOWNSTREAM RIM ELEVATION 21.21' — �'-- --�-- — — — — —�— — — --�-- — — --- I
72"I.D. —
MANHOLE
STRUCTURE _ _ _ _ __
EARYDLA�O STRUCTURE
ANTI-FLOTATION BALLAST WIDTH HEIGHT I ' — -- — -- — — -- — — i
NOTE (1) NOTE (1)
— °— — — — -- — ° —
I I I
NOTES/SPECIAL REQUIREMENTS ' PER SITE CIVIL ENGINEER I • , • , - • j
NOTE (1): SUPPLIER TO PROVIDE ANTI-FLOTATION DESIGN &
CALCULATIONS WITH PRODUCT SUBMITTAL. ANTI- L — ------------------STORMFlLTER CARTRIDGES — J
FLOTATION DESIGN SHALL CONSIDER SOIL LIQUIFACTION — --------------------------- — --------- -------------------------------
RESULTING FROM DESIGN EARTHQUAKE MAGNITUDES PER PRECAST CONCRETE VAULT AND REINFORCING
THE GEOTECHNICAL RECOMMENDATIONS SPECIFIC TO THE TO BE DESIGNED BY VAULT SUPPLIER(CONTECH) AND-FLOTATION BALLAST
CONTRACTOR TO GROUT TO FINISHED GRADE PROJECT SITE. 29'-6'
GRADE RIM ELEV 21.38' 31'-6"
- RINGS/RISERS
TIC PLAN VIEW
CONTRACTOR TO
-- ,A FIBERGL NTS GROUT TO
SS SEPARATION FINISHED GRADE
CYLINDER AND INLET 0
GRADE RING/RISERS 3'X 6' TOP-EL.21,12'
ACCESS WATCH(SPRING AUTO-ASSISTED) GRADE RING/RISERS
TOP E1,.21aL TOP EL 21.12'_
•° II P (AS NECESSARY) INSTALL FLUSH W/FINISHED GRADE (AS NECESSARY)
•. II � •'• � -
INLET PIPE > -��---�-
(MULTIPLE INLET CONTECH'
PIPES MAY BE
ACCOMMODATED) - OUTLET PIPE
I,` • .< - I, ,I
LIE ELEV
ELEV 14.73' --ll— IE ELEV _..._ < < < <
• i.
` - d
STEP
----- ° PERMANENT `
BAFFLE
POOL ELEV. FRAME AND COVER PERMANEN POOL ELEVATION WALL
NTS — d OUTLET SUMP
27"STORMFILTER
OIL BAFFLE SKIRT FLOW SPREADER CARTRIDGE
AND BAFFLE WALL INSTALL ROW KD W/PLUGS
_IE ELEV d �
14.67
L1-9
SEPARATION INLET
SCREEN 6 DISSIPATOR
s� e
PVC HYDRAULIC SHEAR ANn-FLOTATION BALLAST.SUPPLIER TO DESIGN.SEE --
PLATE t, ° SITE SPECIFIC DATA REQUIREMENT NOTE(1).
SOLIDS STORAGE SUMP t e ANTI-FLOTATION BALUST.SUPPLIER y
•' TO DESIGN.SEE SITE SPECIFIC DATA < '
✓ °.,. REQUIREMENT NOTE(1). - - L - EV
IF FIL
-
BTM=8.08' NEW 6"MIN.DEPTH OF CRUSHED SURFACING BASE ----..- --- ---'�------------'�'----- —_—`--- --- ""------------T— --- ----------.— — —j1—
COURSE PER WSDOT STD SPEC 9-03.9(3)COMPACTED `• < '< • ` ' 7-7
--
o o G. o o Q o o TO MINIMUM OF 95%MAX DENSITY PER ASTM D1557
p° ° ELEVATION A—A (NTS) p° GEOTECHNICAL FABRIC
P P
0° o p° ° 0 p° ° o p° ° o p° ° o p° o p° o p° ° 0 p, ° o p° ° o p° ° o pP ° o p° o p° ° o p, ° o p° ° o p° o p° ° o pP ° c . 0° °°�
0 0 )0 0 o . 0 0 ^ 00 ° 00 ° o ° p o ° 0 0 00 ° . 0 0 ° 0 0 ° . 00 ° . 0 0 ° 0 o m
Ln n o o GRANULAR MATERIAL IN ACCORDANCE WITH O • Q o Q • Q o Q Q o Q • Q o Q • Q o Q • Q o Q • Q o Q o Q o Q ° Q o Q o Q • Q o Q • Q o o o o o o o Q
GEOTECHNICAL ENGINEER'S RECOMMENDATIONS o o 0 0 0 0 0 0 0 (3 o 0 o a Q o c) Q Q o Q o (3 Q Q Q o Q o Q o Q o ,°
CONTECH CDS3020 PRE-TREATMENT RTU-7
SCALE: NTS _ CONTECH STORM FILTER VAULT RTU-8
SCALE: NTS
`J W1829787 j
BergerABAM 0 IFC
33301 9th Avmue SDU ,SuHe 300 03.03.14
-- Petl 1 Way,Washington 98003-2600
(206)431-230D Fax:(206)431-2250
SYM REVISION By APPROVED DATE SYM REV1610N BY APPROVED DATE —
DATE0 SW MARSHALING YARD-IFC W1829787 DRS ABAM 03.03.14 ACCEPTABILITY TNP 03.03.14 suam.E cua°ENr aEVISIDN srueot MTE
HIS DESIGN AND/OR CIVIL SECTIONS AND DETAILS wlazs7e7 OR 03.03.14
SPECIFICATION IS APPROVED SA 03.03.14 SNEET
BOE/A/G� APPROVED W OEPT DATE DR$ 03.0314 OF SW MARSHALING YARD C524-F C16
A RENTON SITE oB No. W1829787 coup No.
CIVIL MASTER RENTON Dw NO, RTN-YD-0524-F
Technical Information Report— Re%ision 1
Boeing Renton Site Logistics Project—04-086 Steam Utilidor February 29, 2016
THIS PAGE INTENTIONALLY LEFT BLANK
Davido Consulting Group,Inc.
TIR_Boeing Renton Site Logistics Project_04-086 Steam Utilidor_Final_Revision I
Technical Information Report
Renton Site Logistics
Renton, Washington
Appendix H
Maintenance Manual
r
r
r
0-5-4'� : NTECH'
ENGINEERED SOLUTIONS
CDS Guide
Operation, Design, Performance and Maintenance
+ � ahTEN. N() 7813 134t1
Ww
M
CDS® Design Basics
Using patented continuous deflective separation technology,the There are three primary methods of sizing a CDS system.The
- CDS system screens, separates and traps debris, sediment,and Water Quality Flow Rate Method determines which model size
oil and grease from stormwater runoff.The indirect screening provides the desired removal efficiency at a given flow rate for a
capability of the system allows for 100%removal of floatables defined particle size.The Rational Rainfall Method" or the and
and neutrally buoyant material without blinding. Flow and Probabilistic Method is used when a specific removal efficiency of
screening controls physically separate captured solids,and the net annual sediment load is required.
minimize the re-suspension and release of previously trapped
pollutants. Inline units can treat up to 6 cfs,and internally bypass Typically in the Unites States, CDS systems are designed to
flows in excess of 50 cfs(1416 L/s).Available precast or cast-in- achieve an 80%annual solids load reduction based on lab
place,offline units can treat flows from 1 to 300 cfs(28.3 to generated performance curves for a gradation with an average
8495 Us).The pollutant removal capacity of the CDS system has particle size(d50)of 125 microns(um). For some regulatory
been proven in lab and field testing. environments,CDS systems can also be designed to achieve an
80%annual solids load reduction based on an average particle
Operation Overview size(60)of 75 microns(um)or 50 microns(um).
Stormwater enters the diversion chamber where the diversion Water Quality Flow Rate Method
weir guides the flow into the unit's separation chamber and In some cases, regulations require that a specific treatment rate,
pollutants are removed from the flow.All flows up to the often referred to as the water quality design flow(WQQ), be
system's treatment design capacity enter the separation chamber treated.This WQQ represents the peak flow rate from either
and are treated. an event with a specific recurrence interval, e.g.the six-month
Swirl concentration and screen deflection force floatables and storm,or a water quality depth,e.g. 1/2-inch (13 mm) of
solids to the center of the separation chamber where 100%of rainfall.
floatables and neutrally buoyant debris larger than the screen The CDS is designed to treat all flows up to the WQQ.At influent
apertures are trapped. rates higher than the WQQ,the diversion weir will direct most
Stormwater then moves through the separation screen, under flow exceeding the WQQ around the separation chamber.This
the oil baffle and exits the system.The separation screen remains allows removal efficiency to remain relatively constant in the
clog free due to continuous deflection. separation chamber and eliminates the risk of washout during
bypass flows regardless of influent flow rates.
During the flow events exceeding the treatment design capacity,
the diversion weir bypasses excessive flows around the separation Treatment flow rates are defined as the rate at which the CDS
chamber, so captured pollutants are retained in the separation will remove a specific gradation of sediment at a specific removal
cylinder. efficiency.Therefore the treatment flow rate is variable, based
on the gradation and removal efficiency specified by the design
engineer.
— Rational Rainfall Method"
Differences in local climate,topography and scale make every
_•-'` _ _ site hydraulically unique. It is important to take these factors into
consideration when estimating the long-term performance of
any stormwater treatment system.The Rational Rainfall Method
combines site-specific information with laboratory generated
performance data,and local historical precipitation records to
estimate removal efficiencies as accurately as possible.
Short duration rain gauge records from across the United States
and Canada were analyzed to determine the percent of the total
annual rainfall that fell at a range of intensities. US stations'
depths were totaled every 15 minutes,or hourly,and recorded in
0.01-inch increments. Depths were recorded hourly with 1-mm
resolution at Canadian stations.One trend was consistent at
all sites;the vast majority of precipitation fell at low intensities
i
and high intensity storms contributed relatively little to the total
annual depth.
These intensities,along with the total drainage area and runoff
coefficient for each specific site,are translated into flow rates
using the Rational Rainfall Method. Since most sites are relatively
small and highly impervious,the Rational Rainfall Method is
appropriate. Based on the runoff flow rates calculated for each
- --- intensity, operating rates within a proposed CDS system are
2
determined. Performance efficiency curve determined from full Two different gradations of silica sand material(UF Sediment
scale laboratory tests on defined sediment PSDs is applied to &OK 1 10)were used in the CDS performance evaluation. The
calculate solids removal efficiency.The relative removal efficiency particle size distributions(PSDs)of the test materials were
at each operating rate is added to produce a net annual pollutant analyzed using standard method "Gradation ASTM D-422
removal efficiency estimate. "Standard Test Method for Particle-Size Analysis of Soils" by a
certified laboratory.
Probabilistic Rational Method
The Probabilistic Rational Method is a sizing program Contech OF Sediment is a mixture of three different products produced
developed to estimate a net annual sediment load reduction for by the U.S. Silica Company: "Sil-Co-Sil 106", "#1 DRY"and
a particular CDS model based on site size,site runoff coefficient, 20/40 Oil Frac". Particle size distribution analysis shows that
regional rainfall intensity distribution, and anticipated pollutant the OF Sediment has a very fine gradation(d50 = 20 to 30 pm)
characteristics. covering a wide size range(Coefficient of Uniformity, C averaged
at 10.6). In comparison with the hypothetical TSS gradation
The Probabilistic Method is an extension of the Rational Method specified in the NJDEP(New Jersey Department of Environmental
used to estimate peak discharge rates generated by storm events Protection)and NJCAT(New Jersey Corporation for Advanced
of varying statistical return frequencies(e.g. 2-year storm event). Technology) protocol for lab testing,the OF Sediment covers a
Under the Rational Method, an adjustment factor is used to similar range of particle size but with a finer d50(d50 for NJDEP
adjust the runoff coefficient estimated for the 10-year event, is approximately 50 pm)(NJDEP, 2003). —
correlating a known hydrologic parameter with the target storm
event. The rainfall intensities vary depending on the return The OK-1 10 silica sand is a commercial product of U.S. Silica
frequency of the storm event under consideration. In general, Sand. The particle size distribution analysis of this material,also
these two frequency dependent parameters(rainfall intensity included in Figure 1,shows that 99.9%of the OK-1 10 sand is
and runoff coefficient) increase as the return frequency increases finer than 250 microns,with a mean particle size(d50)of 106
while the drainage area remains constant. microns. The PSDs for the test material are shown in Figure 1.
These intensities,along with the total drainage area and runoff 100.0 -- --- -- ------- •-- -_ -
coefficient for each specific site,are translated into flow rates 90.0 .—OF Sediment(Avg)
using the Rational Method. Since most sites are relatively small 80.0 OK 110(Avg)
and highly impervious,the Rational Method is appropriate. Based 70.0 NJCAT
on the runoff flow rates calculated for each intensity, operating 60.0
rates within a proposed CDS are determined. Performance 50.0
efficiency curve on defined sediment PSDs is applied to calculate 40.0 I
solids removal efficiency. The relative removal efficiency at each 30.0
operating rate is added to produce a net annual pollutant 20.0
removal efficiency estimate. 10.0 - g a ,� y
Treatment Flow Rate 1 10 100 1000
The inlet throat area is sized to ensure that the WQQ passes Particle size(«m)
through the separation chamber at a water surface elevation
equal to the crest of the diversion weir.The diversion weir Figure 1. Particle size distributions
bypasses excessive flows around the separation chamber,
thus preventing re-suspension or re-entrainment of previously Tests were conducted to quantify the performance of a specific
captured particles. CDS unit(1.1 cfs(31.3-L/s)design capacity)at various flow rates,
ranging from 1%up to 125%of the treatment design capacity of
Hydraulic Capacity the unit, using the 2400 micron screen. All tests were conducted
The hydraulic capacity of a CDS system is determined by the with controlled influent concentrations of approximately 200
length and height of the diversion weir and by the maximum mg/L. Effluent samples were taken at equal time intervals
allowable head in the system. Typical configurations allow across the entire duration of each test run. These samples
hydraulic capacities of up to ten times the treatment flow rate. were then processed with a Dekaport Cone sample splitter to
The crest of the diversion weir may be lowered and the inlet obtain representative sub-samples for Suspended Sediment
throat may be widened to increase the capacity of the system Concentration (SSC)testing using ASTM D3977-97 "Standard
at a given water surface elevation. The unit is designed to meet Test Methods for Determining Sediment Concentration in Water
project specific hydraulic requirements. Samples", and particle size distribution analysis.
Performance Results and Modeling
Full-Scale Laboratory Test Results Based on the data from the University of Florida, a performance
A full-scale CDS system (Model CDS2020-58)was tested at the model was developed for the CDS system. A regression analysis
was used to develop a fitting curve representative of the
facility of University of Florida, Gainesville, FL. This CDS unit was scattered data points at various design flow rates.This model,
evaluated under controlled laboratory conditions of influent flow which demonstrated good agreement with the laboratory data,
rate and addition of sediment. can then be used to predict CDS system performance with respect
3
to SSC removal for any particle size gradation,assuming the Maintenance
particles are inorganic sandy-silt. Figure 2 shows CDS predictive The CDS system should be inspected at regular intervals and
performance for two typical particle size gradations(MCAT maintained when necessary to ensure optimum performance.
gradation and OK-1 10 sand)as a function of operating rate. The rate at which the system collects pollutants will depend more
heavily on site activities than the size of the unit. For example,
100.00 - --- ----" unstable soils or heavy winter sanding will cause the grit chamber
_- -.-. . . to fill more quickly but regular sweeping of paved surfaces will
60.00- slow accumulation.
I
40.00 _. _ _ -__ _ Inspection
- - - NJCAT . .
Inspection is the key to effective maintenance and is easily
20.00
OK 110 performed. Pollutant transport and deposition may vary from
o.00 year to year and regular inspections will help ensure that the
0% 20% 40% 60% 8o% 100% 120% 140% system is cleaned out at the appropriate time. At a minimum,
%Design Flow Rate inspections should be performed twice per year(e.g.spring
and fall)however more frequent inspections may be necessary
Figure 2. CDS stormwater treatment predictive performance for in climates where winter sanding operations may lead to rapid
various particle gradations as a function of operating rate. accumulations,or in equipment washdown areas. Installations
Many regulatory jurisdictions set a performance standard for should also be inspected more frequently where excessive
hydrodynamic devices by stating that the devices shall be capable amounts of trash are expected.
of achieving an 80%removal efficiency for particles having a The visual inspection should ascertain that the system
mean particle size(d50)of 125 microns(e.g. Washington State components are in working order and that there are no
Department of Ecology—WASDOE-2008). The model can blockages or obstructions in the inlet and separation screen.
be used to calculate the expected performance of such a PSD The inspection should also quantify the accumulation of
(shown in Figure 3). The model indicates(Figure 4)that the CDS hydrocarbons,trash,and sediment in the system. Measuring
system with 2400 micron screen achieves approximately 80% pollutant accumulation can be done with a calibrated dipstick,
removal at the design (100%)flow rate,for this particle size tape measure or other measuring instrument. If absorbent
distribution(d50 = 125 pm). material is used for enhanced removal of hydrocarbons,the level
of discoloration of the sorbent material should also be identified
Particle Size Distribution
100
90
80
60
50
40
30
20
10
0
1 10 100 1000 10000
Particle Size(micron)
Figure 3. WASDOE PSD
CDS U-A Performance for Ecology PSD
d,,=125 Lun
I z
100 --_ $
80 + w a
< i F
60 .... -
d _
20 ... Y=1t9.145x*100..92
.
R 0.531
0% 20°/u 400/6 600/6 80°/u 100% 120% 140%
k b
%Design Flow Rate , t
Figure 4. Modeled performance for WASDOE PSD. . �
4
during inspection. It is useful and often required as part of an Cleaning _
operating permit to keep a record of each inspection. A simple Cleaning of a CDS systems should be done during dry weather
form for doing so is provided. conditions when no flow is entering the system.The use of a
Access to the CDS unit is typically achieved through two manhole vacuum truck is generally the most effective and convenient
access covers. One opening allows for inspection and cleanout method of removing pollutants from the system. Simply remove
of the separation chamber(cylinder and screen)and isolated the manhole covers and insert the vacuum hose into the sump.
sump. The other allows for inspection and cleanout of sediment The system should be completely drained down and the sump
captured and retained outside the screen. For deep units,a fully evacuated of sediment.The area outside the screen should
single manhole access point would allows both sump cleanout also be cleaned out if pollutant build-up exists in this area.
and access outside the screen. In installations where the risk of petroleum spills is small, liquid
The CDS system should be cleaned when the level of sediment contaminants may not accumulate as quickly as sediment.
has reached 75%of capacity in the isolated sump or when an However,the system should be cleaned out immediately in the
appreciable level of hydrocarbons and trash has accumulated. event of an oil or gasoline spill. Motor oil and other hydrocarbons
If absorbent material is used, it should be replaced when that accumulate on a more routine basis should be removed
significant discoloration has occurred. Performance will not be when an appreciable layer has been captured.To remove these
impacted until 100%of the sump capacity is exceeded however pollutants, it may be preferable to use absorbent pads since they
it is recommended that the system be cleaned prior to that are usually less expensive to dispose than the oil/water emulsion
for easier removal of sediment. The level of sediment is easily that may be created by vacuuming the oily layer.Trash and debris
determined by measuring from finished grade down to the can be netted out to separate it from the other pollutants. The
top of the sediment pile. To avoid underestimating the level of screen should be cleaned to ensure it is free of trash and debris. -
sediment in the chamber,the measuring device must be lowered Manhole covers should be securely seated following cleaning -
to the top of the sediment pile carefully. Particles at the top of activities to prevent leakage of runoff into the system from above
the pile typically offer less resistance to the end of the rod than and also to ensure that proper safety precautions have been -
consolidated particles toward the bottom of the pile. Once this followed. Confined space entry procedures need to be followed
measurement is recorded, it should be compared to the as-built
if physical access is required. Disposal of all material removed
drawing for the unit to determine weather the height of the
sediment pile off the bottom of the sump floor exceeds 75%of from the CDS system should be done in accordance with local
the total height of isolated sump. regulations. In many jurisdictions,disposal of the sediments may
be handled in the same manner as the disposal of sediments
removed from catch basins or deep sump manholes. Check your
local regulations for specific requirements on disposal.
I
u
,s.
u
CDS Diameter Distance from Water Surface Sediment
Model to Top of Sediment Pile Storage Capacity
CDS2015-4 4 1.2 3.0 0.9 0.5 0.4
CDS2020 5 1.5 3.5 1.1 1.3 1.0
..
CDS2025 5 1.5 4.0 1.2
CDS3020 6 8 4.0 1-2 2.1 1.6
CDS3030 6 1.8 4.6 1.4 2.1 1.6
CDS3035 6 1 8 5 0 5
CDS4030 8 2.4 4.6 1.4 5.6 4.3
CDS4040 8 2.4 5.7 1.7 5.6 4.3
CDS4045 8 2.4 62 1 ,5.6 4.3
Table 1: CDS Maintenance Indicators and Sediment Storage Capacities
Note:To avoid underestimating the volume of sediment in the chamber,carefully lower the
measuring device to the top of the sediment pile. Finer silty particles at the top of the pile
may be more difficult to feel with a measuring stick.These finer particles typically offer less
resistance to the end of the rod than larger particles toward the bottom of the pile.
f-•
:t
' I
k$�
66
71
CDS Inspection • Maintenance • •
CDS Model: Location:
Water Floatable Describe
Maintenance
Date depth to Layer Maintenance Comments
Personnel
sediment' Thickness' Performed
1. The water depth to sediment is determined by taking two measurements with a stadia rod:one measurement from the manhole opening to
the top of the sediment pile and the other from the manhole opening to the water surface.If the difference between these measurements is
less than eighteen inches the system should be cleaned out. Note:To avoid underestimating the volume of sediment in the chamber,the
measuring device must be carefully lowered to the top of the sediment pile.
2. For optimum performance,the system should be cleaned out when the floating hydrocarbon layer accumulates to an appreciable thickness.In
the event of an oil spill,the system should be cleaned immediately. 7
I
i
Support
Drawings and specifications are available at www.ContechES.com/urbangreen.
ENGINEERED SOLUTIONS
® Site-specific design support is available from our engineers. 800.925.5240
www.ContechES.com/urbangreen
©2013 Contech Engineered Solutions LLC
Contech Engineered Solutions provides site solutions for the civil engineering industry.Contech's portfolio includes bridges,drainage,sanitary
sewer,stormwater,earth stabilization and wastewater products. For information on other Contech division offerings,visit www.ContechES.com
or call 800.338.1122
NOTHING IN THIS CATALOG SHOULD BE CONSTRUED AS AN EXPRESSED WARRANTY OR AN IMPUED WARRANTY OF MERCHANTABILITY OR FITNESS FOR ANY PARTICULAR PURPOSE.SEE THE
-- Contech STANDARD CONDITION OF SALES(VIEWABLE AT Www.ContechES.com/COS)FOR APPLICABLE WARRANTIES AND OTHER IMPORTANT INFORMATION.
The product(s)described may be protected by one or more of the following US patents: 5,322,629;5,624,576;5,707,527;5,759,415;5,788,848;5,985,157;6,027,639;6,350,374;6,406,218;
6,641,720;6,511,595;6,649,048;6,991,114;6,998,038;7,186,058;7,296,692;7,297,266; related foreign patents or other patents pending.
' 1
RECYC
-- LED
cds manual 2.i13 PDF PAPER
i
I
Important: Inspection should be performed by a person who is
familiar with the StormFilter treatment unit.
STORMWATER StormFilter
SOLUTIONS_ 1. If applicable, set up safety equipment to protect and notify -
surrounding vehicle and pedestrian traffic.
StormFilter Maintenance Guidelines 2.Visually inspect the external condition of the unit and take notes
Maintenance requirements and frequency are dependent on the concerning defects/problems. l
pollutant load characteristics of each site,and may be required in 3.Open the access portals to the vault and allow the system vent.
the event of a chemical spill or due to excessive sediment loading. 4.Without entering the vault,visually inspect the inside of the unit,
Maintenance Procedures and note accumulations of liquids and solids.
Although there are other effective maintenance options, CONTECH 5. Be sure to record the level of sediment build-up on the floor of
recommends the following two step procedure: the vault, in the forebay,and on top of the cartridges. If flow
is occurring, note the flow of water per drainage pipe. Record
1. Inspection: Determine the need for maintenance. all observations. Digital pictures are valuable for historical
2. Maintenance: Cartridge replacement and sediment removal. documentation.
Inspection and Maintenance Activity Timing 6.Close and fasten the access portals.
At least one scheduled inspection activity should take place per year 7. Remove safety equipment.
with maintenance following as warranted. 8. If appropriate, make notes about the local drainage area relative
First, inspection should be done before the winter season. During to ongoing construction, erosion problems, or high loading of
which, the need for maintenance should be determined and, if other materials to the system.
disposal during maintenance will be required,samples of the 9. Discuss conditions that suggest maintenance and make decision
accumulated sediments and media should be obtained. as to weather or not maintenance is needed.
Second, if warranted, maintenance should be performed during Maintenance Decision Tree
periods of dry weather. The need for maintenance is typically based on results of the inspection.
In addition,you should check the condition of the StormFilter unit Use the following as a general guide. (Other factors,such as regulatory
after major storms for potential damage caused by high flows and requirements,may need to be considered)
for high sediment accumulation. It may be necessary to adjust the 1.Sediment loading on the vault floor. If >4"of accumulated
inspection/maintenance activity schedule depending on the actual sediment,then go to maintenance.
operating conditions encountered by the system. 2.Sediment loading on top of the cartridge. If>1/4"of
Generally, inspection activities can be conducted at any time,and accumulation, then go to maintenance.
maintenance should occur when flows into the system are unlikely. 3.Submerged cartridges. If>4"of static water in the cartridge
Maintenance Activity Frequency bay for more that 24 hrs after end of rain event, then go to
Maintenance is performed on an as needed basis, based on maintenance.
inspection. Average maintenance lifecycle is 1-3 years. The primary 4. Plugged media. If pore space between media granules is absent,
factor controlling timing of maintenance of the StormFilter is then go to maintenance.
sediment loading. Until appropriate timeline is determined, use the 5. Bypass condition. If inspection is conducted during an average
following: rain fall event and StormFilter remains in bypass condition
Inspection: (water over the internal outlet baffle wall or submerged
One time per year cartridges),then go to maintenance.
After major storms 6. Hazardous material release. If hazardous material release
(automotive fluids or other)is reported, then go to
Maintenance: maintenance.
As needed 7. Pronounced scum line. If pronounced scum line(say > 1/4"
Per regulatory requirement thick) is present above top cap,then go to maintenance.
In the event of a chemical spill 8.Calendar Lifecycle. if system has not been maintained for 3
Inspection Procedures years,then go to maintenance.
It is desirable to inspect during a storm to observe the relative Assumptions:
flow through the filter cartridges. If the submerged cartridges are No rainfall for 24 hours or more.
severely plugged,then typically large amounts of sediments will be No upstream detention (at least not draining into StormFilter).
present and very little flow will be discharged from the drainage Structure is online. Outlet pipe is clear of obstruction. Construction
pipes. If this is the case,then maintenance is warranted and the bypass is plugged.
cartridges need to be replaced.
Maintenance
Warning: In the case of a spill,the worker should abort inspection Depending on the configuration of the particular system,workers
activities until the proper guidance is obtained. Notify the will be required to enter the vault to perform the maintenance.
local hazard control agency and CONTECH immediately.
To conduct an inspection:
1
I
i
Important: If vault entry is required, OSHA rules for confined space Method 2:
entry must be followed. A. Enter the vault using appropriate confined space protocols.
Filter cartridge replacement should occur during dry weather. It may B. Unscrew the cartridge cap.
be necessary to plug the filter inlet pipe if base flow is occurring.
Replacement cartridges can be delivered to the site or customers C. Remove the cartridge hood screws(3) hood and float.
facility. Contact CONTECH for more information. D. At location under structure access,tip the cartridge on its
Warning: In the case of a spill,the worker should abort side.
maintenance activities until the proper guidance is obtained. Notify
the local hazard control agency and CONTECH immediately. Important: Note that cartridges containing media other than
the leaf media require unscrewing from their threaded
To conduct cartridge replacement and sediment removal: connectors.Take care not to damage the manifold
1. If applicable, set up safety equipment to protect workers and connectors.This connector should remain installed in the
pedestrians from site hazards. manifold and capped if necessary.
2.Visually inspect the external condition of the unit and take notes E. Empty the cartridge onto the vault floor. Reassemble the
concerning defects/problems. empty cartridge.
3.Open the doors(access portals)to the vault and allow the system
F. Set the empty, used cartridge aside or load onto the hauling
to vent.
truck.
4.Without entering the vault,give the inside of the unit, including
components, a general condition inspection. G. Continue steps a through E until all cartridges have been
5. Make notes about the external and internal condition of removed.
the vault. Give particular attention to recording the level of 8. Remove accumulated sediment from the floor of the vault and
sediment build-up on the floor of the vault, in the forebay,and from the forebay. Use vacuum truck for highest effectiveness.
on top of the internal components.
9. Once the sediments are removed, assess the condition of the
6. Using appropriate equipment offload the replacement cartridges vault and the connectors.The connectors are short sections
(up to 150 lbs. each)and set aside. of 2-inch schedule 40 PVC, or threaded schedule 80 PVC that
7. Remove used cartridges from the vault using one of the should protrude about 1"above the floor of the vault. Lightly
following methods: wash down the vault interior.
Method 1: a. If desired, apply a light coating of FDA approved silicon
A. This activity will require that workers enter the vault to lube to the outside of the exposed portion of the
remove the cartridges from the under drain manifold and connectors.This ensures a watertight connection between
place them under the vault opening for lifting (removal). the cartridge and the drainage pipe.
Unscrew(counterclockwise rotations)each filter cartridge
- from the underdrain connector. Roll the loose cartridge,on b. Replace any damaged connectors.
edge,to a convenient spot beneath the vault access. 10. Using the vacuum truck boom, crane,or tripod, lower and
Using appropriate hoisting equipment,attach a cable from install the new cartridges.Take care not to damage connections.
the boom, crane, or tripod to the loose cartridge. Contact 11. Close and fasten the door.
CONTECH for suggested attachment devices. 12, Remove safety equipment.
Important: Cartridges containing leaf media (CSF)do not 13. Finally,dispose of the accumulated materials in accordance with
- require unscrewing from their connectors. Do not applicable regulations. Make arrangements to return the used
damage the manifold connectors.They should remain empty cartridges to CONTECH,
installed in the manifold and can be capped during the Material Disposal
maintenance activity to prevent sediments from entering The accumulated sediment must be handled and disposed of in
the under drain manifold. accordance with regulatory protocols. It is possible for sediments
B. Remove the used cartridges(up to 250 lbs.)from the vault. to contain measurable concentrations of heavy metals and organic
chemicals. Areas with the greatest potential for high pollutant
Important:Avoid damaging the cartridges during removal and loading include industrial areas and heavily traveled roads.
installation.
Sediments and water must be disposed of in accordance with
C. Set the used cartridge aside or load onto the hauling truck. applicable waste disposal regulations. Coordinate disposal of solids
D. Continue steps A through C until all cartridges have been and liquids as part of your maintenance procedure. Contact the
removed. local public works department to inquire how they disposes of their
street waste residuals.
©2007 CONTECH Stormwater Solutions 800.925.5240
contech stormwater.com
Nothing in this catalog should be construed as an expressed warranty or an implied warranty of merchantability or fitness for any particular purpose.
See the CONTECH standard quotation or acknowledgement for applicable warranties and other terms and conditions of sale.
The product(s)described may be protected by one or more of the following US patents: 5,322,629;5,624,576;5,707,527;5,759,415;5,789,848;5,985,157;
6,027,639;6,350,374;6,406,218;6,641,720;6,511,595;6,649,048;6,991,114;6,998,038;7,186,058;related foreign patents or other patents pending.
2
Technical Information Report
Renton Site Logistics
Renton, Washington
Appendix I
Water Quality General Use Level Designations
vmm�
W A S P 1 4 S-7 4 S T A I I
o t PAAi YE Ni Gf
ECOLOGY
January 2013
GENERAL USE LEVEL DESIGNATION FOR BASIC (TSS) TREATMENT
For
CONTECH Engineered Solutions
Stormwater Management StormFilter`)
With ZPG Media at 1 gpm/sq ft media surface area
Ecology's Decision:
Based on the CONTECH Engineered Solutions' (CONTECH)application
submissions,Ecology hereby issues a General Use Level Designation (GULD) for the
Stormwater Management StormFilter° (StormFilter):
1. As a basic stormwater treatment practice for total suspended solids (TSS)
removal,
• Using ZPGTM media (zeolite/perlite/granular activated carbon),with the size
distribution described below,
• Sized at a hydraulic loading rate of 1 gpm/ft2 of media surface area, per
Table 1,and
• Internal bypassing needs to be consistent with the design guidelines in
CONTECH's current product design manual.
Table 1. StormFilter Design Flow Rates per Cartridge
Effective Cartridge Height (inches) 12 18 1 27
Cartridge Flow Rate m/cartrid e 5 7.5 1 11.3
2. Ecology approves StormFilter systems containing ZPGTM media for treatment at
the hydraulic loading rates shown in Table 1,to achieve the maximum water
quality design flow rate. The water quality design flow rates are calculated using
the following procedures:
• Western Washington: For treatment installed upstream of detention or
retention,the water quality design flow rate is the peak 15-minute flow rate
as calculated using the latest version of the Western Washington Hydrology
Model or other Ecology-approved continuous runoff model.
CONTECH -StormFilter GULD Maintenance Update(November 2012) a e 1
• Eastern Washington: For treatment installed upstream of detention or
retention,the water quality design flow rate is the peak 15-minute flow rate
as calculated using one of the three methods described in Chapter 2.2.5 of the
Stormwater Management Manual for Eastern Washington (SWMMEW) or
local manual.
• Entire State: For treatment installed downstream of detention,the water
quality design flow rate is the full 2-year release rate of the detention facility.
3. This designation has no expiration date, but Ecology may amend or revoke it.
Ecology's Conditions of Use:
The StormFilter with ZPG media shall comply with the following conditions:
1. Design,install,operate, and maintain the StormFilter with ZPG media in
accordance with applicable Contech Engineered Solutions manuals,
documents, and the Ecology Decision.
2. Install StormFilter systems to bypass flows exceeding the water quality
treatment rate.Additionally, high flows will not re-suspend captured
sediments. Design StormFilter systems in accordance with the performance
goals in Ecology's most recent Stormwater Manual and CONTECH's
Product Design Manual Version 4.1 (April 2006),or most current version,
unless otherwise specified.
3. Owners must follow the design, pretreatment, land use application,and
maintenance criteria in CONTECH's Design Manual.
4. Pretreatment of TSS and oil and grease may be necessary,and designers
shall provide pre-treatment in accordance with the most current versions of
the CONTECH's Product Design Manual(April2006) or the applicable
Ecology Stormwater Manual. Design pre-treatment using the performance
criteria and pretreatment practices provided on Ecology's "Evaluation of
Emerging Stormwater Treatment Technologies"website.
5. Maintenance: The required maintenance interval for stormwater treatment
devices is often dependent upon the degree of pollutant loading from a
particular drainage basin. Therefore,Ecology does not endorse or
recommend a "one size fits all" maintenance cycle for a particular model/size
of manufactured filter treatment device.
• Typically, CONTECH designs StormFilter systems for a target filter
media replacement interval of 12 months. Maintenance includes
removing accumulated sediment from the vault,and replacing spent
cartridges with recharged cartridges.
CONTECH -StormFilter GULD Maintenance Update(November 2012) a 12
• Indications of the need for maintenance include effluent flow decreasing
to below the design flow rate,as indicated by the scumline above the
shoulder of the cartridge.
• Owners/operators must inspect StormFilter with ZPG media for a
minimum of twelve months from the start of post-construction operation
to determine site-specific maintenance schedules and requirements. You
must conduct inspections monthly during the wet season,and every other
month during the dry season. (According to the SWMMWW the wet
season in western Washington is October 1 to April 30.According to
SWMMEW the wet season in eastern Washington is October I to June
30). After the first year of operation, owners/operators must conduct
inspections based on the findings during the first year of inspections.
• Conduct inspections by qualified personnel, follow manufacturer's
guidelines, and use methods capable of determining either a decrease in
treated effluent flowrate and/or a decrease in pollutant removal ability.
• When inspections are performed, the following findings typically serve as
maintenance triggers:
• Accumulated vault sediment depths exceed an average of 2 inches, or
• Accumulated sediment depths on the tops of the cartridges exceed an
average of 0.5 inches, or
• Standing water remains in the vault between rain events, or
• Bypass occurs during storms smaller than the design storm.
• Note: If excessive floatables (trash and debris) are present, perform a
minor maintenance consisting of gross solids removal, not cartridge
replacement.
6. CONTECH shall maintain readily available reports listed under
"Application Documents" (above) as public, as well as the documentation
submitted with its previous conditional use designation application.
CONTECH shall provide links to this information from its corporate
website, and make this information available upon request, at no cost and in
a timely manner.
7. ZPGTm media used shall conform with the following specifications:
• Each cartridge contains a total of approximately 2.6 cubic feet of media.
The ZPGTM cartridge consists of an outer layer of perlite that is
approximately 1.3 cubic feet in volume and an inner layer, consisting of a
mixture of 90% zeolite and 10% granular activated carbon,which is
approximately 1.3 cubic feet in volume.
• Perlite Media: Perlite media shall be made of natural siliceous volcanic
rock free of any debris or foreign matter. The expanded perlite shall
CONTECH -StormFilter�GULD Maintenance Update(November 2012) !' a 3
have a bulk density ranging from 6.5 to 8.51bs per cubic foot and particle
sizes ranging from 0.09" (#8 mesh)to 0.38"(3/8" mesh).
• Zeolite Media: Zeolite media shall be made of naturally occurring
clinoptilolite. The zeolite media shall have a bulk density ranging from
44 to 50 lbs per cubic foot and particle sizes ranging from 0.13"(#6 mesh)
to 0.19" (#4 mesh). Additionally,the cation exchange capacity(CEC) of
zeolite shall range from approximately 1.0 to 2.2 meq/g.
• Granular Activated Carbon: Granular activated carbon (GAC)shall be
made of lignite coal that has been steam-activated. The GAC media shall
have a bulk density ranging from 28 to 31 lbs per cubic foot and particle
sizes ranging from a 0.09" (#8 mesh) to 0.19" (#4 mesh).
Applicant: Contech Engineered Solutions
Applicant's Address: 11835 NE Glenn Widing Dr.
Portland, OR 97220
Application Documents:
The applicant's master report,titled, "The Stormwater Management StormFilter
Basic Treatment Application for General Use Level Designation in Washington",
Stormwater Management, Inc., November 1, 2004, includes the following reports:
• (Public)Evaluation of the Stormwater Management StormFilter Treatment
System: Data Validation Report and Summary of the Technical Evaluation
Engineering Report (TEER) by Stormwater Management Inc., October 29, 2004
Ecology's technology assessment protocol requires the applicant to hire an
independent consultant to complete the following work:
1. Complete the data validation report.
2. Prepare a TEER summary, including a testing summary and conclusions
compared with the supplier's performance claims.
3. Provide a recommendation of the appropriate technology use level.
4. Recommend relevant information to be posted on Ecology's website.
5. Provide additional testing recommendations, if needed."
6. This report, authored by Dr. Gary Minton, Ph. D., P.E., Resource Planning
Associates, satisfies the Ecology requirement.
• (Public)"Performance of the Stormwater Management StormFilter Relative to the
Washington State Department of Ecology Performance Goals for Basic
Treatment," is a summary of StormFilter performance that strictly adheres to the
criteria listed in the Guidance for Evaluating Emerging Stormwater Treatment
Technologies, Technology Assessment Protocol—Ecology (TAPE).
CONTECH-StormFilter®GULD Maintenance Update(November 2012) P age 14
• "Heritage Marketplace Field Evaluation: Stormwater Management StormFilter
with ZPGTM Media," is a report showing all of the information collected at Site A
as stated in the SMI Quality Assurance Project Plan (QAPP). This document
contains detailed information regarding each storm event collected at this site, and
it provided a detailed overview of the data and project.
• "Lake Stevens Field Evaluation: Stormwater Management StormFilter with
ZPGTM Media," is a report that corresponds to Site E as stated in the SMI QAPP.
This document contains detailed information regarding each storm collected at
this site, and includes a detailed overview of the data and project.
• (Public) "Evaluation of the Stormwater Management StormFilter for the removal
of SIL-CO-SIL 106, a standardized silica product: ZPGTM at 7.5 GPM" is a report
that describes laboratory testing at full design flow.
• "Factors Other Than Treatment Performance."
• 'State of Washington Installations."
Above-listed documents noted as "public" are available by contacting CONTECH.
Applicant's Use Level Request:
That Ecology grant a General Use Level Designation for Basic Treatment for the
StormFilter using ZPGTM media(zeolite/perlite/granular activated carbon)at a hydraulic
loading rate of 1 gpm/ft2 of media surface area in accordance with Ecology's 2011
Technical Guidance Manual for Evaluating Emerging Stormwater Treatment
Technologies Technology Assessment Protocol—Ecology (TAPE)..
Applicant's Performance Claim:
The combined data from the two field sites reported in the TER(Heritage Marketplace
and Lake Stevens) indicate that the performance of a StormFilter system configured for
inline bypass with ZPGTM media and a hydraulic loading rate of l gpm/ft2 of media
surface area meets Ecology performance goals for Basic Treatment.
Ecology's Recommendations:
Based on the weight of the evidence and using its best professional judgment, Ecology
finds that:
• StormFilter, using ZPGTM media and operating at a hydraulic loading rate of no more
than 1 gpm/ft2 of media surface area, is expected to provide effective stormwater
treatment achieving Ecology's Basic Treatment(TSS removal)performance goals.
Contech demonstrated this is through field and laboratory testing performed in
accordance with the approved protocol. StormFilter is deemed satisfactory with
respect to factors other than treatment performance (e.g., maintenance; see the
protocol's Appendix B for complete list).
CONTECH-StormFiltere GULD Maintenance Update(November 2012) Page 15
Findings of Fact:
• Influent TSS concentrations and particle size distributions were generally within the
range of what would be considered"typical" for western Washington (silt to silt
loam).
• Contech sampled thirty-two (32) storm events at two sites for storms from April 2003
to March 2004,of which Contech deemed twenty-two (22)as "qualified" and were
therefore included in the data analysis set.
• Statistical analysis of these 22 storm events verifies the data set's adequacy.
• Analyzing all 22 qualifying events, the average influent and effluent concentrations
and aggregate pollutant load reduction are 114 mg/L, 25 mg/L, and 82%,
respectively.
• Analyzing all 22 qualifying events based on the estimated average flow rate during
the event(versus the measured peak flow rate), and more heavily weighting those
events near the design rate (versus events either far above or well below the design
rate) does not significantly affect the reported results.
• For the 7 qualifying events with influent TSS concentrations greater than 100 mg/L,
the average influent and effluent concentrations and aggregate pollutant load
reduction are 241 mg/L, 34 mg/L, and 89%, respectively. If the 2 of 7 events that
exceed the maximum 300 mg/L specified in Ecology's guidelines are excluded, the
average influent and effluent concentrations and aggregate pollutant load reduction
are 158 mg/L, 35 mg/L, and 78%, respectively.
• For the 15 qualifying events with influent TSS concentrations less than 100 mg/L, the
average influent and effluent concentrations and aggregate pollutant load reduction
are 55 mg/L, 20 mg/L, and 61%, respectively. If the 6 of 15 events that fall below the
minimum 33 mg/L TSS specified in Ecology's guidelines are excluded,the average
influent and effluent concentrations and aggregate pollutant load reduction are 78
mg/L, 26 mg/L, and 67%, respectively.
• For the 8 qualifying events with peak discharge exceeding design flow(ranging from
120 to 257%of the design rate), results ranged from 52%to 96%TSS removal, with
an average of 72%.
• Due to the characteristics of the hydrographs, the field results generally reflect flows
below(ranging between 20 and 60 percent of)the tested facilities' design rate.
During these sub-design flow rate periods, some of the cartridges operate at or near
their individual full design flow rate (generally between 4 and 7.5 GPM for an 18"
cartridge effective height) because their float valves have opened. Float valves
remain closed on the remaining cartridges, which operate at their base "trickle"rate
of 1 to 1.5 GPM.
• Laboratory testing using U.S. Silica's Sil-Co-Sil 106 fine silica product showed an
average 87%TSS removal for testing at 7.5 GPM per cartridge (100%design flow
rate).
• Other relevant testing at I-5 Lake Union, Greenville Yards (New Jersey), and Ski Run
Marina(Lake Tahoe) facilities shows consistent TSS removals in the 75 to 85%
range. Note that I-5 Lake Union was operated at 50%, 100%, and 125%of design
flow.
CONTECH-StormFiltero GULD Maintenance Update(November 2012) Page 16
I
• SMI's application included a satisfactory"Factors other than treatment performance"
discussion.
Note: Ecology's 80% TSS removal goal applies to 100 mg/l and greater influent TSS.
Below 100 mg/L influent TSS, the goal is 20 mg/L effluent TSS.
Technology Description:
The Stormwater Management StormFilter(StormFilter), a flow-through stormwater
filtration system, improves the quality of stormwater runoff from the urban environment
by removing pollutants. The StormFilter is used to treat runoff from a wide variety of
sites including, but not limited to: retail and commercial development, residential streets,
urban roadways, freeways, and industrial sites such as shipyards, foundries, etc.
Operation:
The StormFilter is typically comprised of a vault that houses rechargeable, media-filled,
filter cartridges. Various media may be used, but this designation covers only the zeolite-
perlite-granulated activated carbon (ZPGTM)medium. Stormwater from storm drains is
percolated through these media-filled cartridges, which trap particulates and may remove
pollutants such as dissolved metals, nutrients, and hydrocarbons. During the filtering
process, the StormFilter system also removes surface scum and floating oil and grease.
Once filtered through the media, the treated stormwater is directed to a collection pipe or
discharged to an open channel drainage way.
This document includes a bypass schematic for flow rates exceeding the water quality
design flow rate on page 8.
StormFilter Configurations:
Contech offers the StormFilter in multiple configurations: precast, high flow, catch basin,
curb inlet, linear, volume, corrugated metal pipe, dry-well, and CON/Span form. Most
configurations use pre-manufactured units to ease the design and installation process.
Systems may be either uncovered or covered underground units.
The typical precast StormFilter unit is composed of three sections: the energy dissipater,
the filtration bay, and the outlet sump. As Stormwater enters the inlet of the StormFilter
vault through the inlet pipe, piping directs stormwater through the energy dissipater into
the filtration bay where treatment will take place. Once in the filtration bay, the
-- stormwater ponds and percolates horizontally through the media contained in the
StormFilter cartridges. After passing through the media, the treated water in each
cartridge collects in the cartridge's center tube from where piping directs it into the outlet
sump by a High Flow Conduit under-drain manifold. The treated water in the outlet
sump discharges through the single outlet pipe to a collection pipe or to an open channel
drainage way. In some applications where you anticipate heavy grit loads, pretreatment
by settling may be necessary.
CONTECH-StormFilter®GULD Maintenance Update(November 2012) P age 17
_8'x 16"5TORMFILTER
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(IF REQUIRED)
i
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Figure 1. Stormwater Management StormFilter Configuration with Bypass
CONTECH-StormFilter®GULD Maintenance Update(November 2012) Page 18
AIR LOCK CAP WITH CHECK VALVE\ LIFTING TAB
FLOAT VALVE
-I OUTER MESH
FILTER MEDIA !
4000
CENTER TUBE
--- SCRUBBING REGULATOR
UNFILTERED WATER
UNFILTERED WATER
'[RED WATER
UNDER-DRAIN MANIFOLD
I
FILTERED WATER
VAULT FLOOR
UNDER.DRAIN MANIFOLD
CAST INTO VAULT FLOOR
Figure 2. The StormFilter Cartridge
Cartridge Operation:
As the water level in the filtration bay begins to rise, stormwater enters the StormFilter
cartridge. Stormwater in the cartridge percolates horizontally through the filter media
and passes into the cartridge's center tube, where the float in the cartridge is in a closed
(downward)position. As the water level in the filtration bay continues to rise, more
water passes through the filter media and into the cartridge's center tube. The air in the
cartridge is displaced by the water and purged from beneath the filter hood through the
one-way check valve located in the cap. Once water fills the center tube there is enough
buoyant force on the float to open the float valve and allow the treated water to flow into
the under-drain manifold. As the treated water drains, it tries to pull in air behind it. This
causes the check valve to close, initiating a siphon that draws polluted water throughout
the full surface area and volume of the filter. Thus, the entire filter cartridge is used to
filter water throughout the duration of the storm, regardless of the water surface elevation
in the filtration bay. This continues until the water surface elevation drops to the
elevation of the scrubbing regulators. At this point, the siphon begins to break and air is
quickly drawn beneath the hood through the scrubbing regulators, causing energetic
bubbling between the inner surface of the hood and the outer surface of the filter. This
bubbling agitates and cleans the surface of the filter, releasing accumulated sediments on
the surface, flushing them from beneath the hood, and allowing them to settle to the vault
floor.
Adjustable cartridge flow rate:
Inherent to the design of the StormFilter is the ability to control the individual cartridge
flow rate with an orifice-control disc placed at the base of the cartridge. Depending on
the treatment requirements and on the pollutant characteristics of the influent stream as
CONTECH-StormFilter®GULD Maintenance Update(November 2012) Page 19
specified in the CONTECH Product Design Manual,the flow rate may be adjusted
through the filter cartridges. By decreasing the flow rate through the filter cartridges,the
influent contact time with the media is increased and the water velocity through the
system is decreased, thus increasing both the level of treatment and the solids removal
efficiencies of the filters, respectively(de Ridder, 2002).
Recommended research and development:
Ecology encourages CONTECH to pursue continuous improvements to the Storm Filter.
To that end, the following actions are recommended:
• Determine, through laboratory testing, the relationship between accumulated solids
and flow rate through the cartridge containing the ZPGTM media. Completed 11/05.
• Determine the system's capabilities to meet Ecology's enhanced,phosphorus, and oil
treatment goals.
• Develop easy-to-implement methods of determining that a StormFilter facility
requires maintenance (cleaning and filter replacement).
Contact Information:
Applicant Contact: Sean Darcy
Contech Engineered Solutions
11835 NE Glenn Widing Drive
Portland, OR, 97220
503-258-3105
sdarcy@conteches.com
Applicant Web link http://www.conteches.com/
Ecology web link: http://www.ecy.Wa.goy/programs/wq/stormwater/newtech/index.html
Ecology Contact: Douglas C. Howie, P.E.
Department of Ecology
Water Quality Program
(360)407-6444
douglas.howie(kecy.wa.gov
Revision History
Date Revision
Jan 2005 Original Use Level Designation
Dec 2007 Revision
May 2012 Maintenance requirements updated
November 2012 Design Storm and Maintenance requirements updated
January 2013 Updated format to match Ecology standard format
CONTECH-StormFiltere GULD Maintenance Update(November 2012) Page 110