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HomeMy WebLinkAboutU120081 Technical Information Report (TIR)
for
Renton Municipal Airport
Taxiway B System Rehabilitation
Phase I and Phase II
;��
Owner: �cd
City of Renton 1
1055 South Grady Way
Renton, WA 98057 0 V
1
Y
October 2012
[M
City of Renton
Planninq Division
OCT 18 N11
Technical Information Report (TIR)
for
Renton Municipal Airport
Taxiway B System Rehabilitation —
North Portion Reconstruction &
Airfield Signage Modifications
Phase I
Owner:
City of Renton
1055 South Grady Way
Renton, WA 98057
October 2012
Technical Information Report (TIR)
Renton Municipal Airport
Taxiway B System Rehabilitation — North Portion Reconstruction &
Airfield Signage Modifications
Phase I
October 2012
The engineering material and data contained in this report were prepared under
the supervision and direction of the undersigned, whose seal as a registered
professional engineer is affixed below.
T.
Q. 1�%V �1
/40/1 71t Z-
45$92
Benjamin Sommer, P.E.
Project Engineer
728 134th Street SW, Suite 200
Everett, WA 98204
425-741-3800(Fax 425-741-3900)
File No.232010.007
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I -i -
Technical Information Report(TIR) ' ' 'I i1i Fr. 'I ' '
Contents
SECTION 1: PROJECT OVERVIEW.......................................................................................1
INTRODUCTION..........................................................................................................................................................I
PROJECTDESCRIPTION..............................................................................................................................................I
PROJECTLOCATION...................................................................................................................................................I
EXISTINGSITE CONDITIONS......................................................................................................................................1
PROPOSEDCONDITIONS.............................................................................................................................................2
SOILS.........................................................................................................................................................................3
SECTION 2: CONDITIONS AND REQUIREMENTS SUMMARY....................................14
CORE REQUIREMENT 1: DISCHARGE AT THE NATURAL LOCATION.........................................................................14
CORE REQUIREMENT 2: OFF-SITE ANALYSIS..........................................................................................................14
CORE REQUIREMENT 3: FLOW CONTROL................................................................................................................14
CORE REQUIREMENT 4: CONVEYANCE SYSTEM .....................................................................................................14
CORE REQUIREMENT 5: EROSION AND SEDIMENT CONTROL..................................................................................14
CORE REQUIREMENT 6: MAINTENANCE AND OPERATIONS.....................................................................................14
CORE REQUIREMENT 7: FINANCIAL GUARANTEES AND LIABILITY.........................................................................15
CORE REQUIREMENT 8: WATER QUALITY..............................................................................................................15
SPECIAL REQUIREMENT 1: OTHER ADOPTED AREA-SPECIFIC REQUIREMENTS.......................................................15
SPECIAL REQUIREMENT 2: FLOOD HAZARD AREA DELINEATION...........................................................................15
SPECIAL REQUIREMENT 3: FLOOD PROTECTION FACILITIES...................................................................................16
SPECIAL REQUIREMENT 4: SOURCE CONTROL........................................................................................................16
SPECIAL REQUIREMENT 5: OIL CONTROL...............................................................................................................16
SPECIAL REQUIREMENT 6: AQUIFER PROTECTION AREA........................................................................................17
SECTION3: OFF-SITE ANALYSIS........................................................................................18
STUDYAREA...........................................................................................................................................................18
RESOURCEREVIEW.................................................................................................................................................18
FIELDINSPECTION...................................................................................................................................................19
DRAINAGE SYSTEM DESCRIPTION AND PROBLEM DESCRIPTION.............................................................................2.0
SECTION 4: FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND
DESIGN........................................................................................................................................23
PART A-EXISTING SITE HYDROLOGY....................................................................................................................23
PART B-DEVELOPED SITE HYDROLOGY................................................................................................................23
PART C-PERFORMANCE STANDARDS ....................................................................................................................24
PART D-FLOW CONTROL SYSTEM.........................................................................................................................24
PART E-WATER QUALITY SYSTEM .......................................................................................................................24
SECTION 5: CONVEYANCE SYSTEM ANALYSIS AND DESIGN..................................29
EXISTING CONVEYANCE SYSTEM............................................................................................................................29
PROPOSED CONVEYANCE SYSTEM..........................................................................................................................29
SECTION 6: SPECIAL REPORTS AND STUDIES..............................................................32
SECTION 7: OTHER PERMITS..............................................................................................33
SECTION 8: CSWPPP ANALYSIS AND DESIGN................................................................34
ESCMEASURES ......................................................................................................................................................34
RECOMMENDED CONSTRUCTION SEQUENCE(EROSION AND SEDIMENT CONTROL)................................................35
SWPPSPLAN DESIGN.............................................................................................................................................36
SECTION 9: BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION
OFCOVENANT..........................................................................................................................37
BOND QUANTITIES WORKSHEET.............................................................................................................................37
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I - ii -
Technical Information Report (TIR) F ' 'I j,tr.R.I ' '
FLOW CONTROL AND WATER QUALITY FACILITY SUMMARY SHEET AND SKETCH.................................................37
DECLARATION OF COVENANT FOR PRIVATELY MAINTAINED FLOW CONTROL AND WQ FACILITIES......................37
DECLARATION OF COVENANT FOR PRIVATELY MAINTAINED FLOW CONTROL BMPs............................................37
SECTION 10: OPERATIONS AND MAINTENANCE MANUAL ......................................38
SECTION11: REFERENCES..................................................................................................39
List of Figures
FIGURE 1-1. TIR WORKSHEET................................................................................................. 4
FIGURE1-2. VICINITY MAP. .................................................................................................... 9
FIGURE 1-3. DRAINAGE BASIN & SITE CHARACTERISTICS.......................................... 10
FIGURE1-4. TW B SOIL MAP. ................................................................................................ 11
FIGURE 3-1. OFFSITE ANALYSIS MAP................................................................................. 21
FIGURE 3-2. OFFSITE ANALYSIS DRAINAGE SYSTEM TABLE......................................22
FIGURE 4-1. WATER QUALITY BASIN MAP.......................................................................27
FIGURE 4-2. POLLUTION-GENERATING SURFACE TREATMENT TRADES. ...............28
List of Tables
TABLE 1-1. PROJECT SITE LAND COVER DESIGNATION................................................. 2
TABLE 2-1. OTHER ADOPTED AREA-SPECIFIC REQUIREMENTS................................. 15 -
TABLE 4-1. PERFORMANCE STANDARDS.......................................................................... 24
TABLE 4-2. WET BIOFILTRATION SWALES. ...................................................................... 25
TABLE 4-3. WATER QUALITY TREATMENT AREAS........................................................ 25
TABLE 4-4. POLLUTION-GENERATING SURFACE TREATMENT TRADES.................. 26
TABLE 6-1. SPECIAL REPORTS AND STUDIES. ................................................................. 32
TABLE7-1. OTHER PERMITS................................................................................................. 33
Appendices
APPENDIX A—GEOTECHNICAL REPORT
APPENDIX B — CITY OF RENTON SENSITIVE AREAS
APPENDIX C—WATER QUALITY CALCULATIONS
APPENDIX D—CONVEYANCE SYSTEM CALCULATIONS
APPENDIX E—BOND QUANTITIES WORKSHEET
APPENDIX F—FLOW CONTROL AND WATER FACILITY SUMMARY SHEET
APPENDIX G—OPERATION AND MAINTENANCE MANUAL
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I - iii -
Technical Information Report (TIR)
SECTION 1: PROJECT OVERVIEW
Introduction
The Taxiway B System Rehabilitation project will be constructed in two phases. Phase I, the
north end of the project, will be constructed during the spring and early summer of 2013.
Phase II, the south end of the project, is scheduled to be constructed in late summer and early fall
of 2013 due to Federal Aviation Administration(FAA) funding constraints. The following
passages describe the project site area for Phase I.
Project Description
Phase I consists of reconstructing the portion of Taxiway B lying north of the"s-curve"jog, near
the midway of Runway 16-34. This area of the project will include reconstruction of the taxiway
to create a crowned surface, construction of new underdrains along both sides of the taxiway,
upgrades to the storm drainage facilities, pavement striping, directional safety signage, and
taxiway edge lighting.
The upgrade to the storm drainage system includes the replacement of several failing concrete
drainage lines beneath Taxiways B, M, and N with ductile iron pipe(DIP). New drainage
structures will be constructed to facilitate capturing stormwater from the east crowned area of
Runway 16-34, the east crowned area of Taxiway B, and the turf infield areas between
Runway 16-34 and Taxiway B. The facilities for Phase I will be designed in accordance with the
City of Renton's 2010 Amendment to King County's 2009 Surface Water Design Manual
(KCSWDM).
A Technical Information Report (TIR) Worksheet was developed for the project to describe the
site area and summarize the proposed drainage features for Phase I. This document is included as
Figure 1-1.
Project Location
The Renton Municipal Airport is located along the eastern side of Parcel Number 0723059007,
within the jurisdiction of the City of Renton. The airport is bounded on the north by Lake
Washington, on the east by Logan Avenue North, on the south by Airport Way, and on the west
by Rainier Avenue North. The Public Land Survey System (PLSS) identifies the area as the
Southwest and Northwest Quarter of Section 7, Township 23 North, Range 5 East. The physical
address of the site is 289 Perimeter Road West, Renton, Washington. The site contains
approximately 169 acres (AC). Figure 1-2 identifies the location of the project site.
Existing Site Conditions
The existing site is fully developed and generally flat across the airfield area. The steepest slope
within the parcel is a 5 percent grade. The site consists of building structures and hangars,
asphalt paving, and grass infield areas. In the area of the project, the taxiway and runway slope
inward toward the grass infield area, where surface water is directed,through depressions or
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I - 1 -
Technical Information Report (TIR) t
swales, toward catch basins near the western side of Taxiway B. The flow is collected in the
catch basins, diverted through a series of pipes and catch basins, and then discharged through
outfalls along the western side of Cedar River. Figure 1-3 breaks down the project area into
five drainage subbasins and identifies the existing and proposed discharge locations.
Proposed Conditions
The project proposes to rehabilitate the Taxiway B area by removing the existing asphalt surface
and importing fill materials to raise and crown the facility. It is anticipated that approximately
2,250 cubic yards of gravel import borrow material will be required to elevate the renovated
taxiway for Phase I. The renovated taxiway will consist of new and replaced impervious
surfacing. The total increase of impervious surfacing equates to roughly 0.5 percent over the
existing impervious taxiway. Table 1-1 identifies the existing and proposed project site land
cover areas.
Table 1-1. Project Site Land Cover Designation.
Area
Land Cover Type
(AC)
Untreated Non-targeted Impervious Surfacing 5.47
Treated Non-targeted Impervious Surfacing 1.53
Replaced Impervious Surfacing 2.40
New Impervious Surfacing 0.01
Pervious Surfacing 8.09
Total 17.50
The proposed surface water drainage facilities consist of wet biofiltration swales, filter strips,
catch basins, DIP, and high-density polyethylene(HDPE)pipe. Along the eastern side of the
taxiway crown, surface water will typically be collected and conveyed through catch basins and
sent to the western side of the taxiway, within the grass infield area. These concentrated flows
will be discharged into a flow splitter device for water quality measures. The flow splitters have
been sized to divert the required water flow/volume for treatment and send the remaining water
through a bypass system. Water quality for the concentrated flows shall be conveyed through a
wet biofiltration swale. The swale has been designed to meet the KCSWDM basic treatment
criterion of removing 80 percent of the total suspended solids (TSS) for flows or volumes up to
the water quality design flow/volume. After leaving the swale, the flow will be collected in a
catch basin and diverted toward the east through a series of surface water facilities and
discharged to Cedar River.
Along the western side of the taxiway crown, all nonconcentrated flows will be treated by filter
strips. The infield area will be graded to convey this surface flow to catch basins, where it will
combine with the treated flow from the wet biofiltration swale. For additional information
regarding the proposed development conditions, please refer to Sections 4 and 5 of this report.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I -2 -
Technical Information Report (TIR) ' ' '
Soils
According to the Soil Conservation Service Soil Survey for King County, the soil deposits in the
vicinity of the airport are classified as Urban (Ur). Figure 1-4 identifies the location of the site
for Phase I and its respective soil designation.
A geotechnical report and amendment was prepared for this project as part of the design process.
The final version of the geotechnical report was completed in October 2012. It appears from the
investigation that the existing pavement subbase soils consist of fills ranging from 0.5 to 2.2 feet
in depth below the existing surface. This material is composed of sandy gravel, sand to silty
sand, and dredge fill. Underneath the fill material, the native soil consists of soft organic silt
ranging from 1.2 to 3.2 feet in depth.
The geotechnical exploration identified perched groundwater in 3 of the test pits, at depths of
3.8, 3.5, and 3.6 feet. Groundwater seepage was also observed in several core/hand borings,
ranging from 2.7 to 5.5 feet below the existing ground surface. It is anticipated that the level of
groundwater in this area will fluctuate depending on the season and water height of the adjacent
Cedar River. For additional information regarding the subsurface layers, please refer to the
Geotechnical Report in Appendix A.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I - 3 -
Technical Information Report (TIR)
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
FIGURE 1-1
Part 1 PROJECT OWNER AND Part 2 PROJECT LOCATION AND
PROJECT ENGINEER DESCRIPTION
Project Owner City of Renton Project Name TW B Rehabilitation
Phone (425) 430-7471 DDES Permit#
Address 616 West Perimeter Road, Location Township 23 North
Unit A; Renton, WA 98057 Range 5 East
Project Engineer Benjamin Sommer, PE Section 7
Company Reid Middleton, Inc. Site Address 289 West Perimeter Road
Phone 425 741-3800 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/
❑ FEMA Floodplain
® Clearing and Grading ❑ ESA Section 7
❑ Right-of-Way Use ❑ COE Wetlands
❑ Other ❑ Other
Part 5 PLAN AND REPORT INFORMATION
Technical Information Report Site Improvement Plan (Engr. Plans)
Type of Drainage Review Full / Targeted / Type (circle one): Full / Modified /
(circle): Large Site Small Site
Date (include revision Date (include revision
dates): dates):
Date of Final: Date of Final:
Part 6 ADJUSTMENT APPROVALS
Type (circle one): Standard / Complex / Preapplication / Experimental/ Blanket
Description: (include conditions in TIR Section 2)
N/A
Date of Approval:
2009 Surface Water Design Manual 1/9/2009
I
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Part 7 MONITORING REQUIREMENTS
Monitoring Required: Yes / No Describe:
Start Date:
Completion Date:
Part 8 SITE COMMUNITY AND DRAINAGE BASIN
Community Plan :
Special District Overlays:
Drainage Basin:Lower Cedar River, Cedar Outfall Sub-basin
Stormwater Requirements:
Part 9 ONSITE AND ADJACENT SENSITIVE AREAS
® River/Stream Cedar River ❑ Steep Slope
® Lake Lake Washington ❑ Erosion Hazard
❑ Wetlands ❑ Landslide Hazard
❑ Closed Depression ❑ Coal Mine Hazard
® Floodplain Lake Washington/Cedar River ® Seismic Hazard High Seismic Severity
® Other High Liquefaction Susceptibility ❑ Habitat Protection
Part 10 SOILS
Soil Type Slopes Erosion Potential
Ur
® High Groundwater Table (within 5 feet) ❑ Sole Source Aquifer
❑ Other ❑ Seeps/Springs
❑ Additional Sheets Attached
2009 Surface Water Design Manual 1/9/2009
2
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
LJ
❑ Additional Sheets Attached
Part 12 TIR SUMMARY SHEET (provide one TIR Summary Sheet per Threshold Discharge Area
Threshold Discharge Area:
name or description)
Core Requirements (all 8 apply)
Discharge at Natural Location Number of Natural Discharge Locations:
Offsite Analysis Level: 1 / 2 / 3 dated: 06/04/12
Flow Control N/A Level: 1 / 2 / 3 or Exemption Number
Incl. facility summary sheet Small Site BMPs
Conveyance System Spill containment located at:
Erosion and Sediment Control ESC Site Supervisor: Contractor provide prior to construction.
Contact Phone: Contractor will be selected by public bid.
After Hours Phone:
Maintenance and Operation Responsibility: Private / Public
If Private, Maintenance Log Required: Yes /No
Financial Guarantees and Provided: Yes / No
Liability
Water Quality Type: Basic / Sens. Lake / Enhanced Basicm / Bog
(include facility summary sheet) or Exemption No.
Landscape Management Plan: Yes / No
Special Requirements as applicable)
Area Specific Drainage Type: CDA/SDO/ MDP/ BP/ LMP/Shared Fac. / None
Requirements Name:
Floodplain/Floodway Delineation Type: Major / Minor / Exemption / None
100-year Base Flood Elevation (or range):
Datum:
Flood Protection Facilities Describe: Flood Wall
Source Control Describe landuse: Airport
(comm./industrial landuse) Describe any structural controls:
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 ® Stabilize Exposed Surfaces
® Cover Measures ® Remove and Restore Temporary ESC Facilities
® Perimeter Protection ® Clean and Remove All Silt and Debris, Ensure
® Traffic Area Stabilization Operation of Permanent Facilities
® Sediment Retention ❑ Flag Limits of SAO and open space
preservation areas
Ell Surface Water Collection preservation
® Dewatering Control
® 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 Swale, Filter Strip
❑ Infiltration ❑ Wetpool
❑ Regional Facility ❑ Media Filtration
❑ Shared Facility ❑ Oil Control
❑ Flow Control ® Spill Control CB w/Tee
BMPs
® Flow Control BMPs Basic Dispersion/
❑ Other
❑ Other Sheet Flow
2009 Surface Water Design Manual 1/9/2009
4
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 N/A ❑ Other N/A
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.
Signed/Date
2009 Surface Water Design Manual 1/9/2009
5
CANADA
- - - - - - - - - - - - - - - - -
USA
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FIGURE 1-2
-----_.
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-BASIN E
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EXISTING ASPHALT a -
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———— — — — OUTFACE PIPE EXISTING AND % TO RIVER
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-- —— — I DISCHARGE POINT ;a I EXISTING SLOT EXISTING AND
EXISTING AND — DRAIN
FOR S
PROPOSED — — SUB-BASIN B I OUTFACE PIPE OUTFALL PIPE PROPOSED DISCHARGE POINT EXISTING AND
DISCHARGE POINT TO RIVER TO RIVER PROPOSED
- - FOR SUB-BASIN A I I FOR SUB-BASIN D I DISCHARGE POINT
EXISTING ASPHALT I FOR SUB-BASIN E(TIEDOWN AREA) EXISTING AND
UTF PIPE I I PROPOSED
O ACE FALL I DISCHARGE POINT
TO RIVER __j FOR SUB-BASIN C
PROPOSED
PROJECT LIMITS
LEGEND:
REPLACED/NEW
ASPHALT PAVEMENT
> SWALE
FLOW DIRECTION
SCALE IN FEET
60 0 60 120
DRAINAGE BASINS & SITE CHARACTERISTICS Figure 1 -3
7261340StwtSN Sule20 Renton Airport
Everell fthh lm 98204
k,425 741-3800
Soil Map—King County Area,Washington
(FIGURE 1-4:TW B Soil Map)
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47°29'48" 47°29'48"
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uNi 558930 559020 559110 559200 559290 55180 vNi
Map Scale:1:3,550 rf printed on Asize(8.5"x 11")sheet.
fV
N Meters
^ 0 30 60 120 180 N
Feet
0 100 200 400 600
USDA Natural Resources Web Soil Survey 5/30/2012
Conservation Service National Cooperative Soil Survey Page 1 of 3
Soil Map—King County Area,Washington
(FIGURE 1-4:TW B Soil Map)
MAP LEGEND MAP INFORMATION
Area of Interest(AOI) { Very Stony Spot Map Scale: 1:3,550 if printed on A size(8.5"X 11")sheet.
Area of Interest(AOI) Wet Spot The soil surveys that comprise your AOI were mapped at 1:24,000.
Soils
Other[ I Soil Map Units Warning:Soil Map may not be valid at this scale.
Special Point Features Special Line Features Enlargement of maps beyond the scale of mapping can cause
Blowout Gully misunderstanding of the detail of mapping and accuracy of soil line
�}
Short Steep Slope placement.The maps do not show the small areas of contrasting
® Borrow Pit soils that could have been shown at a more detailed scale.
Other
X Clay Spot
Political Features Please rely on the bar scale on each map sheet for accurate map
Closed Depression Cities measurements.
X Gravel Pit Water Features Source of Map: Natural Resources Conservation Service
Gravelly Spot Streams and Canals Web Soil Survey URL: http://websoilsurvey.nres.usda.gov
Coordinate System: UTM Zone 1 ON NAD83
Landfill Transportation
This product is generated from the USDA-NRCS certified data as of
A. Lava Flow +++ Rails the version date(s)listed below.
41& Marsh or swamp Interstate Highways Soil Survey Area: King County Area,Washington
%I Mine or Quarry US Routes Survey Area Data: Version 6,Sep 22,2009
Miscellaneous Water Major Roads Date(s)aerial images were photographed: 7/24/2006
® Perennial Water iv Local Roads The orthophoto or other base map on which the soil lines were
compiled and digitized probably differs from the background
Rock Outcrop imagery displayed on these maps.As a result,some minor shifting
+ Saline Spot of map unit boundaries may be evident.
Sandy Spot
Severely Eroded Spot
4 Sinkhole
?> Slide or Slip
Af Sodic Spot
aye Spoil Area
d Stony Spot
tSDA Natural Resources Web Soil Survey 5/30/2012
�� Conservation Service National Coonerative Soil Survev Page 2 of 3
Soil Map—King County Area,Washington FIGURE 1-4:TW B Soil Map
Map Unit Legend
King County Area,Washington(WA633)
Map Unit Symbol Map Unit Name Acres in AOI Percent of AOI
Ur Urban land 25.8 99.7%
W Water 0.1 0.3%
Totals for Area of Interest 25.9 100.0%
USDA Natural Resources Web Soil Survey 5/30/2012
® Conservation Service National Cooperative Soil Survey Page 3 of 3
SECTION 2: CONDITIONS AND REQUIREMENTS SUMMARY
The following describes how the Core and Special Requirements from the City of Renton's 2010
SWDM Amendment apply to this project.
Core Requirement 1: Discharge at the Natural Location
The project will not change the stormwater discharge locations. For additional information on the
discharge points, refer to Section 3, Off-site Analysis.
Core Requirement 2: Off-site Analysis
A Downstream Drainage Inventory is addressed in Section 3, Off-site Analysis.
Core Requirement 3: Flow Control
Flow control facilities are not proposed for this project. The project site discharges directly into
Cedar River, downstream of the Taylor Creek confluence and within the backwater of Lake
Washington. All new stormwater conveyance facilities have been designed to meet the discharge
requirements as outlined in the "Direct Discharge Exemption" section of the City of Renton's
SWDM Amendment.
Best Management Practices (BMPs) for flow control are used on the project site. These measures
typically consist of basic dispersion through sheet flow along the impervious taxiway surfacing.
These measures shall be installed in accordance with the requirements of the KCSWDM,
Appendix C.2.4.5.
Core Requirement 4: Conveyance System
The Rational Method and Manning's Equation were utilized to design and size the piping
facilities. All new stormwater conveyance systems were reviewed in relation to the 25-year peak
runoff event. For additional information on the conveyance system design, refer to Section 4,
Flow Control and Water Quality Facility Analysis and Design.
Core Requirement 5: Erosion and Sediment Control
An Erosion and Sediment Control (ESC) plan has been developed for this project. A detailed
summary of the required ESC measures can be found in Section 8, CSWPPP Analysis and
Design.
Core Requirement 6: Maintenance and Operations
Maintenance and operations of the proposed drainage facilities will be performed in compliance
with King County's Appendix A, Maintenance Requirements for Flow Control, Conveyance, and
WQ Facilities. Maintenance requirements for all applicable facilities have been included in
Appendix G.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase 1 - 14 -
Technical Information Report (TIR)
Core Requirement 7: Financial Guarantees and Liability
The Bond Quantity Worksheet and Flow Control and Water Facility Summary Sheet are
provided as part of Section 9, Bond Quantities, Facility Summaries, and Declaration of
Covenant. However, Declarations of Covenants are not required for this project since the City of
Renton owns and maintains the facilities. For additional information on these items, refer to
Appendix E, Bond Quantity Worksheet, and Appendix F, Flow Control and Water Facility
Summary Sheet.
Core Requirement 8: Water Quality
"Basic Water Quality" treatment standards apply to the project site. Wet biofiltration swales and
filter strips will be used to meet these standards. A summary of the water quality design facilities
can be found in Section 4, Flow Control and Water Quality Facility Analysis and Design.
Special Requirement 1: Other Adopted Area-Specific Requirements
A summary of other adopted area-specific requirements associated with the project site is
presented in Table 2-1.
Table 2-1. Other Adopted Area-Specific Requirements.
Regulations Required Comment
Master Drainage Plans(MDPs) No
Basin Plans(BPs) Yes King County's Lower Cedar River Basin Plan
Salmon Conservation Plans(SCPs) Yes WRIA 8 Cedar-Sammamish
Stormwater Compliance Plans(SWCPs) Yes National Pollutant Discharge Elimination System
(NPDES)Phase It
Flood Hazard Reduction Plan Updates Yes City's Critical Area Code RMC IV-4-3-050
(FHRPs)
Shared Facility Drainage Plans(SFDPs) No
A review of the specific drainage requirements, mandated by the area-specific requirements, has
been conducted. Any applicable regulations that were more stringent than the City of Renton's
SWDM Amendment have been applied to the proposed facilities.
From the review of the City of Renton 2009 Storm Water Management Program (SWMP) for the
NPDES Phase II, it was identified that an evaluation by City of Renton staff determined the
Renton Municipal Airport required an Industrial Facility NPDES Permit. It is our understanding,
from discussions with Airport staff, that the specific NPDES Permit has not been completed for
the facility at this time. However, a Stormwater Pollution Prevention Plan (SWPPP) for
construction activities will be developed as part of this overall project.
Special Requirement 2: Flood Hazard Area Delineation
The proposed project is not within the 100-year floodplain; therefore, delineation is not identified
on the improvement plans.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase 1 - 15 -
Technical Information Report (TIR)
DEPARTMENT OF COMMUNITY ® _Cirof�O�
AND ECONOMIC DEVELOPMENT '
M E M O R A N D U M
DATE: October 29, 2012
TO: Ron S.
CC: Kayren Kittrick
FROM: Arneta x7298
SUBJECT: TAXI B REHAB
PHASE 1 AND PHASE 2
I need to explain a little about this project to clear up any confusion.
Projects may and sometimes do submit plans for review prior to completion of the land
use action (green folder). They do so at their own risk but it is allowed.
That is what this project did so yes you have seen the project but not all of it.
Now we have all of it Phase I and Phase 2 of the storm and all of the plans.
There may be some duplication in the plans that I am sending but I wanted to make sure
that you were seeing the entire project.
Thank you! Call me if you have any questions.
Arneta x7298
iAmemo.doc
DEPARTMENT OF COMMUNITY City�f�O�
AND ECONOMIC DEVELOPMENT
M E M O R A N D U M
DATE: October 29, 2012
TO: Ron S.
CC: Kayren Kittrick
FROM: Arneta x7298
SUBJECT: TAXI B REHAB
PHASE 1 AND PHASE 2
1 need to explain a little about this project to clear up any confusion.
Projects may and sometimes do submit plans for review prior to completion of the land
use action (green folder). They do so at their own risk but it is allowed.
That is what this project did so yes you have seen the project but not all of it.
Now we have all of it Phase I and Phase 2 of the storm and all of the plans.
There may be some duplication in the plans that I am sending but I wanted to make sure
that you were seeing the entire project.
Thank you! Call me if you have any questions.
Arneta x7298
iAmemo.doc
Special Requirement 3: Flood Protection Facilities
The site possesses an existing flood protection wall east of Taxiway B. The proposed
improvements are not within the area of this facility nor do they include any upgrades to this
structure.
Special Requirement 4: Source Control
This Special Requirement is not necessary, since the project does not require a commercial
building or site development permit; however, it is included as part of this document. The
ongoing and future source control measures proposed for the project will comply with the City of
Renton's SWDM Amendment and King County's Stormwater Pollution Prevention Manual. The
following BMPs are specific to the proposed improvements:
Structural Source Control Measures
A-27: A Temporary Erosion and Sediment Control (TESC) plan has been developed for
the project site. TESC facilities shall be installed prior to any on-site grading activities.
Excessive amounts of surface water will be collected and pumped to a flow dispersal
system in order to prevent suspended sediments and potential oils from clogging the
TESC measures or being conveyed downstream. All proposed measures are in
conformance with the City of Renton's SWDM Amendment. The plan includes, but is
not limited to: check dams, bio-filter bags, straw wattles, catch basin sediment traps, and
covering of exposed soils.
Nonstructural Source Control Measures
A-17: Fueling operations for the construction equipment will occur on site. All fueling
will be conducted away from standing surface water in order to prevent possible release
into the drainage system. If a spill does occur during construction, the Contractor shall
contain and expose of contaminated materials in accordance with local and state
requirements.
A-26: Landscaping activities will practice the following BMPs: Chemicals will not be
applied directly to surface water, all manufacturers' recommendations and label
directions will be followed, and vegetation will not be disposed of in waterways or
drainage systems. Mulch or other erosion control measures will be utilized when soils are
exposed for more than one week during the dry season and two days during the rainy
season. Noxious plants will be avoided.
The proposed operation and maintenance guidelines for the above facilities have been included
in Appendix G, Operation and Maintenance Manual, in accordance with King County's
Stormwater Pollution Prevention Manual.
Special Requirement 5: Oil Control
The proposed improvements do not meet the definition of a high-use site requiring oil control.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase 1 - 16 -
Technical Information Report (TIR)
Special Requirement 6: Aquifer Protection Area
The project site is not located within an Aquifer Protection Zone; therefore, protection facilities
will not be provided.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I - 17 -
Technical Information Report (TIR) ' " '
SECTION 3: OFF-SITE ANALYSIS
A quantitative downstream, or off-site analysis, survey was conducted at and adjacent to the
project site. The analysis of the project area consisted of four main tasks: a review of the Study
Area, a Resource Review, a Field Inspection, and a Drainage System Description and Problem
Description write-up.
Study Area
A review of the project site was conducted, extending half a mile downstream of the natural
discharge location and a quarter of a mile upstream. It was not feasible to extend the inspection
to the required one mile downstream, since Cedar River discharges directly into Lake
Washington in less than that distance.
The purpose of this review is to identify the project site's impacts on the drainage area tributary
flow path. For this particular site, the surface water is conveyed from the infield runway/taxiway
area through swales to 12-inch-diameter pipe outfalls. The flow is discharged to Cedar River and
carried to Lake Washington, less than half a mile downstream.
Resource Review
A review of the applicable reports and studies of the general project area was included in the off-
site analysis. The coverage area consisted of the property a quarter of a mile upstream and half a
mile downstream of the site. The City of Renton's SWDM Amendment requires that the
following reference materials are reviewed:
• Sensitive Areas Folio
• Adopted Basin Plans/Basin Reconnaissance Summary Reports
• Floodplain/Floodway (FEMA) Maps
• King County Soil Survey
• Washington State Department of Ecology's (DOE) Polluted Waters List
• City of Renton Erosion Maps and Landslide Maps
• Wetlands Inventory Maps
From the evaluation of these reference materials, existing or potential issues were identified and
noted for the field inspection. The research identified the following sensitive areas within the
area of study: flood hazard, seismic hazard, and high liquefaction hazard. Upstream of the
project site, the adjacent properties are within Aquifer Protection Zone 1 and possess a moderate
to high susceptibility to liquefaction. Applicable maps of the City of Renton Sensitive Areas are
included in Appendix B of this report.
The Renton Municipal Airport is located within the Lower Cedar River Basin and Cedar Outfall
Subbasin. King County has developed a Lower Cedar River Basin Plan that provides an
overview of the area and proposes solutions to the issues of flooding,property damage, and
declining salmon and steelhead runs. Additionally,the plan recommends preventative measures
for maintaining water quality standards, groundwater supplies, and natural habitat within the
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I - 18 -
Technical Information Report (TIR)
basin. From the review of this document, it was noted that damage occurred to public facilities at
the airport during flood events in 1990 and 1995. The plan also identified that the overall water
quality in the river is"generally very good";however, it stated that sporadic exceedances of the
water standards have been recorded from fecal coliform bacteria generated by livestock and
failing septic tanks. It does not appear that the airport is a major contributor to these pollutants
within the river.
A review of the DOE's list of polluted waters (Section 303d) was conducted for Cedar River and
Lake Washington. This investigation identified that the project site discharges to a section of
Cedar River labeled as Category 5 Waters, which conveys flow directly downstream to an area
of Lake Washington marked as Category 2 Waters. A Category 2 label identifies water bodies
that are areas of concern for the DOE. This typically indicates waters where there is some
evidence of water quality issues but not enough to require a water quality improvements project.
However, a Category 5 designation marks a waterway violating one or more pollutant standards.
This information was considered when selecting water quality facilities for the project site.
A review of the City of Renton's Erosion and Landslide Maps identified adjacent properties west
of the airport property as carrying a potential for erosion hazards and landslide hazard
designations ranging from moderate to very high. The airport itself is relatively flat and not
directly impacted by the landslide hazard areas.
An evaluation of the City of Renton's Wetland Inventory Map was conducted for the project.
From the review, it did not appear that there were any documented wetlands on or within the
vicinity of the airport facility. No wetland areas have been observed during previous visits to the
site.
Field Inspection
A Level 1 field inspection was conducted at the project site on June 4, 2012. The weather was
overcast during this observation. The inspection encompassed an evaluation of existing catch j
basins near the flood wall (upstream of the outfalls) and downstream of the final discharge
location. The downstream analysis extended from the final discharge location to a point less than
half a mile downstream. The existing storm drainage system was reviewed earlier in the design
phase, on May 11, 2012.
The site's discharge piping extends east of Taxiway B to the outfall locations along Cedar River.
All existing outfalls are corrugated metal pipe (CMP) and fitted with `duckbill' style check
valves. From the discharge point, flow is conveyed to Lake Washington, less than half a mile
downstream. No signs of erosion, overtopping, or scouring were uncovered during the
inspection; however, dense vegetation covered the majority of the seawall area, obstructing a
thorough visual inspection. Please see Figure 3-1 for additional information and a depiction of
the off-site analysis area.
From an evaluation of the existing conveyance system prior to arriving on site, it appeared that
the existing outfall piping systems are undersized for the peak runoff events calculated by the
Rational Method. This evaluation is documented in Section 5, Conveyance System Analysis and
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I - 19 -
Technical Information Report (TIR) ' '
Design. As identified above, a review of these facilities during the field inspection was
conducted. It appeared that one catch basin near the flood wall, north side, exhibited a high level
of backwater within the structure from the outfall. It was assumed that this event was due to the
relatively flat slope of the outfall and the high water level of the river from seasonal runoff. The
water level in the river appeared to be only 4 to 5 feet deep.
Drainage System Description and Problem Description
The drainage system is combined within one Threshold Discharge Area because the outfalls are
located less than a quarter of a mile apart. Each outfall discharges to Cedar River, within Lake
Washington's backwater. The flow is conveyed into Lake Washington, less than half a mile
downstream.
The field inspection did not identify any signs of problem areas within the existing drainage
system. It was noted during discussions with Renton Municipal Airport staff that the site did not
possess existing drainage issues. See Figure 3-2, Off-site Analysis Drainage System Table, for an
outline of the items noted during the field inspection.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase 1 - 20 -
Technical Information Report (TIR) 1=111111011M '
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Renton Airport
728 131ih led SW We 200
Everett wmm*m 9m
Ph:425 741-3800
OFF-SITE ANALYSIS DRAINAGE SYSTEM TABLE
SURFACE WATER DESIGN MANUAL,CORE REQUIREMENT#2
FIGURE 3-2
Basin: Lower Cedar River Subbasin Name: Cedar Outfall Subbasin Number:
Symbol Drainage Drainage Slope ` Distance Existing Potential Observation of field
Component Type, Component from site Problems Problems inspector,resource
Name,and Size Description discharge reviewer,or resident
see map Type:sheet flow,Swale, drainage basin,vegetation, % 1/4 mi=1,320 ft, constrictions,under capacity,ponding, tributary area,likelihood of problem,
stream,channel,pipe, cover,depth;type of sensitive overtopping,flooding,habitat or oganism overflow pathways,potential impacts
pond,Size:diameter, area,volume destruction,scouring,bank sloughing,
surface area sedimentation,incision,other erosion
A Discharge Location 4'to 5'Depth of Channel VA 0 8 None None No evidence of erosion
13 River ChanneVLake Bed 10'Depth of Channel N/A 2000 ft None None No evidence of erosion
23-2010.007 Page 1 of 1 Offsite Drainage System
June 2012 Renton Municipal Airport City of Renton
SECTION 4: FLOW CONTROL AND WATER QUALITY FACILITY
ANALYSIS AND DESIGN
The proposed site area is divided into five subbasins for the existing and developed site
hydrology. The subbasins are divided according to the existing topography of the site. The
following sections will discuss these subbasins in greater detail as they relate to the existing or
developed site hydrology.
Part A—Existing Site Hydrology
The project area is located in the northeast region of the City of Renton's Municipal Airport.
Taxiway B is bordered by Runway 16-34 to the west and hangar buildings on the east. The
project site consists of approximately 17.5 AC of predominately developed land area. The
project site area is broken into five subbasins for the design of the stormwater facilities. These
subbasins were determined by reviewing the existing topography. A breakdown of the existing
and proposed land cover within the area is presented in Table 1-1.
The existing taxiway surface consists of impervious asphalt underlain by a compacted gravel
subgrade. The Soil Conservation Service Soil Survey for King County identifies the soil deposits
in the vicinity of the airport as Urban (Ur). From the geotechnical investigation conducted for
this project, it appears that the subbase soils consist of fills ranging from 0.5 to 2.2 feet in depth.
The material is composed of sandy gravel, sand to silty sand, and dredge fill material.
Underlying the fill material, the native soil consists of soft organic silt ranging from 1.2 to 3.2
feet below the surface. Perched groundwater was observed in 3 test pits, at depths ranging from
3.5 to 3.8 feet. It is anticipated that the level of groundwater is dependent on the season and the
height of the adjacent river.
The site area is graded to drain to catch basins within the grassy infield area. An existing
underdrain system runs along the eastern side of Runway 16-34 and discharges to the infield
catch basins. Flow is conveyed from these basins to the 12-inch-diameter outfalls, along the
eastern edge of the site, into Cedar River. Please refer to Figures 1-3 and 3-1 for more
information on the delineation, flow path, and acreage of areas contributing runoff to the existing
project site.
Part B—Developed Site Hydrology
The developed site hydrology consists of the same five subbasins as identified in the existing site
hydrology review. All areas drain from the infield area through the outfalls along the eastern side
of the site. A breakdown of the existing and proposed land cover within the area can be found in
Table 1-1.
Flow control facilities, as discussed previously, are not required for this project. Flow control
BMPs will be used where appropriate or necessary. A discussion of these facilities can be found
in Part D below.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I - 23 -
Technical Information Report (TIR) ' ' ' ` ' '
The proposed water quality facilities consist of wet biofiltration swales, filter strips, and flow
splitters. Flow splitters are required to divert the runoff into two flows: water quality and bypass
flow. The bypasses account for flows greater than the calculated water quality flow/volume for
the developed conditions. Water quality treatment will consist of a combination of filter strips
and wet biofiltration swales. These facilities are further detailed in Part E below.
Part C—Performance Standards
A summary of flow control, conveyance, water quality, and source and oil control performance
standards for the project is presented in Table 4-1. Calculation documents are provided in
Appendices C and D for the applicable standards.
Table 4-1. Performance Standards.
Category Performance Standards Source
Flow control facilities are not required.
Flow Control Flow Control BMPs required.
Manual Section 1.2.3.1
Conveyance System Capacity Developed 25-year Peak Storm Event Manual Section 1.2.4.1
Basic Treatment of the 2-year Storm Manual Section 1.2.8.1
Event for developed conditions Manual Section 6.2.1
Water Quality Treatment Wet Biofiltration Swales Manual Section 6.3.2
Basic Filter Strips Manual Section 6.3.4
Narrow Area Filter Strips Manual Section 6.3.5
Source Control Stormwater Pollution Prevention Manual Section 1.3.4
Manual
Oil Control N/A Manual Section 1.3.5
Part D—Flow Control System
As discussed in Core Requirement 3, Flow Control, the project site is exempt from providing
flow control facilities since the site discharges directly to a major receiving water body.
Therefore, flow control design and analysis are not included as part of this report.
Flow control BMPs will be installed where appropriate or necessary. These measures consist of
"Basic Dispersion"through sheet flow.
Part E—Water Quality System
Proposed Treatment System
The project site appears to fall within the category of"Basic Treatment" as defined by the
KCSWDM. Properties subject to this type of treatment are areas draining outside the drainage
basin of sensitive lakes or sphagnum bog wetlands. Basic Treatment criterion intends to remove
80 percent of the TSS for flows or volumes up to the water quality design flow or volume. The
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I - 24 -
Technical Information Report (TIR) "
remaining flow quantity is diverted around water quality facilities and passes untreated through
the system.
The KCSWDM requires that all water quality measures treat a minimum of 95 percent of the
annual average runoff volume in the 8-year time series, as determined by the King County
Resource Time Series (KCRTS) model. The designs of the facilities at the site are based on
treating 60 percent of the 2-year Peak Flow rates for a given targeted surface area. At this design
flow rate, the system will successfully treat the minimum required volume.
-- The project's surface water quality facilities consist of a combination of wet biofiltration swales
and filter strips provided to treat surface runoff from targeted pollution-generating surfaces.
Filter strips generally bound both sides of Taxiway B to treat sheet flow, while wet biofiltration
swales provide treatment to concentrated flows from the eastern crowned sections of
Subbasins C and D. The flow in this area is collected and conveyed from the eastern side of the
crowned taxiway to the grass infield west of Taxiway B. Table 4-2 identifies the design
information for the wet biofiltration swale.
Table 4-2. Wet Biofiltration Swales.
Basin Length Bottom Width Side Slope Longitudinal Slope Design Flow
(FT) (FT) T (FT/FT) (CFS
Subbasin C 100 20.0 4H:1 V 0.005 0.56
Subbasin D 100 20.0 4HA V 0.005 0.27
Flow splitters are proposed upstream of the wet biofiltration swales to control the rate of flow
through the facilities. The flow splitters have been designed to allow the required water
flow/volume for water treatment to pass through the wet biofiltration swales. The remaining
water volume will be diverted through a bypass system that runs parallel to the swales in below-
grade piping systems. The calculations for sizing the flow splitters have been included in
Appendix F, Water Quality Calculations.
A breakdown of the water quality areas within each Subbasin is defined in Table 4-3.
Calculations and computer printouts for these facilities have been included as Appendix C,
Water Quality Calculations. The locations of the water quality facilities are identified on
Figure 4-1.
Table 4-3. Water Quality Treatment Areas.
Treatment Type Subbasin A Subbasin B Subbasin C Subbasin D Subbasin E
(SF) (SF) SF (SF) (SF)
Area Treated by Filter Strip 1,610 10,975 17,700 7,470 3,170
Untreated Target Area 1,850 2,725 0 0 0
Area Treated by Wet Bioswale 0 0 85,290* 40,650 0
Total 3,460 13,700 102,990 48,120 3,170
*Includes non-target impervious area being treated(66,790 SF)
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I - 25 -
Technical Information Report (TIR)
Treatment Trades
The City of Renton's SW)M Amendment, Section 1.2.8.2.C, identifies that runoff from
pollution-generating surfaces may be released untreated if an existing non-targeted pollution-
generating surface of equivalent size and pollutant characteristics within the same watershed or
stream reach tributary area is treated on the project site. It is understood that this provision is
included as part of the manual to allow the designer flexibility to trade regions of target areas
that are not feasible to treat with water quality facilities.
Runoff from the airplane tie-down area east of Taxiway B is included as impervious area in the
water quality calculations for Subbasin C. This non-target surfacing area is not currently treated
with the existing facilities. Table 4-4 identifies these proposed areas of pollution-generating
surface treatment trades.
Table 4-4. Pollution-Generating Surface Treatment Trades.
Drainage Basin Treated Non-Target Area Untreated Target Area
(SF) (SF)
Subbasin A 0 1,850
Subbasin B 0 2,725
Subbasin C 66,790 0
Total 66,790 4,575
Please refer to Figure 4-2 for an illustration of these traded areas. Water quality BMPs will be
provided in these locations of untreated target areas to the extent possible.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase 1 - 26 -
Technical Information Report (TIR)
B-BASIN.A I SUB-BASIN B ( S�16 BASIN -- `"-" SUB-BASIN D SUB-BASIN E
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CONTRIBUTING AREA
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�WATER QUALITY TREATMENT BY SUB—BASIN FLOW DIRECTION
TREATMENT TYPE (SF)
A SUB-BASIN B SUB-BASIN C SUB-BASIN D SUB-BASIN E
(SF) (SF) (SF) (SF) (SF)
AREA TREATED BY FILTER STRIP 1,610 10,975 17,700 7.470 3,170
UNTREATED TARGET AREA 1,850 2,725 0 0 0 —
AREA TREATED BY BIOSWALE 0 0 85,290* 40,650 0
TOTAL 3,460 13,700 102,990 48,120 3,170
-INCLUDES NON—TARGET IMPERVIOUS AREA BEING TREATED (66,790 SF). REFER TO FIG 4-2 FOR A VISUAL DEPICTION SCALE IN FEET
OF THE PROPOSED TRADE AREAS.
60 0 60 120
WATER QUALITY BASIN MAP Figure 4-1
Renton Airport
720 1341Y Street SA We 200
Everett"on 98204
PE:425 741-M
-
SUB-BASIN B S�16-"�ASIN C----�—_—^—_—_—�—_-------- � "--�"---SUB-BASIN D --'
sub-�Su�a- SUB-BASIN E
--
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-
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iff TO RIVER TO RIVER TO RIVER
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UNTREATED TARGET
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TREATED
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> SWALE
�POLLUTION-GENERATING SURFACE TREATMENT TRADE FLOW DIRECTION
DRAINAGE BASIN TREATED NON-TARGET AREA UNTREATED TARGET AREA
(SF) (SF)
SUB-BASIN A 0 1,850
SUB-BASIN 8 0 2,725
SUB-BASIN C 66,790 0
TOTAL 66,790 4,575
SCALE IN FEET
60 0 60 120
POLLUTION-GENERATING SURFACE TREATMENT TRADES Figure 4-2
Renton Airport
728 134t6 Street SW Sale 200
Everett.Wm)mgtm 98204
Po:425 741-30110
SECTION 5: CONVEYANCE SYSTEM ANALYSIS AND DESIGN
An evaluation of the existing and proposed conveyance systems was conducted for this project.
This section provides an overview of the existing and proposed conveyance systems and outlines
the criteria utilized in design of the drainage facilities.
Existing Conveyance System
The existing storm drainage conveyance system was analyzed for conveyance of the 10-, 25-,
and 100-year peak storm runoff events. The Rational Method was used to identify the peak storm
runoff events for the project site, while Manning's Equation was used to determine the capacity
of the piping system. The calculations were reviewed to identify if the piping system could
handle the peak flow demands without backwatering. It appeared from this evaluation that the
existing conveyance system does not meet these requirements. Additional analysis was
conducted on this issue and is discussed in the Proposed Conveyance System section below.
The existing outfalls consist of 12-inch-diameter reinforced concrete pipelines that are relatively
flat in nature and do not possess the overall required capacity to meet the runoff storm events.
Sections of this system did pass the requirements of the peak storm runoff events;however, it
appears the limitations to the downstream system inadvertently backwaters into these facilities.
A meeting was held with the Renton Municipal Airport staff on June 4, 2012,to discuss the
calculation findings. From the discussion, it was understood that the Airport is planning to
develop a Capital Improvements Projects (CIP) program to address existing storm drainage
facilities on the site. The staff explained that backwater from the outfalls to the infield area has
not been observed from a storm event. However, the staff intends to include the replacement of
the existing 12-inch-diameter outfalls to Cedar River as part of the CIP program in order to
correct this potential issue from the peak runoff storm events. It was also noted that the invert
elevations for the outfalls was pulled from an older base map, utilizing the National Geodetic
Vertical Datum of 1929 (NGVD 29),provided by the Renton Municipal Airport staff. The
locations of the outfalls are outside the project area and were not surveyed as part of this project.
It is possible that the outfall system possesses additional capacity than currently anticipated.
Calculations for the existing and proposed conveyance systems have been included in
Appendix C.
Proposed Conveyance System
Proposed System Review
The proposed conveyance system intends to replace/relocate storm drainage facilities within the
areas of excavation. As conducted in the review of the existing conveyance system,the Rational
Method was used to determine the peak storm runoff events, while Manning's Equation was
used to size the conveyance system. The proposed facilities are constrained by the invert
elevations of the existing outfall system and the relatively flat terrain of the site. The piping
system was designed to fit the site limitations and convey flow to the existing outfall elevations.
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Following this design path, the proposed conveyance system did not appear to pass the 25-year
peak runoff event as determined by the Rational Method. Upsizing the pipe diameter or
steepening the slope of the facilities was not feasible due to the aforementioned site constraint
and/or lack of cover over the pipes. It is understood that the Rational Method is a conservative
approach to calculating runoff events, since this method does not factor in the attenuation effects
of the existing storage features within a basin. Therefore, the Western Washington Hydrology
Model (WWHM) was utilized to model the infield areas as a storage pond with a 12-inch-
diameter orifice. From this evaluation, it does not appear that the proposed system will adversely
impact the site. The maximum level of standing water was identified within Subbasin C, which
possessed approximately 6 inches for the 25-year and 8 inches for the 100-year peak runoff
events. At this level, potential ponding will be contained entirely within the infield areas, and the
proposed system will adequately drain the site for the peak runoff events. It will require the use
of hydraulic head from backwater to accomplish this task. Taking this approach, it is anticipated
that the site will drain within 10 hours of a peak event.
The conveyance system consists of pipes, culverts, catch basins,berms, and swales. Flow from
the non-target impervious surfacing (Runway 16-34), along the western edge of the project site,
will drain as sheet flow from the edge of the pavement and follow the sloped shoulder area
toward the middle of the infield. The infield will be sloped to direct the runway flow away from
the wet biofiltration swales. The flow will be routed to catch basins just west of these water
quality facilities and conveyed through a series of pipes and catch basins before discharging
through the outfalls.
Flow from the western crowned taxiway surface will be conveyed in a manner similar to the flow
from the runway surfacing. Runoff will travel above grade to the center of the infield area and be
directed to catch basins. From there, the flow will be diverted through a series of pipes and catch
basins before discharging through the outfalls.
Flow from the eastern crowned area within Subbasins A, B, and E will be directed from the edge
of the pavement to drainage swales, which will convey surface water to a series of catch basins
and pipelines before being discharged through the outfalls. In Subbasin C, the eastern crowned
taxiway surface will be graded and paved in a manner that directs surface water to catch basins.
In Subbasin D, the eastern crowned taxiway surface will divert flow to a trench drain. These
flows will be conveyed through pipelines and discharged to flow splitter catch basins. The flow
splitters will divert the required flow/volume for water quality within each subbasin, while the
remaining flow/volume will be diverted to a bypass system. The portion of the flow required for
water quality will be conveyed within the biofiltration swales to collection catch basins. The
bypass flow will travel parallel to the swales through a series of pipes and catch basins, then
discharge to the same collection catch basins as the water quality flow. From these locations,the
surface water will be conveyed through a series of pipes and catch basins and then discharged
through the outfalls. For further information regarding these facilities,please refer to
Appendix C and the project plans.
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Shallow Pipe Loading
Thickness design for DIP was performed on drainage lines crossing beneath Taxiway B at
shallow depths, typically less than 3 feet of cover. The method utilized for the design was
obtained from ANSI/AWWA C150/A21.50-20, Thickness Design of Ductile Iron Pipe. There
were four scenarios reviewed where the crossings possessed cover less than 3 feet: 8-inch DIP at
1 foot, 12-inch DIP at 1.5 feet, 6-inch DIP at 2 feet, and 12-inch DIP at 2 feet. The vehicle
loading on the pipelines was based on the design vehicle,Aircraft Rescue Fire Fighting (ARFF)
Truck,which weighs approximately 82,000 pounds. From the calculations performed, it
appeared that at least a Special Class 51 DIP would be needed from the 8-inch pipe at a 1 foot
depth scenario, while the remaining scenarios required only a Special Class 50 DIP. The design
specifications for the project required a Special Class 52 for all ductile iron pipelines on the
project. A Special Class 52 DIP is thicker than the 50 or 51 type; therefore, the design of the
pipelines at shallow depths is adequate to sustain the loading from the design vehicle. Please
refer to Appendix D for the thickness design calculations.
Spill Control Measures
Spill control measures, in accordance with the City of Renton's SWDM Amendment
requirements,have been included as part of the storm drainage facilities. These measures include
placing inverted tee or elbow sections in the final discharge catch basins within each subbasin.
Locations and details of these facilities are identified in the project plan set.
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SECTION 6: SPECIAL REPORTS AND STUDIES
Table 6-1 summarizes the Special Reports and Studies required for this project site.
Table 6-1. Special Reports and Studies.
Study/Report Date Conducted Appendix
Floodplain Delineation(Section 1.3.2) N/A N/A
Flood Protection Facility Conformance(Section 1.3.3) N/A N/A
Critical Areas Analysis and Delineation N/A N/A
Geotechnical/Soils 04/27/12 Appendix A
Groundwater N/A N/A
Slope Protection/Stability N/A N/A
Erosion and Deposition N/A N/A
Geology N/A N/A
Hydrology N/A N/A
Fluvial Geomorphology N/A N/A
Anadromous Fisheries Impacts N/A N/A
Water Quality N/A N/A
Structural Design N/A N/A
Structural Fill N/A N/A
Aquifer Protection Areas N/A N/A
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SECTION 7: OTHER PERMITS
Table 7-1 summarizes other permits required for the project site.
Table 7-1. Other Permits.
Permit Required Regulating Agency
_ On-site Sewage Disposal No Seattle/King County Department of Public Health
Well Permits No Seattle/King County Department of Public Health
Developer/Local Agency Agreement No Washington State Department of Transportation
Hydraulic Project Approval No Washington State Department of Fish and Wildlife
Short-term Water Quality Modification Approval No Washington State Department of Ecology
Dam Safety Permit No Washington State Department of Ecology
NPDES Stormwater Permit Yes Washington State Department of Ecology
Forest Practices Class IV Permit No Washington State Department of Natural Resources
Sections 10,401,and 404 Permits No United States Army Corps of Engineers
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SECTION 8: CSWPPP ANALYSIS AND DESIGN
A Construction Stormwater Pollution Prevention Plan (CSWPPP) has been developed as an
element of this report. This plan is composed of an Erosion Sediment Control (ESC) plan and a
Stormwater Pollution Prevention and Spill (SWPPS) plan.
ESC Measures
Phase I of the project will be constructed during the spring and early summer of 2013. The site is
relatively flat and the majority of the work is on or near asphalt surfacing; therefore, erosion
potential is anticipated to be very low. Standard erosion control measures will be implemented to
control sediment in the construction area. However, additional measures will be introduced to
provide added protection against sediment transport due to the airport's close proximity to Cedar
River and Lake Washington. The following is a description of the standard and nonstandard
erosion control measures being implemented for Phase I of this project.
ESC Requirement 1: Clearing Limits
The limits of work are identified on the project plans. It is anticipated that the Contractor will
physically mark the limits of work during construction.
ESC Requirement 2: Cover Measures
The Contractor will be required to cover any exposed soils by temporary or permanent means.
Guidelines for cover measures are defined in the ESC Notes on the plans.
ESC Requirement 3: Perimeter Protection
Filter fabric fencing shall be installed down-gradient from any construction activity to prevent
the transportation of sediment to Cedar River or Lake Washington. Fencing materials will be
specified to meet the KCSWDM requirements. Typically, such structures consist of filter fabric,
possess a wire mesh backing, and are buried approximately 8 inches below grade. The
Contractor shall inspect the fence on a weekly basis. Any damage to the structure shall be
repaired immediately. If soil near the barrier is roughly 6 inches high, the sediment shall be
removed and stabilized on site.
ESC Requirement 4: Traffic Area Stabilization
Temporary construction entrances may be installed at various locations along the taxiway
reconstruction to reduce sediment transport onto the adjacent paved surfaces.
ESC Requirement S: Sediment Retention
Check dams and bio-filter bags will be installed within existing swales and around certain catch
basins to protect downstream conveyance systems from sediment accumulation. Straw wattles
will also be used downstream of any soil disturbance that is tributary to existing catch basins.
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Catch basin sediment trap filters will be installed in existing and proposed catch basins to protect
drain inlet structures and reduce sediment in downstream conveyance systems.
All temporary and permanent erosion and sediment control BMPs shall be maintained and
repaired as needed to ensure continued performance of their intended function. All maintenance
and repair shall be conducted in accordance with BMPs. Sediment control BMPs shall be
inspected weekly or after a runoff-producing storm event during the dry season and daily during
the wet season.
ESC Requirement 6: Surface Water Collection
In addition to the traditional BMPs mentioned above, two of the existing catch basins that drain
to the Cedar River will be equipped with a pump and flow dispersal system. The outlet pipes
from the catch basins will be plugged and a temporary sump pump will be installed to convey
runoff to a length of 6-inch perforated pipe placed on undisturbed vegetation. Sediment will
settle in the catch basin and the runoff will be dispersed through the existing vegetation
downstream.
ESC Requirement 7: Dewatering Control
The Contractor shall dewater excavated areas that exhibit excessive water levels from ground or
surface water. Temporary pumping and dispersal equipment shall be used to disperse the flow to
existing vegetation areas downstream of the excavations. Sediment transport shall not be allowed
to bypass existing or proposed stormwater facilities that are fitted with sediment retention
measures.
ESC Requirement 8: Dust Control
The Contractor shall control dust to prevent sediment transport from exposed, dry surfaces to the
adjacent waterways. It is anticipated that the Contractor will use water in these areas; however,
the KCSWDM also allows the Contractor to utilize calcium chloride, magnesium chloride, lignin
derivatives, tree resin emulsions, and synthetic polymer emulsions as other means of suppressing
dust from the project area.
ESC Requirement 9: Flow Control
The Contractor shall be responsible for drainage control at all times. The Contractor shall protect
all work, existing facilities, and adjacent properties and water bodies from erosion and siltation
transportation during construction.
Recommended Construction Sequence (Erosion and Sediment Control)
1. Attend preconstruction meeting.
2. Post sign with name and phone number of ESC supervisor.
3. Grade and install construction entrance(s).
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4. Install perimeter protection (silt fence,brush barrier, etc.).
5. Construct surface water controls simultaneously with grading activities for project
development.
6. Maintain erosion control measures in accordance with King County Standards and
manufacturer's recommendations.
7. Relocate erosion control measures, or install new measures, so that changing site
conditions continue to meet King County erosion and sediment control standards.
8. Cover all areas that will be unworked for more than seven days during the dry season or
two days during the wet season with straw, wood fiber mulch, compost, plastic sheeting,
or equivalent.
9. Seed or sod any areas to remain unworked for more than 30 days.
10. Upon completion of the project, all disturbed pervious areas must be stabilized and BMPs
removed if appropriate.
SWPPS Plan Design
Construction activities that may generate pollutants include: (1) soil disturbance from site
grading, storm installation, and pavement removal; and (2) use of large machinery required to
install new asphalt and storm system components. Potential pollutants in construction runoff as a
result of the operations include the following: oils and greases,nutrients,metals, suspended
solids, and Biochemical Oxygen Demand (BOD).
The major pollutants generated by the activities are suspended solids (from soil disturbance) and
oils and greases from heavy machinery and asphalt placement. These pollutants will be
controlled using a combination of inlet protection filter traps, filter bags, and straw wattles in or
around the new and existing catch basins. An additional measure for water quality will be
utilized by pumping runoff from existing catch basins to a dispersal system. These measures are
described above in the ESC Measures section.
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SECTION 9: BOND QUANTITIES, FACILITY SUMMARIES,AND
DECLARATION OF COVENANT
Bond Quantities Worksheet
A completed Bond Quantity Worksheet has been provided as part of this document. Please refer
to Appendix E, Bond Quantity Worksheet.
Flow Control and Water Quality Facility Summary Sheet and Sketch
A summary of the water quality facilities is discussed in Section 4, Flow Control and Water
Quality Facility Analysis and Design. As discussed previously, flow control facilities are not
required. Flow control BMPs will be provided where necessary or applicable.
Please see Appendix F for the completed Flow Control and Water Quality Facility Summary
Sheet for this project.
Declaration of Covenant for Privately Maintained Flow Control and WQ Facilities
The Renton Municipal Airport is a public facility owned and operated by the City of Renton. All
fees associated with maintenance work are budgeted by the Municipal Airport, and the Public
Works staff maintains the facilities. Therefore, this project is exempt from providing a
Declaration of Covenant for Privately Maintained Flow Control and WQ Facilities.
Declaration of Covenant for Privately Maintained Flow Control BMPs
The Renton Municipal Airport is a public facility owned and operated by the City of Renton. All
fees associated with maintenance work are budgeted by the Municipal Airport, and the Public
Works staff maintains the facilities. Therefore, this project is exempt from providing a
Declaration of Covenant for Privately Maintained Flow Control BMPs.
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SECTION 10: OPERATIONS AND MAINTENANCE MANUAL
The applicable maintenance requirements, provided from the KCSWDM, Appendix A, are
provided in Appendix G of this document.
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SECTION 11: REFERENCES
City of Renton, Washington, 2012. City of Renton Municipal Code, Section 4-6-030, Drainage
(Surface Water) Standards.
City of Renton, Washington, 2012. City of Renton COR Maps. 7 June 2012.
http://rentonwa.gov/govemment/default.aspx?id=29886.
City of Renton, Washington, Public Works Department, Surface Water Utility, 2010. City of
Renton Amendments to the King County Surface Water Design Manual.
HWA GeoSciences, Inc., 2012. Taxiway B North (General Aviation) Section Improvements,
Renton Municipal Airport, Taxiway B Rehabilitation.
King County Department of Natural Resources and Parks, 2009.King County Surface Water
Design Manual.
King County Department of Natural Resources and Parks, Water and Land Resources Division,
2009.King County Stormwater Pollution Prevention Manual.
King County Geographic Information Systems, 2012.King County iMap:Interactive Mapping
Tool. 31 May 2012. http://www.kingcounty.gov/operations/GIS/Maps/iMap.aspx/.
United States Department of Agriculture,Natural Resources Conservation Service, 2012. Soil
Survey of King County Area, Washington.
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Appendix A
Geotechnical Report
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FINAL GEOTECHNICAL ENGINEERING REPORT
Renton Municipal Airport
Taxiway B Rehabilitation
Renton, Washington
HWA Project No. 2011-039-21
Prepared for
Reid Middleton, Inc.
October 17, 2012
HWAGEOSCIENCES INC.
• C eorechnical Engineering
• Hydro, Bolo y
• Geoenvironmental Services
• Inspection & Te4tin
`Y OSCIEN + INC.
October 17,2012
HWA Project No. 2011-039-21
Reid Middleton
728 134th Street SW, Suite 200
Everett, Washington 98204
Attention: -Mr. Randy Hall,P.E.
SUBJECT: Final Geotechnical Engineering Report
Renton Municipal Airport
Taxiway B Rehabilitation
Renton,Washington
Dear Randy:
As requested, HWA GeoSciences Inc. (HWA) has completed a geotechnical engineering
investigation to support design efforts for the Taxiway B Rehabilitation Project at the Renton
Municipal Airport in Renton, Washington. The objective of our investigation was to evaluate the
existing pavement and subgrade conditions in the vicinity of the proposed improvements. Our
scope of work included field reconnaissance, test pit logging,pavement coring, dynamic cone
penetration testing(DCP), laboratory testing, SCBC mix design,engineering analyses,and
preparation of the attached final report summarizing the investigation results and our
recommendations.
We appreciate the opportunity to provide geotechnical services on this project.
Sincerely,
HWA GEOSCIENCES INC.
A""� � ,
Steven E. Greene,L.G., L.E.G. George Minassian,Ph.D.,P.E.
Senior Engineering Geologist Pavement Engineer
Enclosure: Final Geotechnical Report
21312 30th Drive SE
Suite 110
Bothell,WA 98021.7010
Tel: 425.774.0106
Fax: 425.774.2714
www.11-.vageo.com
TABLE OF CONTENTS
1.0 INTRODUCTION..........................................................................................................I
1.1 GENERAL.......................................................................................................1
1.2 PROJECT UNDERSTANDING............................................................................1
1.3 AUTHORIZATION AND SCOPE OF WORK.........................................................1
2.0 INVESTIGATION PROGRAM ........................................................................................1
2.1 SITE EXPLORATIONS......................................................................................1
2.2 LABORATORY TESTING .................................................................................2
3.0 SITE CONDITIONS......................................................................................................3
3.1 SITE DESCRIPTION.........................................................................................3
3.2 GENERAL GEOLOGY......................................................................................4
3.3 SUBSURFACE CONDITIONS.............................................................................4
3.5 EXISTING PAVEMENT STRUCTURE.................................................................5
4.0 SUMMARY AND CONCLUSIONS..................................................................................8
4.1 GENERAL ........................................................................................................8
4.2 NORTH TAXIWAY SECTION RECONSTRUCTION ...............................................9
4.3 SOUTH TAXIWAY SECTION REHABILITATION&RECONSTRUCTION................9
5.0 CONDITIONS AND LIMITATIONS.................................................................................10
LIST OF FIGURES (FOLLOWING TEXT
Figure 1 Project Site and Vicinity Map
Figure 2 Site and Exploration Plan
Figure 3 Geologic Map
APPENDICES
Appendix A: Field Exploration
Figure A-1 Legend of Terms and Symbols Used on Exploration Logs
Figures A-2—A-21 Logs of Cores Core-1 through Core-20
Figures A-22—A-24 Logs of Test Pits TP-1 through TP-3
Appendix B: Laboratory Testing
Figures B-1 —B-8 Particle Size Analysis of Soils
Figure B-9 Liquid Limit, Plastic Limit and Plasticity Index of Soils
Figures B-10—B-12 Laboratory Compaction Characteristics of Soil
Figures B-13 —B-15 CBR of Laboratory Compacted Soil
Figure B-16 Bulk Density of Soil-Drive Cylinder Method
Appendix C: Core Photographs
FINAL GEOTECHNICAL ENGINEERING REPORT
RENTON MUNICIPAL AIRPORT
TAXIWAY B REHABILITATION
RENTON,WASHINGTON
1.0 INTRODUCTION
1.1 GENERAL
This report summarizes the results of a geotechnical engineering investigation completed by
HWA GeoSciences Inc. (HWA) to support design efforts for the Taxiway B Rehabilitation
Project, at the Renton Municipal Airport, in Renton, Washington. The project location is
indicated on the Project Site and Vicinity Map, Figure 1.
1.2 PROJECT UNDERSTANDING
We understand that Taxiway B rehabilitation work involves resurfacing all of Taxiway B on the
east side of the airfield. Currently, Taxiway B is composed of hot mix asphalt and Portland
cement concrete pavement and is approximately 3,300 feet long and ranges from about 25 to 50
feet wide. The objective of our study was to provide field exploration and testing to evaluate the
existing subsurface and pavement conditions, and provide recommendations regarding subgrade
strength properties for pavement design for the taxiway rehabilitation.
1.3 AUTHORIZATION AND SCOPE OF WORK
Authorization to proceed with our work was provided under Agreement for Subconsulting
Services, dated August 2010,between HWA and Reid Middleton. Our work was undertaken in
accordance with our original proposal dated August 7, 2010. The scope of work included field
reconnaissance, test pit excavation, pavement coring and shallow hand-excavated explorations,
DCP and laboratory testing, and preparation of this summary report.
2.0 INVESTIGATION PROGRAM
2.1 SITE EXPLORATIONS
Subsurface conditions in the vicinity of the proposed improvements were investigated by means
of three test pits (designated TP-1 through TP-3) and twenty pavement cores (designated Core-1
through Core-20). Shallow hand borings were performed within the core holes. The
approximate locations of our explorations are shown in Figure 2, Site and Exploration Plan.
The test pits were excavated on June 3, 2011, by an excavator under subcontract to HWA, to
depths ranging from approximately 3.5 to 4 feet. The test pits and cores/hand borings were
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HWA Project No. 2011-039-21
performed by HWA engineering geologist personnel. Pertinent information including soil
sample depths, stratigraphy, soil engineering characteristics, and ground water occurrence were
recorded. The stratigraphic contacts shown on the individual boring logs represent the
approximate boundaries between soil types; actual transitions may be more gradual. The soil
and ground water conditions depicted are only for the specific date and locations reported and,
therefore, are not necessarily representative of other locations and times.
Soil samples obtained from the excavations were classified in the field and representative
portions were placed in plastic bags. These soil samples were then returned to our Bothell,
Washington, laboratory for further examination and testing.
The cores/hand borings were completed using coring equipment, hand augers, and other hand
tools, to depths ranging from about 1.5 to 7.5 feet. The initial phase consisting of(16) sixteen
cores/hand borings were conducted on June 2, June 6, and June 7, 2011. Four (4) supplemental
core/hand borings were conducted on July 11, 2012. The cores/hand borings were used to gather
information on the thickness of the existing pavement and strength of the underlying subgrade
layers in the taxiway area. A legend of the terms and symbols used on the exploration logs is
presented in, Figure A-1, Appendix A. Summary test pit and core logs are presented in Figures
A-2 through A-24, Appendix A.
Dynamic cone penetration (DCP) testing was performed in most pavement core holes to check
relative soil density/strength conditions. The DCP consists of a steel extension shaft assembly,
with a 60 degree hardened steel cone tip attached to one end, which is driven into the soil by
means of a sliding drop hammer. The base diameter of the cone is 20 mm (0.8 in). The diameter
of the shaft is 8 min (0.3 in) less than that of the cone to ensure that, at shallow penetration
depths, the resistance to penetration is exerted on the cone alone. The DCP is driven by
repeatedly dropping an 8 kg (17.6 lbs) sliding hammer from a height of 575 min (22.6 in). The
depth of cone penetration was measured after each hammer drop and the soil shear strength is
reported in terms of the DCP index. The DCP index is based on the average penetration depth
resulting from 1 blow of the 8 kg hammer and is reported as millimeters per blow (mm/blow).
The data obtained from the DCP testing was then correlated to approximate California Bearing
Ratio (CBR) values, in order to evaluate the strength of the subgrade soils. It is important to
note that CBR values derived from DCP data obtained from granular materials may be
exaggerated. The calculated CBR values are plotted on the appropriate core logs in Appendix A.
2.2 LABORATORY TESTING
Laboratory tests were conducted on selected soil samples to characterize relevant properties of
the on-site soils. The laboratory testing program was performed in general accordance with
appropriate ASTM Standards, as outlined below.
Final Report 2 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
MOISTURE CONTENT OF SOIL: The moisture content of selected soil samples (percent by dry
mass) was determined in accordance with ASTM D 2216. The test results are shown at the
sampled intervals on the appropriate summary logs in Appendix A.
PARTICLE SIZE ANALYSIS OF SOILS: Selected granular samples were tested to determine the
particle size distribution of material in accordance with ASTM D 422 (wash sieve or wash sieve
and hydrometer methods). The results are summarized on the attached Particle-Size Distribution
reports (Figures B-1 through B-8, Appendix B), which also provide information regarding the
classification of the samples and the moisture content at the time of testing.
LIQUID LIMIT,PLASTIC LIMIT,AND PLASTICITY INDEX OF SOILS(ATTERBERG LIMITS):
Selected fine-grained samples were tested using method ASTM D 4318, multi-point method.
The results are reported on the attached Liquid Limit, Plastic Limit, and Plasticity Index report
on Figure B-9.
LABORATORY COMPACTION CHARACTERISTICS OF SOIL(PROCTOR TEST): Selected bulk
subgrade samples were tested using either method ASTM D 698 (Standard Proctor) Method C or
ASTM D 1557 (Modified Proctor), as appropriate. The test results are summarized on the
attached Laboratory Compaction Characteristics of Soil reports, Figures B-10 through B-12,
Appendix B.
CBR(CALIFORNIA BEARING RATIO)OF LABORATORY COMPACTED SOILS: Selected bulk
subgrade samples were tested in accordance with method ASTM D 1883. The test results are
summarized on the attached CBR of Laboratory Compacted Soils reports, Figures B-13 through
B-15, Appendix B.
BULK DENSITY OF SOIL DRIVE CYLINDER METHOD: The bulk density, dry density and moisture
content of selected, relatively undisturbed soil samples obtained from test pits TP-1 through TP-
3 were determined in general accordance with ASTM D 2937 test method. The test results are
summarized in the table on Figure B-16, Appendix B.
3.0 SITE CONDITIONS
3.1 SITE DESCRIPTION
Renton Municipal Airport is located in King County, within the northwest portion of the City of
Renton. The Airport has a single runway (Runway 16-34), which is approximately 5,400 feet
long, 100 feet wide, and consists of Portland cement concrete panels overlain with an asphaltic
concrete surface layer. The runway was resurfaced and realigned in the summer of 2009.
Taxiway B extends along the southeast side of runway and is approximately 3,300 feet long, 25
to 50 feet wide, and consists of asphaltic concrete pavement in the general aviation area and
Portland cement concrete panels overlain by asphaltic concrete in the area trafficked by large
Final Report 3 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
commercial aircraft. The ground surface in the vicinity of this project is predominantly flat,
situated at approximately elevation 32 feet MSL and prior to industrial development consisted of
a portion of the alluvial plain of the Cedar River.
3.2 GENERAL GEOLOGY
Background geologic information was obtained from Geologic Map of the Renton Quadrangle,
King County, Washington (D.R. Mullineaux, 1965). This map, a portion of which is reproduced
herein as Figure 3, identifies the surficial deposits in the vicinity of the airport as urban or
industrial land that has been modified by widespread or discontinuous artificial fill (map symbol-
afin). Alluvial deposits consisting of material deposited by the Cedar River (map symbol—Qac)
are mapped along the margins of this industrial land area and belie conditions prior to
industrialization.
3.3 SUBSURFACE CONDITIONS
Locally, construction of pavement structure have been facilitated by the use of fill layers ranging
from 0.6 feet in the general aviation area (north of the wind rose) to 2.25 to 4 feet plus in the
commercial aviation area (central to south portion of Taxiway B). In general, the fill layers
appear to be loose to medium dense and consist of various material types most predominately,
slightly silty to silty, gravel with sand to relatively clean, sand with gravel. In the central area
(between Core-5 and Core-6) material interpreted as dredge fill consisting of sand and gravel
with shell fragments, glass and brick pieces underlies the pavement section at depth. Beneath the
fill layer, the native subgrade soils consists predominately of medium stiff to soft, organic silt
(OH), typically exhibiting estimated in-place CBR values ranging from <1%to about 5%. The
soil moisture content appears to increase with depth.
Perched ground water was encountered in test pits TP-1, TP-2, and TP-3, at depth of 3.8 feet, 3.5
feet and 3.6 feet, respectively. Ground water seepage was observed in core/hand borings Core-4,
Core-6 through Core-9, and Core-18, ranging from about 2.2 to 5.5 feet below the existing
ground surface at the time of our exploration. It is anticipated that the level of ground water in
this area will change depending on the season and the height of the adjacent Cedar River.
Three native soil samples were tested for laboratory CBR values. The tested samples were taken
from Test Pits TP-1, TP-2 and TP-3, which are representative of the native soils encountered
below granular fill along the length of existing Taxiway. The moisture-density curve for the
sample from TP-1 was determined in general accordance with ASTM D 698, as required by FAA
for airfields serving aircrafts with total weight less than 60,000 Lbs. The moisture-density
curves for samples from TP-2 and TP-3 were determined in accordance with ASTM D 1557, as
required by the FAA for areas serving aircraft with a total weight above 60,000 Lbs. The CBR
value of each sample was determined at natural moisture content and maximum compaction
effort. In addition, the sample obtained in TP-3 was dried back to optimum and compacted at
Final Report 4 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
maximum effort in an attempt to determine the potential strength gain available should the
subgrade be allowed to dry out. The measured CBR test results are presented on Figures B-13
through 13-15, in Appendix B and are summarized in Table 1 below:
Table 1: Summary of CBR Tests
Sample Relative CBR Value
Material Description Location Compaction o
Light olive brown, organic SILT (OH) TP-1 57.4' 0.4
Dark brown, organic SILT (OH) TP-2 65.62 0.6
Dark olive gray, SILT with sand (ML) TP-3 85.52 1.2
102.12 53.8
'Relative to Maximum Dry Density determined with Standard Compactive Effort(ASTMD698)
z Relative to Maximum Dry Density determined with Modified Compactive Effort(ASTM D 1557)
3.5 EXISTING PAVEMENT STRUCTURE
We completed twenty (20) core/hand holes at locations selected by Reid Middleton along the
taxiway alignment and on the existing north and south end connectors. Our shallow hand
borings, performed within the core holes, were extended to 1.3 to 7.5 feet in depth using hand
tools. Detailed logs of the core holes are located in Appendix A of this report. Photographs of
pavement cores are presented in Appendix C.
North Taxiway Connector
Based on the exploration within the north taxiway connector(Core-1) the pavement section
consists of an HMA surface of about 2-inches thick over 5-inches of crushed gravel base course.
The existing pavement surface is in fair condition.
Fill soils consisting of Gravel with sand and cobbles were encountered at depth of about 0.6 feet.
No DCP test was conducted at this location due to refusal on cobbles.
Taxiway B North - General Aviation Area
Based on the explorations within the Taxiway B proper in general aviation area (Core-2 and
Core-5) the taxiway pavement section consists of an HMA surface of about 2 to 4.5-inches thick
and a base course layer ranging from 5 to 6 inches thick. The existing pavement surface is in fair
to good condition.
Final Report 5 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
Fill soils consisting of poorly graded gravel with sand were encountered at depth of about 0.5 to
0.7 feet. At the location of Core-5, dredge fill consisting of silty medium sand with shell
fragments, brick and glass fragments was encountered to a depth of 2.5 feet. Below the fill in
Core-2 and Core-5, native alluvial soils consisting of sandy silt to organic silt were encountered.
These soils were similar to those encountered in our test pit TP-1.
Field DCP data obtained at location of Core-2 (See Figure A-3) indicate in-place CBR values of
about 20% for the uppermost 0.7 of a foot of subgrade, then decreasing to about 3-5% for the last
1.1 feet or so to the termination depth of the test at about 4.3 feet below grade in native soils.
Taxiway B North Apron
Based on the explorations east on the Taxiway B in general aviation area within the apron
adjacent to private hangers (Core-3 and Core 4) the taxiway pavement section consists of an
HMA surface of about 1.5 to 2.25-inches thick. At the location of Core-4, a 1.5-inch thick layer
of crushed aggregate was found sandwiched between the surface course of HMA and older 1.75-
thick layer of HMA. A thin gravel base layer about 1.5 —inches thick was encountered under the
pavement at Core-3. No gravel base was encountered below the lower HMA layer in Core-4.
The existing pavement surface is in poor to fair condition.
Fill soils consisting of well graded gravel, poorly graded sand or silty sand were encountered at
depth of about 0.4 to 0.5 feet. At the location of Core-3, a silt layer was encountered
immediately beneath a thin layer of CSBC. Below the fill in Core-3 and Core-4, native organic
silt soils were encountered at depths of 2.3 and 3.2 feet, respectively. These subgrade soils were
similar to those encountered in test pit TP-1.
Field DCP data obtained at location of Core-3 (See Figure A-4) indicates in-place CBR values of
1-3% for alluvial subgrade from 2.8 to 4.9 feet below grade. Field DCP data obtained at location
of Core-4 (See Figure A-5) indicates in-place CBR values of 1-5% for alluvial subgrade from 3.1
to 4.8 feet below grade. At both locations CBR values appear to increase slightly with depth.
Taxiway B South-Commercial Aircraft Area
Based on the explorations within the commercial aviation area the taxiway pavement section
(Core-6 through Core-8, and Core-17 through Core-20) consists of an HMA surface of about 5.5
to 12-inches thick over a PCC section of 5 to 8 inches thick. At the location of Core-9, the
taxiway pavement consisted on 10-inches of HMA without an underlying PCC layer. At the
location of Core-10, which is situated in an infield cut-out (See Figure 2), the pavement
consisted of only 2.25-inches of HMA. At the location of Core-11, which is situated at the
south end of Taxiway B, the pavement consisted of 8.5-inches of HMA over 8-inches of PCC.
At the location of Core-19 within Taxiway K, the pavement consisted of 12.5 inches of HMA
over 7-inches of PCC. No crushed gravel base was encountered beneath the pavement at any of
Final Report 6 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
these locations except for Core-10, where at least 24-inches of gravel base consisting of fine
crushed gravel with sand was encountered. The existing pavement surface at these locations is
in very poor to good condition.
At the locations of Core-17 and Core-20, the pavement surface is deeply gouged within the
upper .HMA layer. The resulting gap had been sealed (See core photos for Core-17 and Core-20
in Appendix Q. It appears that the pavement in these areas had been subject to repeated stress
by heavy wheel loads that plowed and furrowed the surface causing fractures to propagate into
the pavement as much as 0.75 inches deep. At these locations, it is likely that the nose gear tires
of commercial aircraft entering the taxiway from the hardstand are responsible for this damage.
Fill soils consisting of gravelly sand to silty sand layers ranging from 1.0 to 2 feet thick were
encountered directly underlying the pavement sections investigated in this area except at Core-
10 as noted above.
Native soils consisting of sandy and organic silt were encountered at depths ranging from about
2.5 to 3.5 feet; these soils were similar to those encountered in our test pit explorations TP-2 and
TP-3.
Field DCP data obtained at the locations of Core-6 through Core-10 (See Figures A-7 through A-
10) indicate in-place CBR values ranging from 3 to 6% in native subgrade to depths of 4.4 to 5.6
feet below grade. At the location of Core-10, DCP testing encountered granular material with
average CBR values above 40% to depths of 4.2 feet below grade. At the location of Core-11,
DCP testing encountered granular material with average CBR values of 19%to a depth of 3.6
feet below grade. At the locations of Core-17 through Core-20 (see Figures A-18 through A-21)
field DCP data obtained below the granular fill, indicate in-place CBR values of 3 to 4% in
native subgrade from depths of 3.0 to 6.0 feet below grade.
South Taxiway Connector
Based on the explorations within the south taxiway connector (Core-12 through Core-16) the
taxiway pavement section consists of an HMA surface of about 2 to 4 inches thick and a base
course approximately 6 inches thick. The existing pavement surface is in fair condition.
Native soils consisting of sandy silt and silt with sand were encountered at depth of about 0.5
feet; these soils were similar to those encountered in our test pit explorations.
Field DCP data obtained at the locations of Core-12 through Core-14 (See Figure A-13 through
A-15) indicates in-place CBR values ranging from 2 to 6% in native subgrade soils to depth
ranging from 3.6 to 6.8 feet below grade. Field DCP data obtained at the location of Core-15
(See Figure A-16) indicate in-place CBR values averaging greater than 50% for two layers
separated by a soft layer (CBR about 1- 5% ) about 1 foot thick situated between 3.3 and 4.4 feet
Final Report 7 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
below grade. Field DCP data obtained at the location of Core-16 (See Figure A-17) indicate in-
place CBR values averaging greater than 100% for granular material encountered from 2.1 feet
to the termination depth of 4.3 feet below existing grade.
4.0 SUMMARY AND CONCLUSIONS
4.1 GENERAL
Our subsurface investigations reveal that the native soils consist predominately of soft to
medium stiff organic or sandy silts within the northern and central portions of the project
alignment (Core-I through Core-9 and Core-17 through Core-20) at depths ranging from 1.125
to 3.6 below the existing pavement surface. These native subgrade soils are weak exhibiting in-
place CBR values ranging from 1 to 5%, and averaging about 3%. CBR values from laboratory
samples obtained from TP-1 and TP-2 and remolded at natural moisture content indicate CBR
values less than 1% for these soils. The in-place moisture contents of these soils ranged from
about 50 to 75 percent over what is optimum for compaction. Typically, a layer of loose to
medium dense, granular fill of varying quality ranging from 0.75 to 3.0 feet in thickness is
present between the pavement and the underlying soft to medium stiff, native subgrade.
Within the southernmost portion of the project alignment, in the infield cut-out area (Core-10)
and at the southern end of Taxiway B (Core-11) the pavement is underlain by granular fill and
sandy alluvial soils. These subgrade soils appear to be moderately strong exhibiting estimated
in-place CBR values ranging from 19 to 40%. CBR values determined from laboratory samples
obtained from TP-3 and remolded at natural and optimum moisture content indicate CBR values
of about 1% to 54% for material with a moisture content difference of only 10%. It appears that
considerable strength gain can be realized if these soils are allowed to dry prior to compaction.
Along the main portion of southern taxiway connector (Core-12 through Core-14) the pavement
is underlain by loose to medium stiff, silty sand to sandy silt alluvial soils. These subgrade soils
are relatively weak exhibiting in-place CBR values ranging from 2 to 6%, and averaging about
3%. At the locations of Core-15 and Core-16 (situated within the inside turn radius on to
Runway 16-34) the pavement is underlain by relatively thick section of strong granular fill and
native material exhibiting estimated in-place CBR values ranging from 50 to 100% (these values
should be considered in relative terms only as CBR values derived from DCP data from granular
soils is often exaggerated due to presence of gravels).
The local water table, or substantial seasonally perched ground water, was observed in all of our
explorations located within the central portion of the Taxiway (Core-4, Core-6 through Core-9,
and Core-18) and in the infield at all test pit locations at depths ranging from 2.2 to 5.4 feet
below the existing ground surface at the time of our explorations. We anticipate that ground
water levels in the area will be high; especially during the wet weather season and vary locally
Final Report 8 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
with the level of the adjacent Cedar River. This high ground water level will further decrease the
already low infiltration potential of the subgrade soils.
Because of the high fines and organic content in the native subgrade layer, we expect that water
penetrating the surfacing could become trapped in the base layer. Therefore, we recommend that
subsurface drainage be provided below the pavement and along the edge of the taxiways and
apron pavement to intercept and prevent possible incursion of such infiltrated water beneath the
pavement areas. Failure to maintain the subgrade in a positively drained condition could lead to
localized softening and loss of support for the pavement structure, possibly resulting in
premature pavement distress. Moreover, saturation of the subgrade with infiltrated moisture will
exacerbate potential frost-heave effects and increase the rate of subgrade deterioration.
4.2 NORTH TAXIWAY SECTION RECONSTRUCTION
We understand that the reconstruction of the northern portion of Taxiway B referred to herein as
the General Aviation Area has already been designed and bid for construction commencing in
the spring of 2013. We understand reconstruction will entail: removal of the existing HMA
pavement, cement treatment of the underlying subgrade (SCB) for a depth of 8-inches,
placement and compaction of a 6-inch thick layer of crushed base rock, followed by placement
of a 4-inch thick HMA pavement layer. The use of SCB instead of traditional pavement re-
construction methods is expected to save time and reduce the amount of imported materials
required for re-construction by treating existing subgrade soils with cement. We understand that
the construction will be conducted in three phases commencing from south to north. The SCB
Mix design was completed by HWA in August, 2012 and our findings and recommendations are
summarized in a laboratory report entitled: SCB Mix Design Report: Renton Airport Taxiway B
Rehabilitation, General Aviation Area-Phases I through 3, Renton, Washington, prepared for
Reid Middleton.
4.3 SOUTH TAXIWAY SECTION REHABILITATION&RECONSTRUCTION
Currently, the design concept for rehabilitation and reconstruction of the southern portion of
Taxiway B referred to herein as the Commercial Aviation Area is currently being developed.
We understand that current consideration is being given to; total reconstruction of an area
approximately 50 feet wide by about 1,500 long adjacent to the hardstand area, and a grind and
overlay program for all other areas exhibiting surface deterioration. It is likely that this work will
also be constructed in phases to minimize impact to airport operations. Currently, we understand
that total reconstruction will consist of pavement (HMA & PCC) removal, followed by the
placement of HMA for the full-depth of 11 to 13-inches. In these areas, the existing pavement
section is supported by loose to medium dense, sand with gravel to gravel with sand fill directly
underlain by soft to medium stiff, native sandy silt or organic silt. Consideration is being given
to amend the upper 4 to 6 inches of the existing granular fill with Portland cement to create a soil
Final Report 9 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
cement base (SCB) layer that will serve to stabilize and reduce the potential for disturbance of
the subgrade during construction and facilitate efficient HMA layer compaction.
5.0 CONDITIONS AND LIMITATIONS
We have prepared this final report for the City of Renton and Reid Middleton. This report
should be provided in its entirety to prospective contractors for bidding and estimating purposes;
however, the conclusions and interpretations presented herein should not be construed as our
warranty of the subsurface conditions. Experience has shown that soil and ground water
conditions can vary significantly over small distances. Inconsistent conditions may occur
between explorations that may not be detected by a geotechnical study of this scope and nature.
If, during construction, subsurface conditions are encountered which vary appreciably from
those described herein, HWA should be notified for review of the recommendations of this
report, and revision of such if necessary. If there is a substantial lapse of time between
submission of this report and the start of construction, or if conditions change due to construction
operations, it is recommended that this report be reviewed to determine the applicability of the
conclusions and recommendations considering the changed conditions and time lapse.
This report is issued with the understanding that it is the responsibility of the owner, or the
owners' representative, to ensure that the information and recommendations contained herein are
brought to the attention of the appropriate design team personnel and incorporated into the
project plans and specifications, and the necessary steps are taken to see that the contractor and
subcontractors carry out such recommendations in the field.
We recommend HWA GeoSciences Inc. be retained to monitor construction, evaluate subgrade
soil and ground water conditions as they are exposed, and verify that subgrade preparation,
backfilling, and compaction are accomplished in accordance with the specifications.
Within the limitations of scope, schedule and budget, HWA attempted to execute these services
in accordance with generally accepted professional principles and practices in the fields of
geotechnical engineering and engineering geology at the time the report was prepared. No
warranty, express or implied, is made. The scope of our work did not include environmental
assessments or evaluations regarding the presence or absence of wetlands or hazardous or toxic
substances in the soil, surface water, or ground water at this site.
HWA does not practice or consult in the field of safety engineering. We do not direct the
contractor's operations, and cannot be responsible for the safety of personnel other than our own
on the site. As such, the safety of others is the responsibility of the contractor. The contractor
should notify the owner if any of the recommended actions presented herein are considered
unsafe.
Final Report 10 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
O .O
We appreciate the opportunity to be of service to you on this project.
Sincerely,
HWA GEOSCIENCES INC.
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Steven E. Greene, L.G.,L.E.G. George Minassian, Ph.D., P.E.
Senior Engineering Geologist Pavement Engineer
SEG:GM:seg
Final Report 11 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
REFERENCES
Federal Aviation Administration, 2008,Airport Pavement Design and Evaluation Advisory
Circular, AC 150/5320-6E.
Federal Aviation Administration, 2007, Standards for Specifying Construction of Airports, AC
150/5370-10C.
Mullineaux, D.R., 1965, Geologic Map of the Renton Quadrangle, King County, Washington.
U.S.G.S Map QC-405.
WSDOT, 1995, WSDOT Pavement Guide Volume 2 Pavement Notes, Washington State
Department of Transportation.
WSDOT, 2010,Standard Specifications for Road, Bridge and Municipal Construction, M 41-10,
Washington State Department of Transportation.
Final Repoit 12 HWA GEOSCIENCES INC.
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REPORTGEOTECHNICAL ENGINEERING
• RENTON MUNICIPAL AIRPORT •-.
TAXIWAY B REHABILITATION
•
- - - - - - - - Renton Airport Taxiway B
Exploration Locations
I I o Exploration Northing Westing sta Offset
Core-1 47,49516 122.21492 44+09 275 E
I Core-2 47.49447 122.21476 41+54 294 E
CORE-16 Core-3 47.49410 122.21459 40+17 319 E
CORE-14 CORE 191� Core-4 47.49306 122.21441 36+58 323 E
CORE-15 I I Core-5 47.49241 122.21439 34+25 304 E
RE-13 ❑ I Core-6 47.49008 122.21384 25+78 350 E
- TP-3 Core-7 47.48869 122.21350 20+54 383 E
CORE-1 I I Core-8 47.48838 122.21355 19+28 356 E
Core-9 47.48774 122.213,57 16+94 330 E
Core-10 47.48656 122,21362 12+54 278 E
CORE-8 Core-11 47.48649 122.21331 12+24 355 E
-- I CORE ? CORE-7 CORE-21 Core-13 47.48608 122.21405 10+98 148 E
CORE-10 L Core-14 47.48609 122.21412 10+94 129 E
I I Core-15 47,48624 122.21413 11+52 133 E
CORE-18 T Core-16 47.48629 122.21425 11+73 103 E
I Core-17 47.48854 122.21354 19+83 393 E
Core-18 47.48872 122.21332 20+43 455 E
CORE-11 I I I Core-20 47.48932 122.21365 22+67 397 E
0' I SCALE: 1"=100' TP-1 47.48969 122.21400 40+37 278 E
SCALE: 1"=100
JL I 1P-2 47.4969 122.214 24+ 298 E
-J TP-3 47,48816 122.21381 18+62 298 E
DETAIL A DETAIL B
Locations based on field GPS data.
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1 CORE-17
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DETAIL B
LEGEND
TP-3 0' 300' 600' 1200'
TEST PIT DESIGNATION AND APPROXIMATE LOCATION
CORE-14 SCALE: 1"=300'
CORE HOLE DESIGNATION AND APPROXIMATE LOCATION
FIGURE N0.
FINAL GEOTECHNICAL ENGINEERING REPORT DRAWN BY EFK w
� RENTON MUNICIPAL AIRPORT SITE AND DRAWN
HWAGEOSCIENCESINC. TAXIWAY B REHABILITATION EXPLORATION CHECK BY SG
PRO]ECr N0.
RENTON, WASHINGTON PLAN SATE 2011-039-21
BASE MAP PROVIDED BY REID MIDDLETON fm
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Map Symbol Geologic Description NORTH
of Artificial Fill
afm Urban or Industrial land modified by widespread or discontinuous fill
Qac Alluvium—sand and gravel deposited by the Cedar River, and associated
beds of silt, clay and peat.
Qit Kame Terrace Deposits—sand and pebble—to-cobble gravel in scattered
terraces.
Map taken from: D.R. Mullineaux, 1965
GEOLOGIC MAP FIGURE No
GEOTECHNICAL ENGINEERING REPORT 3
�1 RENTON MUNICIPAL AIRPORT PROJECT No
HWAGECISCIENCES INC. TAXIWAY B REHABILITATION 2011-039
RENTON WASHINGTON
APPENDIX A
FIELD EXPLORATION
RELATIVE DENSITY OR CONSISTENCY VERSUS SPT N-VALUE TEST SYMBOLS
COHESIONLESS SOILS COHESIVE SOILS %F Percent Fines
Approximate Approximate AL Atterberg Limits: PL=Plastic Limit
Density N(blows/ft) pp Consistency N(blows/ft) Undrained Shear LL=Liquid Limit
Relative Density(%) Strength(psf) CBR California Bearing Ratio
Very Loose 0 to 4 0 - 15 Very Soft 0 to 2 <250 CN Consolidation
Loose 4 to 10 15 - 35 Soft 2 to 4 250 - 500 DID Dry Density(pcf)
Medium Dense 10 to 30 35 - 65 Medium Stiff 4 to 8 500 - 1000 DS Direct Shear
Dense 30 to 50 65 - 85 Stiff 8 to 15 1000 - 2000 GS Grain Size Distribution
Very Dense over 50 85 - 100 Very Stiff 15 to 30 2000 - 4000 K Permeability
Hard over 30 >4000 MD Moisture/Density Relationship(Proctor)
MR Resilient Modulus
USCS SOIL CLASSIFICATION SYSTEM
PID Photoionization Device Reading
MAJOR DIVISIONS GROUP DESCRIPTIONS PP Pocket Penetrometer
Approx Compressive Strength(tsf)
Gravel and �' GW Well-graded GRAVEL SG Specific Gravity
Coarse Clean Gravel TIC Triaxial Compression
Grained Gravelly Soils (little or no fines)
GP Poorly-graded GRAVEL TV Torvane
Soils ° Approx Shear Strength(tsf)
More than
50%of Coarse Gravel with '41 GM Silty GRAVEL UC Unconfined Compression
Fraction Retained Fines(appreciable
on No.4Sieve amount of fines) GC Clayey GRAVEL SAMPLE TYPE SYMBOLS
Sand and Clean Sand SW Well-graded SAND ® 2.0"OD Split Spoon(SPT)
Sandy Soils (little or no fines) (140 lb.hammerwith 30 in.drop)
More than SID Poorly-graded SAND
50%Retained Shelby Tube
50%or More
on No. of Coarse Sand with r.' SM Silty SAND
200 Sieve Fines(appreciable 3-1/4"OD Split Spoon with Brass Rings
Fraction Passing
Size No.4 Sieve amount of fines) SC Clayey SAND O Small Bag Sample
Fine Silt
ML SILT Large Bag(Bulk)Sample
Grained and Liquid Limit
Less than 50% CL Lean CLAY � Core Run
Soils Clay _
OL Organic SILT/Organic CLAY Non-standard Penetration Test
(3.0"OD split spoon)
MH Elastic SILT
50%or More Silt
Liquid Limit
Passing and 50%orMore CH Fat CLAY GROUNDWATER SYMBOLS
No.200 Sieve Clay
OH Organic SILT/Organic CLAY Groundwater Level(measured at
Size time of drilling)
1 Highly Organic Soils PT PEAT Groundwater Level(measured in well or
110 open hole after water level stabilized)
COMPONENT DEFINITIONS COMPONENT PROPORTIONS
COMPONENT SIZE RANGE PROPORTION RANGE DESCRIPTIVE TERMS
Boulders Larger than 12 in
<5% Clean
Cobbles 3 in to 12 in
Gravel 3 in to No 4(4.5mm)
5-12% Slightly(Clayey,Silty,Sandy)
Coarse gravel 3 in to 314 in
Fine gravel 3/4 in to No 4(4.5mm)
Sand No.4(4.5 mm)to No.200(0.074 mm) 12-30% Clayey,Silty,Sandy,Gravelly
Coarse sand No.4(4.5 mm)to No.10(2.0 mm)
Medium sand No.10(2.0 mm)to No.40(0.42 mm) 30-50% Very(Clayey,Silty,Sandy,Gravelly)
Fine sand No.40(0.42 mm)to No.200(0.074 mm)
Silt and Clay Smaller than No.200(0.074mm) Components are arranged in order of increasing quantities.
NOTES: Soil classifications presented on exploration logs are based on visual and laboratory observation.
Soil descriptions are presented in the following general order: MOISTURE CONTENT
Density/consistency,color,modifier(if any)GROUP NAME,additions to group name(if any),moisture DRY Absence of moisture,dusty,
content. Proportion,gradation,and angularity of constituents,additional comments. dry to the touch.
(GEOLOGIC INTERPRETATION) MOIST Damp but no visible water.
Please refer to the discussion in the report text as well as the exploration logs for a more WET Visible free water,usually
complete description of subsurface conditions. soil is below water table.
FINAL GEOTECHNICAL ENGINEERING REPORT LEGEND OF TERMS AND
1
RENTON AIRPORT TAXIWAY B REHABILITATION SYMBOLS USED ON
HMQ0SCRNCESINC RENTON MUNICIPAL AIRPORT EXPLORATION LOGS
RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: A-1
LEGEND 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/2/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/2/2011 I
SAMPLING METHOD: Hand Tools LOGGED BY: S.Greene
LOCATION: See Figure 2. SURFACE ELEVATION: 18.5 *feet
U) Ir W I
m Z w Dropweight Cone Penetrometer
U a ) Q (140 lb.weight,30"drop) Z
= JO J w LU ° z ♦ Blows per foot I
�^ m EL a W > >w
z o x O
W d } rn Q Q W — N J N
o cn D DESCRIPTION U) rn a O 0 0 10 20 30 40 50 W
0 I
2-inches of HMA Pavement(ASPHALTIC CONCRETE)
Dense,gray crushed rock consisting of 2-inches of CSTC S-1
" overlying 3-inches of CSBC.
(GRAVEL BASE) S-2
GP Med.dense to dense,dark olive brown GRAVEL with sand S-3 GS
° and cobbles,moist.
p (FILL)
O I°Q :....:....:....:....:....:..............
O
Q
I
Hand excavation terminated due to refusal on cobbles. No
Ground water observed while conducting this hand boring.
I
I
I
I
15
I
I
5
0 20 40 60 80 100
Water Content(%)
Plastic Limit f— 0 Liquid Limit I
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-01
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
����N�$�C' RENTON, WASHINGTON
PROJECT NO.. 201 1-039 FIGURE: A-2
BORING-DSM 2011-039.GPJ 9128/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/2/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/2/2011
SAMPLING METHOD: Hand Tools LOGGED BY: S.Greene
LOCATION: See Figure 2. SURFACE ELEVATION: 18.9 t feet
w
m Z w Dropweight Cone Penetrometer
Ua N ) Q (140 lb.weight,30"drop) Z
O w w w— p ♦ Blows per foot O
m co W o o w n Q
o m U Z o = O
LL d } to Q Q w— H K
o cn Z) DESCRIPTION rn U) o-: O O 0 10 20 30 40 50 Lu
0—
riches of HMA Pavement.
(ASPHALTIC CONCRETE)
- Dense,gray,crushed rock.2-inches of CSTC over 3-inches S-1
"(fir of CSBC.
GP (GRAVEL BASE) S-2
o Medium dense,brown,poorly graded GRAVEL with sand
o and cobbles,moist.
Q (FILL)
o
ML Dark olive brown,sandy SILT,moist.Contains 1.2%organic S-3
matter by dry weight.
(ALLUVIUM)
:....:..............:....:....
S-4 AL
GS
♦:
Hand boring terminated at an approximate depth of 2.5 feet
below existing pavement surface. DCP testing conducted
from 2.5 to 4.3 feet below the existing ground surface. No
groundwater observed while conducting this hand boring.
♦
♦ :
15
♦:....:....:....:....:....:.... ....:....:....
♦
♦
5
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
UWA RENTON AIRPORT TAXIWAY B REHABILITATION CORE-02
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSCIENCESINC RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-3
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Casacde Concrete Sawing and Drilling DATE STARTED: 6/2/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/2/2011 I
SAMPLING METHOD: Hand Tools LOGGED BY: S.Greene
LOCATION: See Figure 2. SURFACE ELEVATION: 18.3 *feet
U) of w I
g m a N w Dropweight Cone Penetrometer
w
U a r F_ 2 (140 lb.weight,30"drop) Z
O J J w F z ♦ Blows per foot I
Co U) a s w Z) >
o 2 U 2 2 Z o = O
w a } rn Q Q w— H 0Y Lu
❑ cn DESCRIPTION U) U) a O O 0 10 20 30 40 50 w
0 I 2.25-inches of HMA pavement.(ASPHALTIC CONCRETE)
Dense,gray CSBC.Layer 1.5-inches thick. S-1
ML (GRAVEL BASE) S-2
Medium stiff,grayish brown,sandy SILT,non-plastic. '
SP (FILL) S-3
Loose to medium dense,brown,medium to fine,poorly
graded SAND,moist.
SM Medium dense to loose,grayish brown,Silty fine SAND,
moist to wet.
(FILLIDISTURBED NATIVE ALLUVIUM) I
I
ML Soft,sandy SILT to SILT with fine sand with 1.6%organic S-4 GS
matter by dry weight,wet,slightly plastic.
(NATIVE ALLUVIUM) I
I
15
Hand boring terminated at an approximate depth of 2.8 feet.
DCP testing conducted from 2.8 to 4.9 feet below the
existing pavement surface. No ground water was observed I
while conducting this hand boring.
I
I
5
0 20 40 60 80 100
Water Content(%)
Plastic Limit I--0 Liquid Limit I
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
UWA RENTON AIRPORT TAXIWAY B REHABILITATION CORE-03
HMGEOSCIENCES INC. RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-4
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.5 *feet
W
M Z - w Dropweight Cone Penetrometer
v a r N Q (17.6 Ib.weight,22.6"drop) Z
w w w e o ♦ Blows per foot O
x0 rn J J Z
o 2 U 2 z x O
W } to Q Q W o 0 F- d' J a)
0 rn x DESCRIPTION U) W a'° O 0 0 10 20 30 40 50 w
0
1.5-inches HMA pavement.
[ASPHALTIC CONCRETE]
GW Gray,crushed rock CSTC.Layer 1-inch thick. O S-1
[GRAVEL BASE]
1.75-inches HMA
SM I [ASPHALTIC CONCRETE)
:.. I Loose,brown,fine to coarse sandy,fine to coarse GRAVEL
r (with trace silt,moist. I O S-2
I [FILL]
----------- ---------�
Medium dense,gray,silty SAND to sandy SILT with trace
SP gravel,moist. ______ ____
-----�
Medium dense,gray,fine to medium SAND with fine to
coarse gravel,trace silt,moist.
Cobble at 29 inches.
19
OL Soft to medium stiff,brown organic SILT with gray sand
_ seam,and occasional reeds,moist to wet. 0 S-3
_ [ALLUVIUM]
♦ :
Q A. .... ....:....:....:....:..............:....
Core hole was terminated at 50-inches below ground ♦: 15
surface due.Ground water seepage was observed at A'
5 48-inches below ground surface during the exploration.
♦
...... .................
..
;♦
♦
♦
♦
♦:
♦:
♦:
♦:
10
10—
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
1
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-04
HIMIGEOSCUENCESINC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-5
BORING-DSM 2011-039.GPJ 9128/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/2/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/2/2011 I
SAMPLING METHOD: Hand Tools LOGGED BY: S.Greene
LOCATION: See Figure 2. SURFACE ELEVATION: 19.5 t feet
rn of W
Q M z w Dropweight Cone Penetrometer
U } r Q (140 Ib.weight,30"drop) Z
= JO 0 w W � \ o ♦ Blows per foot
Of
z
F- m U) o- o- w W > >
o-a, U 2 z x O
W a) )_ rn Q Q W o— H OfJ �
o rn > DESCRIPTION U) U) a g O O 0 10 20 30 40 50 W
0 I
2-inches of HN1A pavement.(ASPHALTIC CONCRETE)
Dense, gray,crushed rock,6-inches of CSBC,moist. S-1
(GRAVEL BASE)
SP Medium dense,brown,poorly graded SAND with silt and S-2
SM gravel,moist.
(FILL)
SM Medium dense,dark gray,silty medium SAND with S-3 GS
gravel-contains,pieces of brick,glass,and shell fragments.
(DREDGE FILL) I
I
I
I
Handboring terminated at an approximate depth of 2.5 feet.
Soils appeared saturated and borehole sidewalls began to I
collapse upon withdrawal of the auger.
I
15 I
5 I
0 20 40 60 80 100
Water Content(%)
Plastic Limit I-01 Liquid Limit I
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-05
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
�A����C' RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-6
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/7/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/7/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.5 *feet
w
Q m z w Dropweight Cone Penetrometer
U } i t Q (17.6 lb.weight,22.6"drop) Z
JO 0 J J .\ p ♦ Blows per foot
z
�� m rn a d 3 w D j-
w ai } cUn Q Q w 5 ~ � 2
o N > DESCRIPTION U U) a O c9 0 10 20 30 40 50 w
0
8.5-inches of HMA Pavement.
[ASPHALTIC CONCRETE]
r: .:• 6-inches Portland Cement Concrete
....:....:....:....:....:...
Loose,gray,fine to coarse gravelly,fine to coarse SAND
.•. with cobbles and trace silt,moist.Becoming fine to medium
SAND with gravel. O S-1 '
o.. [FILL)
o.
• --------- --
SM Medium dense,gray,gravelly,silty fine to coarse SAND with S-2
pieces of brick and shell like material,moist.
(DREDGE FILL)
ML Ground water Seepage is encountered from upper fill layer
At is perching on silty sand fill layer. A:
OS3
Medium stiff,gray SILT with trace sand,reeds,and oxide
mottling,moist.
[ALLUVIUM]
15
'. ML Medium stiff to medium dense,gray,silty fine SAND to .
5 — SM sandy SILT,moist to wet. ___________
—/
OL Soft to medium stiff,brown organic SILT with gray sand S 4
_ seams,wood debris and scatteredl reeds,moist to wet. 0 1
ML Medium stiff to stiff,gray,SILT with wood debris and fine
sand seams,wet.
Core hole was terminated at 76-inches below ground A
surface.Ground water seepage was observed during the A:
exploration at 37.5-inches and 66-inches below ground
surface.
A:
:A
A :
A 10
10—
0 20 40 60 80 100
Water Content(%)
Plastic Limit a —I Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
1
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-06
HMGEOSCIENCES INC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-7
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/7/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/7/2011 I
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.7 t feet
of W I
Q m Z w Dropweight Cone Penetrometer
U r 2 _ C (17.6 lb.weight,22.6"drop) Z
O J J w .S p ♦ Blows per foot o I
eD
m m a a- W >
z o x z >
O Wz
W d } U) Q Q W— H J �
o W Z) DESCRIPTION U) N a o 0 0 10 20 30 40 50 W
0 I 8.5-inches HMA Pavement.
[ASPHALTIC CONCRETE]
"9=• 5-inches Portland Cement Concrete
....:....:....:....:....:....:... I
GP Loose,gray,poorly graded GRAVEL with fine to coarse O S-1
° SAND with cobbles and trace silt,moist to wet.
O [FILL]
°(SC
....:....:....:....:....:....:.... .. .. I
0
Q
Medium stiff,gray,gravelly,sandy SILT,moist to wet. I
Core hole was terminated at 39-inches below ground I
surface due to refusal on cobbles.Ground water seepage
was observed during the exploration at 32-inches below -
ground surface.
15 I
5 .... ....:....:....:....:....:....:....:....:....
I
....:... ..................:.... ..
r :
I
:....:....:.. .............. .. I
10
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
1
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-07
HMIGEOSCIENCESINC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: A-$
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/7/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/7/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.9 *feet
w
Q m z w cc Dropweight Cone Penetrometer
U a 2 L Q (17.6 lb.weight,22.6"drop) Z
J ~ Z cn .E H p ♦ Blows per foot O
2 J O i J W � Z Q
m U) a a_ w > >�
O
W } to Q Q W 0 F J �
o cn DESCRIPTION a) N a O c7 0 10 20 30 40 50 w
0
5.5-inches HMA Pavement.
[ASPHALTIC CONCRETE)
^= 6.5-inches Portland Concrete Cement
a'%• [PCC]
Ri•h::.
Loose,gray,fine to coarse gravelly,fine to coarse SAND
.•, with cobbles and trace silt,moist.
[FILL]
d.' O 3-1
.�
o.
A' _______________
SM Medium dense,gray,gravelly sandy SILT to silty SAND,
moist. O S 2 :.... .... .... ...: ..
Medium stiff,gray,SILT with sand to sandy SILT,moist.
[ALLUVIUM]
♦ :
" ------- .........
OH Medium stiff,brown with gray mottling,ORGANIC SILT with -
trace fine sand seams and reeds,moist. O S-3 -
5 ——————— SZ .............:....:....:.... .. 15
ML Medium stiff,gray,fine sandy SILT with interbedds of fine
sand and reeds,wet.
•OS-4 .... ....:....:.... ....: ..
Core hole was terminated at 79-inches below ground ....:....:....r.. ..
surface.Ground water seepage was observed during the
exploration at 60 to 62-inches below ground surface.
:....:....♦.. ....:....:.........:....:....
♦:
10 10
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1— 0—i Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
1
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-08
HMGEOSCIENCESINC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-9
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/7/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/7/2011 I
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.9 *feet
rn [if W I
Q M Z - w Dropweight Cone Penetrometer
U } 2 ) Q (17.6 lb.weight,22.6"drop) Z
= o w W uj z ♦ Blows per foot ¢ I
�^ m a a W > >w
2 2 z = O
W N Y (n Q Q W 0 o H K � �
o u> > DESCRIPTION U) rn a O O 0 10 20 30 40 50 W
0 I 10-inches HMA Pavement.
[ASPHALTIC CONCRETE]
Loose,grayish brown,fine to coarse gravelly,fine to coarse ....:....:....:....:....:....:....
�. . SAND with cobbles and trace silt,moist.Becoming fine to I
medium SAND with gravel.
[FILL)
Q;Q O S-1
SM Medium dense,Dark olive brown,silty,gravelly fine to
medium SAND,moist O S-2
I
ML Medium stiff,gray,SILT to CLAY with trace fine sand, "". . ""
moist. OS-3
[ALLUVIUM]
I
5 '
15
ML Medium stiff to medium dense,gray,silty fine SAND to '
SM sandy SILT,wet.
A:....
S-4 I
0
♦ - I
:♦
♦ :
Core hole was terminated at 90-inches below ground
surface.Ground water seepage was observed during the I
exploration at 65-inches below ground surface.
10 I
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit m 0 Liquid Limit I
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-09
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSQENCESINC. RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-1
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.1 *feet
rn of W
Q m Q Of
Z w Dropweight Cone Penetrometer
U a_ D Q (17.6 Ib.weight,22.6"drop) Z
J ~ z rn p ♦ Blows per foot O
VJ J J W Z H
m U) d a u > >w
0_ U z p x O
W a) } rq Q Q W— � JR
0=w cn Z) DESCRIPTION rn rn a_ O (9 0 10 20 30 40 50 W
0
2.25-inches HMA Pavement.
Q GP [ASPHALTIC CONCRETE]
0
Dense to very dense,gray fine to coarse sandy,fine angular
GRAVEL,moist.
C) [GRAVEL BASE]
0 0 S-1
o Q
Q
- ♦ 33
Core hole was terminated at 26-inches below ground
surface.No ground water seepage was observed during the
exploration. "
A:
15
5 ....:...................:....:....:....:....:....
........................:..............:.........
10
10—
0 20 40 60 80 100
Water Content(%)
Plastic Limit m 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
1
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-10
H M IGEOSCIE rCES INC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: A'1 1
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/7/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/7/2011 I
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.1 t feet
(n 0_ W I
gW m z N w Dropweight Cone Penetrometer
U a L N ~¢ (17.6 lb.weight,22.6"drop) z
O J J w e o ♦ Blows per foot O I
z
m rn o_ o- 3 W > >
o-�, O z o x OLU
W >- (n Q Q W— H J �
o� 0 > DESCRIPTION C0 rn o-a O O 0 10 20 30 40 50 W'
0 I 8.5-inches HMA Pavement.
[ASPHALIC CONCRETE]
8-inches Portland Cement Concrete
[PCC]
Loose,grayish brown,fine to coarse gravelly,fine to coarse
: . SAND with cobbles and trace silt,moist.
. . [FILL]
o. O S-1
.Q
SM Medium dense,dark olive brown,silty fine to medium SAND I
with gravel,moist. S-2 A. :....'....:.... ..
Piece of wood at 35-inches BGS. O
A.
---- » I
Probably gravelly SAND fill,no samples recovered.
Core hole was terminated at 45-inches below ground 15
surface due to refusal on cobbles.No ground water
seepage was observed during the exploration. I
5 ....:....:....:....:....:....
I
I
I
I
10
I
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit I--0 Liquid Limit I
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-11
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
�����$�C' RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: A—1,e
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 20.6 *feet
w
Q m Z w Dropweight Cone Penetrometer
v d � r N ¢ (17.6 lb.weight,22.6"drop) Z
J 1-- Z c 5 F p ♦ Blows per foot O
J O J J wCO Z co a s � � w Z) >w
a 2 U z o T O
w a) } (n Q Q w— 1--
J
0 tt, W T DESCRIPTION N rn a O c9 0 10 20 30 40 50 w
0
ches HMA Pavement.
[ASPHALTIC CONCRETE)
20
IE7
es Portland Cement Concrete
[PCC]oose,brown,fine to coarse gravelly,fine to coarse SAND
,•, with cobbles and trace silt,moist to wet.
[FILL] O S-1
o.•
. . . �.. ....:....:...... ..
°:. SM Loose,grayish brown,silty fine to medium SAND with trace
fine gravel,moist.
O S-2
A:
♦:
a: Piece of wood encountered.
Light grayish brown,gravelly SAND with trace silt and O S-3
5 rootlets,moist.
p:•,.
♦:
p'© 15
d'• Sand becomes coarser.
Medium dense,interbedded gray,silty fine SAND with A:
brown fine to medium SAND,moist. A:
S-4 ♦:
4:
Core hole was terminated at 86-inches below ground
surface due to refusal on cobbles.No ground water
seepage was observed during the exploration.
.................................................
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit a —i Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
1
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-12
HMGEOSCIENCESINC. RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-1 3
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011 I
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 21.4 t feet
W w I
w
CO z w Dropweight Cone Penetrometer
U a t Q (17.6 lb.weight,22.6"drop) z
= OJ 00 W J p ♦ Blows per foot I
Ld co
z
F- m o- o- w D >w
o_ U Z o 2 O
W a) } V) Q Q W — H (D "
o m Z) DESCRIPTION V) U) o- O c7 0 10 20 30 40 50 w
0
3-inches HMA Pavement. I
[ASPHALTIC CONCRETE]
6-inches Portland Cement Concrete
[PCC]
.' GW Loose,brown,well graded GRAVEL with sand and cobbles O S-1 I
and trace silt,moist to wet.
[FILL] 20
....:....:....:....:....:.........:.. .:.. .:.. .
I
.'
ML Gray to light brown,sandy SILT,moist.Oxide mottling S-2
present.
0 l i
(ALLUVIUM) :....:.♦:..............:.
Becoming light brown medium SAND to gray silt.
Interbeds/lenses of gray silt from 49-51 inches.
A. I
O S-3
5 ....:....:....:....:....:...�
Core hole was terminated at 57-inches below ground :>>
surface due to refusal on cobbles.No ground water I
seepage was observed during the exploration. >>
♦ :
15 I
:....:....:....:.A ..
;V
I
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit m is Liquid Limit '
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
=A FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-13
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSCIENCESINC RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-14
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 20.8 *feet
w
Q m Z w Dropweight Cone Penetrometer
U } ) Q (17.6 lb.weight,22.6"drop) z
Z cn 0 w p ♦ Blows per foot O
�� m � o o w > >
a — 2 U
O
w
IL Z
u1 Q w
oa DESCRIPTIONn n n
0 10 20 30 40 50 w
0
4.75-inches HMA Pavement.
[ASPHALTIC CONCRETE]
yg: 6-inches Portland Cement Concrete
20
O.•. Loose,brown,fine to coarse gravelly,fine to coarse SAND ....:....:....:....:....:....:....:....:....:....
y. . with cobbles and trace silt,moist to wet.
[FILL]
d.
u. 0
. . .
SP Light brown,fine SAND with silt and trace gravel,moist.
SM (ALLUVIUM) +
0 S-2
.............................
♦:
Interbeds/lenses of gray silt in sample. S-3 ♦40 L
0 ♦
5 ♦ ... .... ....:....:....:....:....:....:....
♦ :
Core hole was terminated at 60-inches below ground
surface.No ground water seepage was observed during the
exploration.
15
.... .... .........:....:....:....:....:....
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit 2 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
1
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-14
HMGEOSCIENCESINC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-1 5
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011 I
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 20.7 t feet
U) of W I
Q m z w Dropweight Cone Penetrometer
U a F-L Q (17.6 lb.weight,22.6"drop) Z
J O w w w e o ♦ Blows per foot I
x U) J J � Z
m U) a a w
IL a, 2 U 2 2z o x O
W N Y U) Q Q W— H Of
o rn x DESCRIPTION U) N a O O 0 10 20 30 40 50 W
0 I 6-inches HMA Pavement.
[ASPHALTIC CONCRETE]
1r,
6-inches Portland Cement Concrete
[PCC] 20
GP Loose,brown,poorly graded angular GRAVEL with sand,
O �.
° moist. S-1
SW [CRUSHED GRAVEL BASE]
Loose to medium dense,brown,silty,fine to coarse 0 S-2 �' I
'i. gravelly,fine to coarse SAND,moist. .................. ..
SP %————————— [FILL] ---------�
Loose to very loose,light brown,fine to medium SAND with
GP silt,moist. /
`--------------------- O S-3 � ' I
o Loose,grayish brown,poorly graded GRAVEL with sand,
Q moist. .... ..:....:....:....:....:....:....:. .:
A :
o� �
Q I
Q
p:.:. Piece of wood encountered. A: » I
Light grayish brown,gravelly SAND with trace silt and S-4
O
rootlets,moist.
:p.:•. (FILUDISTURBED NATIVE) :
Core hole was terminated at 64-inches below ground 15 I
surface due to refusal on cobbles.No ground water
seepage was observed during the exploration. I
I
I
I
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1--0 Liquid Limit I
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-15
HMIGEOSCIENCESllNC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-1 E
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 20.7 *feet
w
Q m Z w Dropweight Cone Penetrometer
J
V a r ¢ (17.6 Ib.weight,22.6"drop) Z
J O w w w e w p ♦ Blows per foot O
x O d d w j ¢
F m rn
a c> z o x O
w �, r cn ¢ ¢ w— W wd
0 cn D DESCRIPTION U) rn a O O 0 10 20 30 40 50 w
0
3.5-inches HMA Pavement.
[ASPHALTIC CONCRETE]
7-inches Portland Cement Concrete
[PCC]
20
Ai 4
• ••• SW Loose,brown,fine to coarse gravelly,fine to coarse SAND
with silt,moist. O S-1
[FILL]
SM Medium dense,gray,silty fine to medium SAND with fine to
coarse gravel,moist.Pieces of brown silt present.
----------------------
•,•,• SW Loose to medium dense,light brown,fine to coarse gravelly, ....:....:....:....:....:....:....:....:....:....
fine to coarse SAND with trace silt and cobbles,moist.
O S-3 3
�3
�3
33
Core hole was terminated at 36.5-inches below ground
surface due to refusal on cobbles.No ground water
seepage was observed during the exploration. 3
3
:33
5
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1--0—i Liquid Limit
NOTE. This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
1
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-16
HMGEOSMCESINC. RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: /4-1 7
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 7/11/2012
DRILLING METHOD: 12-inch Diamond Core DATE COMPLETED: 7/11/2012 I
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.7 t feet
w
W 0
J w m Q N w Dropweight Cone Penetrometer
U a- N t Q (17.6 lb.weight,22.6"drop) Z
0 ~ Z 0 .� p ♦ Blows per foot O I
r) w ° z Q
m rn a a-w w
a N w > >�
= o w
w a) } rn Q Q w — H J
0 cn D DESCRIPTION N 0 a O 0 0 10 20 30 40 50 w'
0
7-inches HMA Pavement. I
[ASPHALTIC CONCRETE]
i; 8-inches Portland Cement Concrete
a%• [PCC]:.•.. ....:....:....:....:...
GW Medium dense,gray,sandy,cobbly,fine to coarse S-1 >>
•' GRAVEL,moist to wet. !
A Ii
[FILL] ♦. '
•
SM Medium dense,dark gray,slightly silty,
•,• ;; g y, g y gravelly,fine to 0 S-2 ♦
medium SAND,moist.Trace wood debris.
A:.... ..
MIL Medium stiff,gray,slightly sandy,SILT,moist.Organic I
debris and brown mottling observed. ♦:
[ALLUVIUM] O S-3
♦ :
15______________________ ♦ I
OL Medium stiff,brown,ORGANIC SILT,moist.
5 — ♦.:....:....:....:....:....:....:....:....:....
= O S-4 ♦_
I
I
...........................
A A.
Core hole was terminated at 72-inches below ground & I
surface due to refusal on cobbles.No ground water A
seepage was observed during the exploration. r
» I
.A .
I
i
10 I
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1--0 Liquid Limit I
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-17
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSCIENCES INC RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: A- f
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 7/11/2012
DRILLING METHOD: 12-inch Diamond Core DATE COMPLETED: 7/11/2012
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.6 *feet
w
Q Lu m z W Dropweight Cone Penetrometer
cJj a- 2 N t Q (17.6 lb.weight,22.6"drop) Z
o w w w Z ♦ Blows per foot o
w Z) Q
m U) o- CL
a�, o z x o
W } (n Q Q W —o N JN
o ttl u> > DESCRIPTION U) U) o- o c7 0 10 20 30 40 50 w
0—
-nc es HMA Pavement.
[ASPHALTIC CONCRETE]
? 6-inches Portland Cement Concrete
[PCC]
GW Medium dense,gray,sandy,cobbly,fine to coarse
• GRAVEL,moist to wet. S-1
• [FILL]
Ground water seepage observed at 2.16 feet below ground
.' surface.(BGS)
--
SM Medium dense,dark gray,slightly gravelly,sandy SILT,
moist to wet.Trace wood debris.
O S-2 •
♦.
ML Medium stiff,gray,SILT to CLAY,moist.Organic debris and
brown mottling observed.
[ALLUVIUM] 0 S-3 ♦ 15
5 ♦.:....:....:....:....:....:....:....:....:....
OL Medium stiff,brown,ORGANIC SILT,moist.Lenses of gray
fine sand observed.
Core hole was terminated at 72-inches BGS due to refusal
on cobbles.Ground water seepage was observed at 2.16
feet BGS during the exploration.
10
10—
0 20 40 60 80 100
Water Content(%)
Plastic Limit I--0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-18
HMGEOSCIENCESINC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: A'1 9
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 7/11/2012
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 7/11/2012
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.5 t feet
Cf w I
gM zQ N w Dropweight Cone Penetrometer
J a- a) Q (17.6 lb.weight,22.6"drop) Z
J O z v5 .S p ♦ Blows per foot O
= N J J c w Z H
F. m rn a s N j 1.
p 2 O Wa)
W } (n Q Q W — H J �
o v> > DESCRIPTION rn rn a O cD 0 10 20 30 40 50 w
0 I 12-inches HMA Pavement.
[ASPHALTIC CONCRETE]
7-inches Portland Cement Concrete
Ai? [PCC]
rg.•,, i
I
GW Medium dense,gray,sandy,cobbly,fine to coarseAA
•' GRAVEL,moist to wet. S-1 ♦: I
[FILL]
ML Medium stiff,gray to brown,SILT,moist.Organic debris I
and brown mottling observed.
[ALLUVIUM] O S-2
OS3 ♦ :
♦ 15 I
--------------- —
5 — OL Medium stiff,gray,silty CLAY to clayey SILT,moist.Trace O S 4
organics observed.
Core hole was terminated at 66-inches BGS due to refusal
on cobbles.No ground water seepage was observed during
the exploration. I
I
I
10
10 I
0 20 40 60 80 100
Water Content(%)
Plastic Limit I--0 Liquid Limit I
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
=A RENTON AIRPORT TAXIWAY B REHABILITATION CORE-19
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSCIENCES INC RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-2(
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 7/11/2012
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 7/11/2012
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 20.0 t feet
w
2 m Z w Dropweight Cone Penetrometer
U a- F-- Q (17.6 lb.weight,22.6"drop) Z
Lu
J O w w w e o ♦ Blows per foot
F- m d a- W = Q
0_ U Z o 2 O
W y } (n Q Q W— t- J_N
o rn D DESCRIPTION rn U) o O 0 10 20 30 40 50 w
0-
6-inches HMA Pavement.
[ASPHALTIC CONCRETE]
�= 7-inches Portland Cement Concrete
.Aa
.,.; [PCC]
a-, GW Medium dense,gray,sandy,cobbly,fine to coarse S-1 ♦ '
• GRAVEL,moist to wet.
[FILL]
•
•
ML Medium stiff,gray,slightly sandy SILT,moist. O S-2 "A ....
[ALLUVIUM]
OL Medium stiff,gray to brown,SILT to ORGANIC SILT,moist. A
_ Organic debris and brown mottling observed. �
S-3 A
0
5 — ...:....:....:.........:....:....:....:.... 15
Core hole was terminated at 66-inches BGS due to refusal
on cobbles.No ground water seepage was observed during
the exploration.
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1 0 { Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-20
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSCIENCES INC RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-21
BORING-DSM 2011-039.GPJ 9/28/12
EXCAVATION COMPANY: Deeny Construction LOCATION: See Figure 2.
EXCAVATING EQUIPMENT: Case 590 Backhoe DATE COMPLETED: 6/3/11
SURFACE ELEVATION: 19 t Feet LOGGED BY: S.Greene
(1i Of
U) w Of
w °0 _ rn LU
U d o H
Q
o W W z o SKETCH OF SIDE OF PIT w
0- 2 � g g z = O HORIZONTAL DISTANCE(feet) ~a
0 U) D DESCRIPTION (0 2 0 O (D 0 2 4 6 8 10 0
0 a r SP 3-inch layer of grass and sod. 0
Medium dense,brown,poorly graded SAND with silt and gravel, S-1 22 .........:....:.... ....
..... .............
SM moist.
OH B-1 67 AL ..:....:....:.... ....:....:....:.... ....:....:.... .. ..
(FILL) :.. . . .:....:.. .:.. . . .:. .:.. .
Medium stiff,grayish brown,ORGANIC SILT,with 3.5%organic GS - .. .
matter,moist,plastic. In-place density of soil chunk=Dry density MD -
2 of 56.7 pcf @ 79.3%MC. CBR 2
(ALLUVIUM) :....:....:.... ....:.... .. .:.. .:.... . ..:.. .
OL Soft,gray to grayish brown,organic SILT,plastic. Contains thin S-3
layers of highly organic material,moist to wet.
. ..... .... ...... .. .... .
— SZ
4 4
Test pit terminated at an approximate depth of 4 feet below the
existing ground surface. Groundwater seepage was observed at an ...•:••••:....:.... ....:....:....:.... ....:.... .. ..
approximate depth of about 3.8 feet below the existing ground
6 surface. 6
8 8
10 10
NOTE: For a proper understanding of the nature of subsurface conditions,this exploration log should
be read in conjunction with the text of the geotechnical report. This log of subsurface
conditions applies only at the specified location and on the date indicated and therefore may
not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT LOG OF TEST PIT
RENTON AIRPORT TAXIWAY B REHABILITATION TP-1
HMGEDSQENCES INC. RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
_ _ JEC ZO� J -39 F � ^r
TPIT10 2011-039.GPJ 9/2872_
EXCAVATION COMPANY: Deeny Construction LOCATION: See Figure 2.
EXCAVATING EQUIPMENT: Case 590 Backhoe DATE COMPLETED: 6/3/11
SURFACE ELEVATION: 19 t Feet LOGGED BY: S.Greene
w Of
a-
m H
c� o ¢
J } U-1 (n
Jo 0 � w w Z SKETCH OF SIDE OF PIT
a Co U 2 2 O z _ 0 HORIZONTAL DISTANCE(feet) w
o M > DESCRIPTION can can 2 0 O C7 0 2 4 6 8 10 0
0 a r 3-inches of grass and sod. 0
Medium dense,gray silty SAND with trace fine gravel,moist.
ML :....
S-1 11 �•• •�•• •
(FILL)
ML Dense,gray,sandy SILT with fine gravel,moist. S-2 25
Medium stiff,brownish gray SILT with fine sand,moist,law plastic.
....:....:....:.... ....:....:....:.... ....:....:....:.... ................... ...................
2 OH Soft,gray to dark brown,ORGANIC SILT,moist to wet,plastic. B-1 102 AL 2
In-place density of soil chunk=dry density of 48.7 pcf @ 134.2% S-3 213 GS •••.....•.........• ••••.......•••.•••• •• •• ••
MC. MD
(ALLUVIUM) CBR :....:....:.... ....:....:....:.... ....:....:....:.... ....
4 4
Test pit excavation terminated at an approximate depth of 4 feet
below the existing ground surface. Ground water seepage was •••• •••• •••• •••• •••• •••• ••••'•••• •••• ••••:•••• ••
observed at an approximate depth of 3.5 feet below the existing
6 ground surface. 6
Buried concrete storm drain pipe exposed within south sidewall of
test pit excavation between depths of 1.5 to 2.5 feet below the •••• •••• •••• •••• •••• •••• •••• •••• •••• •••• •••• ••••
existing ground surface. Based upon position of pipe bell flow
direction appears to be toward taxiway infield(west). .... """' .... """' .... "" ..
8 8
10 10
NOTE: For a proper understanding of the nature of subsurface conditions,this exploration log should
be read in conjunction with the text of the geotechnical report. This log of subsurface
conditions applies only at the specified location and on the date indicated and therefore may
not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT LOG OF TEST PIT
RENTON AIRPORT TAXIWAY B REHABILITATION TP-2
HmaosC was INC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-23
TPIT10 2011-039.GPJ 9/28/12
EXCAVATION COMPANY: Deeny Construction LOCATION: See Figure 2.
EXCAVATING EQUIPMENT: Case 590 Backhoe DATE COMPLETED: 6/3/11
SURFACE ELEVATION: 20 t Feet LOGGED BY: S.Greene
(i W
U) w Of
w C0 cn W
w
= o 0 W W W SKETCH OF SIDE OF PIT w
a 2 0 2 2 z 0 HORIZONTAL DISTANCE(feet) a
M U) Z) DESCRIPTION W u¢i :5 0 O O 0 2 4 6 8 10 0
0 a r.• 3-inches of grass and sod. 0
GP S-1
Medium dense,brown,sandy GRAVEL with silt,moist. .. .. .. '•
GM
ML (FILL) S-2 16
................... ................... ............ ....
Medium dense,grayish brown,fine sandy SILT,moist,non-plastic.
....:....:....:.... ....:....:......... ....:....
MIL Loose to medium stiff,olive gray,sandy SILT,moist,non plastic. B-1 25 GS
2 In-place density of soil chunk=dry density 98.0 pcf @ 25%MC. MD 2
CBR
OL Medium stiff to soft,gray to grayish brown,organic SILT,moist to O S4 51
wet,low plastic. ....:....:.... ....:....:....: .. .. ..
4 (ALLUVIUM) 4
... .... . .. ......
Test pit excavation terminated at an approximate depth of 4 feet
below the existing ground surface. Ground water seepage was ...•:••••:.••.:.... ...•:•.••:•..•:.... ....:•••• .
observed at an approximate depth of 3.6 feet below the existing :
6 ground surface. 6
8 8
10 10
NOTE: For a proper understanding of the nature of subsurface conditions,this exploration log should
be read in conjunction with the text of the geotechnical report. This log of subsurface
conditions applies only at the specified location and on the date indicated and therefore may
not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT LOG OF TEST PIT
RENTON AIRPORT TAXIWAY B REHABILITATION TP-3
HWAGEOSCIENCES INC. RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
JEC ZO� � 19 F E
TPIT10 2011-039.GPJ 9/28/12 - -- - - - - -- --
APPENDIX B
LABORATORY TESTING
GRAVEL SAND SILT CLAY
Coarse Fine Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
314"
3" 1-1/2" 15/8" 3/8' #4 #10 #20 #40 #60 #100 #200
100
I I I I I I
I I I I I I I I I
90
I I I 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 I I
70
w I I I I I 1 1 I I
m so I I I I I I I I I I
w 50 I I I I I I I
Z I I I I I I I I I
LL I I I I I I I I I
Z 40
LLI I I I I I I I I I I
U I I I I I I I I I
30
w I I I I I I I I I I
20
I I I I I I I I I I
I I I I I I I I I
10
I I I I I I I I I
I I I I I I I I I
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL pl Gravel Sand Fines
• CORE-01 S-3 0.6-1.3 (GP)Dark olive brown,poorly graded GRAVEL with sand 5 52.7 43.4 3.9
■ CORE-02 S-4 2.0-2.5 (ML)Dark olive to gray,sandy SILT with 1.2%organic matter by dry weight 25 25 22 3 1.4 28.1 70.5
A CORE-03 S-4 2.3-2.8 (ML)Dark olive brown,SILT with 1.6%organic matter 39 1.6 29.3 69.1
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
fwaoSCIms INC. RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: B-1
HWAGRSZ 2011-039.GPJ 9/28/12
GRAVEL SAND SILT CLAY
Coarse Fine Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 15/8" 3/8" #4 #10 #20 #40 #60 #100 #200
100
I I I I I I I I I
I I I I I I I
90
I I I I I I 1 I I I
1 I I I I 1 I I I
80
= I I t I I 1 I I I I
70
w I I I I I I I I I
60 I I I I I I I
m I I I I I I I I I
tY I I I I I I I I I I
w 50
z I I I I I I I I I
w I I I I I I I I I
Z 40
w I I I I I I I I I
U I I I I I I I I
30
w I I I I I I I I
20
I I I I I I I I I I
10
I I I I I ILL
I
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
• CORE-05 S-3 1.0-2.4 (SM)Dark Gray,silty SAND with gravel,contains glass and shell fragments. 37 18.9 55.5 25.6
■ CORE-06 S-2 2.9-3.1 (SM)Dark grayish brown,silty SAND with gravel 10 44.3 37.1 18.6
A CORE-07 S-1 1.3-1.6 (GP)Gray,poorly graded GRAVEL with sand 5 54.0 42.5 3.5
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
tMGEOsaENCES INC. RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
JEC ZO 19 F C� .-
Nwar.R97 �mi_ns4t;p.i anan9 - — -
GRAVEL SAND SILT CLAY
Coarse Fine Coarse I Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 15/8" 3/8" #4 #10 #20 #40 #60 #100 #200
100
I I I I I I I I I
I I I I I I I 1
zl-
90
I I I I
I I I I I I
80
= I I I I I I I I I I
LD 70
w I I I I I I I I I
6o I I I I I I I I I
m I I I I I I I I I
W I I I I I I I I I I
w 50 I I I I I I I I I I
Z I I I I I I I I I I
w I I I I I I I I I I
Z 40
W I I I I I I I I I I
of 30
W I I I I I I I I I I
20
I I I I I I I I I I
I I I I I I I I I I
10
I I I I I I I I I I
I I I I I I I I I I
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
• CORE-08 (ML)Dark olive brown,SILT with sand 23 3.6 33.8 62.6
■ CORE-08 S-3 4.2-4.4 (OH)Dark grayish brown,organic SILT 114 108 74 34 3.8 10.8 85.5
A CORE-09 S-2 2.3-2.7 (SM)Dark olive brown,silty SAND with gravel 15 17.2 43.4 39.4
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
HMGEOSC was INC RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: B-3
HWAGRSZ 2011-039.GPJ 9128112
GRAVEL I SAND SILT CLAY
Coarse Fine I Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 15/8" 3/8" #4 #10 #20 #40 #60 #100 #200
100
I I I I I I I I
I I I I I I I I I
90
I I I I I I I I I
I 11 I I I I I
80
= I I I I I I I I I
70
w I I I 1 I I I I I
} 60 I I I I I I I I I
m I I I I I I I I I
w 50 I I I I I I I I I I
z I I I I I I I I I
w I I I I I I I I I
Z 40
w I I I I I I I I I I
30
w I I I I I I I I I I
20
I I I I I I I I I I
I I I I I I I I I
10
I I I I I I I I I
I I I I I I I
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
• CORE-11 S-2 3.0-3.5 (SM)Dark olive brown,silty SAND 16 13.4 51.2 35.4
■ CORE-12 S-2 2.8-3.3 (SM)Brown,silty SAND 14 14.5 49.0 36.5
A CORE-13 S-1 1.0-1.3 (GW)Dark olive brown,well graded GRAVEL with sand 3 70.1 26.8 3.0
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
IMGEOsaENCES INC RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON UEC 2C"" -39 i f
HWA R7 2011-039C;P.l 9/29/17
GRAVEL SAND SILT CLAY
Coarse Fine Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 5/8" 3/8" #4 #10 #20 #40 #60 #100 #200
I
"0�
I I I 1 I I 1 I I
I I 1 I I I I
90
I 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 I I
70
w I I I I I I I I I I
60 I I I I I I I I I
co I I I I I I I I I
Z 50 I I I I I I I I I
LL I I I I I I I I I I
Z 40
W I I I I I I I I I I
U I I I I I I I I I
� 30
LU I I I I I I I I I I
a I I I I I I I I I I
20
I I I I I I I I I
I I I I I I I I
10
I I I 1 I I I
I I I I I I I I I
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
• CORE-13 S-2 2.5-2.9 (ML)Brown,SILT with sand 21 14.6 29.7 55.7
■ CORE-14 S-3 4.4-4.8 (SP-SM)Brown,poorly graded SAND with silt 9 0.5 87.8 11.7
A CORE-15 S-1 1.2-1.4 (GP)Olive brown,poorly graded GRAVEL with sand 6 81.5 13.1 5.4
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
imaoSCIms INC. RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: B-5
HWAGRSZ 2011-039.GPJ 9/28/12
GRAVEL SAND SILT CLAY
Coarse Fine Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 15/8" 3/8" #4 #10 #20 #40 #60 #100 #200
100
I I I I I I I I
I I I I I I I I I I
90
I 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 I
70
w I I I I I I I I I
I I I I I I I I I
} 60 I I I I I I I I I I
co I I I I I I I I
W 50 I I I 1 I I I I I I
Z 1 I I I I I I I I
LL I I I I I I I I I
Z 40
W I I I I I I I I
U I I I I I I I I I
Of 30
20
I I I I I I I I I
I I I I I I I I I
10
I I I L-L0 I I I I
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
• CORE-15 S-4 4.7-5.2 (GP)Olive brown,poorly graded GRAVEL with sand 5 54.5 41.7 3.9
■ CORE-16 S-2 1.5-1.7 (SM)Brownish gray,silty SAND with gravel 25 16.2 49.1 34.7
A TP-1 B-1 0.9-2.5 (OH)Light olive brown,organic SILT with 3.5%organic matter 67 122 68 54 0.0 4.1 95.9
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
IMGEOsaENCESINC. RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON UEc 2C -39 1 F-
HWAGRSZ 2011-039.GPJ 9/28/12 - - - - - --- -- ---- _ -
GRAVEL SAND SILT CLAY
Coarse Fine Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 5/8" 3/8" #4 #10 #20 #40 #60 #100 #200
100
I II I I
90
I I I I I I I I
I I I I I I I I
I I I I I I I I I
80
= I I I I I I 1 I I
70
w I I I I I I I I I I
60 I I I I I I I I I I
m I I I I I I I I I I
W 50 I I I I I I I I I I
Z I I I I I I I I I I
W I I I I I I I I I I
Z 40
W I I I I I I I I I I
C) I I I I I I I I I I
30
W I I I I I I I I I I
20
I I I I I I I I I I
10
I I I I I I
0 1
I I I I
I I I I I I I I I I
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
• TP-2 S-2 1.1 -2.0 (ML)Brownish gray,SILT with sand 25 3.9 22.4 73.7
■ TP-2 B-1 2.0-2.5 (OH)Dark Brown,organic SILT 102 84 62 22 0.0 3.9 96.1
A TP-3 B-1 1.5-2.0 (ML)Dark olive gray,SILT with sand 25 0.0 23.7 76.3
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
BOA RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
HmaosC was INC. RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: B-7
HWAGRSZ 2011-039.GPJ 9/28/12
GRAVEL SAND SILT CLAY
Coarse Fine Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 1 5/8" 3/8' #4 #10 #20 #40 #60 #100 #200
100
I I I I I I I I I
I I I I I I I I I I
90
I I I 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 I I
L2 70
w I I I I I I I I I I
60 I I I I I I I I I I
m I I I I I I I I I I
w 50 I I I I 1 I I I I I
z I I I I I I I I I 1
w I I I I I I I I I I
Z 40
w I I I I I I I I I I
U I I I I I I I I I I
W 30
w I I I I I I I I I I
a I I I I I I I I I I
20
I I I I I I I I I I
I I I I I I I I I I
10
I I I I I I I I I I
I I I I I I I I I i
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
o a o
• TP-3 S-4 3.0-4.0 (OH)Dark gray,organic SILT 51 55 31 24 0.0 11.6 88.4
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
twaoSCImasiNC. RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON. WASHINGTON jEc 20 9 F F
HWAGRSZ 2011-039.GPJ 9/28/12
60
CL CH
50
X 40
W
0
Z_ A
>- 30
_H
U
F-
Q 20
J
10
0 -M --
CLL ML MH
•
0 20 40 60 80 100
LIQUID LIMIT (LL)
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION %MC LL PL PI %Fines
• CORE-02 S-4 2.0-2.5 (ML)Dark olive to gray,sandy SILT with 1.2%organic matter by dry weight 25 25 22 3 70.5
■ CORE-06 S-3 3.8-4.3 (OH)Dark brownish gray,organic SILT,contains 4.4%organic mattter. 58 52 37 15
A CORE-08 S-3 4.2-4.4 (OH)Dark grayish brown,organic SILT 114 108 74 34 85.5
O TP-2 B-1 2.0-2.5 (OH)Dark Brown,organic SILT 102 84 62 22 96.1
❑ TP-3 S-4 3.0-4.0 (OH)Dark gray,organic SILT 51 55 31 24 88.4
I I I I I I __j
FINAL GEOTECHNICAL ENGINEERING REPORT LIQUID LIMIT, PLASTIC LIMIT AND
�■■� RENTON AIRPORT TAXIWAY B REHABILITATION PLASTICITY INDEX OF SOILS
HmaosaENCES INC. RENTON MUNICIPAL AIRPORT METHOD ASTM D4318
RENTON, WASHINGTON
PROJECTNO.: 2011-039 FIGURE: B-9
HWAATTB 2011-039.GPJ 9/28/12
LABORATORY COMPACTION CHARACTERISTICS OF SOIL U01
CLIENT: Reid Middleton HWAGEOSCIENCES INC.
PROJECT: Renton Taxiway B SAMPLE ID: TP-1, B-1
PROJECT NO: 2011-039 Sampled By: SEG Tested By: JH
Date Sampled: 61612011 Date Received: 61612011 Date Tested: 611412011
MATERIAL TYPE OR DESCRIPTION:
Light grayish brown, organic SILT OH
MATERIAL SOURCE, SAMPLE LOCATION AND DEPTH:
TP-1, 2 ft b s
Designation:�X ASTM D 698 F�ASTM D 1557 Natural Moisture Content: 79.3 %
Method: F-]A F-1B �X C Oversize: 0 % retained on: 3/4 in.
Preparation:0 Dry �X Moist Rammer:[ Auto Manual Assumed S.G.: 2.4
Test Data
Dry Density (pcf) 62.2 63.7 64.1 61.5
Moisture Content (%) 24.6 26.8 29.3 31.4
70
Rock Corrected Curve
per ASTM D4718
Lab Proctor Curve
65 _._._._ 100%Saturation Line
s~
a
60
o '
0
55
50
20 22 24 26 28 30 32 34 36 38 40
Moisture Content(%)
Data Summary* Test Values At Other Oversize Percentages
Percent Oversize <5% 0.0% 5.0% 10.0% 15.0% 20.0% 25.0% 30.00o
Max. Dry Density(pcf)* 64.4 64.4 66.3 68.3 70.4 72.7 75.1 77.7
Optimum Moisture(%)* 28.5 28.5 27.1 25.8 24.4 23.0 21.6 20.3
values corrected or oversize material per ASTIVI D4718,using assumed Specific Gravity shown and oversize moisture content of 1%
Reviewed By: Steven Greene FIGURE B-10
This report applies only to the items tested,and may be reproduced in full,with written approval of HWA GEOSCIENCES INC.
LABORATORY COMPACTION CHARACTERISTICS OF SOIL U01
CLIENT: Reid Middleton HWAGEOSCIENCES INC.
PROJECT: Renton Taxiway B SAMPLE ID: TP-2, B-1
PROJECT NO: 2011-039 Sampled By: SEG Tested By: JH
Date Sampled: 61612011 Date Received: 61612011 Date Tested: 611312011
MATERIAL TYPE OR DESCRIPTION:
Dark brown, organic SILT OH
MATERIAL SOURCE, SAMPLE LOCATION AND DEPTH:
TP-2, 2 ft b s
Designation:F�ASTM D 698 �X ASTM D 1557 Natural Moisture Content: 134.2 %
Method: F]A F-]B �X C Oversize: 0 % retained on: 314 in.
Preparation: Dry �X Moist Rammer:�X Auto Manual Assumed S.G.: 2.4
Test Data
Dry Density (pcf) 1 55.2 58.9 59.8 1 58.2
Moisture Content(%) 55.9 57.7 59.0 62.0
70
_ Rock Corrected Curve
per ASTM D4718
Lab Proctor Curve
65 ....... 100%Saturation Line
a
60
77W-
� I
55
50
50 52 54 56 58 60 62 64 66 68 70
Moisture Content(%)
Data Summary* Test Values At Other Oversize Percentages
Percent Oversize <5% 0.0% 5.0% 10.0% 15.0% 20.0% 25.0% 30.0%
Max. Dry Density(pcf)* 59.9 59.9 61.8 63.7 65.8 68.1 70.5 73.1
Optimum Moisture(%)* 59.5 59.5 56.6 1 53.7 50.7 47.8 44.9 42.0
values corrected or oversize ma eria per D4718,using assumed Specific Gravity shown and oversize moisture content of 1%
Reviewed By: Steven Greene FIGURE B-11
This report applies only to the items tested,and may be reproduced in full,with written approval of HWA GEOSCIENCES INC.
LABORATORY COMPACTION CHARACTERISTICS OF SOIL ,Rt�Al
CLIENT: Reid Middleton HWAGECISCIENCES INC.
PROJECT: Renton Taxiway B SAMPLE ID: TP-3, B-1
PROJECT NO: 2011-039 Sampled By: SEG Tested By: JH
Date Sampled: 61612011 Date Received: 61612011 Date Tested: 611012011
MATERIAL TYPE OR DESCRIPTION:
Dark gray, silty SAND SM
MATERIAL SOURCE, SAMPLE LOCATION AND DEPTH:
TP-3, 2 ft b s
Designation:F-]ASTM D 698 ❑X ASTM D 1557 Natural Moisture Content: 25 %
Method: F-]A F-�B �X C Oversize: 0 % retained on: 314 in.
Preparation:0 Dry Moist Rammer:[ Auto Omanual Assumed S.G.: 2.4
Test Data
Dry Density (pcf) 101.9 1 108.6 106.3 1 102.3 110.4
Moisture Content (%) 10.7 13.0 18.6 20.7 15.4
120
_ Rock Corrected Curve
per ASTM D4718
115 Lab Proctor Curve
100%Saturation Line
110
U
a
105
o -
100 --
95
90
5 7 9 11 13 15 17 19 21 23 25
Moisture Content(%)
Data Summary* Test Values At Other Oversize Percentages
Percent Oversize <5% 0.0% 5.0% 10.0% 15.0% 20.0% 25.0% 30.0%
Max. Dry Density(pcf)* 110.5 110.5 112.0 113.5 115.0 116.6 118.3 119.9
Optimum Moisture(%)* 15.0 15.0 14.3 13.6 1 12.9 12.2 11.5 10.8
values corrected or oversize material per ASTIM D4718,using assumed Specific Gravity shown and oversize moisture content of 1%
Reviewed By: Steven Greene FIGURE B-12
This report applies only to the items tested,and may be reproduced in full,with written approval of HWA GEOSCIENCES INC.
CBR(California Bearing Ratio) OF LAB COMPACTED SOILS .R�/;�
(ASTM D 1883)
CLIENT: Reid Middleton HWAGEOSCIENCES INC.
PROJECT: Renton Taxiway B SAMPLE ID: TP-1, B-1
PROJECT NO: 2011-039-21 Sampled By: SEG Tested By: AAC/JH
Date Sampled: 61212011 Date Received: 61212011 Date Tested: 612012011
Material Description: Light olive brown, organic SILT(OH)
Sample Location: Test Pit TP-2 Sample B-1
Compaction Standard: �X D698 QO D1557 Condition: QX Soaked for 96 hrs OUnsoaked
Max. Dry Density: 64.4 pcf @ 28.5 % M.C. with 0 % scalped-off on the 3/4" sieve
Trial 1 Trial 2 Trial 3
Dry Density c 37.0
Percent Compaction 57.4
Moisture before Compaction % 118.2
Moisture after Compaction % 131.9
Percent Swell initial ht= 7" -3.5
Moisture, after Soaking (%) 122.7
Moisture To 1" after Soak % 109.2
CBR at 0.1" Penetration 0.4
CBR at 0.2" Penetration 0.4
CBR Value 0.4
12
10
8 ---
Q
y 6
L
4
2
L�0
0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 0.40 0.45 0.50
Displacement(in)
5.0
4.0
3.0
m
v 2.0
1.0
0.0
50 55 60 65 70 75 80 85 90 95 100
%Compaction
REVIEWED BY: Steven Greene FIGURE: B-13
CBR(California Bearing Ratio) OF LAB COMPACTED SOILS
(ASTM D 1883) Y
CLIENT: Reid Middleton HWAGEOSCIENCES INC.
PROJECT: Renton Taxiway B SAMPLE ID: TP-2, B-1
PROJECT NO: 2011-039-21 Sampled By: SEG Tested By: AAC/JH
Date Sampled: 61212011 Date Received: 61212011 Date Tested: 612012011
Material Description: Dark brown, organic SILT(OH)
Sample Location: Test Pit TP-2 Sample B-1
Compaction Standard: F_�D698 ❑X D1557 Condition: ❑X Soaked for 96 hrs �Unsoaked
Max. Dry Density: 59.9 pcf @ 59.5 % M.C. with 0 % scalped-off on the 3/4" sieve
Trial 1 Trial 2 Trial 3
Dry Density c 39.3
Percent Compaction 65.6
Moisture before Compaction % 122.7
Moisture after Compaction % 111.3
Percent Swell initial ht= 7") -5.9
Moisture, after Soaking % 109.3
Moisture To 1" after Soak % 100.2
CBR at 0.1" Penetration 0.5
CBR at 0.2" Penetration 0.6
CBR Value 0.6
18
16
14
12
0 10
N
N
8
6
4
2
0
0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 0.40 0.45 0.50
Displacement(in)
5.0
4.0
3.0
in
U 2.0
1.0
0.0
50 55 60 65 70 75 80 85 90 95 100
%Compaction
REVIEWED BY: Steven Greene FIGURE: B-14
CBR(California Bearing Ratio) OF LAB COMPACTED SOILS ffir
V
(ASTM D 1883)
CLIENT: Reid Middleton HWAGEOSCI ENCES INC.
PROJECT: Renton Taxiway B SAMPLE ID: TP-3, B-1
PROJECT NO: 2011-039-21 Sampled By: SEG Tested By: AAC/JH
Date Sampled: 61212011 Date Received: 61212011 Date Tested: 612012011
Material Description: Dark olive gray, SILT with sand(ML)
Sample Location: Test Pit TP-3 Sample B-1
Compaction Standard: F-1D698 ❑X D1557 Condition: ❑X Soaked for 96 hrs ❑Unsoaked
Max. Dry Density: 110.5 pcf @ 15 % M.C. with 0 % scalped-off on the 3/4" sieve
Trial 1 Trial 2 Trial 3
Dry Density c 94.5 112.9 #N/A
Percent Compaction 85.5 102.1 #N/A
Moisture before Compaction % 25.5 15.4 #DIV/0!
Moisture after Compaction % 25.2 15.0 #DIV/0!
Percent Swell (initial ht = 7") -0.1 0.5 0.0
Moisture, after Soaking (%) 27.3 17.0 #DIV/0!
Moisture Top 1" after Soak % 25.5 19.4 #DIV/0!
CBR at 0.1" Penetration 0.9 51.4 #DIV/0!
CBR at 0.2" Penetration 1.2 53.8 #DIV/0!
CBR Value 1.2 53.8 #DIV/0!
1600
-_ ♦-85.5
1400 -�102.1
1200
1000
N
a.
y 800
d
in
600
400
200 ---
0
0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 0.40 0.45 0.50
Displacement(in)
- 60
-- 50
40
- m 30
U
20
10
0
80 85 90 95 100 105
%Compaction
REVIEWED BY: Steven Greene FIGURE: B-15
Bulk Density of Soil Chunk Samples
Renton Airport Taxiway B , HWA GEOSCIENCES INC.
Exploration Sample No. Depth Length Diameter Volume Tare Wet+Tare Bulk Density Tare W+T D+T MC Dry Densitv
TP-1 B-1 0.9 6 2.4 0.0157 248 849.83 84.6 8.32 191.5 110.51 79.3% 47.2
TP-2 B-1 2 6 2.4 0.0157 248 924.15 95.1 8.13 183.73 83.11 134.2% 40.6
TP-3 B-1 1.5 6 2.4 0.0157 248 973.92 102.1 8.48 198.17 160.22 25.0% 81.6
HWA Project No. 2011-039 FIGURE B-16
APPENDIX C
CORE PHOTOGRAPHS
HWVAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 2, 2011 Sampled by: SEG
Core Bit Used: 8-inch diameter
Sample Location: Northern Taxiway Connector(see Figure 2)
_ Core Designation: Core-1
-� 2 o l 1 _ o
lore -
PRI
Total Wearing Surface Depth: 2 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
2.0 Hot Mix Asphalt(HMA) 2 Fair
5 CSTC/CSBC - Dense
Gravel with sand and _ Medium dense to dense
Cobbles
Remarks:
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 2, 2011 Sampled by: SEG
Core Bit Used: 8-inch diameter
Sample Location: North end of Taxiway B (See Figure 2)
Core Designation: Core-2
03g
" (ore-
Total Wearing Surface Depth: 4.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
4.5 HMA 4.5 Fair to good
5.0 CSTC/CSBC - Dense
- Sand with gravel - Medium dense to dense
Remarks:
i
U
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 2, 2011 Sampled by: SEG
Core Bit Used: 8-inch diameter
Sample Location: North end of Taxiway B (See Figure 2)
Core Designation: Core-3
2 o _ o39
� i
Core - 3
Total Wearing Surface Depth: 2.25 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
2.25 HMA 2.25 Poor to fair
1.5 CSBC - Dense
2.25 Sandy silt - Medium stiff
Remarks: The subgrade becomes sand to silty sand with depth
ULWAV
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 2 and June 8, 2011 Sampled by: SEG/DRC
Core Bit Used: 8-inch diameter
Sample Location: North end of Taxiway B (See Figure 2)
Core Designation: Core-4
2011 _ 039
Total Wearing Surface Depth: 1.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
1.5 HMA 1.5 Poor
1.4 CSBC - Dense
1.75 HMA 1.75 Good
- Gravel - Loose
Remarks: 1.4 inches of crushed gravel between HMA layers
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 2, 2011 Sampled by: SEG
Core Bit Used: 8-inch diameter
Sample Location: North central portion of Taxiway B (See Figure 2)
Core Designation: Core-5
2oII . 03 �
Total Wearing Surface Depth: 2 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
2 HMA 2 Good
6 CSBC - Dense
- Sand with silt and gravel - Medium dense
Remarks: With depth subgrade appears to consist of dredge spoils.
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 7, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Central portion of Taxiway B (See Figure 2)
Core Designation: Core-6
is
4=
Zail- 039
�oM-G
Total Wearing Surface Depth: 14.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
8.5 HMA 3, 5.5 Poor to good
6 PCC 6 Fair to good
- Sand with gravel and cobbles - Loose
Remarks: The bottom 5.5 inches of HMA is of lower quality(ATB?)
No crushed gravel base course was encountered.
00 1 1 1 MA 'I
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B—Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 7, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: South end of Taxiway B (See Figure 2)
Core Designation: Core-7
Core J
Total Wearing Surface Depth: 13.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
8.5 HMA 3.5, 5 Very poor
5 PCC 5 Very poor
_ Sand with gravel, cobbles
and silt - Loose
Remarks: The bottom 5 inches of HMA is of lower quality(ATB?) and disintegrated
coring and therefore does not appear in the above photo.
No crushed gravel base course was encountered.
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 7, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: South End of Taxiway B (See Figure 2)
Core Designation: Core-8
F
Zola _039
Core_ B
Total Wearing Surface Depth: 12 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
5.5 HMA 2.5, 3 Good
6.5 PCC 6.5 Good
Sand with gravel, cobbles - Loose
and silt
Remarks: A non-woven fabric layer is located between the two lifts of HMA
No crushed gravel base course was encountered.
rip
U =1
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 7, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: South end of Taxiway B (See Figure 2)
Core Designation: Core-9
2oli- 039
are _
Total Wearing Surface Depth: 10 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
10 HMA 2.5, 4.25, 3.25 Good to poor
Sand with gravel, cobbles - Loose
and silt
Remarks: A non-woven fabric layer is located between the first two lifts of HMA
The lower lift of HMA is of lower quality (ATB?)
No crushed gravel base course was encountered.
U
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 6, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Infield apron South end of Taxiway B (See Figure 2)
Core Designation: Core-10
i --
a
zo ►i - o39
Core o
y
Total Wearing Surface Depth: 2.25 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
2.25 HMA 2.25 Good
- Gravel with sand - Dense to very dense
Remarks: No crushed gravel base course was encountered.
ff,LWA I
Mu
HWAGEOSCI ENCES INC.
Client: Reid Middleton
Project: Taxiway B—Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 7, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: South end of Taxiway B (See Figure 2)
Core Designation: Core-11
2on.o39
�oce_\1
Total Wearing Surface Depth: 16.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
8.5 HMA 2.5, 2.5, 3.5 Good to fair
8 PCC 8 Fair to good
- Sand with gravel and cobbles - Loose
Remarks: A non-woven fabric layer is located between the bottom lift of HMA and
PCC. The lower lift of HMA is of lower quality (ATB?)
No crushed gravel base course was encountered.
U �
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B—Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 6, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Southern Taxiway Connector(See Figure 2)
Core Designation: Core-12
f -
2011-039
Cope-IZ
Total Wearing Surface Depth: 13.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
7.5 HMA 3.5, 2 , 2 Good
6 PCC 6 Fair
- Sand with gravel and cobbles - Loose
Remarks: No crushed gravel base course was encountered.
II I AAR it
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 6, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Southern Taxiway Connector(See Figure 2)
Core Designation: Core-13
low
.J
31
•
• .Mtn .. � i
• 3
2-011_ 0
- 13
_1
Total Wearing Surface Depth: 9 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
3 HMA 3 Fair to poor
6 PCC 6 Fair
- Sand with gravel and cobbles - Loose
Remarks: A non-woven fabric layer is located between the bottom lift of HMA and
PCC. No crushed gravel base course was encountered.
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B—Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 6, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Southern Taxiway Connector(See Figure 2)
Core Designation: Core-14
2011_ o3q
Total Wearing Surface Depth: 10.75 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
4.75 HMA 4.75 Fair to good
6 PCC 6 Good
- Sand with gravel and cobbles - Loose
Remarks: No crushed gravel base course was encountered.
u i=,,
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B—Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 6, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Southern Taxiway Connector(See Figure 2)
Core Designation: Core-15
�cN
ri.r}
_ 2oli_ 039
.tom
Total Wearing Surface Depth: 12 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
6 HMA 4, 2 Good to poor
6 PCC 6 Good
4.5 CSBC - Loose
- Sand with silt and gravel - Loose to medium dense
Remarks: The lower lift of HMA is of lower quality(ATB?).
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B—Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 6, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Southern Taxiway Connector(See Figure 2)
Core Designation: Core-16
s- -
r
dire 16
Total Wearing Surface Depth: 10.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
3.5 HMA 1.5, 2 Fair to poor
7 PCC 7 Poor
- Sand with silt and gravel - Loose
Remarks: A non-woven fabric layer is located between the lowest HMA and the PCC
layers. The PCC layer is cracked through and sealed with asphalt sealant
No crushed gravel base course was encountered.
ULWA I
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: July 11, 2012 Sampled by: DRC
Core Bit Used: 12-inch diameter
Sample Location: South end of Taxiway B (See Figure 2)
Core Designation: Core-17
2011-03q r .
1-7
2011-03� .
G,Qf ti�-
Total Wearing Surface Depth: 15 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
7 Hot Mix Asphalt(HMA) 2.5, 4.5 Good to Fair
8 PCC 8 Fair
- Gravel with sand and cobbles - Medium dense
Remarks: There is a 0.75 inch deep and 1.25 inch wide asphalt seal in the middle of
the core covering a crack in the upper HMA layer(see Photo above).
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: July 11, 2012 Sampled by: DRC
Core Bit Used: 12-inch diameter
Sample Location: South end of Taxiway B (See Figure 2)
Core Designation: Core-18
► 2oit_o3q
Total Wearing Surface Depth: 12.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
6.5 HMA 2.75, 3.75 Fair to good
6 PCC 6 Fair
- Gravel with sand and cobbles - Medium dense
Remarks:
Ek I JAR,'$
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: July 11, 2012 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Southern Taxiway Connector(See Figure 2)
Core Designation: Core-19
k,
9
s
1
t y, ^
�►e
2olt_o3q
Total Wearing Surface Depth: 19.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
12.5 HMA 3, 2.5, 3, 4 Fair to good
7 PCC 7 Good
- Gravel with sand and cobbles - Medium dense
Remarks: There is no bond between the 2nd and 3rd layers of HMA.
There is no bond between the 3rd and 4th layers of HMA.
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: July 11, 2012 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: South end of Taxiway B (See Figure 2)
Core Designation: Core-20
2DII
— p3 a1
C Z.O
i*
,xY
Costs-20 .
Total Wearing Surface Depth: 13.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
6 HMA 3.5, 2.5 Poor
7.5 PCC 7.5 Fair
- Gravel with sand and cobbles - Medium Dense
Remarks: There is a 0.5 inch deep and 0.75 inch wide asphalt seal in the middle of the
core covering a crack in the upper HMA layer(see Photo above).
Appendix B
City of Renton Sensitive Areas
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I
Technical Information Report(TIR)
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Printed on May 21, 2009 Flood Hazard Police Department
This tlocu—ni a graphic representation,not p mabon
b survey accuracy,ata is Dasetl b,Ne p at i tende f,,
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Renton City Limits
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Printed on May 20 2009 S, _
Data Source:Public Works,Utilities Systems,Technical Services; high _
Washington State Department of Natural Resources,Geology and Earth Resources Division __- Fire Stations
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G. Zimmerman,Administrator 3. °' Hazard Condition Critical Infrastructure
ittti � lli
ls,j
Technical Services
R. MacOnie, D. Visneski This documenth agnphic repmsenlation,not guaraNeed High Seismic Severity Police Department
b survey axur,oy a,d o based on this best information
vail,ble as of the dale shown This map is intended for
Printed on May 21, 2009 city display puryoasa only _
Fire Stations
Data Source: Public Works, Utilities Systems,Technical Services
r City ofK'r7 ��(�-���■ - Valley-e Centar
Schools
Appendix C
Water Quality Calculations
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I
Technical Information Report (TIR) ' ' '
King County Runoff Time Series Program
Version 6,00
All files will be read/written in the Working Directory
Working Directory:C:Nkc_swdm`,output
-----M-- KCRTS Command
-------------
CREATE a new Time Series
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series SBASIN.tsf
Regional Scale Factor 1.00
Data Type Reduced
Creating 15-minute Time Series File
Loading Time Series File:C:\KC_SVDM\KC DATA`STE115R'.rnf 8
Impervious 1.96 acres Scaling Yr: 8
Total Area 1.96 acres
Peak Discharge: 2.31 CFS at 6:30 on .Ian 9 in Year 8
Storing Time Series File:SBASIN.tsf 8
Time Series Computed
--------------------------------------
KCRTS Command
Enter the Analysis TOOLS Nodule
Analysis Tools Command
Compute PEAKS and Flow Frequencies
Loading Stage/Discharge curve:sbasin.tsf
Flow Frequency Analysis
------------------------------------------------
Time Series File:sbasin.tsf
Project Location:Sea-Tac
Project location:Sea-Tac
---Annual Peak Flou Rates--- -----Flow Frequency Analysis----._-
Flow Rate Rank Time of Peak - - Beaks - - Rank Return Prob
(CFS) (CFS) Period
0.933 6 8/27/O1 18:00 2,31 1 100.00 0,990
0,652 8 9/17/02 17:45 1 ,77 2 25.00 0,960
1.77 2 12/08/02 17:16 1, 27 3 10.00 0,900
0.7S1 7 8/23/04 14:30 1,04 4 S.OD 0,800
0,989 S 10/28/04 16:00 0,989 55 3.00 0.667
1.04 4 10/27/OS 10:45 0.933' 6 2.00 O.SOO
1.27 3 10/2S/O6 22.4E 0.751 7 1,30 0.231
2.31 1 1/09/08 6:30 0.652 8 1.10 0,091
South Bio-filtration Basin Area (See Figure 4-1) — Sub-basin C
Water Quality flow rate= 60% of 2-year storm
0.933 cfs * 0.6 = 0.56 cfs
KCRTS Command
CREATE a nee Time Series
----------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series NBASIN.tsf
Regional Scale Factor 1,00
Data Type Reduced
:renting 15-xinute Time Series File
Loading Time Series File:C:\KC�_SVDM\KC�_DATA\STE115R.rnf
Impervious 0.93 acres Scaling Yr. 8
-------- -----Total Area 0,93 acres
Peak Discharge: 1.10 CFS at 6:30 on Jan 9 in Year 8
Storing Time Series File:NBASIX,tsf 8
Time Series Computed
----- -------- ---------- -------
KCRTS Command
Enter the Analysis TOOLS Module
--------—-——-----------
---------------------------------------------------- --------
Analysis Tools Command
-------—-——-------
Compute PEAKS and Flow Frequencies
----------————----------------
Loading Stage/Discharge curve:nbasin.tsf
Flow Frequency Analysis
Time Series File:nbasin.tsf
Project Location:Sea-Tac
Project Location:Sea-Tac
--Annual Peak Flow Rates— -----Flow Frequency Analysis-----
Flow Rate Rank Time of Peak Peaks Rank Return Prob
(CFS) (CFS) Period
0,443 6 8/27/01 18:00 1.10 1 100.00 0-990
0,309 8 9/17/02 17:45 0.638 2 25.00 0-960
0,838 2 12/06/02 17:15 0,602 3 10.00 0.900
0,356 7 6/23/04 14:30 0,495 4 5,00 0,800
0,469 5 10/28/04 16,00 0.469 5 3,00 0,667
0,496 4 10/27/06 10:45 0,443 6 2,00 0,500
0,602 3 10/25/06 22:45 0,366 7 IAO 0.231
1.10 1 1/09/08 6:30 0.309 8 1.10 0-091
North Bio-filtration Basin Area (See Figure 4-1)— Sub-basin D
Water Quality flow rate= 60% of 2-year storm
0.443 cfs * 0.6 = 0.27 efs
BIOFILTRATION CALCULATION
Based on KCSWDM,pg 6-40
South WQ Basin (Sub-basin C)
Solve for bottom width(b)
Q=0.56 cfs (KCRTS) - 1.96 ac impervious y 0.23
y=0.17 (mowed frequently) 0.33 (infrequent mowing) n 0.2
n=0.2 s= slope z= side slope Q 0.56
b=Q*n/1.49*y^1.67*s^0.5 s 0.005
b (ft) 12.4 Use 20-ft width to meet 5:1 length to width ratio Z 4
Solve for flow Velocity
Z= side slope
A=cross-sectional area A(ft^2) 3.1
v(ft/s) 0.18
Solve swale length
L(ft)= 540 * v 98.9 Min. 100'
Meet criteria for high flow
North WQ Basin (Sub-basin D)
y 0.24
Q=0.27 cfs (KCRTS) - 0.93 ac impervious n 0.2
b (ft) 5.6 Use 20-ft width to meet 5:1 length to width ratio Q 0.27
A(ft-2) 1.6 s 0.005
v(ft/s) 0.17 Z 4
L (ft) 93.2 Min. 100'
Narrow Filter Strip Calculation
Per KCSWDM Section 6, pg 6-66
Flowpath length= 12.5 feet(West side of crown section)
Average slope= 12%
Required Filter Strip Length based on Figure 6.3.5.A attached.
=Approx. 8 feet(interpolation)
Approximately 35 feet of vegetation provided.
6.3.5 NARROW AREA FILTER STRIPS
FIGURE 6.3.5.A FILTER STRIP LENGTHS FOR NARROW RIGHT-OF-WAY
20.0
15.0
w
w Flowpath
= 30 feet
wo
10:0 _
a, 20 feet
L
L
10 et
G. 5.0 E
i
j
t i
a
0.0
0% 5% 10% 1 15% 20%
Filter Strip Slope
Note: minimum allowable filter strip length is 4 feet
6.3.5.2 DESIGN CRITERIA
Required and recommended design criteria for narrow area filter strips are the same as specified for basic
filter strips. Note that for roadway applications, gravel spreaders must meet the specification for shoulder
ballast given in Section 9-03.9(2)of the current Standard Specifications for Road, Bridge and Municipal
Construction, 1994compacted to 90 percent standard proctor.
2009 Surface Water Design Manual 6-67 1/9/2009
FLOW SPLITTER CALCULATIONS
PROJECT: Renton Municipal Airport,Taxiway B,Phase I Calculated by: BTS
PROJ NO.: 23-2010-007 Checked by:
DATE: 8/23/2012 Date Checked:
FILE: H\D0023Ap\I0\007 Renton TV B&Signage\Desip\Drainne\[Flow Splitter—Phase LrJmfbw Splimr
South Biofiltration Swale(Sub-basin C)
Pipe Capacity
Manning Pipe Capacity
No. Diameter Slope Length Capacity Used
(inch) (%) (feet) (cfs) (%)
0.014 8 0.10 10 0.35 158
0.014 12 0.10 10 1.05 54
Head determined by sharp-crested weir equation 0.463 s
Q = D 3 S r�
Known: Q1= 0.56 cfs n
CD= 0.6
IEout[et= 20.1 ft
Length Head Head 2 3
(ft) (ft) (in) QK�, = C, 2gLH
1 0.3122 3.7466 F
4 0.1239 1.4868
6 0.0946 1.1347
Conclusion: A 12-inch diameter pipe shall be utilized for the outlet to the biofiltration swale.
The top of the 1-ft weir shall be placed at 20.42(20.1+0.31).
North Biofiltration Swale(Sub-basin D)
Pipe Capacity
Manning Pipe Capacity
No. Diameter Slope Length Capacity Used
(inch) (%) (feet) (cfs) (%)
0.014 8 0.10 10 0.35 76
0.014 12 0.10 10 1.05 26 F
Head determined by sharp-crested weir equation 0.463 $
Q = D 3 S II
Known: Q2= 0.27 cfs n
CD= 0.6
IEoutlet= 19.9 ft
Length Head Head 2 3
(ft) (ft) (in) Qwg = 3 CD V2gLH 2
1 0.1920 2.3037
4 0.0762 0.9142
6 0.0581 0.6977
Conclusion: A 12-inch diameter pipe shall be utilized for the outlet to the biofiltration swale.
The top of the 1-ft weir shall be placed at 20.09(19.9+0.19).
Page 1 of 1
Appendix D
Conveyance System Calculations
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I
Technical Information Report (TIR) ` ' ' " ` '
PROD: Renton Municipal Airport,Taxiway B PIPE SIZING
WO: 23-2012-2012 (Runoff by Rational Method) Calculated by: U
DATE: 6/20/2012 (Pipe Capacity by Manning's Eqn.) Checked by:
FILE: H.\DOC\23A,\10\007 Ra -TW B& S g„aye\De g,.\D ge\[20120629_P pP S, g..sJR „o„Coe,. ,e„« Date Checked:
Storm: Renton 25 Year
c 0. 9 1 rrper vi ous a 2.66 (see KCSWDM pg3-13)
c- 0. 25 Lawn ", 0.65 (see KCSWDM pg 3-13)
r 3.4 (see KCSWDM pg 3 24-Hour Isopluvials
Inc. Inc. Inc. Time of Rain Pipe % Veloc Flow
Area(sf) Area(so Area Runoff Sum Cone Intens Runoff n Diam Slope Length Capac Capac Full Time Remarks
From To (Imperv) (Perv) (ac) Coef. A*C A*C (min) (in/hr) (cfs) Value (inch) (%) (feet) (cfs) Used (ft/sec) (min)
Sub Basin E
No analysis provided.
Sub Basin D
LOT B 6 260 1 0 0.60 0.90 0.54 0.54 10.00 2.02 1.09 0.014 12 0.10 550 1.05 104 1.33 6.88
CB26 CB25 0 0 0.00 0.58 0.00 0.54 16.88 1.44 0.78 0.014 12 0.83 108 3.01 26 3.84 0.47
CB27 CB25 7626 0 0.18 0.90 0.16 0.16 10.00 2.02 0.32 0.014 12 0.34 88 1.93 17 2.46 0.60
CB25 CB24 7129 0 0.16 0.90 0.15 0.84 17.35 1.42 1.19 0.014 12 0.50 100 2.34 51 2.98 0.56
7B2 CB23 0 0 0.00 0.58 0.00 0.84 24.23 1.14 0.96 0.014 12 0.53 19 2.41 40 3.07 0.10
CB23 CB22 0 0 0.00 0.58 0.00 0.84 24.70 1.12 0.95 0.014 12 0.53 19 2.41 39 3.07 0.10
CB22 CB21 0 0 0.00 0.58 0.00 0.84 24.80 1.12 0.95 0.014 12 0.41 110 2.12 45 2.70 0.68
CB2 CB20 61992 85598 3.39 0.52 177 2.61 25.48 1.10 2.88 0.014 12 0.55 19 2.45 117 3.12 0.10
CB20 CB 19 0 0 0.00 0.58 0.00 2.61 25.59 1.10 2.88 0.014 12 0.53 47 2.41 119 3.07 0.26
CB 19 E7 0 0 0.00 0.58 0.00 2.62 25.84 1.09 2.86 0.014 12 0.50 48 2.34 122 2.98 0.27
E7 E6 0 0 0.00 0.58 0.00 2.62 25.84 1.09 2.86 0.014 12 0.10 42 1.05 273 1.33 0.53 Existing
E6 OUT 0 0 0.00 0.58 0.00 2.62 26.37 1.08 2.82 0.014 12 0.50 114 2.34 121 2.98 0.64 Existing
Sub Basin C
C139 CB 10 36344 0 0.83 0.90 0.75 0.75 10.00 2.02 1.52 0.014 12 0.40 85 2.09 73 2.66 0.53
CB10 CB11 48916 0 1.12 0.90 1.01 1.76 M53 1.96 3.45 0.014 12 0.34 104 L93 179 2.46 0.71
C1311 CB12 0 0 0.00 0.25 0.00 1.76 11.24 1.88 3.31 0.014 12 0.30 49 1.81 182 2.31 0.35
CB12 CB13 0 0 0.00 0.58 1 0.00 1.76 11.59 1.84 3.24 0.014 12 0.50 8 2.34 139 2.98 0.04
Page 1 of 2
PROJ: Renton Municipal Airport,Taxiway B PIPE SIZING
WO: 23-2012-2012 (Runoff by Rational Method) Calculated by: I J
DATE: 6/20/2012 (Pipe Capacity by Manning's Eqn.) Checked by:
FILE: H:\DOC\23A,\10\007 P--TW B& Sig age\Dez gn\D a,.age\[20120629_P, e S= g.=SJR „oF C., 'o e„, Dale Checked:
Storm: Renton 25 Year
c 0. 9 1 rrper v i ous a' 2.66 (see KCSWDM pg 3-13)
c- 0. 25 Lawn 0.65 (see KCSWDM pg 3-13)
r 3.4 (see KCSWDM pg 3 24-Hour Isopluvials
Inc. Inc. Inc. Time of Rain Pipe % Veloc Flow
Area(so Area(so Area Runoff Sum Cone Intens Runoff n Diam Slope Length Capac Capac Full Time Remarks
From To (Imperv) (Perv) (ac) Coef. A*C A*C (min) (in/hr) (cfs) Value (inch) (%) (feet) (cfs) Used (ft/sec) (rain)
B 3 B 67 7 6 83359 7 0. 1.88 3.64 11.64 1.83 6.68 0.014 12 0.34 116 1.93 346 2.46 0.79
CB CB 6 0 0 0.00 0.58 0.00 3.64 12.42 1.76 6.40 0.014 12 0.33 30 1.90 337 2.42 0.21
CB 6 C1317 0 0 0.00 0.58 0.00 3.64 13.21 1.69 6.15 0.014 12 0.32 124 1.87 329 2.38 0.87
C 7 5055 38760 I. 6 0.51 0.74 4.38 14.08 1.62 7.10 0.014 12 0.32 95 1.87 380 2.38 0.66 Existing
CB 8 0 0 0.00 0.58 0.00 4.38 14.74 1.57 6.89 0.014 12 0.01 43.0 0.33 2083 0.42 1.70 Existing
E E 0 0 0.00 0.58 0.00 4.38 16.44 1.47 6.42 0.014 12 0.50 40.0 2.34 274 2.98 0.22 Existing
E E 0 0 0.00 0.58 0.00 4.38 16.67 1.45 6.36 0.014 12 0.20 42.0 1.48 430 1.88 0.37 Existing
E2 joul, 0 0 0.00 0.58 0.00 4.38 17.04 1.43 6.27 0.014 12 1.30 68.0 3.77 166 4.80 0.24 Existing
Sub Basin B
C134 C135 674 513 0.03 0.62 0.02 0.01 10.00 2.02 0.02 0.014 12 0.34 99.0 1.93 1 2.46 0.67
C135 C136 2528 5510 0.18 0.45 0.08 0.09 10.67 1.94 0.18 0.014 12 0.39 82.0 2.07 9 2.63 0.52
C136 C137 26586 41935 1.57 0.50 0.79 0.88 11.19 1.88 1.66 0.014 12 0.33 281.0 1.90 88 2.42 1.94
C137 C138 32193 27660 1.37 0.60 0.82 1.71 13.13 L70 2.90 0.014 12 1.80 95.0 4.44 65 5.65 0.28
C138 El 3329 11580 0.34 0.40 0.14 1.84 13.41 1,67 3.08 0.014 12 1.80 155.0 4.44 69 5.65 0.46
El OUP 0 0 0.00 0.58 0.00 1.84 13.86 1.64 3.02 0.014 12 1.10 127.0 3.47 87 4.42 0.48 Existing
Sub Basin A
No analysis provided
Page 2 of 2
Runoff Coefficients for Rational Method
Source:King County Surface Water Design Manual 2009,Table 3.2.1.A
General Land Covers
Land Cover C
Dense forest 0.10
Light forest 0.15
Pasture 0.20
Lawns 0.25
Playgrounds 0.30
Gravel areas 0.80
Pavement and roofs 0.90
Open water(pond,lakes,wetlands) 1.00
Single Family Residential Areas
Land Cover Density C
0.20 DU/GA(1 unit per 5 ac.) 0.17
0.40 DU/GA(1 unit per 2.5 ac.) 0.20
0.80 DU/GA(1 unit per 1.25 ac.) 0.27
1.00 DU/GA 0.30
1.50 DU/GA 0.33
2.00 DU/GA 0.36
2.50 DU/GA 0.39
3.00 DU/GA 0.42
3.50 DU/GA 0.45
4.00 DU/GA 0.48
4.50 DU/GA 0.51
5.00 DU/GA 0.54
5.50 DU/GA 0.57
6.00 DU/GA 0.60
Source: King County Surface Water Design Manual 2009,Table 3.2.1.13
Coefficients for the Rational Method
Design Storm aR bR
2 Year 1.58 0.58
5 Year 2.33 0.63
10 Year 2.44 0.64
25 Year 2.66 0.65
50 Year 2.75 0.65
100 Year 2.61 0.63
SECTION 3.2 RUNOFF COMPUTATION AND ANALYSIS METHODS
FIGURE 3.2.1.A 2-YEAR 24-HOUR ISOPLUVIALS
SNON_OMISH COUNTY
KING COUNTY
I r.Li
7 1 N N
2. l i .7
.I� r ry 0
fiia°y
suuru■
T/I/ \` f
I
1
-( J ,1AUBURX
-- f
[YM( Yt \\
uo _
—
en,tlro+,
1r
I
�• ...lyl _ _ _KING COUNTY
0 n PIERCE COUNTY
N
WESTERN
KING COUNTY {� 3.5
2-Year 24-Hour
Precipitation ti
in Inches Q Miles r.,
1/9/2009 2009 Surface Water Design Manual
3-14
I
3.2.1 RATIONAL METHOD
FIGURE 3.2.1.13 10-YEAR 24-HOUR ISOPLUVIALS 7711
2S ,�,/ �SI -Nlll Ir ;a Ie '3 1•
!NOC4.0
UNTY
S10 ...... UNTY
• tl �4 N.J.
?,8 /r lip
1 b�
f�0 1 •f"
N.
ttfYY1
3 r IT
-t--
_J' L.
0
l7� 1J.
W.M. •' / 'J
.MR )
N
Y}I 1 e P
{..
,.. !,Y.
ll.Y
a
41 1St �:
., •YW.Y � /
AY
lI. Y• I q.
*•r
� LO -
• j'KING COUNTY
PIERCE COUNTY
WESTERN
KING COUNTY �,Y r`
,.Y.a.� 4.5
N 1 __
1
10-Year 24-Hour �'b* 4.0
Precipitation rbry'b N.-�
in Inches Miles `� �°2009 Surface Water Design Manual 1/9/2009
3-15
' SECTION 3.2 RUNOFF COMPUTATION AND ANALYSIS METHODS
FIGURE 3.2.1.0 25-YEAR 24-HOUR ISOPLUVIALS
_!N HOMISN COUNTY y VINO COUNTY
0 -
[.uN Fa ^ I 1
4
o
1
a
b t'.
i
5.0
' 1 n
� 1
wu[o
•Y � i ou
Cb
M
_NINo eouwrr
�. PIERCE COUNTY
' WESTERN a
KING COUNTY (\ s.s
d
25-Year 24-Hour `' ` 4.5
Precipitation
in Inches Miles
1/9/2009 2009 Surface Water Design Manual
3-16
3.2.1 RATIONAL METHOD
FIGURE 3.2.1.D 100-YEAR 24-HOUR ISOPLUVIALS
3p i N O COUNTY
3? ..0.[li� N COUNTY
4 ,.
4,
11 • �
UA
� 45
J ' 6
'K O COUNTY-
PIE CE COUNTY
WESTERN
6.5
1
KING COUNTY aC4 .�, ... ... 6.0
N b -- 5.5
100-Year 24-Hour
Precipitation
in Inches z """"es '
E—
by
2009 Surface Water Design Manual 3-17 1/9/2009 ,
i
6 C Stl�$AsnvOIL
_ 13Mi1
WAY 34-16 32.1113 sF rtv 67,91(. Sr im#a RUNWAY 34-16
ZT,bi0 s� Lt�W 83,3x9 Sf LAWN 611 U SR IMP
— — — 85,5g8 SF I.A%W
26,586 sF IM - - -- _ ____ _-_ -__`
I Q
- ----- N
El
�„ 120,oss SP Irlf G
rw Si k^VAH f O
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on OR
am
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so -�4---- ----s cd 7 Ca Ica
Q0 AP
10.
I
CB Z - I
y t9 y96st ss ' °
,� 1 � s51 c ..„.
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513 sR /NP ! ib i I i I i i ! ► 1 J __D
11 ! I I I I
3,1Z9 SF i fNl i i 4dt�4/L SIR' VVft 1 ib 7496
, 2s2a 1f + tb tb if
' I I
I ALL
761&i Sir IMP
'` --- 7,12q SP /MFFP
J .
1110
I
SCALE IN FEET
80 0 60 120
Tributary Area/Collection Figure 1
72 1 Renton Airport
EMA%&*91GD1
&10 741-M
THICKNESS DESIGN FOR DUCTILE IRON PIPE
PROJECT: Renton Municipal Airport,Taxiway B,Phase I Calculated by: BTS
PROJ NO.: 23-2010-007 Checked by:
DATE: 9/19/2012 Date Checked:
FILE: HAD0C\23Ap\M007 Renton TW B&Signage\Design\Drainage\[Pipe Loading—Phase Lx1sx-jThickness Calcs
Define: Determine the required pipe thickness to withstand truck loads at shallow depths. There are 4 scenarios where
DIP possess<3 ft of cover: 8 in @ 1 ft, 12 in @ 1.5 ft,6 in @ 2 ft,and 12 in @ 2 ft. The methods set forth by
ANSUAWWA C I50/A21.50-02(Thickness Design of Ductile-Iron Pipe)shall be utilized in the design of the
appropriate pipe thickness.
Known: Type 4 pipe laying conditions per Table 2,ANSUAWWA C I 50/A21.50-02
Design Vehicle(ARFF Truck)= 82,000 pounds
Percent of Load= 95 %
No. of Wheels= 4
P(truck load)= 19475 pounds
w= 120 lb/ft'
a= 144 in2/ft2
R= 1 Road Reduction Factor for cover<4 ft and pipe diameter between 3-12 in
(Table 4,ANSUAWWA C 150/A21.50-02)
F= 1.5 Impact factor(ASCE Manual No. 37)
Solve: Step 1—Design for internal pressure
For ordinary conditions, storm drain pipes shall be sized on the assumption that they will flow full,or
practically full,under the design discharge,but will not be placed under pressure head. Therefore,internal
pressure will be assumed to be 0 psi for the design of the storm system.
Step 2—Design for trench load
a.)Earth Load
Table 1: Earth Load
Depth,H Earth Pressure wH
(ft) (psi) P e =
1.0 0.8333 a
1.5 1.2500
2.0 1.6667
b.)Truck Load
2 AZ+H2+1.52 2 1.5AH 1 + 1
C=1--sin_, H +— l
rr (A2+HZ)0.52+HZ) �( AZ+H2+1.52 L +HZ 1.52+HZ J
Table 2: Surface Load Factor
Depth,H Nominal Pipe Pipe Outside Surface Load
Diameter Radius Factor,C
(ft) (in) (ft)
1.0 8 0.38 0.4207
1.5 12 0.55 0.3770
2.0 6 0.29 0.1423
2.0 12 0.55 0.2624
Page 1 of 4
Pt = RF, CP
bD
Table 3: Truck Load
Depth,H Nominal Pipe OD of Pipe,D Effective Length of Truck Load,P,
Diameter Pipe,b
(ft) (in) (ft) (in) (psi)
1.0 8 9.05 36.00 37.72
1.5 12 13.20 36.00 23.17
2.0 6 6.90 36.00 16.74
2.0 12 13.20 36.00 16.13
c.)Trench Load
Table 4: Trench Load
Depth,H Nominal Pipe Trench Load,Pv �7V _ ]fie �7
Diameter l l l t
(ft) (in) (psi)
1.0 8 38.56
1.5 12 24.42
2.0 6 18.41
2.0 12 17.80
d.)Net Thickness for Bending Stress Design
Note: Refer to Table 10 of AWWA C 150/A21.50-02 for diameter-thickness ratios for Type 4 laying
conditions. Round up the trench loads to the next highest corresponding bending-stress design figure.
D
t =
( D /Table 5: Net Thickness t
Nominal Pipe Thickness Ratio, Net
Depth,H Diameter OD of Pipe,D Trench Load,P� D/t Thickness
(ft) (in) (ft) (psi) (in)
1.0 8 9.05 38.56 58 0.16
1.5 12 13.20 24.42 90 0.15
2.0 6 6.90 18.41 130 0.05
2.0 12 13.20 17.80 136 0.10
Page 2 of 4
Step 3-Selection of Net Thickness and Addition of Service Allowances
Note:the thicknesses calculated in Step 2 were selected due to the assumption that the internal pressure within
the storm pipes are 0 psi.
a.)Minimum Manufacturing Thickness-H=1 ft;D=8 in
Net Thickness= 0.16 in
Service Allowance= 0.08 in
Min Manufacturing Thickness= 0.24 in
b.)Minimum Manufacturing Thickness-H=1.5 ft;D=12 in
Net Thickness= 0.15 in
Service Allowance= 0.08 in
Min Manufacturing Thickness= 0.23 in
c.)Minimum Manufacturing Thickness-H=2.0 ft;D=6 in
Net Thickness= 0.05 in
Service Allowance= 0.08 in
Min Manufacturing Thickness= 0.13 in
d.)Minimum Manufacturing Thickness-H=2.0 ft;D=12 in
Net Thickness= 0.10 in
Service Allowance= 0.08 in
Min Manufacturing Thickness= 0.18 in
Note:a service allowance of 0.08 inches is added to the net thickness per Section 4.1.3.b of ANSI/AW WA
C 150/A21.50-02.
Step 4-Check Deflection of the Pipe
Note:Refer to Table 10 of ANSI/AWWA C150/A21.50-02 for diameter-thickness ratios for Type 4 laying
conditions.Round up the trench loads to the next highest corresponding deflection check.
t =
D
( D / ti )
Table 6: Pipe Deflection
Nominal Pipe Thickness Ratio
Depth,H OD of Pipe,D Trench Load,P`. Thickness
Diameter D/t
(ft) (in) (ft) (psi) (in)
1.0 8 9.05 38.56 56 0.16
1.5 12 13.20 24.42 70 0.19
2.0 6 6.90 18.41 83 0.08
2.0 12 13.20 17.80 85 0.16
Minimum Manufacturing Thickness>Deflection
Therefore,Minimum Manufacturing Thickness Controls for all pipe configurations and depths
Page 3 of 4
Step 5—Add the Casting Tolerance
Table 7: Allowance for Casting
Tolerance
Size Casting Allowance
(in) (in)
3-8 0.05
10-12 0.06
*Note:the table information was derived from Table 3 of ANSUAWWA C150/A21.50-02
a.)Total Thickness—H=1 ft; D=8 in
Min Manufacturing Thickness= 0.24 in —
Casting Tolerance= 0.05 in
Total Thickness= 0.29 in
Total Thickness>Class 50
Therefore,the minimum Special Class pipe required for this scenario is Class 51
b.)Total Thickness—H=1.5 ft; D=12 in
Min Manufacturing Thickness= 0.23 in
Casting Tolerance= 0.06 in
Total Thickness= 0.29 in
Total Thickness<Class 50
Therefore,the minimum Special Class pipe required for this scenario is Class 50s
c.)Total Thickness—H=2.0 ft; D=6 in
Min Manufacturing Thickness= 0.13 in
Casting Tolerance= 0.05 in
Total Thickness= 0.18 in
Total Thickness<Class 50
Therefore,the minimum Special Class pipe required for this scenario is Class 50
d.)Total Thickness—H=2.0 ft; D=12 in
Min Manufacturing Thickness= 0.18 in
Casting Tolerance= 0.06 in
Total Thickness= 0.24 in
Total Thickness<Class 50
Therefore,the minimum Special Class pipe required for this scenario is Class 50 ^�^'
NOTE:the project specification requires Class 52 ductile iron pipe beneath taxiway crossing areas.
Page 4 of 4
PROJECT: Renton Municipal Airport,Taxiway B,Phase I DEPTH OF PIPE COVER
PROJ NO.: 23-2010-007 Calculated by: BTS
DATE: 9/19/2012 Checked by:
FILE: H:\DOC\23Ap\10\007 Renton TW B&Signage\Design\Drainage\[Pipe Loading-Pbase I.xlsx]Pipe Xings Date Checked:
Pipe Sections CB "From" IE Pipe Diameter Approx. Pipe Length of Pipe to Asphalt Crown of Pipe Top of Asphalt Depth to Cover
"From" "To" (ft) (in) Stationing Slope EOA CL EOA EOA CL EOA EOA CL EOA EOA CL EOA
CB5 CB6 21.25 12 30+78 0.34% 14 28 44 22.20 22.15 22.10 24.55 24.74 24.55 2.3 2.6 2.4
CB7 CB8 19.91 12 33+76 1.80% 39 51 63 20.208 19.99 19.78 24.26 24.45 24.26 4.1 4.5 4.5
C139 CB10 21.05 8 37+15 0.40% 0.00 -- -- 21.72 -- -- 22.7 -- -- 1.0 -- --
CB10 CB11 20.6 12 36+48 0.34% 0.00 51 63 21.60 21.43 21.39 23.5 24.1 23.91 1.9 2.7 2.5
CB16 CB17 19.7 12 38+85 0.32% 25 48 71 20.62 20.55 20.47 23.89 24.08 23.89 3.3 3.5 3.4
CB 17 CB 18 19.1 12 39+66 0.32% 3 7 52 95 19.98 19.93 19.80 23.86 23.91 23.85 3.9 4.0 4.1
CB 19 E7 19 12 42+85.5 0.50% 0 13 48 20.00 19.94 19.76 23.6 23.89 23.17 3.6 4.0 3.4
CB25 CB24 20.4 12 44+49.5 0.50% 0 47 65 21.40 21.17 21.08 22.8 23.71 23.52 1.4 2.5 2.4
CB26 CB25 21.3 12 43+41.5 0.85% 0 -- -- 22.3 -- -- 23.3 -- -- 1.0 -- --
- CB27 CB25 21 8 45+22.4 0.34% 0 -- -- 21.67 -- -- 22.7 -- -- 1.0 -- --
CB28 CB29 20 6 46+83 0.20% 23 53 83 20.45 20.39 20.33 22.66 22.96 22.66 2.2 2.6 2.3
IE=Invert Elevation
CB=Catch Basin
EOA=Edge of Asphalt
CL=Centerline
Approx.=Approximate
No.=Number
Page 1 of 1
Appendix E
Bond Quantities Worksheet
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I
Technical Information Report (TIR)
Site Improvement Bond Quantity Worksheet
Original bond computations prepared by:
Name: Benjamin Sommer Date: 06.26.12
PE Registration Number: 45892 Tel.#: (425)741-3800
Firm Name: Reid Middleton, Inc.
Address: 728 134th Street SW,Suite 200,Everett,WA 98204 Project No: 232010.007
ROAD IMPROVEMENTS&DRAINAGE FACILITIES FINANCIAL GUARANTEE REQUIREMENTS
PERFORMANCE BOND*,** PUBLIC ROAD&DRAINAGE MAINTENANCE/DEFECT
AMOUNT BOND-
,'-Stabilization/Erosion Sediment Control(ESC) (A) NA***
Existing Right-of-Way Improvements (B) $
Future Public Road Improvements&Drainage Facilities (C) $ 1,566,901.7
Private Improvements (D) $
Performance Bond*Amount (A+B+C+D) = TOTAL (T) $ 1,566,901.7
Minimum bond*amount is$1000. (B+C)x
0.20= $ 313,380.3
Maintenance/Defect Bond*Total
NAME OF PERSON PREPARING BOND*REDUCTION: Dale:
*NOTE:The word"bond"as used in this document means any financial guarantee acceptable to the City of Renton.
**NOTE:All prices include labor,equipment,materials,overhead and profit. Prices are from RS Means data adjusted for the Seattle area
or from local sources if not included in the RS Means database.
***NOTE: Stabilization/Erosion Sediment Control(ESC)worksheet is not included in the City of Renton 2009 Surface Water Design Manual
Amendment,Reference 8-H.
REQUIRED BOND*AMOUNTS ARE SUBJECT TO REVIEW AND MODIFICATION BY RDSD
Page 1 of 7 Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet.xlsx Report Date:7/2/2012
Site Improvement Bond Quantity Worksheet
Existing Future Public Private Quantity Completed
Right-of-Way Road Improvements Improvements (Bond Reduction)'
&Drainage Facilities Quant.
Number Unit Price Unit Quant. Cost Quant. Cost Quant, Cost Complete Cost
GENERAL ITEMS
Backfill&Compaction-embankment GI-1 $ 5.62 CY 0.00 0.00 0.00 0.00
Backfill&Compaction-trench GI-2 $ 8.53 CY 0.00 0.00 0.00 0.00
Clear/Remove Brush,by hand GI-3 $ 0.36 SY 0.00 0.00 0.00 0.00
Clearing/Grubbing/Tree Removal GI-4 $ 8,876,16 Acre 0.00 0.00 0.00 0.00
Excavation-bulk GI-5 $ 1.50 CY 0.00 5030 7,545.00 0.00 0.00
Excavation-Trench GI-6 $ 4.06 CY 0.00 1 0.00 0.00 0.00
Fencing,cedar,6'high GI-7 $ 18.55 LF 0.00 0.00 0.00 1 0.00
Fencing,chain link,vinyl coated, 6'high GI-8 $ 13.44 LF 0.00 32 430.08 0.00 0.00
Fencing,chain link,gate,vinyl coated, 20' GI-9 $ 1,271.81 Each 0.00 1 1,271.81 0.00 0.00
Fencing,split rail,3'high GI-10 $ 12.12 LF 0,00 0.00 0.00 0.00
Fill&compact-common barrow GI-11 $ 22.57 CY 0.00 2250 50,782.50 0.00 0.00
Fill&compact-gravel base GI-12 $ 25.48 CY 0.00 0.00 0.00 0.00
Fill&compact-screened topsoil GI-13 $ 37.85 CY 0.00 150 5,677.50 1 0.00 0.00
Gabion,12"deep,stone filled mesh GI-14 $ 54.31 SY 0.00 0.00 0.00 0.00
Gabion, 18"deep,stone filled mesh GI-15 $ 74.85 SY 0.00 0.00 0.00 0.00
Gabion,36"deep,stone filled mesh GI-16 $ 132.48 SY 0.00 0.00 0.00 0.00
Grading,fine,by hand GI-17 $ 2.02 SY 0.00 0.00 0.00 0.00
Grading,fine,with grader GI-18 $ 0.95 SY 0.00 32000 30,400.00 0.00 0.00
Monuments,3'long GI-19 $ 135.13 Each 0.00 0.00 0.00 0.00
Sensitive Areas Sign GI-20 $ 2.88 Each 0.00 0.00 1 0.00 0.00
Sodding,1"deep,sloped ground GI-21 $ 7.46 SY 0.00 0.00 0.00 0.00
Surveying,line&grade GI-22 $ 788.26 Day 0.00 0.00 0.00 0,00
Surveying,lot location/lines GI-23 $ 1,556.64 Acre 1 0.00 10.5 16,344.72 0.00 0.00
Traffic control crew(2 flaggers) GI-24 $ 85.18 HR 0.00 0.00 0.00 0.00
Trail,4"chipped wood GI-25 $ 7.59 SY 0.00 0.00 0.00 0.00
Trail,4"crushed cinder GI-26 $ 8.33 SY 0.00 0.00 0.00 0.00
Trail,4"top course GI-27 $ 8.19 SY 0.00 0.00 0.00 0.00
Wall,retaining,concrete GI-28 $ 44.16 SF 0.00 0.00 0.00 0.00
Wall,rockery GI-29 $ 9.49 SF 0.00 1 0.001 1 0.00 0.00
Page 2 of 7 SUBTOTAL 0.00 112,451.61 0.00 0.00
Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet.xlsx Report Date:7/2/2012
Site Improvement Bond Quantity Worksheet
Existing Future Public Private Bond Reduction`
Right-of-way Road Improvements Improvements
&Drainage Facilities Quant.
Number Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Complete Cost
ROADIMPROVEMENT
AC Grinding,4'wide machine<1000sy RI-1 $ 23.00 SY 0.00 450 10,350.00 0.00 0.00
AC Grinding,4'wide machine 1000-2000sy RI-2 $ 5.75 SY 0.00 0.00 0.00 0.00
AC Grinding,4'wide machine>2000sy RI-3 $ 1.38 SY 0.00 0.00 0.00 0.00
AC Removal/Disposal/Repair RI-4 $ 41.14 SY 0.00 11200 460,768.00 0.00 0.00
Barricade,type I RI-5 $ 30.03 LF 0.00 0.00 0.00 0.00
Barricade,type III(Permanent) RI-6 $ 45.05 LF 0.00 0.00 0.00 D.00
Curb&Gutter,rolled RI-7 $ 13.27 LF 0.00 0.00 0.00 0.00
Curb&Gutter,vertical RI-8 $ 9.69 LF 0.00 0.00 0.00 0.00
Curb and Gutter,demolition and disposal RI-9 $ 13.58 LF 0.00 0.00 0,00 0.00
Curb,extruded asphalt RI-10 $ 2.44 LF 0.00 0.00 0.00 0.00
Curb,extruded concrete RI-11 $ 2.56 LF 0.00 0.00 0.00 0.00
Sawcut,asphalt,3"depth RI-12 $ 1.85 LF 0.00 850 1,572.50 0.00 0.00
Sawcut,concrete,per 1"depth RI-13 $ 1.69 LF 0.00 0.00 0.00 0.00
Sealant,asphalt RI-14 $ 0.99 LF 0.00 0.00 0.00 0.00
Shoulder,AC, (see AC road unit price) RI-15 $ - SY 0.00 0.00 0.00 0.00
Shoulder,gravel,4"thick RI-16 $ 7.53 SY 0.00 0.00 0.00 0.00
Sidewalk,4"thick RI-17 $ 30.52 SY 0.00 0.00 0.00 1 0.00
Sidewalk,4"thick,demolition and disposal RI-18 $ 27.73 SY 0.00 0.00 0.00 0.00
Sidewalk,5"thick RI-19 $ 34.94 SY 0.00 0.00 0.00 0.00
Sidewalk,5"thick,demolition and disposal RI-20 $ 34.65 SY 0.00 0.00 0.00 0.00
Sign,handicap RI-21 $ 85.28 Each 0.00 0.00 0.00 0.00
Striping,per stall RI-22 $ 5.82 Each 0.00 0.00 0.00 0.00
Striping,thermoplastic,(for crosswalk) RI-23 $ 2.38 SF 0.00 4350 10,353.00 0.00 0.00
Striping,4"reflectorized line RI-24 $ 0.25 LF 0.o0j 1 0.00 0.00 0.00
Page 3 of 7 SUBTOTAL 0.00 483,043.50 0.00 0.00
Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet.xlsx Report Date:7/2/2012
Site Improvement Bond Quantity Worksheet
Existing Future Public Private Bond Reduction"
Right-of-way Road Improvements Improvements
&Drainage Facilities Quant,
Number Unit Price Unit I Quant. Cost Quant. 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 KC RS'93,(additional 2.5"base)add: RS-1 $ 3.60 SY 0.00 0.00 0.00 0.00
AC Overlay,1.5"AC RS-2 $ 7.39 SY 0.00 0.00 0.00 0.00
AC Overlay,2"AC RS-3 $ 8.75 SY 0.00 0.00 0.00 0.00
AC Road,2",4"rock,First 2500 SY RS-4 $ 17.24 SY 0.00 0.00 0.00 0.00
AC Road,2",4"rock,Qty.over 2500SY RS-5 $ 13.36 SY 0.00 0.00 0.00 0.00
AC Road,3",4"rock,First 2500 SY RS-6 $ 19.69 SY 0.00 0.00 0.00 0.00
AC Road,3",4"rock,Qty.over 2500 SY RS-7 $ 15.81 SY 1 0.00 0.00 0.00 0.00
AC Road,5",First 2500 SY RS-8 $ 14.57 SY 0.00 0.00 0.00 0.00
AC Road,5",Qty.Over 2500 SY RS-9 $ 13.94 SY 0.00 0.00 0.00 0.00
AC Road,6",First 2500 SY RS-10 $ 16.76 SY 0.00 0.00 0.00 0.00
AC Road,6",Qty.Over 2500 SY RS-11 $ 16.12 SY 0.00 0.00 0.00 0.00
Asphalt Treated Base,4"thick RS-12 $ 9.21 SY 0.00 0.00 0.00 0.00
Gravel Road,4"rock,First 2500 SY RS-13 $ 11.41 SY 0.00 0.00 0.00 0.00
Gravel Road,4"rock.Qty.over 2500 SY RS-14 $ 7.53 SY 0.00 0.00 0.00 0.00
PCC Road.5",no base,over 2500 SY RS-15 $ 21.51 SY 0.00 0.00 0.00 0.00
PCC Road, 6",no base,over 2500 SY RS-16 $ 21.87 SY 0.00 0.00 0.00 0.00
Thickened Edge RS-17 $ 6.89 LF 0.00 0.00 0.001 1 0.00
Page 4 of 7 SUBTOTAL 0.00 0.00 0.00 0.00
Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities VVorksheet.xlsx Report Date:7/2/2012
Site Improvement Bond Quantity Worksheet
Existing Future Public Private Bond Reduction`
Right-of-way Road Improvements Improvements
&Drainage Facilities Quant.
Number Unit Price Unit Quant. Cost Ouant. 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 $ 16.74 1 SY 0.00 120 2,008.80 0.00 0.00
Bollards-fixed D-2 1 $ 240.74 1 Each I 1 0.00 0.001 1 0.00 0.00
Bollards-removable D-3 1 $ 452.34 1 Each I 1 0.001 0.001 1 0.00 0.00
(CBs include frame and lid)
CB Type I D-4 S 1,257.64 Each 0.00 17 21,379.88 0.00 0.00
CB Type IL D-5 $ 1,433.59 Each 0.00 2 2,867.18 0.00 0.00
CB Type II,48"diameter D-6 $ 2,033.57 Each 0.00 11 22,369.27 0.00 0.00
for additional depth over 4' D-7 $ 436.52 FT 0.00 0.00 0,00 0.00
CB Type 11.54"diameter D-8 $ 2,192.54 Each 0.00 0.00 0,00 0.00
for additional depth over 4' D-9 $ 486.53 FT 0.00 0.00 0.00 0.00
CB Type 11,60"diameter D-10 $ 2,351.52 Each 0.00 0.00 0.00 0.00
for additional depth over 4' D-11 $ 536.54 FT 0.00 0.00 0.00 0.00
CB Type 11,72"diameter D-12 $ 3,212.64 Each 0.00 0.00 0.00 0.00
for additional depth over 4' D-13 $ 692.21 FT 0.00 0.00 0.00 0.00
Through-curb Inlet Framework(Add) D-14 $ 366.09 Each 0.00 1 0.00 0.00 0.00
Cleanout,PVC,4" D-15 $ 130.55 Each 0.00 0.00 0.00 0.00
Cleanout,PVC.6" D-16 $ 174.90 Each 0.00 21 3,672.90 0.00 0.00
Cleanout,PVC,8" D-17 $ 224.19 Each 0.00 0.00 0.00 0.00
Culvert,PVC,4" D-18 $ 8.64 LF 0.00 0.00 0.00 0.00
Culvert,PVC,6" D-19 $ 12.60 LF 0.00 2625 33.075.00 0.00 0.00
Culvert,PVC, 8" D-20 $ 13.33 LF 0.00 0.00 0.00 0.00
Culvert,PVC,12" D-21 $ 21.77 LF 0.00 0.00 0.00 0.00
Culvert,CMP,8" D-22 $ 17.25 LF 0.00 0.00 0.00 0.00
Culvert,CMP, 12" D-23 $ 26.45 LF 0.00 0.00 0.00 1 0.00
Culvert,CMP,15" D-24 $ 32.73 LF 0.00 0.00 0.00 0.00
Culvert,CMP, 18" D-25 $ 37.74 LF 0.00 550 20,757.00 0.00 0.00
Culvert,CMP,24" D-26 $ 53.33 LF 0.00 0.00 0.00 0.00
Culvert,CMP,30" D-27 $ 71.45 LF 0.00 0.00 0.00 0.00
Culvert,CMP,36" D-28 $ 112.11 LF 0.00 0.00 0.00 0.00
Culvert,CMP,48" D-29 $ 140.83 LF 0.00 0.00 0.00 0.00
Culvert,CMP,60" D-30 $ 235.45 LF 0.00 0.00 0.00 0.00
Culvert,CMP,72" D-31 $ 302.58 LF 0.00 0.00 0.00 0.00
Page 5 of 7 SUBTOTAL 0.00 106,130.03 0.00 0.00
Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet.xlsx Report Date:7/2/2012
Site Improvement Bond Quantity Worksheet
Existing Future Public Private Bond Reduction"
Right-of-way Road Improvements Improvements
DRAINAGE CONTINUED &Drainage Facilities Quant.
Number Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Complete Cost
Culvert,Concrete,8" D-32 $ 21.02 ILE 0 0 0 0
Culvert,Concrete,12" D-33 $ 30.05 0 0 0 0
Culvert,Concrete,15" D-34 $ 37.34 0 0 0 0
Culvert,Concrete,18" D-35 $ 44.51 0 0 0 0
Culvert,Concrete,24" D-36 $ 61.07 0 0 0 0
Culvert,Concrete,30" D-37 $ 104.18 LF 0 0 0 0
Culvert,Concrete,36" D-38 $ 137.63 LF 0 0 0 0
Culvert,Concrete,42" D-39 $ 158.42 LF 0 0 0 0
Culvert,Concrete,48" D-40 $ 175.94 LF 0 0 0 0
Culvert,CPP,6" D-41 $ 10.70 LF 0 370 3959 0 0
Culvert,CPP,8" D-42 $ 16.10 LF 0 0 0 0
Culvert,CPP,12" D-43 $ 20.70 LF 0 450 9315 0 0
Culvert,CPP,15" D-44 $ 23.00 LF 0 1 0 0 0
Culvert,CPP,18" D-45 $ 27.60 LF 0 0 0 0
Culvert,CPP,24" D-46 $ 36.80 LF 0 0 0 0
Culvert,CPP,30" D-47 $ 48.30 LF 0 0 0 0
Culvert,CPP,36" D-48 $ 55.20 LF 0 0 0 0
Ditching D-49 $ 8.08 CY 0 0 1 0 0
Flow Dispersal Trench (1,436 base+) D-50 $ 25.99 LF 0 0 0 0
French Drain (T depth) D-51 $ 22.60 LF 0 1 0 0 0
Geotextile,laid in trench,polypropylene D-52 $ 2.40 SY 0 225 540 0 0
Infiltration pond testing D-53 $ 74.75 HR 0 0 0 0
Mid-tank Access Riser,48"dia, 6-deep D-54 $ 1,605.40 Each 0 0 0 0
Pond Overflow Spillway D-55 $ 14.01 SY 0 0 0 0
Restrictor/Oil Separator,12" D-56 $ 1,045.19 Each 0 0 0 0
Restrictor/Oil Separator,15" D-57 $ 1,095.56 Each 0 0 1 0 0
Restrictor/Oil Separator, 18" D-58 $ 11146.16 Each 0 1 0 0 0
Riprap,placed D-59 $ 39.08 CY 0 0 0 0
Tank End Reducer(36"diameter) D-60 $ 1,000.50 Each 0 0 0 0
Trash Rack,12" D-61 $ 211.97 Each 0 4 847.88 0 0
Trash Rack,15" D-62 $ 237.27 Each 0 0 0 0
Trash Rack,18" D-63 $ 268.89 Each 0 0 0 0
Trash Rack,21" D-64 $ 306.84 Each 0 1 0 0 0
Page 6 of 7 SUBTOTAL 0.00 14661.88 0.00 0.00
Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet.xlsx Report Date:7/2/2012
Site Improvement Bond Quantity Worksheet
Existing Future Public Private Bond Reduction'
Right-of-way Road Improvements Improvements
&Drainage Facilities Quant.
Number Unit Price Unit Quant. Price Quant, Cost Quant. Cost Complete Cost
PARKING LOT SURFACING
2"AC,2"top course rock&4"borrow PL-1 $ 15.84 1 SY I 1 01 1 01 1 0 0
2"AC, 1.5" top course& 2.5"base course PL-2 $ 17.24 SY 0 0 01 1 0
4"select borrow PL-3 $ 4.55 SY 0 0 01 0
1.5 top course rock&2.5 base course PL-4 $ 11.41 SY 0 1 0 01 1 0
WRITE-IN-ITEMS
(Such as detention/water quality vaults.)
Yard Drain WI-1 $ 250.00 EA. 0 10 2,500.00 0.00 0.00
Slotted Drain System WI-2 $ 250.00 LF 0 550 137,500.00 0.00 0.00
Culvert,DIP,8" WI-3 $ 40.00 LF 0 90 3,600.00 0.00 0.00
Culvert,DIP,12" WI-4 $ Woo LF 0 776 69,840.00 0.00 0.00
Asphalt Surface Course 4",2"TC.12"BC WI-5 $ 22.00 SF 0 11627 255,794.00 0.00 0.00
Biofiltration Swale WI-6 $ 60.00 LF 0 200 12,000.00 0.00 0.00
Thermoplastic Pavement Marking WI-7 $ 22.00 SF 0 354 7,788.00 0.00 0.00
SF 0 0.00 0.00 0.00
LF 0 0.00 0.00 0.00
LF 0 0.00 0.00 0.00
SUBTOTAL 0.00 489,022.00 0.00 0.00
SUBTOTAL(SUM ALL PAGES): 0.00 1,205,309.02 0.00 0,00
30%CONTINGENCY&MOBILIZATION: 0.00 361,592.71 0.00 0.00
GRANDTOTAL: 0.00 1,566,901.73 0.00 0.00
COLUMN: B C D E
Page 7 of 7
Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet.xlsx Report Date:7/2/2012
Appendix F
Flow Control and Water Facility Summary Sheet
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I
Technical Information Report (TIR)
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
STORMWATER FACILITY SUMMARY SHEET DDES Permit
Number PRE 12-012
(provide one Stormwater Facility Summary Sheet per Natural Discharge Location)
Overview:
Project Name
City of Renton Taxiway B System Rehabilitation (Phase I) Date June 18, 2002
Downstream Drainage Basins
Major Basin Name Lake Washington
Immediate Basin Name
Flow Control:
Flow Control Facility Name/Number N/A
Facility
Location N/A
If none,
Flow control provided in regional/shared facility (give
location) N/A
No flow control required N/A Exemption number
Cedar River
General Facility Information:
Type/Number of detention facilities: Type/Number of infiltration facilities:
ponds ponds
vaults tanks
tanks trenches
Control Structure Location
N/A
Type of Control Structure N/A Number of Orifices/Restrictions
Size of Orifice/Restriction: No. 1
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 N/A
Number of Lots N/A
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 11x17" reduced size plan sheets may be used)
N/A
2009 Surface Water Design Manual 1/9/2009
2
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
Water Quality:
Type/Number of water quality facilities/BMPs:
X biofiltration swale sand filter(basic or large)
(regula we 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
X 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
pre-settling pond
pre-settling structure:
Manufacturer
high flow bypass structure (e.g., flow-splitter catch basin)
source controls
Design Information Wet Biofiltration Swales
Sub-basin C: 0.56 cfs
Water Quality design flow Sub-basin D: 0.27 cfs
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)
Please refer to Figure 4-1 for more information regarding the water quality types and
locations.
i,
2009 Surface Water Design Manual 1/9/2009
4
Appendix G
Operation and Maintenance Manual
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase I
Technical Information Report (TIR) ` ' 'R. PA '
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 4- CONTROL STRUCTURE/FLOW RESTRICTOR
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Structure Trash and debris Trash or debris of more than'%cubic foot which No Trash or debris blocking or
is located immediately in front of the structure potentially blocking entrance to
opening or is blocking capacity of the structure by structure.
more than 10%.
Trash or debris in the structure that exceeds'/3 No trash or debris in the structure.
the depth from the bottom of basin to invert the
lowest pipe into or out of the basin.
Deposits of garbage exceeding 1 cubic foot in No condition present which would
volume. attract or support the breeding of
insects or rodents.
Sediment Sediment exceeds 60%of the depth from the Sump of structure contains no
bottom of the structure to the invert of the lowest sediment.
pipe into or out of the structure or the bottom of
the FROP-T section or is within 6 inches of the
invert of the lowest pipe into or out of the
structure or the bottom of the FROP-T section.
Damage to frame Corner of frame extends more than%inch past Frame is even with curb.
and/or top slab curb face into the street(If applicable).
Top slab has holes larger than 2 square inches or Top slab is free of holes and cracks.
cracks wider than'%inch.
Frame not sitting flush on top slab, i.e., Frame is sitting flush on top slab.
separation of more than%inch of the frame from
the top slab.
Cracks in walls or Cracks wider than'%inch and longer than 3 feet, Structure is sealed and structurally
bottom any evidence of soil particles entering structure sound.
through cracks,or maintenance person judges
that structure is unsound.
Cracks wider than'%inch and longer than 1 foot No cracks more than 1/4 inch wide at
at the joint of any inlet/outlet pipe or any evidence the joint of inlet/outlet pipe.
of soil particles entering structure through cracks.
Settlement/ Structure has settled more than 1 inch or has Basin replaced or repaired to design
misalignment rotated more than 2 inches out of alignment. standards.
Damaged pipe joints Cracks wider than'/2-inch at the joint of the No cracks more than %-inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of inlet/outlet pipes.
the structure at the joint of the inlet/outlet pipes.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Ladder rungs missing Ladder is unsafe due to missing rungs, Ladder meets design standards and
or unsafe misalignment, rust,cracks,or sharp edges. allows maintenance person safe
access.
FROP-T Section Damage T section is not securely attached to structure T section securely attached to wall
wall and outlet pipe structure should support at and outlet pipe.
least 1,000 Ibs of up or down pressure.
Structure is not in upright position(allow up to Structure in correct position.
10%from plumb).
Connections to outlet pipe are not watertight or Connections to outlet pipe are water
show signs of deteriorated grout. tight;structure repaired or replaced
and works as designed.
Any holes—other than designed holes—in the Structure has no holes other than
structure. designed holes.
Cleanout Gate Damaged or missing Cleanout gate is missing. Replace cleanout gate.
2009 Surface Water Design Manual—Appendix A 1/9/2009
A-7
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 4- CONTROL STRUCTURE/FLOW RESTRICTOR
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Cleanout gate is not watertight. Gate is watertight and works as
designed.
Gate cannot be moved up and down by one Gate moves up and down easily and
maintenance person. is watertight.
Chair/rod leading to gate is missing or damaged. Chain is in place and works as
designed.
Orifice Plate Damaged or missing Control device is not working properly due to Plate is in place and works as
missing, out of place,or bent orifice plate. designed.
Obstructions Any trash,debris, sediment,or vegetation Plate is free of all obstructions and
blocking the plate, works as designed.
Overflow Pipe Obstructions Any trash or debris blocking (or having the Pipe is free of all obstructions and
potential of blocking)the overflow pipe. works as designed.
Deformed or damaged Lip of overflow pipe is bent or deformed. Overflow pipe does not allow
lip overflow at an elevation lower than
design
Inlet/Outlet Pipe Sediment Sediment filling 20%or more of the pipe. Inlet/outlet pipes clear of sediment.
accumulation
Trash and debris Trash and debris accumulated in inlet/outlet No trash or debris in pipes.
pipes(includes floatables and non-floatables).
Damaged Cracks wider than'%-inch at the joint of the No cracks more than '/,inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of the inlet/outlet pipe.
at the joints of the inlet/outlet pipes.
Metal Grates Unsafe grate opening Grate with opening wider than 7/8 inch. Grate opening meets design
(If Applicable) standards.
Trash and debris Trash and debris that is blocking more than 20% Grate free of trash and debris.
of grate surface. footnote to guidelines for disposal
Damaged or missing Grate missing or broken member(s)of the grate. Grate is in place and meets design
standards.
Manhole Cover/Lid Cover/lid not in place Cover/lid is missing or only partially in place. Cover/lid protects opening to
Any open structure requires urgent structure.
maintenance.
Locking mechanism Mechanism cannot be opened by one Mechanism opens with proper tools.
Not Working maintenance person with proper tools. Bolts
cannot be seated. Self-locking cover/lid does not
work.
Cover/lid difficult to One maintenance person cannot remove Cover/lid can be removed and
Remove cover/lid after applying 80 lbs. of lift. reinstalled by one maintenance
person.
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-8
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 5-CATCH BASINS AND MANHOLES
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Structure Sediment Sediment exceeds 60%of the depth from the Sump of catch basin contains no
bottom of the catch basin to the invert of the sediment.
lowest pipe into or out of the catch basin or is
within 6 inches of the invert of the lowest pipe
into or out of the catch basin.
Trash and debris Trash or debris of more than%cubic foot which No Trash or debris blocking or
is located immediately in front of the catch basin potentially blocking entrance to
opening or is blocking capacity of the catch basin catch basin.
by more than 10%.
Trash or debris in the catch basin that exceeds No trash or debris in the catch basin.
1/3 the depth from the bottom of basin to invert the
lowest pipe into or out of the basin.
Dead animals or vegetation that could generate No dead animals or vegetation
odors that could cause complaints or dangerous present within catch basin.
gases(e.g., methane).
Deposits of garbage exceeding 1 cubic foot in No condition present which would
volume. attract or support the breeding of
insects or rodents.
Damage to frame Corner of frame extends more than%inch past Frame is even with curb.
and/or top slab curb face into the street(If applicable).
Top slab has holes larger than 2 square inches or Top slab is free of holes and cracks.
cracks wider than'%inch.
Frame not sitting flush on top slab,i.e., Frame is sitting flush on top slab.
separation of more than%inch of the frame from
the top slab.
Cracks in walls or Cracks wider than'%inch and longer than 3 feet, Catch basin is sealed and
bottom any evidence of soil particles entering catch structurally sound.
basin through cracks,or maintenance person
judges that catch basin is unsound.
Cracks wider than'/=inch and longer than 1 foot No cracks more than'/,inch wide at
at the joint of any inlet/outlet pipe or any evidence the joint of inlet/outlet pipe.
of soil particles entering catch basin through
cracks.
Settlement/ Catch basin has settled more than 1 inch or has Basin replaced or repaired to design
misalignment rotated more than 2 inches out of alignment. standards.
Damaged pipe joints Cracks wider than 1/2-inch at the joint of the No cracks more than '/<-inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of inlet/outlet pipes.
the catch basin at the joint of the inlet/outlet
pipes.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Inlet/Outlet Pipe Sediment Sediment filling 20%or more of the pipe. Inlet/outlet pipes clear of sediment.
accumulation
Trash and debris Trash and debris accumulated in inlet/outlet No trash or debris in pipes.
pipes(includes floatables and non-floatables).
Damaged Cracks wider than'/2-inch at the joint of the No cracks more than '%-inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of the inlet/outlet pipe.
at the joints of the inlet/outlet pipes.
2009 Surface Water Design Manual—Appendix A 1/9/2009
A-9
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 5-CATCH BASINS AND MANHOLES
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Metal Grates Unsafe grate opening Grate with opening wider than 7/8 inch. Grate opening meets design
(Catch Basins) standards.
Trash and debris Trash and debris that is blocking more than 20% Grate free of trash and debris.
of grate surface. footnote to guidelines for disposal
Damaged or missing Grate missing or broken member(s)of the grate. Grate is in place and meets design
Any open structure requires urgent standards.
maintenance.
Manhole Cover/Lid Cover/lid not in place Cover/lid is missing or only partially in place. Cover/lid protects opening to
Any open structure requires urgent structure.
maintenance.
Locking mechanism Mechanism cannot be opened by one Mechanism opens with proper tools.
Not Working maintenance person with proper tools. Bolts
cannot be seated. Self-locking cover/lid does not
work.
Cover/lid difficult to One maintenance person cannot remove Cover/lid can be removed and
Remove cover/lid after applying 80 lbs. of lift. reinstalled by one maintenance
person.
I
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-10
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 6-CONVEYANCE PIPES AND DITCHES
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Pipes Sediment&debris Accumulated sediment or debris that exceeds Water flows freely through pipes.
accumulation 20%of the diameter of the pipe.
Vegetation/roots Vegetation/roots that reduce free movement of Water flows freely through pipes.
water through pipes.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Damage to protective Protective coating is damaged; rust or corrosion Pipe repaired or replaced.
coating or corrosion is weakening the structural integrity of any part of
pipe.
Damaged Any dent that decreases the cross section area of Pipe repaired or replaced.
pipe by more than 20%or is determined to have
weakened structural integrity of the pipe.
Ditches Trash and debris Trash and debris exceeds 1 cubic foot per 1,000 Trash and debris cleared from
square feet of ditch and slopes. ditches.
Sediment Accumulated sediment that exceeds 20%of the Ditch cleaned/flushed of all sediment
accumulation design depth. and debris so that it matches design.
Noxious weeds Any noxious or nuisance vegetation which may Noxious and nuisance vegetation
constitute a hazard to County personnel or the removed according to applicable
public. regulations. No danger of noxious
vegetation where County personnel
or the public might normally be.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Vegetation Vegetation that reduces free movement of water Water flows freely through ditches.
through ditches.
Erosion damage to Any erosion observed on a ditch slope. Slopes are not eroding.
slopes
Rock lining out of One layer or less of rock exists above native soil Replace rocks to design standards.
place or missing(If area 5 square feet or more,any exposed native
Applicable) soil.
2009 Surface Water Design Manual—Appendix A 1/9/2009
A-I I
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 7- DEBRIS BARRIERS (E.G., TRASH RACKS)
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed.
Site Trash and debris Trash or debris plugging more than 20%of the Barrier clear to receive capacity flow.
area of the barrier.
Sediment Sediment accumulation of greater than 20%of Barrier clear to receive capacity flow.
accumulation the area of the barrier
Structure Cracked broken or Structure which bars attached to is damaged- Structure barrier attached to is
loose pipe is loose or cracked or concrete structure is sound.
cracked, broken of loose.
Bars Bar spacing Bar spacing exceeds 6 inches. Bars have at most 6 inche spacing.
Damaged or missing Bars are bent out of shape more than 3 inches. Bars in place with no bends more
bars than%inch.
Bars are missing or entire barrier missing. Bars in place according to design.
Bars are loose and rust is causing 50% Repair or replace barrier to design
deterioration to any part of barrier. standards.
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-12
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 11 - GROUNDS (LANDSCAPING)
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Site Trash or litter Any trash and debris which exceed 1 cubic foot Trash and debris cleared from site.
per 1,000 square feet(this is about equal to the
amount of trash it would take to fill up one
standard size office garbage can). In general,
there should be no visual evidence of dumping.
Noxious weeds Any noxious or nuisance vegetation which may Noxious and nuisance vegetation
constitute a hazard to County personnel or the removed according to applicable
public. regulations. No danger of noxious
vegetation where County personnel
or the public might normally be.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Grass/groundcover Grass or groundcover exceeds 18 inches in Grass or groundcover mowed to a
height. height no greater than 6 inches.
Trees and Shrubs Hazard Any tree or limb of a tree identified as having a No hazard trees in facility.
potential to fall and cause property damage or
threaten human life. A hazard tree identified by
a qualified arborist must be removed as soon
as possible.
Damaged Limbs or parts of trees or shrubs that are split or Trees and shrubs with less than 5%
broken which affect more than 25%of the total of total foliage with split or broken
foliage of the tree or shrub. limbs.
Trees or shrubs that have been blown down or No blown down vegetation or
knocked over. knocked over vegetation. Trees or
shrubs free of injury.
Trees or shrubs which are not adequately Tree or shrub in place and
supported or are leaning over,causing exposure adequately supported;dead or
of the roots. diseased trees removed.
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-16
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 13- BASIC BIOFILTRATION SWALE (GRASS)
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Site Trash and debris Any trash and/or debris accumulated on the No trash or debris on the bioswale
bioswale site. site.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Swale Section Sediment Sediment depth exceeds 2 inches in 10%of the No sediment deposits in grass
accumulation swale treatment area. treatment area of the bioswale.
Sediment inhibits grass growth over 10%of Grass growth not inhibited by
swale length. sediment.
Sediment inhibits even spreading of flow. Flow spreads evenly through swale
Erosion/scouring Eroded or scoured swale bottom due to No eroded or scoured areas in
channelization or high flows. bioswale. Cause of erosion or scour
addressed.
Poor vegetation Grass is sparse or bare or eroded patches occur Swale has no bare spots and grass
coverage in more than 10%of the swale bottom, is thick and healthy.
Grass too tall Grass excessively tall(greater than 10 inches), Grass is between 3 and 4 inches tall,
grass is thin or nuisance weeds and other thick and healthy. No clippings left
vegetation has taken over. in swale. No nuisance vegetation
present.
Excessive shade Grass growth is poor because sunlight does not Health grass growth or swale
reach swale. converted to a wet bioswale.
Constant baseflow Continuous flow through the swale,even when it Baseflow removed from swale by a
has been dry for weeks or an eroded, muddy low-flow pea-gravel drain or
channel has formed in the swale bottom. bypassed around the swale.
Standing water Water pools in the swale between storms or does Swale freely drains and there is no
not drain freely. standing water in swale between
storms.
Channelization Flow concentrates and erodes channel through No flow channels in swale.
swale.
Flow Spreader Concentrated flow Flow from spreader not uniformly distributed Flows are spread evenly over entire
across entire swale width. swale width.
Inlet/Outlet Pipe Sediment Sediment filling 20%or more of the pipe. Iniet/outlet pipes clear of sediment.
accumulation
Trash and debris Trash and debris accumulated in inlet/outlet No trash or debris in pipes.
pipes(includes floatables and non-floatables).
Damaged Cracks wider than'%-inch at the joint of the No cracks more than %-inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of the inlet/outlet pipe.
at the joints of the inlet/outlet pipes.
i
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-18
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 15- FILTER STRIP
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance Is Performed
Site Trash and debris Any trash and debris accumulated on the filter Filter strip site free of any trash or
strip site. debris
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Grass Strip Sediment Sediment accumulation on grass exceeds 2 No sediment deposits in treatment
accumulation inches depth. area.
Erosion/scouring Eroded or scoured swale bottom due to No eroded or scoured areas in
channelization or high flows. bioswale. Cause of erosion or scour
addressed.
Grass too tall Grass excessively tall(greater than 10 inches), Grass is between 3 and 4 inches tall,
grass is thin or nuisance weeds and other thick and healthy. No clippings left
vegetation has taken over. in swale. No nuisance vegetation
present.
Vegetation ineffective Grass has died out,become excessively tall Grass is healthy, less than 9 inches
(greater than 10 inches)or nuisance vegetation is high and no nuisance vegetation
taking over. present.
Flow Spreader Concentrated flow Flow from spreader not uniformly distributed Flows are spread evenly over entire
across entire swale width. swale width.
Inlet/Outlet Pipe Sediment Sediment filling 20%or more of the pipe. Inlet/outlet pipes clear of sediment.
accumulation
Trash and debris Trash and debris accumulated in inlet/outlet No trash or debris in pipes.
pipes(includes floatables and non-floatables).
Damaged Cracks wider than'/-inch at the joint of the No cracks more than'%-inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of the inlet/outlet pipe.
at the joints of the inlet/outlet pipes.
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-20
Fueling Operations
This activity applies if you refuel vehicles on the premises, whether a large sized gas station or a single
pump maintenance yard installation. It also covers mobile fueling operations. Stormwater runoff from
fueling areas may be contaminated with toxic hydrocarbons, oils and greases, and metals.
e
The following BMPs, or equivalent measures, methods, or practices, are
required if you are engaged in dedicated permanent fueling operations:
Cover the fueling area with an overhanging roof structure or canopy so that
precipitation cannot come in contact with the fueling area.
See BMP Info Sheet 3 in Chapter 5 for information on covering options.
An exception to this requirement is granted for mobile fueling equipment,
floating fuel islands on water, and oversized vehicles that can not
maneuver under a roof.
Pave the fueling area with Portland cement concrete and contain the area to
prevent uncontaminated stormwater from running into the fueling area and
carrying pollutants to the onsite storm drainage system or adjacent surface
water or conveyance systems.
1�- See BMP Info Sheet 5 in Chapter 5 for information on containment.
Install and maintain an oil or spill control device in the appropriate catch
basin(s) to treat runoff from the fueling area.
See the King County Surface Water Design Manual for various designs
and the BMP Info Sheet 9 in Chapter 5 for further information on
oil/water separators.
Never hose down the fueling area to the storm drains. Contaminated runoff
must be collected for proper disposal.
Required Routine Maintenance:
• Post signs to remind employees and customers not to top off the fuel
tank when filling. Post signs that ban customers and employees from
changing engine oil or other fluids at that location.
• Store and maintain appropriate spill cleanup materials in a location
known to all. Ensure that employees are familiar with the site's spill
control plan and/or proper spill cleanup procedures.
January 2009 King County Stormwater Pollution Prevention Manual
Fueling Operations(continued)
If you cannot implement the above requirements on your site, consider
ceasing your on-site fueling activities and take your vehicles to a fueling
station that meets these requirements.
The following BMPs, or equivalent measures, methods, or practices, are
required if you are engaged in mobile fueling operations:
Locate the fueling operation to ensure leaks or spills will not discharge,
flow, or be washed into the storm drainage system, surface water, or
groundwater.
Use drip pans or absorbent pads to capture drips or spills during fueling
operations.
If fueling is done during evening hours, lighting must be provided.
Required Routine Maintenance:
• Store and maintain appropriate spill cleanup materials in the mobile
fueling vehicle. Ensure that employees are familiar with proper spill
control and cleanup procedures.
� � � • .
The following BMPs are optional unless the above minimum required
BMPs do not provide adequate source control.
Use absorbent pillows or similar absorbent materials in or around storm
drain inlets on the property to filter oily runoff. These require frequent
maintenance and close attention,but can be useful in short-term situations.
Used absorbent materials containing oil must be picked up by a qualified
disposal contractor.
A catch basin insert configured for oil removal may remove some of the
pollutants in runoff from this activity. Catch basin inserts require frequent
maintenance to be effective. Carefully consider this when evaluating your
options. The oil absorbent filter media must retain absorbed oil during future
storm events. See Chapter 6.6.1 of the King County Surface Water Design
Manual for more information regarding which filter media provide
acceptable oil retention.
I--#- See BMP Info Sheet 10 in Chapter 5 for more information.
For more information or assistance in implementing these best management practices,contact the King County
Department of Natural Resources and Parks Water and Land Resources Division at 206-296-1900.
Reader Note: The above requirements are the minimum required BMPs. If these BMPs fail to prevent discharges to the
storm drainage system,you will be asked to take additional measures to correct the continued pollution discharges.
King County Stormwater Pollution Prevention Manual January 2009
Landscaping Activities and Vegetation Management
This broad activity encompasses all aspects of landscaping and vegetation management, from small-
scale yard maintenance to large-scale commercial landscaping businesses and vegetation
management programs. It includes vegetation removal, herbicide and insecticide application,
fertilizer application,watering, and other gardening and lawn care practices. Stormwater runoff from
areas that have been subject to pesticide or fertilizer application or extensive clearing, grading or
cutting may be contaminated with pesticides and other toxic organic compounds,metals, oils,
suspended solids, nutrients from fertilizer, and coliform bacteria, and may cause biochemical oxygen
demand.
While not required,consider using the Integrated Pest Management(IPM) approach for pest control.
IPM is an approach that uses an array of methods to manage pest damage with the least possible
hazard to people and the environment. IPM uses a combination of biological, cultural, and physical
practices that can significantly reduce or eliminate the use of pesticides.
See Activity Sheets A-5, "Storage of Pesticides and Fertilizers" and A-3, "Storage of Liquid
Materials in Portable Containers."Landscaping activities related to golf courses should refer to King
County's Golf Course BMP Manual (see Chapter 6 of this manual for more information).
Note: The term pesticide includes insecticides, herbicides,fungicides, rodenticides, etc.
The following BMPs,or equivalent measures, methods,or practices
are required if you are engaged in landscaping activities:
Do not apply any pesticides directly to surface waters,unless the
application is approved and permitted by the Washington State Department
of Ecology.
Mix pesticides so that spilled material will not be washed to surface waters,
the storm drainage system, or onto the ground. Clean up any spills
immediately. Ensure employees are trained on the proper use of pesticides
and in pesticide application techniques to prevent pollution. Washington
pesticide law requires most businesses that commercially apply pesticides
to the property of another to be licensed as a Commercial Applicator.
Follow manufacturers' recommendations and label directions. Pesticides
and fertilizers must never be applied if it is raining or about to rain. Do not
apply pesticides within 100 feet of surface waters such as lakes,ponds,
wetlands, and streams. This also can include stormwater conveyance
ditches. Remove weeds/vegetation in stormwater ditches by hand or other
January 2009 King County Stormwater Pollution Prevention Manual
Landscaping Activities and Vegetation Management(continued)
mechanical means. Chemicals should be used as a last resort.
Dispose of grass clippings, leaves,branches, sticks, or other collected
vegetation, by recycling, composting, or burning (if allowed). Do not
dispose of collected vegetation into storm drainage systems, conveyance
ditches, stormwater ponds, or surface water.
Use mulch or other erosion control measures when soils are exposed for
more than one week during the dry season or two days during the rainy
season.
Implement water conservation practices to assure sprinkler systems do not
44overspray"vegetated areas and discharge to hard surfaces such as
sidewalks, driveways, and parking lots. Adjust sprinkler heads accordingly.
Minimize water use so runoff does not occur or enter storm drainage
systems. Use approaches to reduce water use such as those described in the
Natural Yardcare program.
http://your.kingcounty.gov/solidwaste/naturalyardcare/watering.asp
The King County Noxious Weed Control Program provides best
management practices for the removal of typical noxious weeds such as
blackberry and purple loosestrife. Call 206-296-0290 or see
http://www.kingcounty.gov/environment/animalsandplants/noxious-
weeds/weed-control-practices.aspx for more information.
The following BMPs are optional unless the above minimum required
BMPs do not provide adequate source control:
Integrated pest management (IPM), a comprehensive approach to the use of
pesticides is the most effective BMP measure that can be taken for
herbicide, insecticide, and fungicide use.
See BMP Info Sheet 6 in Chapter 5 for information on IPM.
Fertilizers should be worked into the soil rather than dumped or broadcast
onto the surface. Determine the proper fertilizer application for the types of
soil and vegetation involved. Soil should be tested for the correct fertilizer
usage.
Use mechanical methods of vegetation removal rather than applying
herbicides.
King County Stormwater Pollution Prevention Manual January 2009
Landscaping Activities and Vegetation Management(continued)
An effective measure that can be taken to reduce pesticide use, excessive
watering, and removal of dead vegetation involves careful soil mixing and
layering prior to planting. A topsoil mix or composted organic material
should be rototilled into the soil to create a transition layer that encourages
deeper root systems and drought-resistant plants. This practice can improve
the health of planted vegetation, resulting in better disease resistance and
reduced watering requirements.
Use native plants in landscaping.Native plants do not require extensive
fertilizer or pesticide applications.
For more information or assistance in implementing these best management practices,contact the King County
Department of Natural Resources and Parks Water and Land Resources Division at 206-296-1900.
Reader Note: The above requirements are the minimum required BMPs.If these BMPs fail to prevent discharges to
the storm drainage system,you will be asked to take additional measures to correct the continued pollution
discharges.
January 2009 King County Stormwater Pollution Prevention Manual
x. _.
Clearing and Grading of Land for Small Construction Projects
This activity applies if you clear, grade or prepare land for projects. Stormwater runoff from
cleared and graded sites can be loaded with suspended sediments and attached pollutants such as
oils and greases, toxic hydrocarbon and herbicide compounds,metals, and nutrients. Control of
this runoff at the source can prevent large pollutant loadings from entering and degrading
receiving waters. Prior to clearing, grading, and preparation activities for construction sites
greater than 2,000 square feet, the King County Department of Development and Environmental
Services (DDES)must be contacted. You may need to follow the procedures for construction site
erosion and sediment control outlined in the King County Surface Water Design Manual,
Appendix D.
King County DDES coordinates the clearing, grading, and erosion control requirements on
individual sites. The King County Surface Water Design Manual has requirements for erosion
and sediment control measures. Appendix D (Erosion and Sediment Control Standards) outlines
requirements that all sites must implement. The King County Surface Water Design Manual
Appendix C (Small Project Drainage Requirements) addresses small project developments. Even
if your site does not require a permit, erosion control measures are still required to prevent turbid
water from entering drainage systems or surface waters. King County uses the authority of
K.C.C. 9.12 and this manual to develop erosion control requirements for those activities not
covered by the King County Surface Water Design Manual.
For more information or assistance in implementing these best management practices,contact the King County
Department of Natural Resources and Parks Stormwater Services Section at 206-296-1900.
Reader Note: The above requirements are the minimum required BMPs.If these BMPs fail to prevent discharges to
the storm drainage system you will be asked to take additional measures to correct the continued pollution
discharges.
January 2009 King County Stormwater Pollution Prevention Manual
Technical Information Report (TIR)
for
Renton Municipal Airport
Taxiway B System Rehabilitation
Phase II
Owner:
City of Renton
1055 South Grady Way
Renton, WA 98057
October 2012
V D , i
Technical Information Report (TIR)
Renton Municipal Airport
Taxiway B System Rehabilitation
Phase II
October 2012
The engineering material and data contained in this report were prepared under
the supervision and direction of the undersigned,whose seal as a registered
professional engineer is affixed below.
SIN T. S0
Of w�sy��rlr
92
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�fQNAL��
Benjamin Sommer,P.E.
Project Engineer
� 1 1 11 rim
728 134th Street SW,Suite 200
Everett,WA 98204
425-741-3800(Fax 425-741-3900)
File No.232010.007
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - i -
Technical Information Report (TIR)
' 1
Contents
SECTION1: PROJECT OVERVIEW.......................................................................................1
INTRODUCTION..........................................................................................................................................................1
PROJECTDESCRIPTION..............................................................................................................................................I
PROJECTLOCATION...................................................................................................................................................I
EXISTINGSITE CONDITIONS......................................................................................................................................1
PROPOSEDCONDITIONS.............................................................................................................................................2
SOILS.........................................................................................................................................................................2
SECTION 2: CONDITIONS AND REQUIREMENTS SUMMARY....................................14
CORE REQUIREMENT 1: DISCHARGE AT THE NATURAL LOCATION.........................................................................14
CORE REQUIREMENT 2: OFF-SITE ANALYSIS..........................................................................................................14
CORE REQUIREMENT 3: FLOW CONTROL................................................................................................................14
CORE REQUIREMENT 4: CONVEYANCE SYSTEM.....................................................................................................14
CORE REQUIREMENT 5: EROSION AND SEDIMENT CONTROL..................................................................................14
CORE REQUIREMENT 6: MAINTENANCE AND OPERATIONS.....................................................................................14
CORE REQUIREMENT 7: FINANCIAL GUARANTEES AND LIABILITY.........................................................................15
CORE REQUIREMENT 8: WATER QUALITY..............................................................................................................15
SPECIAL REQUIREMENT 1: OTHER ADOPTED AREA-SPECIFIC REQUIREMENTS.......................................................15
SPECIAL REQUIREMENT 2: FLOOD HAZARD AREA DELINEATION...........................................................................16
SPECIAL REQUIREMENT 3: FLOOD PROTECTION FACILITIES...................................................................................16
SPECIAL REQUIREMENT 4: SOURCE CONTROL........................................................................................................16
SPECIAL REQUIREMENT 5: OIL CONTROL...............................................................................................................17
SPECIAL REQUIREMENT 6: AQUIFER PROTECTION AREA........................................................................................17
SECTION 3: OFF-SITE ANALYSIS........................................................................................18
STUDYAREA...........................................................................................................................................................18
RESOURCE REVIEW .........................................................18
FIELDOBSERVATION...............................................................................................................................................19
DRAINAGE SYSTEM DESCRIPTION AND PROBLEM DESCRIPTION.............................................................................20
SECTION 4: FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND
DESIGN........................................................................................................................................23
PARTA-EXISTING SITE HYDROLOGY....................................................................................................................23
PARTB-DEVELOPED SITE HYDROLOGY................................................................................................................23
PART C-PERFORMANCE STANDARDS....................................................................................................................24
PARTD-FLOW CONTROL SYSTEM.........................................................................................................................24
PARTE-WATER QUALITY SYSTEM.......................................................................................................................24
SECTION 5: CONVEYANCE SYSTEM ANALYSIS AND DESIGN..................................28
EXISTINGCONVEYANCE SYSTEM............................................................................................................................28
PROPOSED CONVEYANCE SYSTEM 28
SECTION 6: SPECIAL REPORTS AND STUDIES..............................................................31
SECTION7: OTHER PERMITS..............................................................................................32
SECTION 8: CSWPPP ANALYSIS AND DESIGN................................................................33
ESCMEASURES......................................................................................................................................................33
RECOMMENDED CONSTRUCTION SEQUENCE(EROSION AND SEDIMENT CONTROL)................................................34
SWPPSPLAN DESIGN.............................................................................................................................................35
SECTION 9: BOND QUANTITIES, FACILITY SUMMARIES,AND DECLARATION
OFCOVENANT..........................................................................................................................36
BONDQUANTITIES WORKSHEET.............................................................................................................................36
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - ii -
Technical Information Report (TIR)
FLOW CONTROL AND WATER QUALITY FACILITY SUMMARY SHEET AND SKETCH.................................................36
DECLARATION OF COVENANT FOR PRIVATELY MAINTAINED FLOW CONTROL AND WQ FACILITIES......................36
DECLARATION OF COVENANT FOR PRIVATELY MAINTAINED FLOW CONTROL BMPS............................................36
SECTION 10: OPERATIONS AND MAINTENANCE MANUAL ......................................37
SECTION 11: REFERENCES..................................................................................................38
List of Figures
FIGURE 1-1. TIR WORKSHEET................................................................................................. 4
FIGURE 1-2. VICINITY MAP. .................................................................................................... 9
FIGURE 1-3. DRAINAGE BASIN & SITE CHARACTERISTICS.......................................... 10
FIGURE 1-4. TW B SOIL MAP. ................................................................................................ 11
FIGURE 3-1. OFFSITE ANALYSIS MAP................................................................................. 21
FIGURE 3-2. OFFSITE ANALYSIS DRAINAGE SYSTEM TABLE...................................... 22
FIGURE 4-1. WATER QUALITY BASIN MAP....................................................................... 27
List of Tables
TABLE 1-1. PROJECT SITE LAND COVER DESIGNATION. ................................................ 2
TABLE 2-1. OTHER ADOPTED AREA-SPECIFIC REQUIREMENTS................................. 15
TABLE 4-1. PERFORMANCE STANDARDS.......................................................................... 24
TABLE 4-2. BASIC BIOFILTRATION SWALES.................................................................... 25
TABLE 4-3. WATER QUALITY TREATMENT AREAS........................................................ 25
TABLE 4-4. POLLUTION-GENERATING SURFACE TREATMENT TRADES..................26
TABLE 6-1. SPECIAL REPORTS AND STUDIES. ................................................................. 31
TABLE 7-1. OTHER PERMITS................................................................................................. 32
Appendices
APPENDIX A—GEOTECHNICAL REPORT
APPENDIX B — CITY OF RENTON SENSITIVE AREAS
APPENDIX C—WATER QUALITY CALCULATIONS
APPENDIX D—CONVEYANCE SYSTEM CALCULATIONS
APPENDIX E—BOND QUANTITIES WORKSHEET
APPENDIX F— FLOW CONTROL AND WATER FACILITY SUMMARY SHEET
APPENDIX G—OPERATION AND MAINTENANCE MANUAL
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - iii -
Technical Information Report (TIR)
SECTION 1: PROJECT OVERVIEW
Introduction
The Taxiway B System Rehabilitation project will be constructed in two phases. Phase I,the
north end of the project, will be constructed during the spring and early summer of 2013.
Phase 11, the south end of the project, is scheduled to be constructed in the summer and early fall
of 2013. The following passages describe the project site area for Phase II of the project.
Project Description
Phase II of the project, to rehabilitate and reconstruct the south end of Taxiway B, will employ
various partial or full-depth reconstruction methods. This includes the installation of hot mix
asphalt and Portland Cement Concrete,milling of the existing asphalt pavement surface, and
subsequent overlaying with new asphalt surfacing. New drainage facilities will be constructed to
capture and convey stormwater from the east crowned area of Taxiway B, the apron area east of
Taxiway B,the east crowned area of Runway 16-34, and the turf infield areas between Runway
16-34 and Taxiway B. The facilities for Phase II will be designed in accordance with the City of
Renton's 2010 Amendment to King County's 2009 Surface Water Design Manual (KCSWDM).
A Technical Information Report (TIR) Worksheet was developed for the project to describe the
site area and summarize the proposed drainage features for Phase H. This document is included
as Figure 1-1.
Project Location
The Renton Municipal Airport is located along the eastern side of Parcel Number 0723059007,
within the jurisdiction of the City of Renton. The airport is bounded on the north by Lake
Washington, on the east by Logan Avenue North, on the south by Airport Way, and on the west
by Rainier Avenue North. The Public Land Survey System (PLSS) identifies the area as the
Southwest and Northwest Quarter of Section 7, Township 23 North, Range 5 East. The physical
address of the site is 289 Perimeter Road West, Renton, Washington. The site contains
approximately 169 acres. Figure 1-2 identifies the location of the project site.
Existing Site Conditions
The existing site is fully developed and generally flat across the airfield area. The steepest slope
within the parcel is a 5 percent grade. The site consists of building structures and hangars,
asphalt paving, and grass infield areas. In the area of the project,the taxiway and runway slope
inward toward the grass infield, where surface water is directed, through depressions or swales,
toward catch basins near the western side of Taxiway B. The flow is collected in the catch
basins, diverted through a series of pipes and catch basins, and then discharged through outfalls
along the western side of Cedar River.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 1 -
Technical Information Report(TIR) ' ' ' ' ' '
Proposed Conditions
As discussed previously, Phase I1 of the project proposes to rehabilitate and reconstruct the
southern portion of Taxiway B by employing various partial-depth or full-depth reconstruction
methods. It is anticipated that approximately 6,700 cubic yards of gravel import borrow material
will be required to elevate the renovated taxiway for Phase II. Table 1-1 below identifies the
existing and proposed project site land cover areas.
Table 1-1. Project Site Land Cover Designation.
Area ,
Land Cover Type
(AC)
Untreated Non-targeted Impervious 11.20
Surfacing
Treated Non-targeted Impervious Surfacing 0.49
Replaced Impervious Surfacing 5.42
New Impervious Surfacing 0.05
Pervious Surfacing 7.27
Total 24.43
I
The proposed surface water drainage facilities consist of basic biofiltration swales, filter strips,
catch basins, ductile iron pipe (DIP), and high-density polyethylene (HDPE) pipe. Along the
western side of the crowned taxiway, surface water will drain as sheet flow into the grass infield
area, while runoff from the eastern side of the crowned taxiway is collected in slot drains and
discharged to catch basins. DIP will be used for all instances where storm drainage piping is
required beneath the taxiway surface. For additional information regarding the proposed
development conditions, please refer to Sections 4 and 5 of this report.
Soils
According to the Soil Conservation Service Soil Survey for King County, the soil deposits in the
vicinity of the airport are classified as Urban (Ur). Figure 1-4 identifies the location of the site
for Phase II and its respective soil designation.
A geotechnical report was prepared for this project as part of the design process. The final
version of the report was completed in October 2012, encompassing both Phase I and II work
areas. It appears from the geotechnical exploration that the native subgrade consists
predominately of medium stiff to soft organic silt. The construction of the pavement structure in
the Phase II area was facilitated by the use of fill, ranging from 2.25 to greater than 4 feet in
some localized areas. In general, the fill layers appear to be loose to medium dense and consist of
various material types that are predominately slightly silty to silty gravel with sand to relatively
clean sand with gravel. In the central area of the taxiway, the material appeared to be dredge fill
consisting of sand and gravel with shell fragments, glass, and brick pieces underlying the
pavement section at depth.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 2 -
Technical Information Report (TIR)
The geotechnical exploration identified perched groundwater in 2 of the test pits in the Phase II
work area, ranging from depths of 3.5 to 3.8 feet below the existing ground surface.
Groundwater seepage was observed in several core/hand borings, ranging from 2.7 to 5.5 feet
below the existing ground surface. It is anticipated that the level of groundwater in this area will
fluctuate depending on the season and water height of the adjacent Cedar River. For additional
information regarding the subsurface layers, please refer to the Geotechnical Report in
Appendix A.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 3 -
Technical Information Report (TIR) ` ' '
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
FIGURE 1-1
Part 1 PROJECT OWNER AND Part 2 PROJECT LOCATION AND
PROJECT ENGINEER DESCRIPTION
Project Owner City of Renton Project Name TW B Rehabilitation
Phone (425) 430-7471 DDES Permit#
Address 616 West Perimeter Road, Location Township 23 North
Unit A; Renton, WA 98057 Range 5 East
Project Engineer Benjamin Sommer, PE Section 7
Company Reid Middleton, Inc. Site Address 289 West Perimeter Road
Phone 425 741-3800 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/
El Clearing and Grading ❑ 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 Full / Targeted / Type (circle one): Full / Modified /
(circle): Large Site Small Site
Date (include revision Date (include revision
dates): dates):
Date of Final: Date of Final:
Part 6 ADJUSTMENT APPROVALS
Type (circle one): Standard / Complex / Preapplication / Experimental/ Blanket
Description: (include conditions in TIR Section 2)
N/A
Date of Approval:
2009 Surface Water Design Manual 1/9/2009
1
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL i
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Part 7 MONITORING REQUIREMENTS
Monitoring Required: Yes / No Describe:
Start Date:
Completion Date:
Part 8 SITE COMMUNITY AND DRAINAGE BASIN
Community Plan
Special District Overlays:
Drainage Basin:Lower Cedar River, Cedar Outfall Sub-basin
Stormwater Requirements:
Part 9 ONSITE AND ADJACENT SENSITIVE AREAS
® River/Stream Cedar River ❑ Steep Slope
® Lake Lake Washington ❑ Erosion Hazard
❑ Wetlands ❑ Landslide Hazard
❑ Closed Depression ❑ Coal Mine Hazard
® Floodplain Lake Washington/Cedar River ® Seismic Hazard High Seismic Severity
® Other High Liquefaction Susceptibility ❑ Habitat Protection
Part 10 SOILS
Soil Type Slopes Erosion Potential
Ur
® High Groundwater Table (within 5 feet) ❑ Sole Source Aquifer
❑ Other ❑ Seeps/Springs
❑ Additional Sheets Attached
2009 Surface Water Design Manual 1/9i2009
2
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Part l l DRAINAGE DESIGN LIMITATIONS
REFERENCE LIMITATION /SITE CONSTRAINT
❑ Core 2—Offsite Analysis
® Sensitive/Critical Areas
® SEPA
❑ Other
LJ
❑ Additional Sheets Attached
Part 12 TIR SUMMARY SHEET provide one TIR Summary'Sheet per Threshold Discharge Area
Threshold Discharge Area:
name or description)
Core Requirements (all 8 apply)
Discharge at Natural Location Number of Natural Discharge Locations:
Offsite Analysis Level: 1 / 2 / 3 dated: 09/10/12
Flow Control N/A Level: 1 / 2 / 3 or Exemption Number
(incl. facility summary sheet) Small Site BMPs
Conveyance System Spill containment located at:
Erosion and Sediment Control ESC Site Supervisor: Contractor provide prior to construction.
Contact Phone: Contractor will be selected by public bid.
After Hours Phone:
Maintenance and Operation Responsibility: Private / Public
If Private, Maintenance Log Required: Yes /No
Financial Guarantees and Provided: Yes / No
Liability
Water Quality Type: Basic)/ Sens. Lake / Enhanced Basicm / Bog
(include facility summary sheet) or Exemption No.
Landscape Management Plan: Yes / No
Special Requirements as applicable
Area Specific Drainage Type: CDA/ SDO/MDP/BP/ LMP /Shared Fac. / None
Requirements Name:
Floodplain/Floodway Delineation Type: Major / Minor / Exemption / None
100-year Base Flood Elevation (or range):
Datum:
Flood Protection Facilities Describe: Flood Wall
Source Control Describe landuse: Airport
(comm./industrial landuse) Describe any structural controls:
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: Existin Oil/Water Separator
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 ® Stabilize Exposed Surfaces
® Cover Measures ® Remove and Restore Temporary ESC Facilities
® Perimeter Protection ® Clean and Remove All Silt and Debris, Ensure
® Traffic Area Stabilization Operation of Permanent Facilities
® Sediment Retention ❑ Flag Limits of SAO and open space
preservation areas
® Surface Water Collection Other
® Dewatering Control
® 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 Swale, Filter Strip
❑ Infiltration ❑ Wetpool
❑ Regional Facility ❑ Media Filtration
❑ Shared Facility ❑ Oil Control
❑ Flow Control ® Spill Control CB w/ Tee
BMPs
® Flow Control BMPs Basic Dispersion/
❑ Other
❑ Other Sheet Flow
2009 Surface Water Design Manual 1/9/2009
4
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 N/A ❑ Other N/A
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.
Signed/Date
2009 Surface Water Design Manual 1/9/2009
5
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SCALE IN FEET
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DRAINAGE BASINS & SITE CHARACTERISTICS Figure 1 -3
128 134th Street A We 20) Renton Airport
Evened.WoshuItm 98204
Ph:425 141-3870
Soil Map—King County Area,Washington
(FIGURE 1-4:TW B Soil Map)
N M
N
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558960 559040 559120 559200 559280 559360 559440
47'29'28" z 47'29'28"
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47"29'6"
558960 559040 559120 559200 559280 559360 559440
M Map Scale:1:3,210 if printed on Asize(8.5"x 11")sheet.
� <V
N Meters
n 0 30 60 120 180 v
N Feet
0 100 200 400 600
USDA Natural Resources Web Soil Survey 9/11/2012
Conservation Service National Cooperative Soil Survey Page 1 of 3
Soil Map—King County Area,Washington
(FIGURE 1-4:TW B Soil Map)
MAP LEGEND MAP INFORMATION
Area of Interest(AOI) Very Stony Spot Map Scale: 1:3,210 if printed on A size(8.5"X 11")sheet.
Area of Interest(AOI) Wet Spot The soil surveys that comprise your AOI were mapped at 1:24,000.
Soils
Soil Map Units Other Warning:Soil Map may not be valid at this scale.
Special Point Features Special Line Features= Gully Enlargement of maps beyond the scale of mapping can cause
Blowout misunderstanding of the detail of mapping and accuracy of soil line
Short Steep slope placement.The maps do not show the small areas of contrasting
® Borrow Pit soils that could have been shown at a more detailed scale.
Other
�( Clay Spot
Political Features Please rely on the bar scale on each map sheet for accurate map
Closed Depression 0 Cities measurements.
,X Gravel Pit Water Features Source of Map: Natural Resources Conservation Service
Gravelly Spot Streams and Canals Web Soil Survey URL: hftp://websoilsurvey.nres.usda.gov
Coordinate System: UTM Zone 1ON NAD83
® Landfill Transportation
This product is generated from the USDA-NRCS certified data as of
A. Lava Flow +++ Rails the version date(s)listed below.
A& Marsh or swamp Interstate Highways Soil Survey Area: King County Area,Washington
'X Mine or Quarry iv US Routes Survey Area Data: Version 7,Jul 2,2012
® Miscellaneous Water Major Roads Date(s)aerial images were photographed: 7/24/2006
® Perennial Water N Local Roads The orthophoto or other base map on which the soil lines were
compiled and digitized probably differs from the background
Rock Outcrop imagery displayed on these maps.As a result,some minor shifting
+ Saline Spot of map unit boundaries may be evident.
Sandy Spot
Severely Eroded Spot
0 Sinkhole
3> Slide or Slip
Ar Sodic Spot
11 Spoil Area
d Stony Spot
I;SDA Natural Resources Web Soil Survey 9/11/2012
Conservation Service National Cooperative Soil Survev Page 2 of 3
Soil Map—King County Area,Washington FIGURE 1-4:TW B Soil Map
Map Unit Legend
King County Area,Washington(WA633)
Map Unit Symbol Map Unit Name Acres in AOI Percent of AOI
Ur Urban land 19.4 100.0%
Totals for Area of Interest 19.4 100.0%
USDA Natural Resources Web Soil Survey 9/11/2012
'� Conservation Service National Cooperative Soil Survey Page 3 of 3
SECTION 2: CONDITIONS AND REQUIREMENTS SUMMARY
The following describes how the Core and Special Requirements from the City of Renton's 2010
SWDM Amendment apply to this project.
Core Requirement 1: Discharge at the Natural Location
The project will not alter the stormwater discharge locations. For additional information on the
discharge points, refer to Section 3, Off-site Analysis.
Core Requirement 2: Off-site Analysis
A Downstream Drainage Inventory is addressed in Section 3, Off-site Analysis.
Core Requirement 3: Flow Control
Flow control facilities are not proposed for this project. The project site discharges directly into
Cedar River, downstream of the Taylor Creek confluence and within the backwater of Lake
Washington. All new stormwater conveyance facilities have been designed to meet the discharge
requirements as outlined in the "Direct Discharge Exemption" section of the City of Renton's
SWDM Amendment.
Best Management Practices (BMPs) for flow control are used on the project site. These measures
typically consist of basic dispersion through sheet flow along the impervious taxiway surfacing.
These measures shall be installed in accordance with the requirements of the KCSWDM,
Appendix C.2.4.5.
Core Requirement 4: Conveyance System
The Rational Method and Manning's Equation were utilized to design and size the piping
facilities. All new stormwater conveyance systems were reviewed in relation to the 25- and 100-
year peak runoff events. For additional information on the conveyance system design, refer to
Section 4, Flow Control and Water Quality Facility Analysis and Design.
Core Requirement 5: Erosion and Sediment Control
An Erosion and Sediment Control (ESC) plan has been developed for this project. A detailed
summary of the required ESC measures can be found in Section 8, CSWPPP Analysis and
Design.
Core Requirement 6: Maintenance and Operations
Maintenance and operations of the proposed drainage facilities will be performed in compliance
with King County's Appendix A, Maintenance Requirements for Flow Control, Conveyance, and
WQ Facilities. Maintenance requirements for all applicable facilities have been included in
Appendix G.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 14 -
Technical Information Report (TIR)
Core Requirement 7: Financial Guarantees and Liability
The Bond Quantity Worksheet and Flow Control and Water Facility Summary Sheet are
provided as part of Section 9, Bond Quantities, Facility Summaries, and Declaration of
Covenant. However, Declarations of Covenants are not required for this project since the City of
Renton owns and maintains the facilities. For additional information on these items, refer to
Appendix E, Bond Quantity Worksheet, and Appendix F, Flow Control and Water Facility
Summary Sheet.
I
Core Requirement 8: Water Quality
1
"Basic Water Quality"treatment standards apply to the project site. In order to meet these
standard requirements,basic biofiltration swales and filter strips will be used. A summary of the
water quality design facilities can be found in Section 4, Flow Control and Water Quality
Facility Analysis and Design.
Special Requirement 1: Other Adopted Area-Specific Requirements
A summary of other adopted area-specific requirements associated with the project site is -
presented in Table 2-1.
Table 2-1. Other Adopted Area-Specific Requirements.
Regulations Required Comment
Master Drainage Plans(MDPs) No
Basin Plans(BPs) Yes King County's Lower Cedar River Basin Plan
Salmon Conservation Plans(SCPs) Yes WRIA 8 Cedar-Sammamish
Stormwater Compliance Plans(SWCPs) Yes National Pollutant Discharge Elimination System
DES Phase II
Flood Hazard Reduction Plan Updates FHRPs yes City's Critical Area Code RMC 1V-4-3-050
Shared Facility Drainage Plans(SFDPs) No
A review of the specific drainage requirements, mandated by the area-specific requirements, has
been conducted. Any applicable regulations that were more stringent than the City of Renton's
SWDM Amendment have been applied to the proposed facilities.
From the review of the City of Renton 2009 Storm Water Management Program (SWMP) for the
NPDES Phase II, it was identified that an evaluation by City of Renton staff determined the
Renton Municipal Airport required an Industrial Facility NPDES Permit. It is our understanding,
from discussions with Airport staff,that the specific NPDES Permit has not been completed for
the facility at this time. However, a Stormwater Pollution Prevention Plan (SWPPP) for
construction activities will be developed as part of this overall project.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 15 -
Technical Information Report (TIR)
Special Requirement 2: Flood Hazard Area Delineation
The proposed project is not within the 100-year floodplain; therefore, delineation is not identified
on the improvement plans.
Special Requirement 3: Flood Protection Facilities
The site possesses an existing flood protection wall east of Taxiway B. The proposed
improvements are not within the area of this facility nor do they include any upgrades to this
structure.
Special Requirement 4: Source Control
This Special Requirement is not necessary, since the project does not require a commercial
building or site development permit; however, it is included as part of this document. The
ongoing and future source control measures proposed for the project will comply with the City of
Renton's SWDM Amendment and King County's Stormwater Pollution Prevention Manual. The
following BMPs are specific to the proposed improvements:
Structural Source Control Measures
A-27: A Temporary Erosion and Sediment Control (TESL) plan has been developed for
the project site. TESC facilities shall be installed prior to any on-site grading activities.
Excessive amounts of surface water will be collected and pumped to a flow dispersal
system in order to prevent suspended sediments and potential oils from clogging the
TESC measures or being conveyed downstream. All proposed measures are in
conformance with the City of Renton's SWDM Amendment. The plan includes,but is
not limited to: check dams, bio-filter bags, straw wattles, catch basin sediment traps, and
covering of exposed soils.
Nonstructural Source Control Measures
A-17: Fueling operations for the construction equipment will occur on site. All fueling
will be conducted away from standing surface water in order to prevent possible release
into the drainage system. If a spill does occur during construction, the Contractor shall
contain and expose of contaminated materials in accordance with local and state
requirements.
A-26: Landscaping activities will practice the following BMPs: Chemicals will not be
applied directly to surface water, all manufacturers' recommendations and label
directions will be followed, and vegetation will not be disposed of in waterways or
drainage systems. Mulch or other erosion control measures will be utilized when soils are
exposed for more than one week during the dry season and two days during the rainy
season. Noxious plants will be avoided.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 16 -
Technical Information Report (TIR) 1.'Mr.17 ir, 'I ` '
The proposed operation and maintenance guidelines for the above facilities have been included
in Appendix G, Operation and Maintenance Manual, in accordance with King County's
Stormwater Pollution Prevention Manual.
Special Requirement 5: Oil Control
The proposed improvements do not meet the definition of a high-use site requiring oil control;
however, within the project construction area, an existing oil/water separator is currently utilized.
At this time, it is anticipated that the existing structure will be left in place and continue to
provide treatment for flows through an existing 12-inch-diameter outfall.
Special Requirement 6: Aquifer Protection Area
The project site is not located within an Aquifer Protection Zone; therefore, protection facilities
will not be provided.
i
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 17 -
Technical Information Report (TIR) ' ' '
SECTION 3: OFF-SITE ANALYSIS
A quantitative downstream, or off-site analysis, survey was conducted at and adjacent to the
project site. The analysis of the project area consisted of four main tasks: a review of the Study
Area, a Resource Review, a Field Inspection, and a Drainage System Description and Problem
Description write-up.
Study Area
A review of the project site was conducted, extending three-quarters of a mile downstream of the
natural discharge location and a quarter of a mile upstream. It was not feasible to extend the
inspection to the required one mile downstream, since Cedar River discharges directly into Lake
Washington in less than that distance.
The purpose of this review is to identify the project site's impacts on the drainage area tributary
flow path. For this particular site, the surface water is conveyed from the infield runway/taxiway
area through catch basins to 12- and 18-inch-diameter pipe outfalls. The flow is discharged to
Cedar River and carried to Lake Washington, less than three-quarters of a mile downstream.
Resource Review
A review of the applicable reports and studies of the general project area was included in the
off-site analysis. The coverage area consisted of the property a quarter of a mile upstream and
three-quarters of a mile downstream of the site. The City of Renton's SWDM Amendment
requires that the following reference materials are reviewed:
• Sensitive Areas Folio
• Adopted Basin Plans/Basin Reconnaissance Summary Reports
• Floodplain/Floodway (FEMA) Maps
• King County Soil Survey
• Washington State Department of Ecology's (DOE) Polluted Waters List
• City of Renton Erosion Maps and Landslide Maps
• Wetlands Inventory Maps
From the evaluation of these reference materials, existing or potential issues were identified and
noted for the field inspection. The research identified the following sensitive areas within the
area of study: flood hazard, seismic hazard, and high liquefaction hazard. Upstream of the
project site, the adjacent properties are within Aquifer Protection Zone 1 and possess a moderate
to high susceptibility to liquefaction. Applicable maps of the City of Renton Sensitive Areas are
included in Appendix B of this report.
The Renton Municipal Airport is located within the Lower Cedar River Basin and Cedar Outfall
Subbasin. King County has developed a Lower Cedar River Basin Plan that provides an
overview of the area and proposes solutions to the issues of flooding, property damage, and
declining salmon and steelhead runs. Additionally, the plan recommends preventative measures
for maintaining water quality standards, groundwater supplies, and natural habitat within the
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 18 -
Technical Information Report (TIR) ` ' '
I
basin. From the review of this document, it was noted that damage occurred to public facilities at
the airport during flood events in 1990 and 1995. The plan also identified that the overall water
quality in the river is"generally very good"; however, it stated that sporadic exceedances of the
water standards have been recorded from fecal coliform bacteria generated by livestock and
failing septic tanks. It does not appear that the airport is a major contributor to these pollutants
within the river.
A review of the DOE's list of polluted waters (Section 303d) was conducted for Cedar River and
Lake Washington. This investigation identified that the project site discharges to a section of
Cedar River labeled as Category 5 Waters, which conveys flow directly downstream to an area
of Lake Washington marked as Category 2 Waters. A Category 2 label identifies water bodies
that are areas of concern for the DOE. This typically indicates waters where there is some
evidence of water quality issues but not enough to require a water quality improvements project.
However, a Category 5 designation marks a waterway violating one or more pollutant standards.
This information was considered when selecting water quality facilities for the project site.
A review of the City of Renton's Erosion and Landslide Maps identified adjacent properties west
of the airport property as carrying a potential for erosion hazards and landslide hazard
designations ranging from moderate to very high. The airport itself is relatively flat and not
directly impacted by the landslide hazard areas.
An evaluation of the City of Renton's Wetland Inventory Map was conducted for the project.
From the review, it did not appear that there were any documented wetlands on or within the
vicinity of the airport facility. No wetland areas have been observed during previous visits to the
site.
Field Observation
A Level 1 field observation was conducted at the project site on September 10 and 12, 2012. The
weather was clear and sunny during this observation. The observation encompassed an
evaluation of existing catch basins within the proposed project area and near the flood wall
(upstream of the outfalls), as well as the existing outfalls. The downstream analysis extended
from the final discharge location to a point less than three-quarters of a mile downstream.
The site's discharge piping extends east of Taxiway B to the outfall locations along Cedar River.
All existing outfalls are corrugated metal pipe (CMP) and fitted with `duckbill' style check
valves. The location of the 18-inch-diameter outfall was uncovered within Cedar River; however,
the 12-inch-diameter outfall from the on-site oil/water separator was not found. No signs of
erosion, overtopping, or scouring were observed in the general vicinity of the outfalls or in the
upstream catch basins. Please see Figure 3-1 for additional information and a depiction of the
off-site analysis area.
As is the case for Phase I of the project, the existing conveyance system and outfall piping are
undersized for the peak runoff events as calculated by the Rational Method. This evaluation is
documented in Section 5, Conveyance System Analysis and Design.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 19 -
Technical Information Report (TIR)
Drainage System Description and Problem Description
The drainage system is combined within one Threshold Discharge Area due to the outfalls being
located less than a quarter of a mile apart. The flow is conveyed into Lake Washington, less than
three-quarters of a mile downstream.
The field observation did not uncover signs of existing drainage system issues. See Figure 3-2,
Off-site Analysis Drainage System Table, for an outline of the items noted during the field
observation.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 20 -
Technical Information Report (TIR) E= ' ' ' '
i
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LEGEND:
REPLACED/NEW
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FLOW DIRECTION
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OFFSITE ANALYSIS MAP Figure 3-1
Renton Airport
723 134th Stint SR Silt 200
Evmt J� on 9M4
Po:425 741-3800
w� w rw it r rw w r r� r r r r� r r r r r rr
OFF-SITE ANALYSIS DRAINAGE SYSTEM TABLE
SURFACE WATER DESIGN MANUAL, CORE REQUIREMENT#2
FIGURE 3-2
Basin: Lower Cedar River Subbasin Name: Cedar Outfall Subbasin Number:
Symbol Drainage Drainage Slope Distance Existing Potential Observation of field
Component Type, Component from site Problems Problems inspector,resource
Name,and Size Description discharge reviewer,or resident
see map Type sheet flow,Swale, drainage basin,vegetation, % 1/4 rni=1,320 lt, constrictions,under capacity,ponding, tributary area,likelihood of problem,
stream,channel,pipe, cover,depth,type of sensitive overtopping,flooding,habitat or oganism overflow pathways,potential impacts
pond,Size:diameter, area,volume destruction,scouring,bank sloughing,
surface area sedimentation incision,other erosion
A Discharge Location 1'to 2'Depth of Channel N/A U it None None No evidence of erosion
B River Channel/Lake Bed 5'to 6'Depth ol'Channel N/A 2000 ft None None No evidence of erosion
23-2010.007 Page 1 of 1 Offsite Drainage System
June 2012 Renton Municipal Airport City of Renton
' SECTION 4: FLOW CONTROL AND WATER QUALITY FACILITY
ANALYSIS AND DESIGN
The proposed site area consists of one subbasin broken into two parts for the existing and
1 developed site hydrology. The subbasin is defined according to the existing topography and on-
site drainage facilities. The following sections will discuss areas in greater detail as they relate to
the existing or developed site hydrology.
' Part A—Existing Site Hydrology
The project area is located in the southeast region of the City of Renton's Municipal Airport.
Taxiway B is bordered by Runway 16-34 to the west and Boeing's aircraft manufacturing
stations (concrete hardstands) on the east. The project site consists of approximately 24 acres of
predominately developed land area. The project site consists of one subbasin for the design of the
stormwater facilities,but is broken into two areas due to an existing catch basin splitting flow
between two outfalls. The subbasin area was determined by reviewing the existing topography
and drainage facilities. A breakdown of the existing and proposed land cover within the area is
presented in Table 1-1.
The existing taxiway surface consists of impervious asphalt underlain by a compacted gravel
subgrade. From the geotechnical investigation conducted for this project, it appears that the
native subgrade consists predominately of medium stiff to soft organic silt. Please refer to
' Section 1 for a detailed explanation of the geotechnical exploration.
The site area is graded to drain to catch basins within the grassy infield area. Flow is conveyed
from these basins to the 12- and 18-inch-diameter outfalls, along the eastern edge of the site, into
Cedar River. Please refer to Figures 1-3 and 3-1 for more information on the delineation, flow
path, and acreage of areas contributing runoff to the existing project site.
iPart B—Developed Site Hydrology
The developed site hydrology consists of one subbasin broken into two areas, as identified in the
existing site hydrology review. All areas drain from the infield grass surface through the outfalls
along the eastern side of the site.
The proposed water quality facilities consist of basic biofiltration swales, filter strips, and flow
splitters. Flow splitters are required to divert the runoff into two flows: water quality and bypass
flow. The bypasses account for flows greater than the calculated water quality flow/volume for
the developed conditions. Water quality treatment will consist of a combination of filter strips
and basic biofiltration swales. These facilities are further detailed in Part E below.
' Flow control facilities, as discussed previously, are not required for this project. Flow control
BMPs will be used where appropriate or necessary. A discussion of these facilities can be found
in Part D below.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase Il - 23 -
Technical Information Report (TIR) ' ' '
Part C —Performance Standards
A summary of flow control, conveyance, water quality, and source and oil control performance ,
standards for the project is presented in Table 4-1. Calculation documents are provided in
Appendices C and D for the applicable standards.
Table 4-1. Performance Standards.
Category Performance Standards Source ,
Flow Control Flow control facilities are not required. Manual Section 1.2.3.1
Flow Control BMPs required.
Conveyance System Capacity Developed 25-year Peak Storm Event Manual Section 1.2.4.1
Basic Treatment of the 2-year Storm Manual Section 1.2.8.1
Event for developed conditions Manual Section 6.2.1
Water Quality Treatment i
Basic Biofiltration Swales Manual Section 6.3.1
Basic Filter Strips Manual Section 6.3.4 '
Source Control Stormwater Pollution Prevention Manual Manual Section 1.3.4
Oil Control N/A Manual Section 1.3.5
Part D—Flow Control System
As discussed in Core Requirement 3, Flow Control, the project site is exempt from providing
flow control facilities since the site discharges directly to a major receiving water body.
Therefore, flow control design and analysis are not included as part of this report.
Flow control BMPs will be installed where appropriate or necessary. These measures typically
consist of"Basic Dispersion"through sheet flow.
Part E—Water Quality System
Proposed Treatment System '
The project site appears to fall within the description of"Basic Treatment" as defined by
KCSWDM. Properties subject to this type of treatment are areas draining outside the drainage ,
basin of sensitive lakes or sphagnum bog wetlands. The Basic Treatment standard intends to
remove 80 percent of the TSS for flows or volumes up to the water quality design flow or
volume. The remaining flow quantity is diverted around water quality facilities and passes '
untreated through the system.
The KCSWDM requires that all water quality measures treat a minimum of 95 percent of the ,
annual average runoff volume in the 8-year time series, as determined by the King County
Resource Time Series (KCRTS) model. The designs of the facilities at the site are based on
treating 60 percent of the 2-year Peak Flow rates for a given targeted surface area. At this design
flow rate, the system will successfully treat the minimum required volume.
Renton Municipal Airport October 2012 '
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The project's surface water quality facilities consist of a combination of basic biofiltration
swales and filter strips. Filter strips generally bound the western side of Taxiway B to treat sheet
flow, while biofiltration swales are provided to treat the concentrated flows from the eastern
crowned sections of Subbasin A-1. The flow in this area is collected and conveyed from the
eastern side of the (crowned) taxiway to the grass infield west of Taxiway B. Table 4-2 identifies
the design information for the basic biofiltration swale.
Table 4-2. Basic Biofiltration Swales.
Area Length Bottom Width Side Slope Longitudinal Slope Design Flow
(FT) (FT) (FT) (FT/FT) (CFS)
South 100 10.0 4H:1 V 0.010 0.29
Bioswale
North 100 10.0 4H:1 V 0.010 0.29
Bioswale
Flow splitters are proposed upstream of the basic biofiltration swales to control the rate of flow
through the facilities. The flow splitters have been designed to allow the required water
flow/volume for water treatment to pass through the basic biofiltration swales. The remaining
water volume will be diverted through a bypass system that runs parallel to the swales in below-
grade piping systems. The calculations for sizing the flow splitters have been included in
Appendix F, Water Quality Calculations.
A breakdown of the water quality areas within each section of the subbasin is defined in
Table 4-3. Calculations and computer printouts for these facilities have been included as
Appendix C, Water Quality Calculations. The locations of the water quality facilities are
identified on Figure 4-1 and on the construction plans.
Table 4-3. Water Quality Treatment Areas.
Treatment Type Subbasin A-1 Subbasin A-2
(SF) (SF)
Area Treated by Filter Strip 110,875 3,990
Untreated Target Area 34,520 22,620
Area Treated by Basic Biofiltration Swales 87,500* 0
Total 232,895 26,610
*Area includes Non-Target Tributary Area being treated(21,370 SF)
Treatment Trades
The City of Renton's SWDM Amendment, Section 1.2.8.2.C, identifies that runoff from
pollution-generating surfaces may be released untreated if an existing non-targeted pollution-
generating surface of equivalent size and pollutant characteristics within the same watershed or
stream reach tributary area is treated on the project site. It is understood that this provision is
included as part of the manual to allow the designer flexibility to trade regions of target areas
that are not feasible to treat with water quality facilities.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 25 -
Technical Information Report (TIR)
In Phase II of the project, there are three target areas where it is not feasible to treat surface
runoff. In order to offset these untreated target areas, additional area east of Taxiway B, within
Boeing's concrete hardstand area, has been added to the two basic biofiltration swales in
Phase lI. This hardstand area is not currently being treated.
From Phase I of the project, the water quality measures treated an additional 62,200 square feet
of non-target surfacing (Subbasin C). The outfalls from Phase 11 (both A-1 and A-2) and the
outfall for Subbasin C in Phase I are all within a single threshold discharge area. Therefore, the
overall project proposes to treat a total net of 26,500 square feet of non-target areas. Table 4-4
breaks down the total non-target pollution-generating surfaces proposed for treatment trades by
the individual subbasin areas.
Table 4-4. Pollution-Generating Surface Treatment Trades.
Drainage Basin Treated Non-Target Area Untreated Target Area
(SF) (SF)
Subbasin A-1 0 34,520
Subbasin A-2 21,370 22,620
Phase I Total 66,790 4,575
Total 88,160 61,715
Please refer to Figure 4-1 for the proposed treatment traded areas for Phase II. Water quality
BMPs will be provided in these locations of untreated target areas to the extent possible.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase 11 - 26 -
Technical Information Report (TIR) ' " '
I
EXISTING ASPHALT
(RUNWAY 16-34)
-" SUB-BASIN A-1
- - I SUB-BASIN A-2
TAXIWAY B7 (N) AREA.
- n
IMPERVIOUS = 14,750 S
y� SOUTHfi
BIOFILTRATION
TAXIWAY 87 (S) AREA SWALE(10'x 100') NORTH
IMPERVIOUS = 7,220 SF ' SWALE(10'x on)WET N /
SOUTH FILTER STRIP AREA
IMPERVIOUS - 26,215 SF
u
TAXIWAY B6( 'TAXIWAY B6 N
10,650 SF -TAXIWA
Y
1 r =_ -- � .TAXIWAY B FILTER STRIP.AREA - 15,710 SF ( >., 3,990 SF
r IMPERVIOUS = 28.100 SF I
UNTREATED TARGET AREA -- AREA
IMPERVIOUS = 14,480 SF TAXIWAY 8
rn GET AREA
SOUTH BIOSWALE AREA NORTH BIOSWALE AREA UNTREATED TARGET AREA 22,620 SF
IMPERVIOUS 43,680 SF IMPERVIOUS 43.820 SF _ -IMPERVIOUS 20,040 SF- OUTFALL PIPE
TO RIVER
IPE
I / TO RIVER
AREA BOUNDARY J CROWNED TAXIWAY J
NON—TARGET TRIBUTARY AREA SLOT DRAIN
(NP) CENTERLINE IMPERVIOUS = 21,370 SF
i
EXISTING CONCRETE
(HARD STANDS)
LEGEND:
WATER QUALITY
FILTER STRIP
TREATED NON-TARGET
AREA
—� SWALE
SUB-BASIN BOUNDARY
�— FLOW DIRECTION ARROW
WATER QUALITY TREATMENT BY SUB—BASIN POLLUTION—GENERATING SURFACE TREATMENT TRADE
SUB—BASIN A-1 SUB—BASIN A-2 TREATED NON—TARGET AREA UNTREATED TARGET AREA
TREATMENT TYPE (SF) (SF) DRAINAGE BASIN (SF) (SF)
AREA TREATED BY FILTER STRIP 110,875 3,990 SUB-BASIN A-1 21,370 34,520
UNTREATED TARGET AREA 34,520 22,620 SUB-BASIN A-2 0 22,620 Amw
AREA TREATED BY BIOSWALE 87,500- 0 TOTAL FROM PHASE 1 PROJECT 66,790• 4,575•
TOTAL 232.895 26,610 TOTAL 88,160 61,715
• AREA INCLUDES NON-TARGET TRIBUTARY AREA (21,370 SF). ' SEE FIG. 4-2 OF PHASE 1 TIR. SCALE IN FEET
WATER QUALITY FLOW RATES AND SIZING CALCULATIONS INCLUDED IN APPENDIX C.
60 0 60 120
WATER QUALITY BASIN MAP Figure 4-1
228 1341h Wee(Sl Sub 200 Renton Airport
EwdL Wm*tm 9M
Ph 425 741-M
SECTION 5: CONVEYANCE SYSTEM ANALYSIS AND DESIGN
An evaluation of the existing and proposed conveyance systems was conducted for this project.
This section provides an overview of the existing and proposed conveyance systems and outlines
the criteria utilized in design of the drainage facilities.
Existing Conveyance System
The existing storm drainage conveyance system was analyzed for conveyance of the 25- and
100-year peak storm runoff events for instances where the flow characteristics were changed due
to the proposed project. The existing conveyance system consists of swales, depressions, catch
basins, outfalls, and various types of storm piping. The outfalls are 12- and 18-inch-diameter,
reinforced concrete and corrugated steel pipelines that are relatively flat in nature. These
structures inhibit the capacity of the entire system, requiring the use of hydraulic head to
adequately drain the site after large storm events.
As discussed in the TIR for Phase 1, the Airport is planning to develop a Capital Improvements
Projects (CIP) program to address existing storm drainage facilities on the site. The staff intends
to include the replacement of the existing outfalls to Cedar River as part of the CIP program in
order to correct this potential issue from the peak runoff storm events. Calculations for the
existing and proposed conveyance systems have been included in Appendix C.
Proposed Conveyance System
Proposed System Review
The proposed conveyance system intends to replace/relocate storm drainage facilities within the
areas of excavation. The Rational Method was used to determine the peak storm runoff events,
while Manning's Equation was utilized to size the conveyance system. The proposed facilities
are constrained by the invert elevations of the existing outfall system and the relatively flat
terrain of the site. The piping system was designed to fit the site limitations and convey flow to
the existing outfall elevations.
Following this design path, the proposed conveyance system does not appear to pass the 25- and
100-year peak runoff event through a portion of the system, as determined by the Rational
Method. The existing drainage piping in the infield area was upsized to 18-inch-diameter piping
to alleviate the potential of overtopping structures from the peak event. However, upsizing
beyond this diameter or steepening the slope of the facilities was not feasible due to the site
constraints and lack of cover over the pipes. As is the case in Phase 1, the proposed drainage
system will require the use of hydraulic head from backwatering into upstream structures to
ecompletely drain the area.
The conveyance system consists of pipes, culverts, catch basins, berms, and swales. Flow from
the non-target impervious surfacing (Runway 16-34), along the western edge of the project site,
will drain as sheet flow from the edge of the pavement and follow the sloped shoulder area
toward the middle of the infield. The infield will be sloped to direct the runway flow away from
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 28 - ��
Technical Information Report (TIR) '+'�`;+�i[ ' ' . '
the basic biofiltration swales, which treat the concentrated flows from the eastern side of the
crowned taxiway. The flow from the runway non-target impervious area will be routed to catch
basins just north of these water quality facilities and conveyed through a series of pipes and catch
basins before discharging through the outfalls.
Flow from the western crowned taxiway surface will generally drain as sheet flow into the
infield area. Basic filter strips are proposed along the entire length of the infield along the
western edge of Taxiway B. The runoff will travel above grade to the center of the infield area
and be directed to catch basins. From there, the flow will be diverted through a series of pipes
and catch basins before discharging through the outfalls.
The eastern crowned taxiway surface will be graded and paved in a manner that directs surface
water to a slot drain along the eastern edge of the project area. The flow will be conveyed
through the slot drains and pipelines to flow splitter catch basins. The flow splitters will divert
the required flow/volume for water quality within each subbasin, while the remaining
flow/volume will be diverted to a bypass system. The portion of the flow required for water
quality will be conveyed within the biofiltration swales to a collection catch basin. The bypass
flow will travel parallel to the swales through a series of pipes and catch basins. The flow will be
combined in a collection catch basin north of each basic biofiltration swale. From this location,
the flow will be conveyed through a series of pipes and catch basins and then discharged through
the outfalls. For further information regarding these facilities,please refer to Appendix C and the
project plans.
Shallow Pipe Loading
Thickness design for DIP was performed on drainage lines crossing beneath Taxiway B at
shallow depths, typically less than 3 feet of cover. The method used for the design was obtained
from ANSI/AWWA C I 50/A21.50-20, Thickness Design of Ductile Iron Pipe. There were
4 scenarios reviewed where the crossings possessed cover less than 3 feet: 12-inch DIP at 1 foot,
18-inch DIP at 1 foot, 12-inch DIP at 1.5 feet, and 18-inch DIP at 2 feet. The vehicle loading on
the pipelines was based on the design vehicle, a 737-800 aircraft weighing approximately
130,000 pounds. From the calculations performed, the following conclusions were made:
• 12-inch DIP at 1 foot: a minimum Special Class 54 is required
• 18-inch DIP at 1 foot: a minimum Special Class 55 is required
• 12-inch DIP at 1.5 feet: a minimum Special Class 52 is required
• 18-inch DIP at 2 feet: a minimum Special Class 50 is required
The design specifications for the project will reflect these requirements for any instances where
they may occur. Please refer to Appendix D for the thickness design calculations.
Spill Control Measures
Spill control measures, in accordance with the City of Renton's SWDM Amendment
requirements, have been included as part of the storm drainage facilities. These measures include
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 29 -
Technical Information Report (TIR) ' ' '
placing inverted tee or elbow sections in the final discharge catch basins within the project site.
Locations and details of these facilities are identified in the project plan set.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 30 -
Technical Information Report (TIR) ' `
SECTION 6: SPECIAL REPORTS AND STUDIES
Table 6-1 summarizes the Special Reports and Studies required for this project site.
Table 6-1. Special Reports and Studies.
Study/Report Date Conducted Appendix
Floodplain Delineation(Section 1.3.2) N/A N/A
Flood Protection Facility Conformance(Section 1.3.3) N/A N/A
Critical Areas Analysis and Delineation N/A N/A
Geotechnical/Soils 04/27/12 Appendix A
Groundwater N/A N/A
Slope Protection/Stability N/A N/A
Erosion and Deposition N/A N/A
Geology N/A N/A
Hydrology N/A N/A
Fluvial Geomorphology N/A N/A
Anadromous Fisheries Impacts N/A N/A
Water Quality N/A N/A
Structural Design N/A N/A
Structural Fill N/A N/A
Aquifer Protection Areas N/A N/A
Renton Municipal Airport October 2012
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Technical Information Report (TIR) LX4,T, ' 'I ' '
SECTION 7: OTHER PERMITS
Table 7-1 summarizes other permits required for the project site.
Table 7-1. Other Permits.
Permit Required Regulating Agency
On-site Sewage Disposal No Seattle/King County Department of Public Health
Well Permits No Seattle/King County Department of Public Health
Developer/Local Agency Agreement No Washington State Department of Transportation
Hydraulic Project Approval No Washington State Department of Fish and Wildlife
Short-term Water Quality Modification Approval No Washington State Department of Ecology
Dam Safety Permit No Washington State Department of Ecology
NPDES Stormwater Permit Yes Washington State Department of Ecology
Forest Practices Class IV Permit No Washington State Department of Natural Resources
Sections 10,401,and 404 Permits No United States Army Corps of Engineers
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 32 -
Technical Information Report (TIR)
SECTION 8: CSWPPP ANALYSIS AND DESIGN
A Construction Stormwater Pollution Prevention Plan (CSWPPP) has been developed as an
element of this report. This plan is composed of an Erosion Sediment Control (ESC) plan and a
Stormwater Pollution Prevention and Spill (SWPPS) plan.
ESC Measures
Phase II of the project will be constructed during the summer and early fall of 2013. Rainfall
accumulation during this period of the year is minimal. The site is relatively flat and the majority
of the work is on or near asphalt surfacing; therefore, erosion potential is anticipated to be very
low. Standard erosion control measures will be implemented to control sediment in the
construction area. However, additional measures will be introduced to provide added protection
against sediment transport due to the airport's close proximity to Cedar River and Lake
Washington. The following is a description of the standard and nonstandard erosion control
measures being implemented for Phase II of this project.
ESC Requirement 1: Clearing Limits
The limits of work are identified on the project plans. It is anticipated that the Contractor will
physically mark the limits of work during construction.
ESC Requirement 2: Cover Measures
The Contractor will be required to cover any exposed soils by temporary or permanent means.
Guidelines for cover measures are defined in the ESC Notes on the plans.
ESC Requirement 3: Perimeter Protection
Filter fabric fencing shall be installed down-gradient from any construction activity to prevent
the transportation of sediment to Cedar River or Lake Washington. Fencing materials will be
specified to meet the KCSWDM requirements. Typically, such structures consist of filter fabric,
possess a wire mesh backing, and are buried approximately 8 inches below grade. The
Contractor shall inspect the fence on a weekly basis. Any damage to the structure shall be
repaired immediately. If soil near the barrier is roughly 6 inches high, the sediment shall be
removed and stabilized on site.
ESC Requirement 4: Traffic Area Stabilization
Temporary construction entrances may be installed at various locations along the taxiway
reconstruction to reduce sediment transport onto the adjacent paved surfaces.
ESC Requirement 5: Sediment Retention
Check dams and bio-filter bags will be installed within existing swales and around certain catch
basins to protect downstream conveyance systems from sediment accumulation. Straw wattles
will also be used downstream of any soil disturbance that is tributary to existing catch basins.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 33 -
Technical Information Report (TIR)
Catch basin sediment trap filters will be installed in existing and proposed catch basins to protect
drain inlet structures and reduce sediment in downstream conveyance systems.
All temporary and permanent erosion and sediment control BMPs shall be maintained and
repaired as needed to ensure continued performance of their intended function. All maintenance
and repair shall be conducted in accordance with BMPs. Sediment control BMPs shall be
inspected weekly or after a runoff-producing storm event during the dry season and daily during
the wet season.
ESC Requirement 6: Sui face Water Collection
In addition to the traditional BMPs mentioned above, two of the existing catch basins that drain
to the Cedar River will be equipped with a pump and flow dispersal system. The outlet pipes
from the catch basins will be plugged and a temporary sump pump will be installed to convey
runoff to a length of 6-inch perforated pipe placed on undisturbed vegetation. Sediment will
settle in the catch basin and the runoff will be dispersed through the existing vegetation
downstream.
ESCRequirement 7: Dewatering Control
The Contractor shall dewater excavated areas that exhibit excessive water levels from ground or
surface water. Temporary pumping and dispersal equipment shall be used to disperse the flow to
existing vegetation areas downstream of the excavations. Sediment transport shall not be allowed
to bypass existing or proposed stormwater facilities that are fitted with sediment retention
measures.
ESCRequirement 8: Dust Control
The Contractor shall control dust to prevent sediment transport from exposed, dry surfaces to the
adjacent waterways. It is anticipated that the Contractor will use water in these areas; however,
the KCSWDM also allows the Contractor to utilize calcium chloride, magnesium chloride, lignin
derivatives, tree resin emulsions, and synthetic polymer emulsions as other means of suppressing
dust from the project.
ESC Requirement 9: Flow Control
The Contractor shall be responsible for drainage control at all times. The Contractor shall protect
all work, existing facilities, and adjacent properties and water bodies from erosion and siltation
transportation during construction.
Recommended Construction Sequence (Erosion and Sediment Control)
1. Attend preconstruction meeting.
2. Post sign with name and phone number of ESC supervisor.
3. Grade and install construction entrance(s).
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase 11 - 34 -
Technical Information Report (TIR) '`''
4. Install perimeter protection (silt fence, brush barrier, etc.).
5. Construct surface water controls simultaneously with grading activities for project
development.
6. Maintain erosion control measures in accordance with King County Standards and
manufacturer's recommendations.
7. Relocate erosion control measures, or install new measures, so that changing site
conditions continue to meet King County erosion and sediment control standards.
8. Cover all areas that will be unworked for more than seven days during the dry season or
two days during the wet season with straw, wood fiber mulch, compost, plastic sheeting,
or equivalent.
9. Seed or sod any areas to remain unworked for more than 30 days.
10. Upon completion of the project, all disturbed pervious areas must be stabilized and BMPs
removed if appropriate.
SWPPS Plan Design
Construction activities that may generate pollutants include: (1) soil disturbance from site
grading, storm installation, and pavement removal; and (2) use of large machinery required to
install new asphalt, stormwater, and water system components. Potential pollutants in
construction runoff as a result of the operations include the following: oils and greases,
nutrients, metals, suspended solids, and Biochemical Oxygen Demand (BOD).
The major pollutants generated by the activities are suspended solids (from soil disturbance) and
oils and greases from heavy machinery and asphalt placement. These pollutants will be
controlled using a combination of inlet protection filter traps, filter bags, and straw wattles in or
around the new and existing catch basins. An additional measure for water quality will be
utilized by pumping runoff from existing catch basins to a dispersal system. These measures are
described above in the ESC Measures section.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase 11 - 35 -
Technical Information Report (TIR) 1.1mro I Ill 1V"I M'
SECTION 9: BOND QUANTITIES, FACILITY SUMMARIES,AND
DECLARATION OF COVENANT
Bond Quantities Worksheet
A completed Bond Quantity Worksheet is provided in Appendix E of this document.
Flow Control and Water Quality Facility Summary Sheet and Sketch
A summary of the water quality facilities is discussed in Section 4, Flow Control and Water
Quality Facility Analysis and Design. As discussed previously, flow control facilities are not
required. Flow control BMPs will be provided where necessary or applicable.
Please see Appendix F for the completed Flow Control and Water Quality Facility Summary
Sheet for this project.
Declaration of Covenant for Privately Maintained Flow Control and WQ Facilities
The Renton Municipal Airport is a public facility owned and operated by the City of Renton. All
fees associated with maintenance work are budgeted by the Municipal Airport, and the Public
Works staff maintains the facilities. Therefore, this project is exempt from providing a
Declaration of Covenant for Privately Maintained Flow Control and WQ Facilities.
Declaration of Covenant for Privately Maintained Flow Control BMPs
The Renton Municipal Airport is a public facility owned and operated by the City of Renton. All
fees associated with maintenance work are budgeted by the Municipal Airport, and the Public
Works staff maintains the facilities. Therefore, this project is exempt from providing a
Declaration of Covenant for Privately Maintained Flow Control BMPs.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 36 -
Technical Information Report (TIR)
SECTION 10: OPERATIONS AND MAINTENANCE MANUAL
The applicable maintenance requirements, supplied from the KCSWDM, Appendix A, are
provided in Appendix G of this document.
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 37 -
Technical Information Report (TIR)
SECTION 11: REFERENCES
City of Renton, Washington, 2012. City of Renton Municipal Code, Section 4-6-030, Drainage
(Surface Water) Standards.
i
City of Renton, Washington, 2012. City of Renton COR Maps. 7 June 2012.
http://rentonwa.gov/govemment/default.aspx?id=29886.
City of Renton, Washington, Public Works Department, Surface Water Utility, 2010. City of
Renton Amendments to the King County Surface Water Design Manual.
HWA GeoSciences, Inc., 2012. Taxiway B North (General Aviation) Section Improvements,
Renton Municipal Airport, Taxiway B Rehabilitation.
King County Department of Natural Resources and Parks, 2009.King County Surface Water
Design Manual.
King County Department of Natural Resources and Parks, Water and Land Resources Division,
2009.King County Stormwater Pollution Prevention Manual.
King County Geographic Information Systems, 2012.King County iMap:Interactive Mapping
Tool. 10 September 2012. http://www.kingcounty.gov/operations/GIS/Maps/iMap.aspx/.
United States Department of Agriculture,Natural Resources Conservation Service, 2012. Soil
Survey of King County Area, Washington.
sah\23\10\007\reports\drainage report(tir)\tir renton tw b phase ii.doc\bts
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II - 38 -
Technical Information Report (TIR)
Appendix A
Geotechnical Report
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II �
Technical Information Report (TIR)
FINAL GEOTECHNICAL ENGINEERING REPORT
Renton Municipal Airport
Taxiway B Rehabilitation
Renton, Washington
" HWA Project No. 2011-039-21
i
Prepared for
Reid Middleton, Inc.
October 17, 2012
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HWAGEOSCIENCES INC.
• Geotechnical En�1'14'0'111
- Hydrogeology
Geoenvironmental Servl*"'':-
• In.yection & Testing
IFL
A GEOSCIENCES IBC.
October 17,2012.
HWA Project No. 2011-039-21
Reid Middleton
728 134th Street SW, Suite 200
Everett, Washington 98204
Attention: -Mr.Randy Hall, P.E.
SUBJECT: Final Geotechnical Engineering Report
Renton Municipal Airport
Taxiway B Rehabilitation
Renton, Washington
Dear Randy:
As requested, HWA GeoSciences Inc. (HWA) has completed a geotechnical engineering
investigation to support design efforts for the Taxiway B Rehabilitation Project at the Renton
Municipal Airport in Renton, Washington. The objective of our investigation was to evaluate the
existing pavement and subgrade conditions in the vicinity of the proposed improvements. Our
scope of work included field reconnaissance, test pit logging,pavement coring, dynamic cone
penetration testing(DCP), laboratory testing, SCBC mix design, engineering analyses, and
preparation of the attached final report summarizing the investigation results and our
recommendations.
We appreciate the opportunity to provide geotechnical services on this project.
Sincerely,
HWA GEQSC.IENCES INC.
Steven E. Greene,L.G.,L.E.G. George Minassian,Ph.D.,P.E.
Senior Engineering Geologist Pavement Engineer
Enclosure: Hiai Geoteclmical Report
21312 30th Drive SE
Suite 110
Bothell,WA 98021.7010
'rel: 425.774.0106
Fax: 425.774,2714
www.hwageoxom
TABLE OF CONTENTS
1.0 INTRODUCTION..........................................................................................................1
1.1 GENERAL.......................................................................................................1
1.2 PROJECT UNDERSTANDING............................................................................1
1.3 AUTHORIZATION AND SCOPE OF WORK.........................................................1
2.0 INVESTIGATION PROGRAM ........................................................................................1
2.1 SITE EXPLORATIONS......................................................................................1
2.2 LABORATORY TESTING .................................................................................2
3.0 SITE CONDITIONS......................................................................................................3
3.1 SITE DESCRIPTION.........................................................................................3
3.2 GENERAL GEOLOGY......................................................................................4
3.3 SUBSURFACE CONDITIONS.............................................................................4
3.5 EXISTING PAVEMENT STRUCTURE.................................................................5
4.0 SUMMARY AND CONCLUSIONS..................................................................................8
4.1 GENERAL ........................................................................................................8
4.2 NORTH TAXIWAY SECTION RECONSTRUCTION ...............................................9
4.3 SOUTH TAXIWAY SECTION REHABILITATION&RECONSTRUCTION................9
5.0 CONDITIONS AND LIMITATIONS.................................................................................10
LIST OF FIGURES(FOLLOWING TEXT
Figure I Project Site and Vicinity Map
Figure 2 Site and Exploration Plan
Figure 3 Geologic Map
APPENDICES
Appendix A: Field Exploration
Figure A-1 Legend of Terms and Symbols Used on Exploration Logs
Figures A-2—A-21 Logs of Cores Core-I through Core-20
Figures A-22—A-24 Logs of Test Pits TP-I through TP-3
Appendix B: Laboratory Testing
- Figures B-1 —B-8 Particle Size Analysis of Soils
Figure B-9 Liquid Limit, Plastic Limit and Plasticity Index of Soils
Figures B-10—B-12 Laboratory Compaction Characteristics of Soil
Figures B-13 —B-15 CBR of Laboratory Compacted Soil
Figure B-16 Bulk Density of Soil-Drive Cylinder Method
Appendix C: Core Photographs
FINAL GEOTECHNICAL ENGINEERING REPORT
RENTON MUNICIPAL AIRPORT
TAXIWAY B REHABILITATION
RENTON, WASHINGTON
1.0 INTRODUCTION
1.1 GENERAL
This report summarizes the results of a geotechnical engineering investigation completed by
HWA GeoSciences Inc. (HWA) to support design efforts for the Taxiway B Rehabilitation
Project, at the Renton Municipal Airport, in Renton, Washington. The project location is
indicated on the Project Site and Vicinity Map, Figure 1.
1.2 PROJECT UNDERSTANDING
We understand that Taxiway B rehabilitation work involves resurfacing all of Taxiway B on the
east side of the airfield. Currently, Taxiway B is composed of hot mix asphalt and Portland
cement concrete pavement and is approximately 3,300 feet long and ranges from about 25 to 50
feet wide. The objective of our study was to provide field exploration and testing to evaluate the
existing subsurface and pavement conditions, and provide recommendations regarding subgrade
strength properties for pavement design for the taxiway rehabilitation.
1.3 AUTHORIZATION AND SCOPE OF WORK
Authorization to proceed with our work was provided under Agreement for Subconsulting
Services, dated August 2010,between HWA and Reid Middleton. Our work was undertaken in
accordance with our original proposal dated August 7, 2010. The scope of work included field
reconnaissance, test pit excavation, pavement coring and shallow hand-excavated explorations,
DCP and laboratory testing, and preparation of this summary report.
2.0 INVESTIGATION PROGRAM
2.1 SITE EXPLORATIONS
Subsurface conditions in the vicinity of the proposed improvements were investigated by means
of three test pits (designated TP-1 through TP-3) and twenty pavement cores (designated Core-1
through Core-20). Shallow hand borings were performed within the core holes. The
approximate locations of our explorations are shown in Figure 2, Site and Exploration Plan.
The test pits were excavated on June 3, 2011, by an excavator under subcontract to HWA, to
depths ranging from approximately 3.5 to 4 feet. The test pits and cores/hand borings were
October 17, 2012
HWA Project No. 2011-039-21
performed by HWA engineering geologist personnel. Pertinent information including soil
sample depths, stratigraphy, soil engineering characteristics, and ground water occurrence were
recorded. The stratigraphic contacts shown on the individual boring logs represent the
approximate boundaries between soil types; actual transitions may be more gradual. The soil
and ground water conditions depicted are only for the specific date and locations reported and,
therefore, are not necessarily representative of other locations and times.
Soil samples obtained from the excavations were classified in the field and representative
portions were placed in plastic bags. These soil samples were then returned to our Bothell,
Washington, laboratory for further examination and testing.
The cores/hand borings were completed using coring equipment, hand augers, and other hand
tools, to depths ranging from about 1.5 to 7.5 feet. The initial phase consisting of(16) sixteen
cores/hand borings were conducted on June 2, June 6, and June 7, 2011. Four (4) supplemental
core/hand borings were conducted on July 11, 2012. The cores/hand borings were used to gather
information on the thickness of the existing pavement and strength of the underlying subgrade
layers in the taxiway area. A legend of the terms and symbols used on the exploration logs is
presented in, Figure A-1, Appendix A. Summary test pit and core logs are presented in Figures
A-2 through A-24, Appendix A.
Dynamic cone penetration (DCP) testing was performed in most pavement core holes to check
relative soil density/strength conditions. The DCP consists of a steel extension shaft assembly,
with a 60 degree hardened steel cone tip attached to one end, which is driven into the soil by
means of a sliding drop hammer. The base diameter of the cone is 20 mm (0.8 in). The diameter
of the shaft is 8 mm (0.3 in) less than that of the cone to ensure that, at shallow penetration
depths, the resistance to penetration is exerted on the cone alone. The DCP is driven by
repeatedly dropping an 8 kg (17.6 lbs) sliding hammer from a height of 575 mm (22.6 in). The
depth of cone penetration was measured after each hammer drop and the soil shear strength is
reported in terms of the DCP index. The DCP index is based on the average penetration depth
resulting from 1 blow of the 8 kg hammer and is reported as millimeters per blow (mm/blow).
The data obtained from the DCP testing was then correlated to approximate California Bearing
Ratio (CBR) values, in order to evaluate the strength of the subgrade soils. It is important to
note that CBR values derived from DCP data obtained from granular materials may be
exaggerated. The calculated CBR values are plotted on the appropriate core logs in Appendix A.
2.2 LABORATORY TESTING
Laboratory tests were conducted on selected soil samples to characterize relevant properties of
the on-site soils. The laboratory testing program was performed in general accordance with
appropriate ASTM Standards, as outlined below.
Final Report 2 HWA GEOSCIENCES INC.
I
October 17, 2012
HWA Project No. 2011-039-21
MOISTURE CONTENT OF SOIL: The moisture content of selected soil samples (percent by dry
mass) was determined in accordance with ASTM D 2216. The test results are shown at the
sampled intervals on the appropriate summary logs in Appendix A.
PARTICLE SIZE ANALYSIS OF SOILS: Selected granular samples were tested to determine the
particle size distribution of material in accordance with ASTM D 422 (wash sieve or wash sieve
and hydrometer methods). The results are summarized on the attached Particle-Size Distribution
reports (Figures B-1 through B-8, Appendix B), which also provide information regarding the
classification of the samples and the moisture content at the time of testing.
LIQUID LIMIT,PLASTIC LIMIT,AND PLASTICITY INDEX OF SOILS(ATTERBERG LIMITS):
Selected fine-grained samples were tested using method ASTM D 4318, multi-point method.
The results are reported on the attached Liquid Limit, Plastic Limit, and Plasticity Index report
on Figure B-9.
LABORATORY COMPACTION CHARACTERISTICS OF SOIL(PROCTOR TEST): Selected bulk
subgrade samples were tested using either method ASTM D 698 (Standard Proctor) Method C or
ASTM D 1557 (Modified Proctor), as appropriate. The test results are summarized on the
attached Laboratory Compaction Characteristics of Soil reports, Figures B-10 through B-12,
Appendix B.
CBR(CALIFORNIA BEARING RATIO)OF LABORATORY COMPACTED SOILS: Selected bulk
subgrade samples were tested in accordance with method ASTM D 1883. The test results are
summarized on the attached CBR of Laboratory Compacted Soils reports, Figures B-13 through
13-15, Appendix B.
BULK DENSITY OF SOIL DRIVE CYLINDER METHOD: The bulk density, dry density and moisture
content of selected, relatively undisturbed soil samples obtained from test pits TP-1 through TP-
3 were determined in general accordance with ASTM D 2937 test method. The test results are
summarized in the table on Figure B-16, Appendix B.
3.0 SITE CONDITIONS
3.1 SITE DESCRIPTION
Renton Municipal Airport is located in King County, within the northwest portion of the City of
Renton. The Airport has a single runway (Runway 16-34), which is approximately 5,400 feet
long, 100 feet wide, and consists of Portland cement concrete panels overlain with an asphaltic
concrete surface layer. The runway was resurfaced and realigned in the summer of 2009.
Taxiway B extends along the southeast side of runway and is approximately 3,300 feet long, 25
to 50 feet wide, and consists of asphaltic concrete pavement in the general aviation area and
Portland cement concrete panels overlain by asphaltic concrete in the area trafficked by large
Final Report 3 HWA GEOSCIENCES INC.
r
October 17, 2012
HWA Project No. 2011-039-21
commercial aircraft. The ground surface in the vicinity of this project is predominantly flat,
situated at approximately elevation 32 feet MSL and prior to industrial development consisted of
a portion of the alluvial plain of the Cedar River.
3.2 GENERAL GEOLOGY
Background geologic information was obtained from Geologic Map of the Renton Quadrangle,
King County, Washington (D.R. Mullineaux, 1965). This map, a portion of which is reproduced
herein as Figure 3, identifies the surficial deposits in the vicinity of the airport as urban or
industrial land that has been modified by widespread or discontinuous artificial fill (map symbol-
afire). Alluvial deposits consisting of material deposited by the Cedar River(map symbol—Qac)
are mapped along the margins of this industrial land area and belie conditions prior to
industrialization.
3.3 SUBSURFACE CONDITIONS
Locally, construction of pavement structure have been facilitated by the use of fill layers ranging
from 0.6 feet in the general aviation area (north of the wind rose) to 2.25 to 4 feet plus in the
commercial aviation area(central to south portion of Taxiway B). In general, the fill layers
appear to be loose to medium dense and consist of various material types most predominately,
slightly silty to silty, gravel with sand to relatively clean, sand with gravel. In the central area
(between Core-5 and Core-6) material interpreted as dredge fill consisting of sand and gravel
with shell fragments, glass and brick pieces underlies the pavement section at depth. Beneath the
fill layer, the native subgrade soils consists predominately of medium stiff to soft, organic silt
(OH), typically exhibiting estimated in-place CBR values ranging from<1%to about 5%. The
soil moisture content appears to increase with depth.
Perched ground water was encountered in test pits TP-1, TP-2, and TP-3, at depth of 3.8 feet, 3.5
feet and 3.6 feet,respectively. Ground water seepage was observed in core/hand borings Core-4,
Core-6 through Core-9, and Core-18, ranging from about 2.2 to 5.5 feet below the existing
ground surface at the time of our exploration. It is anticipated that the level of ground water in
this area will change depending on the season and the height of the adjacent Cedar River.
Three native soil samples were tested for laboratory CBR values. The tested samples were taken
from Test Pits TP-1, TP-2 and TP-3, which are representative of the native soils encountered
below granular fill along the length of existing Taxiway. The moisture-density curve for the
sample from TP-1 was determined in general accordance with ASTM D 698, as required by FAA
for airfields serving aircrafts with total weight less than 60,000 Lbs. The moisture-density
curves for samples from TP-2 and TP-3 were determined in accordance with ASTM D 1557, as
required by the FAA for areas serving aircraft with a total weight above 60,000 Lbs. The CBR
value of each sample was determined at natural moisture content and maximum compaction
effort. In addition,the sample obtained in TP-3 was dried back to optimum and compacted at
Final Report 4 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
maximum effort in an attempt to determine the potential strength gain available should the
subgrade be allowed to dry out. The measured CBR test results are presented on Figures B-13
through B-15, in Appendix B and are summarized in Table 1 below:
Table 1: Summary of CBR Tests
Sample Relative CBR Value
Material Description Location Compaction o
Light olive brown, organic SILT (OH) TP-1 57.4' 0.4
Dark brown, organic SILT (OH) TP-2 65.62 0.6
Dark olive gray, SILT with sand (ML) TP-3 85.5' 1.2
t 02.V 53.8
'Relative to Maximum Dry Density determined with Standard Compactive Effort(ASTMD698)
Relative to Maximum Dry Density determined with Modified Compactive Effort(ASTMD 1557)
3.5 EXISTING PAVEMENT STRUCTURE
We completed twenty (20) core/hand holes at locations selected by Reid Middleton along the
taxiway alignment and on the existing north and south end connectors. Our shallow hand
borings, performed within the core holes, were extended to 1.3 to 7.5 feet in depth using hand
tools. Detailed logs of the core holes are located in Appendix A of this report. Photographs of
pavement cores are presented in Appendix C.
North Taxiway Connector
Based on the exploration within the north taxiway connector(Core-1) the pavement section
consists of an HMA surface of about 2-inches thick over 5-inches of crushed gravel base course.
The existing pavement surface is in fair condition.
Fill soils consisting of Gravel with sand and cobbles were encountered at depth of about 0.6 feet.
No DCP test was conducted at this location due to refusal on cobbles.
Taxiway B North - General Aviation Area
Based on the explorations within the Taxiway B proper in general aviation area (Core-2 and
Core-5) the taxiway pavement section consists of an HMA surface of about 2 to 4.5-inches thick
and a base course layer ranging from 5 to 6 inches thick. The existing pavement surface is in fair
to good condition.
Final Report 5 HWA GEOSCIENCES INC.
i
October 17, 2012
HWA Project No. 2011-039-21
Fill soils consisting of poorly graded gravel with sand were encountered at depth of about 0.5 to
0.7 feet. At the location of Core-5, dredge fill consisting of silty medium sand with shell
fragments, brick and glass fragments was encountered to a depth of 2.5 feet. Below the fill in
Core-2 and Core-5, native alluvial soils consisting of sandy silt to organic silt were encountered.
These soils were similar to those encountered in our test pit TP-1.
Field DCP data obtained at location of Core-2 (See Figure A-3) indicate in-place CBR values of
about 20% for the uppermost 0.7 of a foot of subgrade, then decreasing to about 3-5% for the last
1.1 feet or so to the termination depth of the test at about 4.3 feet below grade in native soils.
Taxiway B North Apron
Based on the explorations east on the Taxiway B in general aviation area within the apron
adjacent to private hangers (Core-3 and Core 4) the taxiway pavement section consists of an
HMA surface of about 1.5 to 2.25-inches thick. At the location of Core-4, a 1.5-inch thick layer
of crushed aggregate was found sandwiched between the surface course of HMA and older 1.75-
thick layer of HMA. A thin gravel base layer about 1.5 —inches thick was encountered under the
pavement at Core-3. No gravel base was encountered below the lower HMA layer in Core-4.
The existing pavement surface is in poor to fair condition.
Fill soils consisting of well graded gravel, poorly graded sand or silty sand were encountered at
depth of about 0.4 to 0.5 feet. At the location of Core-3, a silt layer was encountered
immediately beneath a thin layer of CSBC. Below the fill in Core-3 and Core-4, native organic
silt soils were encountered at depths of 2.3 and 3.2 feet, respectively. These subgrade soils were
similar to those encountered in test pit TP-1.
Field DCP data obtained at location of Core-3 (See Figure A-4) indicates in-place CBR values of
1-3% for alluvial subgrade from 2.8 to 4.9 feet below grade. Field DCP data obtained at location
of Core-4 (See Figure A-5) indicates in-place CBR values of 1-5% for alluvial subgrade from 3.1
to 4.8 feet below grade. At both locations CBR values appear to increase slightly with depth.
Taxiway B South -Commercial Aircraft Area
Based on the explorations within the commercial aviation area the taxiway pavement section
(Core-6 through Core-8, and Core-17 through Core-20) consists of an HMA surface of about 5.5
to 12-inches thick over a PCC section of 5 to 8 inches thick. At the location of Core-9, the
taxiway pavement consisted on 10-inches of HMA without an underlying PCC layer. At the
location of Core-10, which is situated in an infield cut-out (See Figure 2), the pavement
consisted of only 2.25-inches of HMA. At the location of Core-11, which is situated at the
south end of Taxiway B, the pavement consisted of 8.5-inches of HMA over 8-inches of PCC.
At the location of Core-19 within Taxiway K, the pavement consisted of 12.5 inches of HMA
over 7-inches of PCC. No crushed gravel base was encountered beneath the pavement at any of
Final Report 6 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
these locations except for Core-10, where at least 24-inches of gravel base consisting of fine
crushed gravel with sand was encountered. The existing pavement surface at these locations is
in very poor to good condition.
At the locations of Core-17 and Core-20, the pavement surface is deeply gouged within the
upper .HMA layer. The resulting gap had been sealed (See core photos for Core-17 and Core-20
in Appendix Q. It appears that the pavement in these areas had been subject to repeated stress
by heavy wheel loads that plowed and furrowed the surface causing fractures to propagate into
the pavement as much as 0.75 inches deep. At these locations, it is likely that the nose gear tires
of commercial aircraft entering the taxiway from the hardstand are responsible for this damage.
Fill soils consisting of gravelly sand to silty sand layers ranging from 1.0 to 2 feet thick were
encountered directly underlying the pavement sections investigated in this area except at Core-
10 as noted above.
Native soils consisting of sandy and organic silt were encountered at depths ranging from about
2.5 to 3.5 feet; these soils were similar to those encountered in our test pit explorations TP-2 and
TP-3.
Field DCP data obtained at the locations of Core-6 through Core-10 (See Figures A-7 through A-
10) indicate in-place CBR values ranging from 3 to 6% in native subgrade to depths of 4.4 to 5.6
feet below grade. At the location of Core-10, DCP testing encountered granular material with
average CBR values above 40%to depths of 4.2 feet below grade. At the location of Core-11,
DCP testing encountered granular material with average CBR values of 19% to a depth of 3.6
feet below grade. At the locations of Core-17 through Core-20 (see Figures A-18 through A-21)
field DCP data obtained below the granular fill, indicate in-place CBR values of 3 to 4% in
native subgrade from depths of 3.0 to 6.0 feet below grade.
South Taxiway Connector
Based on the explorations within the south taxiway connector (Core-12 through Core-16) the
taxiway pavement section consists of an HMA surface of about 2 to 4 inches thick and a base
course approximately 6 inches thick. The existing pavement surface is in fair condition.
Native soils consisting of sandy silt and silt with sand were encountered at depth of about 0.5
feet; these soils were similar to those encountered in our test pit explorations.
Field DCP data obtained at the locations of Core-12 through Core-14 (See Figure A-13 through
A-15) indicates in-place CBR values ranging from 2 to 6% in native subgrade soils to depth
ranging from 3.6 to 6.8 feet below grade. Field DCP data obtained at the location of Core-15
(See Figure A-16) indicate in-place CBR values averaging greater than 50% for two layers
separated by a soft layer (CBR about 1- 5% ) about I foot thick situated between 3.3 and 4.4 feet
Final Report 7 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
below grade. Field DCP data obtained at the location of Core-16 (See Figure A-17) indicate in-
place CBR values averaging greater than 100% for granular material encountered from 2.1 feet
to the termination depth of 4.3 feet below existing grade.
4.0 SUMMARY AND CONCLUSIONS
4.1 GENERAL
Our subsurface investigations reveal that the native soils consist predominately of soft to
medium stiff organic or sandy silts within the northern and central portions of the project
alignment (Core-1 through Core-9 and Core-17 through Core-20) at depths ranging from 1.125
to 3.6 below the existing pavement surface. These native subgrade soils are weak exhibiting in-
place CBR values ranging from 1 to 5%, and averaging about 3%. CBR values from laboratory
samples obtained from TP-1 and TP-2 and remolded at natural moisture content indicate CBR
values less than 1% for these soils. The in-place moisture contents of these soils ranged from
about 50 to 75 percent over what is optimum for compaction. Typically, a layer of loose to
medium dense, granular fill of varying quality ranging from 0.75 to 3.0 feet in thickness is
present between the pavement and the underlying soft to medium stiff, native subgrade.
Within the southernmost portion of the project alignment, in the infield cut-out area (Core-10)
and at the southern end of Taxiway B (Core-11) the pavement is underlain by granular fill and
sandy alluvial soils. These subgrade soils appear to be moderately strong exhibiting estimated
in-place CBR values ranging from 19 to 40%. CBR values determined from laboratory samples
obtained from TP-3 and remolded at natural and optimum moisture content indicate CBR values
of about 1% to 54% for material with a moisture content difference of only 10%. It appears that
considerable strength gain can be realized if these soils are allowed to dry prior to compaction.
Along the main portion of southern taxiway connector(Core-12 through Core-14) the pavement
is underlain by loose to medium stiff, silty sand to sandy silt alluvial soils. These subgrade soils
are relatively weak exhibiting in-place CBR values ranging from 2 to 6%, and averaging about
3%. At the locations of Core-15 and Core-16 (situated within the inside turn radius on to
Runway 16-34) the pavement is underlain by relatively thick section of strong granular fill and
native material exhibiting estimated in-place CBR values ranging from 50 to 100% (these values
should be considered in relative terms only as CBR values derived from DCP data from granular
soils is often exaggerated due to presence of gravels).
The local water table, or substantial seasonally perched ground water, was observed in all of our
explorations located within the central portion of the Taxiway (Core-4, Core-6 through Core-9,
and Core-18) and in the infield at all test pit locations at depths ranging from 2.2 to 5.4 feet
below the existing ground surface at the time of our explorations. We anticipate that ground I
water levels in the area will be high; especially during the wet weather season and vary locally
Final Report 8 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
with the level of the adjacent Cedar River. This high ground water level will further decrease the
already low infiltration potential of the subgrade soils.
Because of the high fines and organic content in the native subgrade layer, we expect that water
penetrating the surfacing could become trapped in the base layer. Therefore, we recommend that
subsurface drainage be provided below the pavement and along the edge of the taxiways and
apron pavement to intercept and prevent possible incursion of such infiltrated water beneath the
pavement areas. Failure to maintain the subgrade in a positively drained condition could lead to
localized softening and loss of support for the pavement structure, possibly resulting in
premature pavement distress. Moreover, saturation of the subgrade with infiltrated moisture will
exacerbate potential frost-heave effects and increase the rate of subgrade deterioration.
4.2 NORTH TAXIWAY SECTION RECONSTRUCTION
We understand that the reconstruction of the northern portion of Taxiway B referred to herein as
the General Aviation Area has already been designed and bid for construction commencing in
the spring of 2013. We understand reconstruction will entail: removal of the existing HMA
pavement, cement treatment of the underlying subgrade (SCB) for a depth of 8-inches,
placement and compaction of a 6-inch thick layer of crushed base rock, followed by placement
of a 4-inch thick HMA pavement layer. The use of SCB instead of traditional pavement re-
construction methods is expected to save time and reduce the amount of imported materials
required for re-construction by treating existing subgrade soils with cement. We understand that
the construction will be conducted in three phases commencing from south to north. The SCB
Mix design was completed by HWA in August, 2012 and our findings and recommendations are
summarized in a laboratory report entitled: SCB Mix Design Report: Renton Airport Taxiway B
Rehabilitation, General Aviation Area-Phases 1 through 3, Renton, Washington, prepared for
Reid Middleton.
4.3 SOUTH TAXIWAY SECTION REHABILITATION&RECONSTRUCTION
Currently, the design concept for rehabilitation and reconstruction of the southern portion of
Taxiway B referred to herein as the Commercial Aviation Area is currently being developed.
We understand that current consideration is being given to; total reconstruction of an area
approximately 50 feet wide by about 1,500 long adjacent to the hardstand area, and a grind and
overlay program for all other areas exhibiting surface deterioration. It is likely that this work will
also be constructed in phases to minimize impact to airport operations. Currently, we understand
that total reconstruction will consist of pavement (HMA & PCC) removal, followed by the
placement of HMA for the full-depth of 11 to 13-inches. In these areas, the existing pavement
section is supported by loose to medium dense, sand with gravel to gravel with sand fill directly
underlain by soft to medium stiff, native sandy silt or organic silt. Consideration is being given
to amend the upper 4 to 6 inches of the existing granular fill with Portland cement to create a soil
Final Report 9 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
cement base (SCB) layer that will serve to stabilize and reduce the potential for disturbance of !
the subgrade during construction and facilitate efficient HMA layer compaction.
5.0 CONDITIONS AND LIMITATIONS
We have prepared this final report for the City of Renton and Reid Middleton. This report
should be provided in its entirety to prospective contractors for bidding and estimating purposes;
however, the conclusions and interpretations presented herein should not be construed as our
warranty of the subsurface conditions. Experience has shown that soil and ground water
conditions can vary significantly over small distances. Inconsistent conditions may occur
between explorations that may not be detected by a geotechnical study of this scope and nature.
If, during construction, subsurface conditions are encountered which vary appreciably from
those described herein, HWA should be notified for review of the recommendations of this
report, and revision of such if necessary. If there is a substantial lapse of time between
submission of this report and the start of construction, or if conditions change due to construction
operations, it is recommended that this report be reviewed to determine the applicability of the
conclusions and recommendations considering the changed conditions and time lapse.
This report is issued with the understanding that it is the responsibility of the owner, or the
owners' representative, to ensure that the information and recommendations contained herein are
brought to the attention of the appropriate design team personnel and incorporated into the
project plans and specifications, and the necessary steps are taken to see that the contractor and
subcontractors carry out such recommendations in the field.
We recommend HWA GeoSciences Inc. be retained to monitor construction, evaluate subgrade
soil and ground water conditions as they are exposed, and verify that subgrade preparation,
backfilling, and compaction are accomplished in accordance with the specifications.
Within the limitations of scope, schedule and budget, HWA attempted to execute these services
in accordance with generally accepted professional principles and practices in the fields of
geotechnical engineering and engineering geology at the time the report was prepared. No
warranty, express or implied, is made. The scope of our work did not include environmental
assessments or evaluations regarding the presence or absence of wetlands or hazardous or toxic
substances in the soil, surface water, or ground water at this site.
HWA does not practice or consult in the field of safety engineering. We do not direct the
contractor's operations, and cannot be responsible for the safety of personnel other than our own
on the site. As such, the safety of others is the responsibility of the contractor. The contractor
should notify the owner if any of the recommended actions presented herein are considered
unsafe.
Final Report 10 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
O.O
We appreciate the opportunity to be of service to you on this project.
Sincerely,
HWA GEOSCIENCES INC.
Wash
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01, 1704 y ,
eased 1;8
8TEVEN M=TT GREENE D"
Steven E. Greene, L.G.,L.E.G. George Minassian, Ph.D., P.E.
Senior Engineering Geologist Pavement Engineer
SEG:GM:seg
y
Final Report 11 HWA GEOSCIENCES INC.
October 17, 2012
HWA Project No. 2011-039-21
REFERENCES
Federal Aviation Administration, 2008,Airport Pavement Design and Evaluation Advisory
Circular, AC 150/5320-6E.
Federal Aviation Administration, 2007, Standards for Specifying Construction of Airports, AC
150/5370-10C.
Mullineaux, D.R., 1965, Geologic Map of the Renton Quadrangle, King County, Washington.
U.S.G.S Map QC-405.
WSDOT, 1995, WSDOT Pavement Guide Volume 2 Pavement Notes, Washington State
Department of Transportation.
WSDOT, 2010, Standard Specifications for Road, Bridge and Municipal Construction, M 41-10,
Washington State Department of Transportation.
i
i
Final Report 12 HWA GEOSCIENCES INC.
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PROJECT SITE AND VICINITY MAP •
REPORTGEOTECHNICAL ENGINEERING
RENTON MUNICIPAL AIRPORT
TAXIWAY B REHABILITATION
1 1 •
- - - - - - - - Renton Airport Taxiway B
IExploration Locations
Exploration Northing Westing Sta Offset
Core-1 47.49516 122.21492 44+09 275 E
Core-2 47.49447 122.21476 41+54 294 E
CORE-16 Core-3 47.49410 122.21459 40+17 319 E
CORE-14 CORE 19 Core-4 47.49306 122.21441 36+58 323 E
ORE-15 C 5
I I I Core-6 47.49008 122.21384 +78 350 E
RE 13� :VP-3
Care-7 47.48869 122.21350 20+54 383 E
1 CORE-1 I I Core-8 47.48838 122.21355 19+28 356 E
t Core-9 47.48774 122.21357 16+94 330 E
II I Core-10 47.48656 122.21362 12+54 278 E
CORE-8 Core-11 47.48649 122.21331 12+24 355 E
CORE-7 CORE-20-tI Core-12 47.48622 122.21394 11+39 183 E
CORE+ Core-13 47.48608 122.21405 10+98 148 E
CORE-10 I Core-14 47.48609 122.21412 10+94 129 E
I Core-15 47.48624 122.21413 11+52 133 E
CORE-18'f Core-16 47.48629 122.21425 11+73 103 E
Core-17 47.48854 122,21354 19+83 393 E
i
Core-18 47.48872 122.21332 20+43 455 E
CORE-11 I I I Core-20 47.48932 122.21365 22+67 397 E
TP-1 47,49422 122.21481 40+63 272 E
SCALE: 1"=100' LSCALE: 1"=100' I TP-2 47.48969 122.21400 24+37 298 E
J TP-3 47.48816 122.213-81 18+62 298 E
DETAIL A DETAIL B
Locations based on field GPS data.
® I
a a
,<
rl
4? �\\ ( TP-1
TP-3 COR 19 TP-2 - - . _ __ _ \�. �- CORE-2 °
- * I - * ♦ CORE-1
LE, I CORE 9 F ♦ CORE-7 I ♦CORE-4 CORE-3
i
J CORE-8 ♦ CORE-2 CORE-6
'CORE-17
DET' IL
DETAIL B
LEGEND
TP-3 0' 300' 600' 1200'
-$- TEST PIT DESIGNATION AND APPROXIMATE LOCATION
CORE-14 SCALE: 1"=300'
CORE HOLE DESIGNATION AND APPROXIMATE LOCATION
FINAL GEOTECHNICAL ENGINEERING REPORT FlGU0.E NO.
A
fm
RENTON MUNICIPAL AIRPORT SITE AND DRAWN BY EFK
L]
HWAGEOSQENCES INC. TAXIWAY B REHABILITATION EXPLORATION CHECK BY SG
P0.0]ECT N0.
DATE
BASE MAP PROVIDED BY REID MIDDLETON RENTON, WASHINGTON PLAN 06.14.11 2011-039-21
S:\2011 PROJECTS\2011-039-21 RENTON TAXIWAY B PRELIM ENGINEERING-PHASE 1\CAD\HWA 2011-039-21.DWG <FIG 2 CORE>Plotted:9/27/2012 5:53 AM
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Map Symbol Geologic Description NORTH
of Artificial Fill
afm Urban or Industrial land modified by widespread or discontinuous fill
Qac Alluvium—sand and gravel deposited by the Cedar River, and associated
beds of silt, clay and peat.
Qit Kame Terrace Deposits—sand and pebble—to-cobble gravel in scattered
terraces.
Map taken from: D.R. Mullineaux, 1965
GEOLOGIC MAP FIGURE No
GEOTECHNICAL ENGINEERING REPORT 3
HWAGEOSCIENCES INC., RENTON MUNICIPAL AIRPORT PROJECT NO
`� TAXIWAY B REHABILITATION 2011-039
RENTON WASHINGTON
APPENDIX A
FIELD EXPLORATION
RELATIVE DENSITY OR CONSISTENCY VERSUS SPT N-VALUE TEST SYMBOLS
COHESIONLESS SOILS COHESIVE SOILS %F Percent Fines
Apprommate AL Atterberg Limits: PL=Plastic Limit
Appro>amate LL=Li quid Limit
Density N(blows/ft) Relative Density(%) Consistency N(blows/ft) Untrained Shear
Strength(psf) CBR California Bearing Ratio
Very Loose 0 to 4 0 - 15 Very Soft 0 to 2 <250 CN Consolidation
Loose 4 to 10 15 - 35 Soft 2 to 4 250 - 500 DID Dry Density(pcf)
Medium Dense 10 to 30 35 - 65 Medium Stiff 4 to 8 500 - 1000 DS Direct Shear
Dense 30 to 50 65 - 85 Stiff 8 to 15 1000 - 2000 GS Grain Size Distribution
Very Dense over 50 85 - 100 Very Stiff 15 to 30 2000 - 4000 K Permeability
Hard over 30 >4000 MD Moisture/Density Relationship(Proctor)
MR Resilient Modulus
USCS SOIL CLASSIFICATION SYSTEM
PID Photoionization Device Reading
MAJOR DIVISIONS GROUP DESCRIPTIONS PP Pocket Penetrometer
Approx Compressive Strength(tsf)
Gravel and �,�GW Well-graded GRAVEL SG Specific Gravity
Coarse Clean Gravel TC Triaxtal Compression
Grained Gravelly Soils (little or no fines)
GP Poorly-graded GRAVEL TV Torvane
Soils ° Approx Shear Strength(tsf)
More than
50%of Coarse Gravel with ° GM Silty GRAVEL UC Unconfined Compression
Fraction Retained Fines(appreciable
on No.4 Sieve amount of fines) GC Clayey GRAVEL SAMPLE TYPE SYMBOLS
Sand and Cl SW Well-graded SAND ® 2.0"OD Split Spoon(SPT)
Clean Sand
Sandy Soils (little or no fines) (140 lb.hammer with 30 in.drop)
More than SP Poorly-graded SAND T
50%Retained 1 Shelby Tube
50%or More
on No. of Coarse Sand with :' SM Silty SAND 3 1/4"OD Split Spoon with Brass Rings
200 Sieve Fines(appreciable
Fraction Passing
Size No.4 Sieve amount of fines) SC Clayey SAND O Small Bag Sample
Fine Silt ML SILT Large Bag(Bulk)Sample
Grained and Liquid Limit
CL Lean CLAY
Soils Clay
Less than 50% n Core Run
i
QL Organic SILT/Organic CLAY Non-standard Penetration Test
(3.0"OD split spoon)
MH Elastic SILT
50%or More SiltLiquid Limit
Passing and 50%orMore CH Fat CLAY GROUNDWATER SYMBOLS
No.200 Sieve ClaySizeQH Organic SILT/Organic CLAY Groundwater Level(measured at
time of drilling)
Highly Organic Soils PT PEAT T Groundwater Level(measured in well or
open hole after water level stabilized)
COMPONENT DEFINITIONS COMPONENT PROPORTIONS
COMPONENT SIZE RANGE PROPORTION RANGE DESCRIPTIVE TERMS
Boulders Larger than 12 in
<5% Clean
Cobbles 3 in to 12 in
Gravel 3 in to No 4(4.5mm)
5-12% Slightly(Clayey,Silty,Sandy)
Coarse gravel 3 in to 3/4 in
Fine gravel 3/4 in to No 4(4.5mm)
Sand No.4(4.5 mm)to No.200(0.074 mm) 12-30% Clayey,Silty,Sandy,Gravelly
Coarse sand No.4(4.5 mm)to No.10(2.0 mm)
Medium sand No.10(2.0 mm)to No.40(0.42 mm) 30-50% Very(Clayey,Silty,Sandy,Gravelly)
Fine sand No.40(0.42 mm)to No.200(0.074 mm)
Silt and Clay Smaller than No.200(0.074mm) Components are arranged in order of increasing quantities.
NOTES: Soil classifications presented on a)ploration logs are based on visual and laboratory observation.
Soil descriptions are presented in the following general order: MOISTURE CONTENT
Density/consistency,color,modifier(if any)GROUP NAME,additions to group name(if any),moisture DRY Absence of moisture,dusty,
content. Proportion,gradation,and angularity of constituents,additional comments. dry to the touch.
(GEOLOGIC INTERPRETATION) MOIST Damp but no visible water.
Please refer to the discussion in the report text as well as the a)ploration logs for a more WET Visible free water,usually
complete description of subsurface conditions. soil is below water table.
FINAL GEOTECHNICAL ENGINEERING REPORT LEGEND OF TERMS AND
RENTON AIRPORT TAXIWAY B REHABILITATION SYMBOLS USED ON
FMQ0SCMNCH1NC RENTON MUNICIPAL AIRPORT EXPLORATION LOGS
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-1
LEGEND 2011-039.GPJ 9128/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/2/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/2/2011
SAMPLING METHOD: Hand Tools LOGGED BY: S.Greene
LOCATION: See Figure 2. SURFACE ELEVATION: 18.5 :it feet
U) Of W
U) m z w Dropweight Cone Penetrometer
0 a. Z
L N ¢ (140 lb.weight,30"drop) Z
J O Z cn.5 w p A Blows per foot O
2 In J J � W' Q
F m rn a_ W N W Z)
W y (n Q Q W H K W y
o" (n Z) DESCRIPTION m (n o- O O 0 10 20 30 40 50 W
0
2-inches of HMA Pavement(ASPHALTIC CONCRETE)
Dense,gray crushed rock consisting of 2-inches of CSTC S-1
"P overlying 3-inches of CSBC.
(GRAVEL BASE) S-2
GP Med.dense to dense,dark olive brown GRAVEL with sand S-3 GS '
° and cobbles,moist.
Q (FILL)
0
O
Q
Hand excavation terminated due to refusal on cobbles. No
Ground water observed while conducting this hand boring.
15
5
0 20 40 60 80 100
Water Content(%)
Plastic Limit [—" Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
1
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-01
HMGEOSCIENCESINC. RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-Z
BORING-DSM 2011-039.GPJ 9128/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/2/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/2/2011
SAMPLING METHOD: Hand Tools LOGGED BY: S.Greene
LOCATION: See Figure 2. SURFACE ELEVATION: 18.9 t feet
U) Of w
U) m z w Dropweight Cone Penetrometer
g a L Q (140 lb.weight,30"drop) z
J o W w e W o ♦ Blows per foot O
_ z
— m CO a Jo- y w
d, U Z o 2 O W m
W } (n Q Q W— H of J W
o 0 > DESCRIPTION 0 U) a O O 0 10 20 30 40 50 W
0
4.5-inches of HMA Pavement.
(ASPHALTIC CONCRETE)
Dense,gray,crushed rock.2-inches of CSTC over 3-inches S-1
of CSBC.
GP (GRAVEL BASE) S-2
o 3C Medium dense,brown,poorly graded GRAVEL with sand
o and cobbles,moist.
Q (FILL)
o
ML Dark olive brown,sandy SILT,moist.Contains 1.2%organic S-3
matter by dry weight.
(ALLUVIUM)
S-4 AL '
GS
:.� .
Hand boring terminated at an approximate depth of 2.5 feet
below exsting pavement surface. DCP testing conducted
from 2.5 to 4.3 feet below the existing ground surface. No 1
groundwater observed while conducting this hand boring.
♦
♦
15
♦:....:....:.... ....:....:....:....:....:....
5
0 20 40 60 80 100
Water Content
Plastic Limit 1 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-02
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
����N�$�C' RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: A-3
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Casacde Concrete Sawing and Drilling DATE STARTED: 6/2/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/2/2011
SAMPLING METHOD: Hand Tools LOGGED BY: S.Greene
LOCATION: See Figure 2. SURFACE ELEVATION: 18.3 t feet
U W
Lu m z — w Dropweight Cone Penetrometer
U D r ¢ (140 lb.weight,30"drop) Z
J p W w w.5 F o ♦ Blows per foot LD
FF--� m V) a ELK y W > >^
3
W d >- rn Q Q W F 2' Jd
o m D DESCRIPTION (n 0 a O 0 0 10 20 30 40 50 W
0
2.25-inches of HMA pavement.(ASPHALTIC CONCRETE)
Dense,gray CSBC.Layer 1.5-inches thick. S-1
ML (GRAVEL BASE) 3-2
Medium stiff,grayish brown,sandy SILT,non-plastic.
SP (FILL) S-3
Loose to medium dense,brown,medium to fine,poorly
graded SAND,moist.
SM Medium dense to loose,grayish brown,Silty fine SAND,
moist to wet.
(FILL1DISTURBED NATIVE ALLUVIUM)
ML Soft,sandy SILT to SILT with fine sand with 1.6%organic S-4 GS
matter by dry weight,wet,slightly plastic.
(NATIVE ALLUVIUM)
.....
15
Hand boring terminated at an approximate depth of 2.8 feet.
DCP testing conducted from 2.8 to 4.9 feet below the
ebsting pavement surface. No ground water was observed
while conducting this hand boring.
.................................................
At
♦
♦
5
0 20 40 60 80 100
Water Content(%)
Plastic Limit I--1 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-03
HMGEOSCIENCESINC. RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: /q-4
BORING-DSM 2011-039.GPJ 9/28112
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.5 t feet
w
M Z w Dropweight Cone Penetrometer
Ua- 2 t G (17.6 lb.weight,22.6"drop) Z
o w w w � Z ♦ Blows per foot
m o o- 3 w > >:
W } (n Q Q W� H 0' J d
o (n D DESCRIPTION CD U) o- O O 0 10 20 30 40 50 w
0
1.5-inches HMA pavement.
[ASPHALTIC CONCRETE]
GW Gray,crushed rock CSTC.Layer 1-inch thick. O S-1
[GRAVEL BASE]
1.75 inches HMA
SM I [ASPHALTIC CONCRETE) ♦:
:.'.: I Loose,brown,fine to coarse sandy,fine to coarse GRAVEL
'•..::• Iwith trace silt,moist.
OS2
--------- [FILL] ---------)
Medium dense,gray,silty SAND to sandy SILT with trace A:
gravel,moist.
---------------------/ :
Medium dense,gray,fine to medium SAND with fine to
coarse gravel,trace silt,moist. iL
Cobble at 29 inches.
OL Soft to medium stiff,brown organic SILT with gray sand 197
_ seam,and occasional reeds,moist to wet. O S-3
[ALLUVIUM]
SZ A. .... .... ....:....:....:....:....:....:....
♦:
Core hole was terminated at 50-inches below ground ♦: 15
surface due.Ground water seepage was observed at ♦'
5 48-inches below ground surface during the exploration.
�A
AA
♦:
♦:
♦:
♦:
♦:
10
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-04
IMGEOSCIENCESINC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-5
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/2/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/2/2011
SAMPLING METHOD: Hand Tools LOGGED BY: S.Greene
LOCATION: See Figure 2. SURFACE ELEVATION: 19.5 t feet
rn Of w
m z w Dropweight Cone Penetrometer
U a D U Q (140 lb.weight,30"drop) Z
J p Z 0r p ♦ Blows per foot O
x p co -j � `° x Z Q
I-�. m cn o- o- w >
o z o x o LU
o t-Q of DESCRIPTION Cn U)i d O w
0 w
0 10 20 30 40 50
— 7 2-inches of HMA pavement.(ASPHALTIC CONCRETE)
Dense, gray,crushed rock,6-inches of CSBC,moist. S-1
(GRAVEL BASE)
. SP Medium dense,brown,poorly graded SAND with silt and S-2
SM gravel,moist.
(FILL)
SM Medium dense,dark gray,silty medium SAND with S-3 GS
gravel-contains,pieces of brick,glass,and shell fragments.
(DREDGE FILL)
.................................................
Handboring terminated at an appropmate depth of 2.5 feet.
Soils appeared saturated and borehole sidewalls began to
collapse upon withdrawal of the auger.
15
5
0 20 40 60 80 100
Water Content(%)
Plastic Limit m 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-05
HMGEOSMCESINC. RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: /q-6
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/7/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/7/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.5 *feet
w
C0 m z w Dropweight Cone Penetrometer
va_ 2 � t N ~¢ (17.6 lb.weight,22.6"drop) Z
J o W W w z ♦ Blows per foot O
x co m a EL w >�
EL c> z a x O
W y } (n Q Q W — H W J N
o N x DESCRIPTION W (n a 0 0 0 10 20 30 40 50 W
0
8.5-inches of HMA Pavement.
[ASPHALTIC CONCRETE]
Y 6-inches Portland Cement Concrete
[pG•C] .. .. .. ..
Loose,gray,fine to coarse gravelly,fine to coarse SAND
with cobbles and trace silt,moist.Becoming fine to medium
SAND with gravel.
•••• [FILL) O S 1
o.
——————————————————————
•. SM Medium dense,gray,gravelly,silty fine to coarse SAND with 0 S-2
pieces of brick and shell like material,moist.
(DREDGE FILL)
ML Ground water seepage is encountered from upper fill layer _
that is perching on silty sand fill layer. S-3 t :: : ~�
Medium stiff,gray SILT with trace sand,reeds,and oxide "' .... """ "'
mottling,moist. O
[ALLUVIUM]
15
I'••: ML Medium stiff to medium dense,gray,silty fine SAND to ♦.
5 — SM sand_y SILT,moist to wet. ____________ "'
OL Soft to medium stiff,brown organic SILT with gray sand S-4
_ seams,wood debris and scatteredl reeds,moist to wet. 0 1
7.
ML Medium stiff to stiff,gray,SILT with wood debris and fine
sand seams,wet.
Core hole was terminated at 76-inches below ground
surface.Ground water seepage was observed during the ♦:
exploration at 37.5-inches and 66-inches below ground .... , ;•
surface.
....
....
...
♦ :
♦ :
10
♦ :
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1 —0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-06
HMQ0SMNCESINC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: A'7
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/7/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/7/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.7 t feet
Un o_ W
m Z — w Dropweight Cone Penetrometer
g a- r coo ¢ (17.6 Ib.weight,22.6"drop) Z
J O Z Un.� H p ♦ Blows per foot O
x N J J o of Z Q
m cn o o W > >-
d U z a x O
W y } U) Q Q W— F of Jd
0 Un x DESCRIPTION m m a U O 0 10 20 30 40 50 W`
0
8.5-inches HMA Pavement.
[ASPHALTIC CONCRETE]
5-inches Portland Cement Concrete
a' [PCC] ....:....
GP Loose,gray,poorly graded GRAVEL with fine to coarse O S-1
° SAND with cobbles and trace silt,moist to wet.
oO [FILL]
0
----------------------
Medium stiff,gray,gravelly,sandy SILT,moist to wet.
Core hole was terminated at 39-inches below ground
surface due to refusal on cobbles.Ground water seepage
was observed during the a)ploration at 32-inches below ♦:
ground surface.
15
5 .... ....:....:....:....:....:....:....:....:....
..................:.... ..
10
10
0 20 40 60 80 100
Water Content
Plastic Limit 1 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
1
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-07
HMGEOSCIENCES INC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: /q'$
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/7/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/7/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.9 *feet
co w
U m z Cn
w Dropweight Cone Penetrometer
g � N r ¢ (17.6 lb.weight,22.6"drop) z
O w w w
m o ♦ Blows per foot O
_ w z
H.--, U) d d L�
o- 2 O z x O
W y } U) Q Q W 2 H of J y
o cn x DESCRIPTION U) U) 1L O O 0 10 20 30 40 50 W
0
5.5-inches HMA Pavement.
[ASPHALTIC CONCRETE)
6.5-inches Portland Concrete Cement
[PCC]
ki4 N.
Loose,gray,fine to coarse gravelly,fine to coarse SAND
<•. with cobbles and trace silt,moist.
[FILL]
OS1
'.Q
o.
�•� -----
SM Medium dense,gray,gravelly sandy SILT to silty SAND,
moist. O S 2 ♦:.... .... .... ....:
Medium stiff,gray,SILT with sand to sandy SILT,moist. ♦ ♦;
[ALLUVIUM]
♦ ;
————————————————-- ............. ..
OH Medium stiff,brown with gray mottling,ORGANIC SILT with
11
trace fine sand seams and reeds,moist.
O S-3
5 ---------------------- 15
ML Medium stiff,gray,fine sandy SILT with interbedds of fine
sand and reeds,wet.
OS-4 ....• ....:....:....:....
♦:
Core hole was terminated at 79-inches below ground
surface.Ground water seepage was observed during the
exploration at 60 to 62-inches below ground surface.
♦
♦
♦
♦:
10
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-08
HMGEOSCIENCESINC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-9
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/7/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/7/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.9 t feet
U) of W
g m zQ n w
0 of
w Dropweight Cone Penetrometer
U r Cn Q (17.6 lb.weight,22.6"drop) z
J O Z cn w p ♦ Blows per foot O
x N J J 0' z Q
m In a. d N W Z) < ..^�
Wa, 2 0 z o x O Wm
Q, } (n Q Q W— H JN
O ti Z) DESCRIPTION U) Cn a O O 0 10 20 30 40 50 w'"
0
10-inches HMA Pavement.
[ASPHALTIC CONCRETE]
Loose,grayish brown,fine to coarse gravelly,fine to coarse ....:....:....:....:....:....:....:....:....:...
.•. SAND with cobbles and trace silt,moist.Becoming fine to
medium SAND with gravel.
�. [FILL)
.Q O S-1 ..
SM Medium dense,Dark olive brown,silty,gravelly fine to
medium SAND,moist 0 S-2
ML Medium stiff,gray,SILT to CLAY with trace fine sand,
moist.
0 S-3 4
[ALLUVIUM]
s �
15
5 �
ML Medium stiff to medium dense,gray,siltyfine SAND to
SM sandy SILT,wet. ♦:
A:....
S-4
0
:♦
:♦
:♦
Core hole was terminated at 90-inches below ground
surface.Ground water seepage was observed during the
e)ploration at 65-inches below ground surface.
1
10 0
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1--0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-09
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSCIENCESINC RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-1 0
BORING-DSM 2011-039.GPJ 9/28112
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.1 t feet
U) Of w
U) m Z - w Dropweight Cone Penetrometer
g a F r ¢ (17.6 lb.weight,22.6"drop) Z
J O :ZD w w .5 p ♦ Blows per foot LD
r cD
m ° o_ w
o U z o x O wm
w r rn ¢ ¢ w— F � m
O E v> > DESCRIPTION U) N CL O O 0 10 20 30 40 50 w
0
2.25-inches HMA Pavement.
Q GP [ASPHALTIC CONCRETE]
0
Dense to very dense,gray fine to coarse sandy,fine angular
O GRAVEL,moist.
Q [GRAVEL BASE] ....:....:....:....:....:.........
O O S-1
Q
o Q
Q
Core hole was terminated at 26-inches below ground
surface.No ground water seepage was observed during the
exploration. .
♦c
A:
15
5 ....:....:....:....:....:....:....:....:....:....
10
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit I--0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-10
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSCIENCES INC. RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-1 1
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/7/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/7/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.1 t feet
w
N m Z w Dropweight Cone Penetrometer
Cn
U a- 2 1 s ¢ (17.6 lb.weight,22.6"drop) Z
J O w w F o ♦ Blows per foot O
CD 2N
W U Q Q w° K -i
o cn D DESCRIPTION (n m o- O O 0 10 20 30 40 50 w
0
8.5-inches HMA Pavement.
[ASPHALIC CONCRETE]
: Y 8-inches Portland Cement Concrete
[PCC] ....:....:....:....:....:....
.............
Loose,grayish brown,fine to coarse gravelly,fine to coarse
.•. SAND with cobbles and trace silt,moist.
[FILL]
ct.• O S-1 �.
'.Q
SM Medium dense,dark olive brown,silty fine to medium SAND
with gravel,moist. S 2
O
Piece of wood at 35-inches BGS.
---- —————— ———— :>
Probably gravelly SAND fill,no samples recovered.
....:..... ........:....:..............
Core hole was terminated at 45-inches below ground 15
surface due to refusal on cobbles.No ground water
seepage was observed during the exploration.
5 :....:....:....:....:....:....:....:....:....
....:....:....:....:....:....:....:....:....:....
10
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-11
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
�A���INC RENTON
WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-1 2
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 20.6 t feet
w
U co Z w Dropweight Cone Penetrometer
UCL 2 �r Q (17.6 lb.weight,22.6"drop) Z
O w w w u o ♦ Blows per foot
x `°
O ii a N w Z
x
2 L) z o x O
a� Cn
wm
UJ } cn ¢ ¢ w— Of �d
o cn x DESCRIPTION Cn (n o-a O O 0 10 20 30 40 50 w
0
7.5-inches HMA Pavement.
[ASPHALTIC CONCRETE)
20
6-inches Portland Cement Concrete
[PCC]
Loose,brown,fine to coarse gravelly,fine to coarse SAND
:•: with cobbles and trace silt,moist to wet. •
[FILL] O S-1
iS:•
SM Loose,grayish brown,silty fine to medium SAND with trace
fine gravel,moist.
O S-2 .
♦:
♦:
p:•;. Piece of wood encountered.
Light grayish brown,gravelly SAND with trace silt and 0 S-3
. .
rootlets,moist.
-
5
♦:
G•Q �! 15
AA..:...................:....
...............
Sand becomes coarser.
Medium dense,interbedded gray,silty fine SAND with
brown fine to medium SAND,moist.
S-4
........... ... ..
Core hole was terminated at 86-inches below ground
surface due to refusal on cobbles.No ground water
seepage was observed during the exploration. ....:.......................................
:....
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit m 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-12
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
�����S�C' RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: A-1 3
BORING-DSM 2011-039.GPJ 9/28/12
ii
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 21.4 t feet
U) of W
g W of
m ¢N w Dropweight Cone Penetrometer
U a - �t N Q (17.6 lb.weight,22.6"drop) Z
J p Z (n C p ♦ Blows per foot O
x0 !n -.1 J W Z Q
F- m !n a a N W >
a U z a x O
W } (n Q Q W— H J_d
o W x DESCRIPTION (n a O O 0 10 20 30 40 50 W
0
3-inches HMA Pavement.
[ASPHALTIC CONCRETE]
6-inches Portland Cement Concrete
GW [PCC]
•' Loose,brown,well graded GRAVEL with sand and cobbles 0 S 1
and trace silt,moist to wet.
[FILL] 20
•
•'
ML Gray to light brown,sandy SILT,moist.Oxide mottling S-2
present. 0
(ALLUVIUM) !' A: '
. :....:.
Becoming light brown medium SAND to gray silt.
♦:
Interbeds/lenses of gray silt from 49-51 inches. '
O S-3
5 . .... .... .... ........�...:... ...
Core hole was terminated at 57-inches below ground >>
surface due to refusal on cobbles.No ground water
seepage was observed during the exploration. a
3
15
iZ>
10
0 20 40 60 80 100
Water Content
Plastic Limit 1 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-13
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSCIENCESINC RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-14
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 20.8 t feet
w
U co Z w Dropweight Cone Penetrometer
UL F ¢ (17.6 lb.weight,22.6"drop) Z
J O W w w r of z ♦ Blows per foot
m U D_ 0_ of y W = Q
o 2 O W m
W d } (D Q Q W.2 H 0' J_R
o v) > DESCRIPTION (n U) o- O (D 0 10 20 30 40 50 w
0
4.75-inches HMA Pavement.
[ASPHALTIC CONCRETE]
Ra: ?; 6-inches Portland Cement Concrete
A; [PCC] 20
Loose,brown,fine to coarse gravelly,fine to coarse SAND ....
b• , with cobbles and trace silt,moist to wet.
[FILL]
d.
c Q O S-1 �..
. .
SP Light brown,fine SAND with silt and trace gravel,moist.
., SM
(ALLUVIUM) + �:
O S-2
♦
♦ :
♦ .... .... ....:....:.... ....:....:....:....
Interbeds/lenses of gray silt in sample. 0 S-3
5 ♦ ... .... ....:....:....:....:....:....:....
♦ :
Core hole was terminated at 60-inches below ground
surface.No ground water seepage was observed during the
exploration. 15
♦.j... .... ....:.... ....
....:....:....:....:....:.... .
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit n 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-14
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
�A���INC RENTON
WASHINGTON
PROJECT NO.: 2011-039 FIGURE: A-1 5
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION. See Figure 2. SURFACE ELEVATION: 20.7 3 feet
W
m W m z w Dropweight Cone Penetrometer
U a L ¢ (17.6lb.weight,22.6"drop) Z
J O Z En p ♦ Blows per foot O
w W W�_ Z
m cn a a y W >�
O
W y } U) Q Q W o 0 H J_N
o cn :S DESCRIPTION W m a O 0 0 10 20 30 40 50 W
0
6-inches HMA Pavement.
[ASPHALTIC CONCRETE]
5 6-inches Portland Cement Concrete
aa�'. 20
[PCC]
GP Loose,brown,poorly graded angular GRAVEL with sand, O
° moist. S-1
SW [CRUSHED GRAVEL BASE]
• • • Loose to medium dense,brown,silty,fine to coarse O S-2
��. gravelly,fine to coarse SAND,moist.
.................................................
SP ----- [FILL] ---------/
Loose to very loose,light brown,fine to medium SAND with
GP silt,moist. /
oQ `--------------------- OS-3 �:
o Loose,grayish brown,poorly graded GRAVEL with sand,
Q moist. ....:....:....:....:....:....:....:
o Q
O
Q
°Q ....:....:....:....:....:....:....:....:...
O
Q
0::•;. Piece of wood encountered.
"' Light grayish brown,gravelly SAND with trace silt and S-4
. O
.o: ....�
rootlets,moist.
: .:• (FILUDISTURBED NATIVE) } i
Core hole was terminated at 64-inches below ground 15
surface due to refusal on cobbles.No ground water
seepage was observed during the exploration.
I
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit 1 0--I Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-15
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSSCIENCESINC RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-1 6
BORING-DSM 2011-039.GPJ 9128/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 6/6/2011
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 6/6/2011
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 20.7 t feet
U) of w
rn ui m z w Dropweight Cone Penetrometer
Um t 1-- (17.6 lb.weight,22.6"drop) z
J O w w w o ♦ Blows per foot
_ z
m a a y w x
a 2 c> 2 z o x O
wy } (n Q Q W— H 2 JN
o cn x DESCRIPTION rn m a 8 O C7 0 10 20 30 40 50 w
0
3.5-inches HMA Pavement.
[ASPHALTIC CONCRETE]
iw 7-inches Portland Cement Concrete
as. [PCC]
>;w.
20
••4:iI�.
i F•:b
• SW Loose,brown,fine to coarse gravelly,fine to coarse SAND
with silt,moist. O S-1
[FILL]
SM Medium dense,gray,silty fine to medium SAND with fine to
coarse gravel,moist.Pieces of brown silt present.
OS2
. : ----------------------
.•.• SW Loose to medium dense,light brown,fine to coarse gravelly, :....:....:....:....:....:....:....:....
fine to coarse SAND with trace silt and cobbles,moist.
0 S-3 • a a3333
33
:99
. .. :?>
33
Core hole was terminated at 36.5-inches below ground 33
surface due to refusal on cobbles.No ground water
seepage was observed during the exploration.
33
5
0 20 40 60 80 100
Water Content(%)
Plastic Limit m 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-16
HMIGEOSCIENCESINC RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-1 7
BORING-DSM 2011-039.GPJ 9128/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 7/11/2012
DRILLING METHOD: 12-inch Diamond Core DATE COMPLETED: 7/11/2012
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.7 t feet
rn w
W
co Z w Dropweight Cone Penetrometer
¢ �
U D N r W Q (17.6 Ib.weight,22.6"drop) Z
J O w w w p Blows per foot O
H
F r of z
m o- o_ of 3 w >
W Q, to Q G w H 2 J N
o" (n Z) DESCRIPTION Cn rn o- O O 0 10 20 30 40 50 W
0
7-inches HMA Pavement.
[ASPHALTIC CONCRETE]
'• 8-inches Portland Cement Concrete
;p.. [PCC]
p GW Medium dense,gray,sandy,cobbly,fine to coarse S-1 _; »
•' GRAVEL,moist to wet. !
• [FILL]
•
•
SM Medium dense,dark gray,slightly silty,gravelly,fine to O S-2
medium SAND,moist.Trace wood debris. 33
�:....:. :....:....:....:....
40
ML Medium stiff,gray,slightly sandy,SILT,moist.Organic A
debris and brown mottling observed.
[ALLUVIUM] O S-3
A
A
A 15
OL Medium stiff,brown,ORGANIC SILT,moist.
5 — .:........................:....:....:....:....
= O S-4 �: A.
Core hole was terminated at 72-inches below ground
surface due to refusal on cobbles.No ground water
seepage was observed during the e)Jloration.
10
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit I--0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-17
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSQENCES INC RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-1 8
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 7/11/2012
DRILLING METHOD: 12-inch Diamond Core DATE COMPLETED: 7/11/2012
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.6 t feet
w
U) ui m Z w Dropweight Cone Penetrometer
v � t ¢ (17.6 lb.weight,22.6"drop) Z
O w w w CO- o ♦ Blows per foot LD
F- m (n o o- 3 w Z) >
w � >- U) Q Q W H �u�i
o cn D DESCRIPTION U) U) o- O O 0 10 20 30 40 50 w
0-
6-inches HMA Pavement.
[ASPHALTIC CONCRETE]
?'> 6-inches Portland Cement Concrete
a a
GW Medium dense,gray,sandy,cobbly,fine to coarse
•' GRAVEL,moist to wet. S-1
[FILL]
....:.. .:.. .:.. .
Ground water seepage observed at 2.16 feet below ground
•' surface.(BGS)
--
SM Medium dense,dark gray,slightly gravelly,sandy SILT,
moist to wet.Trace wood debris.
S-2
ML Medium stiff,gray,SILT to CLAY,moist.Organic debris and
brown mottling observed.
[ALLUVIUM] O S-3 ♦ 15
♦ :
5 ♦.:....:....:....:....:....:....:....:....:....
OL Medium stiff,brown,ORGANIC SILT,moist.Lenses of gray
fine sand observed.
Core hole was terminated at 72-inches BGS due to refusal
on cobbles.Ground water seepage was observed at 2.16
feet BGS during the exploration.
10
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit [---" Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
=A RENTON AIRPORT TAXIWAY B REHABILITATION CORE-18
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSCIENCES INC RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-1 9
BORING-DSM 2011-039.GPJ 9/28/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 7/11/2012
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 7/11/2012
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 19.5 t feet
rn of W
g
m Z w Dropweight Cone Penetrometer W Q n W
U Q �--L F Q (17.6 lb.weight,22.6"drop) Z
J O Z W .5 W p ♦ Blows per foot O
= m U a a y w Z Q
3
W N (n Q Q W H W J (D
o W D DESCRIPTION W rn a O O 0 10 20 30 40 50 W
0
12-inches HMA Pavement.
[ASPHALTIC CONCRETE]
.................................................
7-inches Portland Cement Concrete
pa
[PCC]
a:•�.
GW Medium dense,gray,sandy,cobbly,fine to coarse
•' GRAVEL,moist to wet. S-1 "- ♦:
[FILL]
•'
ML Medium stiff,gray to brown,SILT,moist.Organic debris
and brown mottling observed. •••• •••• •
[ALLUVIUM] 0 S-2
0S3
♦ 15
--- -------------
5 — OL Medium stiff,gray,silty CLAY to clayey SILT,moist.Trace O S 4
organics observed.
♦
Core hole was terminated at 66-inches BGS due to refusal
on cobbles.No ground water seepage was observed during
the exploration.
10
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit a—i Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-19
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSCIENCES INC RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: A-20
BORINGDSM 2011-039.GPJ 9128/12
DRILLING COMPANY: Cascade Concrete Sawing and Drilling DATE STARTED: 7/11/2012
DRILLING METHOD: 8-inch Diamond Core DATE COMPLETED: 7/11/2012
SAMPLING METHOD: Hand Tools LOGGED BY: D.Coltrane
LOCATION: See Figure 2. SURFACE ELEVATION: 20.0 t feet
W Of
U) m Z w Dropweight Cone Penetrometer
V � r N C (17.6 lb.weight,22.6"drop) Z
J O w w Cn w .5 O ♦ Blows per foot
z
I=— m Cn D, ELK y W Q
2 V 2 2 z o x O w m
W } (n Q Q W— H JN
o w 7) DESCRIPTION o O O 0 10 20 30 40 50 W
0-
6-inches HMA Pavement.
[ASPHALTIC CONCRETE]
?" 7-inches Portland Cement Concrete
apt a
GW Medium dense,gray,sandy,cobbly,fine to coarse S-1
•' GRAVEL,moist to wet.
[FILL]
ML Medium stiff,gray,slightly sandy SILT,moist. 0 S-2 ""' '♦'•"""' """""""':""
[ALLUVIUM]
. ....:....:....:.........:....:....:....:....
OL Medium stiff,gray to brown,SILT to ORGANIC SILT,moist.
Organic debris and brown mottling observed. A
0s3
5 — 15
Core hole was terminated at 66-inches BGS due to refusal
on cobbles.No ground water seepage was observed during
the exploration.
10
0 20 40 60 80 100
Water Content(%)
Plastic Limit a 0 Liquid Limit
NOTE: This log of subsurface conditions applies only at the specified location and on the date indicated Natural Water Content
and therefore may not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT PAVEMENT CORE
RENTON AIRPORT TAXIWAY B REHABILITATION CORE-20
RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
HWAGEOSCIENCESINC RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-21
BORING-DSM 2011-039.GPJ 9/28/12
EXCAVATION COMPANY: Deeny Construction LOCATION: See Figure 2.
EXCAVATING EQUIPMENT: Case 590 Backhoe DATE COMPLETED: 6/3/11
SURFACE ELEVATION: 19 t Feet LOGGED BY: S.Greene
ui
g w
a- W m
U o_
w o W W ~5 z o SKETCH OF SIDE OF PIT
� � = Oa- U z _
HORIZONTAL DISTANCE(feet) a
o DESCRIPTION U) vai 2 OU 0 0 0 2 4 6 8 10 0
0 3-inch layer of grass and sod. 0
SP S-1 22
Medium dense,brown,poorly graded SAND with silt and gravel,
.............
:'.•' SM moist. : : : : : :
OH (FILL) B-1 67 AL ................... ................... ..............:.... ....:...
:
Medium stiff,grayish brown,ORGANIC SILT,with 3.5%organic GS ,,,,;,,,,;,,,,;,,,, ,,,, ,
matter,moist,plastic. In-place density of soil chunk=Dry density MD :
2 of 56.7 pcf Q 79.3%MC. CBR 2
(ALLUVIUM) :....:....:.... ....:....:....
OL Soft,gray to grayish brown,organic SILT,plastic. Contains thin S-3
layers of highly organic material,moist to wet.
Q
4 : : 4
.......... ..............
Test pit terminated at an approximate depth of 4 feet below the -
existing ground surface. Groundwater seepage was observed at an :••••:•••• ••••:••••
approximate depth of about 3.8 feet below the existing ground
6 surface. 6
8 8
10 10
NOTE: For a proper understanding of the nature of subsurface conditions,this exploration log should
be read in conjunction with the text of the geotechnical report. This log of subsurface
conditions applies only at the specified location and on the date indicated and therefore may
not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT LOG OF TEST PIT
MAL RENTON AIRPORT TAXIWAY B REHABILITATION TP-1
HWAGEOSCIENCES INC. RENTON MUNICIPAL AIRPORT PAGE: 1 Of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-22
EXCAVATION COMPANY: Deeny Construction LOCATION: See Figure 2.
EXCAVATING EQUIPMENT: Case 590 Backhoe DATE COMPLETED: 6/3111
SURFACE ELEVATION: 19 t Feet LOGGED BY: S.Greene
C6 of
g co W
w
U o- uJ Q
w 0 W w W Z SKETCH OF SIDE OF PIT
0
a U z = o HORIZONTAL DISTANCE(feet) (L
O (n 7) DESCRIPTION uai uai m o O (3 0 2 4 6 8 10 0
0 >_• 3-inches of grass and sod. 0
ML Medium dense,gray silty SAND with trace fine gravel,moist. S-1 11 .
(FILL) :....:....:.... ....:....:....:.... ....:... ..........
ML Dense,gray,sandy SILT with fine gravel,moist. S-2 25
Medium stiff,brownish gray SILT with fine sand,moist,low plastic. .... """' .... """' .... "=""
2 OH Soft,gray to dark brown,ORGANIC SILT,moist to wet,plastic. B-1 102 AL 2
In-place density of soil chunk=dry density of 48.7 pcf @ 134.2% S-3 213 MD
(ALLUVIUM) CBR :....:....:.... ....:....:....:.... ....:...
4 4
:....:.... ....:.............. .........
Test pit excavation terminated at an approximate depth of 4 feet
below the existing ground surface. Ground water seepage was •••• .... •••• •••• •••• •••• •••• ••••
observed at an approximate depth of 3.5 feet below the existing
6 ground surface. 6
.......... ......
Buried concrete storm drain pipe exposed within south sidewall of
test pit excavation between depths of 1.5 to 2.5 feet below the •••• •••• •••• •••• •••• •••• •••• •••• •••• •••• •••• •••• ••••
existing ground surface. Based upon position of pipe bell flow
direction appears to be toward taxiway infield(west). .... """' .... """' .... """' .. ""
8 8
10 10
NOTE: For a proper understanding of the nature of subsurface conditions,this exploration log should
be read in conjunction with the text of the geotechnical report. This log of subsurface
conditions applies only at the specified location and on the date indicated and therefore may
not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT LOG OF TEST PIT
RENTON AIRPORT TAXIWAY B REHABILITATION TP-2
HWAGEOSQENCES INC. RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-23
TPIT10 2011-039.GPJ 9/28/12
EXCAVATION COMPANY: Deeny Construction LOCATION: See Figure 2.
EXCAVATING EQUIPMENT: Case 590 Backhoe DATE COMPLETED: 6/3/11
SURFACE ELEVATION: 20 t Feet LOGGED BY: S.Greene
of
w
LU m U r � Q
o ° J J 5 P.W °z SKETCH OF SIDE OF PIT
n~. Co 0 2 2i O o F 0 HORIZONTAL DISTANCE(feet) d
0 Y) D DESCRIPTION CO uai �0 O c7 0 2 4 6 8 10 0
0 �' 3-inches of grass and sod. 0
GP S-1
Medium dense,brown,sandy GRAVEL with silt,moist.
ME (FILL) 8 S-2 16
................... ................... ................... ...................
Medium dense,grayish brown,fine sandy SILT,moist,non-plastic.
....:....:....:.... ....:....:....:.... ....:....
ML Loose to medium stiff,olive gray,sandy SILT,moist,non plastic. B-1 25 GS
2 In-place density of soil chunk=dry density 98.0 pcf @ 25%MC. 11 MD 2
GBR
....:....:....:.... ....:....:....:.... ....:.... :.... ....:....
OL Medium stiff to soft,gray to grayish brown,organic SILT,moist to O S-4 51
wet,low plastic. 57 ....:....:.... ....:....:...
4 (ALLUVIUM) 4
....:....:....:.... ....:....:....:.... ....:....:....:.... ....:....:....:.... ....:....:....:....
Test pit excavation terminated at an approximate depth of 4 feet
below the existing ground surface. Ground water seepage was .... -•••:••• .... ... ....:....:.... ....:....:....
observed at an approximate depth of 3.6 feet below the existing
6 ground surface. 6
8 8
10 10
NOTE: For a proper understanding of the nature of subsurface conditions,this exploration log should
be read in conjunction with the text of the geotechnical report. This log of subsurface
conditions applies only at the specified location and on the date indicated and therefore may
not necessarily be indicative of other times and/or locations.
FINAL GEOTECHNICAL ENGINEERING REPORT LOG OF TEST PIT
RENTON AIRPORT TAXIWAY B REHABILITATION TP-3
HWAGEOSCIENCES INC. RENTON MUNICIPAL AIRPORT PAGE: 1 of 1
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: A-24
Torn+n 1011-01n -/28/12.
APPENDIX B
LABORATORY TESTING
GRAVEL SAND
SILT CLAY
Coarse Fine I Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 15/8" 3/8" #4 #10 #20 #40 #60 #100 #200
100
I I I I I I
I I I I I I I I I
90
I I I I I I I I I
I 1 1 I I I I I I I
80
= I I I I 1 I I I I I
70
LU I I I I I I I I I
p}p 60 I I I I I I I I I I
Lu 50 I I I I I I I
Z I I I I I I I I
ILL I I I I I I I I I
H 40 1 I I I I I I I I
Z
LU I I I I I I I I I
30
Lu I I I I I I I 1 I I
20
I I I I I I I I I I
i I I I I I I I I
10
I I I I I I I I I
I I I I I I I I I
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
o " o
• CORE-01 S-3 0.6-1.3 (GP)Dark olive brown,poorly graded GRAVEL with sand 5 52.7 43.4 3.9
■ CORE-02 S-4 2.0-2.5 (ML)Dark olive to gray,sandy SILT with 1.2%organic matter by dry weight 25 25 22 3 1.4 28.1 70.5
A CORE-03 S-4 2.3-2.8 (ML)Dark olive brown,SILT with 1.6%organic matter 39 1.6 29.3 69.1
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
fMGE0saENCES INC RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: B-1
HWAGRSZ 2011-039.GPJ 9128/12
GRAVEL I SAND SILT CLAY
Coarse Fine I Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 5/8" 3/8" #4 #10 #20 #40 #60 #100 #200
100
I I I I I I I I I
I I I I I I I
90
I I I I I I I I I I
I 1 1 I 1 I I I I
80
= I I I I I I I I I I
70
w I I I I I I I I I
00
60
w 50 I I I I I I I I I I
Z I II I I I I I
LL I I I I I I I I I
F- 40 I I I I I I I I I
Z I I I I 1 I I I I
0 w I I I I I I I 1
30
w I I I I I 1 I I
20
I I I I I I I I I
I I I I I I I I I
10
1 1 1 I I I I I I
i I I I I I I
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
0 o a
• CORE-05 S-3 1.0-2.4 (SM)Dark Gray,silty SAND with gravel,contains glass and shell fragments. 37 18.9 55.5 25.6
■ CORE-06 S-2 2.9-3.1 (SM)Dark grayish brown,silty SAND with gravel 10 44.3 37.1 18.6
CORE-07 S-1 1.3-1.6 (GP)Gray,poorly graded GRAVEL with sand 5 54.0 42.5 3.5
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
got, RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
HWAaosams INC. RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: B-2
"'"'"^^SZ 20""""^PJ 9/""""
GRAVEL SAND SILT CLAY ]
Coarse Fine Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 15/8" 3/8" #4 #10 #20 #40 #60 #100 #200
100
I I I 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
80
= I I I I I I I I I I
70
w 1 I I I I I I I I
60 I I I I I I I I I
m I 1 1 I I I I I I
W i I I I I I I I I I
Z 50
LL
H 40 1 1 1 I I I I I I I
z I I I I I I I I I I
W I I I I I I I I I I
30
LU I I I I I I I I I I
a I I I I I 1 I I I I
20
I I I I I I I I I I
I I I I I 1 I I I I
10
I I I I I I I I I I
I I I I I I I I I I
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
o "
• CORE-08 (ML)Dark olive brown,SILT with sand 23 3.6 33.8 62.6
■ CORE-08 S-3 4.2-4.4 (OH)Dark grayish brown,organic SILT 114 108 74 34 3.8 10.8 85.5
A CORE-09 S-2 2.3-2.7 1 (SM)Dark olive brown,silty SAND with gravel 15 17.2 43.4 39.4
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
HmaosaEwES INC. RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: B-3
HWAGRSZ 2011-039.GPJ 9/28/12
GRAVEL SAND SILT CLAY
Coarse Fine Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 15/8" 3/8" #4 #10 #20 #40 #60 #100 #200
100
I I I I I I I I I I
90
I 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 I
CD 70
W I I I I I I I I I
pip 60 I I I I I I I I I
z 50 I I I I I I I I I I
LL I I I I I I I I I
H 40 I I I I I I I I I
z I I I I I 1 I I I
W I I I I I I I I I I
30
w I I I I I I I I I I
20
I I I I I I I I I I
I I I I 1 I I I I
10
I I I I I I I I I
1 I I I I I I
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
• CORE-11 S-2 3.0-3.5 (SM)Dark olive brown,silty SAND 16 13.4 51.2 35.4
■ CORE-12 S-2 2.8-3.3 ISM)Brown,silty SAND 14 14.5 49.0 36.5
CORE-13 S-1 1.0-1.3 (GW)Dark olive brown,well graded GRAVEL with sand 3 70.1 26.8 1 3.0
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
90,11 RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
IMGEOSCIENCES INC. RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: B-4
NInier_ocZ 201'-mo r_PJ 9/2n111
GRAVEL I SAND
Coarse Fine Coarse Medium Fine SILT CLAY
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 15/8" 3/8" #4 #10 #20 #40 #60 #100 #200
100�
I I I I I I I I I
I I I I I I I
90
I 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 I I
70
w I I I I I I I I I I
r 60 I I I I I I I 1 I
ca I I I I I I I I I
LU 50 I I I I I I I I I
Z I I I I I I I I I I
LL I I I I I I I I I I
z ao
w I I I I I I I I I I
C) I I I I 1 I I I I
rr_l 30
w I I I I I I I I I I
20
I 1 1 I I I I I I
I I I I I I I I
10
I I I I I I I
I I I I I I I I I
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fio es
• CORE-13 S-2 2.5-2.9 (ML)Brown,SILT with sand 21 14.6 29.7 55.7
■ CORE-14 S-3 4.4-4.8 (SP-SM)Brown,poorly graded SAND with silt 9 0.5 87.8 11.7
A CORE-15 S-1 1.2-1.4 (GP)Olive brown,poorly graded GRAVEL with sand 6 81.5 13.1 5.4
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
15%GEOSCIENCES INC. RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: B-rJ
HWAGRSZ 2011-039.GPJ 9/28/12
GRAVEL I SAND SILT CLAY
Coarse Fine I Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 1 5/8" 3/8" #4 #10 #20 #40 #60 #100 #200
100�
I I I I I IIT 71,
I
1 I I
90
I I I I I I I I
I I I I 1 I I I I
80
= I I I I I 1 I I I
U 70
LU I I I I I I I I I
3: I 1 I I I 1 1 1 I
m 60 I 1 1 I I I I I I I
W 50 I I I I I I I I I
Z I I I I I I I I I I
LL I I I I I I I I I
I— 40 I I I I I I I I I
Z I I I I I I I I
w I I I I I I I I I
30
Uj
d I I I I I I I I I I
20
I I I I I I I I I
I I I I I I I I I
10
I I I I I I I I I
I I I I I I I I I
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
" o 0
• CORE-15 S-4 4.7-5.2 (GP)Olive brown,poorly graded GRAVEL with sand 5 54.5 41.7 3.9
■ CORE-16 S-2 1.5-1.7 (SM)Brownish gray,silty SAND with gravel 25 16.2 49.1 34.7
A TP-1 B-1 0.9-2.5 (OH)Light olive brown,organic SILT with 3.5%organic matter 67 122 68 54 0.0 4.1 95.9
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
Hmaosamas INC RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: B-6
Nminr_PSZ 201 tnao r_PJ 9/121"
GRAVEL I SAND
Coarse Fine Coarse Medium Fine SILT CLAY
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-112" 5/8" 3/8'. #4 #10 #20 #40 #60 #100 #200
100
1 II I I
I I I I I I I I
90
I I I I I I I I I
80
F-
T_ I I I I I I I I
70
LU I I I I I I I I I I
m 60 I I I I I I I I I I
w 5o I I I I I I I I 1 I
z
�
I I I I I I I I I I
I I I I I I I I I I
F— 40 I I I I I I I I I I
Z I I I I I I I I I I
w I I I I I I I I I I
30
w I I I I I I I I I I
w 1 I I I I I I I I I
20
I I I I I I i I I I
I I I I I I I I I I
10
I I I I I I I I I I
I I I I I I I I I 1
0
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI t3.922.4
Fines
• TP-2 S-2 1.1 -2.0 (ML)Brownish gray,SILT with sand 25 73.7
■ TP-2 B-1 2.0-2.5 (OH)Dark Brown,organic SILT 102 84 62 22 96.1
A TP-3 B-1 1.5-2.0 (ML)Dark olive gray,SILT with sand 25 0.0 23.7 76.3
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
fMGE0saENCES INC. RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: B-7
HWAGRSZ 2011-039.GPJ 9/28112
GRAVEL SAND SILT CLAY
Coarse Fine Coarse Medium Fine
U.S. STANDARD SIEVE SIZES
3/4"
3" 1-1/2" 5/8" 3/8" #4 #10 #20 #40 #60 #100 #200
100
I I I I I I I I I
I I I I I I I I I I
90
I I I I I I I I I
I I I I I I I I I I
ao
= I I I I I I I I I I
2 70
w I I I I I I I I I I
m 6o I I I I I I I I I I
w 50
Z I I I I I I I 1 I I
U_ I I I I I I I I I I
I— 40 I I I I I I I I I I
z I I I I I I I I I I
w I I I I I I I I I I
30
w I I I I I I I I I I
w I I I I I I I I I I
20
I I I I I I I I I I
I I I I I I I I I I
10
0 Tf F
I I I I I II I I
I I I I I I I 1—t
I I
50 10 5 1 0.5 0.1 0.05 0.01 0.005 0.001 0.0005
GRAIN SIZE IN MILLIMETERS
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION OF SOIL-ASTM D2487 Group Symbol and Name %MC LL PL PI Gravel Sand Fines
0 o a
• TP-3 S-4 3.0-4.0 (OH)Dark gray,organic SILT 51 55 31 24 0.0 11.6 88.4
FINAL GEOTECHNICAL ENGINEERING REPORT PARTICLE-SIZE ANALYSIS
RENTON AIRPORT TAXIWAY B REHABILITATION OF SOILS
tmuoSCImu INC. RENTON MUNICIPAL AIRPORT METHOD ASTM D422
RENTON, WASHINGTON
PROJECT NO.: 201 1-039 FIGURE: B-H
NInIenacZ 201'-neon-oJ 9/2A"O
60
CL CH
50
CL
X 40
W
0
Z_ �
30 01
H
U
H
Q 20
J
10
CL-ML 1 ML MH
•
0
0 20 40 60 80 100
LIQUID LIMIT (LL)
SYMBOL SAMPLE DEPTH(ft) CLASSIFICATION %MC LL PL PI %Fines
• CORE-02 S-4 2.0-2.5 (ML)Dark olive to gray,sandy SILT with 1.2%organic matter by dry weight 25 25 22 3 70.5
■ CORE-06 S-3 3.8-4.3 (OH)Dark brownish gray,organic SILT,contains 4.4%organic mattter. 58 52 37 15
A CORE-08 S-3 4.2-4.4 (OH)Dark grayish brown,organic SILT 114 108 74 34 85.5
O TP-2 B-1 2.0-2.5 (OH)Dark Brown,organic SILT 102 84 62 22 96.1
❑ TP-3 S-4 3.0-4.0 (OH)Dark gray,organic SILT 51 55 31 24 88.4
FINAL GEOTECHNICAL ENGINEERING REPORT LIQUID LIMIT, PLASTIC LIMIT AND
RENTON AIRPORT TAXIWAY B REHABILITATION PLASTICITY INDEX OF SOILS
HMGEOSCIENCES INC. RENTON MUNICIPAL AIRPORT METHOD ASTM D4318
RENTON, WASHINGTON
PROJECT NO.: 2011-039 FIGURE: B-g
HWAATTB 2011-039.GPJ 9/28/12
LABORATORY COMPACTION CHARACTERISTICS OF SOIL U0
CLIENT: Reid Middleton HWAGEOSCIENCES INC.
PROJECT: Renton Taxiway B SAMPLE ID: TP-1, B-1
PROJECT NO: 2011-039 Sampled By: SEG Tested By: JH
Date Sampled: 61612011 Date Received: 61612011 Date Tested: 611412011
MATERIAL TYPE OR DESCRIPTION:
Light grayish brown, organic SILT OH
MATERIAL SOURCE, SAMPLE LOCATION AND DEPTH:
TP-1, 2 ft b s
Designation:�X ASTM D 698 F-]ASTM D 1557 Natural Moisture Content: 79.3 %
Method: F-]A F-]B ❑X C Oversize: 0 % retained on: 3/4 in.
Preparation: Dry EE Moist Rammer:�X Auto Manual Assumed S.G.: 2.4
Test Data
Dry Density (pcf) 62.2 63.7 1 64.1 1 61.5
Moisture Content (%) 24.6 26.8 29.3 31.4
70
_ Rock Corrected Curve
per ASTM D4718
Lab Proctor Curve
65 _._._.. 100%Saturation Line
C;- -
u
a
60
m
55
50
20 22 24 26 28 30 32 34 36 38 40
Moisture Content(%)
Data Summary* Test Values At Other Oversize Percentages
Percent Oversize <5% 0.0% 5.0% 10.0% 15.0% 20.0% 25.0% 30.0%
Max. Dry Density(pcfl* 64.4 64.4 66.3 68.3 1 70.4 72.7 75.1 77.7
Optimum Moisture(%)* 28.5 28.5 27.1 25.8 1 24.4 23.0 21.6 20.3
values corrected or oversize matenaFper-AM D4718,using assumed Specific Gravity shown and oversize moisture content of 1%
Reviewed By: Steven Greene FIGURE B-10
This report applies only to the items tested,and may be reproduced in full,with written approval of HWA GEOSCIENCES INC.
LABORATORY COMPACTION CHARACTERISTICS OF SOIL ir"n
CLIENT: Reid Middleton HWAGEOSCIENCES INC.
PROJECT: Renton Taxiway B SAMPLE ID: TP-2, B-1
PROJECT NO: 2011-039 Sampled By: SEG Tested By: JH
Date Sampled: 61612011 Date Received: 61612011 Date Tested: 611312011
MATERIAL TYPE OR DESCRIPTION:
Dark brown, organic SILT OH
MATERIAL SOURCE, SAMPLE LOCATION AND DEPTH:
TP-2, 2 ft b s
Designation:❑ASTM D 698 �X ASTM D 1557 Natural Moisture Content: 134.2 %
Method: F-]A F-1B QX C Oversize: 0 % retained on: 314 in.
Preparation:0 Dry �X Moist Rammer:�X Auto 0manual Assumed S.G.: 2.4
Test Data
Dry Density (pcf) 1 55.2 11 58.9 1 59.8 1 58.2
Moisture Content (%) 55.9 57.7 59.0 62.0
70
Rock Corrected Curve
r per ASTM D4718
Lab Proctor Curve
65 1 77T _._._.. 100%Saturation Line
c
a
60
m
o -
0
55
50
50 52 54 56 58 60 62 64 66 68 70
Moisture Content(%)
Data Summary* Test Values At Other Oversize Percentages
Percent Oversize <5% 0.0% 5.0% 10.0% 15.0% 20.0% 25.0% 30.0%
Max. Dry Density (pcf)* 59.9 59.9 61.8 63.7 65.8 68.1 70.5 73.1
Optimum Moisture (%)* 59.5 59.5 56.6 53.7 1 50.7 47.8 44.9 42.0
values corrected or oversize ma ena per D4718,using assumed Specific Gravity shown and oversize moisture content of 1%
Reviewed By: Steven Greene FIGURE B-11
This report applies only to the items tested,and may be reproduced in full,with written approval of HWA GEOSCIENCES INC.
LABORATORY COMPACTION CHARACTERISTICS OF SOIL KFW
CLIENT: Reid Middleton HWAGEOSCIENCES INC.
PROJECT: Renton Taxiway B SAMPLE ID: TP-3, B-1
PROJECT NO: 2011-039 Sampled By: SEG Tested By: JH
Date Sampled: 61612011 Date Received: 61612011 Date Tested: 611012011
MATERIAL TYPE OR DESCRIPTION:
Dark gray, silty SAND SM
MATERIAL SOURCE, SAMPLE LOCATION AND DEPTH:
TP-3, 2 ft b s
Designation:F-]ASTM D 698 �X ASTM D 1557 Natural Moisture Content: 25 %
Method: F-]A [--]B �X C Oversize: 0 % retained on: 314 in.
Preparation: Dry �X Moist Rammer:EAuto Omanual Assumed S.G.: 2.4
Test Data
Dry Density (pcf) 1 101.9 1 108.6 1 106.3 1 102.3 1 110.4
Moisture Content (%) 10.7 1 13.0 18.6 20.7 15.4
120
Rock Corrected Curve
per ASTM D4718
115 ------ Lab Proctor Curve
--- 100%Saturation Line
110 ---
u
a
105
100
95
90
5 7 9 11 13 15 17 19 21 23 25
Moisture Content(%)
Data Summary* Test Values At Other Oversize Percentages
Percent Oversize <5% 0.0% 5.0% 10.0% 15.0% 20.0% 25.0% 30.0%
Max. Dry Density(pcf)* 110.5 110.5 112.0 113.5 1 115.0 116.6 118.3 119.9
Optimum Moisture (%)* 15.0 15.0 14.3 13.6 1 12.9 12.2 11.5 10.8
values corrected or oversize material per ASTIVI D4718,using assumed Specific Gravity shown and oversize moisture content of 1%
Reviewed By: Steven Greene FIGURE B-12
This report applies only to the items tested,and may be reproduced in full,with written approval of HWA GEOSCIENCES INC.
CBR(California Bearing Ratio) OF LAB COMPACTED SOILS
(ASTM D 1883) Y
CLIENT: Reid Middleton HWAGEOSCIENCES INC.
PROJECT: Renton Taxiway B SAMPLE ID: TP-1, B-1
PROJECT NO: 2011-039-21 Sampled By: SEG Tested By: AAC/JH
Date Sampled: 61212011 Date Received: 61212011 Date Tested: 612012011
Material Description: Light olive brown, organic SILT(OH)
Sample Location: Test Pit TP-2 Sample B-1
Compaction Standard: �X D698 EflD1557 Condition: �X Soaked for 96 hrs F]Unsoaked
Max. Dry Density: 64.4 pcf @ 28.5 % M.C. with 0 % scalped-off on the 3/4" sieve
Trial 1 Trial 2 Trial 3
Dry Density c 37.0
Percent Compaction 57.4
Moisture before Compaction % 118.2
Moisture after Compaction % 131.9
Percent Swell (initial ht=7") -3.5
Moisture, after Soaking % 122.7
Moisture Top 1" after Soak % 109.2
CBR at 0.1" Penetration 0.4
CBR at 0.2" Penetration 0.4
CBR Value 0.4
12
10
8
y
G
N 6
4
2
LZ i
0
0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 0.40 0.45 0.50
Displacement(in)
5.0
4.0
3.0
m
V 2.0 --
i
1.0
L fl 0.0
50 55 60 65 70 75 80 85 90 95 100
%Compaction
REVIEWED BY: Steven Greene FIGURE: B-13
CBR(California Bearing Ratio) OF LAB COMPACTED SOILS
(ASTM D 1883) �YYii
CLIENT: Reid Middleton HWAGEOSCIENCES INC.
PROJECT: Renton Taxiway B SAMPLE ID: TP-2, B-1
PROJECT NO: 2011-039-21 Sampled By: SEG Tested By: AAC/JH
Date Sampled: 61212011 Date Received: 61212011 Date Tested: 612012011
Material Description: Dark brown, organic SILT(OH)
Sample Location: Test Pit TP-2 Sample B-1
Compaction Standard: F-]D698 �X D1557 Condition: ❑X Soaked for 96 hrs F]Unsoaked
Max. Dry Density: 59.9 pcf @ 59.5 % M.C. with 0 % scalped-off on the 3/4" sieve
Trial 1 Trial 2 Trial 3
Dry Density c 39.3
Percent Compaction 65.6
Moisture before Compaction % 122.7
Moisture after Compaction % 111.3
Percent Swell initial ht=7" -5.9
Moisture, after Soaking % 109.3
Moisture To 1" after Soak % 100.2
CBR at 0.1" Penetration 0.5
CBR at 0.2" Penetration 0.6
CBR Value 0.6
18
16
14
12 -
a 10
a _
y
8
N
6 -
4
2
0
0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 0.40 0.45 0.50
Displacement(in)
5.0 _
4.0
a 3.0
m
v 2.0
1.0
0.0
50 55 60 65 70 75 80 85 90 95 100
%Compaction
REVIEWED BY: Steven Greene FIGURE: B-14
CBR(California Bearing Ratio) OF LAB COMPACTED SOILS
(ASTM D 1883) Y
CLIENT: Reid Middleton HWAGEOSCIENCES INC.
PROJECT: Renton Taxiway B SAMPLE ID: TP-3, B-1
PROJECT NO: 2011-039-21 Sampled By: SEG Tested By: AAC/JH
Date Sampled: 61212011 Date Received: 61212011 Date Tested: 612012011
Material Description: Dark olive gray, SILT with sand(ML)
Sample Location: Test Pit TP-3 Sample B-1
Compaction Standard: F]D698 �X D1557 Condition: �X Soaked for 96 hrs F]Unsoaked
Max. Dry Density: 110.5 pcf @ 15 % M.C. with 0 % scalped-off on the 3/4" sieve
Trial 1 Trial 2 Trial 3
Dry Density c 94.5 112.9 #N/A
Percent Compaction 85.5 102.1 #N/A
Moisture before Compaction % 25.5 15.4 #DIV/0!
Moisture after Compaction % 25.2 15.0 #DIV/0!
Percent Swell initial ht= 7") -0.1 0.5 0.0
Moisture, after Soaking (%) 27.3 17.0 #DIV/0!
Moisture Top 1" after Soak % 25.5 19.4 #DIV/0!
CBR at 0.1" Penetration 0.9 51.4 #DIV/0!
CBR at 0.2" Penetration 1.2 53.8 #DIV/0!
CBR Value 1.2 53.8 #DIV/0!
1600
--0-85.5
1400 102.1
1200
1000
Q
in 800
N
600
400
200
0
- 0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 0.40 0.45 0.50
Displacement(in)
60
50
40
v 30
20 --
10
0
80 85 90 95 100 105
%Compaction
REVIEWED BY: Steven Greene FIGURE: B-15
i
Bulk Density of Soil Chunk Samples
Renton Airport Taxiway B vial HWA GEOSCIENCES INC.
Exploration Sample No. Depth Length Diameter Volume Tare Wet+Tare Bulk Density Tare W+T D+T MC Dry Density
TP-1 B-1 0.9 6 2.4 0.0157 248 849.83 84.6 8.32 191.5 110.51 79.3% 47.2
TP-2 B-1 2 6 2.4 0.0157 248 924.15 95.1 8.13 183.73 83.11 134.2% 40.6
TP-3 B-1 1.5 6 2.4 0.0157 248 973.92 102.1 8.48 198.17 160.22 25.0% 81.6
HWA Project No. 2011-039 FIGURE B-16
APPENDIX C
CORE PHOTOGRAPHS
ULWA
I
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 2, 2011 Sampled by: SEG
Core Bit Used: 8-inch diameter
Sample Location: Northern Taxiway Connector(see Figure 2)
Core Designation: Core-1
Ili
l�
-� 2 cM - 0
I �
Total Wearing Surface Depth: 2 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
2.0 Hot Mix Asphalt(HMA) 2 Fair
5 CSTC/CSBC - Dense
Gravel with sand and _ Medium dense to dense
Cobbles
Remarks:
MIMI
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 2, 2011 Sampled by: SEG
Core Bit Used: 8-inch diameter
Sample Location: North end of Taxiway B (See Figure 2)
Core Designation: Core-2
f
03q
Co 2
re
.1 4{: .-�;l•_ ,.y: . Y'w!,�' ♦per •�
Total Wearing Surface Depth: 4.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
4.5 HMA 4.5 Fair to good
5.0 CSTC/CSBC - Dense
- Sand with gravel - Medium dense to dense
Remarks:
HWAGEOSCIENCES INC.
rClient: Reid Middleton
' Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 2, 2011 Sampled by: SEG
Core Bit Used: 8-inch diameter
rSample Location: North end of Taxiway B (See Figure 2)
Core Designation: Core-3
r
r = ._
t =
2n� 1 _ Oil
Fore- 3
i
r
r
1
rTotal Wearing Surface Depth: 2.25 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
' 2.25 HMA 2.25 Poor to fair
1.5 CSBC - Dense
2.25 Sandy silt - Medium stiff
Remarks: The subgrade becomes sand to silty sand with depth
r
JLWA I I
HWAGEOSCIENCES INC.
Client: Reid Middleton '
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 2 and June 8, 2011 Sampled by: SEG/DRC
Core Bit Used: 8-inch diameter
Sample Location: North end of Taxiway B (See Figure 2)
Core Designation: Core-4
039
cof e
y
Js
Total Wearing Surface Depth: 1.5 inches
Thickness Description of Material Lifts inches Condition
(inches) p )
1.5 HMA 1.5 Poor '
1.4 CSBC - Dense
1.75 HMA 1.75 Good
Gravel - Loose
Remarks: 1.4 inches of crushed gravel between HMA layers
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 2, 2011 Sampled by: SEG
Core Bit Used: 8-inch diameter
Sample Location: North central portion of Taxiway B (See Figure 2)
Core Designation: Core-5
Total Wearing Surface Depth: 2 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
2 HMA 2 Good
6 CSBC - Dense
- Sand with silt and gravel - Medium dense
Remarks: With depth subgrade appears to consist of dredge spoils.
[rLWA,
HWAGEOSCIENCES INC.
Client: Reid Middleton
i
Project: Taxiway B—Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 7, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Central portion of Taxiway B (See Figure 2)
Core Designation: Core-6
t_
•
r
ZGn- 039
Total Wearing Surface Depth: 14.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
8.5 HMA 3, 5.5 Poor to good
6 PCC 6 Fair to good
- Sand with gravel and cobbles - Loose
i
Remarks: The bottom 5.5 inches of HMA is of lower quality(ATB?)
No crushed gravel base course was encountered.
' HWAGEOSCI ENCES INC.
' Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 7, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: South end of Taxiway B (See Figure 2)
Core Designation: Core-7
cb
2oi�_ 03�
Core_-
Total Wearing Surface Depth: 13.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
' 8.5 HMA 3.5, 5 Very poor
5 PCC 5 Very poor
' Sand with gravel, cobbles -
and silt Loose
Remarks: The bottom 5 inches of HMA is of lower quality (ATB?) and disintegrated
coring and therefore does not appear in the above photo.
No crushed gravel base course was encountered.
U �
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport ,
Project No.: 2011-039 Task No: 100
Date Sampled: June 7, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: South End of Taxiway B (See Figure 2)
Core Designation: Core-8
r
Zoll _D39 '
Core- 8
Total Wearing Surface Depth: t2 inches
Thickness
(inches) Description of Material Lifts (inches) Condition
5.5 HMA 2.5, 3 Good
6.5 PCC 6.5 Good
Sand with gravel, cobbles - Loose
and silt
Remarks: A non-woven fabric layer is located between the two lifts of HMA
No crushed gravel base course was encountered.
� M
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 7, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: South end of Taxiway B (See Figure 2)
Core Designation: Core-9
i
20n_ 039
(ore -9
Total Wearing Surface Depth: 10 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
10 HMA 2.5, 4.25, 3.25 Good to poor
- Sand with gravel, cobbles _ Loose
and silt
Remarks: A non-woven fabric layer is located between the first two lifts of HMA
The lower lift of HMA is of lower quality(ATB?)
No crushed gravel base course was encountered.
i
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 6, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Infield apron South end of Taxiway B (See Figure 2)
Core Designation: Core-10
i
core
Total Wearing Surface Depth: 2.25 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
2.25 HMA 2.25 Good
F-- Gravel with sand - Dense to very dense
Remarks: No crushed gravel base course was encountered.
JLTI
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 7, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: South end of Taxiway B (See Figure 2)
Core Designation: Core-11
i
039
Coco-1\
Total Wearing Surface Depth: 16.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
8.5 HMA 2.5, 2.5, 3.5 Good to fair
' 8 PCC 8 Fair to good
- Sand with gravel and cobbles - Loose
Remarks: A non-woven fabric layer is located between the bottom lift of HMA and
PCC. The lower lift of HMA is of lower quality (ATB?)
�' No crushed gravel base course was encountered.
1
J LWA,
HWAGEOSCIENCES INC.
r
Client: Reid Middleton r
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 6, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Southern Taxiway Connector(See Figure 2) '
Core Designation: Core-12
r
f i
e ri
,H
t '
s
. r
r
2011_039
Copt-IZ r
r
Total Wearing Surface Depth: 13.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
7.5 HMA 3.5, 2 , 2 Good
6 PCC 6 Fair ,
- Sand with gravel and cobbles - Loose
r
Remarks: No crushed gravel base course was encountered.
r
HWAGEOSCIENCES INC.
Client: Reid Middleton
' Project: Taxiway B—Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 6, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Southern Taxiway Connector(See Figure 2)
Core Designation: Core-13
zo L
v,
2.011_ n39
13
1
Total Wearing Surface Depth: 9 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
3 HMA 3 Fair to poor
6 PCC 6 Fair
- Sand with gravel and cobbles - Loose
Remarks: A non-woven fabric layer is located between the bottom lift of HMA and
' PCC. No crushed gravel base course was encountered.
JLWA
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport ,
Project No.: 2011-039 Task No: 100
Date Sampled: June 6, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Southern Taxiway Connector(See Figure 2)
Core Designation: Core-14
' oh- 03q ,
Coct-1�
1
Total Wearing Surface Depth: 10.75 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
4.75 HMA 4.75 Fair to good
6 PCC 6 Good
- Sand with gravel and cobbles - Loose
Remarks: No crushed gravel base course was encountered.
U -e
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B —Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 6, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Southern Taxiway Connector(See Figure 2)
Core Designation: Core-15
t
t
,y1
„y.
201�- p39
Core_IS
Total Wearing Surface Depth: 12 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
6 HMA 4, 2 Good to poor
6 PCC 6 Good
4.5 CSBC - Loose
- Sand with silt and gravel - Loose to medium dense
Remarks: The lower lift of HMA is of lower quality (ATB?).
U M
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B—Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: June 6, 2011 Sampled by: DRC
Core Bit Used: 8-inch diameter
i
Sample Location: Southern Taxiway Connector(See Figure 2)
Core Designation: Core-16
w
Core_ 16
Total Wearing Surface Depth: 10.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
3.5 HMA 1.5, 2 Fair to poor
7 PCC 7 Poor
Sand with silt and gravel - Loose
Remarks: A non-woven fabric layer is located between the lowest HMA and the PCC
layers. The PCC layer is cracked through and sealed with asphalt sealant
No crushed gravel base course was encountered.
UWA
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: July 11, 2012 Sampled by: DRC
Core Bit Used: 12-inch diameter
Sample Location: South end of Taxiway B (See Figure 2)
Core Designation: Core-17
i
I i
i ry s
a
! i
i
ZOtI-p39 '
' 2011-03q
Total Wearing Surface Depth: 15 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
7 Hot Mix Asphalt (HMA) 2.5, 4.5 Good to Fair
8 PCC 8 Fair
- Gravel with sand and cobbles - Medium dense
Remarks: There is a 0.75 inch deep and 1.25 inch wide asphalt seal in the middle of
the core covering a crack in the upper HMA layer(see Photo above).
moil & I
HWAGEOSCI ENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: July 11, 2012 Sampled by: DRC
Core Bit Used: 12-inch diameter
Sample Location: South end of Taxiway B (See Figure 2)
Core Designation: Core-18
c ,µ
4�
2oit-o3a
Total Wearing Surface Depth: 12.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
6.5 HMA 2.75, 3.75 Fair to good
6 PCC 6 Fair
- Gravel with sand and cobbles - Medium dense
Remarks:
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B - Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: July 11, 2012 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: Southern Taxiway Connector(See Figure 2)
Core Designation: Core-19
i
i
I �
2oli-o3q
CORE- 19
Total Wearing Surface Depth: 19.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
12.5 HMA 3, 2.5, 3, 4 Fair to good
7 PCC 7 Good
- Gravel with sand and cobbles - Medium dense
Remarks: There is no bond between the 2nd and 3rd layers of HMA.
There is no bond between the 3rd and 4`h layers of HMA.
HWAGEOSCIENCES INC.
Client: Reid Middleton
Project: Taxiway B—Renton Municipal Airport
Project No.: 2011-039 Task No: 100
Date Sampled: July 11, 2012 Sampled by: DRC
Core Bit Used: 8-inch diameter
Sample Location: South end of Taxiway B (See Figure 2)
Core Designation: Core-20
' 03i01
r
,t`•' fir` 6 -2-0
fia 40 ,
f
CORE-20
Total Wearing Surface Depth: 13.5 inches
Thickness Description of Material Lifts (inches) Condition
(inches)
6 HMA 3.5, 2.5 Poor
7.5 PCC 7.5 Fair
- Gravel with sand and cobbles - Medium Dense
Remarks: There is a 0.5 inch deep and 0.75 inch wide asphalt seal in the middle of the
core covering a crack in the upper HMA layer(see Photo above).
Appendix B
City of Renton Sensitive Areas
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II
Technical Information Report (TIR)
' I
;I
AKE WASHINGTON
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AQUIFER PROTECTION ZONES
Renton Municipal Code
Y Technical Services Zone 1
+ • Planning/Building/Public WorksT� Zone 1 Modified
`` R.MacOnie,D.Visneski _ Zone 2
AN If January 22,2008
Citv Limits
City of Renton Sensitive Areas
Flood Hazard
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G. Zimmerman,Administrator Hazard Condition
Technical Services 0 1,400 2,800' Critical Infrastructure
R. MacOnie, D.Visneski ' t t ' ' ' 'I'
Printed on May 21, 2009 This do—entisa hicre .i°n,not teed Flood Hazard p
9raa preen 9xaran Police Department
b survey accuracy,antl a basetl on Ne best inlorme4on
vailable as of the date shown This map is Inbnded for
C'ty die purposes only.
Data Source: Public Works, Utilities Systems,Technical Services Fire Stations
Renton City Limits
City of Valley Medical Center
jj Schools
City of Renton Sensitive Areas
Liquefaction Hazards
1 �
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to survey accuracy,and Is based on 0,best ln1°nna0on
G. Zimmerman,Administrator a°°"°"°°'° " °'°'"°w^ '"'°�° "°^°°°'°`
G,ytpl.yp °'°^'y HAZARD CONDITION Critical Infrastructure
Technical Services
R. MacOnie, D. Visneski e_� Renton City Limits Liquefaction Susceptibility Police Department
Printed on May 20, 2009
Data Source:Public Works,Utilities Systems,Technical Services; S high
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rSchools
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,,500 t3,000 Hazard Condition
G. Zimmerman,Administrator , , , Critical Infrastructure
Technical Services
R. MacOnie, D. Visneski Thsdocumentlsag,ph,,pns nWbon rolguNanlead High Seismic Severity Pol-N-ronent
b,u,,y accuracy,and is cased on 0,Deal info—to.
evairabla as of the dale sho Tho map is inter ded for
Printed on May 21, 2009 Gtydlspleypurpo—only
Fire Stations
Data Source:Public Works,Utilities Systems,Technical Services
_ � Valley Medical Center
City of
�\l■\JAI��f�����■i ,� �
Appendix C
Water Quality Calculations
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II
Technical Information Report (TIR) '` '
KCRTS
King County Runoff Time Series Program
Version 6.00
All files will be read/written in the Working Directory
Working Directory:C:\kc-swdm\output
------------------------------------------------------------------------------
KCRTS Command
CREATE a new Time Series
---------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series NBASIN.tsf
Regional Scale Factor 1.00
Data Type Reduced
Creating 15-minute Time Series File
Loading Time Series File:C:\KC-SWDM\KC-DATA\STEI15R.rnf 8
Impervious 1.00 acres Scaling Yr: 8
--------------
Total Area 1.00 acres
Peak Discharge: 1.18 CFS at 6:30 on Jan 9 in Year B
Storing Time Series File:NBASIN.tsf 8
Time Series Computed
-------------------------------------------------------------------------------
KCRTS Command
Enter the Analysis TOOLS Module
--------------------
----------------- ----------------------------------------------------------
Analysis Tools Command
------------- ---
Compute PEAKS and Flow Frequencies
Loading Stage/Discharge curve:nbasin.tsf
Flow Frequency Analysis
----------------------------
----------------------------
Time Series File:nbasin.tsf
Project Location:Sea-Tac
-rooect ocation: ea- ac
Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
FlowRate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.476 6 8/27/01 18:00 1.18 1 100.00 0.990
0.332 8 9/17/02 17:45 0.901 2 25.00 0.960
0.901 2 12/08/02 17:15 0.646 3 10.00 0.900
0.383 7 8/23/04 14:30 0.532 4 5.00 0.800
0.505 5 10/28/04 16:00 0.505 5 3.00 0.667
0.632 4 10/27/05 10:45 0.476 6 2.00 0.500
0.646 3 10/25/06 22:45 0.383 7 1.30 0.231
1.18 1 1/09/08 6:30 0.332 8 1.10 0.091
North Bio-filtration Basin Area(See Figure 4-1)
Water Quality flow rate=60%of 2-year storm
0.476 ds * 0.6 = 0.29 ds
Same rate for the South Bio-filtration Basin
ea isc arge: 1.18 CFS at on Jan V in Year
Storing Time Series File:NBASIN.tsf 8
Time Series Computed
KCRTS Command
Enter the Analysis TOOLS Module
------------------------------
------------------- -------------------------------------------------------
Analysis Tools Command
------------- ---
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:nbasin.tsf
Flow Frequency Analysis
Time Series File:nbasin.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:NBASIN.pks
Analysis Tools Command
------------- ---
RETURN to Previous Menu
---------------------------------------------------------------------------
KCRTS Command
CREATE a new Time Series
Production of Runoff Time Series
Project Location Sea-Tac
Computing Series FLT.tsf
Regional Scale Factor 1.00
Data Type Reduced
Creating 15-minute Time Series File
Loading Time Series File:C:\KC-SWDM\KC-DATA\STEI15R.rnf 8
Impervious 0.61 acres Scaling Yr: 8
--------------
Total Area 0.61 acres
Peak Discharge: 0.720 CFS at 6:30 on Jan 9 in Year 8
Storing Time Series File:FLT.tsf 8
Time Series Computed
ime eries i
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
FlowRate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.291 6 8/27/01 18:00 0.719 1 100.00 0.990
0.203 8 9/17/02 17:45 0.549 2 25.00 0.960
0.549 2 12/08/02 17:15 0.394 3 10.00 0.900
0.234 7 8/23/04 14:30 0.325 4 5.00 0.800
0.308 5 10/28/04 16:00 0.308 5 3.00 0.667
0.325 4 10/27/05 10:45 0.291 6 2.00 0.500
0.394 3 10/25/06 22:45 0.234 7 1.30 0.231
0.719 1 1/09/08 6:30 0.203 8 1.10 0.091
Computed Peaks 0.663 50.00 0.980
16
South Filter Strip Area(See Figure 4-1)
Water Quality flow rate=60% of 2-year storm
0.291 cfs * 0.6=0.17 cfs
KCRTS
ea Discharge: I ear
Storing Time Series File:FLT.tsf 8
Time Series Computed
-------------------------------------------------------------------------------
KCRTS Command
Enter the Analysis TOOLS Module
------------------------------
------------------------------ -----------------------------------------
Analysis Tools Command
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
loading Stage/Discharge curve:flt.tsf
Flow Frequency Analysis
--------------------------------------------------------
Time Series File:flt.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:FLT.pks
-------------------------------------------------------------------------------
Analysis Tools Command
------------ ---
RETURN to Previous Menu
-----------------------
-------------------------------------------------------------------------------
KCRTS Command
CREATE a new Time Series
-----------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series TB7N.tsf
Regional Scale Factor 1.00
Data Type Reduced
Creating 15-minute Time Series File
Loading Time Series File:C:\KC-SWDM\KC_DATA\STEI15R.rnf 8
Impervious 0.34 acres Scaling Yr: 8
Total Area 0.34 acres
Peak Discharge: 0.401 CFS at 6:30 on Jan 9 in Year 8
Storing Time Series File:TB7N.tsf 8
Time Series Computed
Heli
r
ime eries i e:t n.ts
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.162 6 8/27/01 18:00 0.401 1 100.00 0.990
0.113 8 9/17/02 17:45 0.306 2 25.00 0.960
0.306 2 12/06/02 17:15 0.220 3 10.00. 0.900
0.130 7 8/23/04 14:30 0.181 4 5.00 0.800
0.172 5 10/28/04 16:00 0.172 5 3.00 0.667
0.181 4 10/27/05 10:45 0.162 6 2.00 0.500
0.220 3 10/25/06 22:45 0.130 7 1.30 0.231
0.401 1 1/09/08 6:30 0.113 8 1.10 0.091
Computed Peaks 0.369 50.00 0.980
Taxiway B7 (N) Area(See Figure 4-1)
Water Quality flow rate=60% of 2-year storm
0.162 cfs * 0.6=0.10 cfs
Water quality flow rates for other areas referenced in the Bio-filtration calculations and
shown in Figure 4-1 are interpolated from the above rates generated with the KCRTS
program.
BIOFILTRATION CALCULATION
Based on KCSWDM,pg 6-40
South WQ Basin
Solve for bottom width(b)
Q=0.29 cfs (KCRTS) - 1.00 ac impervious y 0.17
y=0.17 (mowed frequently) 0.33 (infrequent mowing) n 0.2
n=0.2 s=slope z=side slope Q 0.29
b=Q*n/1.49*y^1.67*s^0.5 s 0.01
b(ft) 7.5 Use 10-ft width in design Z 4
Solve for flow Velocity
Z=side slope
A=cross-sectional area A(ft-2) 1.4
v(ft/s) 0.21
Solve swale length
L(ft)=540 * v 112.5 86ft with b=10ft Min. 100' in design
Meet criteria for high flow
North WQ Basin
y 0.17
Q=0.29 cfs (KCRTS)- 1.00 ac impervious n 0.2
b (ft) 7.5 Use 10-ft width in design Q 0.29
A(ft-2) 1.4 s 0.01
v(ft/s) 0.21 Z 4
L (ft) 112.5 86ft with b=10ft Min. 100' in design
Basic Filter Strip Calculation
Per KCSWDM Section 6.3.4,pg 6-59
South Filter Strip
Q=0.17 cfs (KCRTS)-0.61 ac impervious n 0.35
n=0.35 or 0.45 s=slope W=longitudinal length of imperv. W 277
Design depth(Df)= (Q*n/1.49*W*s^0.5)110.6 s 0.04
Df(ft) 0.013022 Q 0.17
Solve for Velocity
V=Q/W*Df
V(ft/s) 0.047128
Solve for Filter length
L(ft)=540 * V 25.44898 Use 26ft in design
Taxiway B7(N)Filter Strip
Q=0.10 cfs (KCRTS)-0.34 ac impervious n 0.35
n=0.35 or 0.45 s=slope W=longitudinal length of imperv. W 175
Design depth(Df)=(Q*n/1.49*W*s^0.5)^0.6 s 0.04
Df(ft) 0.012476 Q 0.1
Solve for Velocity
V=Q/W*Df
V(ft/s) 0.045801
Solve for Filter length
L (ft)=540 * V 24.73247 Use 26ft in design
Taxiway B7(S) Filter Strip
Q=0.05 cfs (KCRTS)-0.17 ac impervious n 0.35
n=0.35 or 0.45 s=slope W=longitudinal length of imperv. W 150
Design depth(Df)=(Q*n/1.49*W*s^0.5)^0.6 s 0.01
Df(ft) 0.013685 Q 0.05
Solve for Velocity
V=Q/W*Df
V(ft/s) 0.024357
Solve for Filter length
L (ft)= 540 * V 13.15274 Use 14ft in design
Taxiway B Filter Strip
Q=0.19 cfs(KCRTS)-0.65 ac impervious n 0.35
n=0.35 or 0.45 s=slope W=longitudinal length of imperv. W 625
Design depth(Df)=(Q*n/1.49*W*s^0.5)^0.6 s 0.04
Df(ft) 0.008543 Q 0.19
Solve for Velocity
V=Q/W*Df
V(ft/s) 0.035583
Solve for Filter length
L(ft)=540 * V 19.21463 Use 26ft in design
Taxiway B6(S)Filter Strip
Q=0.07 cfs(KCRTS)-0.24 ac impervious n 0.35
n=0.35 or 0.45 s=slope W=longitudinal length of imperv. W 180
Design depth(Df)=(Q*n/1.49*W*s^0.5)^0.6 s 0.04
Df(ft) 0.009904 Q 0.07
Solve for Velocity
V=Q/W*Df
V(ft/s) 0.039266
' Solve for Filter length
L(ft)=540 * V 21.20376 Use 26ft in design
Taxiway B6(N)Filter Strip
Q=0.1 cfs (KCRTS)-0.36 ac impervious n 0.35
n=0.35 or 0.45 s=slope W=longitudinal length of imperv. W 190
Design depth(Df)=(Q*n/1.49*W*s^0.5)^0.6 s 0.04
Df(ft) 0.011876 Q 0.1
Solve for Velocity
V=Q/W*Df
V(ft/s) 0.044319
Solve for Filter length
L(ft)=540 * V 23.93212 Use 26ft in design
FLOW SPLITTER CALCULATIONS
PROJECT: Renton Municipal Airport,Taxiway B,Phase II Calculated by: BTS
PROJ NO.: 23-2010-007 Checked by:
DATE: 10/15/2012 Date Checked:
FILE: H:\D0C\23Ap\10\007 Renton TW B&Signage0esign0minageff1m Splitta—Phase 1.x6x]F1m Spliw
South Biofiltration Swale
Pipe Capacity
Manning Pipe Capacity
No. Diameter Slope Length Capacity Used
(inch) (%) (feet) (cfs) (%)
0.014 8 0.10 10 0.35 82
0.014 12 0.10 10 1.05 28
Head determined by sharp-crested weir equation 0.463 s
O = D ' JS,
Known: Q1= 0.29 cfs JZ
CD= 0.6
IlEoutlet= 25.5 ft
Length Head Head 3
(ft) (ft) (in) QwQ = 3 CD 2gLH 2
1 0.2013 2.4161 4—
4 0.0799 0.9588 -
6 0.0610 0.7317
i
Conclusion: A 12-inch diameter pipe shall be utilized for the outlet to the biofiltration swale.
The top of the 1-ft weir shall be placed at 25.7(25.5+0.20).
North Biofiitration Swale
Pipe Capacity
Manning Pipe Capacity
No. Diameter Slope Length Capacity Used
(inch) (%) (feet) (cfs) (%)
0.014 8 0.10 10 0.35 82
0.014 12 0.10 10 1.05 28
Head determined by sharp-crested weir equation _ 0.463 s
Q — D 3 IS,
Known: Q2= 0.29 cfs n
CD= 0.6
IIE.utld= 23.0 ft
Length Head Head 2 3
(ft) (ft) (in) 3 Cn 2gLH 2
1 0.2013 2.4161 - ^-
4 0.0799 0.9588
6 0.0610 0.7317
Conclusion: A 12-inch diameter pipe shall be utilized for the outlet to the biofiltration swale.
The top of the 1-ft weir shall be placed at 23.2(23.0+0.20).
Page 1 of 1
Appendix D
Conveyance System Calculations
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II
Technical Information Report (TIR) ' ' ' ` ' '
SUB—BASIN A-1 SUB—BASIN A-2�
21,889 SF IMP\\ fr �!T� l ` — FJ(ISTING ASF LT — _ __ -------- _--- �— _ — — r--- ._- _.-__._ —'
�� {1J r (RLINWAY I6- I ' — --._--------
7,500 SF LA1NN ` Jr _r---- -----------
f r r
f r
SF IMP -
t
� 1,578 SF-LIWV_N 7fl;623 SF IMP
44r167 SF IMP ' 9,299 SF IMP/ '
; /81,78ySF C�WN r 58,540 SF LAWN
2,1,658 SF Wit /
j
�°" � 53,803 SF LA
7,935 SF IMP �� J -" - ! 44,030 SF ��
( , —' t� 7 '
( 28,279 SF LAWN ` � . !
;- - SD- --
M `� SD
99 -- Sp
.. 1". S ^n ....... p -..--_-- ---_.. ——�`6 �- - / ....._.._._.gip
ti
/ _
f
' Fa , — -- -��---- _--- ---- ----- —�- ---- ------ --
� 18,398 SF IMP' y 1 _ �w; ` � T c
t
�. 32,834 SF IMP ( `
i 29,330 SF4hT (TAXIWAY
ASPHALT
TAxlwav a) 26,131 SF IMP
840 SF LAWN
--)
fi
NEW SLOT DRAIN EXISTING SLOTDRAIN
� ..
TRIBUTARY AREA 59,198 SF 1 85,423 SF IMP
BOUNDARY (TYP) 166,735 SF IMP
---- ----- - - i
OUTFALL PIPE �"�'"• _r OUTFALL PIPE
TO RIVER TO RIVER
!!! LEGEND:
REPLACED/NEW
ASPHALT PAVEMENT
-� SWALE
FLOW DIRECTION
Tributary Area/Collection Figure 1
72B130 9nd3W wle100 Renton Airport
EmdL Wmhin tm 98204
Pk 425 741-3800
PROJ: Renton Municipal Airport,Taxiway B PIPE SIZING
WO: 23-2012-2012 (Runoff by Rational Method) C by: BTS
DATE: 1 01212 01 2 (Pipe Capacity by Manning's Eqn.) C.ey:
FILE: H:\DOC\23Ao\10\007 Renton TW B&Sienaee\Desien\Draina c\120121002 Pine Sizine I Phase II.x1sIPioe Sizine 100vr BASIN D. Ch-k. :
Storm: Renton 25 Year
c= 0.9 1 rrper vi ous ° 2.66 (,..KCSWDM pp 3-13)
c= 0.25 Lawn " 0.65 (,,.KCSWDM py 3-13)
3.4 (_„KCSWDM pg 3 24-Hour Isopluvials
I Tim.o P. PIP % V.- F1,w
A-(.,) A...(..) A,.. R S.- Cp°p 11-1 Ru°orr St.- L-g- C.P.. C.P F.1.
F T, (I mP., (P.1 C.- _ A'C (mi„) (i°/nr) (pr.) V.I..
ub-basin Al
E 1 39 0 0.4 0. 0 0.38 0.38 10.00 2.02 0.77 0.014 6 0.76 145 0.45 169 2.31 1.04 Existing-No change in flow characteristic
B 1 5 28279 0.33 0.71 11.04 1.90 1.34 0.014 8 1.02 96 1.13 118 3.25 0.49 Existing-No change in flow characteristic
30 0 "'' 0. 0.61 1.31 10.00 2.02 2.66 0.014 12 0.39 107 2.07 129 2.63 0.68 Existing-No change in flow characteristic
1 )'I�j 0.00 1.31 10.68 1.94 2.55 0.014 10 0.27 84 1.06 241 1.94 0.72 Existing-No change in flow characteristic
CB3 218897500 11.73 0.50 2.51 12.94 1.71 4.31 0.014 18 0.42 266 6.32 68 3.59 1.24
B B3 44167 �058 '1 0.69 1.04 1.04 10.00 2.02 2.10 0.014 12 0.63 23 2.62 80 3.33 0.12
B3 0 0 0.00 0.2 0.00 3.55 14.29 1.61 5.70 0.014 18 0.83 125 8.89 64 5.03 0.41
134 " 21578 1.30 0.65 0.85 1 4.40 14.71 1.58 6.94 0.014 18 0.59 130 7.49 1 93 4.24 1 0.51
5 CB6 32834 0.75 0.90 0.68 0.68 10.00 2.02 1.37 0.014 12 0.55 181 2.45 56 3.12 0.97 Slot Drain
7 0 0. 0.25 0.00 0.68 10.97 1.91 1.29 0.014 12 1.00 9 3.31 39 4.21 0.04 Swale
B7 CB9 0 T 25 0.00 5.08 16.22 1.48 7.51 0.014 18 0.61 1 135 7.62 99 4.31 0.52 Bypass
B9 B1 5 2 81787 3. 52 1.69 6.78 1 16.74 1.45 1 9.81 0.014 1 18 0.31 240 5.43 1 181 3,07 1.30
CB11 BI 1 735 0 3 3.44 3.44 10.00 2.02 6.97 0.014 12 2.38 8 10.20 68 12.98 0.01 Parallel 12"SD Lines
1312 71313 0 0. 5 0.00 3.44 10.01 2.02 6.97 0.014 18 0.49 166 6.83 102 3.86 0.72
7B13 CB14 0 0. 0.25 0.00 3.44 10.73 1.93 6.66 0.014 18 2.08 12 14.07 47 1 7.96 0.03
CB14 CB16 0 „ 0. 0.25 0.00 10.22 1 18.76 1.35 1 13.75 1 0.014 1 18 0.31 148 5.43 253 3.07 0.80
516 CBl 70623 ,, 2.97 1 1.80 12.02 19.56 1.31 15.73 1 0.014 18 0.47 199 6.69 2' 3.78 0.88
B1 CB IN 57 ? _7= 1.44 13.46 20.44 1.27 0,014 18 0.20 298 4.41 233 2.49 1.99 Assumed 60%of total flow to Sub-basin A2
E5 u „ 0,00 0.21 1 0.00 0.00 20.44 1.27 6.85 0.014 12 1.29 210 3.76 182 4.?fl 0.73 Assumed 40%of total flow to Sub-basin Al
Page 1 of 2
PROJ: Renton Municipal Airport,Taxiway B PIPE SIZING
WO: 23-2012-2012 (Runoff by Rational Method) C......-by: BTS
DATE: 1 01212 01 2 (Pipe Capacity by Manning's Eqn.) Ch--d by:
FILE: H-OOC123Au\10\007 Renton TW B&Sienaee\Desien\DrainweV20121002 Pioe Sizine I Phase ILzlalPioe Sizine 100vr BASIN D.t.Cn-..d:
Storm: Renton 25 Year
c= 0.9 1 rrper vi ous "' 2.66 (,..KCSWDM pg 3-13)
c- 0.25 Lawn °' 0.65 (,..KCSWDM pg 3-13)
r 3.4 (...KCSWDM pg 3 24-Hour Isopluvials
Ino. Ino. I o. Tim.or R..., P.p. % V.... F-
A-(.r) A...(..) A- R.n.1 Sim C... I n R....orr D..m S.P. L.,.- C.p . C.p.. F- T- P,.,,,.,,..
F. ,. To (Imp., (P., ) (.0 C.- A'C A"C (oin) (ib/br) (.r.) V.- (loon) (%) (r.-) ( r.) U- (Id... (.ate)
1.3 7 0 1.22 1.22 20.44 1.27 1.56 0.014 12 0.75 265 2.87 54 3.65 1.21 Slot Drain
5 E6 0.00 0.25 0.00 1.22 22.38 1.20 0.59 0.014 12 0.33 255 1.90 31 2.42 1.76 Existing-No change in flow characteristic
l;"1 0.00 0.00 1.22 24.14 1.14 0.56 0.014 12 0.33 23 1.90 29 2.42 0.16 Existing-No change in flow characteristic
Tub-basin A2
B 1 N 2 l 31 440 0.54 0.54 10.00 2.02 1.10 0.014 12 0.68 104 2.73 40 3.47 0.50
53603 0.96 14.42 22.93 1.18 10.21 0.014 18 0.42 157 6.31 162 3.57 0.73 Existing-No change in flow characteristic
RE 4 712 0. 0.88 15.30 23.66 1.16 10.62 0.014 18 0.42 34 6.32 168 3.58 0.16 Existing-No change in flow characteristic
F9 42711 0 0. 0.90 0.88 16.18 23.82 1.15 11.18 0.014 18 0.42 203 6.32 177 3.58 0.95 Existing-No change in flow characteristic
tHIT ri 0 0.58 0.00 16.18 24.77 1.12 10.90 0.014 18 0.43 61 6.37 171 3.60 0.28 Existing-No change in flow characteristic
4u'
Page 2 of 2
PROJ: Renton Municipal Airport,Taxiway B PIPE SIZING
WO: 23-2012-2012 (Runoff by Rational Method) C.1 1-a ey: BTS
DATE: 10/2/2012 (Pipe Capacity by Manning's Eqn.) Ch.,k.<ey:
FILE: H:\DOC\23Ao\IO\007 Renton TW B&Sienaee\Desien\Drainaee\120121002 Pioe Sizine 1 Phase II.xIslPioe Sizine 100vr BASIN D. Cnk
Storm: Renton 10 Year
c- 0.9 1 rrper vi ous ° 2.44 (_..KCSWDM pe 3-13)
c- 0.25 Lawn ° 0.64 (...KCSWDM p.3-13)
r, 2.9 (=ee KCSWDM P9 3 24-Hour Isopluvials
I I T. R.,° Pip. % V.- F
A-(.r) Ar..(.r) Ar.. R.-, S.- C.- I° R non D,.. Si L.,,otn C.p.. Cap.. Feu Ti R.-k.
0mP-) (P.r A`C A'C (M ) (i°/-) (cr. V.- °) (i.,�n) (/o) (r.ec) (er.) Ussa
tiu6-basin AI
JE2 1 398 0 0,47 0.90 0.38 0.38 10.00 1.62 0.62 0.014 6 0.76 145 0.45 136 2.31 1.04 Existing-No change in flow characteristic
JCBI 7 5 28279 0.83 0.39 0.33 0.71 11.04 1.52 1.07 0.014 8 1.02 96 1.13 95 3.25 0.49 Existing-No change in flow characteristic
3 0 .67 0.61 1.31 10.00 1.62 2.13 0.014 12 0.39 107 2.07 103 2.63 0.68 Existing-No change in flow characteristic
Il! CB 1 0 0.0 5 0.00 1.31 10.68 1.55 2.04 0.014 10 0.27 84 1.06 193 1.94 0.72 Existing-No change in flow characteristic
It CB3 21889 7500 0.67 0.50 2.51 12.94 1.37 3.46 0.014 18 0.42 266 6.32 55 3.58 1.24
CB-1 CB3 441 7 21658 1.51 1.04 1.04 10.00 1.62 1.68 0.014 12 0.63 23 2.62 64 3.33 0.12
11; CB4 0 0 5 0.00 3.55 14.29 1.29 4.58 0.014 18 0.83 125 8.89 51 5.03 0.41
Elsa CB7 35239 21578 1. 5 0.85 4.40 14.71 1.27 5.58 0.014 18 0.59 130 7.49 1 74 4.24 0.51
CB5 CB6 32834 0 0.75 0 0.68 0.68 10.00 1.62 1.10 0.014 12 0.55 181 2.45 45 3.12 0.97 Slot Drain
B6 B7 0 0. � 5 0.00 0.68 10.97 1.53 1.04 0.014 12 1.00 9 3.31 31 4.21 0.04 Swale
CB9 0 0 700 0.25 0.00 5.08 16.22 1.19 6.04 0.014 18 0.61 135 7.62 79 4.31 0.52 Bypass
B14 5 299 81787 3.24 0.52 1.69 6.78 16.74 1.17 7.90 0.014 18 0.31 1 240 5.43 1 145 3.07 1.30
CB11 CB12 1 735 0 0. 3.44 3.44 10.00 1.62 5.58 0.014 12 2.38 8 10.20 55 12.98 0.01 Parallel 12"SD Lines
B1 0 .00 0.25 0.00 3.44 10.01 1.62 5.58 0.014 18 0.49 166 6.83 82 3.86 0.72
rTIT CB14 0 0 0.00 0.25 0.00 3.44 10.73 1.55 5.34 0.014 18 2.08 12 14.07 38 7.96 0.03
B1 B16 0 0 0.00 0.25 0.00 10.22 18.H, 1.03
11.08 0.014 18 0.31 148 5.43 204 3.07 0.80
B1 CBI 70623 58540 2.97 1 1.80 12.02 19. 12.68 0.014 18 0.47 199 6.69 90 3.78 0.88
B1 B1N 57 44030 2717 • 2 1.44 13.46 20. 0.014 18 0.20 298 4.41 188 2.49 1.99 Assumed 60%of total flow to Sub-basin A2
CB 18 E5 0 0 .0 5 0.00 0.00 20. 0.014 12 1.29 210 3.76 147 4.78 0.73 jAssumed 40%of total flow to Sub-basin Al
Page 1 of 2
PROJ: Renton Municipal Airport,Taxiway B PIPE SIZING
WO: 23-2012-2012 (Runoff by Rational Method) C---d.y: BTS
DATE: 1 01212 01 2 (Pipe Capacity by Manning's Eqn.) C---
FILE: HA00CUMM10\007 Renton TW B&Sienaee\Desien\Drainaee\I20121002 Pioc Sizine I Phase II.x1slPioe Sizine IOOw BASIN D-Ch-k.d.
Storm: Renton 10 Year
C= 0.9 1 riper vi ous a, 2.44 ( ..KCSWDM pfl 3-13)
c- 0.25 Lawn U, 0.64 ( ..KCSWDM pfl 3-13)
r, 2.9 (,..KCSWDM pfl 3 24-Hour Isopluvials
I. I... I Tim..r R- Pip. % V.- F-
A-(.r) A...(.r) A,.. R S.m C.- 1-.. R...- Di- Si- L-oth C.P.. C.p.P F- Tim. R.m -
T. 0 P.,0 (P.,1) Cam A'C A'C (-) (i l-) (ter.) \:.,I_. (i-n) (%) (I-) (Cr.) U..d (red..=) (-)
7B17 E5 5 1 1.36 0.90 1.22 1.22 20.44 1.03 0.014 12 0.75 265 2.87 44 3.65 1.21 Slat Drain
0.00 1.22 22.38 0.97 0.47 0.014 C 0.33 255 1.90 25 2.42 1.76 Existing-No change in flow characteristic
0.00 1.22 24.14 0.92 0.45 0.014 12 0.33 23 1.90 24 2.42 0.16 Existing-No change in flow characteristic
u asm:12
CBI 131 840 0.54 0.54 10.00 1.62 0.88 0.014 12 0.68 104 2.73 32 3.47 0.50
7 31417 53603 0.96 14.42 22.93 0.95 8.24 0.014 18 0.42 157 6.31 131 3.57 0.73 Existing-No change in flow characteristic
I 8 4 712 0 0. 0.90 0.88 15.30 23.66 0.93 8.58 0.014 18 0.42 34 6.32 136 3.58 0.16 Existing-No change in flow characteristic
I E9 42711 0 0 0.88 16.18 23.82 0.93 9.03 0.014 18 0.42 203 6.32 143 3.58 0.95 Existing-No change in flow characteristic
� OUT 0 00. 6 .5 0.00 16.18 24.77 0.91 8.81 0.014 18 0.43 61 6.37 138 3.60 0.28 Existing-No change in flow characteristic
40%
60%
Page 2 of 2
PROD: Renton Municipal Airport,Taxiway B PIPE SIZING
WO: 23-2012-2012 (Runoff by Rational Method) C. BTS
DATE: 1 01212 01 2 (Pipe Capacity by Manning's Eqn.) Ch-k-ey:
FILE: H:\DOC\23Ao\I0\007 Renton TW B a Sienaec\Deaien\Draina¢eV20121002 Pine Sizine I Phaw II.xlslPioe Sizine 100w BASIN D.c.Cn.d:
Storm: Renton 100 Year
c= 0.9 1 rrper vi ous a, 2.61 (...KCSWDM pg 3-13)
c= 0.25 Lawn " 0.63 (...KCSWDM pg 3-13)
r, 3.9 (. KCSWDM pg 3 24-Hour Isopluvials
IPp. I g. T,-.or R., P.P. % V.I.. F.-
Ar.. (.) Ar..(.r) Are. R..., S. Coy,. I.,c Pff Di.- S-P. L.,, C.P.. C.P.. F.,n Tim. R.m.r..
(I m (P.r C.- A`C A'C (,..�) (ice/er) (�r.) V.- (Iope) (%) (r..c) (ter.) U..a
dub-basin AI
E I 1' 18399 0 0.42 0.90 0.38 0.38 10.00 2.39 0.91 0.014 6 0.76 145 0.45 200 2.31 1.04 Existing-No change in flow characteristic
2 (131 935 2g2,9 . 3 0.33 0.71 11.04 2.24 1.58 0.014 8 1.02 96 1.13 140 3.25 0.49 Existing-No change in flow characteristic
3 - 293_ 0 7 0.61 1.31 10.00 2.39 3.13 0.014 12 0.39 107 2.07 152 2.63 0.68 Existing-No change in flow characteristic
4 I I 0 0.00 1.31 10.68 2.29 3.00 0.014 10 0.27 84 1.06 284 1.94 0.72 Existing-No change in flow characteristic
CBI CB3 21889 7500 0.670.730.50 2.51 12.94 2.03 5.10 0.014 18 0.42 266 6.32 1 81 3.58 1,24
B B 44167 1658 1.51 0. 9 1.04 1.04 10.00 2.39 2.47 0.014 12 0.63 23 2.62 95 3.33 0.12
7B3 B li 0. 25 0.00 3.55 1 14.29 1.91 6.77 0.014 18 0.83 1 125 8.89 76 5.03 1 0.41
CB4 CB7 35239 21578 1.30 0.65 0.85 4.40 14.71 1.87 8.24 0.014 18 0.59 130 7.49 110 4.24 0.51
5 7B6 704 0.75 0 0.68 0.68 10.00 2.39 1.62 0.014 12 0.55 181 2.45 66 3.12 0.97 Slot Drain
rF
57 0 0.0 5 0.00 0.68 10.97 2.25 1.53 0.014 12 1.00 9 3.31 46 4.21 0.04 Swale
B7 CB9 1, 0.00 0.25 0.00 5.08 1 16.22 1.76 8.94 0.014 18 0.61 1 135 7.62 117 4.31 0.52 Bypass
B9 7B14 59299 81787 3.24 0.52 1.69 6.78 16.74 1.72 11.69 0.014 18 0.31 240 5.43 215 3.07 1.30
B11 B1 166735 0 3.83 .9 3.44 3.44 10.00 2.39 8.22 0.014 12 2.38 8 10.20 81 12.98 0.01 Parallel 12"SD Lines
B12 B1 0 0.25 0.00 3.44 10.01 2.38 8.21 0.014 18 0.49 166 6.83 120 3.86 0.72
B13 CB14 0 0 0.00 0.25 0.00 3.44 10.73 2.28 7.87 0.014 18 2.08 12 14.07 56 7.96 0.03
B14 71 0 . 0 0.25 0.00 10.22 18.76 1.61 16.41 0.014 18 0.31 148 5.43 302 3.07 0.80
B1 Bl 70 58540 7 0. 1 1.80 12.02 19.56 1.56 18.79 0.014 18 0.47 199 6.69 281 3.78 0.88
B 1 Bl 57 44030 33 1.44 13.46 20.44 1.52 12.28 0.014 18 0.20 298 4.41 279 2.49 1.99 Assumed 60%of total flow to Sub-basin A2
B1 ES 0 .00 0. 5 0.00 0.00 20.44 1.52 8.19 0.014 12 1.29 210 3.76 218 4.78 0.73 1 Assumed 40%of total flow to Sub-basin AI
Page 1 of 2
PROD: Renton Municipal Airport,Taxiway B PIPE SIZING
WO: 23-2012-2012 (Runoff by Rational Method) Cad--by: BTS
DATE: 10/2/2012 (Pipe Capacity by Manning's Eqn.) Ch- by:
FILE: H:VDOC\23Ao\1OW07 Renton TW B&Sienaee\Desien\Drainaee\120121002 Pioe Sizine 1 Phaae II.z131Pioe Sizin¢IOOvr BASIN D.-Cn. -:
Storm: Renton 100 Year
c 0.9 1 rTper VI OUS a' 2.61 (_..KCSWDM pe 3-13)
C- 0.25 Lawn "' 0.63 ( ..KCSWDM py 3-13)
r, 3.9 (...KCSWDM p9 3 24-Hour Isopluvials
Ids. I d. Ind. Timor R., RP. % V.tp. F..-
Ar..(e) A-(.r) A- R-rr S,.m C. p I - R, ,. D- S.P. L..o- C.p.. C.p.. Fro Ti.. R.�,, . .
F,:, T. (ImP-) (P.r1) (..) C.-I. A'C A'C U..d (re/...) (mtd)
B17 5 0 `�" 1.22 1.22 20.44 1.52 1.86 0.014 0.75 265 ?.87 65 3.65 1.21 Slot Dram
S E6 0 11 n 00 025 0.00 1.22 22.38 1.44 0.70 0,014 12 0.33 255 37 2.42 1.76 Existing-No change in flow characteristic
U I o "" 0.2 0.00 1.22 24.14 1.37 0.67 0.014 _ 0.33 23 35 2.42 0.16 Existing-No change in flow characteristic
Eub-basin A
1N 1 840 0. 2 0.54 0.54 10.00 2.39 1.30 0.014 0.68 104 2.73 48 3.47 0.50
17 53603 1.95 49, 0.96 14.42 22.93 1.41 12.24 0.014 0.42 157 6.31 194 3.57 0.73 Existing-No change in flow characteristic
7 4 712 0 0 0.88 15.30 23.66 1.39 12.73 0.014 18 0.42 34 6.32 201 3.58 0.16 Existing-No change in flow characteristic
E -ET--42711 0 0. 0.88 16.18 23.82 1.38 13.41 0.014 18 0.42 203 6.32 212 3.58 0.95 Existing-No change in flow characteristic
E OC T 0 0 0.00 .5 0.00 16.18 24.77 1.35 13.09 0.014 18 0.43 61 6.37 206 3.60 0.28 Existing-No change in flow characteristic
l0%
,0%
Page 2 of 2
- Runoff Coefficients for Rational Method
Source: King County Surface Water Design Manual 2009,Table 3.2.LA
General Land Covers
Land Cover C
Dense forest 0.10
Light forest 0.15
Pasture 0.20
Lawns 0.25
Playgrounds 0.30
Gravel areas 0.80
Pavement and roofs 0.90
Open water(pond,lakes,wetlands) 1.00
Single Family Residential Areas
Land Cover Density C
0.20 DU/GA(1 unit per 5 ac.) 0.17
0.40 DU/GA(1 unit per 2.5 ac.) 0.20
0.80 DU/GA(1 unit per 1.25 ac.) 0.27
1.00 DU/GA 0.30
1.50 DU/GA 0.33
2.00 DU/GA 0.36
- 2.50 DU/GA 0.39
3.00 DU/GA 0.42
3.50 DU/GA 0.45
4.00 DU/GA 0.48
4.50 DU/GA 0.51
5.00 DU/GA 0.54
5.50 DU/GA 0.57
6.00 DU/GA 0.60
Source:King County Surface Water Design Manual 2009,Table 3.2.1.13
Coefficients for the Rational Method
Design Storm aR bR
2 Year 1.58 0.58
5 Year 2.33 0.63
10 Year 2.44 0.64
25 Year 2.66 0.65
50 Year 2.75 0.65
100 Year 2.61 0.63
SECTION 3.2 RUNOFF COMPUTATION AND ANALYSIS METHODS
FIGURE 3.2.1.A 2-YEAR 24-HOUR ISOPLUVIALS
—�— SNONOMIEN COUNTY
` � -- _---- — ---- -�--— — — — — — KING COUNTY
i 1
r'• � .�j. N N N
2• 9 --
shrq, - 44 (V 4z)
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�• .�.f � _ '—KING COUNTY
^Q „ PIERCE COUNTY
WESTERN
KING COUNTY
Z 3.5
2-Year 24-Hour
Precipitation Iti
in Inches Miles
1/9/2009 2009 Surface Water Design Manual
3-14
3.2.1 RATIONAL METHOD
FIGURE3.2.1.B 10-YEAR 24-HOUR ISOPLUVIALS
LNO� MIIL�COUNTy
KING COUNTY
N-.4
d C4.0
O
-j
Ij I-A
I
A
Al
N V
y
PIERCE COUNTY0U N;m -',.
WESTERN
KING COUNTY
I-Z Al;, 4.5
N
10-Year 24-Hour 1b, 4.0
Precipitation 411b
0 2 4 Miles Ib IbIl
in Inches
2009 Surface Water Design Manual 1/9/2009
3-15
SECTION3.2 RUNOFF COMPUTATION AND ANALYSIS METHODS
FIGURE 3.2.1.0 25-YEAR 24-HOUR ISOPLUVIALS
nnani-OVIT—Y
KING COUNTY
9 d
.0
A
5.0
-w 171-
Ay
17
C9 N
'KING COUNTY
03* PIERCE COUNTY
WESTERN o.
KING COUNTY
N 5.0
26-Year 24-Hour 4.5
b*
Precipitation P 1b
112* , n
0 2 4 Miles
in Incheso
1/9/2009 2009 Surface Water Design Manual
3-16
3.2.1 RATIONAL METHOD
FIGURE 3.2.1.D 100-YEAR 24-HOUR ISOPLUVIALS
`�0 _
_ N G COUNTY
3? ..o.[u� • — \ --Nees •[.( -_ s — - --- — N COUNTY
if
Q A
0 s.o.d•
�3
ID
.` 1 oou•
I
i
.[Ile
r
/ F
S Q
eyb�` r
IA
..:�: -- - � Y.Y.• \ � _
\ ® 1
K G COUNTY
PiE CC COUNTY
WESTERN �° � '--.,
KING COUNTY Qj .1 11 5
•.. s.
N b 5.5
100-Year 24-Hour a• ltl.`�
Precipitation p'
in Inches 0-- 2-- 4"""es
2009 Surface Water Design Manual 1/9/2009
3-17 ' _
DEPTH OF PIPE COVER
PROJECT: Renton Municipal Airport,Taxiway B,Phase II
PROJ NO.: 23-2010-007 Calculated by: BTS
DATE: 10/12/2012 Checked by:
- FILE: H:00023Ap\10\007 Renton TW B&Signage\Design\Dramage\[Pipe Loading-Phase II.x1sx]Thickness Calcs Date Checked:
Pipe Sections CB "From" IE Pipe Diameter Approx. Pipe Length of Pipe to Asphalt Crown of Pipe Top of Asphalt Depth to Cover
"From" "To" (ft) (in) Stationing Slope EOA CL EOA EOA CL EOA EOA CL EOA EOA CL EOA
CB 1 CB3 26.34 18 12+38 0.42% 0 59 126 27.84 27.59 27.31 30.2 31.06 30.77 2.4 3.5 3.
CB5 CB6 26.64 12 17+69 0.55% (1 69 115 27.64 27.26 27.01 28.64 29.36 28.71 1.0 2.1 1.7
CB 11 CB 12 24.1 12 21+51 1.10% 0 -- -- 25.10 -- -- 26.2 -- -- 1.1 -- --
CB12 CB13 23.81 18 21+51 0.49% 0 57 106 25.31 25.03 24.79 26.33 26.93 26.28 1.0 1.9 1.5
CB18 E5 21.01 12 25+08 1.29% 5(I 101 210 21.2876 20.71 19.30 24.9 25.56 24.84 3.6 4.9 5.5
CB1N E8 20.3 18 28+30 0.42% 49 63 189 21.59 2 1.54 21.01 24.86 25.17 -- 3.3 3.6 --
IE=Invert Elevation
CB=Catch Basin
EOA=Edge of Asphalt
CL=Centerline
Approx.=Approximate
No.=Number
Page 1 of 1
THICKNESS DESIGN FOR DUCTILE IRON PIPE
PROJECT: Renton Municipal Airport,Taxiway B,Phase II Calculated by: BTS
PROJ NO.: 23-2010-007 Checked by:
DATE: 10/12/2012 Date Checked:
FILE: H:\D0C\23ApU0\007 Renton TW B&Signageocsign\Drainage\[Pipe Loading-Phase r1.x1sxlnuckness Coles
Define: Determine the required pipe thickness to withstand truck loads at shallow depths.There are 4 scenarios where
DIP possess<3 ft of cover: 12 in @ 1 ft, 18 in @ 1.0 ft, 12 in @ 1.5 ft,and 18 in @ 2 ft.The methods set forth
by ANSI/AWWA C150/A21.50-02(Thickness Design of Ductile-Iron Pipe)shall be utilized in the design of
the appropriate pipe thickness.
Known: Type 4 pipe laying conditions per Table 2,ANSFAWWA C150/A21.50-02
Design Vehicle(737-800)= 130,000 pounds
Percent of Load= 46.79 %
No.of Wheels= 2
P(truck load)= 30413.5 pounds
w= 120 lb/ft'
a= 144 in2/ft2
R= 1 Road Reduction Factor for cover<4 ft and pipe diameter between 3-12 in
(Table 4,ANSFAWWA C150/A21.50-02)
R= 0.85 Road Reduction Factor for cover<4 ft and pipe diameter between 18 in
(Table 4,ANSFAWWA C150/A21.50-02)
F= 1.5 Impact factor(ASCE Manual No.37)
Solve: Step 1-Design for internal pressure
For ordinary conditions,storm drain pipes shall be sized on the assumption that they will flow full,or
practically full,under the design discharge,but will not be placed under pressure head.Therefore,internal
pressure will be assumed to be 0 psi for the design of the storm system.
Step 2-Design for trench load
a.)Earth Load
Table 1:Earth Load wH
Depth,H Earth Pressure P e
(ft) (psi) a
1.0 0.8333
1.5 1.2500
2.0 1.6667
b.)Truck Load
C=1--sin 2 _, AZ+HZ+1.52 2 1.5AH 1 1
H +- +
(A2+H2)0.52+H2) ;r( A2+HZ+1.52J�+H' 1.52+HZ
Table 2:Surface Load Factor
Depth,H Nominal Pipe Pipe Outside Surface Load
Diameter Radius Factor,C
(ft) (in) (ft)
1.0 12 0.55 0.5621
1.0 18 0.81 0.7086
1.5 12 0.55 0.3770
2.0 18 0.81 0.3658
Page 1 of 4
P, = RF CP
bD
Table 3:Truck Load
Depth,H Nominal Pipe OD of Pipe,D Effective Length of Truck Load,Pt
Diameter Pipe,b
(it) (in) (it) (in) (psi)
1.0 12 13.20 36.00 53.96
1.0 18 19.50 36.00 39.14
1.5 12 13.20 36.00 36.19
2.0 18 19.50 36.00 20.21
c.)Trench Load
Table 4:Trench Load � - T
Depth,H Nominal Pipe Trench Load,P, V e t
Diameter
(ft) (in) (psi)
1.0 12 54.80
1.0 18 39.97
1.5 12 37.44
2.0 18 21.87
d.)Net Thickness for Bending Stress Design
Note:Refer to Table 10 of AWWA C150/A21.50-02 for diameter-thickness ratios for Type 4 laying
conditions.Round up the trench loads to the next highest corresponding bending-stress design figure.
D
t =
( D / t )
Table 5:Net Thickness
Nominal Pipe Thickness Ratio, Net
Depth,H OD of Pipe,D Trench Load,P,
Diameter D/t Thickness
(ft) (in) (ft) (psi) (in)
1.0 12 13.20 54.80 46 0.29
1.0 18 19.50 39.97 57 0.34
1.5 12 13.20 37.44 60 0.22
2.0 18 19.50 21.87 103 0.19
Page 2 of 4
Step 3-Selection of Net Thickness and Addition of Service Allowances
Note:the thicknesses calculated in Step 2 were selected due to the assumption that the internal pressure within
the storm pipes are 0 psi.
a.)Minimum Manufacturing Thickness-H=1 ft;D=12 in
Net Thickness= 0.29 in
Service Allowance= 0.08 in
Min Manufacturing Thickness= 0.37 in
b.)Minimum Manufacturing Thickness-H=1.0 ft; D=18 in
Net Thickness= 0.34 in
Service Allowance= 0.08 in
Min Manufacturing Thickness= 0.42 in
c.)Minimum Manufacturing Thickness-H=1.5 ft;D=12 in
Net Thickness= 0.22 in
Service Allowance= 0.08 in
Min Manufacturing Thickness= 0.30 in
d.)Minimum Manufacturing Thickness-H=2.0 ft;D=18 in
Net Thickness= 0.19 in
Service Allowance= 0.08 in
Min Manufacturing Thickness= 0.27 in
Note:a service allowance of 0.08 inches is added to the net thickness per Section 4.1.3.b of ANSUAWWA
C 150/A21.50-02.
Step 4-Check Deflection of the Pipe
Note:Refer to Table 10 of ANSI/AWWA C 1 50/A21.50-02 for diameter-thickness ratios for Type 4 laying
conditions.Round up the trench loads to the next highest corresponding deflection check.
D
t =
( D / t, )
Table 6:Pipe Deflection
Nominal Pipe Thickness Ratio
Depth,H OD of Pipe,D Trench Load,P, Thickness
Diameter D/t
(ft) (in) (ft) (psi) (in)
1.0 12 13.20 54.80 48 0.28
1.0 18 19.50 39.97 55 0.35
1.5 12 13.20 37.44 57 0.23
2.0 18 19.50 21.87 75 0.26
Minimum Manufacturing Thickness>Deflection
Therefore,Minimum Manufacturing Thickness Controls for all pipe configurations and depths
Page 3 of 4
Step 5—Add the Casting Tolerance
Table 7:Allowance for Casting
Tolerance*
Size Casting Allowance
(in) (in)
10- 12 0.06
1442 0.07
*Note:the table information was derived from Table 3 of ANSUAWWA C150/A21.50-02
a.)Total Thickness—H=1 ft;D=12 in
Min Manufacturing Thickness= 0.37 in
Casting Tolerance= 0.06 in
Total Thickness= 0.43 in
Total Thickness=Class 54(0.43 inches)
Therefore,the minimum Special Class pipe required for this scenario is Class 54
b.)Total Thickness—H=1.0 ft;D=18 in
Min Manufacturing Thickness= 0.42 in
Casting Tolerance= 0.07 in
Total Thickness= 0.49 in
Total Thickness<Class 55(0.50 inches)
Therefore,the minimum Special Class pipe required for this scenario is Class 55 E—
c.)Total Thickness—H=1.5 ft;D=12 in
Min Manufacturing Thickness= 0.30 in
Casting Tolerance= 0.06 in
Total Thickness= 0.36 in
Total Thickness<Class 52(0.37 inches)
Therefore,the minimum Special Class pipe required for this scenario is Class 52
d.)Total Thickness—H=2.0 ft;D=18 in
Min Manufacturing Thickness= 0.27 in
Casting Tolerance= 0.07 in
Total Thickness= 0.34 in
Total Thickness<Class 50(0.35 inches)
Therefore,the minimum Special Class pipe required for this scenario is Class 50
Page 4 of 4
Appendix E
Bond Quantities Worksheet
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II
Technical Information Report (TIR)
Site Improvement Bond Quantity Worksheet
Original bond computations prepared by:
Name: Benjamin Sommer Date: 10.16.12
PE Registration Number: 45892 Tel.#: (425)741-3800
Firm Name: Reid Middleton, Inc.
Address: 728 134th Street SW,Suite 200, Everett,WA 98204 Project No: 232010.007
ROAD IMPROVEMENTS&DRAINAGE FACILITIES FINANCIAL GUARANTEE REQUIREMENTS
PERFORMANCE BOND','* PUBLIC ROAD&DRAINAGE MAINTENANCE/DEFECT
AMOUNT BOND','*
Stabilization/Erosion Sediment Control(ESC) (A) NA—
Existing Right-of-Way Improvements (B) $
Future Public Road Improvements&Drainage Facilities (C) $ 8,687,968.7
Private Improvements (D) $
Performance Bond*Amount (A+B+C+D) = TOTAL (T) $ 8,687,968.7
Minimum bond'amount is$1000. (B+C)x
0.20= $ 1,737,593.7
Maintenance/Defect Bond*Total
NAME OF PERSON PREPARING BOND*REDUCTION: Date:
'NOTE: The word"bond"as used in this document means any financial guarantee acceptable to the City of Renton.
**NOTE:All prices include labor,equipment,materials,overhead and profit. Prices are from IRS Means data adjusted for the Seattle area
or from local sources if not included in the RS Means database.
***NOTE: Stabilization/Erosion Sediment Control(ESC)worksheet is not included in the City of Renton 2009 Surface Water Design Manual
Amendment,Reference 8-H.
REQUIRED BOND*AMOUNTS ARE SUBJECT TO REVIEW AND MODIFICATION BY RDSD
Page 1 of 7 Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet Report Date: 10/16/2012
Site Improvement Bond Quantity Worksheet
Existing Future Public Private Quantity Completed
Right-of-Way Road Improvements Improvements (Bond Reduction)"
&Drainage Facilities Quant.
Number Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Com _e Cost
GENERAL ITEMS
Backfill&Compaction-embankment GI-1 $ 5.62 CY 0.00 0.00 0.00 0.00
Backfill&Compaction-trench GI-2 $ 8.53 CY 0.00 0.00 0.00 0.00
Clear/Remove Brush,by hand GI-3 $ 0.36 SY 0.00 0.00 0.00 0.00
Clearing/Grubbing/Tree Removal GI-4 $ 8,876.16 Acre 0.00 0.00 0.00 0.00
Excavation-bulk GI-5 $ 1.50 CY 0.00 8300 13,200.00 0.00 0.00
Excavation-Trench GI-6 $ 4.06 CY 0.00 0.00 0.00 0.00
Fencing,cedar,6'high GI-7 $ 18.55 LF 0.00 0.00 0.00 0.00
Fencing,chain link,vinyl coated, 6'high GI-8 $ 13.44 LF 0.00 50 672.00 0.00 0.00
Fencing,chain link,gate,vinyl coated, 20' GI-9 $ 1,271.81 Each 0.00 1 1,271.81 0.00 0.00
Fencing,split rail,3'high GI-10 $ 12.12 LF 0,00 0.00 0.00 0.00
Fill&compact-common barrow GI-11 $ 22.57 CY 0.00 6700 151.219.00 0.00 0.00
Fill&compact-gravel base GI-12 $ 25.48 CY 0.00 0.00 0.00 0.00
Fill&compact-screened topsoil GI-13 $ 37.85 CY 0.00 1000 37.850.00 1 0.00 0.00
Gabion,12"deep,stone filled mesh GI-14 $ 54.31 SY 0.00 0.00 0.00 0.00
Gabion,18"deep,stone filled mesh GI-15 $ 74.85 SY 0.00 0.00 0.00 0.00
Gabion,36"deep,stone filled mesh GI-16 $ 132.48 SY 0.00 0.00 0.00 0.00
Grading,fine,by hand GI-17 $ 2.02 SY 0.00 0.00 0.00 0.00
Grading,fine,with grader GI-18 $ 0.95 SY 0.00 12000 11,400.00 0.00 0.00
Monuments,3'long GI-19 $ 135.13 Each 0.00 0.00 0.00 0.00
Sensitive Areas Sign GI-20 $ 2.88 Each 0.00 0.00 1 0.00 0.00
Sodding,1"deep,sloped ground GI-21 $ 7.46 SY 0.00 0.00 0.00 0.00
Surveying,line&grade GI-22 $ 788.26 Day 0.00 0.00 0.00 0.00
Surveying,lot location/lines GI-23 $ 1,556,64 Acre 0.00 24.41 37,982.02 0.00 0.00
Traffic control crew 2 flaggers) GI-24 $ 85.18 HR 0.00 0.00 0.00 0.00
Trail,4"chipped wood GI-25 $ 7.59 SY 0.00 0.00 0.00 0,00
Trail,4"crushed cinder GI-26 $ 8.33 SY 0.00 0.00 0.00 0.00
Trail,4"top course GI-27 $ 8.19 SY 0.00 0.00 1 0.00 0.00
Wall,retaining,concrete GI-28 $ 44.16 SF 0.00 0.00 0.001 1 0.00
Wall,rockery GI-29 $ 9.49 SF 0.00 0.00 o.001 0.00
Page 2 of 7 SUBTOTAL 0.00 253,594.83 0.00 0.00
Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet Report Date: 10/16/2012
Site Improvement Bond Quantity Worksheet
Existing Future Public Private Bond Reduction'
Right-of-way Road Improvements Improvements
&Drainage Facilities Quant.
Number Unit Price Unit Quant Cost Quant. Cost Quant. Cost Com fete Cost
ROADIMPROVEMENT
AC Grinding,4'wide machine<1000sy RI-1 $ 23.00 SY 0.00 450 10,350.00 0.00 0.00
AC Grinding,4'wide machine 1000-2000sy RI-2 $ 5.75 SY 0.00 0.00 0.00 0.00
AC Grinding,4'wide machine>2000sy RI-3 $ 1.38 SY 0.00 0.00 0.00 0.00
AC Removal/Disposal/Repair RI-4 $ 41.14 SY 0.00 11200 460,768.00 0.00 0.00
Barricade,type I RI-5 $ 30.03 LF 0.00 0.00 0.00 0.00
Barricade,type III(Permanent) RI-6 $ 45.05 LF 0,00 0.00 0.00 0.00
Curb&Gutter,rolled RI-7 $ 13.27 LF 0.00 0.00 0.00 0.00
Curb&Gutter,vertical RI-8 $ 9.69 LF 0.00 0.00 0,00 0.00
Curb and Gutter,demolition and disposal RI-9 $ 13.58 LF 0.00 0.00 0.00 0.00
Curb,extruded asphalt RI-10 $ 2.44 LF 0.00 0.00 0.00 0.00
Curb,extruded concrete RI-11 $ 2.56 LF 0.00 0.00 0.00 0.00
Sawcut,asphalt,3"depth RI-12 $ 1.85 LF 0.00 850 1,572.50 0.00 0.00
Sawcut,concrete,per 1"depth RI-13 $ 1.69 LF 0.00 0.00 0.00 0.00
Sealant,asphalt RI-14 $ 0.99 LF 0.00 0.00 0.00 0.00
Shoulder,AC, (see AC road unit price) RI-15 $ - SY 0.00 0.00 0.00 0.00
Shoulder,gravel,4"thick RI-16 $ 7.53 SY 0.00 0.00 0.00 0.00
Sidewalk,4"thick RI-17 $ 30.52 SY 0.00 0.00 0.00 0.00
Sidewalk,4"thick,demolition and disposal RI-18 $ 27.73 SY 0.00 0,00 0.00 0.00
Sidewalk,5"thick RI-19 $ 34.94 SY 0.00 0.00 0.00 0.00
Sidewalk,5"thick,demolition and disposal RI-20 $ 34.65 SY 0.00 0,00 0.00 0.00
Sign,handicap RI-21 $ 85.28 Each 0.00 0.00 0.00 0.00
Striping,per stall RI-22 $ 5.82 Each 0.00 0.00 0.00 0.00
Striping,thermoplastic,(for crosswalk) RI-23 $ 2.38 SF 0.00 0.00 0.00 0.00
Striping,4"reflectorized line RI-24 $ 0.25 LF 0.001 1 0.00 1 0.001 1 0.00
Page 3 of 7 SUBTOTAL 0.00 472,690.50 0.00 0.00
Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet Report Date: 10/16/2012
Site Improvement Bond Quantity Worksheet
Existing Future Public Private Bond Reduction*
Right-of-way Road Improvements Improvements
&Drainage Facilities Quant.
Number Unit Price Unit Quant Cost Quant. Cost OuantT 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 1 $ 3.60 SY 0.00 0.00 0.00 0.00
AC Overlay,1.5"AC RS-2 $ 7.39 SY 0.00 0.00 0.00 0.00
AC Overlay,2"AC RS-3 $ 8.75 SY 0.00 0.00 0.00 0.00
AC Road,2",4"rock,First 2500 SY RS-4 $ 17.24 SY 0.00 0.00 0.00 0.00
AC Road,2",4"rock,Qty,over 2500SY RS-5 $ 13.36 SY 0.00 0.00 0.00 0.00
AC Road,3",4"rock,First 2500 SY RS-6 $ 19.69 SY 0.00 0.00 0.00 0.00
AC Road,3",4"rock,Qty.over 2500 SY RS-7 $ 15.81 SY 0.00 0.00 0.00 0.00
AC Road,5",First 2500 SY RS-8 $ 14.57 SY 0.00 0.00 0.00 0.00
AC Road,5",Qty.Over 2500 SY RS-9 $ 13.94 SY 0.00 0.00 0.00 0.00
AC Road,6",First 2500 SY RS-10 $ 16.76 SY 0.00 0.00 0.00 0.00
AC Road,6",Qty.Over 2500 SY RS-11 $ 16.12 SY 0.00 0.00 0.00 0.00
Asphalt Treated Base,4"thick RS-12 $ 9.21 SY 0.00 0.00 0.00 0.00
Gravel Road,4"rock,First 2500 SY RS-13 $ 11.41 SY 0.00 0.00 0.00 0.00
Gravel Road,4"rock,Qty.over 2500 SY RS-14 $ 7.53 SY 0.00 0.00 0.00 0.00
PCC Road,5",no base,over 2500 SY RS-15 $ 21,51 SY 0.00 0.00 0.00 0.00
PCC Road, 6",no base,over 2500 SY RS-16 $ 21.87 SY 0.00 0.00 0.00 0.00
Thickened Edge RS-17 $ 6.89 LF 0.00 0.00 0.00 0.00
Page 4 of 7 SUBTOTAL 0.00 0.00 0.00 0.00
Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet Report Date: 10/16/2012
Site Improvement Bond Quantity Worksheet
Existing Future Public Private Bond Reduction`
Right-of-way Road Improvements Improvements
&Draina a Facilities Quant.
Number Unit Price Unit Quant. Cost Quant: I Cost Quant. Cost Com fete 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 $ 16.74 SY 0.00 250 4,185.00 1 0.001 0.00
Bollards-fixed D-2 $ 240.74 Each 0.00 1 0.00 1 0.00 0.00
Bollards-removable D-3 $ 452.34 Each 0.001 1 0.001 1 0.001 0.00
(CBs include frame and lid)
CB Type I D-4 $ 1,257.64 Each 0,00 6 7,545.84 0.00 0.00
CB Type IL D-5 $ 1,433.59 Each 0.00 2 2,867.18 0.00 0.00
CB Type II,48"diameter D-6 $ 2,033.57 Each 0.00 9 18,302.13 0.00 0.00
for additional depth over 4' D-7 $ 436.52 FT 0.00 0.00 0.00 0.00
CB Type II,54"diameter D-8 $ 2,192.54 Each 0.00 0.00 0.00 0.00
for additional depth over 4' D-9 $ 486.53 FT 0.00 1 0.00 0.00 0.00
CB Type II,60"diameter D-10 $ 2,351.52 Each 0.00 1 2,351.52 0.00 0.00
for additional depth over 4' D-11 $ 536.54 FT 0.00 0.00 0.00 0.00
CB Type II,72"diameter D-12 $ 3,212.64 Each 0.00 0.00 0.00 0.00
for additional depth over 4' D-13 $ 692.21 FT 0.00 0.00 0.00 0.00
Through-curb Inlet Framework(Add) D-14 $ 366.09 Each 0.00 0.00 0.00 0.00
Cleanout,PVC,4" D-15 $ 130.55 Each 0.00 0,00 0.00 0.00
Cleanout,PVC,6" D-16 $ 174.90 Each 0.00 20 3,498.00 0.00 0.00
Cleanout,PVC,8" D-17 $ 224.19 Each 0.00 1 0.00 0.00 0.00
Culvert,PVC,4" D-18 $ 8.64 LF 0.00 0.00 0.00 0.00
Culvert,PVC,6" D-19 $ 12.60 LF 0.00 3000 37.800.00 0.00 0.00
Culvert,PVC, 8" D-20 $ 13.33 LF 0.00 0.00 0.00 0.00
Culvert,PVC, 12" D-21 $ 21.77 LF 0.00 0.00 0.00 0.00
Culvert,CMP,8" D-22 $ 17.25 LF 0.00 0.00 0.00 0.00
Culvert,CMP, 12" D-23 $ 26.45 LF 0.00 0.00 0.00 0.00
Culvert,CMP, 15" D-24 $ 32.73 LF 0.00 0.00 0.00 0.00
Culvert,CMP, 18" D-25 $ 37.74 LF 0.00 0.00 0.00 1 0.00
Culvert,CMP,24" D-26 $ 53.33 LF 0,00 0.00 0.00 0.00
Culvert.CMP,30" D-27 $ 71.45 LF 0.00 0.00 0.00 0.00
Culvert,CMP,36" D-28 $ 112.11 LF 0.001 0.00 1 0.00 0.00
Culvert,CMP,48" D-29 $ 140.83 LF 0.00 0.00 0.00 0.00
Culvert,CMP,60" D-30 $ 235.45 LF 0.00 0.00 0.00 0.00
Culvert,CMP,72" D-31 $ 302.58 LF 0.001 1 0.001 1 0.00 0.00
Page 5 of 7 SUBTOTAL 0.00 76,549.67 0.00 0.00
Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet Report Date: 10/16/2012
Site Improvement Bond Quantity Worksheet
Existing Future Public Private Bond Reduction'
Right-of-way Road Improvements Improvements
DRAINAGE CONTINUED &Drainage Facilities Quant.
Number Unit Price Unit Quant. Cost Quant. Cost Quant. Cost CornpleteF Cost
Culvert,Concrete,8" D-32 $ 21.02 LF 0 0 0 0
Culvert,Concrete, 12" D-33 $ 30.05 LF 0 0 0 0
Culvert,Concrete, 15" D-34 $ 37.34 LF 0 0 0 0
Culvert,Concrete, 18" D-35 $ 44.51 LF 0 0 0 0
Culvert,Concrete,24" D-36 $ 61.07 LF 0 0 0 0
Culvert,Concrete,30" D-37 $ 104.18 LF 0 0 0 0
Culvert,Concrete,36" D-38 $ 137.63 LF 0 0 0 1 0
Culvert,Concrete,42" D-39 $ 158.42 LF 0 0 0 0
Culvert,Concrete,48" D-40 $ 175.94 LF 0 0 0 0
Culvert,CPP,6" D-41 $ 10.70 LF 0 0 0 0
Culvert,CPP,8" D-42 $ 16.10 LF 0 0 0 0
Culvert,CPP,12" D-43 $ 20.70 LF 0 0 0 0
Culvert,CPP,15" D-44 $ 23.00 LF 0 0 0 0
Culvert,CPP,1 B" D-45 $ 27.60 LF 0 0 0 0
Culvert,CPP,24" D-46 $ 36.80 LF 0 0 0 0
Culvert,CPP,30" D-47 $ 48.30 LF 0 0 0 0
Culvert,CPP,36" D-48 $ 55.20 LF 0 0 0 1 0
Ditching D-49 $ 8.08 CY 0 0 0 0
Flow Dispersal Trench (1,436 base+) D-50 $ 25.99 LF 0 0 0 0
French Drain (3'depth) D-51 $ 22.60 LF 0 0 0 0
Geotextile,laid in trench,polypropylene D-52 $ 2.40 SY 0 0 0 0
Infiltration pond testing D-53 $ 74.75 HR 0 0 0 0
Mid-tank Access Riser.48"dia, 6'deep D-54 $ 1,605.40 Each 0 0 0 0
Pond Overflow Spillway D-55 $ 14.01 SY 0 0 0 0
Restrictor/Oil Separator.12" D-56 $ 1,045.19 Each 0 1 0 0 0
Restrictor/Oil Separator.15" D-57 $ 1,095.56 Each 0 0 0 0
Restrictor/Oil Separator,18" D-58 $ 1,146.16 Each 0 0 0 0
Riprap,placed D-59 $ 39.08 CY 0 0 0 0
Tank End Reducer 36"diameter D-60 $ 1,000.50 Each 0 0 0 0
Trash Rack,12" D-61 $ 211.97 Each 0 4 847.88 0 0
Trash Rack, 15" D-62 $ 237.27 Each 0 0 0 0
Trash Rack,18" D-63 1 $ 268.89 Each 01 0 0 0
Trash Rack,21" D-64 1 $ 306.84 Each 01 01 0 0
Page 6 of 7 SUBTOTAL 0.00 847.88 0.00 0.00
Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet Report Date: 10/16/2012
Site Improvement Bond Quantity Worksheet
Existing Future Public Private Bond Reduction*
Right-of-way Road Improvements Improvements
&Drainage Facilities Quant.
Number Unit Price Unit Quant. Price Quant. Cost Quant. Cast Com fete Cost
PARKING LOT SURFACING
2"AC,2"top course rock&4"borrow PL-1 $ 15.84 SY 0 0 0 0
2"AC, 1.5 top course& 2.5 base course PL-2 $ 17.24 SY 0 0 0 0
4"select borrow PL-3 $ 4.55 SY 0 0 0 0
1.5"top course rock&2.5"base course PL-4 $ 11.41 SY 0 0 0 0
WRITE-IN-ITEMS
(Such as detention/water quality vaults.)
Slotted Drain System WI-1 $ 250.00 LF 0 1150 287,500.00 0.00 0.00
Culvert,DIP, 12" WI-2 $ 90.00 LF 0 509 45,810.00 0.00 0.00
Culvert,DIP, 18" WI-3 $ 105.00 LF 0 1614 169,470.00 0.00 0.00
Asphalt Surface Course 4",2"TC, 12"BC WI-4 $ 22.00 SF 0 235645 5,184,190.00 0.00 0.00
Biofiltration Swale WI-5 $ 60.00 LF 0 200 12,000.00 0.00 0.00
Thermoplastic Pavement Marking WI-6 $ 22.00 SF 01 82001 180,400.00 0.001 0.00
SF 0 0.00 0.00 0.00
LF 0 0.00 0.00 0.00
LF 0 0.00 0.00 0.00
SUBTOTAL 0.00 5,879,370.00 0.00 0.00
SUBTOTAL(SUM ALL PAGES): 0.00 6,683,052.88 0.00 0.00
30%CONTINGENCY&MOBILIZATION: 0.00 2,004,915.86 0.00 0.00
GRANDTOTAL: 0.00 8,687,968.74 0.00 0.00
COLUMN: B C D E
Page 7 of 7
Unit prices updated: 02/12/02
Version: 4/22/02
Bond Quantities Worksheet Report Date: 10/16/2012
Appendix F
Flow Control and Water Facility Summary Sheet
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II
Technical Information Report (TIR) ' `
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
STORMWATER FACILITY SUMMARY SHEET DDES Permit
Number PRE12-012
(provide one Stormwater Facility Summary Sheet per Natural Discharge Location)
Overview:
Project Name
City of Renton Taxiway B System Rehabilitation (Phase II) Date October 16, 2012
Downstream Drainage Basins
Major Basin Name Lake Washington
Immediate Basin Name
Flow Control:
Flow Control Facility Name/Number N/A
Facility
Location N/A
If none,
Flow control provided in regional/shared facility (give
location) N/A
No flow control required N/A Exemption number
Cedar River
General Facility Information:
Type/Number of detention facilities: Type/Number of infiltration facilities:
ponds ponds
vaults tanks
tanks trenches
Control Structure Location
N/A
Type of Control Structure N/A Number of Orifices/Restrictions
Size of Orifice/Restriction: No. 1
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 N/A
Number of Lots N/A
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 -
i
All detention, infiltration and water quality facilities must include a detailed sketch.
(11"xl7" reduced size plan sheets may be used)
N/A
2009 Surface Water Design Manual 1/9/2009
2
` I
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
Water Quality:
Type/Number of water quality facilities/BMPs:
X 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
X 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
i (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 Wet Biofiltration Swales
South Facility: 0.29 cfs
Water Quality design flow North Facility: 0.29 cfs
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 11xl7" reduced size plan sheets may be used)
Please refer to Figure 4-1 for more information regarding the water quality types and
locations.
2009 Surface Water Design Manual 1/9/2009
4
Appendix G
Operation and Maintenance Manual
Renton Municipal Airport October 2012
TW B System Rehabilitation, Phase II
Technical Information Report (TIR) 'R.
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 4-CONTROL STRUCTURE/FLOW RESTRICTOR
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Structure Trash and debris Trash or debris of more than'%cubic foot which No Trash or debris blocking or
is located immediately in front of the structure potentially blocking entrance to
opening or is blocking capacity of the structure by structure.
more than 10%.
Trash or debris in the structure that exceeds'/3 No trash or debris in the structure.
the depth from the bottom of basin to invert the
lowest pipe into or out of the basin.
Deposits of garbage exceeding 1 cubic foot in No condition present which would
volume. attract or support the breeding of
insects or rodents.
Sediment Sediment exceeds 60%of the depth from the Sump of structure contains no
bottom of the structure to the invert of the lowest sediment.
pipe into or out of the structure or the bottom of
the FROP-T section or is within 6 inches of the
invert of the lowest pipe into or out of the
structure or the bottom of the FROP-T section.
Damage to frame Corner of frame extends more than%inch past Frame is even with curb.
and/or top slab curb face into the street(If applicable).
Top slab has holes larger than 2 square inches or Top slab is free of holes and cracks.
cracks wider than'%inch.
Frame not sitting flush on top slab, i.e., Frame is sitting flush on top slab.
separation of more than%inch of the frame from
the top slab.
Cracks in walls or Cracks wider than'/2 inch and longer than 3 feet, Structure is sealed and structurally
bottom any evidence of soil particles entering structure sound.
through cracks,or maintenance person judges
that structure is unsound.
Cracks wider than%inch and longer than 1 foot No cracks more than 1/4 inch wide at
at the joint of any inlet/outlet pipe or any evidence the joint of inlet/outlet pipe.
of soil particles entering structure through cracks.
Settlement/ Structure has settled more than 1 inch or has Basin replaced or repaired to design
misalignment rotated more than 2 inches out of alignment. standards.
Damaged pipe joints Cracks wider than 1/2-inch at the joint of the No cracks more than '%-inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of inlet/outlet pipes.
the structure at the joint of the inlet/outlet pipes.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Ladder rungs missing Ladder is unsafe due to missing rungs, Ladder meets design standards and
or unsafe misalignment, rust,cracks,or sharp edges. allows maintenance person safe
access.
FROP-T Section Damage T section is not securely attached to structure T section securely attached to wall
wall and outlet pipe structure should support at and outlet pipe.
least 1,000 Ibs of up or down pressure.
Structure is not in upright position(allow up to Structure in correct position.
10%from plumb).
Connections to outlet pipe are not watertight or Connections to outlet pipe are water
show signs of deteriorated grout. tight;structure repaired or replaced
and works as designed.
Any holes—other than designed holes—in the Structure has no holes other than
structure. designed holes.
Cleanout Gate Damaged or missing Cleanout gate is missing. Replace cleanout gate.
2009 Surface Water Design Manual—Appendix A 1/9/2009
A-7
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 4- CONTROL STRUCTURE/FLOW RESTRICTOR
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Cleanout gate is not watertight. Gate is watertight and works as
designed.
Gate cannot be moved up and down by one Gate moves up and down easily and
maintenance person. is watertight.
Chain/rod leading to gate is missing or damaged. Chain is in place and works as
designed.
Orifice Plate Damaged or missing Control device is not working properly due to Plate is in place and works as
missing,out of place,or bent orifice plate. designed.
Obstructions Any trash,debris,sediment,or vegetation Plate is free of all obstructions and
blocking the plate. works as designed.
Overflow Pipe Obstructions Any trash or debris blocking(or having the Pipe is free of all obstructions and
potential of blocking)the overflow pipe. works as designed.
Deformed or damaged Lip of overflow pipe is bent or deformed. Overflow pipe does not allow
lip overflow at an elevation lower than
design
Inlet/Outlet Pipe Sediment Sediment filling 20%or more of the pipe. Inlet/outlet pipes clear of sediment.
accumulation
Trash and debris Trash and debris accumulated in inlet/outlet No trash or debris in pipes.
pipes(includes floatables and non-floatables).
Damaged Cracks wider than'/z-inch at the joint of the No cracks more than Y<-inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of the inlet/outlet pipe.
at the joints of the inlet/outlet pipes.
Metal Grates Unsafe grate opening Grate with opening wider than 7/8 inch. Grate opening meets design
(If Applicable) standards.
Trash and debris Trash and debris that is blocking more than 20% Grate free of trash and debris.
of grate surface. footnote to guidelines for disposal
Damaged or missing Grate missing or broken member(s)of the grate. Grate is in place and meets design
standards.
Manhole Cover/Lid Cover/lid not in place Cover/lid is missing or only partially in place. Cover/lid protects opening to
Any open structure requires urgent structure.
maintenance.
Locking mechanism Mechanism cannot be opened by one Mechanism opens with proper tools.
Not Working maintenance person with proper tools. Bolts
cannot be seated. Self-locking cover/lid does not
work.
Cover/lid difficult to One maintenance person cannot remove Cover/lid can be removed and
Remove cover/lid after applying 80 lbs.of lift. reinstalled by one maintenance
person.
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-8
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 5-CATCH BASINS AND MANHOLES
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Structure Sediment Sediment exceeds 60%of the depth from the Sump of catch basin contains no
bottom of the catch basin to the invert of the sediment.
lowest pipe into or out of the catch basin or is
within 6 inches of the invert of the lowest pipe
into or out of the catch basin.
Trash and debris Trash or debris of more than'/2 cubic foot which No Trash or debris blocking or
is located immediately in front of the catch basin potentially blocking entrance to
opening or is blocking capacity of the catch basin catch basin.
by more than 10%.
Trash or debris in the catch basin that exceeds No trash or debris in the catch basin.
1/3 the depth from the bottom of basin to invert the
lowest pipe into or out of the basin.
Dead animals or vegetation that could generate No dead animals or vegetation
odors that could cause complaints or dangerous present within catch basin.
gases(e.g.,methane).
Deposits of garbage exceeding 1 cubic foot in No condition present which would
volume. attract or support the breeding of
insects or rodents.
Damage to frame Corner of frame extends more than%inch past Frame is even with curb.
and/or top slab curb face into the street(If applicable).
Top slab has holes larger than 2 square inches or Top slab is free of holes and cracks.
cracks wider than%inch.
Frame not sitting flush on top slab,i.e., Frame is sitting flush on top slab.
separation of more than%inch of the frame from
the top slab.
Cracks in walls or Cracks wider than Yz inch and longer than 3 feet, Catch basin is sealed and
bottom any evidence of soil particles entering catch structurally sound.
basin through cracks,or maintenance person
judges that catch basin is unsound.
Cracks wider than'/=inch and longer than 1 foot No cracks more than 1/4 inch wide at
at the joint of any inlet/outlet pipe or any evidence the joint of inlet/outlet pipe.
of soil particles entering catch basin through
cracks.
Settlement/ Catch basin has settled more than 1 inch or has Basin replaced or repaired to design
misalignment rotated more than 2 inches out of alignment. standards.
Damaged pipe joints Cracks wider than'/z-inch at the joint of the No cracks more than Y<inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of inlet/outlet pipes.
the catch basin at the joint of the inlet/outlet
pipes.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Inlet/Outlet Pipe Sediment Sediment filling 20%or more of the pipe. Inlet/outlet pipes clear of sediment.
accumulation
Trash and debris Trash and debris accumulated in inlet/outlet No trash or debris in pipes.
pipes(includes floatables and non-floatables).
Damaged Cracks wider than'/z-inch at the joint of the No cracks more than'%-inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of the inlet/outlet pipe.
at the joints of the inlet/outlet pipes.
2009 Surface Water Design Manual—Appendix A 1/9/2009
A-9
I
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 5-CATCH BASINS AND MANHOLES
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Metal Grates Unsafe grate opening Grate with opening wider than 7/8 inch. Grate opening meets design
(Catch Basins) standards.
Trash and debris Trash and debris that is blocking more than 20% Grate free of trash and debris.
of grate surface. footnote to guidelines for disposal
Damaged or missing Grate missing or broken member(s)of the grate. Grate is in place and meets design
Any open structure requires urgent standards.
maintenance.
Manhole Cover/Lid Cover/lid not in place Cover/lid is missing or only partially in place. Cover/lid protects opening to
Any open structure requires urgent structure.
maintenance.
Locking mechanism Mechanism cannot be opened by one Mechanism opens with proper tools.
Not Working maintenance person with proper tools. Bolts
cannot be seated. Self-locking cover/lid does not
work.
I
Cover/lid difficult to One maintenance person cannot remove Cover/lid can be removed and
Remove cover/lid after applying 80 lbs.of lift. reinstalled by one maintenance
person.
I
I
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-10
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 6-CONVEYANCE PIPES AND DITCHES
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Pipes Sediment&debris Accumulated sediment or debris that exceeds Water flows freely through pipes.
accumulation 20%of the diameter of the pipe.
Vegetation/roots Vegetation/roots that reduce free movement of Water flows freely through pipes.
water through pipes.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Damage to protective Protective coating is damaged;rust or corrosion Pipe repaired or replaced.
coating or corrosion is weakening the structural integrity of any part of
pipe.
Damaged Any dent that decreases the cross section area of Pipe repaired or replaced.
pipe by more than 20%or is determined to have
weakened structural integrity of the pipe.
Ditches Trash and debris Trash and debris exceeds 1 cubic foot per 1,000 Trash and debris cleared from
square feet of ditch and slopes. ditches.
Sediment Accumulated sediment that exceeds 20%of the Ditch cleaned/flushed of all sediment
accumulation design depth. and debris so that it matches design.
Noxious weeds Any noxious or nuisance vegetation which may Noxious and nuisance vegetation
constitute a hazard to County personnel or the removed according to applicable
public. regulations. No danger of noxious
vegetation where County personnel
or the public might normally be.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Vegetation Vegetation that reduces free movement of water Water flows freely through ditches.
through ditches.
Erosion damage to Any erosion observed on a ditch slope. Slopes are not eroding.
slopes
Rock lining out of One layer or less of rock exists above native soil Replace rocks to design standards.
place or missing(If area 5 square feet or more,any exposed native
Applicable) soil.
2009 Surface Water Design Manual—Appendix A 1/9/2009
A-11
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 7- DEBRIS BARRIERS (E.G., TRASH RACKS)
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed.
Site Trash and debris Trash or debris plugging more than 20%of the Barrier clear to receive capacity flow.
area of the barrier.
Sediment Sediment accumulation of greater than 20%of Barrier clear to receive capacity flow.
accumulation the area of the barrier
Structure Cracked broken or Structure which bars attached to is damaged- Structure barrier attached to is
loose pipe is loose or cracked or concrete structure is sound.
cracked, broken of loose.
Bars Bar spacing Bar spacing exceeds 6 inches. Bars have at most 6 inche spacing.
Damaged or missing Bars are bent out of shape more than 3 inches. Bars in place with no bends more
bars than 3%inch.
Bars are missing or entire barrier missing. Bars in place according to design.
Bars are loose and rust is causing 50% Repair or replace barrier to design
deterioration to any part of barrier. standards.
I
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-12
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 11 -GROUNDS (LANDSCAPING)
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Site Trash or litter Any trash and debris which exceed 1 cubic foot Trash and debris cleared from site.
per 1,000 square feet(this is about equal to the
amount of trash it would take to fill up one
standard size office garbage can). In general,
there should be no visual evidence of dumping.
Noxious weeds Any noxious or nuisance vegetation which may Noxious and nuisance vegetation
constitute a hazard to County personnel or the removed according to applicable
public. regulations. No danger of noxious
vegetation where County personnel
or the public might normally be.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint, according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Grass/groundcover Grass or groundcover exceeds 18 inches in Grass or groundcover mowed to a
height. height no greater than 6 inches.
Trees and Shrubs Hazard Any tree or limb of a tree identified as having a No hazard trees in facility.
potential to fall and cause property damage or
threaten human life. A hazard tree identified by
a qualified arborist must be removed as soon
as possible.
Damaged Limbs or parts of trees or shrubs that are split or Trees and shrubs with less than 5%
broken which affect more than 25%of the total of total foliage with split or broken
foliage of the tree or shrub. limbs.
Trees or shrubs that have been blown down or No blown down vegetation or
knocked over. knocked over vegetation. Trees or
shrubs free of injury.
Trees or shrubs which are not adequately Tree or shrub in place and
supported or are leaning over,causing exposure adequately supported;dead or
of the roots. diseased trees removed.
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-16
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 13- BASIC BIOFILTRATION SWALE (GRASS)
i
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Site Trash and debris Any trash and/or debris accumulated on the No trash or debris on the bioswale
bioswale site. site.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Swale Section Sediment Sediment depth exceeds 2 inches in 10%of the No sediment deposits in grass
accumulation swale treatment area. treatment area of the bioswale.
Sediment inhibits grass growth over 10%of Grass growth not inhibited by
Swale length. sediment.
Sediment inhibits even spreading of flow. Flow spreads evenly through swale
Erosion/scouring Eroded or scoured swale bottom due to No eroded or scoured areas in
channelization or high flows. bioswale. Cause of erosion or scour
addressed.
Poor vegetation Grass is sparse or bare or eroded patches occur Swale has no bare spots and grass
coverage in more than 10%of the swale bottom. is thick and healthy.
Grass too tall Grass excessively tall(greater than 10 inches), Grass is between 3 and 4 inches tall,
grass is thin or nuisance weeds and other thick and healthy. No clippings left
vegetation has taken over. in swale. No nuisance vegetation
present.
Excessive shade Grass growth is poor because sunlight does not Health grass growth or swale
reach swale. converted to a wet bioswale.
Constant baseflow Continuous flow through the swale,even when it Baseflow removed from swale by a
has been dry for weeks or an eroded,muddy low-flow pea-gravel drain or
channel has formed in the Swale bottom. bypassed around the swale.
Standing water Water pools in the swale between storms or does Swale freely drains and there is no
not drain freely. standing water in swale between
storms.
Channelization Flow concentrates and erodes channel through No flow channels in swale.
swale.
Flow Spreader Concentrated flow Flow from spreader not uniformly distributed Flows are spread evenly over entire
across entire swale width. swale width.
Inlet/Outlet Pipe Sediment Sediment filling 20%or more of the pipe. Inlet/outlet pipes clear of sediment.
accumulation
Trash and debris Trash and debris accumulated in inlet/outlet No trash or debris in pipes.
pipes(includes floatables and non-floatables).
Damaged Cracks wider than%-inch at the joint of the No cracks more than %-inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of the inlet/outlet pipe.
at the joints of the inlet/outlet pipes.
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-18
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 15- FILTER STRIP
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance Is Performed
Site Trash and debris Any trash and debris accumulated on the filter Filter strip site free of any trash or
strip site. debris
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Grass Strip Sediment Sediment accumulation on grass exceeds 2 No sediment deposits in treatment
accumulation inches depth. area.
Erosion/scouring Eroded or scoured swale bottom due to No eroded or scoured areas in
channelization or high flows. bioswale. Cause of erosion or scour
addressed.
Grass too tall Grass excessively tall(greater than 10 inches), Grass is between 3 and 4 inches tall,
grass is thin or nuisance weeds and other thick and healthy. No clippings left
vegetation has taken over. in swale. No nuisance vegetation
present.
Vegetation ineffective Grass has died out,become excessively tall Grass is healthy,less than 9 inches
(greater than 10 inches)or nuisance vegetation is high and no nuisance vegetation
taking over. present.
Flow Spreader Concentrated flow Flow from spreader not uniformly distributed Flows are spread evenly over entire
across entire swale width. swale width.
Inlet/Outlet Pipe Sediment Sediment filling 20%or more of the pipe. Inlet/outlet pipes clear of sediment.
accumulation
Trash and debris Trash and debris accumulated in inlet/outlet No trash or debris in pipes.
pipes(includes floatables and non-floatables).
Damaged Cracks wider than Yz-inch at the joint of the No cracks more than%-inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of the inlet/outlet pipe.
at the joints of the inlet/outlet pipes.
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-20
Fueling Operations
This activity applies if you refuel vehicles on the premises, whether a large sized gas station or a single
pump maintenance yard installation. It also covers mobile fueling operations. Stormwater runoff from
fueling areas may be contaminated with toxic hydrocarbons, oils and greases, and metals.
e
The following BMPs,or equivalent measures,methods, or practices, are
required if you are engaged in dedicated permanent fueling operations:
Cover the fueling area with an overhanging roof structure or canopy so that
precipitation cannot come in contact with the fueling area.
See BMP Info Sheet 3 in Chapter 5 for information on covering options.
An exception to this requirement is granted for mobile fueling equipment,
floating fuel islands on water, and oversized vehicles that can not
maneuver under a roof.
Pave the fueling area with Portland cement concrete and contain the area to
prevent uncontaminated stormwater from running into the fueling area and
carrying pollutants to the onsite storm drainage system or adjacent surface
water or conveyance systems.
I-,r- See BMP Info Sheet 5 in Chapter 5 for information on containment.
Install and maintain an oil or spill control device in the appropriate catch
basin(s)to treat runoff from the fueling area.
See the King County Surface Water Design Manual for various designs
and the BUT Info Sheet 9 in Chapter 5 for further information on
oil/water separators.
Never hose down the fueling area to the storm drains. Contaminated runoff
- must be collected for proper disposal.
Required Routine Maintenance:
• Post signs to remind employees and customers not to top off the fuel
tank when filling. Post signs that ban customers and employees from
changing engine oil or other fluids at that location.
• Store and maintain appropriate spill cleanup materials in a location
known to all. Ensure that employees are familiar with the site's spill
control plan and/or proper spill cleanup procedures.
January 2009 King County Stormwater Pollution Prevention Manual
Fueling Operations(continued)
If you cannot implement the above requirements on your site, consider
ceasing your on-site fueling activities and take your vehicles to a fueling
station that meets these requirements.
The following BMPs, or equivalent measures, methods, or practices,are
required if you are engaged in mobile fueling operations:
Locate the fueling operation to ensure leaks or spills will not discharge,
flow, or be washed into the storm drainage system, surface water, or
groundwater.
Use drip pans or absorbent pads to capture drips or spills during fueling
operations.
If fueling is done during evening hours, lighting must be provided.
Required Routine Maintenance:
• Store and maintain appropriate spill cleanup materials in the mobile
fueling vehicle. Ensure that employees are familiar with proper spill
control and cleanup procedures.
The following BMPs are optional unless the above minimum required
BMPs do not provide adequate source control.
Use absorbent pillows or similar absorbent materials in or around storm
drain inlets on the property to filter oily runoff. These require frequent
maintenance and close attention,but can be useful in short-term situations. -
Used absorbent materials containing oil must be picked up by a qualified
disposal contractor.
A catch basin insert configured for oil removal may remove some of the
pollutants in runoff from this activity. Catch basin inserts require frequent
maintenance to be effective. Carefully consider this when evaluating your
options. The oil absorbent filter media must retain absorbed oil during future
storm events. See Chapter 6.6.1 of the King County Surface Water Design
Manual for more information regarding which filter media provide
acceptable oil retention.
See BMP Info Sheet 10 in Chapter 5 for more information.
For more information or assistance in implementing these best management practices,contact the King County
Department of Natural Resources and Parks Water and Land Resources Division at 206-296-1900.
Reader Note:The above requirements are the minimum required BMPs.If these BMPs fail to prevent discharges to the
storm drainage system,you will be asked to take additional measures to correct the continued pollution discharges.
King County Stormwater Pollution Prevention Manual January 2009
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Landscaping Activities and Vegetation Management
This broad activity encompasses all aspects of landscaping and vegetation management, from small-
scale yard maintenance to large-scale commercial landscaping businesses and vegetation
management programs. It includes vegetation removal, herbicide and insecticide application,
fertilizer application,watering, and other gardening and lawn care practices. Stormwater runoff from
areas that have been subject to pesticide or fertilizer application or extensive clearing, grading or
cutting may be contaminated with pesticides and other toxic organic compounds,metals, oils,
suspended solids,nutrients from fertilizer, and coliform bacteria, and may cause biochemical oxygen
demand.
While not required, consider using the Integrated Pest Management(IPM) approach for pest control.
IPM is an approach that uses an array of methods to manage pest damage with the least possible
hazard to people and the environment. IPM uses a combination of biological, cultural, and physical
practices that can significantly reduce or eliminate the use of pesticides.
See Activity Sheets A-5,"Storage of Pesticides and Fertilizers" and A-3, "Storage of Liquid
Materials in Portable Containers."Landscaping activities related to golf courses should refer to King
County's Golf Course BMP Manual(see Chapter 6 of this manual for more information).
Note: The term pesticide includes insecticides, herbicides,fungicides, rodenticides, etc.
The following BMPs,or equivalent measures,methods, or practices
are required if you are engaged in landscaping activities:
Do not apply any pesticides directly to surface waters,unless the
application is approved and permitted by the Washington State Department
of Ecology.
Mix pesticides so that spilled material will not be washed to surface waters,
the storm drainage system, or onto the ground. Clean up any spills
immediately. Ensure employees are trained on the proper use of pesticides
and in pesticide application techniques to prevent pollution. Washington
pesticide law requires most businesses that commercially apply pesticides
to the property of another to be licensed as a Commercial Applicator.
Follow manufacturers' recommendations and label directions. Pesticides
and fertilizers must never be applied if it is raining or about to rain. Do not
apply pesticides within 100 feet of surface waters such as lakes,ponds,
wetlands, and streams. This also can include stormwater conveyance
ditches. Remove weeds/vegetation in stormwater ditches by hand or other
January 2009 King County Stormwater Pollution Prevention Manual
Landscaping Activities and Vegetation Management(continued)
mechanical means. Chemicals should be used as a last resort.
Dispose of grass clippings, leaves,branches, sticks, or other collected
vegetation, by recycling, composting, or burning (if allowed). Do not
dispose of collected vegetation into storm drainage systems, conveyance
ditches, stormwater ponds, or surface water.
Use mulch or other erosion control measures when soils are exposed for
more than one week during the dry season or two days during the rainy
season.
Implement water conservation practices to assure sprinkler systems do not
"overspray"vegetated areas and discharge to hard surfaces such as
sidewalks, driveways, and parking lots. Adjust sprinkler heads accordingly.
Minimize water use so runoff does not occur or enter storm drainage
systems. Use approaches to reduce water use such as those described in the
Natural Yardcare program.
http://your.kingcounty.gov/solidwaste/naturalyardcare/watering.asp
I
The King County Noxious Weed Control Program provides best
management practices for the removal of typical noxious weeds such as
blackberry and purple loosestrife. Call 206-296-0290 or see
http://www.kingcounty.gov/environment/animal sandplants/noxious-
weeds/weed-control-practices.aspx for more information.
� � � • .
The following BMPs are optional unless the above minimum required
BMPs do not provide adequate source control:
Integrated pest management (IPM), a comprehensive approach to the use of
pesticides is the most effective BMP measure that can be taken for
herbicide, insecticide, and fungicide use.
See BMP Info Sheet 6 in Chapter 5 for information on IPM.
J* "A,-
Fertilizers should be worked into the soil rather than dumped or broadcast
onto the surface. Determine the proper fertilizer application for the types of
soil and vegetation involved. Soil should be tested for the correct fertilizer
usage.
Use mechanical methods of vegetation removal rather than applying
herbicides.
King County Stormwater Pollution Prevention Manual January 2009
Landscaping Activities and Vegetation Management(continued)
An effective measure that can be taken to reduce pesticide use, excessive
watering, and removal of dead vegetation involves careful soil mixing and
layering prior to planting. A topsoil mix or composted organic material
should be rototilled into the soil to create a transition layer that encourages
deeper root systems and drought-resistant plants. This practice can improve
the health of planted vegetation, resulting in better disease resistance and
reduced watering requirements.
Use native plants in landscaping.Native plants do not require extensive
fertilizer or pesticide applications.
For more information or assistance in implementing these best management practices,contact the King County
Department of Natural Resources and Parks Water and Land Resources Division at 206-296-1900.
Reader Note: The above requirements are the minimum required BMPs.If these BMPs fail to prevent discharges to
the storm drainage system,you will be asked to take additional measures to correct the continued pollution
discharges.
January 2009 King County Stormwater Pollution Prevention Manual
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gala
Clearing and Grading of Land for Small Construction Projects
This activity applies if you clear, grade or prepare land for projects. Stormwater runoff from
cleared and graded sites can be loaded with suspended sediments and attached pollutants such as
oils and greases,toxic hydrocarbon and herbicide compounds,metals, and nutrients. Control of
this runoff at the source can prevent large pollutant loadings from entering and degrading
receiving waters. Prior to clearing, grading, and preparation activities for construction sites
greater than 2,000 square feet, the King County Department of Development and Environmental
Services (DDES)must be contacted. You may need to follow the procedures for construction site
erosion and sediment control outlined in the King County Surface Water Design Manual,
Appendix D.
King County DDES coordinates the clearing, grading, and erosion control requirements on
individual sites. The King County Surface Water Design Manual has requirements for erosion
and sediment control measures. Appendix D (Erosion and Sediment Control Standards) outlines
requirements that all sites must implement. The King County Surface Water Design Manual
Appendix C (Small Project Drainage Requirements) addresses small project developments. Even
if your site does not require a permit, erosion control measures are still required to prevent turbid
water from entering drainage systems or surface waters. King County uses the authority of
K.C.C. 9.12 and this manual to develop erosion control requirements for those activities not
covered by the King County Surface Water Design Manual.
For more information or assistance in implementing these best management practices,contact the King County
Department of Natural Resources and Parks Stormwater Services Section at 206-296-1900.
Reader Note: The above requirements are the minimum required BMPs.If these BMPs fail to prevent discharges to
the storm drainage system you will be asked to take additional measures to correct the continued pollution
discharges.
January 2009 King County Stormwater Pollution Prevention Manual
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