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TECHNiCAL INFORMATION REPORT
for
Guy Lund Rlat
King eounfy Tax Parcef No. 4088Q04?7Q
Project#A04PM120, # L04S003?
Site Address:
16217 114th Avenue SE
Renton, Washington
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Prepared by: Loma M. Taylor, P.E.
TEC Project No. 281-PLS Date: September 12, 2005
2Q5 Front St.S. • P.O.Box 178 • tssaquah,WA 98027-0073 • tel.(425)39t-14f 5 • fax(425)391-1551 • www.teccivit.com
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TECHNICAL INFORMATION REPORT
for
Guy Lund P/at
King County Tax Parce/No. 0088000170
Project#A04PM120, # L04S0037
Site Address:
16217 114 h Avenue,SE
Renton, Washingtan
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PreparedDat: L ep e•.b 112,2a05',.
TEC Project No. 281-PLS Re sed, -Ma r 10, 2006
205 Front St.S. • P.O.Box 1787 . Issaquah,WA 98027-0073 • tel.425)391-1415 • fax(425)391-1.551 • www teccivil.com
Technical Information Report
Lund Plat
TABLE OF CONTENTS
Section Description Paae Number
1. Project Overview.......................................... 1
2. Conditions and Requirements Summary...........1
3. Off-Site Analysis..........................................5
4. Flow Control and Water Quality Facility Analysis 6
andDesign.....................................
5. Conveyance System Analysis and Design........9
6. Special Reports and Studies..........................9
7. Other Permits.............................................. 9
8. ESC Analysis and Design.............................. 9
9. Bond Quantities, Facility Summaries, and 9
Declaration of Covenant................................
10. Operations and Maintenance Manual............... 10
Apqendices
Appendix A: Figures
1. Technical Information Report (TIR) Worksheet
2. Site Location
3. Drainage Basins, Subbasins, & Site Characteristics
4. SCS Soils Map
Appendix B: Off-site Analysis Drainage System Table and Map
Appendix C: Analysis and Design
Appendix D: Maintenance Requirements for Privately Maintained Drainage
Facilities
Appendix E: Retention/Detention Facility Summary Sheet and Sketch
Engineering Plan in Lieu of Minor Floodplain Study
Appendix F: Sensitive Areas Study
Appendix G: Bond Quantities Worksheet
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SECTION 1
PROJECT OVERVIEW
This Technical Information Report is submitted to the King County DDES in accordance with
the King County Surface Water Design Manual (KCSWDM).
Appendix A contains a Technical Information Report (TIR) worksheet for the project (Figure 1),
as well as a Site Location Map (Figure 2), a Drainage Basins, Subbasins, and Site
Characteristics figure (Figure 3), and a Soils map (Figure 4). More detailed site information is
included in Appendix C with the existing and developed site runoff model data. The 2.05-acre
site is located at 16217 114 h Avenue SE in Renton, Washington.
SECTION 2
CONDITIONS AND REQUIREMENTS SUMMARY
Following is the text of the Preliminary Conditions of Approval. All of the conditions 1 — 12
either have been addressed, or will be addressed for the project. Note: number 3 is missing
from the original text of the conditions and is assumed to be a typographical error.
G. DECISION:
Proposed Short Plat (file No. L04S0037), received October 4, 2004 as described by Attachment 1 of this
report is GRANTED PRELIMINARY APPROVAL;subject to the following conditions of final approval:
1.Title 19A
A. Compliance with all platting provisions of Title 19A.of the King County Code.
B. All persons having an ownership interest in the subject property shall sign on the face of the final short
subdivision.
C. All utilities within proposed rights-of-way must be included within a franchise
approved by the King County Council prior to final short plat recording.
2.Surface Water Management(KCC 9)
1998 King County Surtace Water Design Manual(SWDM)
FULL REVIEW
The proposed short plat qualifies for full drainage review as outlined in Chapter One of the Surface Water
Design Manual. Final short plat approval shall require full compliance with the drainage provisions set forth in
King County Code 9.04.A professional civil engineer,licensed in the State of Washington,shall prepare
drainage plans and a technical information report as outlined in Chapter 2 of the drainage manual.The
drainage plan submittal shall demonstrate compliance with all applicable Core and Special Requirements.
Compliance may resu t in reducing the number and/or location of lots as shown on the preliminary approved
short plat. Preliminary review has identified the following conditions of approval,which represent portions of
the drainage requirements.All other applicable requirements in KCC 9.04 and the Surface Water Design
Manual(SWDM)must also be satisfied during engineering and final review.
A. Drainage plans and analysis shall comply with the 1998 King County Surface Water Design Manual. Prior to
short plat recording,the applicant shall submit drainage and engineering plans to address the required short
plat improvements. King County approval of drainage and roadway plans is required prior to any construction.
Permit fees for review and inspection shall be paid as required by County codes and policies.Bonding for the
drainage plans will also be established as determined by DDES prior to ptan approval.After receiving
drainage plan approval,the applicant shall contact the DDES Land Use Inspection Section to schedule a pre-
construction meeting prior to pertorming work on the site.
B. Current standard plan notes and ESC notes,as established by DDES Engineering Review shatl be shown on
the engineering plans.
C. The following note shall be shown on the final recorded plat:
All building downspouts,footing drains,and drains from all impervious surfaces such as patios and driveways
shall be connected to the permanent storm drain outlet as shown on the approved construction drawings on
file with DDES and/or the Department of Transportation.This plan shall be submitted with the application of
any building permit.All connections of the drains must be constructed and approved prior to the final building
inspection approval. For those lots designated for perforated stub-outs,dispersion, or infiltration systems,the
designs shall be constructed at the time of the building permit and shall comply with the plans on file."
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SITE SPECIFIC CONDITIONS
As required by Special Requirement No.2 in the drainage manual,the 100-year floodplain limits determination
calculations shall be included in the Technical Drainage Report(TIR)and delineated/shown on the final
engineering plans and the recorded short plat for the existing onsite depression.
4.Road Standards(KCC 14)1993 King County Road Standards
All construction and upgrading of public and private roads shall be done in accordance with the King County
Road Standards established and adopted by Ordinance No. 11187,as amended(1993 KCRS).The proposed
short subdivision shall comply with the 1993 King County Road Standards(KCRS)including the following
requirements:
A. The proposed subdivision shall comply with the 1993 King County Road Standards(KCRS)including the
following requirements:
1. The proposed on-site access serving proposed lots 5,6&8 shall be placed in a Private Access Tract(PAT).
These lots shall have undivided ownership of the tract and be responsible for its maintenance.The PAT road
improvements shall conform to KCRS 2.03 for Urban Minor Access Road Standards and shall include 22 feet
of paving with concrete curb and gutter on both sides of the road.The minimum tract width shall be 26 feet
with a maximum length of 150 feet.
2. 114w Avenue Southeast fronting the subject property shall be improved to Urban Sub-Access Standards,per
the 1993 King County Road Standards,Section 2.03.
3. Southeast 162"d Street fronting the subject property shall be improved to Urban Sub-Access Standards,per
the 1993 King County Road Standards,Section 2.03.
4. Southeast 164'Street fronting the subject property shall improved to Urban Neighborhood Collector
Standards,per the 1993 King County Road Standards,Section 2.03.
5. Street trees shall be included in the design of all road improvements,and shall comply with Section 5.03 of
the KCRS.
5.Health(KCC 13)
This project is exempt from further King County Heath Department review. However, if improvements are
required from the Sewer and/or the Water District,then verification shall be required from said District(s)that
the improvements have been bonded and/or installed,prior to final recording of the short plat.
6.Building and Construction Standards(Title 16)
A. The applicant shall comply with all applicable provisions of KCC 16.82.T
B. The applicant shall demonstrate compliance with KCC 16.82.150(clearing standards)requirements at
engineering and final short plat.
7.Fire Code(KCC 17) Section 902 of the 1997 Edition of Uniform Fire Code
The applicant must obtain the approval of the King County Fire Protection Engineer for the adequacy of the
fire hydrant,water main and fire flow standards of Chapter 17.08 of the King County Code.
8.Zoning Code(KCC 21A)
A. Density and Dimensions(KCC 21A.12)
All lots shall meet the density and dimensions requirements of the R-8 zone classification or shall be as
shown on the face of the approved preliminary short subdivision,whichever is larger.Minor revisions to the
short subdivision,which do not result in substantiat changes and/or do not create additional lots may be
approved at the discretion of the Department of Development and Environmental Services.
B. Street Trees(KCC 21A.16)Street trees shall be provided as fol ows(per KCRS 5.03 and KCC 21A.16.050):
1. Trees shall be planted at a rate of one tree for every 40 feet of frontage along all roads. Spacing may be
modified to accommodate sight distance requirements for driveways and intersections.
2. Trees shall be located within the street right-of-way and planted in accordance with Drawing No.5-009 of the
1993 King County Road Standards, unless King County Department of Transportation determines that trees
should not be located in the street right-of-way.
3. If King County determines that the required street trees should not be located within the right-of-way,they
shall be located no more than 20 feet from the street right-of-way line.
4. The trees shall be owned and maintained by the abutting lot owners or the homeowners association or other
workable organization unless the County has adopted a maintenance program.Ownership and maintenance
shall be noted on the face of the final recorded plat.
5. The species of trees shall be approved by DDES if located within the right-of-way,and shall not include
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poplar,cottonwood,soft maples,gum,any fruit-bearing trees,or any other tree or shrub whose roots are likely
to obstruct sanitary or storm sewers,or that is not compatible with overhead utility lines.
6. The applicant shall submit a street tree plan and bond quantity sheet for review and approval by DDES prior
to engineering plan approval.
7. The street trees must be installed and inspected,or a performance bond posted prior to recording of the plat.
If a performance bond is posted,the street trees must be installed and inspected within one year of recording
of the plat.At the time of inspection,if the trees are found to be installed per the approved plan,a
maintenance bond must be submitted or the performance bond replaced with a maintenance bond,and held
for one year.After one year,the maintenance bond may be released after DDES has completed a second
inspection and determined that the trees have been kept healthy and thriving.
9.Sensitive Areas(KCC 21A.24)
The proposed subdivision shall comply with the Sensitive Areas Code as outlined in KCC 21A.24.Permanent
survey markings and signs as specified in KCC 21A.24.160 shall also be addressed prior to final plat
approval.Temporary marking of sensitive areas and their buffers(e.g.,with bright orange construction
fencing)shall be placed on the site and shall remain in place until all construction activities are completed.
Preliminary plat review has identified the following specific requirements which apply to this project.All other
applicable requirements from KCC 21A.24 shall also be addressed by the applicant.
A. Wetlands
1. Class 3 wetland(s)shall have a minimum buffer of 25 feet,measured from the wetland edge.
2. The wetland(s)and their respective buffers shall be placed in a Sensitive Area Tract(SAT).
3. Buffer Averaging,as shown on the approved plan set,meets provisions of the King County Sensitive Area
Code 21A.24320(b).
4. A minimum building setback line of 15 feet shall be required from the edge of the tract.
B. Streams
1. Class 3 stream(s)shall have a 25-foot buffer.
2. The stream(s)and their respective buffers shall be placed in a Sensitive Area Tract(SAT).
3. A minimum building setback line of 15 feet shall be required from the edge of the tract.
C. Alterations to Streams or Wetlands
1. Alterations of streams and/or wetlands are approved in conformance with KCC 21A.24.As an alternative to
mitigation plantings,the applicant has provided buffer averaging in excess of 2:1.
2. The Sensitive Area Tract that includes the Class 3 wetlands and associated Class 3 stream shall be fenced
with split rails(spit rail fence)and posted with Sensitive Area signs.
D. SDO Conditions(KCC 21A.38)-The following Special District Over ays apply to this site:
1. Significant trees-Calls for the retention of a certain percentage of the trees on the site.
2. Seasonal clearing restrictions-Clearing is limited to April 1 SGthrough September 30"'.
10. Road Mitigation Payment System
The applicant or subsequent owner shall comply with Road Mitigation Payment System(MPS),King County
Code 14.75,by paying the required MPS fee and administration fee as determined by King County
Department of Transportation.The applicant has an option to either:
A. Pay the MPS fee at final short ptat recording,or
B. Pay the MPS fee at the time of building permit issuance.
If the first option is chosen,the fee paid shall be the fee in effect at the time of short plat application and a
note shall be placed on the face of the short plat that reads,"All fees required by King County code 14.75
have been paid."
If the second option is chosen,the fee paid shall be the amount in effect as of the date of the building permit
application.
11. Lots within this subdivision are subject to King County Code 21A.43,which imposes impact fees to fund
school system improvements needed to serve new development.As a condition of final approval,fifty percent
50%)of the impact fees due for the plat shall be assessed and collected immediately prior to recording, using
the fee schedules in effect when the plat receives final approval.The balance of the assessed fee shall be
allocated evenly to the dwelling units in the plat and shall be collected prior to building permit issuance.
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12. Suitable recreation space shall be provided consistent with the requirements of K.C.C.21A.14.180 and K.C.C.
21A. 14.190(i.e.,sport court[s],children's play equipment,picnic table[s],benches,etc.).
a.A detailed recreation space plan(i.e.,location,area calculations,dimensions,landscape specs,equipment
specs,etc.)shall be submitted for review and approval by DDES and King County Parks prior to or concurrent
with the submittal of engineering plans.
b.A performance bond for recreation space improvements shall be posted prior to recording of the plat.
Other Considerations
tr,
A. Preliminary approval of this application does not limit the applicant's responsibility to obtain any required
permit or license from the State or other regulatory body.This may include,but not be limited to,obtaining a
forest practice permit,an HPA permit,building permits,and other types of entitlements as necessitated by
circumstances.
B. The short subdivision shall conform to KCC 16.82 relating to grading on private property.
C. Development of the subject property may require registration with the Washington State Department of
Licensing, Real Estate Division
The following summary describes how this new project will meet the eight "Core Requirements"
and the "Special Requirements" that apply:
Core Repuirements
1. Discharge at the Natural Location: The site currently contains three distinct threshold
drainage areas and a wetland. The site "developed" system will maintain these
drainage areas and discharge runoff at its historic locations.
2. Off-Site Analysis:A Level 1 offsite analysis was conducted for this plat as described in
Section 3.
3. Flow Control: The Level 2 detention pond was sized for onsite drainage and a Level 2
detention tank was sized for roadway drainage along
114th Avenue SE to meet the
requirements of the KCSWDM, using the KCRTS routine. Appendix C contains the
KCRTS input and output.
4. Conveyance System: The conveyance system was sized to convey the 25-year storm
without flooding and in fact, the predicted 100-year storm flows can be conveyed without
flooding as shown on the output data from the KCBWP analysis in Appendix C.
5. Erosion and Sedimentation Contro/: Runoff from the grading and trer ching
construction areas will be contained by a temporary construction entrance, silt fencing
and a sediment trap in accordance with the KCSWDM during construction. The ESC
facilities will only be removed once all exposed site surFaces have been stabilized.
Other temporary erosion and sedimentation control measures will be installed as
needed.
6. Maintenance and Operations: The detention pond and all drainage and street work
within public tracts, rights-of-ways and easements will become the property of King
County.
7. Financial Guarantees and Liability:The bond quantities worksheet is in Appendix G. I
8. Water Quality: Treatment of runoff will not be required because none of the threshold
drainage areas will have more than 5,000 square feet of new and replaced Pollution
Generating Impervious Surfaces (PGIS).
Special Requirements
1. Other Adopted Area-Specific Requirements: Level 2 Flow Control will be required.
The north basin area contains a closed depression, which does not receive any runoff
from off-site. The project does not propose any changes to the runoff in this basin.
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2. Floodplain/Floodway Delineation: An engineering plan, in lieu of a minor floodplain
study is required to document that the proposed development will be at least 10 feet
above the ordinary high water mark, or 2 feet above the downstream overflow elevation.
See Appendix E.
3. Flood Protection Facilities: Not Applicable.
4. Source Controls: Not Applicable.
5. Oil Control: Not Applicable.
SECTION 3
OFF-SITE ANALYSIS
The following subsections describe the inspection and evaluation of the site and its surrounding
areas particularly the downstream drainage paths.
Task 1. Study Area Definition and Maps
The Figures in Appendix B show the extent of the study area and the local topography. There
is no runoff onto the site because the roadside drainage system transports runoff from the north
and east of the property around the property to the west. The Site Plan drawing shows more
detailed topographic information on the project site.
Task 2. Resource Review
King County mapping was consulted and King County's Drainage basin mapping shows the site
draining in three different directions to three different drainage basins: to the Black River to the
north and west, to the Lower Cedar River to the east, and to Soos Creek to the south.
However, as described below, physical inspection of the site shows this mapping to be
inaccurate. In fact, the entire site ultimately drains to the Black River, but in three distinct
drainage paths creating three different threshold drainage areas.
Task 3. Field Inspection
A Level 1 off-site analysis was conducted on January 27, 2004, with several subsequent site
visits to verify the initial findings. At the time of the initial site inspection, the weather was cool
and sunny.
Task 4. Drainage System Descriptions and Problem Descriptions
The figures in Appendix B show the three downstream drainage paths for the four drainage
basins on the site. Any overflow from the wetland area on the south side of the site drains into
the South Downstream Drainage Path described below, which also conveys runoff from the
east portions of the site. All these drainage paths converge at a point more than %4 miles from
the site as described below.
1) North Downstream Drainaqe Path: The runoff from the north portion of the site flows into
the closed depression on the site, which does not show any signs of overtopping. It
appears that all runoff into this depression currently infiltrates because the depression
typically does not contain standing water and does not support any wetland indicators. The
adjacent roadway ditch prevents runoff from the road and upstream areas from entering this
depression.
However, the downstream drainage path described herein is for the overflow from the
closed depression should it overtop: From the closed depression, the north portion of the
site would drain west in a roadside ditch and culvert system along the south side of SE
162"d Street, flowing west to the end of the roadside ditch. From there, it flows overland
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across a semi-vacant storage yard to a sharp grade break and down to the bottom of a
large natural ravine draining to the northwest.
2) South Downstream DrainaQe Path: The eastern and southern (wetland) portions of the
property, as well as the 114`"Avenue SE and SE 164' Street drainage from the roads and a
small upstream tributary area to the east, drain west in a roadside ditch and drivewa
culvert system along the north side of SE 164th Street to the bottom of the hill near 109
Avenue SE. This roadside system discharges into the same large natural ravine draining to
the northwest.
3) West Downstream Draina4e Path: The remainder of the property drains directly west
through private property, initially in a drainage ditch and stream and then in a long piped
system which discharges into the same large natural ravine between the discharge points
for the northwest and southwest drainage paths.
Task 5. Mitigation of Existing or Potential Problems
To mitigate any water quantity impacts from the project, Level 2 detention in accordance with
the King County Surface Water Design Manual (KCSWDM) will be required as part of the
development.
Treatment of runoff will not be required because none of the threshold drainage areas will have
more than 5,000 square feet of new and replaced Pollution Generating Impervious SurFaces
PGIS).
SECTION 4
FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND DESIGN
The following subsections describe the measurements and criteria used to size the detention
facilities
Existing Site Hydrology (Part A)
The drainage on the existing site was analyzed for this project with KCRTS. Figures provided
in the KCSWDM and KCRTS manual were used to determine project location and scale factor
parameters. The figures in Appendix C show the delineation of the areas generating runoff on
the site. The site soils are classified Alderwood Gravelly Sandy Loam, 6% - 15% slopes.
Appendix C also contains the data and output from the hydrologic analysis.
The following table lists the existina site conditions identified for this project and used in the
KCRTS modeling included. The NW basin will not be changed.
N Basin E Basin W Basin S Basin
Area (ac) Area (ac) Area (ac) Area (ac)
Description (Site) (Street) (Site) (Street) (Street) (Site) (Street)
Forest 0.38 0.18 0.09
Impervious 0.03 0.06 0.03 0.26 0.05
Pasture 0.05 0.10 0.25 0.57 0.47 0.03
Grass
Wetland 0.01 0.01 0.12 0.01
Total Area 0.41 0.11 0.32 0.51 0.72 0.59 0.04
Note:Some areas include some round-off error.
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Developed Site Hydrology (Part B)
The runoff from the four different drainage basins on site will be discharged as follows:
North Basin. The total allowable development in the North Basin will not increase the
impervious surface area by more than 5,000 square feet. Runoff from this basin will continue to
be discharged to the surface on-site or to the downstream ditch and culvert system via a
perforated downspout connection per existing conditions.
East Basin. The proposed drainage systems will route East Basin runoff to a Level 2 detention
tank that will release runoff to the ditch along SE 164'h Street, as shown on the plans and
described in the "Offsite Analysis" section of this report.
West Basin. The proposed drainage systems will route West Basin runoff to a Level 2
detention pond that will release runoff to the stream at the west property boundary.
South Basin. Clean runoff from discreet roof areas will be directed to the wetland area also
known as the South Basin. This situation has been determined to mimic existing conditions in
the South Basin.
This configuration very closely mimics existing conditions and discharges all runoff in the
directions and locations where runoff from these basins currently flows.
The developed site conditions identified for this project and used in the KCRTS modeling
included:
N Basin E Basin W Basin S Basin
Area (ac) Area (ac) Area (ac) Area (ac)
Description (Site) (Street) (Site) (Street) (Street) (Site) (Street)
Forest
Impervious 0.11 0.07 0.06 0.37 0.41 0.16
Pasture 0.25
Grass 0.28 0.04 0.15 0.15 0.52 0.02
Wetland 0.12 0.00
Total Area 0.39 0.11 0.21 0.52 0.91 0.54 0.02
Note:Some areas include some round-off error
Performance Standards (Part C)
The potential increase in impervious surface area for the North Basin is less than 5,000 square
feet; therefore, detention is not required for this basin per the Impervious Surface Exemption to
Core Requirement #3. No significant development is proposed for this basin at this time. For
the East Basin detention tank and West Basin detention pond, Level 2 Flow Control
requirements and parameters were used to size the facilities. The South Basin required careful
consideration of tributary areas to match existing conditions and not deprive the wetland of
water nor inundate it with too much flow.
Water quality treatment is not anticipated; however, the project site is in an area designated for
Basic Water Quality Treatment.
Conveyance features were sized to convey the 25-year developed runoff and their performance
during the 100-year event checked to be sure that significant flooding will not occur as a result.
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Flow Control System (Part D)
North Basin. No flow control is required for the North Basin per the "Impervious Surface
Exemption".
East Basin. The East Basin detention tank was sized using the KCRTS routine. The following
table summarizes the sizing and control requirements for the detention tank.
Detention Facility East Basin Tank
Required detention volume 1,143 cf
Effective storage depth 3.5 ft
Tank Diameter 4 sf
Tank Length 98 ft
Orifice#1 diamete 0.88" (7/8")
Orifice#2 diameter 1.13" (1-1/8")
Orifice#2 heiqht above bottom 1.80 ft
West Basin. The West Basin detention pond was sized using the KCRTS routine. The
following table summarizes the sizing and control requirements for the detention pond.
Detention Facility I West Basin Pond
Required detention volume 7,605 cf
Effective storage depth 3.0 ft
Top area (@ 1' freeboard) 4,164 sf
Bottom Area 1,821 sf
Orifice#1 diameter 0.71" (11/16")
Orifice#2 diameter 0.68" (11/16")
Orifice#2 heiqht above bottom 2.0 ft
South Basin. Minimal development is proposed for the South Basin; however, it contains an
existing wetland which must be protected. Of particular concern is maintaining adequate flow to
the 0.13-acre wetland once the required frontage improvements along 114'Avenue SE and SE
164' Street are completed. The existing onsite and adjacent frontage areas tributary to the
wetland total only about 0.51 acres. This is probably not enough area to support the wetland so i
the existence of the wetland strongly suggests that there is a hydraulic connection with the
adjacent ditch.
Assuming there is a hydraulic connection, the exact volume of runoff currently supplying the
wetland would be impractical to accurately determine. The upstream area tributary to the
adjacent ditch is at least three times the wetland tributary on-site area; however, since the
connection is subsurface, only a small portion of this upstream runoff may impact the wetland.
The design solution is to disperse clean runoff to the wetland from discreet non-tra c areas.
The areas were selected so the peak flows and volumes exceed the flows from existing on-site
tributary areas (which can be easily analyzed) by about 80 percent to approximately match the
existing runoff regime, but more importantly to provide adequate water for the proposed
wetland buffer mitigation. The proposed flow rates and volumes have been coordinated with
the Wetland Mitigation Plan.
Descriptions of the procedures used and calculations and computer output are included in
Appendix C.
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Water Quality (Part E)
Treatment of runoff will not be required because none of the threshold drainage areas wiil have
more than 5,000 square feet of new and replaced Pollution Generating Impervious Surfaces
PGIS). The following is a table summarizing the PGIS Surfaces proposed for each basin area.
PGIS Areas by Basin
North East West South
Lot 1) Lot 2)Lots 3, 5, 6, 8) (Lots 4, 7)
Driveways 400 sf 400 sf 1,600 sf 800 sf
Road Tracts 545 sf 2,859 sf
Frontage Improvements 584 sf 3,928 sf
Total 984 sf 4,873 sf 4,459 sf 800 sf
SECTION 5
CONVEYANCE SYSTEM ANALYSIS AND DESIGN
The conveyance piping was analyzed using the County's Backwater Analysis routine (BWPIPE)
and runoff generated by KCRTS using 15-minute time steps to be sure the 25-year flows can
be conveyed, and that significant flooding will not occur during a 100-year event. The results of
this analysis are included in Appendix C.
SECTION 6
SPECIAL REPORTS AND STUDIES
In lieu of a Minor Floodplain Study, an engineering plan is submitted showing that the proposed
building sites are located more than 2 feet above the downstream overflow elevation. This
Engineering Plan is included in Appendix E.
A Sensitive Areas Study was completed for the project site by Wetland Resources, Inc. This
report is included in Appendix F.
SECTION 7
OTHER PERMITS
No other permits beyond those required by King County are anticipated to be required for this
project.
SECTION 8
ESC ANALYSIS AND DESIGN
The erosion control facilities are shown on the erosion control plan. The proposed detention
pond will be used for a temporary sediment trap. At 960 square feet, the bottom area of the
pond exceeds the top area required for the sediment trap, which is 685 square feet. The
calculations (2,080 x QZ) used to size the erosion control facilities are included in Appendix C.
SECTION 9
BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT
Bond Quantities: The County's Bond Quantities Worksheet is included in Appendix G for the
site and frontage improvements.
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Facilitv Summaries: The County's Facilities Summary Sheet is included in Appendix E.
Declaration of Covenant: The County's Declaration of Covenant document will be provided
separately.
SECTION 10
OPERATIONS AND MAINTENANCE MANUAL
The drainage facilities should be maintained as described in Appendix D (part of which was
excerpted from the KCSWM Maintenance Requirements for Privately Maintained Drainage
Facilities). The detention pond and all drainage and street work within public tracts, rights-of-
ways and easements will become the property of King County.
1 o TEC
APPENDIX A
FIGURES
1. Technical Information Report(TIR)Worksheet
2. Site Location Map
3. Drainage Basins, Subbasins, 8 Site Characteristics
4. SCS Soils Map
King County Department of Development and Environinental Services
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
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t:::::::`:`::::;::::::::::::::::::::::::::::;::::::::::::::`:::::;::::::::::::::::::::::::::::::::;::::;:::>:;:::::::>::::;:'
Project Owner Project Name ,/
r,
Address 0 Q Qf 1"'i f1 Location
o, /Pf./a/9 -jr.GZ Township 3
Phone Range S30 -NS2 - 3b(o
Project En ineer Section 9 ll
rnc: T-
Company /n c.
Address/Phone_ t.A 35 y S
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Subdivison DFW HPA Shoreline Management
Short Subdivision COE 404 Rockery
Grading DOE Dam Safety Structural Vaults
Commercial FEMA Floodplain Other
Other COE Wetlands
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Community
aoS C Ye l
Drainage Basin ,
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River Flood lain
Wetland
Stream Seeps Springs
Critical Stream Reach High Groundwater Table
Depressions/Swales
Groundwater Recharge
Lake
Other
Steep Slopes
Figure 1
TIR Worksheet
3 pages)
a
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Soil Type Slopes Erosion Poter tial Erosive Velcoties
ln- /S l
Additional Sheets Attached
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REFERENCE LIMITATIOWSITE CONSTRAINT
Ch. 4—Downstream Analvsis
Additional Sheets Attached
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5:::i:'
MINIMUM ESC REQUIREMENTS MINIMUM ESC REC UIREMENTS
DURING CONSTRUCTION AFTER CONSTRUCTION
Sedimentation Facilities Stabilize Exposed Surtace
Stabilized Construction Entrance Remove and Restore Temporary ESC Facilities
Perimeter Runoff Control Clean and Remove All Silt and Debris
Clearing and Graing Restrictions Ensure Operation of Permanent Facilities
Cover Practices iFlag Limits of SAO and open space
Construction Sequence preservation areas
Other Other
Part 1(3 :SUR ACE WATER SYSTEM
Grass Lined Tank Infiltration
Method of Analysis
Channel l%j PiK/z
Vauit Depression
J Pipe System Compensation/Mitigati
Energy Dissapator Flow Dispersal on of Eliminated Site
Open Channel Stora eWetlandWaiver9
Dry Pond Stream Regional
Wet Pond Detention
I
Brief Description of System Operation r Cl Zu Y Qf CLvt
j iTc ov T,h,n oc 1LS1 a./Y i br J'Lt ri -
Facility Related Site Limitations
Reference Facility Limitation
Part 11 STRlJCTURA.ANALYStS Part'f2 EASE1VlE1VTS/'('RAGTS
Cast in Place Vault Drainage Easement
Retaining Wall Access Easement
Rockery> 4' High Native Growth Protection Easement
Structural on Steep Slope Tract
Other Other
Part 13 SiGNATURE OF PROFESSIONAL ENGINEER
I or a civil engineer under my supervision my supervision have visited the site. Actual site
conditions as observed were incorporated into this worksheet and the attachments. To the best of
my knowledge the information provided here is accurate.
i i` 4/Z Y/..5`
Signed/Date
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The information included on this map has been compiled by King County staff from a variety of sources and is subject to change without notice.
King County makes no representations or warranties,express or implied,as to accuracy,completeness,timeliness,or rights to the use of such
information.Ki g County shall not be liable for any general,special,indirect,incidental,or consequential damages including,but not limited to,
lost revenues or lost profits resulting from the use or misuse of the information contained on this map.Any sale ofthis map or information on
ihis map is prohibited except by written permission of King County.
Kina Countv GIS Center News Services Comments Search
By visiting this and other King County web pages,you expressly agree to be bound by terms and conditions of the site.The details.
Figure 2
Site Location Map
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The information included on this map has been compiled by King County staff from a variety of sources and
is subject to change without notice. King County makes no representations or warranties, express or
implied,as to accuracy, completeness,timeliness, or rights to the use of such information. King County shall
ot be liable for any general, special, indirect, incidental, or consequential damages including, but not limited
to, lost revenues or lost profits resuRing from the use or misuse of the information contained on this map.
Any sale of this map or information on this map is prohibited except by written permission of Kinq County.
Kin,g County_I GIS Center 1 News I Se vices I Comments I Search
By visiting this and other King County web pages, you expressly agree to be bound by terms and conditions
of the site. The details.
Figure 3
Drainage Basins, Subbasins,
Site Characteristics
Scale as shown
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APPENDIX B
OFF-SITE ANALYSIS
DRAINAGE SYSTEM TABLE AND MAP
OFF-
SITE
ANALYSIS
DRAINAGE
SYSTEM
TABLE
SURFACE
WATER
DESIGN
MANUAL,
CORE
REQUIREMENT #
Z
Basin:
Black
River
Subbasin
Name:
Subbasin
Number:
Symbol
Drainage
Drainage
Slope
Distance
Existing
Potential
Observa
ions
of
field,:
Component
Type,
Component
from
site
Problems
Problems
inspe
tor,
resour'
Name,
and
Size
Description
discharge.
reviewe'
r,
oir
resident`- ` '
see
map
Type:
sheet
flow,
swale,
drainage
basin,
vegetation, , %
ml=
1,
324:
ft.
constrictions,
under
eapacity;
ponding,
t
ibutarj+
aiea;:
GkeUfio.
qd,
f
piobiem;
stream,
channel,
pipe,
cover,
depth,
type
of
sensitive
overtopping,
flbvding,
habitat
oi
organism
overflow
pathwa}
rs,
potentia[
unp8c:
ts '
pond;
Si2e:
diameter,
area,
volume
destruction,
sCouring;
banks{
oughing,
surface
area
sedimentation,.
incisiort,
other.:
erosion
North
Downstream
Drainage
Path
A-
B
Ditch
w/
8"—
12"
Dirt
and
grass
lined
2
0' —
900'
None
noted
Ditch
capacity
is
Ditch
appears
to
end
at
B
and
driveway
culverts
ditch
sections,
1 —
2
feet
small,
potential
overtop
to
sheet
flow
across
cover
for
flooding
vacant
storage
yard
B-
C
Sheet
flow
Dirt
and
grass
storage
2
900' —
1,
270'
None
noted
Erosion
and
yard
and
flooding
C-
D
Sheet
flow
Overland
flow
down
to
8
1,
270' —
Inaccessible
on
private
bottom
of
ravine
1,
540'
property
South
Downstream
Draina
e
Path
E-
F
12"
cone.
d/
w
culvert
Grass
lined
ditch,
depth
4
0' —
1,
270'
None
noted
erosion
and
ditch
system
varies.
N
side
of
SE
164th
F-
G
12"
conc,
pipe
discharges
to
bottom
of
5
1,
270' —
drainage
ravine
1,
380'
G-
D
Large
wetland/
Headwaters
of
drainage
2
1,
380' —
Inaccessible
on
private
drainage
area
path
to
NW
1,
700'
property
West
Downstream
Draina
e
Path
H-
I
Drainage
swale,
2' —
Brushy
and
wooded
2
0' —
800'
I
None
noted
flooding
Area
has
been
used
by
adjacent
8'
wide
property
owners
to
dump
yard
waste
and
other
debris
I-
J
12"—
18"—
10"
pipe
Crosses
under
private
5
800' —
1,
330'
Inaccessible
on
private
property
property
J-
K
Drainage
swale
Down
slope
to
bottom
of
5
1,
330' —
Inaccessible
on
private
drainage
ravine
i
1,
750'
property
K-
D
Large
wetland/
Headwaters
of
drainage
2
1,
750' —
Inaccessible
on
private
I
drainage
area
path
to
NW
i
1
880'
property
98-
4\
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The information included on this map has been compiled by King County staff from a variety of sources and is subject to change without notice.
King County makes no representations orwarranties,express or implied,as to accuracy,completeness,timeliness,or rights to ihe use of such
information.King County shall not be liable for any general,special,indirect,incidental,or consequential damages including,but not limited to,
lost revenues or lost profits resulting from the use or misuse of the information contained on this map.Any sale of this map or information on
ihis map is prohibited except by written permission of King County.
Kino Countv GIS Center News Services Comments Search
By visiting this and other King County web pages,you expressly agree to be bound by terms and conditions of the site.The detaiis.
Off-site Analysis Drainage
System Map
Downstream Drainage Paths
Scale as shown
httn//www5 metrnkc.v/ervlet/c m.esri.esriman.Esriman?ServiceName=overview&Clie... 8/24/2005
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King County makes no representations or warranties,express or implied,as to accuracy,completeness,timeliness,or rights to the use of such
information.King County shall not be liable for any general,special,indirect,incidental,or consequential damages including,but not limited to,
ost revenues or lost profits resulting from the use or misuse of the information contained on this map.Any sale of this map or information on
ihis map is prohibited except by written permission of Kinq County.
Kina Countv GIS Center(News Services Comments Search
By visiting this and other King County web pages,you expressly agree to be bound by terms and conditions of the site.The details.
Off-site Analysis Drainage
System Map
Upstream Tributary Basins
Scale as shown
httn•//www5 mPtr kr unv/cPrvlet/nm ecri esriman.Rsriman?ServiceName=verview&C'lie... R/24/2 5
4
1
APPENDIX C
ANALYSIS AND DESIGN
D
0
a
o
OC
1Da[
l
i
K,.,.
T
II
S.&
a . . . .. ,`.. , .
Npl'
J741'
E `—
g
515
pi
BEARINCj
1,
N1GlE
0
l
v
ses]
l` . , ... . . . . .
65ti.
J3(
Hj
r-
r, . .. . .
056..
1J'(
P)
t ' ' . . . ..
1 ,
ir
1
11
i
i
Y. .
u
i .
i..¢ • ' • •
NCt]
7'
79'
EAST
t '
K
N, -.• ,
oa„«, — — -`"—_—
a
e.
or
P
i
5% ,:
vi.'..^^
Y '
r... .-
m
R
8 ..
s ,
SAU11
i
D' {
k ,
o
x± ; .. . .
1 ;
R `
wEST
y
n. :
s
h
I
NORTFi ,
r
gl `
N
i']]'!
T
J
n
95
OG'(
1
T
U-D'':.. .,. / ' +. ,
S91
9!'(
P
s
e
3i
s
0.
ST
7
St
Ew --}-
p+
uru4t
ri'K[
1
NORTH
BASIN (
AC)
EAST
BASIN (
AC)
SITE
STREET
TOTAL
SITE
STREET
TOTAL
FOREST:
16,
716 (
0.
38)
16,
716 (
0.
38)
8,
007 (
0.
18)
8,
007 (
0.
18)
IMPERV+
iOUS:
1,
224 (
0.
03)
2,
519 (
0.
06)
3,
743 (
0.
09)
1,
292 (
0.
03)
11,
252 (
0.
26)
12,
544 (
0.
29)
a
4o
eo
PASTURE:
2,
429 (
0.
06)
2,
429 (
0,
06)
4,
394 (
0.
10)
10,
917 (
0.
25)
15,
311 (
0.
35)
WETLAhD:
431 (
0.
01)
431 (
0.
01)
Z
TOTAL:
18,
050 (
0.
41)
4,
948 (
0.
11)
22,
998 (
0.
53)
14,
124 (
0.
32)
22,
69 (
0.
51)
36,
293 (
0,
83)
SCALE; " =
8o
ft.
WEST
BASIN (
AC)
SOUTH
BASIN (
AC)
TOTALS (
AC)
SITE
SITE
STREET
TOTAL
SITE
STREET
T07AL
FORES
i;
4,
194 (
0.
10)
28,
917 (
0.
66)
28,
917 (
0.
66)
IMPERV
IOUS:
2,
036 (
0.
05)
4,
552 (
0.
10)
13,
771 (
0.
32)
18,
323 (
0.
42)
PASTURE:
24,
682 (
0.
57)
20,
543 (
0.
47)
1,
464 (
0.
03)
22,
007 (
0.
51)
49,
619 (
1.
14)
14,
810 (
0.
34)
64,
429 (
1.
48) •
WETLA
dD:
289 (
p.
p
5,
365 (
0.
12)
104 (
6.
00)
5,
469 (
0.
13)
6,
085 (
0.
14)
104 (
0.
00)
6,
189 (
0.
14)
TOTAL:
31,
201 {
0.
72)
25,
908 (
a.
59)
1,
568 (
0.
04)
27,
476 (
0.
63)
gg,
t73 (
2.
05)
28,
685 (
0.
66)
117,
858 (
2.
71)
SOME
AREAS
SHOW "
ROUND—
OFF"
ERROR
Lot
Coverage
Areas
Project:
Lund
Plat
Date:
1/
10/
2006 Existing
North
Basir
East
Basin
West
Basin
South
Basir
Totals
Site
Frontage
Total
Site
Frontage
Total
Site
Site
Fronta
e
Total
Site
Frontage
Total
s
ac
s
ac
s
ac
s
ac (
s (
ac)
s
ac
s
ac
s
ac
s
ac (
s (
ac)
s
ac (
s
I(
ac) (
s
1(
ac)
Forest
16,
716
0.
38
16,
716
0.
38
8,
007
0.
18
8,
007
0.
18
4,
194
0.
10
28,
917
0.
66
28,
917
0.
66
Impervious
1,
224
0.
03
2,
519
0.
06
3,
743
0.
09
1,
292
0.
03
11,
252
0.
26
12,
544
0.
29
2,
036
0.
05
4,
552
0.
10
13,
771
0.
32
18,
323
0.
42
Pasture
2,
429
0.
06
2,
429
0.
06
4,
394
0.
10
10,
917
0.
25
15,
311
0.
35
24,
682
0.
57
20,
543
0.
47
1,
464
0.
03
22,
007
0.
51
49,
619
1.
14
14,
810
0.
34
64,
429
1.
48
Grass Wetland
431
0.
01
431
0.
01
289
0.
01
5,
365
0.
12
104
0.
00
5,
469
0.
13
6,
085
0.
14
104
0.
00
6,
189
0.
14
Total
18,
050
0.
41
4,
948
0.
11
22,
998
0.
53
14,
124
0.
32
22,
169
0.
51
36,
293
0.
83
31,
201
0.
72
25,
908
0.
59
1,
568
0.
04
27,
476
0.
63
89,
173
2.
05
28,
685
0.
66
117,
858
2.
71
Proposed
North
Basir
East
Basin
West
Basin
South
Basir
Totals
Site
Frontage
Total
Site
Frontage
Total
Site
Site
Frontage
Total
Site
Fronta
e
Total
s (
ac)
s
ac (
s (
ac) (
s (
ac) (
s (
ac) (
s (
ac) (
s (
ac) (
s (
ac)
s
ac (
s (
ac) (
s (
ac)
s
ac (
s (
ac)
Forest Impervious
4,
804
0.
11
3,
037
0.
07
7,
841
0.
18
2,
560
0.
06
16,
212
0.
37
18,
772
0.
43
17,
726
0.
41
7,
049
0.
16
7,
049
0.
16
32,
139
0.
74
19,
249
0.
44
51,
388
1.
18
Pasture
11,
027
0.
25
11,
027
0.
25
11,
027
0.
25
11,
027
0.
25
Grass
12,
021
028
1,
911
0.
04
13,
932
0.
32
6,
751
0.
15
6,
467
0.
15
13,
218
0.
30
21,
977
0.
50
954
0.
02
954
0.
02
40,
749
0.
94
9,
332
0.
21
50,
081
1.
15
Wetland
5,
365
0.
12
104
0.
00
5,
469
0.
13
5,
365
0.
12
104
0.
00
5,
469
0.
13
Total
16,
825
0.
39
4,
948
0.
11
21,
773
0.
50
9,
311
0.
21
22,
679
0.
52
31,
990
0.
73
39,
703
0.
91
23,
441
0.
54
1,
058
0.
02
24,
499
0.
56
89,
280
2.
05
28,
685
0.
66
117,
965
2.
71
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281-
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reports\
Drainage
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xls
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10/
2006
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STR
T
SF' (
AC:
TQTAL
SF
f
AC:
SCALE:
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rt.
FOREST:
q.,
8p4 (
0.
11)
3,
437 (
0.
0T)
7,
841 (
0.
1$)
IMPERVl4US:PASTURE:
2,
021 (
0.
28)
1,
911 (
0.
04)
13,
932 {
4,
32)
GR
ASS;
Z
TOTAI:
16
825 {
0.
39}
4,
948 {
0.
11)
21
773 {
0.
50)
S4ME
AREAS
5HOW "
ROUND-
OFF"
ERROR
ROOF
AND
D1W'
S:
75
OF
OT
AREA
OR
4,
004
SF -
WHICHEVER
IS
LESS)
pGiS
AREA =
9S4
SF <
5,
044
SF
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DRIVEWAY)
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po
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ai,
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1 PROPOSED:
BY—
PASS:
o
o
so
i
SITE
SF (
AC);
SIREET
SF
AC :
TOTAL
SF (
ACI:
STREET
SF (
AC);
FOREST:IMPERVIOUS:
2,
560 (
0.
06)
11,
571 (
0.
27)
14,
131 (
0.
33)
4,
641 (
0.
10)
SCALE:
i" =
eo
ft.
PASTURE:GRASS:
6,
751 (
0.
15)
6,
130 (
0.
14)
12,
881 (
0.
29)
337 (
0.
01)
WETLAND:TOTAL:
9,
311 (
0.
21)
17,
701 (
0.
41)
27,
012 (
0,
62)
4,
978 (
0.
11)
Z
SOME
AREAS
SHOW
ROUND—
OFF'
ERROR
PGIS
AREA =
4,
873
SF <
5,
000
SF
ROAD
WIDENING &
DRIVEWAYS)
KCRTS Command
CREATE a new Time Series
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : exist.tsf J f, ()
Regional Scale Factor : 1.00 r
Data Type : Reduced
Creating Hourly Time Series File
Loading Time Series File:C:\KC SWDM\KC DATA\STTF60R.rnf .
Till Forest 0.18 acres
Loading Time Series File:C:\KC SWDM\KC DATA\STTP60R.rnf .
Till Pasture 0.35 acres
Loading Time Series File:C:\KC SWDM\KC DATA\STWL60R.rnf .
Wetland 0.01 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STE160R.rnf .
Impervious 0.29 acres
Total Area : 0.83 acres
Peak Discharge: 0.193 CFS at 6:00 on Jan 9 in Year 8
Storing Time Series File:exist.tsf .
Time Series Computed
KCRTS Command
Enter the Analysis TOOLS Module
Analysis Tools Command
Compute PEAKS and Flow Frequencies
Loading Stage/Discharge curve:exist.tsf .
Flow Frequency Analysis
Time Series File:exist.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:exist.pks .
Analysis Tools Command
RETURN to Previous Menu
KCRTS Command
CREATE a new Time Series
Production of Runoff Time Series
Project Location : Sea-Tac
A'=_Computing Series : dev.tsf rwr
Regional Scale Factor : 1.00
Data Type : Reduced
Creating Hourly Time Series File
Loading Time Series File:C:\KC SWDM\KC DATA\STTG60R.rnf .
Till Grass 0.29 acres
Loadinq Time Series File:C:\KC SWDM\KC DATA\STE160R.rnf .
Impervious 0.33 acres
Total Area : 0.62 acres
Peak Discharge: 0.217 CFS at 6:00 on Jan 9 in Year 6
Storing Time Series File:dev.tsf .
Time Series Computed
KCRTS Command
Enter the Analysis TOOLS Module
Analysis Tools Command
Compute PEAKS and Flow Frequencies
Loading Stage/Discharge curve:dev.tsf .
Flow Frequency Analysis
Time Series File:dev.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:dev.pks .
Analysis Tools Command
RETURN to Previous Menu
KCRTS Command
CREATE a new Time Series
Production of Runoff Time Seri
Project Location : Sea-Tac
Computing Series : bypass.tsf C Gf (y
Regional Scale Factor : 1.00
Data Type : Reduced
Creating Hourly Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTG60R.rnf .
Till Grass 0.01 acres
Loading Time Series File:C:\KC SWDM\KC DATA\STEI60R.rnf .
Impervious 0.10 acres
Total Area : 0 11 acres
Peak Discharge: 0.049 CFS at 6:00 on Jan 9 in Year 8
Storing Time Series File:bypass.tsf .
Time 5eries Computed
KCRTS Command
Enter the Analysis TOOLS Module
Analysis Tools Command
Compute PEAKS and Flow Frequencies
Loading Stage/Discharge curve:bypass.tsf .
Flow Frequency Analysis
Time Series File:bypass.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:bypass.pks .
Analysis Tools Command
RETURN to Previous Menu
KCRTS Command
eXit KCRTS Program
sum.txt
Lund Plat - East easin (114th Ave.)
Runoff Calculations
12/30/05
Flow Frequency Analysis
Time series File:exist.tsf
Project ocation:sea-Tac
Annual veak Flow Rates--- -----Flow Frequency nnalysis-------
Flow Rate Rank rime of veak reaks - - Rank Return vrob
CFS) CCFS)Period
0.098 5 2/09/O1 2:00 0.193 1 100.00 0.990
0.074 7 1/05/02 16:00 0.114 2 25.00 0.960
0.114 2 2/27/03 7:00 0.106 3 10.00 0.900
0.074 8 8/26/04 2:00 0.104 4 5.00 0.800
0.089 6 10/28/04 16:00 0.098 5 3.00 0.667
0.104 4 1/18/06 16:00 0.089 6 2.00 0.500
0.106 3 10/26/06 0:00 0.074 7 1.30 0.231
0.193 1 1/09/08 6:00 0.074 8 1.10 0.091
Computed Peaks 0.167 50.00 0.980
Flow Frequency Analysis
Time series File:dev.tsf
Project Location:Sea-Tac
AnhUdl veak FIOw Rat25--- -----FIOw Frequency Analysis-------
Flow Rate Rank Time of veak reaks - - Rank Return Prob
CFS) CFS)Period
0.106 5 2/09/O1 2:00 0.217 1 100.00 0.990
0.084 8 1/05/02 16:00 0.128 2 25.00 0.960
0.128 2 2/27/03 7:00 0.127 3 10.00 0.900
0.088 7 8/26/04 2:00 0.112 4 5.00 0.800
0.106 6 10/28/04 16:00 0.106 5 3.00 0.667
0.112 4 1/18/06 16:00 0.106 6 2.00 0.500
0.127 3 10/26/06 0:00 0.088 7 1.30 0.231
0.217 1 1/09/O8 6:00 0.084 8 1.10 0.091
Computed Peaks 0.188 50.00 0.980
Flow Frequency Analysis
Time series File:bypass.tsf
Project Location:sea-Tac
nnnual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak Peaks - - Rank Return Prob
CFS) CFS)Period
0.025 7 2/09/O1 2:00 0.049 1 100.00 0.990
0.022 8 1/OS/02 16:00 0.036 2 25.00 0.960
0.031 3 12/OS/02 18:00 0.031 3 10.00 0.900
0.025 6 8/26/04 2:00 0.030 4 5.00 0.800
0.030 4 10/28/04 16:00 0.027 5 3.00 0.667
0.027 5 1/18/06 16:00 0.025 6 Z.00 0.500
0.036 2 10/26/06 0:00 0.025 7 1.30 0.231
0.049 1 1/09/08 6:00 0.022 8 1.10 0.091
Computed Peaks 0.045 50.00 0.980
Flow Frequency Analysis
Time 5eries File:devl5.tsf
Project Location:Sea-Tac
Annual Peak F10W Rdt25--- -----F10W F eqU2nCy AndlySlS-------
Flow Rate Rank Time of Peak veaks - - Rank Return Prob
cF5) CFS)Period
0.157 6 8/27/O1 18:00 0.536 1 100.00 0.990
0.117 8 1/OS/02 15:00 0.361 2 25.00 0.960
0.361 2 12/OS/02 17:15 0.225 3 10.00 0.900
0.127 7 8/23/04 14:30 0.223 4 5.00 0.800
0.225 3 11/17/04 5:00 0.195 5 3.00 0.667
0.195 5 10/27/05 10:45 0.157 6 2.00 0.500
0.223 4 10/25/06 22:45 0.127 7 1.30 0.231
0.536 1 1/09/08 6:30 0.117 8 1.10 0.091
Computed Peaks 0.478 50.00 0.980
evel 2 Det. rank (4' deep)
int. size = [0.167-(0.089 0.50)/(36-1) = 0.004
lst Int. = 0.089*0.5 = 0.04
Ht. of Orif. (2) = 3/4 3.5 = 2.63
Q(max) <1) _ (4/3"0.04)-0.027 = 0.026
EC Sed. 7rap = 2,080°Q<2) = 2,080°0.157 = 327 sf
Page 1
Lund Plat - East Basin (114th Ave.)
Retention/Detention Facility Sizing
12/30/05
Retention/Detention Facility
Type of Facility: Detention Tank
Tank Diameter: 4,.00 ft
Tank Length: ft
Effective Storage Depth: 0 ft
Stage 0 Elevation: 0.00 ft y 7'
Storage Volume: 1193. cu. ft
Riser Head: 3.50 ft
Riser Diameter: 12.00 inches
Number of orifices:
Full Head Pipe
Orifice #Height Diameter Discharge Diameter
ft)in) CFS) in)
1 0.00 0.039
2 1.80 1 13 0.095 4.0
Top Notch Weir: None
Outflow Rating Curve: None
Stage Elevation Storage Discharge Percolation
ft) ft) (cu. ft) (ac-ft) (cfs) cfs)
0.00 0.00 0. 0.000 0.000 0.00
0.01 0.01 3. 0.000 0.002 0.00
0.02 0.02 5. 0.000 0.003 0.00
0.03 0.03 8. 0.000 0.003 0.00
0.09 0.09 11. 0.000 0.004 0.00
0.05 0.05 13. 0.000 0.005 0.00
0.06 0.06 16. 0.000 0.005 0.00
0.07 0.07 19. 0.000 0.006 0.00
0.17 0.17 97. 0.001 0.009 0.00
0.27 0.27 77. 0.002 0.011 0.00
0.37 0.37 109. 0.002 0.013 0.00
0.47 0.97 192. 0.003 0.019 0.00
0.57 0.57 176. 0.009 0.016 0.00
0.67 0.67 211. 0.005 0.017 0.00
0.77 0.77 247. 0.006 0.018 0.00
0.87 0.87 284. 0.007 0.020 0.00
0.97 0.97 322. 0.007 0.021 0.00
1.07 1.07 360. 0.006 0.022 0.00
1.17 1.17 396. 0.009 0.023 0.00
1.27 1.27 437. 0.010 0.024 0.00
1.37 1.37 476. 0.011 0.025 0.00
1.97 1.47 515. 0.012 0.025 0.00
1.57 1.57 559. 0.013 0.026 0.00
1.67 1.67 599. 0.019 0.027 0.00
1.77 1.77 632. 0.015 0.028 0.00
1.80 1.80 644. 0.015 0.028 0.00
1.81 1.81 698. 0.015 0.029 0.00
1.82 1.82 652. 0.015 0.029 0.00
1.89 1.89 660. 0.015 0.031 0.00
1.85 1.85 663. 0.015 0.033 0.00
1.86 1.86 667. 0.015 0.035 0.00
1.87 1.87 671. 0.015 0.038 0.00
1.88 1.86 675. 0.015 0.039 0.00
1.89 1.89 679. 0.016 0.090 0.00
1.99 1.99 717. 0.016 0.095 0.00
2.09 2.09 755. 0.017 0.099 0.00
2.19 2.19 792. O.O1B 0.053 0.00
2.29 2.29 828. 0.019 0.056 0.00
2.39 2.39 864. 0.020 0.059 0.00
2.99 2.99 899. 0.021 0.062 0.00
2.59 2.59 932. 0.021 0.065 0.00
2.69 2.69 964. 0.022 0.067 0.00
2.79 2.79 995. 0.023 0.070 0.00
2.89 2.89 1024. 0.029 0.072 0.00
2.99 2.99 1051. 0.029 0.074 0.00
3.09 3.09 1076. 0.025 0.076 0.00
3.19 3.19 10 9. 0.025 0.078 0.00
3.29 3.29 1118. 0.026 0.080 0.00
3.39 3.39 1133. 0.026 0.082 0.00
3.49 3.49 1192. 0.026 0.089 0.00
3.50 3.50 1193. 0.026 0.089 0.00
3.60 3.60 1193. 0.026 0.394 0.00
3.70 3.70 1193. 0.026 0.959 0.00
3.80 3.80 1193. 0.026 1.690 0.00
3_90 3.90 1143. 0.026 2.480 0.00
9.00 4.00 1143. 0.026 2.770 0.00
9.10 9.10 1143. 0.026 3.020 0.00
9.20 4.20 1143. 0.026 3.260 0.00
9.30 4.30 1193. 0.026 3.480 0.00
4.40 4.90 1143. 0.026 3.690 0.00
9.50 4.50 1143. 0.026 3.880 0.00
4.60 4.60 1143. 0.026 4.070 0.00
9.70 9.70 1143. 0.026 9.250 0.00
9.80 9.80 1193. 0.026 4.920 0.00
9.90 9.90 1143. 0.026 9.580 0.00
S.OQ 5.00 1193. 0.026 9.790 0.00
5.10 5.10 1193. 0.026 4.890 0.00
5.20 5.20 1143. 0.026 5.040 0.00
5.30 5.30 1193. 0.026 5.190 0.00
5.90 5.90 1143. 0.026 5.330 0.00
5.50 5.50 1143. 0.026 5.960 0.00
Hyd Inflow Outflow Peak Storage
Stage Elev (Cu-Ft) (Ac-Ft)
1 0.22 0.22 3.59 3.59 1193.0.026
2 0.13 0.08 3.36 3.36 1129.0.026
3 0.13 0.09 3.50 3.50 1143.0.026
9 0.11 0.09 3.50 3.50 1143.0.026
5 0.11 0.08 3.16 3.16 1091.0.025
6 0.11 0.06 2.37 2.37 857.0.020
7 0.09 0.03 1.65 1.65 586.0.013
8 0.08 0.03 1.85 1.85 665.0.015
Hyd R/D Facility Tributary Reservoir POC Outflow
Outflow Inflow Inflow Target Calc
1 0.22 0.05 ******** 0.19 0.26
2 0.08 0.03 ******** ******* 0.10
3 0.09 0.04 ******** ******* 0.12
4 0.09 0.03 ******** ******* 0.11
5 0.08 0.02 ******** ******* 0.10
6 0.06 0.03 ******** ******* 0.08
7 0.03 0.03 ******** ******* 0.04
8 0.03 0.02 ******** ******* 0.05
Route Time Series through Facility
Inflow Time Series File:dev.tsf
Outflow Time Series File:rdout
POC Time Series Eile:dsout
Znflow/outflow Analysis
Peak Inflow Discharge: 0.217 CFS at 6:00 on Jan 9 in Year 8
Peak Outflow Discharge: 0.218 CFS at 7:00 on Jan 9 in Year 8
Peak Reservoir Stage: 3.54 Ft
Peak Reservoir Elev: 3.54 Ft
Peak Reservoir Storage: 1193. Cu-Ft
0.026 AC-Ft
Add Time Series:bypass.tsf
Peak Summed Discharge: 0.263 CFS at 7:00 on Jan 9 in Year 8
Point of Compliance File:dsout.tsf
Flow Duration from Time Series File:rdout.tsf
Cutoff Count Frequency CDF Exceedence Probability
CFS
I_
0.001 46720 79.452 79.452 20.548 0.205E+00
0.009 5362 8.799 88.196 11.804 0.116E+00
0.006 1772 2.890 91.086 8.919 0.891E-01
0.009 1937 2.393 93.430 6.570 0.657E-01
0.012 1251 2.040 95.470 4.530 0.453E-01
0.014 943 1.538 97.007 2.992 0.299E-01
0.017 558 0.910 97.917 2.083 0.208E-01
0.019 369 0.602 98.519 1.481 0.148E-01
0.022 267 0.935 98.955 1.045 O.lOSE-01
0.024 236 0.385 99.340 0.660 0.660E-02
0.027 171 0.279 99.618 0.382 0.382E-02
0.030 66 0.108 99.726 0.274 0.274E-02
0.032 6 0.010 99.736 0.264 0.264E-02
0.035 10 0.016 99.752 0.248 0.248E-02
0.037 8 0.013 99.765 0.235 0.235E-02
0.090 10 0.016 99.781 0.219 0.219E-02
0.092 18 0.029 99.811 0.189 0.189E-02
0.045 12 0.020 99.830 0.170 0.170E-02
0.047 12 0.020 99.850 0.150 0.150E-OZ
0.050 8 0.013 99.863 0.137 0.137E-02
0.053 9 0.015 99.878 0.122 0.122E-02
0.055 9 0.015 99.892 0.108 0.108E-02
0.058 7 0.011 99.904 0.096 0.962E-03
0.060 11 0.018 99.922 0.078 0.783E-03
0.063 10 0.016 99.938 0.062 0.620E-03
0.065 6 0.010 99.948 0.052 0.522E-03
0.068 7 0.011 99.959 0.091 0.908E-03
0.071 3 0.005 99.964 0.036 0.359E-03
0.073 5 0.008 99.972 0.028 0.277E-03
0.076 5 0.008 99.980 0.020 0.196E-03
0.078 5 0.008 99.989 0.011 0.114E-03
0.081 2 0.003 99.992 0.008 0.815E-04
0.083 3 0.005 99.997 0.003 0.326E-04
0.086 0 0.000 99.997 0.003 0.326E-04
0.086 1 0.002 99.996 0.002 0.163E-04
0.091 0 0.000 99.998 0.002 0.163E-09
Flow Duration from Time Series File:dsout.tsf
Cutoff Count Frequency CDF Exceedence Probability
CFS s
0.002 99479 80.690 80.690 19.310 0.193E+00
0.005 9703 7.670 86.359 11.641 0.116E+00
0.008 1864 3.090 91.399 8.601 0.860E-01
0.011 1417 2.311 93.710 6.290 0.629E-01
0.015 1261 2.056 95.766 4.239 0.923E-01
0.018 784 1.279 97.045 2.955 0.295E-01
0.021 562 0.917 97.962 2.036 0.204E-01
0.024 389 0.639 98.596 1.409 0.190E-01
0.028 297 0.469 99.080 0.920 0.920E-02
0.031 173 0.282 99.362 0.638 0.638E-02
0.039 113 0.184 99.597 0.953 0.953E-02
0.037 55 0.090 99.636 0.364 0.364E-02
0.091 36 0.059 99.695 0.305 0.305E-02
0.044 27 0.094 99.739 0.261 0.261E-02
0.097 13 0.021 99.760 0.240 0.240E-02
0.050 24 0.039 99.799 0.201 0.201E-02
0.054 14 0.023 99.822 0.178 0.178E-02
0.057 13 0.021 99.843 0.157 0.157E-02
0.060 12 0.020 99.863 0.137 0.137E-02
0.063 6 0.010 99.873 0.127 0.127E-02
0.067 9 0.015 99.887 0.113 0.113E-02
0.070 8 0.013 99.901 0.099 0.995E-03
0.073 10 0.016 99.917 0.083 0.632E-03
0.076 9 0.015 99.932 0.068 0.685E-03
0.080 10 0.016 99.948 0.052 0.522E-03
0.083 5 0.008 99.956 0.099 0.440E-03
0.086 6 0.010 99.966 0.039 0.342E-03
0.089 2 0.003 99.969 0.031 0.310E-03
0.093 9 0.007 99.976 0.024 0.245E-03
0.096 7 0.011 99.967 0.013 0.130E-03
0.099 2 0.003 99.990 0.010 0.978E-04
O.Y02 3 0.005 99.995 0.005 0.489E-04
0.106 0 0.000 99.995 0.005 0.989E-04
0.109 2 0.003 99.998 0.002 0.163E-04
0.112 0.000 99.998 0.002 0.163E-04
0.115 0 0.000 99.998 0.002 0.163E-04
Duration Comparison Anaylsis
Base File: exist.tsf
New File: dsout.tsf
Cutoff Units: Discharge in CFS
I Fraction of Time----- ---------Check of Tolerance-------
Cutoff Base New Change Probability Base New $Change
0.096 0.29E-02 0.24E-02 -19.8 0.29E-02 0.046 0.042 -9.0
0.051 0.22E-02 0.19E-02 -11.3 0.22E-02 0.051 0.049 -3.8
0.056 0.17E-02 0.16E-02 -3.9 0.17E-02 0.056 0.056 -0.9
I 0.062 0.13E-02 0.13E-02 5.1 0.13E-02 0.062 0.63 2.9
0.067 O.10E-02 O.IlE-02 9.7 O.10E-02 0.067 0.070 9.2
0.072 0.70E-03 0.85E-03 20.9 I 0.70E-03 0.072 0.076 9.6
0.078 0.99E-03 0.65E-03 33.3 0.49E-03 0.078 0.081 9.5
0.083 0.39E-03 0.49E-03 28.6 ( 0.34E-03 0.083 0.086 4.0
0.088 0.28E-03 0.31E-03 11.8 I 0.28E-03 0.088 0.091 3.0
I 0.093 0.16E-03 0.21E-03 30.0 0.16E-03 0.093 0.095 1.9
0.099 0.82E-09 0.11E-03 40.0 0.82E-04 0.099 0.099 0.8
0.109 0.82E-09 0.99E-04 -40.0 0.82E-09 0.109 0.099 -4.3
0.109 0.16E-09 0.16E-09 0.0 ( 0.16E-09 0.109 0.116 6.5
Maximum positive excursion = 0.010 cfs ( 9.3$)
occurring at 0.106 cfs on the Base Data:exist.tsf
and at 0.116 cfs on the New Data:dsout.tsf
Maximum negative excursion = 0.004 cfs ( -9.3)
occurring at 0.096 cfs on the Base Data:exist.tsf
and at 0.042 cfs on the New Data:dsout.tsf
I
Route Time Series through Facility
Inflow Time Series File:dev.tsf
Outflow Time Series File:rdout
POC Time Series File:dsout
Inflow/Outflow Analysis
Peak Inflow Discharge: 0.217 CFS at 6:00 on Jan 9 in Year 8
Peak Outflow Discharge: 0.218 CFS at 7:00 on Jan 9 in Year 8
Peak Reservoir Stage: 3.59 Ft
Peak Reservoir Elev: 3.54 Ft
Peak Reservoir Storage: 1143. Cu-Ft
0.026 Ac-Ft
Add Time Series:bypass.tsf
Peak Summed Discharge: 0.263 CFS at 7:00 on Jan 9 in Year 8
Point of Compliance File:dsout.tsf
Flow Duration from Time Series File:rdout.tsf
Cutoff Count Frequency CDF Exceedence_Probability
CFS
0.001 48720 79.452 79.952 20.598 0.205E+00
0.009 5362 8.744 88.196 11.809 0.116E+00
0.006 1772 2.890 91.086 8.919 0.891E-01
0.009 1937 2.393 93.930 6.570 0.657E-01
0.012 1251 2.090 95.470 4.530 0.453E-01
0.019 943 1.538 97.007 2.992 0.299E-01
0.017 558 0.910 97.917 2.083 0.208E-01
0.019 369 0.602 98.519 1.981 0.148E-01
0.022 267 0.435 98.955 1.095 O.lOSE-01
0.029 236 0.385 99.390 0.660 0.660E-02
0.027 171 0.279 99.618 0.382 0.382E-02
0.030 66 0.108 99.726 0.274 0.279E-02
0.032 6 0.010 99.736 0.264 0.264E-02
0.035 10 0.016 99.752 0.248 0.298E-02
0.037 8 0.013 99.765 0.235 0.235E-02
0.040 10 0.016 99.781 0.219 0.219E-02
0.042 18 0.029 99.811 O.I89 0.189E-02
0.045 12 0.020 99.830 0.170 0.170E-02
0.097 12 0.020 99.850 0.150 0.150E-02
0.050 8 0.013 99.863 0.137 0.137E-02
0.053 9 0.015 99.878 0.122 0.122E-02
0.055 9 0.015 99.892 0.108 0.108E-02
0.058 7 0.011 99.904 0.096 0.962E-03
0.060 11 0.018 99.922 0.078 0.783E-03
0.063 10 0.016 99.938 0.062 0.620E-03
0.065 6 0.010 99.948 0.052 0.522E-03
0.068 7 0.011 99.959 0.091 0.908E-03
0.071 3 0.005 99.964 0.036 0.359E-03
0.073 5 0.008 99.972 0.028 0.277E-03
0.076 5 0.008 99.980 0.020 0.196E-03
0.078 5 0.008 99.989 0.011 0.119E-03
0.081 2 0.003 99.992 0.008 0.815E-04
0.083 3 0.005 99.997 0.003 0.326E-04
0.086 0 0.000 99.997 0.003 0.326E-04
0.086 1 0.002 99.998 0.002 0.163E-04
0.091 0 0.000 99.998 0.002 0.163E-04
Flow Duration from Time Series File:dsout.tsf
Cutoff Count Frequency CDF Exceedence_Probability
CFS
0.002 99479 80.690 80.690 19.310 0.193E+00
0.005 9703 7.670 88.359 11.641 0.116E+00
0.008 1869 3.040 91.399 8.601 0.860E-01
0.011 1917 2.311 93.710 6.290 0.629E-01
0.015 1261 2.056 95.766 4.239 0.423E-01
0.018 789 1.279 97.095 2.955 0.295E-01
0.021 562 0.917 97.962 2.038 0.209E-01
0.024 389 0.634 98.596 1.409 0.140E-01
0.028 297 0.484 99.080 0.920 0.920E-02
0.031 173 0.282 99.362 0.638 0.638E-02
0.034 113 0.189 99.597 0.453 0.453E-02
0.037 55 0.090 99.636 0.364 0.369E-02
0.041 36 0.059 99.695 0.305 0.305E-02
0.049 27 0.049 99.739 0.261 0.261E-02
0.047 13 0.021 99.760 0.240 0.240E-02
0.050 29 0.039 99.799 0.201 0.201E-02
0.054 19 0.023 99.822 0.178 0.178E-02
0.057 13 0.021 99.893 0.157 0.157E-02
0.060 12 0.020 99.863 0.137 0.137E-02
0.063 6 0.010 99.873 0.127 0.127E-02
0.067 9 0.015 99.887 0.113 0.113E-OZ
0.070 8 0.013 99.901 0.099 0.995E-03
0.073 10 0.016 99.917 0.083 0.832E-03
0.076 9 0.015 99.932 0.068 0.685E-03
0.080 10 0.016 99.998 0.052 0.522E-03
0.083 5 0.006 99.956 0.044 0.490E-03
0.086 6 0.010 99.966 0.034 0.392E-03
0.089 2 0.003 99.969 0.031 0.310E-03
0.093 4 0.007 99.976 0.024 0.245E-03
0.096 7 0.011 99.967 0.013 0.130E-03
0.099 2 0.003 99.990 0.010 0.978E-09
0.102 3 0.005 99.995 0.005 0.489E-04
0.106 0 0.000 99.995 0.005 0.489E-04
0.109 2 0.003 99.998 0.002 0.163E-09
0.112 0 0.000 99.998 0.002 0.163E-09
0.115 0 O.Q00 99.998 0.002 0.163E-09
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KCRTS Command
CREATE a new Time Series G'f a
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : exist.tsf
Regional Scale Factor : 1.00 i
Data Type : Reduced
Creating Hourly Time Series File
Loading Time Series File:C:\KC SWDM\KC DATA\STTF60R.rnf .
Till Forest 0.09 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTP60R.rnf .
Till Pasture 0.57 acres
Loading Time Series File:C:\KC SWDM\KC DATA\STWL60R.rnf .
Wetland 0.01 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STE160R.rnf .
Impervious 0.05 acres
Total Area : 0.72 acres
Peak Discharge: 0.100 CFS at 6:00 on Jan 9 in Year 8
Storing Time Series File:exist.tsf .
Time Series Computed
KCRTS Command
Enter the Analysis TOOLS Module
Analysis Tools Command
Compute PEAKS and Flow Frequencies
Loading Stage/Discharge curve:exist.tsf .
Flow Frequency Analysis
Time Series File:exist.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:exist.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 : dev.tsf
Regional Scale Factor : 1.00
Data Type : Reduced
Creating Hourly Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTG60R.rnf .
Till Grass 0.50 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STEI60R.rnf .
Impervious 0.91 acres
Total Area : 0.91 acres
Peak Discharge: 0.299 CFS at 6:00 on Jan 9 in Year 8
Storing Time Series File:dev.tsf .
Time Series Computed
KCRTS Command
Enter the Analysis TOOLS Module
a
Analysis Tools Command
Compute PEAKS and Flow Frequencies
Loading Stage/Discharge curve:dev.tsf .
Flow Frequency Analysis
Time Series File:dev.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:dev.pks .
Analysis Tools Command
RETURN to Previous Menu
KCRTS Command
eXit KCRTS Program
I
sum.txt
Lund Plat - West Basin
Runoff Calculations
I
4 4 6
Flow Frequency Analysis r
Time Series File:exist.tsf
z
P OJeCt Location:Sea-Tac
Annual Peak Flow Rates---Flow Frequency Analysis-------
Flow Rate Rank Time of Peak Peaks - - Rank Return Prob
CFS) CFS) PeriOd
0.055 2 2/09/O1 15:00 0.100 1 100.00 0.990
0.027 7 1/05/02 16:00 0.055 2 25.00 0.960
0.054 3 2/27/03 7:00 0.054 3 10.00 0.900
0.015 8 8/26/04 2:00 0.051 4 5.00 0.800
0.031 6 1/05/05 8:00 0.049 5 3.00 0.667
0.051 4 1/18/06 16:00 0.031---- 6 2.00 0.500
0.049 5 11/24/06 4:00 0.027 7 1.30 0.231
0.100 1 1/09/08 6:00 0.015 8 1.10 0.091
Computed Peaks 0.085 50.00 0.980
Flow Frequency Analysis
C
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Time Series File:dev.tsf vv Project ocation:sea-Tac
Annual Peak Flow Rates---Flow Frequency Analysis-------
Flow Rate Rank Time of Peak Peaks - - Rank Return Prob
CFS) CFS) Period
0.144 5 2/09/O1 2:00 0.300 1 100.00 0.990
0.110 8 1/05/02 16:00 0.175 2 25.00 0.960
0.175 2 2/27/03 7:00 0.162 3 10.00 0.900
0.112 7 8/26/04 2:00 0.152 4 5.00 0.800
0.136 6 10/28/04 16:00 0.144 5 3.00 0.667
0.152 4 1/18/06 16:00 0.136 6 2.00 0.500
0.162 3 10/26/06 0:00 0.112 7 1.30 0.231
0.300 1 1/09/08 6:00 0.110 8 1.10 0.091
Computed Peaks 0.258 50.00 0.980
Flow Frequency Analysis
Time series File:devl5.tsf
Project ocation:sea-Tac
annual Peak Flow Rates---Flow Frequency analysis-------
Flow Rate Rank Time of Peak Peaks - - Rank Return Prob
CFS) CFS) Period
0.195 6 8/27/O1 18:00 0.736 1 100.00 0.990
0.152 8 1/05/02 15:00 0.479 2 25.00 0.960
0.479 2 12/08/02 17:15 0.324 3 10.00 0.900
0.157 7 8/23/04 14:30 0.281 4 5.00 0.800
0.324 3 11/17/04 5:00 0.251 5 3.00 0.667
0.251 5 10/27/05 10:45 0.195 6 2.00 0.500
0.281 4 10/25/06 22:45 0.157 7 1.30 0.231
0.736 1 1/09/O8 6:30 0.152 8 1.10 0.091
Computed Peaks 0.651 50.00 0.980
evel 2 et. Pond (3' deep)
int. Size = 0.031*.05)]/(36-1) = 0.002
lst Int. _ .04 .5 = 0.02
Ht. of ori 3/4 * 3 = 2.25 ft
Q(max) (1 = 4/3 * 0.02 = 0.03 cfs
EC sed Trap = 2080*Q(2) = 2080*0.195 = 408 sf
3
Page 1
Retention/Detentian Facility
Type of Facility: Detention Pond
Side Slope: 2.50 H:iV
Pond Battam Length: 7i.89 ft
Pond Bottorn Width: 25.31 ft
Ppnd Bottom Area: 1820. sq. ft
Tap Area at 1 ft. FB: 4164. sq. ft
0.096 acres
Effective Storage Depth: 3.00 ft
Staqe 4 Elevatian: Q.00 ft
Storage Volume: 7872. cu. ft
0.1$1 ac-ft
R.iser Head; 3,40 ft
Riser Diameter: 12.00 inches
Number of orifices: 2
Full Head Pipe
Orifice #Heiqht Diameter Discharge Diameter
ft)in) CFS} in)
1 4.00 0.?2 0.024
2 2.00 0.68 0.013 9.0
Top Notch Weir: None
Outflow Rating Curve: None
Stage Elevatian Storage Discharge Percalatipn Surf Area
ft) ft) (cu. Pt) (ac-ft) (cfs) cfs) sq. ft)
4.00 0.00 0. O.Q00 0.000 0.00 1820.
0.01 4.01 1$. 4.40Q 0.002 4.44 1825,
0.02 0.02 37. 0.001 0.002 0.00 183p.
0.03 0.03 55. 0.001 0.002 0.00 1835.
0.44 0.04 73. Q.042 Q.d03 0.44 1839.
0.05 0.05 92. 0.002 0.003 0.00 1894.
0.06 0.06 110. O.dd3 0.409 0.00 1849.
0.16 0.16 298. 0.047 4.Q46 4.00 1898.
0.26 0.26 490. 0.011 0.007 0.00 1998.
0.36 0.36 6@7, O.d16 0.008 0.00 1998.
0,46 0.96 89. Q.024 0.009 0.44 20q9.
0.56 0.56 1q97. 0.025 0.010 0.00 2100.
O.b6 0.66 1310. 0.030 0.011 0.00 2152.
0.76 0.7fi 1527. Q.035 0.012 0.00 2204.
0.86 0.86 1750. 0.090 0.013 0.00 2256.
0.96 0.96 i979. 0.085 O.OlA 0.00 2310.
1.06 1.46 2212. Q.051 O.Q14 0.00 2363.
1.16 1.16 2951. 0.056 0.015 0.00 2417.
1.26 1.26 2696. 0.062 0.016 0.00 2972.
1.36 1.36 2946. 0.068 0.016 0.00 2527.
1.96 1.96 3201. 0.073 0.017 0.00 2583.
1.56 1.56 3462. 0.079 d.01 0.00 2639.
1.66 I.66 3729. Q.486 4.Q1$Q.00 2696.
1.76 1.76 4001. 0.092 0.01$0.00 2753.
1.$6 1.86 9280. d.098 d.019 0.00 2811.
1.46 1.96 4554. 0.105 0.019 0.00 2869.
2.00 2.00 4679. 0.107 0.020 0.00 2892.
2,01 2.01 4708. 0.108 d.024 O.dd 2898.
2.02 2.Q2 4737. 0.149 0.021 0.00 2904.
2.03 2.03 4766. 0.109 0.021 O.QO 2910.
2.04 2.09 4795. 0.110 0.022 O.dO 2916.
2.05 2.45 4824. 0,111 0.423 0.00 2921.
2.06 2.06 4853. 0.111 0.023 0.00 2927.
2.16 2.16 5149. 0.118 0.025 O.dO 2987.
2.26 2.26 5451. 4.125 4.02?0.00 3046.
2.36 2.36 5758. 0.132 0.029 0.00 3106.
2.4fi 2.46 6072. 0.139 0.430 0.00 316.
2.56 2.56 5392. p.147 0.032 0.04 3228.
2.66 2.66 6718. 0.159 0.033 0.00 3290.
2.76 2,76 705d, d.162 0.034 d.00 3352.
z. e 3, a. g e
2.96 2.96 7733. p.178 0.036 O.QO 3978.
3.00 3.00 7872. 0.181 0.037 0.00 3503.
3.10 3.10 8226. 0.189 0.346 0.00 3567.
3.20 3.20 8586. 0.197 0.910 0.00 3631.
3.30 3.30 8952. 0.206 1.690 0.00 3696.
3.40 3.40 9325. 0.219 2.930 0.00 3762.
3.50 3.50 9704. 0.223 2.720 0.00 3827.
3.60 3.60 10090. 0.232 2.970 0.00 3899.
3.70 3.70 10983. 0.241 3.210 0.00 3961.
3.80 3.80 10883. 0.250 3.930 0.00 9028.
3.90 3.90 11289. 0.259 3.630 0.00 4096.
9.00 4.00 11702. 0.269 3.830 0.00 4169.
9.10 9.10 12122. 0.278 4.010 0.00 9233.
9.20 4.20 12548. 0.288 4.190 0.00 4302.
9.30 4.30 12982. 0.298 4.360 0.00 9372.
4.40 9.40 13423. 0.308 4.520 0.00 9943.
9.50 9.50 13671. 0.318 9.680 0.00 4513.
4.60 4.60 19326. 0.329 9.830 0.00 4585.
9.70 4.70 14788. 0.339 4.980 0.00 4657.
4.80 4.60 15257. 0.350 5.130 0.00 9729.
4.90 9.90 15733. 0.361 5.270 0.00 4802.
5.00 5.00 16217. 0.372 5.400 0.00 4875.
Hyd Inflow Outflow Peak Storage
Target Calc Stage Elev (Cu-Ft) (Ac-Ft)
1 0.30 ******* 0.17 3.04 3.04 8022.0.184
2 0.14 0.05 0.06 3.01 3.01 7896.0.181
3 0.16 ******* 0.03 2.54 2.59 6321.0.145
9 0.15 ******* 0.03 2.31 2.31 5615.0.129
5 0.18 ******* 0.03 2.92 2.42 5941.0.136
6 0.14 ******* 0.02 1.80 1.80 4123.0.095
7 0.11 ******* 0.02 1.39 1.39 3019.0.069
8 0.11 ******* 0.01 0.94 0.94 1932.0.094
Duration Comparison Anaylsis
Base File: exist.tsf
New File: rdout.tsf
Cutoff Units: Discharge in CFS
Fraction of Time----- ---------Check of Tolerance-------
Cutoff Base New BChange Probability Base New Change
0.021 0.43E-02 0.43E-02 1.1 0.93E-02 0.021 0.021 0.2
0.024 I 0.32E-02 0.37E-02 17.9 I 0.32E-02 0.024 0.025 7.5
0.026 I 0.24E-02 0.29E-02 16.8 ( 0.24E-02 0.026 0.028 4.3
0.029 I 0.17E-02 0.16E-02 -4.6 0.17E-02 0.029 0.029 -0.9
0.032 I 0.13E-02 0.91E-03 -31.7 I 0.13E-02 0.032 0.030 -7.0
0.035 I O.10E-02 0.59E-03 -41.9 ( O.10E-02 0.035 0.031 -9.5
0.037 I 0.82E-03 0.65E-09 -92.0 I 0.82E-03 0.037 0.033 -12.1
0.040 I 0.60E-03 0.49E-09 -91.9 I 0.60E-03 0.040 0.035 -13.B
0.043 I 0.44E-03 0.49E-09 -88.9 I 0.99E-03 0.043 0.035 -17.2
0.095 I 0.29E-03 0.33E-04 -88.9 0.29E-03 0.045 0.036 -21.3
0.098 I 0.16E-03 0.33E-04 -80.0 I 0.16E-03 0.098 0.036 -29.7
0.051 0.98E-04 0.33E-04 -66.7 I 0.98E-04 0.051 0.037 -27.7
0.054 0.82E-04 0.16E-09 -80.0 0.82E-04 0.059 0.037 -31.2
Maximum positive excursion = 0.002 cfs ( 7.6)
occurring at 0.023 cfs on the Base Data:exist.tsf
and at 0.025 cfs on the New Data:rdout.tsf
Maximum negative excursion = 0.018 cfs (-32.28)
occurring at 0.059 cfs on the Base Data:exist.tsf
and at 0.037 cfs on the New Data:rdout.tsf
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Probability Exceedence
Project: Lund Plat
Jailhouse Window OverFlow
Date:1/19/2006
By: LT
Rectangular, Sharp Crested Weir
Q= C (L-0.2H) H"3/2
C=3.27+0.40H/P
Q(100)= 0.736cfs
H P L C Q
0.17 3.5 2.5 3.3 0.57 Jailhouse Window
0.25 3.5 2.5 3.3 1.01 I
Specify 3'wide window to account for bar area and height> 3" I,
Drainage Calcs.xls Sharp Crested Weir
Printed: 7/19/2006
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Cumulative Probability
r
Flowsum.txt
Lund Plat
Summary of Peak flows Tributary to wetland from Site
9/9/05
Flow Frequency Analysis
Time Series File:exist.tsf
Project ocation:5ea-Tac
Annual Peak Flow Rates---Flow Frequency Analysis-------
Flow Rate Rank Time of Peak Peaks - - Rank Return Prob
CFS) CFS) Period
0.052 2 2/09/O1 15:00 0.080 1 100.00 0.990
0.016 7 1/05/02 16:00 0.052 2 25.00 0.960
0.050 3 2/27/03 7:00 0.050 3 10.00 0.900
0.004 8 3/24/04 19:00 0.031 4 5.00 0.800
0.020 6 1/05/05 8:00 0.029 5 3.00 0.667
0.031 4 1/18/06 16:00 0.020 6 2.00 0.500
0.029 5 11/24/06 4:00 0.016 7 1.30 0.231
0.080 1 1/09/08 9:00 0.004 8 1.10 0.091
Computed Peaks 0.071 50.00 0.980
Flow Frequency analysis
Time series File:dev.tsf
Project ocation:sea-Tac
Annual Peak Flow Rates---Flow Frequency Analysis-------
Flow Rate Rank Time of Peak Peaks - - Rank Return Prob
CFS) CFS) PeriOd
0.083 3 2/09/O1 2:00 0.144 1 100.00 0.990
0.050 7 1/05/02 16:00 0.096 2 Z5.00 0.960
0.096 2 2/27/03 7:00 0.083 3 10.00 0.900
0.044 8 8/26/04 2:00 0.069 4 5.00 0.800
0.053 6 10/28/04 16:00 0.065 5 3.00 0.667
0.069 4 1/18/06 16:00 0.053 6 2.00 0.500
0.065 5 11/24/06 3:00 0.050 7 1.30 0.231
0.144 1 1/09/08 6:00 0.044 8 1.10 0.091
Computed Peaks 0.128 50.00 0.980
Page 1
volsum.txt
Lund Plat
5ummary of Runoff volume irected to wetland from site
9/9/05
Discharge volume from Time series
exist.tsf
between 10/O1/00 00:00 and 10/30/00 23:59
2879. Cu-Ft or 0.066 AC-Ft in 30.0 days
Discharge volume from Time series
dev.tsf
between 10/O1/00 00:00 and 10/30/00 23:59
5858. Cu-Ft or 0.134 Ac-Ft in 30.0 days
Page 1
Rational Method
Project: Lund Plat
Date:1/20/2006
WEST BASIN -25-YR
Calculates the peak runoff
Q=CIRA
1) Compute Composite Runoff Coefficient C:
A AZ As Aa Cc
A 0.5 0.41 0 Q ' (tributary areas, acres)
L 100 100 0 length along flowpath, ft)
So 0.03 0.02 0.02 slope along flowpath, ft/ft)
k 7 20 20 from Table 3.2.1.0-- pg 3-13)
C 0.25 0.9 0.9 from Tabte 3.2.1.A---pg 3-13)
2) Compute Peak Rainfall Intensity IR:
2a) First, compute Travel Time T:
T TZ T3 T
T travel time, min)
2b)Second, compute unit peak rainfall intensity factor, iR= aR"T^-bR:
R = 25 (storm return frequency, years)
aR= 2.66 (coefficient from Table 3.2.1.6--- pg 3-13)
bR= 0.65 (coefficient from Table 3.2.1.B--- pg 3-13)
IR=
2c)Third, compute IR= PR"iR:
PR= 3.4 (precipitation, in)
R s .0 , . .
3) Compute Peak Runoff Rate, QR= CIRA:
QR= cfs
3
Drainage Calcs.xls Rational Method
1/2M2006
Rational Method
Project: Lund Plat
Date:1/20/2006
WEST BASIN -100-YR
Calculates the peak runoff
Q=CIRA
1) Compute Composite Runoff Coefficient C:
Ati A2 As pk, Cc
A 0.5 0.41 0 tributary areas, acres)
L 100 100 0 length along flowpath, ft)
So 0.03 0.02 0.02 slope along flowpath, ft/ft)
k 7 20 20 from Table 3.2.1.0— pg 3-13)
C 0.25 0.9 0.9 from Table 3.2.1.A---pg 3-13)
2) Compute Peak Rainfall Intensity IR:
2a) First, compute Travel Time T:
Ti TZ T3 T
T travel time, min)
2b)Second, compute unit peak rainfall intensity factor, iR = aR"T^-bR:
R = 100 (storm return frequency, years)
aR= 2.61 (coefficient from Table 3.2.1.B-- pg 3-13)
bR= 0.63 (coefficient from Table 3.2.1.6---pg 3-13)
IR=
2c)Third, compute IR = PR*iR:
PR= 3.9 (precipitation, in)
R—
3) Compute Peak Runoff Rate, QR= CIRA:
QR=cfs
Drainage Calcs.xls Rational Method
1/24/2006
Rational Method
Project: Lund Plat
Date:1/20/2006
EAST BASIN -25-YR
Caiculates the peak runoff
Q=CIRA
1) Compute Composite Runoff Coefficient C:
A Az As Cc
A 0.3 0.43 0 ' " ' '"' """ (tributary areas, acres)
L 100 100 0 length along flowpath, ft)
So 0.03 0.02 0.02 slope along flowpath, ft/ft)
k 7 20 20 from Table 3.2.1.0 -- pg 3-13)
C 0.25 0.9 0.9 from Table 3.2.1.A--- pg 3-13)
2) Compute Peak Rainfall Intensity IR:
2a First com ute Travel Time T :P c
T TZ T3 T
T travel time, min)
2b)Second, compute unit peak rainfall intensity factor, iR= aR"T^-bR:
R = 25 (storm return frequency, years)
aR= 2.66 (coefficient from Table 3.2.1.B --- pg 3-13)
bR= 0.65 (coefficient from Table 3.2.1.B --- pg 3-13)
R - w °:....,...:
2c)Third, compute IR= PR'`iR:
PR= 3.4 (precipitation, in)
R
3 Com ute Peak Runoff Rate, Q = CI A:P R R
QR =cfs
Drainage Calcs.xls Rational Method
1/24/2006
Rational Method
Project: Lund Plat
Date:1/20/2006
EAST BASIN -100-YR
Calculates the peak runoff
Q=CIRA
1) Compute Composite Runoff Coefficient C:
Ai A2 As Ac Cc
A 0.3 0.43 0 tributary areas, acres)
L 100 100 0 length along flowpath,ft)
So 0.03 0.02 0.02 slope along flowpath, ft/ft)
k 7 20 20 from Table 3.2.1.0--pg 3-13)
C 0.25 0.9 0.9 from Table 3.2.1.A---pg 3-13)
2) Compute Peak Rainfall Intensity IR:
2a) First, compute Travel Time T:
T TZ T3 T
T travel time, min)
2b) Second, compute unit peak rainfall intensity factor, iR= aR*T^-bR:
R = 100 (storm return frequency, years)
aR= 2.61 (coefficient from Table 3.2.1.B---pg 3-13)
bR= 0.63 (coefficient from Table 3.2.1.6---pg 3-13)
R -
2c)Third, compute IR = PR"iR:
PR= 3.9 (precipitation, in)
I - t
R—
3)Compute Peak Runoff Rate, QR= CIRA:
QR= I,, cfs
Drainage Calcs.xls Rational Method
1/24/2006
Rational Method
Project: Lund Plat
Date:1/20/2006
UPSTREAM TRIBUTARY AREA-25-YR
Calculates the peak runoff
Q=CIRA
1)Compute Composite Runoff Coefficient C:
Ai A2 As At, Cc
A 1.85 1.85 0 tributary areas, acres)
L 200 535 0 length along flowpath, ft)
So 0.02 0.02 0.02 slope along flowpath, ft/ft)
k 7 15 20 from Table 3.2.1.0---pg 3-13)
C 0.36 0.36 0.9 from Table 3.2.1.A--- pg 3-13)
2)Compute Peak Rainfall Intensity IR:
2a) First, compute Travel Time T:
T, T2 T3 T
T travel time, min)
2b) Second, compute unit peak rainfall intensity factor, iR= aR*T^-bR:
R = 25 (storm return frequency, years)
aR= 2.66 (coefficient from Table 3.2.1.B ---pg 3-13)
bR= 0.65 (coefficient from Table 32.1.B---pg 3-13)
R
2c)Third, compute IR= PR"iR:
PR= 3.4 (precipitation, in)
IR -
4 . .,
3) Compute Peak Runoff Rate, QR= CIRA:
QR=cfs
Drainage Calcs.xls Rational Method
1/24/2006
Rational Method I
Project: Lund Plat
Date:1/20/2006
UPSTREAM TRIBUTARY AREA-100-YR
Calculates the peak runoff
Q=CIRA
1) Compute Composite Runoff Coefficient C:
A Az As C Cc
A 1.85 1.85 0 tributary areas, acres)
L 200 535 0 length along flowpath, ft)
So 0.02 0.02 0.02 slope along flowpath, ff/ft)
k 7 15 20 from Table 3.2.1.0--pg 3-13)
C 0.36 0.36 0.9 from Table 3.2.1.A---pg 3-13)
2) Compute Peak Rainfall Intensity IR:
2a) First, compute Travel Time T:
T, T2 T3 T
T travel time, min)
2b) Second, compute unit peak rainfall intensity factor, iR=aR`T^-bR:
R = 100 (storm return frequency, years)
aR= 2.61 (coefficient from Table 3.2.1.B--- pg 3-13)
bR= 0.63 (coefficient from Table 3.2.1.6--- pg 3-13)
R
2c)Third, compute IR= PR*iR:
PR= 3.9 (precipitation, in)
IR
3)Compute Peak Runoff Rate, QR=CIRA:
QR =cfs
Drainage Calcs.xls Rational Method
1/24/2006
BWPIPE INPUT DATA
Project: Lund Plat
Date: 2/20/2006
sitepipe. CONVEYANCE PIPING TO POND (West Basin)
1.4 = 25-yr flow for site
1.6 = 100-yr flow for site
I 472.29 = tailwater elev. (25-yr WS in pond)
CB# L (ft) DIA(in) TYPE OUTLET-IE INLET-IE INLET-TYPE
RIM/O.F. EL. BND ANG STR. DIA (ft)Q-RAT
N3-W 21 12 1 468.28 469.51 5
473.28 90 2.5 0
N4-W 115 12 1 169.61 470.18 5
473.28 0 2.5 1
N5-W 123 8 1 470.28 475.33 5
478.33
pondpipe. CONVEYANCE PIPING FROM POND (West Basin)
1.4 = 25-yr flow for site
1.6 = 100-yr flow for site
469 = Highwater downstream
I CB# L (ft) DIA(in) TYPE OUTLET-IE INLET-IE INLET-TYPE
RIM/O.F. EL. BND ANG STR. DIA(ft)Q-RAT
I N 1-W 39 12 1 467.34 468.28 5
474.78
roadpipe. CONVEYANCE PIPING TO TANK(East Basin)
1.3 =25-yr flow for site
1.5 = 100-yr flow for site
471.15 =tailwater elev. (25-yr WS in tank)
CB# L (ft) DIA(in) TYPE OUTLET-IE INLET-IE INLET-TYPE
RIM/O.F. EL. BND ANG STR. DIA(ft)Q-RAT
N5-E 7 12 1 468.89 470.41 5
473.51 90 2.5 0
N6-E 144 12 1 470.51 472 5
474.92 0 2.5 0
N7-E 178 12 1 472.1 475.7 5
478.7
tankpipe. CONVEYANCE PIPING FROM TANK(East Basin)
4.5 = 25-yr flow for site (1.3) + upstream (3.2)
5.3 = 100-yr flow for site (1.5) + upstream (3.8)
470 = Highwater downstream
CB# L (ft) DIA(in) TYPE OUTLET-IE INLET-IE INLET-TYPE
RIM/O.F. EL. BND ANG STR. DIA(ft)Q RAT
N 1-E 125 12 1 466.8 46728 5
471.8 45 2.5 10
N2-E 32 12 1 467.38 467.79 5
473.79
Drainage Calcs.xls BWPIPE
2/20/2006
sitepipe.txt
KZNG COUP!TY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 5.30h
File Opened for Reading:sitepipe.bwp
File opened for writing:sitep pe.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:sitepipe.bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:472.29 feet
Discharge Range:0.5 to 2. Step of 0.5 [cfs]
Overflow Elevation:478.33 feet
weir:NONE
Upstream velocity:l. feet/sec
PIPE NO. 1: 70 LF - 12 CP @ 1.76% OUTLET: 468.28 INLET: 469.51 INTYP: 5
UNC N0. 1: OVERFLOW-EL: 473.28 BEND: 90 DEG DIA/WIDTH: 2.5 Q-RATIO: 0.00
Q(CFS) HW(FT) HW ELEV. '` N-FAC DC DN TW DO DE HWO HWI
rt*t+i+:rtrt fr t fr ai a t:*fr i******
0.50 2.81 472.32 * 0.012 0.30 0.22 4.01 4.01 2.80 2.81 0.40
1.00 2.87 472.38 0.012 0.43 0.30 4.01 4.01 2.83 2.87 0.59
1.50 2.99 472.50 0.012 0.52 0.38 4.01 4.01 2.89 2.99 0.77
2.00 3.15 472.66 f° 0.012 0.61 0.44 4.01 4.01 2.97 3.15 0.94
PIPE N0. 2: 115 LF - 12 CP @ 0.50% OUTLET: 469.61 INLET: 470.18 INTYP: 5
7UNC N0. 2: OVERFLOW-EL: 473.28 BEND: 0 DEG DIA WIDTH: 2.5 Q-RATIO: 1.00
Q(CFS) HW(FT) HW ELEV. N-FAC DC DN TW DO DE HWO HWI
ftt tr***4*hrt i i rt rtrt rt:ric frtri:f'.<rt rtrtirrt frfrhi:rtrt#rtfr*t rti*tr***ft*frh*
0.50 2.18 472.36 * 0.012 0.30 0.30 2.71 2.71 2.17 2.18 0.40
1.00 2.30 472.48 i° 0.012 0.43 0.42 2.77 2.77 2.28 2.30 0.58
1.50 2.55 472.73 0.012 0.52 0.54 2.89 2.89 2.49 2.55 0.73
2.00 2.89 473.07 ` 0.012 0.61 0.64 3.05 3.05 2.79 2.89 0.86
PIPE No. 3: 123 LF - 8 CP @ 4.11% OUT ET: 470.28 zN ET: 475.33 INTYP: 5
Q(CFS) HW(FT) HW ELEV. N-FAC DC DN TW DO DE HWO HWI
rt*'.r rt****frtr trir*fr**trk***f**fr'.rt it rthth i:'.:rt frk**h fr
0.25 0.29 475.62 rt 0.012 0.24 0.14 2.08 2.08 0.24 **** 0.29
0.50 0.45 475.78 * 0.012 0.34 0.20 2.20 2.20 0.34 **** 0.45
0.75 0.60 475.93 * 0.012 0.41 0.25 2.45 2.45 0.41 **** 0.60
1.00 0.75 476.08 rt 0.012 0.48 0.29 2.79 2.79 0.48 **** 0.75
File Opened for writing:sitepipe.bwt
save results to Hw/7w file:sitepipe.bwt
Exit KCBW Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 5.30h
Page 1
roadpipe.txt
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
Water and Land Resources Division
BA KWATER ANALYSIS PROGRAM
version 5.30h
File Opened for Reading:roadpipe.bwp
File Opened for writing:roadpipe.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:roadpipe.bwp
surcharge condition at intermediate junctions
Tailwater Elevation:471.15 feet
ischarge Range:0.5 to 2. Step of 0.5 [cfs]
overflow Elevation:478.7 feet
weir:NONe
upstream velocity:l. feet/sec
PIPE N0. 1: 7 LF - 12 CP @ 21.7190 OUTLET: 468.89 INLET: 470.41 INTYP: 5
JUNC NO. 1: OVERFLOW-EL: 473.51 BEND: 90 DEG DIA/WIDTH: 2.5 Q-RATIO: 0.00
Q(CFS) HW(FT) HW ELEV. rt N-FAC DC DN TW DO DE HWO HWI
rtAa*trtr rtrtk**fr ft*rt**h*tr tr*tr*tr**h*4ici*ft tr**fth*h ic i ft
0.50 0.30 470.71 rt 0.012 0.30 0.12 2.26 2.26 0.30 ***** 0.30
1.00 0.49 470.90 i° 0.012 0.43 0.17 2.26 2.26 0.43 rt i° 0.49
1.50 0.67 471.08 s 0.012 0.52 0.20 2.26 2.26 0.52 i°xi°* 0.67
2.00 0.84 471.25 * 0.012 0.61 0.23 2.26 2.26 0.61 ••AA 0.84
PIPE N0. 2: 144 LF - 12 CP @ 1.03% OUTLET: 470.51 INLET: 472.00 INTYP: 5
JUNC N0. 2: OVERFLOW-EL: 474.92 BEND: 0 DEG DIA/WIDTH: 2.5 Q-RATIO: 0.00
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
rtrt4frrt rtkfr i*hh4*tr ftfr*tr fr**firt ir*fr*h i<***rtfr ir hrthtri rtft rtrtrti'.c ki;
0.50 0.39 472.39 * 0.012 0.30 0.25 0.20 0.25 0.30 ***** 0.39
1.00 0.57 472.57 * 0.012 0.43 0.35 0.39 0.39 0.43 TM**{° 0.57
1.50 0.70 472.70 * 0.012 0.52 0.43 0.57 0.57 0.52 **rt** 0.70
2.00 0.82 472.82 * 0.012 0.61 0.51 0.74 0.74 0.61 **** 0.82
PIPE NO. 3: 178 LF - 12 CP @ 2.02% OUTLET: 472.10 INLET: 475.70 INTYP: 5
Q(FS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
fr fr+*+*t****kA**ft****i t*t i+t*f:t+t
0.50 0.38 476.08 0.012 0.30 0.21 0.29 0.29 0.30 ***** 0.38
1.00 0.57 476.27 * 0.012 0.43 0.29 0.47 0.47 0.43 **rtrt 0.57
1.50 0.74 476.44 * 0.012 0.52 0.36 0.60 0.60 0.52 ***** 0.74
2.00 0.89 476.59 * 0.012 0.61 0.42 0.72 0.72 0.61 '°*** 0.89
File Opened for writing:roadpipe.bwt
save results to Hw/Tw file:roadpipe.bwt
Exit KCBW Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 5.30h
Page 1
pondpipe.txt
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
Water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 5.30h
File opened for Reading:pondpipe.bwp
File opened for writing:pondpipe.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:pondpipe.bwp
surcharge condition at intermediate junctions
Tailwater Elevation:469. feet
Discharge Range:0.5 to 2. step of 0.5 [cfs]
overflow Elevation:474.78 feet
Weir:NONE
upstream velocity:l. feet/sec
PIPE N0. 1: 39 LF - 12"CP @ 2.41% OUTLET: 467.34 INLET: 468.28 INTYP: 5
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
t,t t,t,t,t,r**,t*,r,t,t,t,t*,ts,t,t,t,t,t*tr,t,r,t**,t,t,r,t t***,t******,t,t,t,t,t
0.50 0.73 469.01 0.012 0.30 0.20 1.66 1.66 0.73 0.73 0.38
1.00 0.78 469.06 * 0.012 0.43 0.28 1.66 1.66 0.74 0.78 0.57
1.50 0.87 469.15 * 0.012 0.52 0.35 1.66 1.66 0.76 0.87 0.73
2.00 0.99 469.27 * 0.012 0.61 0.40 1.66 1.66 0.79 0.99 0.89
File Opened for writing:pondpipe.bwt
5ave results to Hw/Tw file:pondpipe.bwt
Exit ic Bw Program
KZNG COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 5.30h
Page 1
roadpipe.txt
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water dnd and Re50UrCe5 DiVision
BACKWATER ANALYSIS PROGRAM
version 5.30h
File opened for Reading:roadpipe.bwp
File opened for writing:roadpipe.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:roadpipe.bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:471.15 feet
ischarge Range:0.5 to 2. Step of 0.5 [cfs]
Overflow Elevation:478.7 feet
Weir:NONE
upstream velocity:l. feet/sec
PIPE NO. 1: 16 LF - 12"CP @ 8.31% OUTLET: 469.08 INLET: 470.41 INTYP: 5
UNC NO. 1: OVERFLOW-EL: 473.51 BEND: 90 DEG DIA/WIDTH: 2.5 Q-RATIO: 0.00
Q(CFS) HW(FT) HW ELEV. N-FAC DC DN TW DO DE HWO HWI
0.50 0.76 471.17 * 0.012 0.30 0.15 2.07 2.07 0.74 0.76 0.36
1.00 0.81 471.22 * 0.012 0.43 0.21 2.07 2.07 0.74 0.81 0.56
1.50 0.89 471.30 * 0.012 0.52 0.25 2.07 2.07 0.74 0.89 0.74
2.00 1.01 471.42 * 0.012 0.61 0.29 2.07 2.07 0.74 1.01 0.91
PIPE N0. 2: 58 LF - 12 CP @ 2.57% OUTLET: 470.51 INLET: 472.00 INTYP: 5
7UNC NO. 2: OVERFLOW-EL: 474.92 BEND: 0 DEG DIA/WIDTH: 2.5 Q-RATIO: 0.00
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
a**ft********
0.50 0.38 472.38 * 0.012 0.30 0.20 0.66 0.66 0.30 ***** 0.38
1.00 0.56 472.56 * 0.012 0.43 0.28 0.71 0.71 0.43 *** 0.56
1.50 0.69 472.69 * 0.012 0.52 0.34 0.79 0.79 0.52 * 0.69
2.00 0.81 472.81 * 0.012 0.61 0.40 0.91 0.91 0.61 ***rt 0.81
PZPE NO. 3: 178 LF - 12 CP @ 2.02% OUTLET: 472.10 INLET: 475.70 INTYP: 5
Q(CFS) HW(FT) HW ELEV. rt N-FAC DC DN TW DO DE HWO HWI
ft ft*****************ft*art****
0.50 0.38 476.08 * 0.012 0.30 0.21 0.28 0.28 0.30 ***** 0.38
1.00 0.57 476.27 rt 0.012 0.43 0.29 0.46 0.46 0.43 ***** 0.57
1.50 0.74 476.44 * 0.012 0.52 0.36 0.59 0.59 0.5Z ***** 0.74
2.00 0.89 476.59 * 0.012 0.61 0.42 0.71 0.71 0.61 ***rt* 0.89
File opened for writing:roadpipe.bwt
Save results to Hw/Tw file:roadpipe.bwt
Exit KCBw Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources DlVlSIOn
BACKWATER ANALYSIS PROGRAM
version 5.30h
Page 1
tankpipe.txt
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
Water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 5.30h
File opened for Reading:tankpipe.bwp
File Opened for writing:tankpipe.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:tankpipe.bwp
surcharge condition at intermediate junctions
Tailwater Elevation:470. feet
Discharge Range:0.5 to 5.5 Step of 0.5 [cfs]
overflow Elevation:473.79 feet
weir:NONe
Upstream Velocity:l. feet/sec
PIPE NO. 1: 125 LF - 12"CP @ 0.38% OUTLET: 466.80 INLET: 467.28 INTYP: 5
UNC N0. 1: OVERFLOW-EL: 471.80 BEND: 45 DEG DIA/WIDTH: 2.5 Q-RATIO: 0.40
I Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
0.50 2.76 470.04 0.012 0.30 0.32 3.20 3.20 2.75 2.76 0.40
1.00 2.84 470.12 0.012 0.43 0.46 3.20 3.20 2.80 2.84 0.59
1.50 2.98 470.26 * 0.012 0.52 0.58 3.20 3.20 2.91 2.98 0.75
2.00 3.19 470.47 0.012 0.61 0.70 3.20 3.20 3.06 3.19 0.90
2.50 3.45 470.73 * 0.012 0.68 0.87 3.20 3.20 3.24 3.45 1.05
3.00 3.78 471.06 * 0.012 0.75 1.00 3.20 3.20 3.48 3.78 1.21
3.50 4.16 471.44 0.012 0.80 1.00 3.20 3.20 3.75 4.16 1.41 1
OVERFLOW ENCOUNTERED AT 4.00 CFS DISCHARGE **************** Y U V'v
OVERFLOW CONDITIONS CALCULATED ASSUMING SURCHARGE CONDITIONS ******
4.50 5.10 472.38 * 0.012 0.89 1.00 3.20 3.20 4.42 5.10 1.89 "
r 7
5.00 5.66 472.94 * 0.012 0.92 1.00 3.20 3.20 4.82 5.66 2.17
C 1
5.50 6.27 473.55 * 0.012 0.94 1.00 3.20 3.20 5.26 6.27 2.49
PIPE NO. 2: 32 LF - 12 CP @ 1.28% OUTLET: 467.38 INLET: 467.79 INTYP: 5 ` U" '''' `
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI ,(/,, /rA
t,t,t,t i t,t t n t n,r n t*,r,ti frtt,r r*,rt n,t,r* C vK.SiXJ : r
0.36 2.26 470.05 * 0.012 0.25 0.20 2.66 2.66 2.26 2.25 0.31 ` }
0.71 2.34 470.13 * 0.012 0.36 0.28 2.74 2.74 2.34 2.34 0.47 I tl. .
1.07 2.53 470.32 i° 0.012 0.44 0.34 2.88 2.88 2.50 2.53 0.60
1.43 2.79 470.58 * 0.012 0.51 0.40 3.09 3.09 2.72 2.79 0.72
1.79 3.12 470.91 * 0.012 0.57 0.45 3.35 3.35 3.01 3.12 0.83
2.14 3.52 471.31 0.012 0.63 0.50 3.68 3.68 3.37 3.52 0.94
2.50 4.00 471.79 * 0.012 0.68 0.55 4.06 4.06 3.78 4.00 1.06
2.86 4.56 472.35 * 0.012 0.73 0.59 4.50 4.50 4.26 4.56 1.17
3.21 5.19 472.98 * 0.012 0.77 0.64 5.00 5.00 4.81 5.19 1.31
3.57 5.89 473.68 * 0.012 0.81 0.69 5.56 5.56 5.42 5.89 1.47
OVERFLOW ENCOUNTERED AT 3.93 CFS DISCHARGE ****'`***`****''* ' S C DD1 nW
3.93 6.66 474.45 * 0.012 0.85 0.75 6.17 6.17 6.09 6.66 1.64 J
File opened for writing:tankpipe.bwt
O
save results to Hw/Tw file:tankpipe.bwt
Exit KCBW Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
r Water and Land Resources Division n ", r i
V f!/•
BACKWATER ANALYSIS PROGRAM
version 5.30h
Page 1
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APPENDIX E
RETENTIONIDETENTION FACILITY
SUMMARY SHEET & SKETCH
ENGINEERING PLAN
IN LIEU OF MINOR FLOODPLAIN STUDY
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
STORMWATER FACILITY SUMMARY SHEET
Development de Date n,
Location Z(02 I 1 t.( f
ENGINEER DEVELOPER
Name (pr,y Name ',,,,, L,n(
Firm _. 1 r c . Firm T+
i Address 7,QC.,. - , Q/) ga,l- Address g Q
rkt.l . 1/ 'D7 c, 2
Phone (_S' _ q - / (" Phone !/1—
I
Developed Site: Acres 2 0 5 Number of lots `Z3
Number of detention facilities on site: Number of infiltration facilities on site:
1 ponds ponds
vaults vaults
tanks (r sh.--oF-•"a•j tanks
Flow control provided in regional facility(give location)
No flow control required x Exemption number . T-. Q. , S _
Downstream Drainage Basins
Immediate Major Basin
Basin A N R la c lc 2,u e,
Basin B
Basin C //
Basin D S
Number&type of water quality facilities on site:
biofiltration swale(regular/wet/or sand filter(basic or large?)
continuous inflow?) sand filter, linear(basic or large?)
combined detention/WQ pond sand filter vault(basic or large?)
WQ portion basic or large?)
combined detention/wetvault stormwater wetland
compost filter wetpond(basic or large?)
filter strip wetvault
flow dispersion
farm management plan
landscape management plan
oil/water separator(baffle or coalescing plate?)
catch basin inserts: Manufacturer
pre-settling pond
pre-settling structure: Manufacturer
flow-splitter catchbasin
DESIGN INFORMATION INDIVIDUAL BASIN
IA (t.) IBf I c(W) Iol'S
Water Quality design flow T/k
Water Quality treated volume or wetpond Vr
IDESIGN TOTAL INDNIDUAL BASIN IINFORMATION, cont'd
1998 Surface Water Design Manual 9/1/98
1
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
IDrainage basin(s) A (( B ( C D $
Onsite area
y (
I Offsite area
Type of Storage Facility fi'
Live Storage Volume 1. I-t ,' 7..Q e ('-'
Predeveloped Runoff Rate 2-year n S k
I 10-year V2..Q(p ^ t..i u
I 100-year 19 3 " b.l t
Developed runoffrate ( 2-year i. 1,1 ` l7.=j.(r
I 0-year I 58 '- I .I le
100-year Q,7 p .. .3Q
Type of restrictor Q, .. r•
Size of orifice/restriction No. 1 7. i,yi. _Q.In I i,w _)
No.2 i,13 im.R') 0.iw 3)
No. 3
No.4
FLOW CONTROL&WATER QUALITY FACILITY SUMMARY SHEET SKETCH
All detention,infiltration and water quality facilities must include a sketch per the following criteria:
1. Heading for the drawings should be located at the top of the sketch(top right-hand corner).
The heading should contain:
North arrow(point up or to left) D9#
Plat name or short plat number Address(nearest)
Date drawn(or updated) Thomas Brothers page,grid number
2. Label CBs and MHs with the plan and profile designation. Label the control structure in writing or abbreviate
with C.S. Indicate which structures provide spill control.
3. Pipes--indicate:
Pipe size
Pipe length
Flow direction
Use s single heavyweight line
4. Tanks--use a double,heavyweight line and indicate size(diameter)
5. Access roads
Outline the limits ofthe road
I Fill the outline with dots if the road is gravel. Label in writing if another surface.
6. Other Standard Symbols:
Bollards: • • • •
Rip rap o00000
000000
Fences --x---x---x---x---x---x---
Ditches –D--CD CD-CD
7. Label trash racks in writing.
8. Label all streets with the actual street sign designation. If you don't know the actual street name,consult the plat
map.
9. Include easements and lot lines or tract limits when possible.
10. Arrange all the labeling or writing to read from left to right or from bottom to top with reference to a properly
oriented heading.
I 1. Indicate driveways or features that may impact access,maintenance or replacement.
9/1/98 1998 Surface Water Design Manual
2
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APPENDIX D
MAINTENANCE REQUIREMENTS
FOR
PRIVATELY MAINTAINED DRAINAGE FACILITIES
MAINTENANCE AND OPERATIONS MANUAL
FOR PRIVATELY MAINTAINED DRAINAGE FACILITIES
ADDRESS: 16217 114th Avenue SE
Renton, Washington
RETENTION/DETENTION FACILITIES
The purpose of the detention pond and tank is to reduce the rate of runoff from the developed
portions of the property and frontage. Water can flow freely into the pond and tank, but orifices
in the outflow risers restrict the outflows. When the inflow exceeds the capacity of the orifices,
the excess water is "stored" in the pond or tank, and released slowly after the storm abates.
In order to function properly, the facilities must be kept free of accumulated sediment. The
outlet pipes also must be kept clean, as even a partial blockage could significantly impact the
ability of a facility to store runoff. The facilities should be visually inspected for sediment
accumulation and blockages at least once each year and also after every major storm greater
than or equal to a 10-year return frequency.
CONVEYANCE SYSTEMS
Pipes transport runoff from one place to another, in this case from catch basins to the pond or
tank, then to the downstream drainage system. To work properly, pipes must be kept free of
silt and other debris. If pipes become blocked, surFace flooding will usually occur.
CATCH BASINS AND AREA DRAINS
Catch basins collect surface drainage and direct it into storm conveyance pipes. They help
prevent downstream drainage problems by trapping sediment and other debris that would
otherwise flow downstream with the runoff. It is important to keep catch basins clean so
accumulated silt is not flushed out during a significant storm. Also, if the outflow pipe becomes
blocked with debris, surface flooding will usually occur. All catch basins should be inspected at
least once each year and after major storms.
Area drains convey runoff directly into conveyance pipes. To prevent surface flooding, their
surface grates must be kept free of litter and debris. If dirt or other sediment gets into the pipes
and they become blocked, the pipes will need to be cleaned, either manually or using a Vactor
truck.
The following tables identify maintenance issues, which should be addressed re ularl9Y
describing possible problems with the drainage system and their respective solutions.
1
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
APPENDIX A
MAINTENANCE STANDARDS FOR
PRIVATELY MAINTAINED DR.AINAGE FACILITIES
N0. 1 -DETENTION PONDS
Maintenance Defect Conditions When Maintenance Results Expected When
Component Is Needed Maintenance Is Performed
Genera Trash 8 Debris Any trash and debris which exceed 1 cubic foot Trash and debris cieared 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.
Poisonous Vegetation Any poisonous or nuisance vegetation which No dangerof poisonous vegetation
may constitute a hazarcl to County personnel or where County personnel orthe
the public. public might normally be.
Coordination with Seattle-King
County Health Departrnent)
Pollution Oil,gasoline,or other contaminants of one No contaminants present other than
gallon or more or any amount found that could: a surface film. (Coordination with
1)cause damage to plant,animat,or marine tife; Seattle/King Counry Health
2)constitute a fire hazard;or 3)be flushed Departrnent)
downstream during rain storms.
Unmowed Grass/If facility is located in private residential area, When mowing is needed,
Ground Cover mowing is needed when grass exceeds 18 grass/ground cover should be
inches in height. In other areas,the general mowed to 2 inches in height.
policy is to make the pond site match adjacent Mowing of selected higher use
ground cover and temain as long as there is no areas rather than the entire slope
interference with the function of the facility. may be acceptable for some
situations.
Rodent Holes Any evidence of rodent holes if faciliry is acUng Rodents destroyed and dam or
as a dam or berm,or any evidence of water berm repaired. (Coordination with
piping through dam or berm via rodent holes. Seattle/King County Health
Department)
Insects When insects such as wasps and homets InsecLs destroyed or removed from
interfere with maintenance activities.site.
Tree Growth Tree growth does not allow maintenance access Trees do not hinder maintenance
or interferes with maintenance activity(i.e.,slope activities. Selectively cultivate trees
mowing,silt removal,vactoring,or equipment such as alders for firewood.
movements). If trees are not interfering with
axess,leave trees alone.
Side Slopes of Pond Erosion Eroded damage over 2 inches deep where Slopes should be stabilized by
cause of damage is still present or where there using appropnate erosion control
is potential for continued erosion. measure(s);e.g.,rock
reinforcement,planting of grass,
compaction.
Storage Area Sediment Accumulated sediment that exceeds 10%of the Sediment cleaned out to designed
designed pond depth. pond shape and depth;pond
reseeded if necessary to control
erosion.
Pond Dikes Settlements Any part of dike which has settled 4 inches lower Dike should be built back to the
than the design elevation. design elevation.
Emergency Rock Missing Only one layer of rock exists above native soil in Replace rocks to design standards.
Overflow/Spillway area five square feet or larger,or any exposure
of native soil at the top of out flow path of
spillway. Rip-rap on inside slopes need not be
replaced.
1998 Surface Water Design Manual 9/1/98
A-1
APPENDIX A MAINTENANCE STANDARDS FOR PRIVATELY MAINTAINED DRAINAGE FACII.ITIES
NO.3-CLOSED DEfENT10N SYSTEMS(PIPES/TANKS)
Maintenance Defect Conditions When Malntenance is Needed Results Expected When
Component Maintenance is Performed
Storage Area Ptugged Air Vents One-half of the cross section of a vent is blocked at Vents free of debris and
any point with debris and sediment sediment
Debris and Accumulated sediment depth exceeds 10 0 of the All sediment and debris
Sediment diameter of the storage area for'rz tength of storage removed from storage area.
vault or any point depth exceeds 15'/0 of diameter.
Example:72-inch storage tank would require cleaning
when sediment reaches depth of 7 inches for more
than 3 length of tank.
Joints Between Any crack allowing material to be transported into All joint between tank/pipe
TanWPipe Section faciliy sections are sealed
Tank Pipe Bent Any part of tank/pipe is bent out of shape more than Tank/pipe repaired or replaced
Out of Shape 109'0 of iYs design shape to design.
Manhole Cover Not in Place Cover is missing or only partially in place.Any open Manhole is closed.
manhole requires maintenance.
Lodcing Mechanism cannot be opened by one maintenance Mechanism opens with proper
Mechanism Not person with proper tools.Bolts into frame have less tools.
Working than Yz inch of thread(may not apply to self-locking
lids.)
Cover Difficult to One maintenance person cannot remove lid after Cover can be removed and
Remove applying 801bs of lift. Intent is to keep cover from reinstalled by one maintenance
sealing off access to maintenance.person.
Ladder Rungs King County Safety Office and/or maintenance person Ladder meets design standards
Unsafe judges that ladder is unsafe due to missing rungs,allows maintenance person safe
misalignment,rust,or cracks. access.
Catch Basins See"Catch Basins"Standards No.5 See"Catch Basins"Standards
No.5
1998 Surface Water Design Manual 9/I/98
A-3
APPENDIX A MAINTENANCE STANDARDS FOR PRIVATEI,Y MAINTAINED DRAINAGE FACILTTIES
NO.4-CONTROL STRUCTURE/FLOW RESTRICTOR
Maintenance Defect Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
General Trash and Debris Distance between debris build-up and bottom of All trash and debris removed.
Includes Sediment) orifice plate is less than 1-1/2 feet.
Structural Damage Structure is not securely attached to manhole wall SVucture securely attached to
and outlet pipe structure should support at least wall and ouUet pipe.
1,000 Ibs of up or down pressure.
Structure is not in upright position(aliow up to Structure in correct position.
10%from plumb).
ConnecGons to ouUet pipe are not watertight and Connectlons to outlet pipe are
show signs of rust. water tight;structure repaired or
replaced and works as
designed.
Any holes—other than designed holes—in the Structure has no holes other
structure. than designed holes.
Cleanout Gate Damaged or Missing Cleanout gate is not watertight or is missing. • Gate is watertight and works as
designed.
Gate cannot be moved up and down by one Gate moves up and down easily
maintenance person.and is watertight.
Chain leading to gate is missing or damaged.Chain is in place and works as
designed.
Gate is rusted over 50'/0 of its surface area. Gate is repaired or replaced to
meet design standards..
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
blocking the plate. and works as designed.
Overflow Pipe Obstructions Any trash or debris blocking(or having the Pipe is iree of all obstructions
potential of blocking)the overflow pipe. and works as designed.
Manhole See"Closed Detention Systems"Standards No.3 See"Closed Detention Systems'
Standards No.3
Catch Basin See"Catch Basins"Standards No.5 See'Catch Basins"Standards
No.5
9/1/98 1998 Surface Water Design Manual
A-4
APPENDIX A MAINTENANCE STANDARDS FOR PRIVATELY MAINTAINED DRAIIVAGE FACILITIES
NO. 5-CATCH BASINS
Maintenance Defect Conditions When Maintenance is Needed Results Expected When
Component Maintenance is pertormed
General Trash 8 Debris Trash or debris of more than 1/2 cubic foot which is No Trash or debris located
Indudes Sediment) located immediately in front of the catch basin immediately in front of catch
opening or is blocking capaciry of the basin by basin opening.
more than 10%
Trash or debris(in the basin)that exceeds 1/3 the No trash or debris in the catch
depth from the bottom of basin to invert the lowest basin.
pipe into or out of the basin.
Trash or debris in any inlet or outlet pipe blocking Inlet and ouUet pipes free of
more than 1/3 of its height. trash or debris.
Dead animals or vegetation that could generate No dead animals or vegetation
odors that could cause complaints or dangerous present within the catch basin.
gases(e.g.,methane).
Deposits of garbage exceeding 1 cubic foot in No condition present which
volume would attract or support the
breeding of insects or rodents.
Structure Damage to Comer of frame extends more than 3/4 inch past Frame is even with curb.
Frame 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:Jer than 1/4 inch(intent is to make sure cracks.
all material is running into basin).
Frame not sitting flush on top slab,i.e.,separation Frame is sitting flush on top
of more than 3/4 inch of the frame from the top slab.
slab.
Cracks in 6asin Walls/ Cracks wider than 1/2 inch and longer than 3 feet, Basin replaced or repaired to
Bottom any evidence of soil particles entering catch basin design standards.
through cracks,or maintenance person judges that
structure is unsound.
Cracks wider than 1/2 inch and longer than 1 foot No cracks more than 1/4 inch
at the joint of any inleU ouUet pipe or any evidence wide at the joint of inleVouUet
of soil paRides entering catch basin through pipe.
cracks.
SedimenU Basin has settled more than 1 inch or has rotated Basin replaced or repaired to
Misalignment more than 2 inches out of alignment. design standards.
1998 Surface Water Design Manual 9/1/98
A-5
NTAINED DRAINAGE FACILTI'IESAPPENDIXAMAINTENANCESTANDARDSFORPRIVATELYMAI
NO. 5-CATCH BASINS(CON71NUED
Maintenance Defect Conditions When Maintenance is Needed Results Expected When
Component Maintenance is performed
Fire Hazard Presence of chemicals such as natural gas,al and No flammable chemicais
gasoline. present.
i
Vegetation Vegetation growing across and blocking more than No vegetation blocking opening
10%of the basin opening. to basin.
Vegetation growing in inleUouUet pipe jants that is No vegetation or root growth
more than six inches tall and less than six inches present.
apart.
Pollution Nonflammable chemicals of more than 1/2 cubic foot No pollution present other than
per three feet of basin length. surface film.
Catch Basin Cover Cover Not in Place' Cover is missing or only partially in place.Any open Catch basin cover is closed I
catch basin requires maintenance.
Locking Mechanism Mechanism cannot be opened by on maintenance Mechanism opens with proper
Not Working person with proper tools.Bolts into frame have less tools.
than 1/2 inch of thread.
Cover Difficult to One maintenance person cannot remove lid after Cover can be removed by one
Remove applying 80 Ibs.of lift;intent is keep cover from maintenance person.
sealing off access to maintenance.
Ladder Ladder Rungs Ladder is unsafe due to missing rungs,misalignment, Ladder meets design standards
Unsafe rust,cracks,or sharp edges. and allows maintenance person
safe access.
Metal Grates Grate with opening wider than 7/8 inch. Grate opening meets design
ff p,ppiicable) standards.
Trash and Debris Trash and debris that is blocking more than 20%of Grate free of trash and debris.
grate surface.
Damaged or Grate missing or broken member(s)of the grate.Grate is in place and meets
Missing. design standards.
NO. 6 DEBRIS BARRIERS(E.G.,TRASH RACKS)
Results Ex ected WhenMaintenanceDefectConditionWhenMaintenanceisNeededp
Components Maintenance is Pertormed.
General Trash and Debris Trash or debris that is plugging more than 20%of Barrier clear to receive capacity
the openings in the barrier. flow.
Metal Damaged/Missing Bars are bent out of shape more than 3 inches. Bars in place with no bends more
Bars. than 3/4 inch.
Bars are missing or entire barrier missing. Bars in place according to
design.
Bars are loose and rust is causing 50%deterioration Repair or replace barrier to
to any part of barrier. design standards.
9/1/98 1998 Surface Water Design Manual
A-6
APPENDIX A MAINTENANCE STANDARDS FOR PRIVATEI,Y MAINTAINED DRAINAGE FACILITTES
N0. 10-CONVEYANCE SYSTEMS(PIPES& DITCHES)
Maintenance Defect Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Pipes Sediment&Debris Accumulated sediment that exceeds 20%of the Pipe cleaned of ail sediment
diameter of the pipe. and debris.
Vegetation Vegetation that reduces free movement of water All vegetaUon removed so water
through pipes. flows freely through pipes.
Damaged Protective coating is damaged;rust is causing Pipe repaired or replaced.
more than 50%deterioration to any part of pipe.
Any dent that decreases the cross section area of Pipe repaired or replaced.
pipe by more than 20%.
Open Ditches Trash&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 atl
design depth.sediment and debris so that it
matches design.
Vegetation Vegetation that reduces free movement of water Water flows freely through
through ditches. ditches.
Erosion Damage to See"Ponds"Shandard No. 1 See"Ponds"Standard No.1
Slopes
Rock Lining Out of Maintenance person can see native soil beneath Replace rocks to design
Place or Missing(If the rock lining. standards.
Applicable).
Catch Basins See"Catch Basins:Standard No.5 See"Catch Basins"Standard
No.5
Debris Barriers See"Debris Barriers"Standard No.6 See"Debris Barriers"Standard
e.g.,Trash Rack)No.6
N0. 11 -GROUNDS(LANDSCAPING)
Maintenance Defect Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
General Weeds Weeds growing in more than 20%of the landscaped Weeds present in less than 5%
Nonpoisonous) area(trees and shrubs only). of the landscaped area.
Safety Hazard Any presence of poison ivy or other poisonous No poisonous vegetation
vegetation. present in landscaped area.
Trash or Litter Paper,cans,botttes,totaling more than 1 cubic foot Area clear of litter.
within a landscaped area(trees and shrubs only)of
1,000 square feet.
Trees and Shrubs Damaged Limbs or parts of trees or shrubs that are split or Trees and shrubs with less than
broken which affect more than 25%of the total 5%of total foliage with split or
foliage of the tree or shrub. broken limbs.
Trees or shrubs that have been blown down or Tree or shrub in place free of
knocked over. injury.
Trees or shrubs which are not adequately supported Tree or shrub in place and
or are leaning over,causing exposure of the roots. adequately supported;remove
any dead or diseased Vees.
1998 Surface Water Design Manual 9/1/98
A-9
APPENDIX A MAIN'TENANCE STANDARDS FOR PRIVATELY MAINTAINED DRAINAGE FACII.TI'IES
N0. 12-ACCESS ROADSJ EASEMENTS
Maintenance Defect Condltion When Maintenance is Needed Results Expected When
Component Maintenance is Performed
General Trash and Debris Trash and debris exceeds 1 cubic foot per 1,000 Roadway free of debris which
square ieet i.e.,trash and debris would fill up could damage tires.
one standards size garbage can.
Biodced Roadway Debris which could damage vehicle tires(glass Roadway free of debris which
or metal). could damage tires.
Any obstruction which reduces clearance above Roadway overhead clear to 14 feet
i
road surface to less than 14 feet high.
Any obstruction restricting the access to a 10 to Obstruction removed to allow at
12 foot width for a distance of more than 12 feet least a 12 foot access.
or any point restricting access to less than a 10
foot width.
Road Surface Setdement,Potholes, When any surface defect exceeds 6 inches in Road surface uniformly smooth
Mush Spots,Ruts depth and 6 square feet in area.In general,any with no evidence of settlement,
surface defect which hinders or prevents potholes,mush spots,or ruts.
maintenance access.
Vegetation in Road Weeds growing in the road surface that are Road surface free of weeds taller
Surtace more than 6 inches tall and less than 6 inches than 2 inches.
tall and less than 6 inches apart within a 400-
square foot area.
Modular Grid Build-up of sediment mildly contaminated with Removal of sediment and disposal
Pavement petroleum hydrocarbons. in keeping with Health Department
recommendations for mildly
contaminated soils or catch basin
sediments.
Shoulders and Erosion Damage Erosion within 1 foot of the roadway more than 8 Shoulder free of erosion and
Ditches inches wide and 6 inches deep. matching the surrounding road.
Weeds and Brush Weeds and brush exceed 18 inches in height or Weeds and brush cut to 2 inches
hinder maintenance access.in height or cleared in such a way
as to allow maintenance access.
9/l/98 1998 Surface Water Design Manual
A-10
APPENDIX E
RETENTION/DETENTION FACILITY
SUMMARY SHEET & SKETCH
ENGINEERING PLAN
IN LIEU OF MINOR FLOODPLAIN STUDY
I
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
STORMWATER FACILITY SUMMARY SHEET
Development d P G Date
Location (,(1 I I'h ,'4 P ,t (,y
ENGINEER DEVELOPER
r- Name r r Name
Firm _. r c , Firm
Address 7 Cj' ,S.{. S. PQ gn, I-jS- I Address glp t-I l.b, .C--
S qr1Gt,L . 1 07 r /1Ai'PS ,(1! 3 a I
Phone {2 9 - l l t (^ Phone ,- —-
Developed Site: Acres 2•0 5 Number of lots `(3
Number of detention facilities on site: Number of infiltration facilities on site:
1 ponds ponds
vaults
J__tanks ( S w1--oF-va..j
Flow control provided in regional facility(give tocation)
No flow control required x Exemption number i. _M. }y pQ+ , .S r„nS .Downstream Drainage Basins
Immediate Major Basin
Basin A N Ic r I (Z,ue..
Basin B I
Basin C /
Basin D S I ` _ J
Number&type of water quality facilities on site:
biofiltration swale(regular/wet/or sand filter(basic or large?)
continuous inflow?) sand filter, linear(basic or large?)
combined detention/WQ pond sand filter vault(basic or large?)
WQ portion basic or large?)
combined detention/wetvault stonnwater wetland
compost filter wetpond(basic or large?)
filter strip wetvault
flow dispersion
farm management plan
landscape management plan
oilhvater separator(baffle or coalescing plate?)
catch basin inserts: Manufacturer
pre-settling pond
pre-settling structure: Manufacturer
flow-splitter catchbasin
DESIGN INFORMATION INDIVIDUAL BASIN
I I a fr)I B fEl 1 c(w D/'Sl _ I
Water Quality design flow y J
Water Quality treated volume or vetpond Vr I
DESIGN TOTAL INDNIDUAL BASIN j
INFORMATION, cont'd
1998 Surface Water Design Manual q qg
1 I
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
I Drainage basin(s) A rJ B (E C(w)_ . D (S)
Onsite area 2.C
Offsite area t./nS
Type of Storage Facility j-Q,, py --
Live Storage Volume q r Z(Q r
Predeveloped Runoff Rate 2-year 0 I C
10-year D,1'Db P.S D.US c'
100-year n.f P f • I 1 v f
Developed runoff rate 2-year 1 p.t n.I r,
10-year 9. i I I'{ !,jJpl f
100-year 7f- (',FS f.a
Type ofrestrictor fl. ) ,r,.)
Size of orifice/restriction No. 1 G}" `f.,,<' ''
No.2 I.I ' 2 . '
I I No. 3
No.4
FLOW CONTROL&WATER QUALITY FACILITY SUMMARY SHEET SKETCH
All detention,infiltration and water quality facilities must include a sketch per the following criteria:
1. Heading for the drawings should be located at the top of the sketch(top right-hand corner).
The heading should contain:
North arrow(point up or to left) D9#
Plat name or short plat number Address(nearest}
Date drawn(or updated) Thomas Brothers page, grid number
2. Label CBs and MHs with the plan and profile designation. Label the controi structure in writing or abbreviate
with C.S. Indicate which structures provide spill control.
3. Pipes-- indicate:
Pipe size
Pipe length
Flow direction
Use s single heavyweight line
4. Tanks--use a double,heavyweight line and indicate size(diameter)
5. Access roads
Outline the limits of the road
Fill the outline with dots if the road is gravel. Label in vriting if another surface.
6. Other Standard Symbols:
Bollards: • • • •
Rip rap o00000
000000
Fences --x---x---x---x---x---x---
Ditches D CD CD--CD
7. Label trash racks in writing.
8. Label all streets with the actual street sign designation. If you don't know the actual street name,consult the plat I
map.
9. Include easements and lot lines or tract limits when possible.
0. Arrange all the labeling or vriting to read from left to right or from bottom to top with reference to a properly
oriented heading.
1 1. Indicate driveways or features that may impact access, maintenance or replacement.
9/1/98 1998 Surface Water Design Manual
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I
APPENDIX F
SENSITIVE AREAS STUDY
d
V!/t/' o c /c.
Delineation/Mitigation/Restoration/Habitat Creation/PermitAssistance 9505 19th Avenue S.E.
Suite 106
Everett, Washington 98208
425)337-3174
Fax (425) 337-3045
SENSITIVE AREA STUDY
FOR
Lund 114th Ave ue
King County, WA
Wet(and Resources, Inc. Project #04153
Prepared By:
Wetfond Resources, Inc.
9505 19th Ave. SE
Suite 106
Everett, WA 98208
i 425) 337-3174
For:
Gu and Fran LundY
810 4' Street
Port Angetes, WA 98362
June 7, 2004
Revision 1: September 27, 2004
TABLE OF CONTENTS
SITE DESCRIPTION 2
PROJECT DESCRIPTION
PROPOSED SENSITIVE AREA IMPACTS AND MITIGATION 2
WETLAND CLASSIFICATION - COWARDIN SYSTEM 3
WETLAND CLASSIFICATION - KING COUNTY 3
ENVIRONMENTALLY $ENSITIVE AREAS 3
WETLAND DETERMINATION REPORT 4
BOUNDARY DETERMINATION FINDINGS 5
FUNCTIONS AND VALUES ANALYSIS 6
WILDLIFE 7
USE OF THIS REPORT 7
REFERENCES 9
FIELD DATA 10
SENSITIVE AREA STUDY MAP 1/1
I 1
SITE DESCRIPTION
Wetlond Resources, Inc. conducted a wetland delineation on May 10, 2004 to locate
jurisdictional wetlands on the approximate 2 acre site located at 16217 114"'
Avenue SE in King County, Washington. The site is located as portion of Section 29,
Township 23N, Range 5E, W.M. The applicant is proposing a multi-lot residential
development for this property.
This site is generally flat with a slight depression in the southern portion. One
single-family residence and associated infrastructure is located on the northern
portion of the site. Surrounding land use is comprised of single-family residences.
Access is from the east, via 114' Avenue SE. The northern portion of the site is
occupied by maintained lawn associated with the existing single-family residence.
The southern part of the site is vacant land, with vegetation represented by sapling
black cottonwood, Scotch broom, Himalayan blackberry, and tall fescue. Three
wetlands and an intermittent stream are tocated on the subject site. Wetlands A, -
B, and C, are emergent wetlands tocated in the southern portion of the site.
Wetland A is a Class 3 wetland. Regulated Class 3 wettands in King County typically
receive 25-foot protective buffers. Wetlands B and C are less than 2,500 square feet
in size. Urban Class 3 wetlands less than 2,500 square feet in size in are unclassified
in King County. The stream is located in a man-made ditch paralleling the sites'
western property boundary and begins approximately 112 feet north of the
southwest property corner. This point is the top of the drainage sub-basin with
the stream flowing north and roadside ditch flowin north (per Taylor Engineering
Consultants draina e anat sis . This Class 3 stream is desi nated a 25-footY )
protective buffer from its flagged OHWM.
PROJECT DESCRIPTION
PROPOSED $ENSITIVE AREA IMPACTS AND MITIGATION
The applicant is proposing a multi lot devetopment on this property. To
accommodate portions of Lot 7 and Drainage tract 2, the applicant is proposing to
reduce a total of 609 square feet (374 + 235) of the buffer of Wetland A. Mitigation
for this buffer reduction is offered through desi nating a total of 1,119 square feet
771 + 284 + 64) of area as additional buffer. This represents a stightly better than
2:1 ratio of additional buffer to reduced buffer. The buffer areas proposed to be
reduced and the areas proposed to be additional buffer contain similar species and
provide equivalent functions and values. The designation of additional area as
buffer at a better than 2:1 ratio should maintain or improve functions and values for
the site. in addition to buffer averaging, the applicant is proposin to fill the
unclassified Wetlands B and C.
2 I
Impact and Mitigation Tabte
Impact Mitigation
Buffer Averaging Reduction Buffer Averaging Addition 1,119 SF
609 SF total Greater than 2:1 ratio
WETLAND CLASSIFICATION - COWARDIN SYSTEM
Accordin to the Cowardin System, as described in Classification of Wetlands and
Deepwater Habitats of the United States, the on-site wetlands are classified as
follows:
Wettands A - C: Palustrine, Emergent Wetland, Persistent, Seasonatly ftooded/
Saturated.
Stream: Intermittent, Streambed, Mud
WETLAND CLASSIFICATION - KING COUNTY
Pursuant to King County Code (KCC) section 21A.06.1415, the on-site wetlands are
ctassified as follows:
Wettand A Class 3: This wetland is less than one acre in size and has one wetland
class. Class 3 Wetlands in King County typically receive 25-foot protective buffers.
Wetlands B and C: These wetlands are less than 2,500 square feet in size and have
one wetland class. In King County, urban wetlands less than 2,500 square feet in
size are not classified.
Stream: This stream is intermittent in years of normat rainfall and is not used by
salmonids. Class 3 streams are typically desi nated 25-foot protective buffers from
their flagged OHWM.
ENVIRONMENTALLY SENSITIVE AREAS
The on-site wetland and buffer shall be designated as an Environmentally Sensitive
Area (ESA). Environmentally Sensitive Areas are not to be disturbed in compliance
with Kin County's restrictions. Concurrent with future development proposals,
Sensitive Area Signs will be required and shall be installed no greater than 150 feet
apart with minimum of one per lot. An example of a Sensitive Areas Si n is as
follows:
3
ENVIRONMENTALLY SENSITIVE AREA
THIS WETLAND IS PROTECTED TO PROVIDE WILDLIFE HABITAT AND
MAINTAIN WATER QUALITY
PLEASE DO NOT DISTURB THIS VALUABLE RESOURCE
BUILDING SETBACK
Under KCC 21A.24.200 Building Setbacks, unless otherwise provided, buildin s and
other structures shall be set back a distance of 15 feet from the edges of all
sensitive area buffers or from edges of all sensitive areas, if no buffers are required.
The following may be allowed in the buitding setback area:
3) Landscaping;
4) Uncovered Decks;
5) Building overhan s if such overhangs do not extend more than 18 inches into
the setback area:
6) impervious ground surfaces, such as driveways and patios, provided that such
improvements may be subject to special drainage provisions specified in
administrative rules adopted for the various sensitive areas.
WETLAND DETERMINATION REPORT
Methodotogy
On site, routine methodology as described in the WashinQton State Wetlands
Identification and Delineation Manual (Washington State Department of Ecology
Publication #96-94, March 1997), was used for this determination, as required by
King County durin the permitting process. Under this method, the process for
makin a wetland determination is based on three sequential steps:
1) Examination of the site for hydrophytic vegetation (species present and
percentage cover).
2) If hydrophytic vegetation is found, then the presence of hydric soils is
determined.
3) Determination of the presence of wetland hydrotogy in the area examined
under the first two steps.
Vegetation Criteria
The WashinQton State Wetlands Identification and Detineation Manual, 1997 edition,
defines hydrophytic vegetation as the sum total of macrophytic plant life that
occurs in areas where the frequency and duration of inundation or soil saturation
4
Ir
produce permanently or periodically saturated soits of sufficient duration to exert
a controlling influence on the plant species present. One of the most common
indicators for hydrophytic ve etation is when more than 50 ercent of a lantPP
community consists of species rated Facultative and wetter on tists of plant
species that occur in wetlands.
Soil Criteria and Mapped Description
The Washin ton State Wetlands Identification and Delineation Manual, 1997 edition
defines hydric soils as those that formed under conditions of saturation floodin
or ponding long enough during the growing season to develop anaerobic conditions
in the upper part. Field indicators are used for determinin whether a given soil
meets the definition and criteria for hydric soils.
The soils underlying this site are mapped in the Soil Survey of KinQ County Area -
Washin ton, 1973 edition as Alderwood gravelly sandy loam, 6 to 15 percent slopes
AgC). The AgC soil unit is described as rollin with irregularly shaped areas ranging
from 10 to about 600 acres in size. The A horizon ranges from very dark brown to
dark brown. The B horizon is dark brown, grayish brown, and dark yellowish brown.
Permeability is moderately rapid in the surface layer and subsoil and very stow in
the substratum. Available water capacity is described as low. Included within this
soil unit are the-poorly drained Norma, Bellingham, Seattle, Tukwila, Shalcar soils,
and Alderwood soils that have slopes more gentle or steeper than 6 to 15 percent.
Included soil units make up no more than 30 percent of the total acrea e.
Hydrology Criteria
The Washin ton State Wetlands Identification and Delineation Manual, 1997 edition,
states that "areas which are seasonally inundated and/or saturated to the surface
for a consecutive number of days greater than or equal to 12.5% of the growing
season are wetlands, provided the soil and ve etation parameters are met. Areas
inundated or saturated between 5 and 12.5% of the growin season in most years
may or may not be wetlands. Areas saturated to the surface for less than 5% of the
growing season are non-wetlands." Field indicators are used for determining
whether wetland hydrotogy parameters are met.
BOUNDARY DETERMINATION FINDINGS
Wetland A: Wetland A is located in the south central portion of the site.
Vegetation in this wetland is represented by soft rush (Juncus effusus, FacW), reed
canarygrass (Pholaris orundinacea, FacW), sedge species (Corex spp.), and sparse
tall fescue (Festuca arundinaceo, Fac-). Several black cottonwood (Populus
balsomifero, Fac) are located near the southern edge of this wettand. Typical soils
within this wetland have a Munsell color of very dark rayish brown (10 YR 3/2) with
redoximorphic features of dark yellowish brown (10 YR 4/4) and a texture of sandy
5
loam from 0 to 18 inches below the surface. Soils were moist during our May 2004
site investigation.
Wetland B: Wetland B is located in the southwest part of the property. Vegetation
in this wettand is represented by reed canarygrass and creeping buttercup
Ranunculus repens, FacW). Soils have a Munsell color of very dark gray (10 YR 3/1)
and a texture of silt loam from 0 to 18 inches below the surface. Soils were moist
throughout during our May 2004 site visit.
Wetland C: This wetland is located in the eastern central portion of the site,
adjacent to 114' Ave SE. Vegetation in Wetland C is represented by overhanging,
sapling Bitter cherry (Prunus emarginata, FacU) and willow (Solix Sp., Fac -FacW+),
with field horsetail (Equisetum crrvense, Fac) rooted in the wetland. Soils in this
wetland have a Munselt color of very dark gray (10 YR 3/1) with redoximorphic
features of brown (10 YR 4/3) and a texture of silt loam from 0 to 18 inches below
the surface. Soils were sti htly moist during our May 2004 site visit.
Non-Wettand: Vegetation in the portions of the site mapped as non-wetland is
represented sapling black cottonwood (Popu us ba(somifera, Fac) and Bitter
cherry, with Scotch broom (Cytisus scoparius, nol/Upl), Himalayan blackberry
Rubus discolor, FacU), tall fescue (Festuccr arundinaceo, Fac-), sweet vernalgrass
Anthoxonthum odoratum, FacU+), common vetch (Vicia sativa, Upl), common
dandelion (Taroxocum officinale, FacU), and Engtish plantain (P(antago lanceoloto,
FacU+). Soils in the upland portions of the site are disturbed and appear to be
primarily comprised of fill. These soils have Munsell colors ranging from very dark
gray (10 YR 3/1) to olive (5 Y 5!3) with textures ranging from silt loam to sandy loam.
Soils in the upland portions of the property were dry to moist at the time of our
May 2004 site investigation.
There were no surface indicators of saturation or inundation in the non-wetland
areas. It appears that the areas mapped as non-wetland are not saturated for a
period greater than 5% of the rowin season, and therefore do not meet the
wetland hydrology criteria.
FUNCTIONS AND VALUES ANALYSIS
Methodology
The methodology for this functions and values assessment is based on professional
opinion developed through past field analyses and interpretation. This assessment
pertains specifically to the on-site wetland, but is typical for assessments of simitar
systems common to western Washin ton.
Functions and Values Components
Wetlands in western Washington perform a variety of ecosystem functions.
Included amon the most important functions provided by wetlands are stormwater
6
storage and itood flow attenuation, water quality improvement, and fish and wildlife
habitat. An assessment of these functions for the project site are provided below.
Existinq Conditions
Overall functions and values provided by these wetlands are low. These wetlands
make minor contributions to stormwater storage and water quality as a result of
their depressional nature, presence of emer ent vegetation and location adjacent
to a Class 3 stream. Functions for all values provided by these wetlands are limited
by their small size, lack or shortage of native and woody ve etation, and proximity
to roads and development, as well as the extent of disturbance within these
wetlands.
Proposed Impocts to Functions and Values
The applicant is proposing a multi lot development on this property. To
accommodate portions of Lot 7 and Drainage tract 2, the applicant is proposing to
reduce a total of 609 square feet (374 + 235) the buffer off of Wetland A. In
addition to buffer averaging, the applicant is proposing to fill the unclassified
Wetlands B and C. As a result of the current low overalt quality of the area, these
activities should have minimal im acts to overall functions and values of the site.P
Post Miti ation Functions and Values
Miti ation for this buffer reduction is offered throu h desi natin a total of 1 234
square feet of area as additional buffer. This represents a slightly better than 2:1
ratio of buffer averaging addition to buffer avera ing reduction. The designation of
additional area as buffer at a better than 2:1 ratio should maintain or improve
functions and values for the site, includin water quality and wildlife habitat.
WILDLIFE
At the time of our investigation, fauna typical of western Washington forests at that
time of year were heard or observed. Several species of birds were noted includin
white-crowned sparrow, American robin, dark-eyed junco, and black-capped
chickadee. Other resident and migratory species may utilize this site during some
portion of their lives. No herpetofauna were noted.
USE OF THIS REPORT
This Sensitive Area Study and Buffer Averaging Ptan is supplied to Guy Lund as a
means of describing jurisdictional wetland conditions, as required by Kin County
during the permitting process. This report is based largely on readily observable
conditions and to a lesser extent, on readily ascertainable conditions. No attempt
has been made to determine hidden or concealed conditions. Reports may be
adversety affected due to the physicat condition of the site and the difficulty of
access which may lead to observation or probing difficutties.
7
The laws applicable to wetlands are subject to varying interpretations and may be
changed at any time by the courts or legislative bodies. This report is intended to
provide information deemed relevant in the applicant's attempt to comply with the
laws now in effect.
The work for this report has conformed to the standard of care employed by
wetland ecologists. No other representation or warranty is made concerning the
work or this report and any implied representation or warranty is disclaimed.
Wetland Resources, Inc.
Scott Brainard
Principal Wetland Ecologist
8
REFERENCES
Classification of Wetlands and Deepwater Habitats of the United States. FWS/OBS-
79/31. December 1979. U.S. Department of the Interior, Fish and Wildlife
Service. Washington, D.C.
Corps of En ineers Wetlands Delineation Manual, 1987. Technical Report Y-87-1.
Environmental Laboratory. U.S. Army Engineer Waterway Experiment Station.
Vicksburg, MS.
Kin County Zonin Code, Title 21A. King County, WA. February 2000.
National List of Plant Species that Occur in Wetlands, Northwest Region. 1996.
U.S. Department of the Interior, Fish and Wildlife Service. Washington, D.C.
Soil Survev of KinQ County Area WashinQton. November 1973. U.S. Department of
Agriculture, Soil Conservation Service. Washington, D.C.
WashinQton State Wettands Identification and Delineation Manual. Washington
State Department of Ecology. Publication #96-94. March 1997.
9
Field Data Sheet
Lund-114th Ave - WRI# 04153
Investigation Date: 05/10/04
Pit Depth Texture Color Moisture Species Status Strata
S1 0-18"Sandy Loam 10YR 3/1 sl. moist Festuca arundinacea 90 Fac-Herb
Non-Wetland 10YR 4/3 Agrostis tenuis 5 Fac Herb
Redox Vicia sativa 5 Not/Upt Herb
Conctusion: Non-Wetland - Parameters for hydrophytic vegetation and wetland hydrotoqy are not met.
S2 0-6" Silt Loam 2.5Y 3/3 moist Anthoxanthum odoratum 50 FacU Herb
Non-Wetland 6"-10"Sandy Loam 2.5Y 4/3 moist Festuca arundinocea 20 Fac-Herb
10YR 4I4 redox Agrostis tenuis 10 Fac Herb
10"-18"+ Sand 5Y 5/3 moist Vicia sativa 10 Nol/Upt Herb
10YR 5/6 redox Plantago lanceolata 5 Fac Herb
Juncus patens 5 FacW Herb
Conclusion: Non-Wetland - Parameters for hydrophytic veqetation, hydric soils, and wetland hydroloQy are not met.
S3 0-18"Sandy Loam 10YR 3/2 moist Juncus effusus 40 FacW Herb
Wetland 7.5YR 4/4 Phalaris arundinacea 30 FacW Herb
redox Carex sp 20 Fac-Obl Herb
Festuca arundinacea 5 Fac-Herb
Conclusion: Wetland - Parameters for hydrophytic vegetation, hydric soils, and wetland hydrology are met.
S4 0-18" ravelty Sandy Loan 2.5Y 4/4 dry Populus bafsamifera 10 Fac sapling
Non-Wetland Prunus emorginato 5 FacU sapling
Cytisus scoparius 10 Nol/Upl Shrub
Rubus discolor 20 FacU Woody Vine
Festuca arundinacea 50 Fac-Herb
Anthoxanthum odoratum 30 FacU+ Herb
Vicio sativa 10 Nol/Upl Herb
Taraxacum officinale 5 FacU Herb
P(antagolonceolata 5 FacU+ Herb
Conclusion: Non-Wetland - Parameters for hydrophytic veQetation, hydric soils, and wettand hydrolo y are not met.
10
ENVIRONMENTALLY .._. .
SITIVE
AREA
STUDY
AND
BUFFER
AVERAGING
MAP
LUND
114TH
AVE
PORTION
OF
SECTION
29,
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950519th
Avenue
S.
E.
Suite
106
Everett,
Washington
98208
Phone: (
425)
337-
3174
BUFFER
AVERAGING
Fax: (
425)
337-
3045
ADDITION
Email:
mailboxC
wetlandresources.
com
BUFFER
AVERAGING REDUCTION
ENVIRONMENTALLY
EN
S
SITIVE
AREA
STUDY
WETLAND
FILL
AND
BUFFER
AVERAGING
MAP
m-
m
DATASITES
LUND -
114TH
AVE
KING
COUNTY
SENSITIVE
AREA
Sheet
1/
1
S
GNS
WRI
Job#
04153
Guy
and
Fran
Lund
Drawn
by:
L.
Emenhiser
X
SENSITIVE
AREA
810
4th
Street
Date:
06/
07/
2004
FENCING
Port
Angetes,
WA
98362
Revision
1:
09/
27/
04
APPENDIX G
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SWDM
5.
4.
3.
1 $
1.
38
LF
1490
1
2056
Fence,
Temporary(
NGPE)
ESC-
7 (
1.
38
LF
385
1
531
Hydroseeding
ESC-
8
SWDM
5.
4.
2.
4 $
0.
59
SY
Jute
Mesh
ESC-
9 (
SWDM
5.
4.
2.
2 $
1.
45
SY
Mulch,
by
hand,
straw,
3"
deep
ESC-
10
SWDM
5.
4.
2.
1 $
2.
01
SY
Mulch,
by
machine,
straw,
2"
deep
ESC-
11
SWDM
5.
4.
2.
1 $
0.
53
SY
Piping,
temporary,
CPP,
6"
ESC-
12
10.
70 (
LF
Piping,
temporary,
CPP,
8"
ESC-
13
16.
10
LF
Piping,
temporary,
CPP,
12"
ESC-
14
20.
70
LF
Plastic
covering,
6mm
thick,
sandbagged
ESC-
15
SWDM
5.
4.
2.
3 $
2.
30 (
SY
Rip
Rap,
machine
placed;
slopes
ESC-
16
WSDOT
9-
13.
1(
2) $
39.
08 (
CY
Rock
Construction
Entrance,
50'
x15'
x1'
ESC-
17
SWDM
5.
4.
4.
1 $
1,
464.
34
Each
Rock
Construction
Entrance,
100'
x15'
x1'
ESC-
18
SWDM
5.
4.
4.
1 $
2,
928.
68
Each
1
1
2929
Sediment
pond
riser
assembly
ESC-
19
SWDM
5.
4.
52 $
1,
949.
38
Each
Sediment
trap,
5'
high
berm
ESC-
20 (
SWDM
5.
4.
5.
1 $
17.
91
LF
Sed.
trap,
5'
high,
riprapped
spillway
berm
section
ESC-
21
SWDM
5.
4.
5.
1 $
68.
54
LF
Seeding,
by
hand
ESC-
22
SWDM
5.
4.
2.
4 $
0.
51
SY
Sodding,
1"
deep,
level
ground
ESC-
23
SWDM
5.
42.
5 $
6.
03
SY
Sodding,
1"
deep,
sloped
ground
ESC-
24
SWDM
5.
4.
2.
5 $
7.
45
SY
TESC
Supervisor
ESC-
25
74.
75
HR
20
1
1495
Water
truck,
dust
control
ESC-
26
SWDM
5.
4.
7 $
97.
75
HR
20
1
1955
y
Vfi
i,
TE=
IN.-
ITEM**{
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aaa
9) -. ~'
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t.
I
Each
I
ESC
SUBTOTAL:
8,
966.
18
30°/
a
CONTINGENCY
8
MOBILIZATION:
2,
689.
85
ESC
TOTAL:
11,
656.
03
COLUMN:
A
Page
2
of
9
Unit
prices
updated:
02/
12/
02
Version:
04/
22/
02
bond
quantities.
XLS
Check
out
the
DDES
Web
site
at
www.
metrokc.
pov/
ddes
Report
Date:
1/
12/
2006
Site
Improvement
B
Quantity
Worksheet
w ._ . ;.
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s.€
Backfill& _
w
Compaction-
embankment
GI-
1 $
5.
62
CY
Backfill&
Compaction-
trench
GI-
2 $
8.
53
CY
185
1,
578.
05
77
656.
81
36
307.
08
Clear/
Remove
Brush,
by
hand
GI-
3 $
0.
36
SY
Clearing/
Grubbing/
Tree
Removal
GI-
4 $
8,
876.
16
Acre
Excavation-
bulk
GI-
5 $
1.
50
CY
410
615.
00
Excavation-
Trench
GI-
6 $
4.
06
CY
185
751.
10
77
312.
62
36
146.
16
Fencing,
cedar,
6'
high
GI-
7 $
18.
55
LF
Fencing,
chain
link,
vinyl
coated,
6'
high
GI-
8 $
13.
44
LF
284
3,
816.
96
Fencing,
chain
link,
gate,
vinyl
coated,
2
GI-
9 $
1,
271.
81
Each
1
1,
271•
81
Fencing,
split
rail,
3'
high
GI-
10 $
12.
12
LF
385
4,
666.
20
Fill&
compact-
common
barrow
GI-
11 $
22.
57
CY
100
2,
257.
00
Fill&
compact-
gravel
base
GI-
12 $
25.
48
CY
84
2,
140.
32
Fill&
compact-
screened
topsoil
GI-
13 $
37.
85
CY
Gabion,
12"
deep,
stone
filled
mesh
GI-
14 $
54.
31
SY
Gabion,
18"
deep,
stone
filled
mesh
GI-
15 $
74.
85
SY
47
3,
517.
95
Gabion,
36"
deep,
stone
filled
mesh
GI-
16 $
132.
48
SY
Grading,
fine,
by
hand
GI-
17 $
2.
02
SY
Grading,
fine,
with
grader
GI-
18 $
0.
95
SY
Monuments,
3'
long
GI-
19 $
135.
13
Each
Sensitive
Areas
Sign
GI-
20 $
2.
88
Each
7
20•
16
Sodding,
1"
deep,
sloped
ground
GI-
21 $
7.
46
SY
I
Surve
in ,
line&
rade
GI-
22 $
788.
26
Da
5
3,
941.
30
2
1
576.
52
Y
9
9
Y
Surveying,
lot
location/
lines
GI-
23 $
1,
556.
64
Acre
3
4,
669.
92
Traffic
control
crew(
2
flaqgers)
GI-
24 $
85.
18
HR
80
6,
814.
40
Trail,
4"
chipped
wood
GI-
25 $
7.
59
SY
Trail,
4"
crushed
cinder
GI-
26 $
8.
33
SY
Trail,
4"
top
course
GI-
27 $
8.
19
SY
Wall,
retaining,
concrete
GI-
28 $
44.
16
SF
Wa
l,
rockery
GI-
29 $
9.
49
SF
Page
3
of
9
SUBTOTAL
17,
482.
17
10,
191.
15
11,
386.
04 Unit
prices
updated:
02/
12/
02
KCC
27A
authorizes
only
one
bond
reduction.
VersiO:
4/
22/
02
bond
quantities.
XLS
Check
out
the
DDES
Web
site
at
www.
metrokc.
qov/
ddes
Report
Date:
1/
10/
2006
Site
Improvement
B
Quantity
Worksheet
9
Y
y
F"`'
ry' ' . ., ..
z
T
s
J
t*
i°r^
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ja'^
Y'.
Y
5
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x
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Y:
tl:
tt
rria;
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r„-
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k;.
ac•`"
ri
AC
Grinding,
4'
wide
machine<
1000sy
RI-
1 $
23.
00
SY
AC
Grinding,
4'
wide
machine
1000-
200d
RI-
2 $
5.
75
SY
AC
Grinding,
4'
wide
machine>
2000sy
RI-
3 $
1.
38
SY
AC
Removal/
Disposal/
Repair
RI-
4 $
41.
14
SY
200
8,
228.
00
Barricade,
type
I
RI-
5 $
30.
03
LF
Barricade,
type
Iil(
Permanent)
RI-
6 $
45.
05
LF
Curb&
Gutter,
rolled
RI-
7 $
13.
27
LF
90
1,
194.
30
98
1,
300.
46
Curb&
Gutter,
vertical
RI-
8
9.
69
LF
900
8,
721.
00
Curb
and
Gutter,
demolition
and
disposa
RI-
9 $
13.
58
LF
Curb,
extruded
asphalt
RI-
10 $
2.
44
LF
Curb,
extruded
concrete
RI-
11 $
2.
56
LF
Sawcut,
asphalt,
3"
depth
RI-
12 $
1.
85
LF
900
1,
665.
00
Sawcut,
concrete,
per
1"
depth
RI-
13I $
1•
69
F
Sealant,
asphalt
RI-
14 $
0.
99
LF
Shoulder,
AC, (
see
AC
road
unit
price)
RI-
15I $ -
I
SY
Shoulder,
gravel,
4"
thick
RI-
16 $
7.
53
SY
Sidewalk,
4"
thick
RI-
17 $
30.
52
SY
500
15,
260.
00
Sidewalk,
4"
thick,
demolition
and
dispos
Rl-
18 $
27.
73
SY
Sidewalk,
5"
thick
RI-
19 $
34.
94
SY
Sidewalk,
5"
thick,
demolition
and
dispos
Rl-
20 $
34.
65
SY
Sign,
handicap
RI-
21 $
85.
28
Each
Striping,
per
stall
RI-
22 $
5.
82
Each
Striping,
thermoplastic,(
for
crosswalk)
RI-
23 $
2.
38
SF
Striping,
4"
reflectorized
line
RI-
24 $
0.
25
LF
Page
4
of
9
SUBTOTAL
33,
874.
00
1,
194.
30
1,
300.
46 Unit
prices
updated:
02/
12/
02
KCC
27A
authorizes
only
one
bond
reduction.
Version:
4/
22/
02
bond
quantities.
XLS
Check
out
the
DDES
Web
slte
at
www.
metrokc.
aov/
ddes
Report
Date:
1l10l2006
Site
Improvement
f
d
Quantity
Worksheet
i
M ,.,
A4;=, . . `'£, °..
w`,,, :
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S
I.
o-',
a >
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s
t1t3t""_
4
f. ,° " _
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t2Tght-
of
nr
r -
dail
pr
nv
ti
en,''
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w:
fr;YAr.`'
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ra7riage
Facit[
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f
r
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c
st `"
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nit
at'€':: .
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a
I
b .
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k.' . . .
V
a :=
4,z ° ,.,
m'
For
KCRS'
93,(
additional
2.
5"
base)
add
RS-
1 $
3.
60
SY
AC
Overlay,
1.
5"
AC
RS-
2 $
7.
39
SY
AC
Overlay,
2"
AC
RS-
3 $
8.
75
SY
AC
Road,
2",
4"
rock,
First
2500
SY
RS-
4 $
17.
24
SY
300
5,
172.
00
150
2,
586.
00
165
2,
844.
60
AC
Road,
2",
4"
rock,
Qty.
over
2500SY
RS-
5 $
13.
36
SY
AC
Road,
3",
4"
rock,
First
2500
SY
RS-
6 $
19.
69
SY
AC
Road,
3",
4"
rock,
Qty.
over
2500
SY
RS-
7 $
15.
81
SY
AC
Road,
5",
First
2500
SY
RS-
8 $
14.
57
SY
300
4,
371.
00
150
2,
185.
50
165
2,
404.
05
AC
Road,
5",
Qty.
Over
2500
SY
RS-
9 $
13.
94
SY
AC
Road,
6",
First
2500
SY
RS-
1C $
16.
76
SY
AC
Road,
6",
Qty.
Over
2500
SY
RS-
11 $
16.
12
SY
Asphalt
Treated
Base,
4"
thick
RS-
1 $
9.
21
SY
Gravel
Road,
4"
rock,
First
2500
SY
RS-
1: $
11.
41
SY
170
1,
939.
70
Gravel
Road,
4"
rock,
Qty.
over
2500
SY
RS-
14 $
7.
53
SY
PCC
Road,
5",
no
base,
over
2500
SY
RS-
1: $
21.
51
SY
PCC
Road,
6",
no
base,
over
2500
SY
RS-
tE $
21.
87
SY
Thickened
Edge
RS-
17 $
6.
89
LF
Page
5
of
9
SUBTOTAL
9,
543.
00
6,
711.
20
5,
248.
65 Unit
prices
updated:
02/
12/
02
KCC
27A
authorizes
only
one
bond
reduction.
Ve'
Slon:
4/
22/
02
bond
quantities.
XLS
Check
out
the
DDES
Web
site
at
www.
metrokc.
qov/
ddes
Report
Date:
1/
10/
2006
r—
Site
Improvement
d
Quantity
Worksheet
m,
s
s
a
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Access
Road,
R/
D
D-
1 $
16.
74
SY
Bollards-
fixed
D-
2 $
240.
74
Each
Bollards-
removable
D-
3 $
452.
34
Each
CBs
include
frame
and
lid)
I
CB
Type
I
D-
4 $
1,
257.
64
Each
6
7,
545.
84
3
3,
772.
92
1
1,
257.
64
CB
Type
IL
D-
5 $
1,
433.
59
Each
CB
Type
II,
48"
diameter
D-
6 $
2,
033.
57
Each
for
additional
depth
over
4'
D-
7 $
436.
52
FT (
CB
Type
II,
54"
diameter
D-
8 $
2,
192•
54
Each
1
2,
192.
54
1
2,
192.
54
for
additional
depth
over
4'
D-
9 $
486.
53
FT
CB
Type
II,
60"
diameter
D-
10I $
2,
351.
52
Each
for
additional
depth
over
4'
D-
11 $
536.
54
FT
CB
Type
II,
72"
diameter
D-
12 $
3,
212.
64
Each
for
additional
depth
over
4'
D-
13 $
692.
21
FT
Through-
curb
Inlet
Framework(
Add)
D-
14 $
366.
09
Each
Cleanout,
PVC,
4"
D-
15 $
130.
55
Each
Cleanout,
PVC,
6"
D-
16 $
174.
90
Each
Cleanout,
PVC,
8"
D-
17 $
224.
19
Each
Culvert,
PVC,
4"
D-
18 $
8.
64
LF
c
i
ert,
Pvc,
s
o-
s
I
z.
so
LF
I
I
I
I
I
I
I
Culvert,
PVC,
8"
D-
20 $
13.
33
LF
Culvert,
PVC,
12"
D-
21 $
21.
77
LF
Culvert,
CMP,
8"
D-
22 $
17.
25
LF
Culvert,
CMP,
12"
D-
23 $
26.
45
LF
Culvert,
CMP,
15"
D-
24 $
32.
73
LF
Culvert,
CMP,
18"
D-
25 $
37.
74
lF
Culvert,
CMP,
24"
D-
26 $
53.
33
LF
Culvert,
CMP,
30"
D-
27 $
71.
45
LF
Culvert,
CMP,
36"
D-
28 $
112.
11
LF
Cuivert,
CMP,
48"
D-
29 $
140.
83
LF
98
13,
801.
34
Culvert,
CMP,
60"
D-
30 $
235.
45
LF
Culvert,
CMP,
72"
D-
31 $
302.
58
LF
Page
6
of
9
SUBTOTAL
23,
539.
72
5,
965.
46
1,
257.
64 Unit
prices
updated:
02/
12/
02
KCC
27A
authorizes
only
one
bond
reduction.
Vefsion:
4/
22/
02
bond
quantities.
X
S
Check
ouf
the
DDES
Web
site
at
www.
mefrokc.
qov/
ddes
Report
Date:
1/
10/
2006
Site
Improvement
E
d
Quantity
Worksheet
I
a
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INAGE
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Quant. (
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M,
Culvert,
Concrete.
8"
D-
32 $
21.
02
LF
Culvert,
Concrete,
12"
D-
33I $
30.
05
LF
Culvert,
Concrete,
15"
D-
34 $
37.
34
LF
Culvert,
Concrete,
18"
D-
35 $
44.
51
LF
Culvert,
Concrete,
24"
D-
36 $
61.
07
LF
Culvert,
Concrete,
30"
D-
37 $
104.
18
LF
Culvert,
Concrete,
36"
D-
38 $
137.
63
LF
Culvert,
Concrete,
42"
D-
39 $
158.
42
LF
Culvert,
Concrete,
48"
D-
40 $
175.
94
LF
Culvert,
CPP,
6"
D-
41 $
10.
70
LF
Culvert,
CPP,
8"
D-
42 $
16.
10
F
Culvert,
CPP,
12"
D-
43 $
20.
70
LF
622
12875.
4
259
5361.
3
123
2546.
1
Culvert,
CPP,
15"
D-
44 $
23.
00
LF
Culvert,
CPP,
18"
D-
45 $
27.
60
LF
Culvert,
CPP,
24"
D-
46 $
36.
80
LF
Culvert,
CPP,
30"
D-
47 $
48.
30
LF
Culvert,
CPP,
36"
D-
48 $
55.
20
LF
Ditching
D-
49 $
8.
08
CY
Flow
Dispersai
Trench (
1,
436
base+) (
D-
50 $
25.
99
LF
50
2735.
5
French
Drain (
3'
depth)
D-
51 $
22.
60
LF
Geotextile,
laid
in
trench,
polypropylene
D-
52 $
2.
40
SY
Infiltration
pond
testing
D-
53 $
7475
HR
Mid-
tank
Access
Riser,
48"
dia,
6'
deep
D-
54 $
1,
605.
40
Each
Pond
Overflow
Spillway
D-
55 $
14.
01
SY
1
14•
01
I
Restrictor/
Oil
Separator,
12"
D-
56 $
1,
045.
19
Each
1
1045.
19
1
1045.
19
I
Restrictor/
Oil
Separator,
15"
D-
57 $
1,
095.
56
Each
I
Restrictor/
Oil
Separator,
18"
D-
58 $
1,
146.
16
Each
I
Riprap,
placed
D-
59 $
39.
08
CY
Tank
End
Reducer(
36"
diameter)
D-
60 $
1,
000.
50
Each
1
1000.
5
Trash
Rack,
12"
D-
61 $
211.
97
Each
1(
211•
97
i
Trash
Rack,
15"
D-
62 $
237.
27
Each
I
Trash
Rack,
1
S"
D-
63 $
268.
89
Each
Trash
Rack,
21"
D-
64 $
306.
84
Each
Page
7
of
9
SUBTOTAL
14921.
09
6632.
47
5281.
6 Unit
prices
updated:
02/
12/
02
KCC
27A
authorizes
only
one
bond
reduction.
Ve
SiO:
4/
22/
02
bond
quantities.
X
S
Check
out
the
DDES
Web
site
at
www.
metrokc.
aov/
ddes
Report
Date:
1/
10/
2006
Site
Improvement
B
Quantity
Worksheet
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2"
AC,
2"
top
course
rock
8
4"
borrow
PL-
1 $
15.
84
SY
2"
AC,
1.
5"
top
course&
2.
5"
base
cour
PL-
2 $
17.
24
SY
4"
select
borrow
PL-
3 $
4.
55
SY
1.
5"
top
course
rock&
2.
5"
base
course
PL-
4 $
11.
41
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as
detention/
water
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1
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2
SY
WI-
3
CY
WI-
4
LF
WI-
5
FT
WI-
6
WI-
7
WI-
8
WI-
9
wi-
o
SUBTOTAL
SUBTOTAL(
SUM
ALL
PAGES):
99,
359.
98
30,
694.
58
24,
474.
39
30%
CONTINGENCY
8
MOBILIZATION:
29,
807.
99
9,
208.
37
7,
342.
32
GRAN
DTOTAL:
129,
167.
97
39,
902.
95
31,
816.
71
COLUMN:
B
C
D
E
Page
8
of
9
Unit
prices
updated:
02/
12/
02
KCC
27A
authorizes
only
one
bond
reduction.
Ve
slon:
4/
22/
02
bond
quantities.
XLS
Check
out
the
DDES
Web
slte
at
www.
metrokc.
aov/
ddes
Report
Date:
1/
10/
2006
1
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