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TECHNICAL INFORMATION REPORT
for
1500 and 1600 Benson Apartments and Offices
Tax Parcel No. 2023059162
Pre-application No. 05-125
Site Address:
15xx Benson Road South
Renton, Washington 98055
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Prepared by: Lorna M. Taylor, P.E.
Date: November 20, 2012
Revised: June 6, 2013
TEC Project Number:307-TFC Published for building permit record set: July 31, 2013
485 Rainier Blvd N, Ste#201, P.O. Box 1787 • Issaquah,Washington 98027 • telephone(425)391-1415 • fax(425)391-1551
Technical Information Report
1500 and 1600 Benson Apartments and Offices
TABLE OF CONTENTS
Section Description Page Number
1. Project Overview 1
2. Conditions and Requirements Summary 1
3. Off-Site Analysis 2
4. Flow Control and Water Quality Facility Analysis 4
and Design
5. Conveyance System Analysis and Design........ 6
6. Special Reports and Studies . 6
7. Other Permits 6
8. ESC Analysis and Design 6
9. Bond Quantities, Facility Summaries, and 9
Declaration of Covenant
10. Operations and Maintenance Manual 9
Appendices
Appendix A: Figures:
Figure 1. Technical Information Report (TIR) Worksheets
Figure 2. Site Location
Figure 3. Drainage Basins, Subbasins, & Site Characteristics
Figure 4. NRCS Soils Map
Appendix B: Off-site Analysis Drainage System Table and Map
Appendix C: Analysis and Design:
C-1 Flow Control
C-2 Runoff Treatment
C-3 Conveyance System
C-4 Erosion Control
Appendix D: Maintenance Requirements for Privately Maintained Drainage
Facilities
Appendix E: Bond Quantities Worksheets
Appendix F: Retention/Detention Facility Summary Sheet and Sketch
TEC
Technical Information Report
1500 and 1600 Benson Apartments and Offices
SECTION 1
PROJECT OVERVIEW
This drainage Technical Information Report (TIR) is submitted to the City of Renton in
accordance with the City-adopted King County Surface Water Design Manual (KCSWDM) and
the City of Renton Amendments thereto (Renton Amendment).
Appendix A contains a 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 copy
of the NRCS Soils map for the vicinity (Figure 4). The project will construct two multistory
apartment and office buildings, just east of Benson Road South at South 15th Street. The
property totals 1.88 acres.
SECTION 2
CONDITIONS AND REQUIREMENTS SUMMARY
The following summary describes how this new project will meet the eight "Core Requirements"
and the "Special Requirements" that apply:
Core Requirements
1. Discharge at the Natural Location: The site currently drains in a dispersed manner to
the west/northwest to the Benson Road drainage system. The project proposes to
discharge all runoff to the existing Benson Road system.
2. Off-Site Analysis: A Level 1 offsite analysis was conducted for this site as described in
Section 3 and Appendix B.
3. Flow Control: The project will increase the 100-year runoff more than 0.1 cfs, and
therefore is providing Conservation Flow Control assuming forested pre-developed
conditions in two buried detention vaults sized per the KCSWDM. Detention sizing
calculations are summarized in Section 4, and KCRTS input and files and other
supporting documents are included in Appendix C.1.
4. Conveyance System: The conveyance pipes were analyzed for capacity under the
anticipated backwater conditions using King County's Backwater routing program
(KCBW). The pipes can safely convey the required 25-year flows with at least 6 inches
of freeboard per the City Amendment.
5. Erosion and Sedimentation Control: Runoff from the construction areas will be
collected and preliminarily treated in a proprietary "Baker Tank" and discharged by
special permit to the sanitary sewer during construction only. The erosion control
facilities will also include stabilized construction entrances, silt fencing, interceptor
swales and/or dikes, and temporary catch basin protection 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 drainage system should be regularly inspected and
maintained as described in Section 10 and Appendix D.
7. Financial Guarantees and Liability: The County's Bond Quantities Worksheet will be
provided for the public frontage improvements and drainage elements of the project.
8. Water Quality:The area of new and replaced Pollution Generating Impervious Surfaces
(PGIS) totals 22,472 square feet, which is more than the 5,000 square foot threshold for
requiring treatment. Treatment of runoff from 17,729 square feet of pavement will be
provided by the soil which must meet or be amended to meet the "groundwater
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1500 and 1600 Benson Apartments and Offices
protection criteria" stipulated in Exemption 4 of the Exemptions from Core Requirement
#8, page 1-61 of the City Amendments. Runoff from the pavement surface that is too
steeply sloping to utilize permeable pavement, will be treated in a series of two treatment
catch basins, a CDS 2015-4-C hydrodynamic separator upstream for pretreatment
sediment removal followed by a 48-Inch Stormfilter Manhole downstream for treatment—
both located upstream of the south detention vault. Sizing calculations for the treatment
facilities are included in Section 4 and Appendix C.2.
Special Requirements
1. Other Adopted Area-Specific Requirements: Not Applicable.
2. Floodplain/Floodway Delineation: Not Applicable.
3. Flood Protection Facilities: Not Applicable.
4. Source Controls: Source controls are required for this multifamily residential and office
project, in accordance with the King County Stormwater Pollution Prevention Manual.
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 path.
Task 1. Study Area Definition and Maps
The figure in Appendix B shows the extent of the study area and the local topography. The Site
Plan drawing shows more detailed topographic information on the project site. No runoff flows
onto the site from the north, south, or west as shown on the Figure in Appendix B.
Task 2. Resource Review
The City's utility mapping was consulted, as well as King County's iMAP data. Following is a
summary of the KCSWDM's recommended resources for review.
Adopted Basin Plans - The project site is not within any adopted basin plan area, nor is
there a finalized drainage study for the area.
Finalized Drainage Studies - No finalized drainage studies were available for projects in the
immediate vicinity.
Basin Reconnaissance Summary Reports - The project site is not covered by any basin
reconnaissance summary reports.
Critical Drainage Area Maps - The project site is not within or adjacent to any mapped
critical area.
Floodplain/floodway (FEMA) Maps - The project site is not located within any FEMA mapped
flood plain/floodway.
Other Off-Site Analysis Reports in the same sub-basin, if available - The offsite analysis
report for the Lodge at Eagle Ridge project immediately to the east was consulted.
Sensitive Areas Folio - The project site is mapped with the following critical areas: SAO
Erosion Hazard, Areas Susceptible to Groundwater Contamination.
Drainage Complaints and Studies - There are no reports of problems in the immediate
vicinity of the project.
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1500 and 1600 Benson Apartments and Offices
US Department of Agriculture, King County Soils Survey - A copy of the NRCS (SCS) soils
map is included in Appendix A, Figure 4. The soils are predominantly Alderwood gravelly
sandy loam, 15 to 30 percent slopes. These soils have moderate to high runoff potential.
Wetlands Inventory Maps - There are no wetlands systems on the site identified in the King
County Wetlands Inventory.
Migrating River Studies—There are no rivers on the site.
Task 3. Field Inspection
A Level 1 off-site inspection was conducted on January 29th, 2007. The site and its surrounds
were also inspected and documented as part of field investigations for several nearby properties
before that time and since. At the time of the most recent site inspection, the weather was clear
and cold.
Task 4. Drainage System Descriptions and Problem Descriptions
The drainage tributary area extends up to, and for the northern portion of the site, onto the
adjacent Lodge at Eagle Ridge property. This runoff must be taken into account in the detention
sizing. Elsewhere, the land uphill of the site is served by catch basins and pipes that collect and
transport runoff across the project site to Benson Road South.
The site itself slopes down, steeply in places, toward the west and the Benson Road South
frontage. Benson Road was cut into the hillside and slopes down to the north. There is a piped
storm drain conveyance system along Benson Road, with an overflow to Talbot Road South,
just north of the project property.
There are several existing storm drains crossing the site, as well as other utilities including
sanitary sewer, water, electrical service, cable and gas. There is an existing detention pond on
the property along Benson Road, near the northern boundary. This detention pond serves the
office building directly north of the proposed development and was probably designed and built
to older, obsolete detention design standards.
The downstream drainage system is shown on the map in Appendix B and The Offsite Analysis
Drainage System Table in the same appendix describes each segment of the downstream
drainage path. No drainage problems were observed or reported except for historic flooding in
the vicinity of Renton Village more than '/4 mile downstream.
Task 5. Mitigation of Existing or Potential Problems
No existing or potential offsite drainage problems were identified; however, it should be noted
that:
• Water quantity impacts from the project will be mitigated using permeable pavement
BMP's wherever the pavement slopes are less than 5%, together with standard
detention in concrete vaults, in accordance with the King County Surface Water Design
Manual (KCSWDM).
• Water quality impacts from PGIS surfaces will also be mitigated using permeable
pavement BMP's wherever the pavement slopes are less than 5%, and using proprietary
treatment catch basins upstream of the south detention vault where pavement slopes
are steep.
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1500 and 1600 Benson Apartments and Offices
SECTION 4
FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND DESIGN
The project proposes 62,736 square feet of new impervious surface on the project site, 22,472
square feet of which is traffic pavement (PGIS), as shown on the first Figures in Appendices C-1
& C-2. Frontage improvements will be limited to curb cuts for access and utility connections.
Existing Site Hydrology (Part A)
The drainage on the existing site was analyzed for this project with King County's KCRTS
routine assuming historic fully forested conditions per the City of Renton Flow Control
Applications Map (Renton Amendment Reference 11-A). Data provided in the KCSWDM were
used to determine modeling parameters. The figures in Appendix C.1 show the delineation of
the areas generating runoff on the existing site. Appendix C.1 also contains the data and output
from the hydrologic analyses. The site soils are predominantly classified Alderwood Gravelly
Sandy Loam, 15- 30 percent slopes, with two small areas near the two northwest corners
classified as Beausite gravelly sandy loam, 15 -30 percent slopes (see Figure 4 in Appendix
A).
Developed Site Hydrology (Part B)
The developed site drainage system will discharge site runoff to the Benson Road South
drainage system. The developed site conditions identified for this project and used in the
KCRTS modeling are as follows:
Developed Site North Detention South Detention
Conditions used for
Hydrologic Modeling
Vault Trib. Area Vault Trib. Area Total
(areas in acres areas in acres)
Building 0.43 0.46 0.89
Pavement 0.00 0.20 0.20
'/2 Permeable Pavement 0.07 0.14 0.21
Sidewalk <0.01 004 0.04
Impervious Subtotal 0.50 0.74 1.24
1/2 Permeable Pavement 0.06 0.13 0.19
Landscaping 0.36 0.37 0.73
Forest(offsite) 0.21 0.00 0.21
Pervious Subtotal 0.63 0.50 1.13
Total 1.13 1.24 2.37
Permeable pavement BMP's are proposed wherever the pavement is less than 5 percent slope.
This represents 17,729 square feet and these areas were modeled in KCRTS as 50%
impervious and 50% grass. The driveway entrance area totals 4,351 square feet, and is too
steep to use permeable pavement.
Performance Standards (Part C)
Detention is required because the 100-year flow is predicted by KCRTS to increase more than
0.1 cfs. Detention must meet the Conservation Flow Control Standards established in the
KCSWDM, which in this case means Level 2 flow control, assuming historic forested site
conditions for peak flow and duration matching.
Treatment is required because the PGIS area is increasing more than 5,000 square feet. And,
because the project is a multifamily land use, runoff treatment facilities would need to meet
Enhanced Basic Water Quality Treatment parameters, except that the project meets the criteria
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1500 and 1600 Benson Apartments and Offices
set forth in Exception 4 of the City Amendment, and so must only meet Basic Water Quality
Treatment parameters as established in the KCSWDM. This exemption requires that:
a) no leachable metals (e.g. galvanized metals) are currently used or proposed to be used
in areas of the site exposed to the weather, AND
b) a covenant is recorded that prohibits future such use of leachable metals on the site,
AND
c) less than 50% of the runoff draining to the proposed treatment facility is from any area of
the site comprised of one or both of the following land uses:
• commercial land use with an expected ADT of 100 or more vehicles per 1,000
square feet of gross building area
• commercial land use involved with vehicle repair, maintenance, or sales.
Because the Target Impervious Surface Area (62,936 sf) is greater than 65% of the site, BMP's
are required to be applied to at least the lesser of 10 percent of the site area (0.1 x 81,918 sf=
8,192 sf) or 20 percent of the target surface area (0.2 x 62,936 sf = 12,587 sf). So, BMP's must
be applied to at least 8,192 sf of impervious surface area.
Conveyance features must be able to convey the predicted 25-year flows with at least 6-inches
of freeboard between the water surface elevation and the structure grate.
Flow Control System (Part D)
Flow control is being provided in two separate detention vaults which will function completely
independently. The following table summarizes the sizing requirements for the two vaults. The
full KCRTS input and output data is included in Appendix C.1
Detention Vault North Detention South Detention Total
Requirements Vault Vault
Required storage volume 10,800 cf 17,600 cf 28,400 cf
Effective storage depth 10 ft 10 ft
Facility length 54 ft 88 ft 142 ft
Facility width 20 ft 20 ft 40 ft
Facility area 1,080 sf 1,760 sf 2,840 sf
Orifice #1 diameter 0.47" (1/2") 0.47" (1/2")
Orifice#2 diameter 0.86" (7/8") 0.70" (11/16")
Orifice#2 height 6.00 ft 5.80 ft
Water Quality (Part E)
The area of new PGIS pavement totals 22,472 square feet, so water quality treatment is
required. Treatment of runoff from 17,729 square feet of pavement can be provided by the
permeable pavement BMP proposed for that area as long as the soil underlying the permeable
pavement meets the "groundwater protection criteria" set forth in the Exceptions from Core
Requirement #8 Soil Treatment Exemption 4 (see Section 1.2.8 of the City Amendments). The
soil under the permeable pavement will be tested and augmented as necessary so that the first
2 feet of soil beneath the permeable pavement has a cation exchange capacity (tested using
EPA Lab Method 9081) greater than 5 and an organic content (measured on a dry weight basis
using ASTM D2974) greater than 0.5% AND a) has a measured infiltration rate of less than or
equal to 9 inches per hour, except in groundwater protection areas where the measured rate
must be less than or equal to 2.4 inches per hour, OR b) the soil must be composed of less than
25% gravel by weight with at least 75% of the soil passing the #4 sieve, and the portion passing
the#4 sieve must meet one of the following gradations:
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• at least 50% must pass the #40 sieve and at least 2% must pass the #100 sieve, OR
• at least 25% must pass the #40 sieve and at least 5% must pass the #200 sieve.
The remaining 4,351 square feet of pavement surface is too steeply sloping to utilize permeable
pavement, and runoff from this area will be treated using a series of two treatment catch basins;
a CDS 2015-4-C hydrodynamic separator upstream for pretreatment sediment removal and a
48-Inch Stormfilter Manhole downstream for treatment—both located upstream of the south
detention vault. Because the CDS facility isn't on King County's pretreatment list, this
configuration requires an adjustment to Core Requirement #6. An adjustment request is
submitted under separate cover in accordance with the City Amendment Section 1.4.3. Sizing
calculations for the cartridge filter are included in Appendix C-2.
The 138 square foot south building dumpster concrete area will naturally drain to the adjacent
permeable pavement and thus be treated. Only two small asphalt areas, and the north
dumpster concrete area, totaling 392 sf will be unable to be treated due to physical constraints.
Treatment of roof runoff is not required.
SECTION 5
CONVEYANCE SYSTEM ANALYSIS AND DESIGN
Conveyance pipes were analyzed using King County's Standard Step Backwater Analysis
routine. The pipes must convey the predicted 25-year flow with at least 6-inches of freeboard.
The analyses show that all pipes can convey the predicted 25-year flows and the 100-year flow
can also be will be conveyed without flooding.
The 100-year flows were also be modeled to be sure that significant flooding will not result
under extreme runoff conditions.
SECTION 6
SPECIAL REPORTS AND STUDIES
A site-specific geotechnical report, dated June 23, 2012 was prepared for this project by
GeoTech Consultants, Inc. This report is available under separate cover.
SECTION 7
OTHER PERMITS
Because the project requires clearing of greater than one acre, this project is required to obtain
a Construction Stormwater General Permit from the Washington State Department of Ecology.
Stormwater is proposed to be temporarily discharged to the public sanitary sewer during
construction and a temporary discharge permit will be required for this.
No other permits beyond those required by the City of Renton are anticipated to be required for
this project.
SECTION 8
CSWPPP ANALYSIS AND DESIGN
ESC Analysis and Design (Part A)
Proposed ESC facilities are shown on the Construction Stormwater Pollution Prevention Plan
(CSWPPP). All of the proposed erosion control measures comply with KCSWDM Appendix D.
Because of the sloping nature of the site and the extent of the development proposed, runoff
from the proposed construction areas will be collected and treated in a proprietary "Baker Tank"
and with permit approval, be discharged to the public sanitary sewer during construction. Other
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1500 and 1600 Benson Apartments and Offices
erosion control facilities will include stabilized construction entrances, silt fencing, interceptor
swales and/or dikes, and temporary catch basin protection 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.
ESC measures shown on the plans include:
1. Clearing Limits are shown on the plans and will be delineated with Survey Fencing
and/or Silt Fencing.
2. Cover Measures are shown on the plans and include Plastic Covering over all soil
stockpiles, Temporary and Permanent Seeding.
3. Perimeter Protection will be provided by Silt Fence as shown on the Plans.
4. Traffic Area Stabilization will be provided by Stabilized Construction Entrances as shown
on the plans.
5. Sediment Retention will be provided in a Baker Tank located in the paved parking area
northwest of the site. If necessary, Baker Tank(s) can be sized for Wet Season
Construction using the 10-year runoff predicted for the project. All existing and proposed
storm inlets in the vicinity of the project will be fitted with Storm Drain Inlet Protection
Catch Basin Inserts.
6. Surface Water Collection will occur in Interceptor Swales or Dikes located along the
downhill side of the grading areas.
7. Dewaterinq Control is anticipated for trenches, and foundation excavations, and per the
plans, shall be pumped to the Baker Tank.
8. Dust Control will be necessary during dry months and is covered in the ESC notes.
9. Flow Control will be achieved for the ESC portion of this project the Baker Tank storage
with controlled discharge.
If construction occurs during the wet season, then ESC facilities must be sized in accordance
with Wet Season Requirements, the sediment facilities (Baker Tanks) will need to be sized for
runoff predicted from the 10-year storm modeled using 15-minute time steps (0.97 cfs). The
KCRTS runoff model output and sediment trap sizing calculations are included in Appendix C.
All ESC flow control sizing must be coordinated with the selected discharge options, which
include the public sanitary sewer or storm drain system
SWPPS Plan Design (Part B)
Activities that could contribute pollutants to surface and stormwater during construction for this
project include clearing and grubbing the site, grading, and soil excavation and storage. Most of
the ESC measures identified in the CSWPPP (Part A) above will also address the pollutants
likely to be generated by these activities.
The Activity Sheets for the Pollution Prevention BMPs identified for this site and relevant BMP
Info Sheets are listed below and included in Appendix E.
• Activity Sheet A-1 Required BMPs for All commercial Properties
• Activity Sheet A-4 Storage of Soil, Sand, and Other Erodible Materials
• Activity Sheet A-27 Clearing and Grading of Land for Small Construction Projects
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1500 and 1600 Benson Apartments and Offices
• BMP Info Sheet#3 Covering Options: Tarp, Roof, or Awning
• BMP Info Sheet #7 Maintenance of Drainage Systems
• BMP Info Sheet #10 Catch Basin Insert
Since sediment is the primary pollutant of concern for this project, stormwater discharges from
the site must be monitored weekly, and more frequently during periods of rainfall. The project
may seek permission to discharge construction runoff to the public sanitary sewer in order to
reduce the on-site treatment requirements. In the event that construction stormwater is to be
discharged to the public storm drain system, then the ESC measure's performance shall be
assessed by the project's ESC supervisor as stipulated in KCSWDM Section D.4:
1. IF a turbidity test of surface and storm water discharges leaving the project site is
greater than the benchmark value of 25 NTU (nephelometric turbidity units) set by the
Washington State Department of Ecology, but less than 250 NTU, the ESC Supervisor
shall do all of the following:
a) Review the ESC plan for compliance and make appropriate revisions within 7 days of
the discharge that exceeded the benchmark of 25 NTU, AND
b) Fully implement and maintain appropriate ESC measures as soon as possible but no
later than 10 days after the discharge that exceeded the benchmark, AND
c) Document ESC implementation and maintenance in the site log book.
2. IF a turbidity test of surface or storm water entering onsite wetlands, streams, or lakes
indicates a turbidity level greater than 5 NTU above background when the background
turbidity is 50 NTU or less, or 10% above background when the background turbidity is
greater than 50 NTU, then corrective actions and/or additional measures beyond those
specified in Section 1.2.5.1 shall be implemented as deemed necessary by the County
inspector or onsite ESC supervisor.
3. IF discharge turbidity is 250 NTU or greater, the ESC Supervisor shall do all of the
following:
a) Notify the County by telephone, AND
b) Review the ESC plan for compliance and make appropriate revisions within 7 days of
the discharge that exceeded the benchmark of 25 NTU, AND
c) Fully implement and maintain appropriate ESC measures as soon as possible but no
later than 10 days after the discharge that exceeded the benchmark, AND
d) Document ESC implementation and maintenance in the site log book. AND
e) Continue to sample discharges until turbidity is 25 NTU or lower, or the turbidity is no
more than 10% over background turbidity.
4. IF the County determines that the condition of the construction site poses a hazard to
adjacent property or may adversely impact drainage facilities or water resources,
THEN additional measures beyond those specified in Section 1.2.5.1 may be required
by the County.
The receiving water for this project is the Black/Duwamish River. Its tributary, Springbrook
Creek is listed as a Category 5 polluted water of the state under the State's Clean Water Act
Section 303(d) list due to dissolved oxygen content and fecal coliform contamination, not
sediments/turbidity. Closer to the Duwamish River, the Black River is also listed due to fecal
coliform bacteria. Copies of the Section 303(d) Map and Listings are included at the end of
Appendix B.
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1500 and 1600 Benson Apartments and Offices
SECTION 9
BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT
King County's Bond Quantities Worksheet is included in Appendix E.
King County's Facility Summary Sheets and Sketches are included in Appendix F.
The City's Declaration of Covenant forms are submitted under separate cover for Inspection and
Maintenance of Stormwater Facilities and BMPs and for Prohibiting Use of Leachable Metals.
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).
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APPENDIX A
FIGURES
1. Technical Information Report (TIR) Worksheets
2. Site Location Map
3. Drainage Basins, Subbasins, & Site Characteristics
4. NRCS Soils Map
1
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Part 1 PROJECT OWNER AND j Part 2 PROJECT LOCATION AND
PROJECT ENGINEER j DESCRIPTION
Project Owner ( le I korL y, 4 &rf I4a j,.,jf Project Name 1511 1(0 a ?-Qns�9,�'1
Phone ?Ola ` 56'15 51i ( DDES Permit# " wh 4 CSHZ 4-eo
Address Location Township -1.3
Range 5
Project Engineer LD, AA j t V Section 3 u./ 2.0
Company TE.7 t Site Address J5 Xx_ Re/150/1 t S
Phone '-(2-Ci 1- 1 9
Part 3 TYPE OF PERMIT APPLICATION Part 4 OTHER REVIEWS AND PERMITS
❑ Landuse Services ❑ DFW HPA ❑ Shoreline
Subdivison / Short Subd. / UPDManagement
❑ COE 404
3 Building Services ❑ DOE Dam Safety © Structural
/� ommerica / SFR RockeryNault/
Clearing and Grading ❑ FEMA Floodplain
❑ ESA Section 7
CIRight-of-WayUse LI COE Wetlands
CI Other LI Other
Part 5 PLAN AND REPORT INFORMATION
Technical Information Report Site Improvement Plan (Engr. Plans)
Type of Drainage Review Ful / Targeted / Type (circle one): ull / Modified /
(circle): arge Site Small Site
Date(include revision U-20- t2- Date(include revision LI -20 i Z
dates): dates):
Date of Final: Date of Final:
Part 6 ADJUSTMENT APPROVALS
Type (circle one): Standard / Complex / Preapplication / Experimental/ Blanket
Description: (include conditions in TIR Section 2)
Date of Approval:
2009 Surface Water Design Manual 1/9/2009
1
24
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Part 7 MONITORING REQUIREMENTS
Monitoring Required: Ye / No Describe: —; U,,t71,(z.►--,1 t�.u,�r; cons e/
Start Date:
Completion Date:
Part 8 SITE COMMUNITY AND DRAINAGE BASIN
Community Plan : (Lt-) a t (,4pvr
Special District Overlays:
Drainage Basin: I la c(( 2r v.e✓ ,
Stormwater Requirements: C�:✓1SC✓�/C-11M ri%SW' CC-ialb j
Part 9 ONSITE AND ADJACENT SENSITIVE AREAS
I
❑ River/Stream j Steep Slope
❑ Lake ❑ Erosion Hazard
❑ Wetlands ❑ Landslide Hazard
❑ Closed Depression ❑ Coal Mine Hazard
❑ Floodplain ❑ Seismic Hazard
❑ Other ❑ Habitat Protection
LI
Part 10 SOILS
Soil Type Slopes Erosion Potential
IgD i5 --307.,
Be D15 -301
❑ High Groundwater Table (within 5 feet) ❑ Sole Source Aquifer
❑ Other ❑ Seeps/Springs
Additional Sheets Attached (1.-;(vie Chem.612 (Le ri- c,.✓c IAA L vete••SKerArcje.a ve,-
2009 Surface Water Design Manual 1/9/2009
2
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL 3/1D
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Pa IN DRAINAGE DESIGN LIMITATIONS
REFERENCE LIMITATION /SITE CONSTRAINT
Core 2—Offsite Analysis
U Sensitive/Critical Areas
U SEPA
U Other
U
❑ Additional Sheets Attached
Part 12 TIR SUMMARY SHEET (provide one TIR Summary Sheet per Threshold Discharge Area)
Threshold Discharge Area:
(name or description) Sk•lc
Core Requirements (all 8 apply)
Discharge at Natural Location Number of Natural Discharge Locations:
Offsite Analysis Level: ) 2 / 3 dated: .o-t t (;nt l.t<e rA
Flow Control Level: 1 /0/ 3 or Exemption Number
(incl. facility summary sheet) Small Site BMPs
Conveyance System Spill containment located at:
Erosion and Sediment Control ESC Site Supervisor:
Contact Phone:
After Hours Phone:
Maintenance and Operation Responsibility: Privat / Public
IfPrivate, Maintenance Log Required: Yes /No
Financial Guarantees and Provided: (LW/ No
Liability IS iAcl 0-C-1-.414 le r
Water Quality Type. Bas / Sens. Lake / Enhanced Basicm / Bog
(include facility summary sheet) or ExemptionKNo.i‘ Li 1-0 9.nlnrL-nrn_r( 613;c,
Landscape Management Plan: Yes /LIVg,
Special Requirements (as applicable)
Area Specific Drainage Type: CDA/SDO/MDP/ BP/LMP/Shared Fac. /None
Requirements Name:
Floodplain/Floodway Delineation Type: Major / Minor / Exemption /101 nee
100-year Base Flood Elevation (or range):
Datum:
Flood Protection Facilities Describe:
Source Control Describe landuse: (4- (.444/C _
(comm./industrial landuse) Describe any structural controls:
2009 Surface Water Design Manual 1/9/2009
3
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL D
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Oil Control High-use Site: Yes / No
Treatment BMP:
Maintenance Agreement: Yes / No
with whom?
Other Drainage Structures
Describe:
Part 13 EROSION AND SEDIMENT CONTROL REQUIREMENTS
MINIMUM ESC REQUIREMENTS MINIMUM ESC REQUIREMENTS
DURING CONSTRUCTION AFTER CONSTRUCTION
U Clearing Limits ® Stabilize Exposed Surfaces
❑ Cover Measures ❑ Remove and Restore Temporary ESC Facilities
® Perimeter Protection ® Clean and Remove All Silt and Debris, Ensure
Traffic Area Stabilization Operation of Permanent Facilities
41
Sediment Retention U Flag Limits of SAO and open space
preservation areas
❑ Surface Water Collection
LI Other
Dewatering Control
4. Dust Control
Flow Control
Part 14 STORMWATER FACILITY DESCRIPTIONS (Note: Include Facility Summary and Sketch)
Flow Control Type/Description Water Quality Type/Description
11 Detention V4 Biofiltration
U Infiltration ❑ Wetpool
U Regional Facility Media Filtration I-trir►t Ife'S _
U Shared Facility U Oil Control
51 Flow Control (2$fim P - U Spill Control
BMPs
3 Flow Control BMPs
❑ Other Pt(m. $4,-
`
U Other
2009 Surface Water Design Manual 1/9/2009
4
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL �/10
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
Part 15 EASEMENTS/TRACTS Part 16 STRUCTURAL ANALYSIS
❑ Drainage Easement U Cast in Place Vault
U Covenant Si Retaining Wall
❑ Native Growth Protection Covenant 1 Rockery >4' High
❑ Tract ❑ Structural on Steep Slope
LI Other LI Other
Part 17 SIGNATURE OF PROFESSIONAL ENGINEER
I, or a civil engineer under my supervision, have visited the site. Actual site conditions as observed were
incorporated into this worksheet and the attached Technical Information Report. To the best of my
knowledge the information prpvid ere is accurate.
#— - ,Z..
Signed/Date
,Kc✓ i/—?-l3
2009 Surface Water Design Manual 1/9/2009
5
Site Location Map - Figure 2
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The Information included on this map has been compiled by King County staff from a varietyof sources and is sub ect 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
This document is not intended for use as a survey product.King County shall not be liable for any general,special,indirect,incidental,or consequential 3
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 King County
,j■/+ounty
this map or information on this map is prohibitedexcept by written permission of King County.
Date:3/5/2009 Source:King County iMAP-Property Information(hftp://www.metrokc.govIGISIiMAP)
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The information included On thismap
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County makes no representationsor
This document is not intended for use as a survy product.King County she
damages including,but not limited to,lrevenues or lost profits resulting from the use or misuse of the information
this map or information on this map is prohibited except by written permission of King County.
,, r t
Date:3;912009 Source:King County iMAP-Property Information(http://www.rnetrokc.govIGlSIIMAP)
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County Area,Washington
Soil Map—King V
(Figure 4) fl1)
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Meters
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0 50 100 200 300
USDA Natural Resources Web Soil Survey 2.1 3/6/2009
Conservation Service National Cooperative Soil Survey Page 1 of 3
Soil Map—King County Area,Washington
(Figure 4)
MAP LEGEND MAP INFORMATION
Area of Interest(AOI) as Very Stony Spot Map Scale: 1:1,800 if printed on A size(8.5"x 11")sheet.
Area of Interest(AOI) t Wet Spot The soil surveys that comprise your AOl were mapped at 1:24,000.
soils Other Please rely on the bar scale on each map sheet for accurate map
Soil Map Units measurements.
Special Line Features
Special Point Features Gully Source of Map: Natural Resources Conservation Service
Q) Blowout Web Soil Survey URL: http://websoilsurvey.nres.usda.gov
Short Steep Slope
® Borrow Pit Coordinate System: UTM Zone 10N NAD83
) Clay Spot ^ Other This product is generated from the USDA-NRCS certified data as of
Political Features the version date(s)listed below.
Closed Depression Cities
Soil Survey Area: King County Area,Washington
X Gravel Pit I 1 PLSS Township and Survey Area Data: Version 4, Nov 21,2006
Gravelly Spot Range Date(s)aerial images were photographed: 7/24/2006
PLSS Section
▪ Landfill The orthophoto or other base map on which the soil lines were
Water Features
compiled and digitizedprobablydiffers from the background
A. Lava Flow Oceans pg g
imagery displayed on these maps.As a result,some minor shifting
Marsh or swamp Streams and Canals of map unit boundaries may be evident.
Mine or Quarry
Transportation
p Miscellaneous Water Rails
© Perennial Water ,,hp Interstate Highways
v Rock Outcrop US Routes
{ Saline Spot Major Roads
Sandy Spot Local Roads
Severely Eroded Spot
Q Sinkhole
3> Slide or Slip
Rt Sodic Spot
E Spoil Area
{ Stony Spot
USDA Natural Resources Web Soil Survey 2.1 3/6/2009
;MU Conservation Service National Cooperative Soil Survey Page 2 of 3
10/0
Soil Map—King County Area,Washington Figure 4
Map Unit Legend
King County Area,Washington(WA633)
Map Unit Symbol Map Unit Name Acres in AOI Percent of AOI
AgC Alderwood gravelly sandy loam,6 to 15 4.5 29.0%
percent slopes
AgD Alderwood gravelly sandy loam,15 to 30 5.9 38.1%
percent slopes
BeD Beausite gravelly sandy loam,15 to 30 5.1 32.9%
percent slopes
Totals for Area of Interest 15.6 100.0%
L,D;a Natural Resources Web Soil Survey 2.1 3/6/2009
Conservation Service National Cooperative Soil Survey Page 3 of 3
APPENDIX B
OFF-SITE ANALYSIS
DRAINAGE SYSTEM TABLE AND MAP
OFF-SITE ANALYSIS DRAINAGE SYSTEM TABLE
SURFACE WATER DESIGN MANUAL, CORE REQUIREMENT#2
Basin: Black River Subbasin Name: Rolling Hills Subbasin Number:
Symbol Drainage Component Drainage Component Slope Distance from Existing Potential Problems Observations of field inspector,
Type, Name, and Size Description site discharge Problems resource reviewer, or resident
see map Type:sheet flow,Swale, drainage basin,vegetation,cover; % '/4 ml=1,320 ft constrictions, under capacity, ponding, tributary area, likelihood of problem,
stream, channel,pipe, depth,type of sensitive area, overtopping,flooding, habitat or organism overflow pathways, potential impacts
pond; Size:diameter, volume destruction,scouring, bank sloughing,
surface area sedimentation, incision,other erosion
A-B Pipe 12"CMP E side of Benson Rd S 5.8 0' (pipe None None This pipe is undocumented on
drainage conveyance. along the City's GIS&drainage
frontage) maps. The City GIS shows a
system just S of"A"which
drains W to Puget Dr. S.
B-C Pipe 12"CMP E side of Benson Rd S 6.0 0' (pipe None None This pipe is undocumented on
drainage conveyance. along the City's GIS and drainage
frontage) maps.
C-D Pipe 12"CMP E side of Benson Rd S 3.3 0' — 155' None None Ditto above.
drainage conveyance,w/
add'n of pond outlet from E
D-E Pipe 12"CMP E side of Benson Rd S 5.4 155'—213' None None Ditto above.
drainage conveyance.
E-F Pipe 12"RCP E side of Benson Rd S 6.9 213'—303' None None Ditto above. Survey shows this
drainage conveyance w/ system carries on to the N as
addition of runoff from E 12"RCP,but it is not
(Lodge @ Eagle Ridge). documented.
F-G Pipe 18"RCP Crosses Benson Rd to W ? 303' —553' None None This pipe is undocumented on
onto private property w/ the City's GIS and drainage
add'n of runoff from E. maps.
G-H Pipe 18"RCP Crosses private property ? 553' —653' None None This pipe is undocumented on
(presumed) and connects to the city the City's GIS and drainage
system described under maps.
"observations..." for A-B.
H-I Pipe 36"CMP, Parallels Talbot Rd 0.3 653' —793' None None No invert elev. info., length
1.046— 1.029 from City GIS maps.
I-J Pipe 42"CMP, Crosses Talbot Rd 793' —933' None None Ditto above.
1.029— 1.023
J-K Pipe 42", 1.023 -? Flows N on W side of 933' — 1,193' None None Ditto above.
Talbot Rd S.
L-M Pipe 42",?— 1.020 Flows N along Talbot Rd S 1,193' — None Flooding Historic flooding problems
under I-405 1.423' reported downstream
98-4\inB04
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Section 303(d) Map
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7 +? � v of category 5 Waters
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Pucet Sound , r 1 r Highways
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509 i s+m'l
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it 1 , 3 11 Estuary Names
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Tub+L 7h g - ` 4' ` l j -. —! r (limier
, -�. - Vit3 'Riven q ' III Marsh
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PROJECT LOCATION; Vii; 0 . �
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,_ ` _ D Impoundment
} n Land
PRINGBROOK CREEK -..., n Wator
Bati`:.r.eke - 4
oAt - it �+f Streams
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4btapLathd by the WA State f�partment of EcolagQ � 9 d/'
http://apps.ecy.wa.gov/servlet/com.esri.esrimap.Esrimap?ServiceName=state ov&Client... 11/20/2012
Ly,
Category 5: Polluted Waters/303(d) List
Rec Listing NameParameter Medium Waterbody ID Lower Upper
IDAddress Address
SPRINGBROOK (MILL) Dissolved
'1 1'7705 CREEK OxygenWater 1222256474521 1.444 3.465
2 13155 SPRINGBROOK (MILL) Fecal Coliform Water 1222256474521 1.444 3.465
CREEK
County
Rec 1County Name!
Township/Range/Section
Rec Township Township Township Range Range Range Section
Number Fraction Direction Number Fraction Direction Number
0 N 04 0 E 24
Streams
Rec Lat/Long ID Name
1222256474521 Black River
Category 5: Polluted Waters/303(d) List
Rec Listing ID Name Parameter Medium Waterbody ID Lower Address Upper Address
1 12567 BLACK RIVER Fecal Coliform Water 1222256474521 0.245 1.444
County
Rec County Name
1 King
Township/Range/Section
Township Township Township Range Range Range Section
IRec Number Fraction Direction Number Fraction Direction Number
11 23 O N 04 0 E 13
Water Bodies
Rec Lat/Long ID Name Feature Type
1 1222435474754 421
APPENDIX C
ANALYSIS AND DESIGN
APPENDIX C-1
DETENTION FACILITIES DESIGN
5 f o o ` BC f o EKIS f H QPan7_ M]E 1'3 o CFFOCES
(NORTH DET[ NTo )
e` :, �,; k
•FFSITE , , ', ar y
p"
TRIBUTARY AREA rn -. '� '
ORTH DETENTION - / "� "'� ,,.
--` —si .3x.....yii IV, 944,. <'�
�. 1=. TRIBUTARY AREA �:F ' Y
F
t A t5��'
z
Nt
iii,
.r
r r
..t\,,, ,h.-,. ,
t //fir _ kl
. ✓✓✓/// /"0 a"r"r'i''r 9ai4 t, " d -�. ,.k+ r i /'4.
r r= w NORTH BUILDING / -`£A `: , ,—, , ' '`r se ,wf � ;
N 1t ck ,
t ..2 k C aIru t _ // "aQ...� • i rvi. t .rr�S,,:' ,; �4,:'-',-;=—..-,',,N\,-,, ; .....
4 .s u _ It
// ,, - ' ��
•ER, .. •LE -/ , ��,.
µ ^4
I 72– - ^-� —�l' si; �/
,,,x,s- y, s`' %.'.,.. ROAD f
, 0160,
' ,ma
{SI 44234 r sn la roq•.°3c1[ .u':
EXISTING SF (AC): PROPOSED SF (AC):
IMPERVIOUS PERVIOUS
Z.-
FOREST: 49,300 (1.13 AC) BLDG: 18,806 (0.43 AC) 18,806 (0.43) Z
e ,
PERM. PAVE: 5,797 (0.13 AC) 2,899 (0.07) 2,898 (0.06) :-..1/4_
TOTAL: 49,300 (1.13 AC) SIDEWALK: 226 (NEG.) 226 (NEG.) 0
FOREST: 8,967 (0.21 AC) 8,967 (0.21)
LANDSCAPE: 15,504 (0.36 AC) 15,504 (0.36)
TOTAL: 49,300 (1.13 AC) 22,233 (0.50) 27,067 (0.63) j 50
100
mmilimid
SCALE: 1" = 100 ft.
/4- /11
sumpksl5 !l' /
1500 & 1600 Benson Apartments & offices (N Detention) tl, 1k) Pck QS t tr -/%^-1,)
Summary of 15-minute Predicted Runoff
4/8/13
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:existl5.tsf Mean= -1.485 StdDev= 0.262
Project Location:Sea-Tac Skew= 1. 598
---Annual Peak Flow Rates--- Flow Frequency Analysis
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
�
Computed Peaks 0.252 ,UO 100.00 0.990
Computed Peaks 0.175 50.00 0.980
Computed Peaks 0.121 25.00 0.960
Computed Peaks 0.073 10.00 0.900 SSI"Ni
Computed Peaks 0.066 8.00 0.875
Computed Peaks 0.049 5.00 0.800
Computed Peaks 0.028 2.00 0. 500
Computed Peaks 0.021 1.30 0.231
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:devl5.tsf Mean= -0. 532 StdDev= 0.168
Project Location:Sea-Tac Skew= 1.463
---Annual Peak Flow Rates--- Flow Frequency Analysis
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
Computed Peaks 1.05 Q1oD 100.00 0.990
Computed Peaks 0.842 50.00 0.980
Computed Peaks 0.670 25.00 0.960
Computed Peaks 0.491 10.00 0.900
Computed Peaks 0.462 8.00 0.875
Computed Peaks 0.384 5.00 0.800 /
Computed Peaks 0.268 2.00 0. 500
Computed Peaks 0.218 1.30 0.231
Increase in Q100 = 0.80 cfs (> 0.1 cfs) for only a portion of the site, so detention
is required.
Page 1
vaultl5
KCRTS Program. . .File Directory:
C:\KC_SWDM\KC_DATA\ t 3k f t I,JPUT
[C] CREATE a new Time Series
ST I15'NU t 11 _
1.13 0.00 0.000000 Till Forest
0.00 0.00 0.000000 Till Pasture -.
0.00 0.00 0.000000 Till Grass
0.00 0.00 0.000000 Outwash Forest
0.00 0.00 0.000000 Outwash Pasture
0.00 0.00 0.000000 Outwash Grass ! x :R.J1
0.00 0.00 0.000000 wetland JJJ
0.00 0.00 0.000000 Impervious
existl5.tsf
F
1.00000
F
[T] Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
existl5.tsf
existl5.pks
[R] RETURN to Previous Menu
[C] CREATE a new Time Series
ST
0.21 0.00 0.000000 Till Forest
0.00 0.00 0.000000 Till Pasture
0.42 0.00 0.000000 Till Grass
0.000.00 0.000000 Outwash Forest
0.00 0.00 0.000000 Outwash Pasture ��
0.00 0.00 0.000000 Outwash Grass
0.00 0.00 0.000000 Wetland
0.50 0.00 0.000000 Impervious
devl5.tsf
F
1.00000
F
[T] Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
devl5.tsf
devl5.pks
[R] RETURN to Previous Menu
[x] eXit KCRTS Program
Page 1
N- 41/1Z
sumpks
1500 & 1600 Benson Apartments & Offices (N Detention) Aftj N PL f\� ( ,12,L_Y)
Summary of Predicted Runoff
4/8/13
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:exist.tsf Mean= -1. 563 StdDev= 0.233
Project Location:Sea-Tac Skew= -0.132
---Annual Peak Flow Rates--- Flow Frequency Analysis
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
Computed Peaks 0.090 100.00 0.990
Computed Peaks 0.079 50.00 0.980
Computed Peaks 0.068 25.00 0.960
Computed Peaks 0.054 10.00 0.900
Computed Peaks 0.051 8.00 0.875 /�' �� ���
Computed Peaks 0.043 5.00 0.800 /
Computed Peaks 0.028 2.00 0. 500
Computed Peaks 0.018 1.30 0.231
Flow Frequency Analysis Log Pearson III Coefficients
Time Series File:dev.tsf Mean= -0.805 StdDev= 0.117
Project Location:Sea-Tac Skew= 0.390
---Annual Peak Flow Rates--- Flow Frequency Analysis
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
Computed Peaks 0.316 100.00 0.990
Computed Peaks 0.287 50.00 0.980
Computed Peaks 0.259 25.00 0.960
Computed Peaks 0.223 10.00 0.900 +
Computed Peaks 0.216 8.00 0.875 //lc 'Ai
Computed Peaks 0.195 5.00 0.800
Computed Peaks 0.154 2.00 0. 500
Computed Peaks 0.127 1. 30 0.231
Level 2 Detention Vault (10')
Int size=[0.079-(0.028'0. 5)]/(36-1)
=0.002
1st Int.=0.028*0. 5
=0.014
Qmax=(4/3'0.014)
=0.019
Orif(2)=3/4'10
=7. 5'
Page 1
N- 5/ QZ
vault
KCC:\KCRSWDM\KTS CCrDATA\.File Directory: `, elb �� i L)P'J,,.,. ci
[C] CREATE a new Time Series 'v 1�
ST '
1.13 0.00 0.000000 Ti 11 Forest 1 ,)O2�--Y ► -
0.00 0.00 0.000000 Till Pasture
0.00 0.00 0.000000 Till Grass
0.00 0.00 0.000000 outwash Forest
0.00 0.00 0.000000 Outwash Pasture
0.00 0.00 0.000000 Outwash Grass 0‘ 111`311
0.00 0.00 0.000000 wetland
0.00 0.00 0.000000 Impervious
exiSt.tsf
F
1.00000
T
[T] Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
exist.tsf
exist.pks
[R] RETURN to Previous Menu
[C] CREATE a new Time Series
ST
0.21 0.00 0.000000 Till Forest
0.00 0.00 0.000000 Till Pasture
0.42 0.00 0.000000 Till Grass
0.00 0.00 0.000000 Outwash Forest
0.00 0.00 0.000000 Outwash Pasture J
0.00 0.00 0.000000 Outwash Grass 1 ,--",./ Lt� c;.,ti
0.00 0.00 0.000000 wetland
0. 50 0.00 0.000000 Impervious
dev.tsf
F
1.00000
T
[T] Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
dev.tsf
dev.pks
[R] RETURN to Previous Menu
[X] eXit KCRTS Program
Page 1
- 6/ ,v
1500 & 1600 Benson Apartments & Offices (N Detention)
te �t
ReMQ (LvT//
Retenn3 tion/Detention Facility 'N
Type of Facility: Detention Vault f \ tN
Facility Length: 54.00 ft nl
Facility Width: 20.00 ft
Facility Area: 1080. sq. ft
Effective Storage Depth: 10.00 ft
Stage 0 Elevation: 0.00 ft
Storage Volume: 10800. cu. ft
Riser Head: 10.00 ft
Riser Diameter: 12.00 inches
Number of orifices: 2
Full Head Pipe
Orifice # Height Diameter Discharge Diameter
(ft) (in) (CFS) (in)
1 0.00 0.47 0.019
2 6.00 0.86 0.040 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 11. 0.000 0.001 0.00
0.02 0.02 22. 0.000 0.001 0.00
0.03 0.03 32. 0.001 0.001 0.00
0.04 0.04 43. 0.001 0.001 0.00
0.21 0.21 227. 0.005 0.003 0.00
0.38 0.38 410. 0.009 0.004 0.00
0.55 0.55 594. 0.014 0.004 0.00
0.72 0.72 778. 0.018 0.005 0.00
0.89 0.89 961. 0.022 0.006 0.00
1.06 1.06 1145. 0.026 0.006 0.00
1.23 1.23 1328. 0.030 0.007 0.00
1.40 1.40 1512. 0.035 0.007 0.00
1.57 1.57 1696. 0.039 0.008 0.00
1.74 1.74 1879. 0.043 0.008 0.00
1.91 1.91 2063. 0.047 0.008 0.00
2.08 2.08 2246. 0.052 0.009 0.00
2.25 2.25 2430. 0.056 0.009 0.00
2.42 2.42 2614. 0.060 0.009 0.00
2.59 2.59 2797. 0.064 0.010 0.00
2.76 2.76 2981. 0.068 0.010 0.00
2.93 2.93 3164. 0.073 0.010 0.00
3.09 3.09 3337. 0.077 0.011 0.00
3.26 3.26 3521. 0.081 0.011 0.00
3.43 3.43 3704. 0.085 0.011 0.00
3.60 3.60 3888. 0.089 0.011 0.00
3.77 3.77 4072. 0.093 0.012 0.00
3.94 3.94 4255. 0.098 0.012 0.00
4.11 4.11 4439. 0.102 0.012 0.00
4.28 4.28 4622. 0.106 0.012 0.00
4.45 4.45 4806. 0.110 0.013 0.00
4.62 4.62 4990. 0.115 0.013 0.00
4.79 4.79 5173. 0.119 0.013 0.00
4.96 4.965357. 0.123 0.013 0.00
5.13 5.13 5540. 0.127 0.014 0.00
5.30 5.30 5724. 0.131 0.014 0.00
5.47 5.47 5908. 0.136 0.014 0.00
5.64 5.64 6091. 0.140 0.014 0.00
5.81 5.81 6275. 0.144 0.014 0.00
5.98 5.98 6458. 0.148 0.015 0.00
6.00 6.00 6480. 0.149 0.015 0.00
6.01 6.01 6491. 0.149 0.015 0.00
6.02 6.02 6502. 0.149 0.015 0.00
6.03 6.03 6512. 0.150 0.016 0.00
6.04 6.04 6523. 0.150 0.019 0.00
6.05 6.05 6534. 0.150 0.019 0.00
6.06 6.06 6545. 0.150 0.020 0.00
6.07 6.07 6556. 0.150 0.020 0.00
6.24 6.24 6739. 0.155 0.025 0.00
6.41 6.41 6923. 0.159 0.028 0.00
6.58 6.58 7106. 0.163 0.031 0.00
6.75 6.75 7290. 0.167 0.033 0.00
6.92 6.92 7474. 0.172 0.035 0.00
7.09 7.09 7657. 0.176 0.037 0.00
7.26 7.26 7841. 0.180 0.039 0.00
7.43 7.43 8024. 0.184 0.040 0.00
7. 60 7.60 8208. 0.188 0.042 0.00
7.77 7.77 8392. 0.193 0.043 0.00
7.94 7.94 8575. 0.197 0.045 0.00
8.11 8.11 8759. 0.201 0.046 0.00
8.28 8.28 8942. 0.205 0.047 0.00
8.44 8.44 9115. 0.209 0.049 0.00
8.61 8.61 9299. 0.213 0.050 0.00
8.78 8.78 9482. 0.218 0.051 0.00
8.95 8.95 9666. 0.222 0.052 0.00
9.12 9.12 9850. 0.226 0.054 0.00
9.29 9.29 10033. 0.230 0.055 0.00
9.46 9.46 10217. 0.235 0.056 0.00
9.63 9.63 10400. 0.239 0.057 0.00
9.80 9.80 10584. 0.243 0.058 0.00
9.97 9.97 10768. 0.247 0.059 0.00
10.00 10.00 10800. 0.248 0.059 0.00
10.10 10.10 10908. 0.250 0.368 0.00
10.20 10.20 11016. 0.253 0.931 0.00
10.30 10.30 11124. 0.255 1.660 0.00
10.40 10.40 11232. 0.258 2.450 0.00
10.50 10.50 11340. 0.260 2.740 0.00
10.60 10.60 11448. 0.263 2.990 0.00
10.70 10.70 11556. 0.265 3.230 0.00
10.80 10.80 11664. 0.268 3.450 0.00
10.90 10.90 11772. 0.270 3.650 0.00
11.00 11.00 11880. 0.273 3.850 0.00
11.10 11.10 11988. 0.275 4.030 0.00
11.20 11.20 12096. 0.278 4.210 0.00
11.30 11.30 12204. 0.280 4.380 0.00
11.40 11.40 12312. 0.283 4.540 0.00
11.50 11.50 12420. 0.285 4.700 0.00
11.60 11.60 12528. 0.288 4.850 0.00
11.70 11.70 12636. 0.290 5.000 0.00
Hyd Inflow Outflow Peak Storage
Target Calc Stage Elev (Cu-Ft) (Ac-Ft)
1 0.17 0.09 0.06 9.82 9.82 10609. 0.244
2 0.20 ******* 0.06 9.68 9.68 10459. 0.240
3 0.30 ******* 0.05 9.27 9.27 10014. 0.230
4 0.21 ******* 0.05 8.20 8.20 8852. 0.203
5 0.17 ******* 0.05 8.06 8.06 8708. 0.200
6 0.25 ******* 0.04 7.41 7.41 8008. 0.184
7 0.12 ******* 0.01 5.99 5.99 6474. 0.149
8 0.11 ******* 0.01 4.59 4.59 4954. 0.114
N - i,-
Route Time Series through Facility
Inflow Time Series File:dev.tsf
Outflow Time Series File:rdout
Inflow/Outflow Analysis
Peak Inflow Discharge: 0.301 CFS at 6:00 on Jan 9 in 1990
Peak Outflow Discharge: 0.059 CFS at 21:00 on Feb 9 in 1951
Peak Reservoir Stage: 9.90 Ft
Peak Reservoir Elev: 9.90 Ft
Peak Reservoir Storage: 10695. Cu-Ft
0.246 Ac-Ft
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:rdout.tsf Mean= -1.667 StdDev= 0.245
Project Location:Sea-Tac Skew= 0.326
---Annual Peak Flow Rates--- Flow Frequency Analysis
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) (ft) Period
0.013 38 2/22/49 22:00 0.059 9.90 1 89.50 0.989
0.033 14 3/05/50 6:00 0.057 9.69 2 32.13 0.969
0.059 1 2/09/51 21:00 0.055 9.27 3 19.58 0.949
0.012 43 2/04/52 8:00 0.050 8.59 4 14.08 0.929
0.014 31 1/23/53 8:00 0.049 8.51 5 10.99 0.909
0.017 27 1/07/54 20:00 0.047 8.20 6 9.01 0.889
0.014 32 2/08/55 23:00 0.046 8.06 7 7.64 0.869
0.040 11 1/06/56 11:00 0.045 7.96 8 6.63 0.849
0.014 33 2/26/57 12:00 0.045 7.93 9 5.86 0.829
0.027 20 1/17/58 7:00 0.041 7.53 10 5.24 0.809
0.013 39 1/27/59 1:00 0.040 7.35 11 4.75 0.789
0.050 4 11/21/59 5:00 0.036 6.98 12 4.34 0.769
0.031 17 11/24/60 11:00 0.034 6.87 13 3.99 0.749
0.011 47 12/24/61 6:00 0.033 6.79 14 3.70 0.729
0.018 26 11/27/62 5:00 0.032 6.68 15 3.44 0.709
0.022 24 11/19/63 17:00 0.032 6.66 16 3.22 0.690
0.032 15 12/01/64 2:00 0.031 6.62 17 3.03 0.670
0.014 36 1/07/66 4:00 0.030 6.50 18 2.85 0.650
0.025 22 12/15/66 8:00 0.027 6.37 19 2.70 0.630
0.014 34 1/20/68 22:00 0.027 6.35 20 2.56 0.610
0.014 35 12/11/68 10:00 0.026 6.29 21 2.44 0.590
0.020 25 1/27/70 4:00 0.025 6.26 22 2.32 0.570
0.015 28 12/07/70 13:00 0.023 6.17 23 2.22 0.550
0.047 6 3/06/72 22:00 0.022 6.15 24 2.13 0.530
0.034 13 12/26/72 6:00 0.020 6.07 25 2.04 0.510
0.026 21 1/16/74 18:00 0.018 6.04 26 1.96 0.490
0.014 37 12/27/74 22:00 0.017 6.03 27 1.89 0.470
0.015 29 12/04/75 9:00 0.015 6.02 28 1.82 0.450
0.010 49 8/26/77 7:00 0.015 5.91 29 1.75 0.430
0.030 18 12/15/77 18:00 0.014 5.83 30 1.70 0.410
0.011 48 2/13/79 0:00 0.014 5.78 31 1.64 0.390
0.045 9 12/17/79 20:00 0.014 5.76 32 1.59 0.370
0.014 30 12/30/80 23:00 0.014 5.73 33 1.54 0.350
0.041 10 10/06/81 18:00 0.014 5.51 34 1.49 0.330
0.023 23 1/08/83 1:00 0.014 5.38 35 1.45 0.310
0.012 42 12/10/83 20:00 0.014 5.33 36 1.41 0.291
0.012 40 11/04/84 1:00 0.014 5.12 37 1.37 0.271
0.036 12 1/19/86 1:00 0.013 4.80 38 1.33 0.251
0.046 7 11/24/86 8:00 0.013 4.76 39 1.30 0.231
0.012 41 12/10/87 8:00 0.012 4.04 40 1.27 0.211
0.012 44 11/05/88 22:00 0.012 3.86 41 1.24 0.191
0.055 3 1/09/90 14:00 0.012 3.86 42 1.21 0.171
0.049 5 4/05/91 6:00 0.012 3.85 43 1.18 0.151
0.027 19 1/31/92 6:00 0.012 3.77 44 1.15 0.131
4 _ (4/IL
0.011 46 3/23/93 18:00 0.012 3.76 45 1.12 0.111
0.010 50 2/17/94 22:00 0.011 3.68 46 1.10 0.091
0.032 16 12/27/94 7:00 0.011 3.36 47 1.08 0.071
0.057 2 2/09/96 4:00 0.011 3.13 48 1.05 0.051
0.045 8 1/02/97 12:00 0.010 2.91 49 1.03 0.031
0.012 45 10/30/97 16:00 0.010 2.80 50 1.01 0.011
Computed Peaks 0.091 10.01 100.00 0.990
Computed Peaks 0.075 10.01 50.00 0.980
Computed Peaks 0.061 10.00 25.00 0.960
Computed Peaks 0.045 7.95 10.00 0.900
Computed Peaks 0.042 7.61 8.00 0.875
Computed Peaks 0.034 6.85 5.00 0.800
Computed Peaks 0.021 6.10 2.00 0.500
Computed Peaks 0.014 5.12 1.30 0.231
Flow Duration from Time Series File:rdout.tsf
Cutoff Count Frequency CDF Exceedence_Probability
CFS $ $ $
0.001 222118 50.712 50.712 49.288 0.493E+00
0.002 53663 12.252 62.964 37.036 0.370E+00
0.004 50613 11.555 74.519 25.481 0.255E+00
0.006 22872 5.222 79.741 20.259 0.203E+00
0.007 29724 6.786 86.527 13.473 0.135E+00
0.009 19887 4.540 91.068 8.932 0.893E-01
0.011 17352 3.962 95.029 4.971 0.497E-01
0.012 11678 2.666 97.696 2.304 0.230E-01
0.014 4547 1.038 98.734 1.266 0.127E-01
0.015 3835 0.876 99.609 0.391 0.391E-02
0.017 49 0.011 99.621 0.379 0.379E-02
0.019 23 0.005 99.626 0.374 0.374E-02
0.020 131 0.030 99.656 0.344 0.344E-02
0.022 156 0.036 99.691 0.309 0.309E-02
0.024 130 0.030 99.721 0.279 0.279E-02
0.025 109 0.025 99.746 0.254 0.254E-02
0.027 135 0.031 99.777 0.223 0.223E-02
0.028 111 0.025 99.802 0.198 0.198E-02
0.030 99 0.023 99.825 0.175 0.175E-02
0.032 90 0.021 99.845 0.155 0.155E-02
0.033 100 0.023 99.868 0.132 0.132E-02
0.035 74 0.017 99.885 0.115 0.115E-02
0.037 80 0.018 99.903 0.097 0.968E-03
0.038 62 0.014 99.917 0.083 0.826E-03
0.040 75 0.017 99.934 0.066 0.655E-03
0.041 41 0.009 99.944 0.056 0.562E-03
0.043 39 0.009 99.953 0.047 0.473E-03
0.045 43 0.010 99.963 0.037 0.374E-03
0.046 41 0.009 99.972 0.028 0.281E-03
0.048 22 0.005 99.977 0.023 0.231E-03
0.049 19 0.004 99.981 0.019 0.187E-03
0.051 21 0.005 99.986 0.014 0.139E-03
0.053 15 0.003 99.989 0.011 0.105E-03
0.054 10 0.002 99.992 0.008 0.822E-04
0.056 18 0.004 99.996 0.004 0.411E-04
0.058 12 0.003 99.999 0.001 0.137E-04
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 %Change Probability Base New %Change
0.014 I 0.97E-02 0.12E-01 26.0 I 0.97E-02 0.014 0.014 0.4
0.019 I 0.50E-02 0.37E-02 -24.9 1 0.50E-02 0.019 0.015 -22.2
it'- '°1,1,
0.023 0.28E-02 0.28E-02 -1.4 0.28E-02 0.023 0.023 -0.8
0.028 0.17E-02 0.20E-02 19.6 0.17E-02 0.028 0.031 8.9
0.033 0.10E-02 0.14E-02 29.4 0.10E-02 0.033 0.036 8.7
0.038 0.67E-03 0.86E-03 27.1 0.67E-03 0.038 0.040 4.9
0.043 0.45E-03 0.51E-03 14.4 0.45E-03 0.043 0.044 2.6
0.047 0.30E-03 0.24E-03 -21.1 0.30E-03 0.047 0.046 -3.2
0.052 0.21E-03 0.12E-03 -45.7 0.21E-03 0.052 0.049 -6.3
0.057 0.12E-03 0.27E-04 -76.5 0.12E-03 0.057 0.052 -8.4
0.062 0.59E-04 0.00E+00 -100.0 0.59E-04 0.062 0.055 -10.8
0.066 0.32E-04 0.00E+00 -100.0 0.32E-04 0.066 0.057 -14.6
0.071 0.68E-05 0.00E+00 -100.0 0.68E-05 0.071 0.058 -17.8
0.076 0.23E-05 0.00E+00 -100.0 0.23E-05 0.076 0.059 -22.7
Maximum positive excursion = 0.003 cfs ( 9.3%) 4%0%1 o k_,
occurring at 0.029 cfs on the Base Data:exist.tsf
and at 0.031 cfs on the New Data:rdout.tsf
Maximum negative excursion = 0.006 cfs (-27.4%)
occurring at 0.021 cfs on the Base Data:exist.tsf
and at 0.015 cfs on the New Data:rdout.tsf
Return Period
2 5 10 20 E L
— 50 10Q
_ o rdout.pks in Sea-Tac
• exist.pks j��
� .
...-4r...-
4, .�—��
R
N DETTa•ril oiv VAu.0-.-" rr o o i �' o
•i•oao ° �'
. °•
--
� -
0
U — • o 00-0 0 0
J.-_ • o -
2 10 Z �- --- - -
co -- — —
——
- '
- •
U
-•
L
103 I I I I 1 I ----1— , - I , 1
1 2 5 10 20 30 40 50 60 70 80 90 95 98 99
Cumulative Probability
CO
o-
rdout.dur o
target.dur .
ti
•
•
•
u_
a)
CD o •
CD.
o • ,
AILoo
•
•
•
•
0
Q • I
O 1 i ! 1 I I 1 1 ! 1 I I I 1 i I I [ I I I I i ! I I I I 1 1 1 1111 I I 1 1 1 1111
10-6 10-5 104 103 102 10-1100 .-
Probability Exceedence N
z 6 0 82, z_ j off D FRIED QPQTti-1,`•JME = o CFFTICES
(ROUTH DD[VENT ON)
„
Ltr
o ,,\ ' �'
Jo,
I r
=
} ';';''':4;'"k4c PE BLE SOUTH DETENTION' TRIBUTARY AREA� r — MENT _I I�I, .7---
� �' 19 •, a
"^f / %11.--''''.:-0:1-4.,-;‘, " ®
�"#i "Ai3 ,', VVI _! \ M ,k,
\\j. a .''' .v..�MM@� '. * •—r\, i ® �}� /j-%F° 'c w��� .j //e'/e-'NU ,./1;^/j/ iat �`.r'rs- ,r \ //
as
` L � .
-t
o-
—
EXISTING SF (AC): PROPOSED SF (AC):
IMPERMEABLE PERMEABLE
FOREST: 53,825 (1.24 AC) BLDG: 19,966 (0.46 AC) 19,966 (0.46) 2ED
PAVEMENT: 4,351 (0.10 AC) 4,351 (0.10)
PERM. PAVE.: 11,932 (0.27) 5,966 (0.14) 5,966 (0.13) tA
SIDEWALK: 1,658 (0.04 AC) 1,658 (0.04) I
LANDSCAPE: 15,918 (0.37 AC) 15,918 (0.37)
TOTAL: 53,825 (1.24 AC) 31,941 (0.74) 21,884 (0.50)
o so loo
I
nsimmi
SCALE: 1" = 100 ft.
S- %___
sumpksl5 �. OS( (5- -M f,
1500 & 1600 Benson Apartments & Offices (S Detention) S- iNI
Summary of 15-Minute Time steps Predicted Runoff
4/8/13
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:existl5.tsf Mean= -1.445 StdDev= 0.262
Project Location:Sea-Tac Skew= 1. 597
---Annual Peak Flow Rates--- Flow Frequency Analysis
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
Q
Computed Peaks 0.277 ,0v 100.00 0.990 -,
Computed Peaks 0.192 50.00 0.980
Computed Peaks 0.132 25.00 0.960 R
Computed Peaks 0.080 10.00 0.900 ll
tic,
Computed Peaks 0.072 8.00 0.875
Computed Peaks 0.054 5.00 0.800
Computed Peaks 0.031 2.00 0. 500
Computed Peaks 0.023 1.30 0.231
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:devl5.tsf Mean= -0.376 StdDev= 0.162
Project Location:Sea-Tac skew= 1.364
---Annual Peak Flow Rates--- Flow Frequency Analysis
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
Computed Peaks 1.41Q 100.00 0.990
Computed Peaks 1.15 (uL) 50.00 0.980 \\
Computed Peaks 0.927 25.00 0.960 _
Computed Peaks 0.692 10.00 0.900 ,
Computed Peaks 0.653 8.00 0.875 +
Computed Peaks 0. 548 5.00 0.800
Computed Peaks 0.388 2.00 0. 500
Computed Peaks 0.316 1.30 0.231
Page 1
'1 Z
vault 15 5 'RPV NGV DA' ""4
KCRTS Program. . . File Directory:
C:\KC_SWDM\KC_DATA\ 15- aV\ pN« 6'�tR ,S Ca-to
[C] CREATE a new Time Series
ST
1.24 0.00 0.000000 Till Forest
0.00 0.00 0.000000 Till Pasture
0.00 0.00 0.000000 Till Grass
0.00 0.00 0.000000 Outwash Forest /
0.00 0.00 0.000000 Outwash Pasture {S 1tJ(
0.00 0.00 0.000000 Outwash Grass
0.00 0.00 0.000000 Wetland
0.00 0.00 0.000000 Impervious
existl5.tsf
F
1.00000
F
[T] Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
existl5.tsf
existl5.pks
[R] RETURN to Previous Menu
[C] CREATE a new Time Series
ST
0.00 0.00 0.000000 Till Forest
0.00 0.00 0.000000 Till Pasture
0. 50 0.00 0.000000 Till Grass
0.00 0.00 0.000000 Outwash Forest
0.00 0.00 0.000000 Outwash Pasture ,,,; ,.-' l r
0.00 0.00 0.000000 Outwash Grass
0.00 0.00 0.000000 Wetland
0.74 0.00 0.000000 Impervious
devl5.tsf
F
1.00000
F
[T] Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
devl5.tsf
devl5.pks
[R] RETURN to Previous Menu
[X] eXit KCRTS Program
Page 1
sumpks « -Si^Ill -0
1500 & 1600 Benson Apartments & offices (S Detention)
Summary of Predicted Runoff 0 Y t t_oS
4/8/13
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:exist.tsf Mean= -1. 522 StdDev= 0.232
Project Location:Sea-Tac Skew= -0.138
---Annual Peak Flow Rates--- Flow Frequency Analysis
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
Computed Peaks 0.099 100.00 0.990
Computed Peaks 0.086 50.00 0.980
Computed Peaks 0.075 25.00 0.960 �'S'��(A
Computed Peaks 0.059 10.00 0.900 .
Computed Peaks 0.056 8.00 0.875
Computed Peaks 0.047 5.00 0.800
computed Peaks 0.030 2.00 0. 500
Computed Peaks 0.020 1.30 0.231
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:dev.tsf Mean= -0.658 StdDev= 0.111
Project Location:Sea-Tac Skew= 0.424
---Annual Peak Flow Rates--- Flow Frequency Analysis
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
Computed Peaks 0.431 100.00 0.990 \
Computed Peaks 0.393 50.00 0.980 t 0
Computed Peaks 0.356 25.00 0.960
Computed Peaks 0.308 10.00 0.900
Computed Peaks 0.298 8.00 0.875
Computed Peaks 0.271 5.00 0.800
Computed Peaks 0.216 2.00 0. 500 I
Computed Peaks 0.181 1.30 0.231
Level 2 Detention vault (10')
Int Size=[0.086-(0.030;°0. 5)]/(36-1)
=0.002
1st Int.=0.030*0. 5
=0.015
Qmax=(4/3"0.015)
=0.020
orif(2)=3/4*10.0
=7. 5'
Page 1
S_ 5 2-
vault
KCRTS Program. . . File Directory:
C:\KC_SWDM\KC_DATA\ clVtS1 1 NA-1r. A
[C]
CREATE a new Time Series
ST � � I7M(: SmS
1.24 0.00 0.000000 Till Forest
0.00 0.00 0.000000 Till Pasture
0.00 0.00 0.000000 Till Grass
0.00 0.00 0.000000 outwash Forest
0.00 0.00 0.000000 Outwash Pasture 07)N4i
0.00 0.00 0.000000 outwash Grass I
0.00 0.00 0.000000 wetland /
0.00 0.00 0.000000 Impervious
exist.tsf
F
1.00000
T
[T] Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
exist.tsf
exist.pks
[R] RETURN to Previous Menu
[C] CREATE a new Time Series
ST
0.00 0.00 0.000000 Till Forest
0.00 0.00 0.000000 Till Pasture
0. 50 0.00 0.000000 Till Grass
0.00 0.00 0.000000 Outwash Forest
'Y
0.00 0.00 0.000000 Outwash Pasture si' :'
0.00 0.00 0.000000 Outwash Grass
0.00 0.00 0.000000 wetland
0.74 0.00 0.000000 Impervious
dev.tsf
F
1.00000
T
[T] Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
dev.tsf
dev.pks
[R] RETURN to Previous Menu
[X] eXit KCRTS Program
Page 1
C- 9/(
1500 & 1600 Benson Apartments & Offices (S Detention) SAllEjl..37 ON [u1Y
4/8/13
Retention/Detention Facility i '/ /
Type of Facility: Detention Vault � `.t�V
Facility Length: 88.00 ft
Facility Width: 20.00 ft
Facility Area: 1760. sq. ft
Effective Storage Depth: 10.00 ft
Stage 0 Elevation: 0.00 ft
Storage Volume: 17600. cu. ft
Riser Head: 10.00 ft
Riser Diameter: 12.00 inches
Number of orifices: 2
Full Head Pipe
Orifice # Height Diameter Discharge Diameter
(ft) (in) (CFS) (in)
1 0.00 0.47 0.019
2 5.80 0.70 0.027 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 18. 0.000 0.001 0.00
0.02 0.02 35. 0.001 0.001 0.00
0.03 0.03 53. 0.001 0.001 0.00
0.04 0.04 70. 0.002 0.001 0.00
0.21 0.21 370. 0.008 0.003 0.00
0.38 0.38 669. 0.015 0.004 0.00
0.55 0.55 968. 0.022 0.004 0.00
0.72 0.72 1267. 0.029 0.005 0.00
0.89 0.89 1566. 0.036 0.006 0.00
1.06 1.06 1866. 0.043 0.006 0.00
1.23 1.23 2165. 0.050 0.007 0.00
1.40 1.40 2464. 0.057 0.007 0.00
1.57 1.57 2763. 0.063 0.008 0.00
1.74 1.74 3062. 0.070 0.008 0.00
1.91 1.91 3362. 0.077 0.008 0.00
2.08 2.08 3661. 0.084 0.009 0.00
2.25 2.25 3960. 0.091 0.009 0.00
2.42 2.42 4259. 0.098 0.009 0.00
2.59 2.59 4558. 0.105 0.010 0.00
2.76 2.76 4858. 0.112 0.010 0.00
2.93 2.93 5157. 0.118 0.010 0.00
3.09 3.09 5438. 0.125 0.011 0.00
3.26 3.26 5738. 0.132 0.011 0.00
3.43 3.43 6037. 0.139 0.011 0.00
3.60 3.60 6336. 0.145 0.011 0.00
3.77 3.77 6635. 0.152 0.012 0.00
3.94 3.94 6934. 0.159 0.012 0.00
4.11 4.11 7234. 0.166 0.012 0.00
4.28 4.28 7533. 0.173 0.012 0.00
4.45 4.45 7832. 0.180 0.013 0.00
4.62 4.62 8131. 0.187 0.013 0.00
4.79 4.79 8430. 0.194 0.013 0.00
4.96 4.96 8730. 0.200 0.013 0.00
5.13 5.13 9029. 0.207 0.014 0.00
5.30 5.30 9328. 0.214 0.014 0.00
5.47 5.47 9627. 0.221 0.014 0.00
5.64 5.64 9926. 0.228 0.014 0.00
5.80 5.80 10208. 0.234 0.014 0.00
5.81 5.81 10226. 0.235 0.015 0.00
5.82 5.82 10243. 0.235 0.015 0.00
5.83 5.83 10261. 0.236 0.016 0.00
5.84 5.84 10278. 0.236 0.017 0.00
5.85 5.85 10296. 0.236 0.017 0.00
5.86 5.86 10314. 0.237 0.018 0.00
6.03 6.03 10613. 0.244 0.021 0.00
6.20 6.20 10912. 0.251 0.023 0.00
6.37 6.37 11211. 0.257 0.025 0.00
6.54 6.54 11510. 0.264 0.027 0.00
6.71 6.71 11810. 0.271 0.028 0.00
6.88 6.88 12109. 0.278 0.029 0.00
7.04 7.04 12390. 0.284 0.031 0.00
7.21 7.21 12690. 0.291 0.032 0.00
7.38 7.38 12989. 0.298 0.033 0.00
7.55 7.55 13288. 0.305 0.034 0.00
7.72 7.72 13587. 0.312 0.035 0.00
7.89 7.89 13886. 0.319 0.036 0.00
8.06 8.06 14186. 0.326 0.037 0.00
8.23 8.23 14485. 0.333 0.038 0.00
8.40 8.40 14784. 0.339 0.039 0.00
8.57 8.57 15083. 0.346 0.040 0.00
8.74 8.74 15382. 0.353 0.041 0.00
8.91 8.91 15682. 0.360 0.041 0.00
9.08 9.08 15981. 0.367 0.042 0.00
9.25 9.25 16280. 0.374 0.043 0.00
9.42 9.42 16579. 0.381 0.044 0.00
9.59 9.59 16878. 0.387 0.044 0.00
9.76 9.76 17178. 0.394 0.045 0.00
9.93 9.93 17477. 0.401 0.046 0.00
10.00 10.00 17600. 0.404 0.046 0.00
10.10 10.10 17776. 0.408 0.355 0.00
10.20 10.20 17952. 0.412 0.918 0.00
10.30 10.30 18128. 0.416 1.650 0.00
10.40 10.40 18304. 0.420 2.440 0.00
10.50 10.50 18480. 0.424 2.720 0.00
10.60 10.60 18656. 0.428 2.980 0.00
10.70 10.70 18832. 0.432 3.210 0.00
10.80 10.80 19008. 0.436 3.430 0.00
10.90 10.90 19184. 0.440 3.640 0.00
11.00 11.00 19360. 0.444 3.830 0.00
11.10 11.10 19536. 0.448 4.020 0.00
11.20 11.20 19712. 0.453 4.190 0.00
11.30 11.30 19888. 0.457 4.360 0.00
11.40 11.40 20064. 0.461 4.530 0.00
11.50 11.50 20240. 0.465 4.680 0.00
11.60 11.60 20416. 0.469 4.840 0.00
11.70 11.70 20592. 0.473 4.980 0.00
11.80 11.80 20768. 0.477 5.130 0.00
Hyd Inflow Outflow Peak Storage
Target Calc Stage Elev (Cu-Ft) (Ac-Ft)
1 0.23 0.10 0.08 10.01 10.01 17619. 0.404
2 0.26 ******* 0.04 9.57 9.57 16845. 0.387
3 0.25 ******* 0.04 8.83 8.83 15548. 0.357
4 0.29 ******* 0.04 8.56 8.56 15074. 0.346
5 0.24 ******* 0.04 8.50 8.50 14961. 0.343
6 0.21 ******* 0.03 7.67 7.67 13501. 0.310
7 0.19 ******* 0.02 6.03 6.03 10613. 0.244
8 0.23 ******* 0.01 4.98 4.98 8772. 0.201
Route Time Series through Facility
Inflow Time Series File:dev.tsf
Outflow Time Series File:rdout
Inflow/Outflow Analysis
Peak Inflow Discharge: 0.403 CFS at 6:00 on Jan 9 in 1990
Peak Outflow Discharge: 0.087 CFS at 20:00 on Feb 9 in 1951
Peak Reservoir Stage: 10.01 Ft
Peak Reservoir Elev: 10.01 Ft
Peak Reservoir Storage: 17623. Cu-Ft
0.405 Ac-Ft
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:rdout.tsf Mean= -1.667 StdDev= 0.218
Project Location:Sea-Tac Skew= 0.303
---Annual Peak Flow Rates--- Flow Frequency Analysis
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) (ft) Period
0.013 38 2/22/49 22:00 0.087 10.01 1 89.50 0.989
0.028 16 3/05/50 7:00 0.044 9.58 2 32.13 0.969
0.087 1 2/09/51 20:00 0.041 8.83 3 19.58 0.949
0.012 43 2/04/52 8:00 0.041 8.73 4 14.08 0.929
0.027 20 1/18/53 21:00 0.040 8.57 5 10.99 0.909
0.014 33 1/07/54 21:00 0.040 8.56 6 9.01 0.889
0.013 39 11/19/54 20:00 0.040 8.50 7 7.64 0.869
0.035 10 1/06/56 12:00 0.039 8.38 8 6.63 0.849
0.014 35 3/10/57 4:00 0.036 7.87 9 5.86 0.829
0.023 24 1/17/58 8:00 0.035 7.67 10 5.24 0.809
0.014 36 1/27/59 1:00 0.034 7.58 11 4.75 0.789
0.039 8 11/21/59 7:00 0.033 7.30 12 4.34 0.769
0.031 15 11/24/60 16:00 0.032 7.24 13 3.99 0.749
0.012 44 12/24/61 6:00 0.032 7.19 14 3.70 0.729
0.023 25 11/30/62 19:00 0.031 7.02 15 3.44 0.709
0.028 17 11/19/63 17:00 0.028 6.74 16 3.22 0.690
0.032 13 12/01/64 8:00 0.028 6.71 17 3.03 0.670
0.021 28 1/07/66 3:00 0.028 6.63 18 2.85 0.650
0.027 19 12/13/66 15:00 0.027 6.60 19 2.70 0.630
0.014 32 1/20/68 22:00 0.027 6.55 20 2.56 0.610
0.019 30 12/11/68 7:00 0.026 6.48 21 2.44 0.590
0.026 21 1/27/70 4:00 0.025 6.41 22 2.32 0.570
0.019 31 12/07/70 12:00 0.025 6.40 23 2.22 0.550
0.040 6 3/06/72 23:00 0.023 6.20 24 2.13 0.530
0.033 12 12/26/72 6:00 0.023 6.17 25 2.04 0.510
0.022 26 1/18/74 18:00 0.022 6.09 26 1.96 0.490
0.013 37 1/14/75 1:00 0.021 6.05 27 1.89 0.470
0.014 34 12/04/75 8:00 0.021 6.03 28 1.82 0.450
0.011 49 8/26/77 8:00 0.020 5.98 29 1.75 0.430
0.028 18 12/15/77 19:00 0.019 5.91 30 1.70 0.410
0.011 48 2/13/79 1:00 0.019 5.90 31 1.64 0.390
0.041 3 12/18/79 4:00 0.014 5.74 32 1.59 0.370
0.020 29 12/30/80 22:00 0.014 5.62 33 1.54 0.350
0.034 11 10/06/81 20:00 0.014 5.56 34 1.49 0.330
0.021 27 1/08/83 3:00 0.014 5.44 35 1.45 0.310
0.012 45 12/13/83 8:00 0.014 5.31 36 1.41 0.291
0.012 42 11/11/84 9:00 0.013 5.04 37 1.37 0.271
0.025 23 1/19/86 4:00 0.013 4.98 38 1.33 0.251
0.036 9 11/24/86 9:00 0.013 4.95 39 1.30 0.231
0.013 40 12/10/87 8:00 0.013 4.79 40 1.27 0.211
0.012 46 11/05/88 23:00 0.013 4.47 41 1.24 0.191
0.041 4 1/09/90 17:00 0.012 4.14 42 1.21 0.171
0.040 5 11/24/90 17:00 0.012 4.05 43 1.18 0.151
0.025 22 1/31/92 7:00 0.012 3.99 44 1.15 0.131
0.011 47 1/26/93 5:00 0.012 3.96 45 1.12 0.111
0.010 50 2/17/94 23:00 0.012 3.94 46 1.10 0.091
0.032 14 12/27/94 7:00 0.011 3.62 47 1.08 0.071
0.044 2 2/09/96 5:00 0.011 3.21 48 1.05 0.051
0.040 7 1/02/97 13:00 0.011 3.10 49 1.03 0.031
0.013 41 1/25/98 0:00 0.010 2.93 50 1.01 0.011
Computed Peaks 0.077 10.01 100.00 0.990
Computed Peaks 0.065 10.01 50.00 0.980
Computed Peaks 0.055 10.00 25.00 0.960
Computed Peaks 0.042 9.00 10.00 0.900
Computed Peaks 0.039 8.42 8.00 0.875
Computed Peaks 0.033 7.31 5.00 0.800
Computed Peaks 0.021 6.03 2.00 0.500
Computed Peaks 0.015 5.81 1.30 0.231
Flow Duration from Time Series File:rdout.tsf
Cutoff Count Frequency CDF Exceedence_Probability
CFS $ $ $
0.001 204052 46.587 46.587 53.413 0.534E+00
0.004 57381 13.101 59.688 40.312 0.403E+00
0.006 69899 15.959 75.647 24.353 0.244E+00
0.008 44560 10.174 85.820 14.180 0.142E+00
0.011 28825 6.581 92.401 7.599 0.760E-01
0.013 24566 5.609 98.010 1.990 0.199E-01
0.016 5369 1.226 99.236 0.764 0.764E-02
0.018 205 0.047 99.282 0.718 0.718E-02
0.021 610 0.139 99.422 0.578 0.578E-02
0.023 550 0.126 99.547 0.453 0.453E-02
0.025 465 0.106 99.653 0.347 0.347E-02
0.028 415 0.095 99.748 0.252 0.252E-02
0.030 296 0.068 99.816 0.184 0.184E-02
0.033 266 0.061 99.876 0.124 0.124E-02
0.035 176 0.040 99.917 0.083 0.833E-03
0.037 113 0.026 99.942 0.058 0.575E-03
0.040 126 0.029 99.971 0.029 0.288E-03
0.042 64 0.015 99.986 0.014 0.142E-03
0.045 41 0.009 99.995 0.005 0.479E-04
0.047 18 0.004 99.999 0.001 0.685E-05
0.050 1 0.000 100.000 0.000 0.457E-05
0.052 0 0.000 100.000 0.000 0.457E-05
0.054 0 0.000 100.000 0.000 0.457E-05
0.057 0 0.000 100.000 0.000 0.457E-05
0.059 1 0.000 100.000 0.000 0.228E-05
0.062 0 0.000 100.000 0.000 0.228E-05
0.064 0 0.000 100.000 0.000 0.228E-05
0.066 0 0.000 100.000 0.000 0.228E-05
0.069 0 0.000 100.000 0.000 0.228E-05
0.071 0 0.000 100.000 0.000 0.228E-05
0.074 0 0.000 100.000 0.000 0.228E-05
0.076 0 0.000 100.000 0.000 0.228E-05
0.079 0 0.000 100.000 0.000 0.228E-05
0.081 0 0.000 100.000 0.000 0.228E-05
0.083 0 0.000 100.000 0.000 0.228E-05
0.086 0 0.000 100.000 0.000 0.228E-05
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 %Change Probability Base New %Change
0.015 I 0.10E-01 0.79E-02 -22.8 I 0.10E-01 0.015 0.014 -5.7
0.020 I 0.51E-02 0.60E-02 17.6 I 0.51E-02 0.020 0.022 8.3
0.025 1 0.30E-02 0.35E-02 17.2 1 0.30E-02 0.025 0.027 6.2
F' �t
0.031 0.18E-02 0.18E-02 -0.3 I 0.18E-02 0.031 0.031 -0.2
0.036 0.11E-02 0.72E-03 -34.2 I 0.11E-02 0.036 0.034 -6.4
0.041 0.68E-03 0.16E-03 -76.3 I 0.68E-03 0.041 0.036 -12.1
0.046 0.46E-03 0.68E-05 -98.5 I 0.46E-03 0.046 0.038 -17.3
0.052 0.31E-03 0.46E-05 -98.5 I 0.31E-03 0.052 0.040 -23.2
0.057 0.22E-03 0.46E-05 -97.9 I 0.22E-03 0.057 0.041 -28.1
0.062 0.12E-03 0.23E-05 -98.0 I 0.12E-03 0.062 0.043 -30.2
0.067 0.62E-04 0.23E-05 -96.3 I 0.62E-04 0.067 0.044 -34.5
0.073 0.34E-04 0.23E-05 -93.3 I 0.34E-04 0.073 0.045 -37.7
0.078 0.68E-05 0.23E-05 -66.7 I 0.68E-05 0.078 0.048 -37.9
0.083 0.23E-05 0.23E-05 0.0 I 0.23E-05 0.083 0.087 4.3
Maximum positive excursion = 0.007 cfs ( 8.4%) 'L (Q% fl L
occurring at 0.080 cfs on the Base Data:exist.tsf
and at 0.087 cfs on the New Data:rdout.tsf
Maximum negative excursion = 0.032 cfs (-40.8%)
occurring at 0.078 cfs on the Base Data:exist.tsf
and at 0.046 cfs on the New Data:rdout.tsf
Return Period
2 5 10 20 50 10Q
rdout.pks in Sea-Tac
® exist.pks �� Y
• • •--
//— /
• moi
i -
i
-
i
Lo
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..--- 0
•
-- • o ,
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•� 0Oo
0,— ea,,,,,, li.::-:---.)-‘a c-r:14-1
— • 00000 00
u_ -- —---0 0000
0 ___-•o--- • 0 _0-0'0 0
a) o 0
0 10 —
m
U _ -
(0
o •
--
kfi
103I I i I I i I I i i i I
1 2
5 10 20 30 40 50 60 70 80 90 95 98 99 r
Cumulative Probability
0
0 rdout.dur
target.dur
10%
co
♦ ' De7 1T1 k) VAt,t�.:7"
o _ _
UuehrY tai Mitrz)En—
U-
U_
a)
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co
=
R •
U)
•
oo
•
•
a
V •
O ♦
N •
• 1
o •
o 11111111-5
i l i Iliil i 11111-3 i l i i ilii i i i i III ! ' i i i I.
10-6 10 5 10 10 3 10 2 10-1 10° V
Probability Exceedence
APPENDIX C-2
TREATMENT FACILITIES DESIGN
aC� -, � � � � n - oCLU\ii � cam - - :\I u
J J _ J
(WjQ1ET auza-A-v TREA- E 1T FADL.r_v TRIBUTARY UTARY AREAS)
v
,'�~_ , /y_. SOUTH PGIS PERMEABLE
zee
PAVEMENT AREA 1
NORTH PGIS PERMEABLE ai _ r ri: EXISTING (8,7 3 SF)
PAVEMENT AREA Y,e- —== ROAD
(5,797 SF) — _ � - ---
-- ,- - a SOUTH PGIS
— _ �`
i `PAVEMENT AREA >5%
TI —
J4351SF)
1L.` l„Y ; �'4:/11;
b �' \� ` \ / / 7_..{ ";. €sty \\\\\ N '.
\
I'o` 1 ' �\ \� 01 ma
\'} // `tM"1\''.*I1:4*1."ii,'" ,r \\ 4\ R� `
w _.,_ ® `,.O '/' / I {}/' /:,, / / . t �, -,
�/ ` // / /. / }�- t` n ''' — ��
'—� /� _�.--^ i
,/' i / ��
1 . . - - _
I v -/ ,,.%
, ,_ al
�� BSONRonvs°" /� 'i SOUTH PGIS PERMEABLE
____
PAVEMENT AREA 2
I z: ,� — 3,139 SF)
i
i
_ 44 S` Z4girg::4z ._� ,
._.
PGIS AREAS SF (AC):
PERMEABLE PAVEMENT: 17,729 (0.41 AC)* z
ASPHALT >5%: 4,351 (0.10 AC)
OTHER ISOLATED ASPHALT Sc CONCRETE: 392 (0.01 AC)
TOTAL PCIS: 22,472 (0.52 AC) o 5O 100
*120 SF OF CONCRETE DRAINS TO HERE (INCLUDED IN
392 SF TALLY) SCALE: 1" = 100 ft.
�y
dev15
Flow Frequency Analysis
Time Series File:devl5.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- Flow Frequency Analysis
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.048 6 8/27/01 18:00 0.118 1 100.00 0.990
0.033 8 9/17/02 17:45 0.090 2 25.00 0.960
0.090 2 12/08/02 17:15 0.065 3 10.00 0.900
0.038 7 8/23/04 14:30 0.053 4 5.00 0.800
0.051 5 10/28/04 16:00 0.051 5 3.00 0.667
0.053 4 10/27/05 10:45 0.048 6 2.00 0. 500
0.065 3 10/25/06 22:45 0.038 7 1.30 0.231
0.118 1 1/09/08 6:30 0.033 8 1.10 0.091
Computed Peaks 0.108 50.00 0.980
1500/1600 Benson South Pavement Area Entrance Runoff Calcs.
6/6/13
South CB Stormfilter
N(flow)=Q(trt)*[(449gpm/cfs)/Q(trt) gpm/cart]
Q(trt)=0.35*Q(2)
Q(trt)=0.35(0.048)
Q(trt)=0.0168 cfs
N(flow)=0.0168*(449/7. 5)
N(flow)=1.0 cartridges
Page 1
devl5
KCRTS Program. . . File Directory:
C:\KC_SWDM\KC_DATA\
[C] CREATE a new Time Series
ST
0.00 0.00 0.000000 Till Forest
0.00 0.00 0.000000 Till Pasture
0.00 0.00 0.000000 Till Grass
0.00 0.00 0.000000 outwash Forest
0.00 0.00 0.000000 outwash Pasture
0.00 0.00 0.000000 outwash Grass
0.00 0.00 0.000000 wetland
0.10 0.00 0.000000 Impervious
devl5.tsf
T
1.00000
F
[T] Enter the Analysis TOOLS Module
[P] Compute PEAKS and Flow Frequencies
devl5.tsf
devl5.pks
[R] RETURN to Previous Menu
[X] exit KCRTS Program
Page 1
4! Lj
ail
Determining Number of
► iv a ri Cartridges for Flow Based
ENGINEERED SOLUTIONS
Systems
CONTECH Stormwater Solutions Inc. Engineer: CRH
Date 6/6/2013
Site Information
Project Name Eagle Ridge
Project State Washington
Project Location Renton
Drainage Area, Ad 0.10 ac
Impervious Area,Ai 0.10 ac
Pervious Area, Ap 0.00
% Impervious 100%
Runoff Coefficient, Rc 0.95
Water quality flow 0.02 cfs
Peak storm flow 1.80 cfs Max Bypass
Filter System
Filtration brand StormFilter
Cartridge height 18 in
Specific Flow Rate 1.00 gpm/ft`
Flow rate per cartridge 7.5 gpm
SUMMARY
Number of Cartridges 1
©2006 CONTECH Stormwater Solutions
contechstormwater.com 1 of 1
APPENDIX C-3
CONVEYANCE FACILITIES DESIGN
Pli
A G AI :D 0FIaCOND ,,,- y - N - u -v-vs
QscirOoJu
l�a�� C�B�dL .7Q�]C� �
�� CB10 CD9 _ CB #s
k� RIM 89.16 RIM 187.30 f CB ;7
1 IE 186.16 `�� -,. EXISTING RIM 186.77`
f IE 184 70 RIM 186.75
ROAD IE 183.88
CB 14 �r _ IE 182.52
`�� ` RIM 181.50 _
1 I E 179.00 _`` '
•
— TI — --- _ � RIM 176 8
1 1 J � \% IEC 173.755
BLa� �;
A { i � CB ;5
4
�: ` _ : �. (TRI$ TO �� \-\:\.\ -.. -\'"--';''',d /� � �\�v-.
,(NIm //� 2/ ��r6,� \ EM
•�i .�,� , � 179 19
_ ,< ,Aye
�� 494,E d
"'£ j/ •.. t 1,;96;51TRIB
� v .- /- �rfi? /AULT / CB J 4 i
CB 11 d--
r
� ; RIM 182.05 \ -‘--,e,/... /-_ " - 173.22
IE 168.70 I IE 170.65
f = ��N� ILTER CB ;2.''
Ap S01/1.14 ........ / „
i 173.40 VORT CB 3
I • i RIM 173.
RIM 173.54
�., ."�, '_ —�= XISIING CB CB ;1 IE 170.54
,,,,,,,,..7 7 ' RIM 161.72 RIM 164.48
_� — _` ! t, IE 158.10 IE 158.18
2
0 50 100
SCALE: 1" = 100 ft.
r.
G/
Conveyance Calculations
Project: Eagle Ridge Offices and Condominiums
Proj.#: 307-TFC
Date: 4/8/2013
Use area weighted flows from KCRTS 15-minute analysis for conveyance calcs.
Discharge Pipe from South Detention Vault
filename: svltout
Conveys entire flow from this basin
Overflow 169.1
Qum= 1.5 cfs
Length Dia Pipe Type Outlet-IE Inlet-IE Inlet Type
O.F. Elev. Bnd Ang. Str. Dia. Q-Ratio
1 15.00 12.00 1 158.10 158.18 5
164.48 35.00 2 0.00
57.00 12.00 1 158.28 159.10 5
8" Pipe from Driveway Entrance
filename: svltinl
Conveys flow from 4,400 sf of parking and entrance blvd (about 8% of S basin tributary area)
Overflow 179.19
Qioo = 0.12 cfs (.08*1.5)
# Length Dia Pipe Type Outlet-IE Inlet-IE Inlet Type
O.F. Elev. Bnd Ang. Str. Dia. Q-Ratio
2 3.00 8.00 1 168.10 168.13 5
173.40 90.00 4 0.00
3 11.00 8.00 1 170.43 170.54 5
173.54 45.00 4 0.00
4 11.00 8.00 1 170.54 170.65 5
173.22 80.00 2 0.50
5 50.00 8.00 1 170.75 176.09 5
8" Pipe from Upper Driveway
filename: svltinl
Conveys flow from 8,800 sf of parking and entrance drive
+ S bldg 19,966sf(about 54% of S basin tributary area)
Overflow 189.16
Qioo = 0.81 cfs (.54*1.5)
Length Dia Pipe Type Outlet-IE Inlet-IE Inlet Type
O.F. Elev. Bnd Ang. Str. Dia. Q-Ratio
6 12.00 12.00 1 168.10 173.75 5
176.85 2.00 2 0.37
Z:\JOBS\300-399\307-tfc\TIR\Drainage CalcsConveyance
4/8/2013
f/
7 53.00 8.00 1 173.85 182.52 5 Jf f0
186.75 40.00 2 0.33
8 68.00 8.00 1 182.42 183.88 5
186.77 0.00 2 0.50
9 36.00 8.00 1 183.88 184.70 5
187.30 0.00 2 1.00
10 189.16 8.00 1 184.80 186.16 5
Discharge Pipe from North Detention Vault
filename: nvltout
Conveys entire flow from this basin
Overflow 179.06
Qmo= 1.1 cfs
# Length Dia Pipe Type Outlet-IE Inlet-IE Inlet Type
O.F. Elev. Bnd Ang. Str. Dia. Q-Ratio
11 12.00 12.00 1 168.97 169.06 5
8" Pipe from North Parking Area
filename: nvltinl
Conveys flow from entire N basin tributary area)
Overflow 181
am= 1.1 cfs
# Length Dia Pipe Type Outlet-IE Inlet-IE Inlet Type
O.F. Elev. Bnd Ang. Str. Dia. Q-Ratio
14 15.00 8.00 1 177.64 179.00 5
Z:\JOBS\300-399\307-tfc\TIR\Drainage CalcsConveyance
4/8/2013
tqi
svltout
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
Water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
Version 6.00
File Opened for Reading:svltout.bwp
File Opened for Writing:svltout.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:svltout.bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:159.1 feet
Discharge Range:0. 5 to 3. Step of 0. 5 [cfs]
Overflow Elevation:169.1 feet
Weir:NONE
Upstream Velocity:l. feet/sec
PIPE NO. 1: 15 LF - 12"CP @ 0. 53% OUTLET: 158.10 INLET: 158.18 INTYP: 5
JUNC NO. 1: OVERFLOW-EL: 164.48 BEND: 35 DEG DIA/WIDTH: 2.0 Q-RATIO: 0.00
Q(CFS) HW(FT) HW ELEV. N-FAC DC DN TW DO DE HWO HWI
is it it dr***** itd....,..„.,..'.r*e'r'rit**it**:r it i;***...,***it it it*i;:,::**it*it i; ....*•*it it it it it*it****it**it::..****it
0. 50 0.94 159.12 * 0.012 0.30 0.29 1.00 1.00 0.93 0.94 0.40
1.00 0.95 159.13 0.012 0.43 0.42 1.00 1.00 0.93 0.95 0. 57
1. 50 0.99 159.17 0.012 0. 52 0. 52 1.00 1.00 0.94 0.99 0.72
2.00 1.04 159.22 s, 0.012 0.61 0.63 1.00 1.00 0.96 1.04 0.84
2. 50 1.10 159.28 0.012 0.68 0.74 1.00 1.00 0.98 1.10 0.96
3.00 1.18 159. 36 * 0.012 0.75 0.90 1.00 1.00 1.01 1.18 1.08
PIPE NO. 2: 57 LF - 12"CP @ -0.32% OUTLET: 158.28 INLET: 158.10 INTYP: 5
Q(CFS) HW(FT) HW ELEV. N-FAC DC DN TW DO DE HWO HWI
.r*****is*i.is**** .:*i.********it4:*******•*it**it****$r****dr'...,*************** k::................
0.50 1.04 159. 14 0.012 0.30 0.00 0.84 0.84 1.04 1.03 0.39
1.00 1.10 159.20 0.012 0.43 0.00 0.85 0.85 1.08 1.10 0. 58
1.50 1.23 159.33 * 0.012 0. 52 0.00 0.89 0.89 1.16 1.23 0.75
2.00 1.41 159. 51 0.012 0.61 0.00 0.94 0.94 1.27 1.41 0.91
2.50 1.64 159.74 * 0.012 0.68 0.00 1.00 1.00 1.42 1.64 1.07
3.00 1.93 160.03 0.012 0.75 0.00 1.08 1.08 1.61 1.93 1.23
File Opened for Writing:svltout.bwt
Save results to HW/TW file:svltout.bwt
Exit KCBW Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
Water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
Version 6.00
Page 1
q0
svltin1
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
Water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
Version 6.00
File Opened for Reading:svltinl.bwp
File Opened for Writing:svltinl.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:svltinl.bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:I09.I feet
Discharge Range:0. 5 to 2. Step of 0.5 [cfs]
Overflow Elevation:179.I9 feet
Weir:NONE
Upstream Velocity:l' feet/sec
PIPE NO. 1: 3 LF - 8^[P @ I.00& OUTLET: I68.I0 INLET: I68.13 INTYP: 5
JUNC NO. 1: OVERFLOW-EL: I73.40 BEND: 90 DEG DIA/WIDTH: 4.0 Q-RATIO: 0.00
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
***********w******^**^****w*******^^***^*^^***+^**w^************»***^******+*a*
0. 50 I.04 169.I7 * 0.012 0.34 0.29 1.00 1.00 0.98 I.04 0.49
1.00 1.22 169. 35 * 0.0I2 0.48 0.44 I.00 1.00 0.99 I.22 0.8I
1. 50 1. 53 169.66 * 0.0I2 0. 58 0.67 1.00 1.00 I.01 1. 53 1.27
2.00 1.97 170.I0 * 0.012 0.63 0.67 1.00 1.00 1.04 1.97 1.91
PIPE NO. 2: 11 LF - 8"CP @ 1.00% OUTLET: I70.43 INLET: I70. 54 INTYP: 5
JUNC NO. 2: OVERFLOW-EL: 173. 54 BEND: 45 DEG DIA/WIDTH: 4.0 Q-RATIO: 0.00
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
*****a****^*^***++**+^****+***+++*^^***^*+**+*****^*****a+^^*^****+*^^*********
0.50 0.46 171.00 * 0.0I2 0.34 0.29 0.00 0.29 0.34 ***** 0'46
1.00 0.69 I7I.23 * 0.0I2 0.48 0.44 0.00 0.44 0.48 «^^+* 0.69
1. 50 1.00 171. 54 * 0.012 0.58 0.67 0.00 0. 58 0.64 0.91 I.00
2.00 1.44 I71.98 * 0.0I2 0.63 0.67 0.00 0.63 0.79 1.24 1.44
PIPE NO. 3: 11 LF - 8"CP @ 1.00% OUTLET: 170. 54 INLET: 170.85 INTYP: 5
JUNC NO. 3: OVERFLOW-EL: I73.22 BEND: 80 DEG DIA/WIDTH: 2.0 Q-RATIO: 0' 50
Q(CFS) HW(FT) Hw ELEV. + N-FAC DC DN TW DO DE HWO HWI
***^*++*x**********+*^******+*******+***^^****+*^+*^+^******+*+**^^********w***
0. 50 0.48 171.13 * 0.012 0.34 0.29 0.46 0.46 0. 34 *^*** 0.48
1.00 0.86 171. 51 * 0.0I2 0.48 0.44 0.69 0.69 0.64 0.86 0.79
1.50 1. 52 172.I7 * 0.012 0.58 0.67 1.00 I.00 I.04 1. 52 1.23
2.00 2.44 173'09 * 0.012 0.63 0.67 1.44 1.44 1. 59 2.44 1.84
PIPE NO. 4: 50 LF - 8^[P @ 8.68% OUTLET: 170.75 INLET: 175.09 INTYP: 5
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HwZ
*+*+^**^**********a*^^*^****+************^a**^*^^*^+^**^******^*+**^^*******^^*
0.33 0.33 175.42 * 0.012 0.27 0.14 0.38 0.38 0.27 ***^* 0.33
0.67 0. 53 175.62 * 0.012 0.39 0.I9 0.76 0.76 0.39 ***** 0. 53
1.00 0.73 175.82 * 0.012 0.48 0.24 1.42 1.42 0.48 ***** 0.73
1.33 0.98 176.07 * 0.012 0. 55 0.28 2.34 2.34 0. 55 *+^** 0.98
Page 1
svltinl
File opened for writing:svltinl.bwt
save results to Hw/TW file:svltinl.bwt
Exit KCBW Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
version 6.00
Page 2
7f)
(10
svltin2
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
Water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
Version 6.00
File Opened for Reading:svltin2.bwp
File Opened for Writing:svltin2.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:svltin2.bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:169.1 feet
Discharge Range:0. 5 to 2. Step of 0. 5 [cfs]
Overflow Elevation:189.16 feet
Weir:NONE
Upstream velocity:l. feet/sec
PIPE NO. 1: 12 LF - 12"CP @ 47.08% OUTLET: 168.10 INLET: 173.75 INTYP: 5
JUNC NO. 1: OVERFLOW-EL: 176.85 BEND: 2 DEG DIA/WIDTH: 2.0 Q-RATIO: 0.37
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
..******........*****ire....* ***'..*..**R*******..*****************:':*****..******:r****..........
0. 50 0. 30 174.05 * 0.012 0.30 0.10 1.00 1.00 0. 30 ***** 0.16
1.00 0.43 174.18 * 0.012 0.43 0.14 1.00 1.00 0.43 -r*';."r 0.31
1.50 0. 52 174.27 * 0.012 0. 52 0.17 1.00 1.00 0. 52 ***** 0.42
2.00 0.61 174.36 * 0.012 0.61 0.19 1.00 1.00 0.61 ***** 0.49
PIPE NO. 2: 53 LF - 8"CP @ 16.36% OUTLET: 173.85 INLET: 182. 52 INTYP: 5
JUNC NO. 2: OVERFLOW-EL: 186.75 BEND: 40 DEG DIA/WIDTH: 2.0 Q-RATIO: 0.33
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
*****4.........*ti.........***......**...,*......................***,...........'r:,...,.,...........,......................***..**..***
0.36 0. 34 182.86 * 0.012 0.29 0.12 0.20 0.20 0.29 ***** 0.34
0.73 0. 56 183.08 * 0.012 0.41 0.17 0.33 0.33 0.41 ***** 0. 56
1.09 0.78 183.30 * 0.012 0. 50 0.21 0.42 0.42 0. 50 ***** 0.78
1.46 1.09 183.61 * 0.012 0. 57 0.24 0. 51 0. 51 0. 57 ***** 1.09
PIPE NO. 3: 68 LF - 8"CP @ 2.15% OUTLET: 182.42 INLET: 183.88 INTYP: 5
JUNC NO. 3: OVERFLOW-EL: 186.77 BEND: 0 DEG DIA/WIDTH: 2.0 Q-RATIO: 0. 50
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
*****i.*** *R....***d.*****..****d.**'.r'.********** *'.r'.;*****..*********?.*....***d.*********
0.27 0.33 184.21 * 0.012 0.25 0.18 0.44 0.44 0.25 ***** 0.33
0. 55 0.49 184. 37 * 0.012 0.35 0.25 0.66 0.66 0.35 ***** 0.49
0.82 0.64 184. 52 * 0.012 0.43 0.31 0.88 0.88 0.43 ***** 0.64
1.10 0. 79 184.67 * 0.012 0.50 0.37 1.19 1.19 0. 50 ***** 0.79
PIPE NO. 4: 36 LF - 8"CP @ 2.28% OUTLET: 183.88 INLET: 184.70 INTYP: 5
JUNC NO. 4: OVERFLOW-EL: 187.30 BEND: 0 DEG DIA/WIDTH: 2.0 Q-RATIO: 1.00
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
***********************:r*..**********4;**********;***************..**************
0.18 0.26 184.96 * 0.012 0.20 0.14 0.33 0.33 0.20 ***** 0.26
0.37 0.39 185.09 0.012 0.29 0.20 0.49 0.49 0.29 ***** 0.39
0. 55 0. 50 185.20 * 0.012 0.35 0.25 0.64 0.64 0. 35 ***** 0. 50
Page 1
afro
svltin2
0.73 0.60 185.30 * 0.012 0.41 0.29 0.79 0.79 0.41 ***** 0.60
PIPE NO. 5: 189 LF - 8"CP @ 0.72% OUTLET: 184.80 INLET: 186.16 INTYP: 5
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
*:r'rir'.ririririr:r*•'.r****ir'r::'.r;Y'r'.rir'.rir'rir**** rir:rir*irir* ***irir'r******'..•iririri ****iririr*******i;irir***
0.09 0.17 186.33 * 0.012 0.14 0.13 0.16 0.16 0.14 ***** 0.17
0.18 0.25 186.41 * 0.012 0.20 0.19 0.29 0.29 0.20 ***** 0.25
0.27 0.32 186.48 * 0.012 0.25 0.23 0.40 0.40 0.25 ***** 0.32
0.37 0.38 186. 54 * 0.012 0.29 0.27 0. 50 0.50 0.29 ***** 0.38
File Opened for Writing:svltin2.bwt
Save results to HW/TW file:svltin2.bwt
Exit KCBW Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
Water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
Version 6.00
Page 2
nvltout
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
Water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
Version 6.00
File Opened for Reading:nvltout.bwp
File Opened for writing:nvltout.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:nvltout.bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:169.7 feet
Discharge Range:0. 5 to 3. Step of 0. 5 [cfs]
Overflow Elevation:179.06 feet
Weir:NONE
Upstream Velocity:l. feet/sec
PIPE NO. 1: 12 LF - 12"CP @ 0.75% OUTLET: 168.97 INLET: 169.06 INTYP: 5
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
**********i.** **........**** ***....................*4........,.,*..**......******k**- ***.,..*****'.......'.r**
0. 50 0.65 169.71 * 0.012 0.30 0.27 0.73 0.73 0.64 0.65 0.38
1.00 0.71 169.77 * 0.012 0.43 0.38 0.73 0.73 0.64 0.71 0. 58
1. 50 0.81 169.87 * 0.012 0. 52 0.47 0.73 0.73 0.64 0.81 0.74
2.00 0.96 170.02 * 0.012 0.61 0. 56 0.73 0.73 0.63 0.96 0.90
2.50 1.06 170.12 * 0.012 0.68 0.65 0.73 0.73 0.68 ****'r 1.06
3.00 1.23 170.29 * 0.012 0.75 0.74 0.73 0.74 0.75 *** 1.23
File Opened for Writing:nvltout.bwt
Save results to HW/TW file:nvltout.bwt
Exit KCBW Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
Water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
Version 6.00
Page 1
rD1(0
nvltinl
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
Water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
Version 6.00
File Opened for Reading:nvltinl.bwp
File Opened for Writing:nvltinl.doc
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:nvltinl.bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:179.06 feet
Discharge Range:0. 5 to 2. Step of 0. 5 [cfs]
Overflow Elevation:181. feet
Weir:NONE
Upstream Velocity:l. feet/sec
PIPE NO. 1: 15 LF - 8"CP @ 9.07% OUTLET: 177.64 INLET: 179.00 INTYP: 5
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
******** ************:Y ***** ;4':',: *************'.:::::':* ir* **':'.:::'.:a:************i::Y**
0. 50 0.44 179.44 0.012 0.34 0.17 1.42 1.42 0.34 °**** 0.44
1.00 0.73 179.73 * 0.012 0.48 0.23 1.42 1.42 0.48 ***** 0.73
1. 50 1.14 180.14 * 0.012 0. 58 0.29 1.42 1.42 0. 58 ***** 1.14
2.00 1.71 180.71 * 0.012 0.63 0.34 1.42 1.42 0.63 ***** 1.71
File Opened for Writing:nvltinl.bwt
Save results to HW/TW file:nvltinl.bwt
Exit KCBW Program
KING COUNTY DEPARTMENT OF NATURAL RESOURCES
Water and Land Resources Division
BACKWATER ANALYSIS PROGRAM
Version 6.00
Page 1
APPENDIX C-4
EROSION CONTROL FACILITIES DESIGN
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. 0.0.„v -' OUTLINE OF AREA TRIBUTARY TO
- SA {S i , BAKER TANK SETTLEMENT AND
_.."'J nc,; f 4 µ.t MA, rrr +'..t. 7 FLOW CONTROL,::
AREA TRIBUTARY TO PROPOPSED BAKER TANK
MITIGATION = 115,971 SF (2.66 ACRES) z
e)
0 50 100
I
SCALE: 1" = 100 ft.
Flow Frequency Analysis 2/3
Time Series File:escl5.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- Flow Frequency Analysis
Flow Rate Rank Time of Peak -- Peaks-- Rank Return Prob ta203 I Oki 6OL.
(CFS) (CFS) Period
1.27 6 8/27/01 18:00 3.51 1 100.00 0.990 Ci:
0.885 8 9/17/02 17:45 2.56 2 25.00 0.960 1� .5
2.56 2 12/08/02 17:15 1.74 3 10.00 0.900
1.02 7 8/23/04 14:30 1.46 4 5.00 0.800
1.38 5 10/28/04 16:00 1.38 5 3.00 0.667
1.46 4 10/27/05 10:45 1.27 6 2.00 0.500 de-- QZ
1.74 3 10/25/06 22:45 1.02 7 1.30 0.231
3.51 1 1/09/08 6:30 0.885 8 1.10 0.091
Computed Peaks 3.19 50.00 0.980
Sediment Pond Sizing:
SA=2080`Q2
SA=2080`1.27
SA=2,642 sf >> space available, so use Baker Tanks
KCRTS Program...File Directory:
?!3
C:\KC_SWDM\KC_DATA\
[C]CREATE a new Time Series
ST
0.21 0.00 0.000000 Till Forest pstu N Cou-rt?Oc--
0.00 0.00 0.000000 Till Pasture
0.70 0.00 0.000000 Till Grass I pLer- Dyk-FA
0.00 0.00 0.000000 Outwash Forest
0.00 0.00 0.000000 Outwash Pasture
0.00 0.00 0.000000 Outwash Grass
0.00 0.00 0.000000 Wetland
2.66 0.00 0.000000 Impervious
esc15.tsf
T
1.00000
F
[T] Enter the Analysis TOOLS Module
[P]Compute PEAKS and Flow Frequencies
esc15.tsf
esc15.pks
[R] RETURN to Previous Menu
[X]eXit KCRTS Program
APPENDIX D
MAINTENANCE REQUIREMENTS
FOR
PRIVATELY MAINTAINED DRAINAGE FACILITIES
MAINTENANCE AND OPERATIONS MANUAL
FOR PRIVATELY MAINTAINED DRAINAGE FACILITIES
ADDRESS: 1500 & 1600 Benson Road South
Renton, Washington
RETENTION/DETENTION FACILITY YI 3
The purpose of the detention vaults is to reduce the rate of runoff from the developed portions of
the property to historic levels. Water can flow freely into the vaults, but orifices in the outflow
risers restrict the outflow. When the inflow exceeds the capacity of the orifices, the excess
water is "stored" in the vaults and released slowly after the storm abates.
In order to function properly, the vaults must also 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.
STORMWATER MANAGEMENT CARTRIDGE FILTER MANHOLE AND CDS
HYDRODYNAMIC TREATMENT FACILITIES
The hydrodynamic separation and cartridge filter treatment facilities should be inspected and
maintained in accordance with the manufacturer's recommendations (attached).
CONVEYANCE SYSTEMS
Pipes transport runoff from one place to another, in this case from catch basins and cartridge
filters to the vaults, 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.
PERMEABLE PAVEMENT
Permeable pavements must be inspected after one major storm each year to make sure it is
working properly. Prolonged ponding or standing water on the pavement surface is a sign that
the system is defective and may need to be replaced. If this occurs, contact the pavement
installer or the King County Water and Land Resources Division for further instructions. A typical
permeable pavement system has a life expectancy of approximately 25-years. To help extend
the useful life of the system, the surface of the permeable pavement should be kept clean and
free of leaves, debris, and sediment through regular sweeping or vacuum sweeping. The owner
is responsible for the repair of all ruts, deformation, and/or broken paving units.
The following tables identify maintenance issues, which should be addressed regularly,
describing possible problems with the drainage system and their respective solutions.
1
z
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES /(3
NO. 3-DETENTION TANKS AND VAULTS
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Storage Area Plugged Air Vents One-half of the cross section of a vent is blocked Vents free of debris and sediment
at any point with debris and sediment.
Debris and Sediment Accumulated sediment depth exceeds 10%of All sediment and debris removed
the diameter of the storage area for%length of from storage area.
storage vault or any point depth exceeds 15%of
diameter. Example:72-inch storage tank would
require cleaning when sediment reaches depth of
7 inches for more than'/z length of tank.
Joints Between Any crack allowing material to be transported into All joint between tank/pipe sections
Tank/Pipe Section facility. are sealed
Tank Pipe Bent Out of Any part of tank/pipe is bent out of shape more Tank/pipe repaired or replaced to
Shape than 10%of its design shape. design.
Vault Structure Damage to Wall, Cracks wider than%-inch and any evidence of Vault replaced or repaired to design
Frame, Bottom, soil particles entering the structure through the specifications.
and/or Top Slab cracks,or maintenance inspection personnel
determines that the vault is not structurally
sound.
Damaged Pipe Joints Cracks wider than%-inch at the joint of any No cracks more than 1A-inch wide at
inlet/outlet pipe or any evidence of soil particles the joint of the inlet/outlet pipe.
entering the vault through the walls.
Manhole Cover Not in Place Cover is missing or only partially in place.Any Manhole is closed.
open manhole requires maintenance.
Locking Mechanism Mechanism cannot be opened by one Mechanism opens with proper tools.
Not Working maintenance person with proper tools.Bolts into
frame have less than 1/2 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 Unsafe King County Safety Office and/or maintenance Ladder meets design standards.
person judges that ladder is unsafe due to Allows maintenance person safe
missing rungs, misalignment, rust,or cracks. access.
Large access Gaps, Doesn't Cover Large access doors not flat and/or access hole Doors closes flat and covers access
doors/plate Completely not completely covered. NOTE however that hole completely.
grated doors are acceptable.
Lifting Rings Missing, Lifting rings not capable of lifting weight of door Lifting rings sufficient to remove lid.
Rusted or lid.
1/24/2005 2005 Surface Water Design Manual—Appendix A
A-4
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES 3�3
NO. 4-CONTROL STRUCTURE/FLOW RESTRICTOR
Maintenance Defect or Problem 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 1.5 feet.
Structural Damage Structure is not securely attached to manhole Structure securely attached to wall
wall and outlet pipe structure should support at and outlet pipe.
least 1,000 lbs of up or down pressure.
Structure is not in upright position(allow up to Structure in correct position.
10%from plumb).
Connections to outlet pipe are not watertight and Connections to outlet pipe are water
show signs of rust. tight;structure repaired or replaced
and works as designed.
Any holes--other than designed holes—in the Structure has no holes other than
structure. designed holes.
Cleanout Gate Damaged or Missing Cleanout gate is 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 and
maintenance person. is watertight.
Chain/rod leading to gate is missing or damaged. Chain is in place and works as
designed.
Gate is rusted over 50%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 and
blocking the plate. works as designed.
Overflow Pipe Obstructions Any trash or debris blocking(or having the Pipe is free of all obstructions and
potential of blocking)the overflow pipe. works as designed.
Manhole See"Detention Tanks See"Detention Tanks and Vaults"Table No. 3 See"Detention Tanks and Vaults"
and Vaults" Table No. 3
2005 Surface Water Design Manual–Appendix A 1/24/2005
A-5
94
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES 3
NO. 5-CATCH BASINS
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is performed
General Trash&Debris Trash or debris of more than 1/2 cubic foot which No Trash or debris located
(Includes Sediment) is located immediately in front of the catch basin immediately in front of catch basin
opening or is blocking capacity of the basin by 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 basin.
lowest pipe into or out of the basin.
Trash or debris in any inlet or outlet pipe blocking Inlet and outlet pipes free of trash or
more than 1/3 of its height. 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 would
volume. attract or support the breeding of
insects or rodents.
Structure Damage to Comer of frame extends more than%inch past Frame is even with curb.
Frame and/or Top curb face into the street(If applicable).
Slab
Top slab has holes larger than 2 square inches Top slab is free of holes and cracks.
or cracks wider than'/4 inch(intent is to make
sure all material is running into basin).
Frame not sitting flush on top slab, i.e., Frame is sitting flush on top slab.
separation of more than%inch of the frame from
the top slab.
Cracks in Basin Cracks wider than'/7 inch and longer than 3 feet, Basin replaced or repaired to design
Walls/Bottom any evidence of soil particles entering catch standards.
basin through cracks,or maintenance person
judges that structure is unsound.
Cracks wider than'A inch and longer than 1 foot No cracks more than 1/4 inch wide at
at the joint of any inlet/outlet pipe or any the joint of inlet/outlet pipe.
evidence of soil particles entering catch basin
through cracks.
Settlement/ Basin has settled more than 1 inch or has rotated Basin replaced or repaired to design
Misalignment more than 2 inches out of alignment. standards.
Fire Hazard Presence of chemicals such as natural gas,oil No flammable chemicals present.
and gasoline.
Vegetation Vegetation growing across and blocking more No vegetation blocking opening to
than 10%of the basin opening. basin.
Vegetation growing in inlet/outlet pipe joints that No vegetation or root growth
is more than 6 inches tall and less than 6 inches present.
apart.
Pollution Nonflammable chemicals of more than'/z cubic No pollution present other than
foot per three feet of basin length. surface film.
Catch Basin Cover Cover Not in Place Cover is missing or only partially in place.Any Catch basin cover is closed
open catch basin requires maintenance.
Locking Mechanism Mechanism cannot be opened by on Mechanism opens with proper tools.
Not Working maintenance person with proper tools. Bolts into
frame have less than''A inch of thread.
Cover Difficult to One maintenance person cannot remove lid after Cover can be removed by one
Remove applying 80 lbs.of lift;intent is keep cover from maintenance person.
sealing off access to maintenance.
Ladder Ladder Rungs Unsafe Ladder is unsafe due to missing rungs, Ladder meets design standards and
misalignment,rust, cracks,or sharp edges. allows maintenance person safe
access.
1/24/2005 2005 Surface Water Design Manual—Appendix A
A-6
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES 5�3
NO. 5-CATCH BASINS
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is performed
Metal Grates Unsafe Grate Grate with opening wider than 7/8 inch. Grate opening meets design
(If Applicable) Opening standards.
Trash and Debris Trash and debris that is blocking more than 20% Grate free of trash and debris.
of grate surface.
Damaged or Missing. Grate missing or broken member(s)of the grate. Grate is in place and meets design
standards.
NO. 6- DEBRIS BARRIERS (E.G., TRASH RACKS)
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed.
General Trash and Debris Trash or debris that is plugging more than 20% Barrier clear to receive capacity
of 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% Repair or replace barrier to design
deterioration to any part of barrier. standards.
NO. 7-ENERGY DISSIPATERS
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed.
External:
Rock Pad Missing or Moved Only one layer of rock exists above native soil in Replace rocks to design standards.
Rock area five square feet or larger,or any exposure
of native soil.
Dispersion Trench Pipe Plugged with Accumulated sediment that exceeds 20%of the Pipe cleaned/flushed so that it
Sediment design depth. matches design.
Not Discharging Visual evidence of water discharging at Trench must be redesigned or
Water Properly concentrated points along trench(normal rebuilt to standards.
condition is a"sheet flow"of water along trench).
Intent is to prevent erosion damage.
Perforations Plugged. Over'/2 of perforations in pipe are plugged with Clean or replace perforated pipe.
debris and sediment.
Water Flows Out Top Maintenance person observes water flowing out Facility must be rebuilt or
of"Distributor"Catch during any storm less than the design storm or redesigned to standards.
Basin. its causing or appears likely to cause damage.
Receiving Area Over- Water in receiving area is causing or has No danger of landslides.
Saturated potential of causing landslide problems.
Internal:
Manhole/Chamber Worn or Damaged Structure dissipating flow deteriorates to'A or Replace structure to design
Post.Baffles,Side of original size or any concentrated worn spot standards.
Chamber exceeding one square foot which would make
structure unsound.
2005 Surface Water Design Manual—Appendix A 1/24/2005
A-7
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
' +.
NO. 10-CONVEYANCE PIPES AND DITCHES
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Pipes Sediment&Debris Accumulated sediment that exceeds 20%of the Pipe cleaned of all sediment and
diameter of the pipe. debris.
Vegetation Vegetation that reduces free movement of water All vegetation 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 Pipe repaired or replaced.
of 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 all
design depth. sediment and debris so that it
matches design.
Vegetation Vegetation that reduces free movement of water Water flows freely through ditches.
through ditches.
Erosion Damage to See"Detention Ponds"Table No. 1 See"Detention Ponds"Table No. 1
Slopes
Rock Lining Out of Maintenance person can see native soil beneath Replace rocks to design standards.
Place or Missing(If the rock lining.
Applicable).
NO. 11 -GROUNDS (LANDSCAPING)
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
General Weeds Weeds growing in more than 20%of the Weeds present in less than 5%of
(Nonpoisonous,not landscaped area(trees and shrubs only). the landscaped area.
noxious)
Safety Hazard Any presence of poison ivy or other poisonous No poisonous vegetation present in
vegetation. landscaped area.
Trash or Litter Paper,cans, bottles,totaling more than 1 cubic Area clear of litter.
foot 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 5%
broken which affect more than 25%of the total of total foliage with split or broken
foliage of the tree or shrub. limbs.
Trees or shrubs that have been blown down or Tree or shrub in place free of injury.
knocked over.
Trees or shrubs which are not adequately Tree or shrub in place and
supported or are leaning over,causing exposure adequately supported;remove any
of the roots. dead or diseased trees.
2005 Surface Water Design Manual—Appendix A 1/24/2005
A-9
7
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES 13
NO. 20-STORMFILTER°
Maintenance Defect or Problem Condition When Maintenance is Needed Recommended Maintenance to
Component Correct Problem
Media Section Sediment Sediment depth exceeds 0.25 inches. No sediment deposits that would
Accumulation on impede permeability of the compost
Media. media.
Trash/Debris Trash and debris accumulated on compost filter Trash and debris removed from the
Accumulation bed. compost filter bed.
First Chamber Sediment Sediment depth exceeds 6 inches in first No sediment deposits in vault
Accumulation chamber. bottom of first chamber.
Drain Pipes Clean- Sediment When drain pipes,clean-outs, become full with Remove the accumulated material
Outs Accumulation sediment and/or debris. from the facilities.
NO. 21 -STORMFILTER°(CARTRIDGE TYPE)
Maintenance Defect or Problem Condition When Maintenance is Needed Recommended Maintenance to
Component Correct Problem
Compost Media Plugged Drawdown of water through the media takes Replace media cartridges.
longer than 1 hour,and/or overflow occurs
frequently.
Short Circuiting Flows do not properly enter filter cartridges. Replace filter cartridges.
Pipes Damaged Any part of the pipes that are crushed,damaged Pipe repaired and/or replaced.
due to corrosion and/or settlement.
Access Cover Damaged/Not Cover cannot be opened,one person cannot Cover repaired to proper working
Working open the cover,corrosion/deformation of cover. specifications or replaced.
Vault Structure Damage to Wall, Cracks wider than 1/4-inch and any evidence of Vault replaced or repaired to design
Frame, Bottom, soil particles entering the structure through the specifications.
and/or Top Slab cracks,or maintenance/inspection personnel
determines that the vault is not structurally
sound.
Damaged Pipe Joints Cracks wider than'/3-inch at the joint of any No cracks more than'/.-inch wide at
inlet/outlet pipe or any evidence of soil particles the joint of the inlet/outlet pipe.
entering the vault through the walls.
Baffles Damaged Baffles corroding,cracking warping,and/or Repair or replace baffles to
showing signs of failure as determined by specification.
maintenance/inspection person.
Access Ladder Damaged Ladder is corroded or deteriorated,not Ladder replaced or repaired and
functioning properly,missing rungs,cracks,and meets specifications,and is safe to
misaligned. use as determined by inspection
personnel.
2005 Surface Water Design Manual—Appendix A 1/24/2005
A-17
A��ii \IT!'Al> Important: Inspection should be performed by a person who is
erro:d��i i'�n The sto,mwaterManagement y►
CONSTRUCTION PRODUCTS INC. StormFilter familiar with the StormFilter treatment unit.
1. If applicable,set up safety equipment to protect and notify
surrounding vehicle and pedestrian traffic.
StormFilter Maintenance Guidelines 2.Visually inspect the external condition of the unit and take notes
Maintenance requirements and frequency are dependent on the concerning defects/problems.
pollutant load characteristics of each site, and may be required in 3. Open the access portals to the vault and allow the system vent.
the event of a chemical spill or due to excessive sediment loading. 4.Without entering the vault,visually inspect the inside of the unit,
Maintenance Procedures and note accumulations of liquids and solids.
Although there are other effective maintenance options, CONTECH 5. Be sure to record the level of sediment build-up on the floor of
recommends the following two step procedure: the vault, in the forebay, and on top of the cartridges. If flow
is occurring, note the flow of water per drainage pipe. Record
1. Inspection: Determine the need for maintenance. all observations. Digital pictures are valuable for historical
2. Maintenance: Cartridge replacement and sediment removal. documentation.
Inspection and Maintenance Activity Timing 6.Close and fasten the access portals.
At least one scheduled inspection activity should take place per year 7. Remove safety equipment.
with maintenance following as warranted. 8.If appropriate, make notes about the local drainage area relative
First, inspection should be done before the winter season. During to ongoing construction, erosion problems, or high loading of
which,the need for maintenance should be determined and, if other materials to the system.
disposal during maintenance will be required, samples of the 9. Discuss conditions that suggest maintenance and make decision
accumulated sediments and media should be obtained. as to weather or not maintenance is needed.
Second, if warranted, maintenance should be performed during Maintenance Decision Tree
periods of dry weather. The need for maintenance is typically based on results of the inspection.
In addition,you should check the condition of the StormFilter unit Use the following as a general guide. (Other factors,such as regulatory
after major storms for potential damage caused by high flows and requirements, may need to be considered)
for high sediment accumulation. It may be necessary to adjust the 1.Sediment loading on the vault floor. If >4" of accumulated
inspection/maintenance activity schedule depending on the actual sediment,then go to maintenance.
operating conditions encountered by the system. 2.Sediment loading on top of the cartridge. If >1/4" of
Generally, inspection activities can be conducted at any time, and accumulation, then go to maintenance.
maintenance should occur when flows into the system are unlikely. 3.Submerged cartridges. If >4" of static water in the cartridge
Maintenance Activity Frequency bay for more that 24 hrs after end of rain event,then go to
Maintenance is performed on an as needed basis, based on maintenance.
inspection. Average maintenance lifecycle is 1-3 years. The primary 4. Plugged media. If pore space between media granules is absent,
factor controlling timing of maintenance of the StormFilter is then go to maintenance.
sediment loading. Until appropriate timeline is determined, use the 5. Bypass condition. If inspection is conducted during an average
following: rain fall event and StormFilter remains in bypass condition
Inspection: (water over the internal outlet baffle wall or submerged
One time per year cartridges), then go to maintenance.
After major storms 6. Hazardous material release. If hazardous material release
(automotive fluids or other) is reported,then go to
Maintenance: maintenance.
As needed 7. Pronounced scum line. If pronounced scum line(say>_ 1/4"
Per regulatory requirement thick)is present above top cap,then go to maintenance.
In the event of a chemical spill 8.Calendar Lifecycle. If system has not been maintained for 3
Inspection Procedures years,then go to maintenance.
Assumptions:
It is desirable to inspect during a storm to observe the relative
flow through the filter cartridges. If the submerged cartridges are No rainfall for 24 hours or more.
severely plugged,then typically large amounts of sediments will be No upstream detention (at least not draining into StormFilter).
present and very little flow will be discharged from the drainage Structure is online. Outlet pipe is clear of obstruction. Construction
pipes. If this is the case,then maintenance is warranted and the bypass is plugged.
cartridges need to be replaced.
Maintenance
Warning: In the case of a spill, the worker should abort inspection Depending on the configuration of the particular system,workers
activities until the proper guidance is obtained. Notify the will be required to enter the vault to perform the maintenance.
local hazard control agency and CONTECH immediately.
To conduct an inspection:
1
Cl/13
Important: If vault entry is required, OSHA rules for confined space Method 2:
entry must be followed. A. Enter the vault using appropriate confined space protocols.
Filter cartridge replacement should occur during dry weather. It may
be necessary to plug the filter inlet pipe if base flow is occurring. B. Unscrew the cartridge cap.
Repfacementtartridges can be delivered to the site or customers C. Remove the cartridge hood screws(3)hood and float.
facility. Contact CONTECH for more information. D. At location under structure access,tip the cartridge on its
Warning: In the case of a spill, the worker should abort side.
maintenance activities until the proper guidance is obtained. Notify
the local hazard control agency and CONTECH immediately. Important: Note that cartridges containing media other than
the leaf media require unscrewing from their threaded
To conduct cartridge replacement and sediment removal: connectors.Take care not to damage the manifold
1.If applicable, set up safety equipment to protect workers and connectors.This connector should remain installed in the
pedestrians from site hazards. manifold and capped if necessary.
2.Visually inspect the external condition of the unit and take notes E. Empty the cartridge onto the vault floor. Reassemble the
concerning defects/problems. empty cartridge.
3.Open the doors(access portals)to the vault and allow the system
to vent. F. Set the empty, used cartridge aside or load onto the hauling
truck.
4.Without entering the vault, give the inside of the unit, including
components,a general condition inspection. G. Continue steps a through E until all cartridges have been
5.Make notes about the external and internal condition of removed.
the vault. Give particular attention to recording the level of 8. Remove accumulated sediment from the floor of the vault and
sediment build-up on the floor of the vault, in the forebay, and from the forebay. Use vacuum truck for highest effectiveness.
on top of the internal components.
9. Once the sediments are removed, assess the condition of the
6.Using appropriate equipment offload the replacement cartridges vault and the connectors.The connectors are short sections
(up to 150 lbs.each)and set aside. of 2-inch schedule 40 PVC,or threaded schedule 80 PVC that
7.Remove used cartridges from the vault using one of the should protrude about 1" above the floor of the vault. Lightly
following methods: wash down the vault interior.
Method 1: a. Replace any damaged connectors.
A. This activity will require that workers enter the vault to
remove the cartridges from the under drain manifold and 10. Using the vacuum truck boom,crane,or tripod, lower and
place them under the vault opening for lifting (removal). install the new cartridges.Take care not to damage connections.
Unscrew(counterclockwise rotations)each filter cartridge 11. Close and fasten the door.
from the underdrain connector. Roll the loose cartridge,on 12. Remove safety equipment.
edge,to a convenient spot beneath the vault access. 13. Finally, dispose of the accumulated materials in accordance with
Using appropriate hoisting equipment, attach a cable from applicable regulations. Make arrangements to return the used
the boom, crane, or tripod to the loose cartridge. Contact empty cartridges to CONTECH.
CONTECH for suggested attachment devices. Material Disposal
Important: Cartridges containing leaf media (CSF)do not The accumulated sediment must be handled and disposed of in
require unscrewing from their connectors. Do not accordance with regulatory protocols. It is possible for sediments
damage the manifold connectors.They should remain to contain measurable concentrations of heavy metals and organic
installed in the manifold and can be capped during the chemicals. Areas with the greatest potential for high pollutant
maintenance activity to prevent sediments from entering loading include industrial areas and heavily traveled roads.
the under drain manifold. Sediments and water must be disposed of in accordance with
B. Remove the used cartridges(up to 250 lbs.)from the vault. applicable waste disposal regulations. Coordinate disposal of solids
and liquids as part of your maintenance procedure. Contact the
Important:Avoid damaging the cartridges during removal and local public works department to inquire how they disposes of their
installation. street waste residuals.
C. Set the used cartridge aside or load onto the hauling truck.
D. Continue steps A through C until all cartridges have been
removed.
©2007 CONTECH Stormwater Solutions 800.338.1122
www.contech-cpi.com
Nothing in this catalog should be construed as an expressed warranty or an implied warranty of merchantability or fitness for any particular purpose.
See the CONTECH standard quotation or acknowledgement for applicable warranties and other terms and conditions of sale.
The product(s)described may be protected by one or more of the following US patents: 5,322,629;5,624,576;5,707,527;5,759,415;5,788,848;5,985,157;
6,027,639;6,350,374;6,406,218;6,641,720;6,511,595;6,649,048;6,991,114;6,998,038;7,186,058;related foreign patents or other patents pending.
2
CONSTRUCTION PRODUCTS INC.
CDS° Inspection and Maintenance Guide
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CDS
TECHNOLOGIES
11113
Maintenance Cleaning
The CDS system should be inspected at regular intervals and Cleaning of a CDS systems should be done during dry weather
maintained when necessary to ensure optimum performance. conditions when no flow is entering the system.The use of a
The rate at which the system collects pollutants will depend more vacuum truck is generally the most effective and convenient
heavily on site activities than the size of the unit. For example, method of removing pollutants from the system. Simply remove
unstable soils or heavy winter sanding will cause the grit chamber the manhole covers and insert the vacuum hose into the sump.
to fill more quickly but regular sweeping of paved surfaces will The system should be completely drained down and the sump
slow accumulation. fully evacuated of sediment.The area outside the screen should
also be cleaned out if pollutant build-up exists in this area.
Inspection In installations where the risk of petroleum spills is small, liquid
Inspection is the key to effective maintenance and is easily contaminants may not accumulate as quickly as sediment.
performed. Pollutant transport and deposition may vary from However, the system should be cleaned out immediately in
year to year and regular inspections will help ensure that the the event of an oil or gasoline spill should be cleaned out
system is cleaned out at the appropriate time. At a minimum, immediately. Motor oil and other hydrocarbons that accumulate
inspections should be performed twice per year(e.g. spring on a more routine basis should be removed when an appreciable
and fall)however more frequent inspections may be necessary layer has been captured. To remove these pollutants, it may
in climates where winter sanding operations may lead to rapid be preferable to use absorbent pads since they are usually less
accumulations,or in equipment washdown areas. Installations expensive to dispose than the oil/water emulsion that may be
should also be inspected more frequently where excessive created by vacuuming the oily layer.Trash and debris can be
amounts of trash are expected. netted out to separate it from the other pollutants. The screen
The visual inspection should ascertain that the system should be power washed to ensure it is free of trash and debris.
components are in working order and that there are no Manhole covers should be securely seated following cleaning
blockages or obstructions in the inlet and separation screen. activities to prevent leakage of runoff into the system from above
The inspection should also quantify the accumulation of and also to ensure that proper safety precautions have been
hydrocarbons, trash, and sediment in the system. Measuring followed. Confined space entry procedures need to be followed
pollutant accumulation can be done with a calibrated dipstick, if physical access is required. Disposal of all material removed
tape measure or other measuring instrument. If absorbent from the CDS system should be done in accordance with local
material is used for enhanced removal of hydrocarbons, the level regulations. In many jurisdictions,disposal of the sediments may
of discoloration of the sorbent material should also be identified be handled in the same manner as the disposal of sediments
during inspection. It is useful and often required as part of an removed from catch basins or deep sump manholes.
operating permit to keep a record of each inspection. A simple
form for doing so is provided.
Access to the CDS unit is typically achieved through two manhole
access covers. One opening allows for inspection and cleanout
of the separation chamber(cylinder and screen)and isolated
sump. The other allows for inspection and cleanout of sediment
captured and retained outside the screen. For deep units, a
single manhole access point would allows both sump cleanout
and access outside the screen. •
The CDS system should be cleaned when the level of sediment
has reached 75%of capacity in the isolated sump or when an
appreciable level of hydrocarbons and trash has accumulated.
If absorbent material is used, it should be replaced when . •
significant discoloration has occurred. Performance will not be
impacted until 100%of the sump capacity is exceeded however
it is recommended that the system be cleaned prior to that
for easier removal of sediment. The level of sediment is easily
determined by measuring from finished grade down to the
top of the sediment pile. To avoid underestimating the level of
sediment in the chamber,the measuring device must be lowered
to the top of the sediment pile carefully. Particles at the top of r �.�
the pile typically offer less resistance to the end of the rod than '41-.1.1;‘•` '. w„. •
consolidated particles toward the bottom of the pile. Once this ..
measurement is recorded, it should be compared to the as-built
drawing for the unit to determine weather the height of the
sediment pile off the bottom of the sump floor exceeds 75%of
3 s zap. t ,� ,
the total height of isolated sump. a w: , ,q > 4 {A g ter
g
z/i 3
CDS Diameter Distance from Water Surface Sediment
Model to Top of Sediment Pile Storage Capacity
ft m ft m yd3 m3
CDS2015-4 4 1.2 3.0 0.9 0.5 0.4
CDS2020 5 1.5 3.5 1.1 1.3 1.0
CDS3020 6 1.8 4.0 1.2 2.1 1.6
CDS3035 6 1.8 5.0 1.5 2.1 1.6
CDS4040 8 2.4 5.7 1.7 5.6 4.3
Table 1:CDS Maintenance Indicators and Sediment Storage Capacities
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supper
• Drawings and specifications are available at www.contechstormwatercom.
• Site-specific design support is available from our engineers.
T2010 CONTECH Stormwater Solutions
CONTECH Construction Products Inc provides site solutions for the civil engineering industry,
CONTECH's portfolio indudes bridges,drainage,sanitary sewer,stormwater and earth
stabilization products.For information on other CONTECH division offerings,visit contech-
cpi.com or call 800.338.1122
Nothing in this catalog should be construed as an expressed warranty or an implied
warranty of merchantability or fitness for any particularpurpose.See the CONTECH standard
quotation or acknowledgement for applicable warranties and other terms and conditions of
sake.
The product(s)described may be protected by one or more of the following US patents:
5,322,629;5,624,576;5,707,527;5,759,415;5,788,848;5,985,157;6,027,639;6. 350,374; A \ITCApJ`
6,406,218;6,641,720;6,511,595;6,649,048;6,991,114;6,998,038;7,186,058;7,296,692;
1%..';'4‘4 i��!7
7,297,266;7,517,450 related foreign patents or other patents pending. CONSTRUCTION PRODUCTS ina
800.925.5240
cdsMaintenance 01/10 contechstormwateccom
130
CDS Inspection & Maintenance Log
CDS Model: Location:
Water Floatable Describe
Maintenance
Date depth to Layer Maintenance Comments
Personnel
sediment' Thickness' Performed
1. The water depth to sediment is determined by taking two measurements with a stadia rod:one measurement from the manhole opening to
the top of the sediment pile and the other from the manhole opening to the water surface. If the difference between these measurements is
less than eighteen inches the system should be cleaned out. Note:To avoid underestimating the volume of sediment in the chamber,the
measuring device must be carefully lowered to the top of the sediment pile.
2. For optimum performance,the system should be cleaned out when the floating hydrocarbon layer accumulates to an appreciable thickness.In
the event of an oil spill,the system should be cleaned immediately.
I
APPENDIX E
BOND QUANTITIES WORKSHEETS
Site Improvement Bond Quantity Worksheet Web date: 12/02/2008
La King County
Department of Development & Environmental Services
900 Oakesdale Avenue Southwest
Renton, Washington 98057-5212 For alternate formats, call 206-296-6600.
206-296-6600 TTY 206-296-7217
Project Name: 1500 and 1600 Benson Apartments and Offices Date: 4/8/2013
Location: 15xx Benson Road South Project No.: 05-125
Activity No.:
Note: All prices include labor, equipment, materials, overhead and
Clearing greater than or equal to 5,000 board feet of timber? profit. Prices are from RS Means data adjusted for the Seattle area
or from local sources if not included in the RS Means database.
yes x no
If yes,
Forest Practice Permit Number:
(RCW 76.09)
Page 1 of 9
Unit prices updated: 02/12/02
Version: 11/26/2008
Bond Quantities Report Date: 4/8/2013
Site Improvement Bond Quantity Worksheet Web date 12/02/2008
Unit #of
Reference# Price Unit Quantity Applications Cost
EROSION/SEDIMENT CONTROL Number
Backfill &compaction-embankment ESC-1 $ 5.62 CY
Check dams,4"minus rock ESC-2 SWDM 5.4.6.3 $ 67.51 Each
Crushed surfacing 1 1/4" minus ESC-3 WSDOT 9-03.9(3) $ 85.45 CY
Ditching ESC-4 $ 8.08 CY
Excavation-bulk ESC-5 $ 1.50 CY
Fence, silt ESC-6 SWDM 5.4.3.1 $ 1.38 LF 920 1 1270
Fence,Temporary(NGPE) ESC-7 $ 1.38 LF
Hydroseeding ESC-8 SWDM 5.4.2.4 $ 0.59 SY 4840 1 2856
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 4840 1 2565
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 2000 1 4600
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 3 1 8786
Sediment pond riser assembly ESC-19 SWDM 5.4.5.2 $ 1,949.38 Each
Sediment trap, 5' high berm ESC-20 SWDM 5.4.5.1 $ 17.91 LF
Sed.trap,5'high, riprapped spillway berm section ESC-21 SWDM 5.4.5.1 $ 68.54 LF
Seeding, by hand ESC-22 SWDM 5.4.2.4 $ 0.51 SY
Sodding, 1"deep, level ground ESC-23 SWDM 5.4.2.5 $ 6.03 SY
Sodding, 1"deep, sloped ground ESC-24 SWDM 5.4.2.5 $ 7.45 SY
TESC Supervisor ESC-25 $ 74.75 HR 40 1 2990
Water truck, dust control ESC-26 SWDM 5.4.7 $ 97.75 HR 20 1 1955
WRITE-IN-ITEMS **** (see page 9)
Baker Tank per week $ 1,000 00 Each 16 1 16000
I
ESC SUBTOTAL: $ 41,021.44
30%CONTINGENCY&MOBILIZATION: $ 12,306.43
ESC TOTAL: $ 53,327.87
COLUMN: A
Page 2 of 9
Unit prices updated: 02/12/02
Version: 11/26/2008
Bond Quantities Report Date: 4/8/2013
Site Improvement BciPi Quantity Worksheet Webda.z/zoos
Existing Future Public Private Quantity Completed
Right-of-Way Road Improvements Improvements (Bond Reduction)*
&Drainage Facilities Quant.
Unit Price _ Unit Quant. Cost Quant. - Cost Quant. Cost Complete Cost
GENERAL ITEMS No.
Backfill&Compaction-embankment GI-1 $ 5.62 CY
Backfill&Compaction-trench GI-2 $ 8.53 CY 170 1,450.10
Clear/Remove Brush,by hand GI-3 $ 0.36 SY
Clearing/Grubbing/Tree Removal GI-4 $ 8,876.16 Acre 2.16 19,172.51
Excavation-bulk GI-5 $ 1.50 CY 13482 20,223.00
Excavation-Trench GI-6 $ 4.06 CY 227 921.62
Fencing,cedar,6'high GI-7 $ 18.55 LF
Fencing,chain link,vinyl coated, 6'high GI-8 $ 13.44 LF
Fencing,chain link,gate,vinyl coated, 2 GI-9 $ 1,271.81 Each
Fencing,split rail,3'high GI-10 $ 12.12 LF
Fill&compact-common barrow GI-11 $ 22.57 CY 2000 45,140.00
Fill&compact-gravel base GI-12 $ 25.48 CY
Fill&compact-screened topsoil GI-13 $ 37.85 CY
Gabion, 12"deep,stone filled mesh GI-14 $ 54.31 SY
Gabion, 18"deep,stone filled mesh GI-15 $ 74.85 SY
Gabion,36"deep,stone filled mesh GI-16 $ 132.48 SY
Grading,fine,by hand GI-17 $ 2.02 SY
Grading,fine,with grader GI-18 $ 0.95 SY
Monuments,3'long GI-19 $ 135.13 Each
Sensitive Areas Sign GI-20 $ 2.88 Each
Sodding, 1"deep,sloped ground GI-21 $ 7.46 SY
Surveying,line&grade GI-22 $ 788.26 Day
Surveying,lot location/lines GI-23 $ 1,556.64 Acre
Traffic control crew(2 flaggers) GI-24 $ 85.18 HR 40 3,407.20
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 7931 350,232.96
Wall,rockery GI-29 $ 9.49 SF 68 645.32
Page 3 of 9 SUBTOTAL 441,192.71
Unit prices updated: 02/12/02
*KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantities Report Date:4/8/2013
• Site Improvement B Web da 2/2008
p Quantity Worksheet
Existing Future Public Private Bond Reduction*
Right-of-way Road Improvements Improvements
&Drainage Facilities Quant.
Unit Price Unit Quant. Cost Quant, Cost Quant. Cost Complete Cost
ROAD IMPROVEMENT No.;
AC Grinding,4'wide machine<1000sy RI-1 S 28.00 SY
AC Grinding,4'wide machine 1000-200C RI-2 $ 15.00 SY
AC Grinding,4'wide machine>2000sy RI-3 $ 7.00 SY
AC Removal/Disposal/Repair RI-4 $ 67.50 SY
Barricade,type I RI-5 $ 30.03 LF
Barricade,type III(Permanent) RI-6 $ 45.05 LF
Curb&Gutter,rolled RI-7 $ 17.00 LF
Curb&Gutter,vertical RI-8 $ 12.50 LF 1300 16,250.00
Curb and Gutter,demolition and disposa RI-9 $ 18.00 LF
Curb,extruded asphalt RI-10 $ 5.50 LF
Curb,extruded concrete RI-11 $ 7.00 LF
Sawcut,asphalt,3"depth RI-12 $ 1.85 LF 30 55.50
Sawcut,concrete,per 1"depth RI-13 $ 1.69 LF
Sealant,asphalt RI-14 $ 1.25 LF 30 37.50
Shoulder,AC, (see AC road unit price) RI-15 $ - SY
Shoulder,gravel,4"thick RI-16 $ 15.00 SY
Sidewalk,4"thick RI-17 $ 35.00 SY 200 7,000.00
Sidewalk,4"thick,demolition and dispos RI-18 $ 29.50 SY
Sidewalk,5"thick RI-19 $ 38.50 SY
Sidewalk,5"thick,demolition and dispos RI-20 $ 37.50 SY
Sign,handicap RI-21 $ 85.28 Each
Striping,per stall RI-22 $ 5.82 Each 50 291.00
Striping,thermoplastic,(for crosswalk) RI-23 $ 2.38 SF
Striping,4"reflectorized line RI-24 $ 0.25 LF 1
Page 4 of 9 SUBTOTAL 93.00 23,541.00
Unit prices updated: 02/12/02
*KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantities Report Date:4/8/2013
Site Improvement Bc Quantity Worksheet Web da 2/2008
Existing Future Public Private Bond Reduction*
Right-of-way Road Improvements Improvements
&Drainage Facilities Quant.
Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Complete Cost
ROAD SURFACING (4"Rock=2.5 base&1.5"top course) For'93 KCRS(6.5"Rock=5"base&1.5"top course)
For KCRS'93,(additional 2.5"base)add RS- 1 $ 3.60 SY
AC Overlay, 1.5"AC RS-2 $ 11.25 SY
AC Overlay,2"AC RS-3 $ 15.00 SY
AC Road,2",4"rock,First 2500 SY RS-4 $ 21.00 SY 2500 52,500.00
AC Road,2",4"rock,Qty.over 2500SY RS-5 $ 19.00 SY 65 1,235.00 _
AC Road,3",4"rock,First 2500 SY RS-6 $ 23.30 SY
AC Road,3",4"rock,Qty.over 2500 SY RS-7 $ 21.00 SY
AC Road,5",First 2500 SY RS-8 $ 27.60 SY
AC Road,5",Qty.Over 2500 SY RS-9 $ 25.00 SY
AC Road,6",First 2500 SY RS-1C $ 33.10 SY
AC Road,6",Qty.Over 2500 SY RS-11 $ 30.00 SY
Asphalt Treated Base,4"thick RS-12 $ 20.00 SY
Gravel Road,4"rock,First 2500 SY RS-13 $ 15.00 SY 130 1,950.00
Gravel Road,4"rock,Qty.over 2500 SY RS-14 $ 8.50 SY
PCC Road,5",no base,over 2500 SY RS-15 $ 27.00 SY
PCC Road, 6",no base,over 2500 SY RS-18 $ 25.50 SY
Thickened Edge RS-17 $ 8.60 LF
Page 5 of 9 SUBTOTAL 55,685.00
Unit prices updated: 02/12/02
*KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantities Report Date:4/8/2013
• Site Improvement B Webda 2/2008
p Quantity Worksheet '�
Existing Future Public Private Bond Reduction*
Right-of-way Road Improvements Improvements
&Drainage Facilities Quant.
Unit Price Unit _ Quant. Cost Quant. Cost Quant. Cost Complete Cost
DRAINAGE (CPP=Corrugated Plastic Pipe. N12 or Equivalent) For Culvert prices, Average of 4'cover was assumed Assume perforated PVC is same price as solid pipe.
Access Road, R/D D-1 $ 21.00 SY _
Bollards-fixed D-2 $ 240.74 Each
Bollards-removable D-3 $ 452.34 Each
*(CBs include frame and lid)
CB Type I D-4 $ 1,257.64 Each 12 15,091.68
CB Type IL D-5 $ 1,433.59 Each
CB Type II,48"diameter D-6 $ 2,033.57 Each 3 6,100.71
for additional depth over 4' D-7 $ 436.52 FT
CB Type II,54"diameter D-8 $ 2,192.54 Each
for additional depth over 4' D-9 $ 486.53 FT
CB Type II,60"diameter D-10 $ 2,351.52 Each
for additional depth over 4' D-11 $ 536.54 FT
CB Type II,72"diameter D-12 $ 3,212.64 Each
for additional depth over 4' D-13 $ 692.21 FT
Through-curb Inlet Framework(Add) D-14 $ 366.09 Each
Cleanout,PVC,4" D-15 $ 130.55 Each
Cleanout,PVC,6" D-16 $ 174.90 Each
Cleanout,PVC,8" D-17 $ 224.19 Each
Culvert,PVC,4" D-18 $ 8.64 LF
Culvert,PVC,6" D-19 $ 12.60 LF
Culvert,PVC, 8" D-20 $ 13.33 LF
Culvert,PVC, 12" D-21 $ 21.77 LF
Culvert,CMP,8" D-22 $ 17.25 LF
Culvert,CMP,12" D-23 $ 26.45 LF
Culvert,CMP,15" D-24 $ 32.73 LF
Culvert,CMP, 18" D-25 $ 37.74 LF
Culvert,CMP,24" D-26 $ 53.33 LF
Culvert,CMP,30" D-27 $ 71.45 LF
Culvert,CMP,36" D-28 $ 112.11 LF
Culvert,CMP,48" D-29 $ 140.83 LF
Culvert,CMP,60" D-30 $ 235.45 LF
Culvert,CMP,72" D-31 $ 302.58 LF
Page 6 of 9 SUBTOTAL 21,192.39
Unit prices updated: 02/12/02
*KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantities Report Date:4/8/2013
Site Improvement 13( Quantity Worksheet Web da 2,2008
Existing Future Public Private Bond Reduction*
Right-of-way Road Improvements Improvements
DRAINAGE CONTINUED &Drainage Facilities Quant.
No. _ Unit Price Unit Quant. Cost _ Quant. Cost Quant. Cost Complete Cost
Culvert,Concrete,8" D-32 $ 21.02 LF
Culvert,Concrete, 12" D-33 $ 30.05 LF
Culvert,Concrete, 15" D-34 $ 37.34 LF
Culvert,Concrete, 18" D-35 $ 44.51 LF
Culvert,Concrete,24" D-36 $ 61.07 LF
Culvert,Concrete,30" D-37 $ 104.18 LF
Culvert,Concrete,36" D-38 $ 137.63 LF
Culvert,Concrete,42" D-39 $ 158.42 LF
Culvert,Concrete,48" D-40 $ 175.94 LF
Culvert,CPP,6" D-41 $ 10.70 LF 76 813.2
Culvert,CPP,8" D-42 $ 16.10 LF 247 3976.7
Culvert,CPP, 12" D-43 $ 20.70 LF 528 10929.6
Culvert,CPP, 15" D-44 $ 23.00 LF
Culvert,CPP, 18" D-45 $ 27.60 LF
Culvert,CPP,24" D-46 $ 36.80 LF
Culvert,CPP,30" D-47 $ 48.30 LF
Culvert,CPP,36" D-48 $ 55.20 LF
Ditching D-49 $ 8.08 CY
Flow Dispersal Trench (1,436 base+) D-50 $ 25.99 LF
French Drain (3'depth) D-51 $ 22.60 LF
Geotextile,laid in trench,polypropylene ,D-52, $ 2.40 SY
Infiltration pond testing D-53 $ 74.75 HR
Mid-tank Access Riser,48"dia, 6'deep D-54 $ 1,605.40 Each
Pond Overflow Spillway D-55 $ 14.01 SY
Restrictor/Oil Separator, 12" D-56 $ 1,045.19 Each 2 2090.38
Restrictor/Oil Separator, 15" D-57 $ 1,095.56 Each
Restrictor/Oil Separator, 18" D-58 $ 1,146.16 Each
Riprap,placed D-59 $ 39.08 CY
Tank End Reducer(36"diameter) D-60 $ 1,000.50 Each
Trash Rack, 12" D-61 $ 211.97 Each
Trash Rack, 15" D-62 $ 237.27 Each
Trash Rack, 18" D-63 $ 268.89 Each
Trash Rack,21" D-64 $ 306.84 Each
Page 7 of 9 SUBTOTAL 17809.88
Unit prices updated: 02/12/02
*KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantities Report Date:4/8/2013
Site Improvement Bc Quantity Worksheet Web da )2/2008
Existing Future Public Private Bond Reduction*
Right-of-way Road Improvements Improvements
&Drainage Facilities Quant.
Unit Price _ Unit Quant. Price Quant. Cost Quant. Cost Complete Cost
PARKING LOT SURFACING
No.
2"AC,2"top course rock&4"borrow PL-1 $ 21.00 SY
2"AC, 1.5" top course&2.5"base cour PL-2 $ 28.00 SY
4"select borrow PL-3 $ 4.55 SY
1.5"top course rock&2.5"base course PL-4 $ 11.41 SY
UTILITY POLES & STREET LIGHTING Utility pole relocation costs must be accompanied by Franchise Utility's Cost Statement
Utility Pole(s)Relocation UP-1 Lump Sum
Street Light Poles w/Luminaires UP-2 Each
WRITE-IN-ITEMS
(Such as detention/water quality vaults.) No.
Detention Vault WI-1 $ 5.00 CF 38400 192,000.00
Stormfilter Insert WI-2 $ 4,000.00 EA 1 4,000.00
Vortsentry Insert WI-3 $ 4,000.00 EA 1 4,000.00
WI-4 LF
WI-5 FT
WI-6
WI-7
WI-8
WI-9
w)-io
SUBTOTAL 200,000.00
SUBTOTAL(SUM ALL PAGES): 93.00 759,420.98
30%CONTINGENCY&MOBILIZATION: 27.90 227,826.29
GRANDTOTAL: 120.90 987,247.27
COLUMN: B C D E
Page 8 of 9
Unit prices updated: 02/12/02
*KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantities Report Date:4/8/2013
Web date: 12/02/2008
Site Improvement Bond Quantity Worksheet
Original bond computations prepared by:
Name: Lorna M Taylor Date: 4/8/2013
PE Registration Number: 29351 Tel.#: 425-391-1415
Firm Name: TEC, Inc.
Address: 485 Rainier Blvd N., #102, PO Box 1787, Issaquah, WA 98027 Project No: 05-125
ROAD IMPROVEMENTS&DRAINAGE FACILITIES FINANCIAL GUARANTEE REQUIREMENTS
PERFORMANCE BOND* PUBLIC ROAD&DRAINAGE
AMOUNT BOND*AMOUNT MAINTENANCE/DEFECT BOND*
REQUIRED AT RECORDING OR
Stabilization/Erosion Sediment Control (ESC) (A) $ 53,327.9 TEMPORARY OCCUPANCY***
Existing Right-of-Way Improvements (B) $ 120.9
Future Public Road Improvements& Drainage Facilities (C) $ -
Private Improvements (D) $ 987,247.3
Calculated Quantity Completed (E) $ -
Total Right-of Way and/or Site Restoration Bond*/** (A+B) $ 53,448.8
(First$7,500 of bond*shall be cash.)
Performance Bond*Amount (A+B+C+D) = TOTAL (T) $ 1,040,696.0 T x 0.30 $ 312,208.8 OR
Minimum bond*amount is$1000.
Reduced Performance Bond*Total*** (T-E) $ 1,040,696.0
Use larger of Tx30%or(T-E)
(B+C)x
Maintenance/Defect Bond*Total 0.25= $ 30.2
NAME OF PERSON PREPARING BOND*REDUCTION: Date:
*NOTE: The word"bond"as used in this document means any financial guarantee acceptable to King County.
**NOTE: KCC 27A authorizes right of way and site restoration bonds to be combined when both are required.
The restoration requirement shall include the total cost for all TESC as a minimum, not a maximum. In addition,corrective work,both on-and off-site needs to be included.
Quantities shall reflect worse case scenarios not just minimum requirements. For example,if a salmonid stream may be damaged,some estimated costs for restoration
needs to be reflected in this amount. The 30%contingency and mobilization costs are computed in this quantity.
***NOTE: Per KCC 27A,total bond amounts remaining after reduction shall not be less than 30%of the original amount(T)or as revised by major design changes.
SURETY BOND RIDER NOTE: If a bond rider is used,minimum additional performance bond shall be $ 987,247.3 (C+D)-E
REQUIRED BOND*AMOUNTS ARE SUBJECT TO REVIEW AND MODIFICATION BY DDES
Page 9 of 9 Unit prices updated: 02/12/02
Check out the DDES Web site at www.kingcountvgov/permits Version: 11/26/08
Bond Quantities Report Date: 4/8/2013
APPENDIX F
RETENTION/DETENTION FACILITY
SUMMARY SHEETS & SKETCHES
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL e3
STORMWATER FACILITY SUMMARY SHEET DDES Permit
Number / /./a/eTh
(provide one Stormwater Facility Summary Sheet per Natural Discharge Location)
Overview:
Project Name
/5710 4xt9 /6'0O , AJcoAl.4W-Ei7 1/ 1Tc 44/D ac-iiaj Date //- 2o-- /2--
Downstream
ZDownstream Drainage Basins
Major Basin Name a> L ,e /2,,
Immediate Basin Name tic tA/4 mcz_f
Flow Control:
Flow Control Facility Name/Number Nt,er/ j- E NpOiL '(r
Facility
Location _ow /1012rh/ "6(44 £o7 Oen iJf 4,1 J9m.J4
If none,
Flow control provided in regional/shared facility(give
location)
No flow control required Exemption number
General Facility Information:
Type/Number of detention facilities: Type/Number of infiltration facilities:
ponds ponds
vaults tanks
tanks trenches
Control Structure Location
hk-73/(A/ VAULT
Type of Control Structure 7-- f/c,U,p Number of Orifices/Restrictions
2-
Size of Orifice/Restriction: No. 1 a',7
No. 2 f).
No. 3
No. 4
Flow Control Performance Standard /f -9)OA/
2009 Surface Water Design Manual 1/9/2009
1
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL 2/G
Live Storage Volume /Ll, N�( 't Depth l0 / Volume Factor of Safety
Z '4411PiVJI./TTlfi_j
Number of Acres Served /, / 3
Number of Lots
Dam Safety Regulations (Washington State Department of Ecology)
Reservoir Volume above natural grade
Depth of Reservoir above natural grade
Facility Summary Sheet Sketch
All detention, infiltration and water quality facilities must include a detailed sketch.
(11"x17" reduced size plan sheets may be used)
/-OLL.O`ud/ ado /244z-
2009 Surface Water Design Manual 1/9/2009
2
te
54g
P- • ir VENTILATION PIPE
es (TYPICAL 4 CORNERS)
1 PRECAST_______-3\ GLIM-.-
,_, SD OUT
1:, I SUMP
I -179.06
IA
I I _/169.06
• cl -------4.—"" f.r.— —
• _
168.06
SD IN/ PM 'e SMINi-5
. • • • • • . . •
- • . . . . ' • . •
. . .
' ' . • • . .
. RIM 180.87. • . HANDHOLDS AND
• =
,..---- -4 .
•
.
•
.
lay...179.0167_,.:8114 181:196/DST9'wG.SNoPER2_Koo6C R.S
• FINISHED GRADE
GRAVEL ACCESS ROAD
•
: — 1 g__ __,w
IE IN 177.06 - = --IR.— a— . .----- ---- -- ______
---- '
.— --,---
2.b 0 :„.......----SEE CONTROL STRUCTURE —
_ .
•
.0 • DETAIL.THIS SHEET
• • . • - .
• • •
168 0 - '''•-BOTTOM OF MEE(BACKGROUND) . -i7-‘-IE OUT
W.- 169.06 •
. _
•
• .
• . . . ip,. . ...*N..N"-PRECJST:
SUMP • .
• • • • ' ' . .
. . . . . . . • .
• . . . • • - . .
• • • • • • • . .
. . . . .
' ' • .
• • • .
' . •
. . . • . . .
PROD F
NORTH DETENTION VAULT
SCALE. 1 =2O
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL 9/8
STORMWATER FACILITY SUMMARY SHEET DDES Permit
Number Sou
(provide one Stormwater Facility Summary Sheet per Natural Discharge Location)
Overview:
Project Name
/SZYM'10/10001b .0A/ JJ44f/) 26 J Date It- ZD 'a--
Downstream
aZDownstream Drainage Basins
Major Basin Name 34Cle le i.
Immediate Basin Name Rot-cm/4 /5'
Flow Control:
Flow Control Facility Name/Number f(Urn ii l7pni („7,41A L_7
Facility
Location Ezz/Mr cDlr-1/J)49 i 4 GOT, SjC, 6F Sou77 evc.Om /
If none,
Flow control provided in regional/shared facility (give
location)
No flow control required Exemption number
General Facility Information:
Type/Number of detention facilities: Type/Number of infiltration facilities:
ponds ponds
vaults tanks
tanks trenches
Control Structure Location
him/iv vI i'-r
Type of Control Structure 7 -r/Cdp Number of Orifices/Restrictions
Size of Orifice/Restriction: No. 1 di.
No. 2 670 "
No. 3
No. 4
Flow Control Performance Standard (vn/S2v477 dAt
2009 Surface Water Design Manual 1/9/2009
1
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL /g
Live� Storage Volume / 7 j,,OO c; Depth /0 Volume Factor of Safety
IN4DM
Number of Acres Served /. 21
Number of Lots
Dam Safety Regulations (Washington State Department of Ecology)
Reservoir Volume above natural grade
Depth of Reservoir above natural grade
Facility Summary Sheet Sketch
All detention, infiltration and water quality facilities must include a detailed sketch.
(11"x17" reduced size plan sheets may be used)
FOI.LowiAJ‘ E
2009 Surface Water Design Manual 1/9/2009
2
4:1
88.0'
SO IN I
RD INp iVENTILATION )
4
-169.10
b
" ` 1 1r _A
PRECAST
,..._n,---
_SUMP -- J-159.10
�vr����i—158.61
tii
4'�J 158.11
I SD OUT PIAN ze SD iN 1
A1
'177:56_ .EXISiINC GRADE _i FINISHED GRADE _ . RI=176.54 � �..
.170;60. _ _ . . . _ . . _ . . .
ELEV.189.1
HANDHOLDS ANDS`�` . ... '
STEPS PER K.C.R.S. � -IE:IN 166.02
O .NO.2-006 SEE CONTROL SIRUCIURE • . 2 ti 0 m
DE1NL THIS SHEET 0�n e •
e 15861
• -IE OUT 159• .10 • .801T011 OF NEE(BAC(GROUND) • 158.11
. .''''''-PRECAST •
• • • . .
.. .. SUMP _ . _ _ _ _ _
PROFILE
SOUTH DETENTION VAULT
SCALE 1"=20'
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL 7/3
Water Quality:
Type/Number of water quality facilitiesBMPs:
biofiltration swale sand filter(basic or large)
(regular/wet/or continuous inflow) sand filter, linear(basic or
large)
combined detention/wetpond sand filter vault(basic or
large)
(wetpond portion basic or large) sand bed depth (inches)
combined detention/wetvault stormwater wetland
filter strip / storm filter
)flow dispersion wetpond`(basicor larges
farm management plan wetvault
landscape management plan Is facility Lined?
oil/water separator If so, what marker is used
above
(baffle or coalescing plate)
Liner?
catch basin inserts:
Manufacturer
pre-settling pond
pre-settling structure:
Manufacturer
high flow bypass structure (e.g., flow-splitter catch basin)
source controls
Design Information //-
Water Quality design flow _ b'. Q Z C/s. , _ _ r_—
Water Quality treated volume (sandfilter)
Water Quality storage volume (wetpool)
ax-4/2 ail 'S•
Facility Summary Sheet Sketch / /7W— s/f7j
2009 Surface Water Design Manual 1/9/2009
3
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL `3/e
All detention, infiltration and water quality facilities must include a detailed sketch.
(11"x17" reduced size plan sheets may be used)
2009 Surface Water Design Manual 1/9/2009
4