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' Technical Information Report
(TIR)
for
Saddlebrook
13426 156`h Avenue SE, Renton,Washington
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DRS Project No. 12040
City of Renton File No. LUA 12-077
OwnedApplicant
PNW Holdings LLC
9675 SE 36th Street, Suite 105
Mercer Island, Washington 98040
Report Prepared by
I �� �
D. R. STRONG Consulting Engineers, Inc.
10604 N.E. 38th Place, Suite 232
Kirkland WA 98033
(425) 827-3063
Report Issue Date
November 14, 2012
Revised Date
January 28, 2013
OO 2012 D.R. STRONG Consulting Engineers Inc.
1
TECHNICAL INFORMATION REPORT
Saddlebrook
TABLE OF CONTENTS
SECTION1.....................................................................................................................................................1
' PROJECT OVERVIEW:............................................................................................................................1
PREDEVELOPED SITE CONDITIONS:....................................................................................................1
DEVELOPED SITE CONDITIONS:...........................................................................................................1
NATURAL DRAINAGE SYSTEM FUNCTIONS: .......................................................................................2
FlGURE9. TIR WORKSHEET............................................................................................................3
FlGURE 2. VICINITY MAP...............................:..................................................................................6
I
FlGURE 3. DRAINAGE BASINS, SUBBASINS, AND SlTE CHARACTERISTICS.............................7
FIGURE4. SOlLS................................................................................................................................8
SECTION11..................................................................................................................................................10
CONDITIONS AND REQUIREMENTS SUMMARY................................................................................10
SECTION111.................................................................................................................................................12
OFF-SITE ANALYSIS..............................................................................................................................12
SECTIONIV................................................................................................................................................13
FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND DESIGN ..................................13
EXISTING SITE HYDROLOGY(PARTA)...............................:................................................................13
FIGURE 5. PREDEVELOPMENT AREA MAP..................................................................................14
DEVELOPED SITE HYDROLOGY(PART B)..........................................................................................15
BYPASS AREA HYDROLOGY................................................................................................................17
FIGURE 6. POST DEVELOPMENT AREA MAP...............................................................................19
PERFORMANCE STANDARDS(PART C).............................................................................................20
FLOW CONTROL SYSTEM(PART D)...................................................................................................20
FLOW CONTROL BMP SELECTION .....................................................................................................20
FLOW CONTROL SYSTEM....................................................................................................................21
WATER QUALITY TREATMENT(PART E)............................................................................................29
FlGURE 7. DETENTION FAClUTY DETAILS AND BAYFlLTER SIZING........................................30
SECTIONV.................................................................................................................................................31
CONVEYANCE SYSTEM ANALYSIS AND DESIGN..............................................................................31
DEVELOPED 15-MINUTE TIME SERIES...............................................................................................31
BACKWATERANALYSIS.......................................................................................................................33
BACKWATERANALYSIS MAP..............................................................................................................35
BACKWATER ANALYSIS RESULTS......................................................................................................36
SECTIONVI................................................................................................................................................39
SPECIAL REPORTS AND STUDIES......................................................................................................39
SECTIONVII...............................................................................................................................................40
OTHER PERMITS,VARIANCES AND ADJUSTMENTS........................................................................40
SECTIONVIII ..............................................................................................................................................41
ESC PLAN ANALYSIS AND DESIGN(PART A) .....................................................................................41
SWPPS PLAN DESIGN (PART B)..........................................................................................................41
SECTIONIX................................................................................................................................................43
BOND QUANTITIES, FACILITY SUMMARIES,AND DECLARATION OF COVENANT........................43
STORMWATER FACILITY SUMMARY SHEET.....................................................................................44
SECTIONX.................................................................................................................................................46
O 2012 D. R.STRONG Consulting Engineers Inc. Saddlebrook
' Technical Information Report Renton,Washington
OPERATIONS AND MAINTENANCE MANUAL .....................................................................................46
APPENDICES..............................................................................................................................................47
APPENDIX«A„ LEGALDESCRIPTION..................................................................................................48
APPENDIX"B� BOND QUANTITY WORKSHEET.................................................................................49
APPENDIX"C" OPERATIONSAND MAINTENACE MANUAL..............................................................50
APPENDIX"D" CSWPPP.......................................................................................................................51
O 2012 D. R.STRONG Consulting Engineers Inc. Saddiebrook
' Technical Information Report Renton,Washington
SECTION I
PROJECT OVERVIEW:
The Site is located at 13426 156th Avenue SE in Renton, Washington, also known as
King County Tax Parcel Numbers 366450-0260 and 366450-0261. The Project is the
subdivision of these two existing parcels zoned R4 (4.36 ac. total) into 14 single-familty
residential lots, per the City of Renton's (City) subdivision process. Although the Site
drains in two directions, an adjustment has been granted to combine the drainage into
one detention pond designed to Level Three Flow Control Standards (Adjustment 2012-
03). The Project will meet the drainage requirements of the 2009 King County SurFace
Water Design Manual (Manual), as adopted by the City.
PREDEVELOPED SITE CONDITIONS:
Total existing Site area is approximately 189,797 s.f. (4.36 ac). Total proposed Project
area is 200,420 s.f. (4.60 ac) which includes 10,623 s.f. (0.24 ac) for the right-of-way
frontage improvements on 156�h and 158th. The Parcels are currently developed with
two single-family residences, out buildings and a gravel driveway. The remainder of the
Site is lawn, landscaping, scattered trees and horse pasture.
The 4.36 acre parcel is situated atop a ridge and discharges runoff into two subbasins.
TDA West is approximately 1.78 acres and discharges to 156th Avenue SE while TDA
East is comprised of the remaining 2.58 acres and discharges to 158th Avenue SE. The
discharge elevation of TDA West is approximately six feet lower than that of TDA East.
The two flowpaths converge at a point approximately 3,000 feet downstream of TDA
West and 4,900 feet downstream of TDA East at the corner of 156th Avenue SE and SE
144th Street.
For the purpose of hydrologic calculations, the entire Site is modeled as till forest.
DEVELOPED SITE CONDITIONS:
The applicant has gained approval to subdivide 4.36 acres into 14 single-family
residential lots (Project), with lot sizes ranging from approximately 9,400 to 11,734 s.f.
All existing improvements will be demolished or removed during plat construction. The
proposed impervious surface area will include a new subdivision road right-of-way with
26 feet of pavement, vertical curb, gutter, 8-foot planter and a 5-foot sidewalk (53-foot
right of way) as well as offsite half-street improvements along 156th Avenue SE and
158th Aveneu SE. The proposed right-of-way improvements total approximately 39,130
s.f. The 14 single-family residences and their driveways combined will create
approximately 61,230 s.f. of impervious area (reduced from maximum allowable, see
next paragraph for details). Post-de�eloped impervious areas including rights-of-way,
sidewalks, roofs, driveways and site frontage improvements total approximately
110,642 s.f. (includes Bypass area). The remainder of the Project will be modeled as
till grass with the total being approximately 89,733 s.f. (See Section IV)
Per the 2009 King County Surface Water Design Manual (Manual), Appendix C, each
lot within a new subdivision is required to mitigate for impervious surface area equal to
10% of the lot area. Per Figure C.1.3.A, Flow Control BMP Flowchart, the Project will
O 2012 D.R.STRONG Consulting Engineers Inc. 1 Saddlebrook
' Technical Information Report Renton,Washington
utilize Basic Dispersion with the use of splash blocks. Two splash blocks mitigating a �
total of 1,400 s.f. of impervious area, will be installed with each residence. This shall
mitigate for 11.93% to 14.89% of impervious area for each lot, thus accommodating
flow control BMP requirements. Additionally, use of Basic Dispersion allows for a 50%
flow control BMP sizing credit which was used in detention facility calculations. See ;
table below for lot area, percent impervious mitigated per lot, impervious area used for !,
detention calculations, and actual allowable impervious area per lot. I
ROOF AREA ROUTEDTO PERCENT IMPERVIOUS 45%Of LOT AREA(S.F.) ACTUALALLOWABLE �
LOT N0. LOTAREA(S.F.) SPLASH BLOCK�S.F.) MITIGATED AREA FOR DEf.CALCS (LIMITED IMPERVIOUS AREA(S.F.)
1 10690 1400 13.10 4811 5511
2 9400 1400 14.89 4230 4930
3 9400 1400 14.89 4230 4930
4 9400 1400 14.89 4230 4930
5 9400 1400 14.89 4230 4930
6 9400 1400 14.89 4230 4930
7 9400 1400 14.89 4230 4930
8 11734 1400 11.93 5280 5980
9 9445 1400 14.82 4250 4950
10 9437 1400 14.84 4247 4947
11 9429 1400 14.85 4243 4943
12 9421 1400 14.86 4239 4939
13 9413 1400 14.87 4236 4936
14 10704 1400 13.08 4817 5517
Two drainage adjustments have been granted to this subdivision (Saddlebrook Plat
Adjustment 2012-03 and Saddlebrook Plat — ADS BayFilter Adjustment 2012-04).
Saddlebrook Plat Adjustment 2012-03 allows the two existing TDAs onsite to combine
runoff into one single drainage facilty. As a condition of this adjustment, the Project
drainage facility is required to adhere to Level 3 Flow Control Criteria. The Project is
required to provide Basic Water Quality treatment and Level 3 Flow Control, per the
2009 KCSWDM (Manual). All surFace water runoff from impervious surFaces will be '
collected and conveyed to a storm detention pond located in Tract "A. From there, the
water runoff will be conveyed through a BayFilter vault before entering the existing
conveyance system within 156th Avenue SE. The BayFilter adjustment allows the use
of a BayFilter for this project to meet water quality treatment standards.
NATURAL DRAINAGE SYSTEM FUNCTIONS:
A review of the SCS soils map for the area (see Figure 4, Soils) indicates Alderwood
gravelly sandy loam with 6 to 15 percent slopes (AgC). Per the Manual, this soil type is
classified as "Till" material. The SCS Soil series descriptions follow Figure 4.
In evaluating the upstream area, we reviewed the existing offsite analysis and King �
County IMAP aerial topography and imagery and conducted field reconnaissance and
have concluded that upstream tributary area for the Site is negligible.
� 2 12 D.R. TR N n I i En in r I�
� 0 S O G Co su t ng g ee s Inc. 2 Saddlebrook
' Technical Information Report Renton,Washington
FIGURE 1. TIR WORKSHEET
King County Department of Development and Environmental Services
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET �,
Part 1 PROJECT OWNER AND Part 2 PROJECT LOCATION AND I
PROJECT ENGINEER DESCRIPTION
Project Owner: Project Name: I
PNW Holdings LLC Saddlebrook �',
AddressJPhone: Location: '
9675 SE 36t" Street, Suite 105 Township: 23 North
Mercer Island, Washington 98040 Range: 05 East
(206) 588-1147 Section: 14
Project Engineer:
Maher A. Joudi, P.E.
D. R. STRONG Consulting Engineers
Inc.
Address/Phone:
10604 NE 38th Place, Suite 232
Kirkland WA 98033
(425) 827-3063
Part 3 TYPE OF PERMIT Part 4 OTHER REVIEWS AND PERMITS
APPLICATION
� Subdivision ❑ DFW HPA ❑ Shoreline
❑ Short Subdivision Management
� Clearing and Grading ❑ COE 404 � Rockery
❑ Commercial ❑ DOE Dam Safety ❑ Structural Vault
❑ Other: ❑ FEMA Floodplain ❑ Other:
❑ COE Wetlands
Part 5 SITE COMMUNITY AND DRAINAGE BASIN
Community:
Newcastle
Drainage Basin
Lower Cedar River
O 2012 D.R.STRONG Consulting Engineers Inc. 3 Saddlebrook
Technical Information Report Renton,Washington
Part 6 SITE CHARACTERISTICS
❑River: ❑ Floodplain
❑ Wetlands
❑ Stream: ❑ Seeps/Springs
❑ Critical Stream Reach ❑ High Groundwater Table ,
❑ Depressions/Swales ❑ Groundwater Recharge ��
❑ Lake: ❑ Other: I,
❑ Stee Slo es ��,
Part 7 SOILS '
Soil Type: Slopes: Erosion Potential: Erosive Velocities:
Alderwood 6-15% Moderate Slow to Medium
(AgC)
� Additional Sheets Attached: SCS Map and Soil Description, Figure 4
Part 8 DEVELOPMENT LIMITATIONS
REFERENCE LIMITATION/SITE CONSTRAINT
� Level 1 Downstream Analysis None
� Geotechnical Engineering Study
❑ Environmentally Sensitive Areas
❑ Le�el 2 Off-Site Stormwater Analysis
� Level I Traffic Impact Analysis
❑ Structural Report
❑ Additional Sheets Attached
Part 9 ESC REQUIREMENTS
MINIMUM ESC REQUIREMENTS MINIMUM ESC REQUIREMENTS
DURING CONSTRUCTION AFTER CONSTRUCTION
� Sedimentation Facilities � Stabilize Exposed Surface
� Stabilized Construction � Remove and Restore Temporary ESC
Entrance Facilities
� Perimeter Runoff Control � Clean and Remove All Silt and Debris
� Clearing and Grading � Ensure Operation of Permanent Facilities
Restrictions ❑ Flag Limits of SAO and open space
� Cover Practices preservation areas
� Construction Sequence ❑ Other
❑ Other '
O 2012 D. R.STRONG Consulting Engineers Inc. 4 Saddlebrook
� Technical Information Report Renton,Washington
Part 10 SURFACE WATER SYSTEM
❑ Grass Lined ❑ Tank ❑ Infiltration Method of Analysis:
Channel ❑ Vault ❑ Depression KCRTS
� Pipe System ❑ Energy Dissipater ❑ Flow Dispersal Compensation/Mitigatio
❑ Open Channel ❑ Wetland ❑ Waiver n of Eliminated Site
� Dry Pond ❑ Stream ❑ Regional Storage
❑ Wet Pond Detention NlA
Brief Description of System Operation: Runoff from impervious surfaces will be collected
and conveyed to the detention pond in Tract A. From there it will be discharged to the
existing conveyance system within 156t" Avenue SE.
Facility Related Site Limitations:
Reference Facility Limitation
.
Part 11 STRUCTURAL ANALYSIS Part 12 EASEMENTS/TRACTS
❑ Cast in Place Vault � Drainage Easement
❑ Retaining Wall ❑ Access Easement
❑ Rockery > 4' High ❑ Native Growth Protection Easement
❑ Structural on Steep Slope � Tracts
❑ Other: ❑ Other:
Part 13 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 attachments. To the best
of my knowled the information provided here is accurate.
. �/�� �%
Si ned/Date
�
O 2012 D.R.STRONG Consulting Engineers Inc. 5 Saddlebrook
' Technical Information Report Renton,Washington
FIGURE 2. VICINITY MAP
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The information included on this map has been compiled by King County staff from a variety of sources and is subject to change
without notice. King County makes no representations or warranties,express or implied,as to accuracy,completeness,timeliness,
or rights to the use of such information.King County shall not be liable for any general,special,indirect, incidental,or consequential
damages including,but not limited to, lost revenues or lost profits resulting from the use or misuse of the information contained on
this map.Any sale of this map or information on this map is prohibited except by written permission of King County.
O 2012 D. R. STRONG Consulting Engineers Inc. 6 Saddlebrook
, Technical Information Report Renton,Washington
FIGURE 3. DRAINAGE BASINS, SUBBASINS, AND SITE CHARACTERISTICS
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O 2012 D. R.STRONG Consulting Engineers Inc. 7 Saddlebrook
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N O RT H DRAF7E0 BY.• �,
LEGEND DES/GNED BY.• dAJ
PRO„�CT ENGlN£ER: YAJ
S/TE BOUNDARY GRAPHIC SCALE DA7F.• 01.2813
� � � BAS/N BOUNDARY 0 3 60 120
PRo„�cr No.: tzo�o
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1 INCH =60 FT. R:�Zo�2�o�,�04��3����w�,9s\Plcts\PP\Report Fl�i.res\Ol-3FIG312�4vCN� 1/28/ZCi3 1:57:35 ?b1 PST f7GURE 3
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FIGURE 4. SOILS
s«��+ay—xn9 ca�my,vea,was���,y�o,�
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Frequency of flooding: None
Frequency of ponding:None
Available watercapacity:Very low(about 2.5 inches)
Interpretive groups
Land capability(nonirrigafed):4s
Typical profile
0 fo 92 inches:Graveily sandy loam
12 to 27 inches:Very graveliy sandy loam
27 to 60 inches:Very gravelly sandy loam
Minor Components
Norma
Percent of map unit:1 percent
Landform:Depressions I
Bellingham I
Percent of map unit:1 percent �,
Landform:Depressions ',
Seattle '
Percent of map unif:1 percent
Landform:Depressions
Tukwila
Percent of map unit:1 percent
Landform:Depressions �!,
Shalcar �
Percenf ofmap unit: 1 percent I
Landform:Depressions �
�2012 D. R.STRONG Consulting Engineers Inc. 9 Saddlebrook
' Technical Information Report Renton,Washington
SECTION II
CONDITIONS AND REQUIREMENTS SUMMARY
The Project must comply with the following Core and Speciai Requirements:
• C.R. #1 — Discharge at the Natural Location: An adjustment has been granted to
allow for combination of runoff from two basins into one; Adjustment 2012-03.
• C.R. #2 — Offsite Analysis: An Offsite Analysis is included in Section III. The
Analysis describes the Site's runoff patterns in detail.
• C.R. #3 — Flow Control: The Project is required to adhere to Level 3 Flow Control
Standards per Adjustment 2012-03. One detention pond will provide flow control as
required for both drainage basins. The Project is required to "match developed
discharge durations to predeveloped durations for the range of predeveloped
discharge rates from 50% of the two-year peak flow up to the full 50-year peak
flow." (KCSWDM, Sec. 1.2) Also match developed peak discharge rates to
predeveloped peak discharge rates for the 2, 10 and 100 year return periods.
Furthermore, the Project must meet the Flow Control BMP requirements as
specified in Section 1.2.3.3 of the Manual. The Project will utilize basic dispersion to
meet this requirement.
• C.R. #4 — Conveyance System: New pipe systems and ditches/channels are
required to be designed with sufficient capacity to convey and contain (at minimum)
the 25-year peak flow, assuming developed conditions for onsite tributary areas and
existing conditions for any offsite tributary areas. Pipe system structures and
ditches/channels may overtop for runoff events that exceed the 25-year design
capacity, provided the overtlow from a 100-year runoff event does not create or
aggravate a "severe flooding problem" or "severe erosion problem" as defined in
C.R. #2. Any overFlow occurring onsite for runoff events up to and including the
100-year event must discharge at the natural location for the project site. In
residential subdivisions, such overflow must be contained within an onsite drainage
easement, tract, covenant or public right-of-way. The proposed conveyance system
was analyzed using the KCBW program, and is capable of conveying the 100-year
peak storm without overtopping any structures or channels (see Section V).
• C.R. #5 — Erosion and Sediment Control: The Project provides the nine minimum
ESC measures.
• C.R. #6 — Maintenance and Operations: Maintenance of the proposed storm
drainage facility will be the responsibility of the City. An Operation and Maintenance
Manual is included in Section X.
• C.R. #7 — Financial Guarantees: Prior to commencing construction, the Applicant
must post a drainage facilities restoration and site stabilization financial guarantee.
For any constructed or modified drainage facilities to be maintained and operated by
the City, the Applicant must: 1) Post a drainage defect and maintenance financial
guarantee for a period of two years, and 2) Maintain the drainage facilities during the
O 2012 D.R.STRONG Consulting Engineers Inc. 10 Saddlebrook
' Technical Information Report Renton,Washington
two-year period following posting of the drainage defect and maintenance financial
guarantee.
• C.R. #8 - The Project is located in the Basic Water Quality Treatment area.
Stormwater runoff will be collected in the detention pond and then con�eyed through
a BayFilter vault which will accommodate water quality requirements.
• S.R. #1 — Other Adopted Area-Specific Requirements: Not applicable for this
Project.
• S.R. #2 — Floodplain/Floodway Delineation: Not applicable for this Project.
• S.R. #3 — Flood Protection Facilities: Not applicable for this Project.
• S.R. #4 — Source Control: Not applicable for this Project.
il
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O 2012 D. R.STRONG Consulting Engineers Inc. 11 Saddlebrook
' Technical Information Report Renton,Washington
SECTION III
OFF-SITE ANALYSIS
A Level One Downstream Analysis was prepared by DR Strong Consulting Engineers.
A copy has been included in this Section.
O 2012 D. R.STRONG Consulting Engineers Inc. 12 Saddlebrook
� Technical Information Report Renton,Washington
LEVEL ONE DOWNSTREAM ANALYSIS
for
SADDLEBROOK
Preliminary Plat
13426 156`h Avenue SE, Renton,Washington
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DRS Project No. 12040
Renton File No. LUA 12-077
O�vnedApplicant
PNW Holdings LLC i
9675 SE 36th Street, Suite 105 I
Mercer Island, WA 98040 I,
Report Prepared by . �
' � � 'I
� �
D. R. STRONG Consulting Engineers, Inc. �
10604 N.E. 38th Place, Suite 232
Kirkland WA 98033 I
(425) 827-3063 '
Report Issue Date
September 4, 2012
02012 D. R.STRONG Consulting Engineers Inc.
LEVEL ONE DOWNSTREAM ANALYSIS
SADDLEBROOK
TABLE OF CONTENTS
TASK 1 DEFINE AND MAP THE STUDY AREA .........................................................1
TASK 2 RESOURCE REVIEW.....................................................................................5
TASK 3 FIELD INSPECTION .....................................................................................15
Upstream Tributary Area............................................................................................15
General Onsite and Offsite Drainage Description ......................................................15
TASK 4 DRAINAGE SYSTEM DESCRIPTION AND PROBLEM DESCRIPTIONS...16
Drainage System Description.....................................................................................16
Downstream Path TDA East...................................................................................16
Downstream Path TDA West..................................................................................17
TASK 5 MITIGATION OF EXISTING OR POTENTIAL PROBLEMS .........................24
List of Figures
Figure1 Vicinity Map .......................................................................................................2
Figure2 Site Map ............................................................................................................3
Figure 3 King County iMap Topography ..........................................................................4
Figure 4 Streams and 100-Year Floodplains and Floodway............................................6
Figure 5 King County iMap Wetlands...............................................................................7
Figure 6 King County iMap Erosion Hazard Areas ..........................................................8
Figure 7 King County iMap Landslide Hazard Areas .......................................................9
Figure 8 King County iMap Seismic Hazard Areas........................................................10
Figure 9 FEMA — Flood Insurance Rate Map.................................................................11
Figure 10 King County iMap Drainage Complaints........................................................12
Figure 11 USDA King County Soils Survey Map ...........................................................13
Figure 12 Downstream Map...........................................................................................19
Figure 13 Downstream Table.........................................................................................20
02012 D. R.STRONG Consulting Engineers Inc. Page i of i
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
TASK 1 DEFINE AND MAP THE STUDY AREA I
- This Offsite Analysis was prepared in accordance with Core Requirement #2, Section �II
1.2.2 of the 2009 King County Surface Water Design Manual (Manual). The Site is '�
located at 13426 156th Avenue SE in Renton, Washington. '�
See Figure 1, Figure 2, and Figure 3 for maps of the study area.
02012 D. R.STRONG Consulting Engineers Inc. Page 1
, Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
FIGURE 1
VICINITY MAP
SITE
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The information included on this map has been compiled by King County staff from a variety of sources and is subject to change
without notice. King County makes no representations or warranties, express or implied, as to accuracy,completeness,timeliness,
or rights to the use of such information.King County shall not be liable for any general,special,indirect, incidental,or consequential
damages including, but not limited to, lost revenues or lost profits resulting from the use or misuse of the information contained on
this map.Any sale of this map or information on this map is prohibited except by written permission of King County.
02012 D. R.STRONG Consulting Engineers Inc. Page 2
, Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
FIGURE 2
SITE MAP
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02012 D. R.STRONG Consulting Engineers Inc. Page 3
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
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02012 D. R.STRONG Consulting Engineers Inc. Page 4
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
TASK 2 RESOURCE REVIEW
• Adopted Basin Plans: May Creek Basin Action Plan was adopted in April 2001.
• Floodplain/Floodway (FEMA) Map: No floodplains exist on site, See Figure 9. �
• Other Offsite Analysis Reports: None available at this time. I
• Sensitive Areas Folio Maps: See Figures 4-8 for documentation of the distance �
downstream from the proposed project to the nearest critical areas. Included, are ;
sections of the King County Sensitive Areas Folio which indicate fhe following:
• Figure 4 Streams and 100-Year Floodplains and Floodway: There is a
C/ass 2 Stream within one mile of the Site along the downstream path.
• Figure 5 Wetlands: There are no mapped Wetlands within one mile of the
Site along the downstream path.
• Figure 6 Erosion Hazard: There are mapped Erosion Hazard Areas
within one mile of the Site along the downsfream path.
• Figure 7 Landslide Hazard: There are mapped Landslide Hazard Areas
within one mile of the Site along the downstream path.
• Figure 8 Seismic Hazard: There are no mapped Seismic Hazard Areas
within one mile of the Site along the downstream path.
• DNRP Drainage Complaints and Studies: As shown in Figure ?O,fhere are no
drainage complaints within 1 mile of the Site along the downstream path.
• Road Drainage Problems: None noted.
• USDA King County Soils Survey: See Figure 91.
• Wetlands Inventory: Vol. 3South (1990) — The wetland inventory revealed no
additional wetlands wifhin the downstream path.
• Migrating River Studies: None are applicable to the sife.
• Washington State Department of Ecology's latest published Clean Water Act Section
303d list of polluted waters: None listed along the downstream path.
• King County Designated Water Quality Problems: None at this time.
• Adopted Stormwater Compliance Plans: None applicable to this site.
• Basin Reconnaissance Summary Reports: None available at this time
��2012 D. R.STRONG Consulting Engineers Inc. Page 5
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
FIGURE 4
STREAMS AND 100-YEAR FLOODPLAINS AND FLOODWAY
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�,z SF _� . . ---� --
o l�rr.
Legend
� Highiighted Feature 5A0 Stream
� � County 8oundary � ctast
x AburttainPeaks �/ C�s2Pmmn01
Highways A/ Ctaa2sa4�wnid
I'
5treats �f Ctrm s
Eiqn,� ... u,�r�+a
�� O Lakes and larpe Rivers
�� f,f Streams
Parcels � 700 Year Floodplain
�2012 D.R.STRONG Consulting Engineers Inc. Page 6
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
i
� FIGURE 5
- KING COUNTY IMAP WETLANDS
, r
Z: - NE-0iH 5T t�'I
H£'9RUPi � NE� - -��- - i;. -. _ L� .� J
. pp� = NE3R�jCT - �. - � � � '. .�_ ---_._5�128THST�
.. M£9ftOST w �; y —._ ._,_... . �:-
z $ � y�;'a,�.� �1
2 r aF � � y � �- � .;.. �, ,
> �u� � f� `� �1 ,
s. ; �CT `J` a � � r�1 tn .-- � y .� 4
Z f�
� ! �'�. � ���� ;S G
���n Rento.nJ � �,��=�,,�b� � m �
' NE 1S1'Ci' W P, !f 13�iDCT �, - � '� �
... . NEISTST ��.I � �'�' � M£1STP4. y ;I �
�. ���i oi e'�' NEt5T5? � � .Q
� 4
����� � , ��ST "� � (� �S£i9ITFi57_--_-..�.�-: i�
SE 2N4 �i J SE�ND CT :. � SE 7 T�b �, .
1 � ���� �
S+ 7,'1� $T
SITE � � �"�"�T
,l� ! � ,; � �
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I
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se�� [edar�River__. �,' � � � � x'.; ' f'
�r����ARE vA�f ; ct' ��SRQ �t t_�,._€ , �
Y�� � �_ � t� � -� -
¢ = 1� h �, '�-."�� t_
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� � � _ !r d� � �` ,���� ��^
...� .� �i E f`7 "�` ��'•Vr,F '^ •-
�., :?�.
RC�2o0eKingCoun�y ��SS�lp� ����Hsr a �asert�__�----.�,�.
Le ge nd
� Highlighted Featura �e�h
'i� C011nty$oundary Lod
x Mountain Peaks Parcels
Highways n Lakes and Large ftivers
. Streets �� Sireams
i�qhw�r x<;. SAOYVeUand
" (C ont)
02012 D. R.STRONG Consulting Engineers Inc. Page 7
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
FIGURE 6
KING COUNTY IMAP EROSION HAZARD AREAS
,
_ :_ _NE 4TH ST , �
HE9RDPl. � NE3Rpp� . . i NE]ROCT . . �g; ��.: . � _ SE.128TNSi.
HE3RDST � O '� pQ a I D _ _.___.__.._.__- �
. •! � '. '{ O t �i.' I 1�(Q1'' i� � �.
le' 4 f�l) � q � •�/ 'l' �
I ;i ��r `� � � �i � ._ � �y F� �'
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� s�, ,sr=«,,�nm,�. m
►+F�srcTl z Q„ �i�ocr '� � ��' �1
• HEtSTST �..i � ti� �ISTPL > �
�� � �i < �, NE1STg7 � �! �{
j y O
SE blD S7; � SE�U ST ���c � (�{ �SE 11(TH�__ _ _ �
SE�10 �� � � SE?NOCT �� !� �� y II
1 SE1JiOPL �
�� SITE � i! � � � s�rxrNSY
�� _ H ST Ft �3RO PL SE t]7TH PL j;
.= I� �1�8TM R �7f I i �!.
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1 Ii
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r d � ^ F' �
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o � � � � y `� �� �' [E.14.7TH ST-- � i�
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o �, _1� . � -.; � =J_ _��-,�„ ,
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SC�200L Ning Ca�oty S��557Nf+� ���H gr 0 145fi}Yr�r.�-
FIGURE 7
KING COUNTY �MAP LANDSLIDE HAZARD AREAS
� . . . -- - NE 4TH Sfi _ ��
- : �
NE32DR '.' NE3Rp� . . z NE]ROCT � .. . . - ; �1 1 .� - SE_128TH ST �
KE�DSi = � ;� kV d y �i'-------- ----_-- �.
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� � r.-. j:p,� �y
C � N � RI S� 1, � y '6s 7
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� "��'°�` Rento_n�! � �
ta ;�
, . �, �, �_,.�.,,� ,� !
HE fST CT'�� ui � �13.ZRQ CT � . � i
� z
• NEISTST I W� �y� kE1$TPL D '.; �
I ,; v<i �, HEtSTST � .., q �I
SEbfDSTI � 5£TNDST � � � (g iSE1J(TM81'_---.-'.�j i
�' '' SE$10CT 'i � �� 1 > " I
��� � SE 1j10 R �.:
SITE � I' � »arHsr sEr�tNs7
se�'�sr a SE�tOR � s�� �i
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�1
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.�
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i.� � -• �'utk�q � �«rHv� _ . r— — sE�.sre,sr =- — - _:..,�
dTH S
//SE��g1+!s��-A� ,//l�! ,�� � f�;'� � e' ��
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/�~�• � •� C �
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�.. ..f s---��K``(`%,//}'//l/ ��'�.� SEraeik� � � � " � t
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������ � �l'��'f,���; :j" /� j�l��l sE�.sni sT � �
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�� �� *� ^'••�-�!�,
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_,- 4{aFteva i d''` _ fis,q� �•�.�!�f...%;�: L�f'�,�;/�//i�//.
�/�j1,, 4evRo � �;� �� rt � --� ,
� `�f�� o � _��� N �-,� � �r\-\�` `rti-
//� %' � o ` f, '��� � f}�� --- _-- —�
,7/4� ' ` --�`�y. ; � ��`z�
_ ''%'.- �/� /���/���5� � ' i�.'-- �'•�� ti �7`"''".i''��
(C�2CpLKinqCaunly r � /� % � //E� �Y-Ipl ��H.ST•'-'^;-0 1456Rr��.-=--
__�.,`
Lege nd
� Highlighted Feature ' �Q;,�
i_� County Boundary �ad
x hbunWin Peaks Parcels
Highways I� l.akes and Large Rivers
L_I
5treeta f� Streams
��yh,,,�,y � SAO Landslide
(cont}
G2012 D. R.STRONG Consulting Engineers Inc. Page 9
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
FIGURE 8
KING COUNTY IMAP SEISMIC HAZARD AREAS
,
__ - �_NEdTHST -_ �� �
H£3RDPL i; NE�p� � NE7illCT ''-- ---- -- � ---- �- -���--� ��� "._:-._.SE128TMST .;----_-
t1E]ROST z ii . � � I� y . _. (-- - —�---
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!R � ~-.f�R > �
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,� � �, ,�
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'� NE IS?ST i� _ �� HE 15T ST N£15T Pt y � �
♦ � I <
� �13RH �
� SE7/iD � � SE4NO5T �� _ � i._.._� �—�---�-
� �� 'i
J�� 1 '' SE2MJCT � —p ,,
� s�zvn at � �3en sr sE��H sr
I; � ��
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i� s��ao a ss t3m+a I I
s�TH sr � f
� W I SE 1]dTH PL SE�TH Pl �f�TH ST
/ v� � w
-- �' � SE 1�3TH R SE 5TH PL � VWWi' �
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�p ^ ' �
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a < dx �_ � _� — ---__5�`e21� � SE �� � ') �
Y � t 4 � ~ N---�` � SE tt�2O 5T � � }\
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d � � tN � �sF
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� TQV -,-�F\::� C�'����� ' ...
� f� --�fAFt� \ �t���\\�����_•�-ti�'�'o�. � �\'�{•. , ��r-• e�. - , -:'�'��
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� �.��� '� �.,`` \ .� .a .i� ., 7_ � ��
(CIZODEK¢�qCounty \�' � E7$S?yfPl�\\����H.ST�•.•�;�.Q 1!�56�Y�c'�� '` - ��
LB�e Ilil
� Highlighted Feature Art«vK
ii� County Bou�dary ��
X Mountain Feaks Parcels
Highways �I Lakes and Large}2ivers
�I
Streets f:l SVeams
��reh�, � SAd Seismic
(cont)
02012 D.R.STRONG Consulting Engineers Inc. Page 10
Levei One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
FIGURE 9
FEMA - FLOOD INSURANCE RATE MAP
�.
.;��:,, ,,.,;_. ::<«-
Y
Q
ZONE X t4
p.p:�,�k:Si 736TN SiRE[l _
1?d'r� ?1.45
LEGEND
� ,�ca�t r�000 �t�v�nu ,�kc-�s mun�>�nu
61�7tN;-Yb\R FI.001)
ZONE A �.�h�v 1vd rk��.ni.aa�4��+:ne�..:.
ZONE AE tk.�.rl.�.,.1 ii��-.n.r..�i�.m.��d.
ZONE AH �4...t<L��I:+.�1��� 1 khY�u.�::1'..
�( �x.tnAi: Ixw d„�al �..•..Min.
iL�e��mi�n*i.
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i6n. J,�Nr'; . ;ih.
�kn� n�d fix .uC�,Ji.�I�L1xi I���,nl:nv,
,.i,�r.,,�e..,avm�.�,,,i
ZONE A99 I•• t.� ;,��i.u•I fu,m tt'A�year f•..I In
;i.l.+.d IM�e: p�Waat:ea �
�...,,r�viF�rc M1r�,Iw't'�^.dti../�<��nM i'ilkrl.
ZONE V t:�,..�.d iUKw� e-;h ,iy�r��� n�r•��1 ;..
..i�.,�...���Ir.nc i��.rl�•L�..a„re ifrmr.r.�..�.1.
ZONE VE I.�,.i��.�l dirwl ..dh �d..ein h.».d �u.
� .atiun.: 6a..a. Ihaxl �L.,Ni�rs ii.r��r.v�..,l,
FI.OpU1V:1Y AFk�S IN ZOt�E AE
� OT}tER Fl.00)D ARfAS
ZONe% ��.�,..:z(N�-}rvr tGud:.xr,�.:f t�:�'�r
�i:..�i .,.ah a cnq,r drf,�. �i :
i :�K. � „�iA d,ir:.M� .i . .. �I,.�.n
i v��,: ,�:i��� ��i ��.,,��.d-i��,
i.��.,1i.:,m ice�:,�.r r..�.:i.
� OT}IER;1RfA5 >`An.^, ,
ZONf X :n,i i: I.v..:;iii� i��,Fy...,r
.��.I��L.n.
ZONE D . .n ,.h��!� �Svd hai��c. ...
u�,1_.a..n.n:�<t
02012 D. R.STRONG Consulting Engineers Inc. Page 11
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
FIGURE 10
KING COUNTY IMAP DRAINAGE COMPLAINTS
_ :__ _. __ NE4fHST .. _ _ ,�� ' , ,,
_ __ �s�
Nf 3RD Ft i NE� � -� .. ._. ..... --.._._ � � .;;
O ; ��DCT . - ��- -� �'...T i � SE 128TH ST' .
��aos� Z g ' � ��:;� o > ___.._ . _
yF a � � � � ��. £n � ;:f?�_(�R' � ' }31
d�� � � � � �i Y,i '_` '� � �'
T z ` ,� y� ------'� x �
�, ` d. � .
�; `��'D� Renton = :
� � sE,�,o sr�.,�,o.sr "'
; ++�+srcr'� W �, s€a�cr � y y�
z "'
• NE 15T ST ; � ,�� ME IST PL y y�
� ; a � PIE 15T� �� � d
Q
�SE2Nn5T t�.. .��ST �{ � �({ SE�I+TN_;7 --,....._�i
J ��ff6CT . � ��7�TNST�p �.����
S�2N�P���,� . �
..,,1� p
J � ��a� � �aart�sr � s��xrk sr
�1 S9TN ST . � �9RD PL � SE 137TF1 Pt .
� SE 1�9TM PL � �.:
�: � SE tTH PL SE l]BTN ST'
¢i t� }}f $ SE 139T!}PL �SE 57'H PC � '�j: ..
i' � � W.... � � ..
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. �ST `t� .. - �+j . � �1[STN ST - 1
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1
K
�.--.�..�_��� f� � $f'�V f .s. 5Fla�H57 � � � .�s., . �`n� _��j
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4� � � �
J w
; �
sF R�r Cedar R�ver.-- �y, � � �
�� ��
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u o - . _ /fj,• '}(��`� .
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a � � "�� _____—
�,.�- �,� t ��� �
�C)ZD�!Kinq Cou�ty 5�7c.rry ��,� . �:.�r; � �7�''r`'�ci�
R HST fl 795b}tr`:�--�"'_---_J�_
lagond
� Solrctod Rartoh uqnwry
�_� Caunty Boundary Ane�s
� Afauntain Peaks iOG1
Hl�hways Parsola
� Incorporated Area U �kos end Lerpu Rhiar•
Streots f/ 5treams
(Conf) �.A� O�ainapo Comp�sints
02012 D. R.STRONG Consulting Engineers Inc. Page 12
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
FIGURE 11
USDA KING COUNTY SOILS SURVEY MAP
�1 M��ICing Cour.ry:.rea,`l�ashi�y.on
e.
+_s_� :L'_" - - ��l ' _
�i'277 � -' �� � I]•_F7
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AgC—Alderwood gravelly sandy loam, 6 to 15 percent slopes
Map Unit Setting
• Elevation: 50 to 800 feet
• Mean annual precipitation: 25 to 60 inches
• Mean annual air temperature: 48 to 52 degrees F
• Frost-free period: 180 to 220 days
Map Unit Composition
• Alderwood and similar soils: 95 percent
• Minor components: 5 percent
Description of Alderwood
Setting
• Landform: Moraines, till plains
02012 D. R.STRONG Consulting Engineers Inc. Page 13
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
• Parent materiai: Basal till with some volcanic ash
• Properties and qualities
• Slope: 6 to 15 percent
• Depth to restrictive feature: 24 to 40 inches to dense material
• Drainage class: Moderately well drained
• Capacity of the most limiting layer to transmit water (Ksat): Very low to moderately
low (0.00 to 0.06 in/hr)
• Depth to water table: About 18 to 37 inches
• Frequency of flooding: None
• Frequency of ponding: None
• Available water capacity: Very low (about 2.5 inches)
Interpretive groups
• Land capability (nonirrigated): 4s
Typical profile
• 0 to 12 inches: Gravelly sandy loam
• 12 to 27 inches: Very gravelly sandy loam
• 27 to 60 inches: Very gravelly sandy loam
Minor Components
Norma
• Percent of map unit: 1 percent
• Landform: Depressions
Bellingham
• Percent of map unit: 1 percent
• Landform: Depressions
Seattle
• Percent of map unit: 1 percent
• Landform: Depressions
Tukwila
• Percent of map unit: 1 percent
• Landform: Depressions
Shalcar
• Percent of map unit: 1 percent '
• Landform: Depressions ,
02012 D. R.STRONG Consulting Engineers Inc. Page 14
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
�
TASK 3 FIELD INSPECTION
UPSTREAM TRIBUTARY AREA
In evaluating the upstream area, we reviewed King County IMAP aerial topography and I
imagery and conducted field reconnaissance and have concluded that upstream '
tributary area for the Site is negligible. The upstream properties developed portions ,
drain in southeasterly and southwesterly directions almost directly to the respective '
rights of way and the areas producing runoff that may enter the Site are densely
vegetated.
GENERAL ONSITE AND OFFSITE DRAINAGE DESCRIPTION
The 4.36 acre parcel is situated atop a ridge and discharges runoff into two subbasins.
TDA West is approximately 1.78 acres and discharges to 156th Avenue SE while TDA
East is comprised of the remaining 2.58 acres and discharges to 158t" Avenue SE. The
discharge elevation of TDA West is approximately six feet lower than that of TDA East.
These two flowpaths converge at a point approximately 3,000 feet downstream of TDA
West and 4,900 feet downstream of TDA East at the corner of 156th Avenue SE and SE
144th Street.
Runoff from the developed Site will be collected and conveyed by a typical catch basin/
pipe network to a detention pond in the southwest corner of the Site. The pond will
discharge to the conveyance system in 156th Avenue SE.
02012 D. R.STRONG Consulting Engineers Inc. Page 15
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
TASK 4 DRAINAGE SYSTEM DESCRIPTION AND PROBLEM
DESCRIPTIONS
DRAINAGE SYSTEM DESCRIPTION
The downstream analysis is further illustrated and detailed in the Downstream Map and
Downstream Table located in Appendix A. The downstream area is located within the
Cedar River; more specifically the Lower Cedar River sub basin. The downstream area
was evaluated by reviewing available resources, and by conducting a field
reconnaissance on July 12, 2012 under overcast conditions.
Downstream Path TDA East
Point "A" is the natural discharge point of this subbasin. Runoff exits the Site as sheet
flow to the southeast.
From Point "A" to Point "B", runoff heads southeast as sheet flow and into a roadside
ditch. (0' - ±10')
From Point "B" to Point "C", runoff travels southerly as channel flow. The grass-lined
channel is approximately 3 feet wide and 2 feet deep. The water depth was 2 inches at
the time of analysis. (±10' — ±25')
From Point "C" to Point "D", runoff continues south as pipe flow via a 12-inch Lined
Corrugated Polyethylene (LCPE) Pipe. The pipe discharges into a channel at Point "D".
(±25' — ±55')
From Point "D" to Point "E", runoff travels southerly as channel flow. The grass-lined
channel is approximately 3 feet wide and 2 feet deep. The water depth was 3 inches at
the time of analysis. (±55' — ±100')
From Point "E" to Point "F", runoff continues south as pipe flow via a 12-inch LCPE
Pipe. The pipe discharges into a channel at Point "F". At the point of discharge, the
water depth was 6 inches at the time of analysis. (±100' — ±130')
From Point "F" to Point "G", runoff travels southerly as channel flow. The grass-lined
channel is approximately 3 feet wide and 2 feet deep. The water depth was 6 inches at
the time of analysis. (±130' — ±155')
From Point "G" to Point "H", runoff continues south as pipe flow via a 12-inch Reinforced
Concrete Pipe (RCP). The pipe discharges into a channel at Point "H". At the point of
discharge, the water depth was 6 inches at the time of analysis. (±155' — ±190')
From Point "H" to Point "I", runoff travels southerly as channel flow. The grass-lined
channel is approximately 3 feet wide and 2 feet deep. The water depth was 3 inches at
the time of analysis. (±190' — ±310')
From Point "I" to Point "J", runoff heads east as pipe flow via a 12-inch Corrugated
Metal Pipe (CMP). This is located near the intersection of 158th Avenue SE and SE 2"a
Place. The Pipe tees into a 15-inch LCPE Pipe heading south on the eastern side of
158th Avenue SE. (±310' — ±340')
02012 D. R.STRONG Consulting Engineers Inc. Page 16
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
From Point "J" to Point "K", runoff is directed south as pipe flow via a 15-inch LCPE
Pipe. The pipe connects to a Type 2 Catch Basin located near the intersection of 158tn
Avenue SE and SE 2"d Place. (±340' — ±370')
From Point "K" to Point "L", runoff heads east as pipe flow via a 15-inch Ductile Iron
Pipe (DIP}. The pipe connects to a Type 2 Catch Bain. (±370' — ±440')
From Point "L" to Point "M", runoff heads east as pipe flow via a 15-inch DIP. The pipe
connects to a Type 1 Catch Bain. (±440' — ±650')
From Point "M" to Point "N", runoff heads east as pipe flow via a 15-inch DIP. The pipe
connects to a Type 1 Catch Bain. (±650' — ±800')
From Point "N" to Point "O", runoff heads east as pipe flow via a 15-inch DIP. The pipe
connects to a Type 1 Catch Bain. (±800' — ±950')
From Point "O" to Point "P", runoff heads east as pipe flow via a 15-inch DIP. The pipe
connects to a Type 2 Catch Bain located near the intersection of SE 2"d Place and 160tn
Avenue SE. (±950' —±990')
From Point "P" to Point "Q", runoff is directed south as pipe flow via a 24-inch DIP. The
pipe discharges into a roadside ditch along the west side of 160t" Avenue SE. (±990' —
±1100'}
From Point "Q" to Point "R", runoff continues southerly as channel flow. The grass-lined
channel is approximately 4 feet wide and 2 feet deep. (±1100' — ±1560')
Qualitative analysis of the downstream path continued through the conveyance system
in 160th Avenue SE, then west through the conveyance system in SE 144t" Street. The
analysis was concluded at the intersection of SE 144th Street and 156th Avenue SE
which was found to be the point of convergence with the downstream path from TDA
West. (±4925')
Downstream Path TDA West
Point "A" is the natural discharge point of this subbasin. Runoff exits the Site as sheet
flow to the southwest.
From Point "A" to Point "B", runoff heads southwest as sheet flow and into a Type 2
Catch Basin located along the east side of 156t" Avenue SE. (0' - ±15')
From Point "B" to Point "C", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 1 Catch Basin. (±15' — ±105')
From Point "C" to Point "D", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 1 Catch Basin. (±105' — ±330')
From Point "D" to Point "E", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 2 Catch Basin. (±330' — ±345')
From Point "E" to Point "F", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 2 Catch Basin. (±345' — ±360'}
From Point "F" to Point "G", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 2 Catch Basin. (±360' — ±435')
02012 D. R.STRONG Consulting Engineers Inc. Page 17
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
From Point "G" to Point "H", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 2 Catch Basin. (±435' — ±480')
From Point "H" to Point "I", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 2 Catch Basin. (±480' — ±555')
From Point "I" to Point "J", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 2 Catch Basin. (±555' — ±595')
From Point "J" to Point "K", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 1 Catch Basin. (±595' — ±610'}
From Point "K" to Point "L", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 1 Catch Basin. (±610' — ±750')
From Point "L" to Point "M", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 1 Catch Basin. (±750' — ±850')
From Point "M" to Point "N", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 1 Catch Basin. (±850' — ±925')
From Point "N" to Point "O", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 1 Catch Basin. (±925' — ±1025')
From Point "O" to Point "P", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 1 Catch Basin. (±1025' — ±1185')
From Point "P" to Point "Q", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 1 Catch Basin. (±1185' — ±1215')
From Point "Q" to Point "R", runoff continues south as pipe flow via a 12-inch PVC Pipe.
The pipe connects to a Type 1 Catch Basin. (±1215' — ±1350')
Qualitative Analysis of the downstream path continued along 156t" Avenue SE. The
analysis was c�ncluded at the intersection of 156t" Avenue SE and SE 144th Street
which was found to be the convergence point with the downstream path from TDA East.
(±3010')
02012 D. R.STRONG Consulting Engineers Inc. Page 18
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
FIGURE 12 �
DOWNSTREAM MAP '
02012 D. R.STRONG Consulting Engineers Inc. Page 19
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
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COPYRIGHT �O z��2. D.R. STRONG COkSUL?1NG EK3WEE4S INC.
FIGURE 13
DOWNSTREAM TABLE
TDA EAST
Basin: Cedar River Subbasin Name: Lower Cedar River Subbasin Number: N/A
Symbol Drainage Drainage Component Slope Distance Existing Potential Observations of field inspector
Component Type, Description From site Problems Problems resource reviewer, or resident
Name, and Size Dischar e
Type: sheet flow, Constrictions, under capacity, ponding, tributary area, likelihood of problem,
See map swale, Stream, drainage basin,vegetation,cover, % 1/4 mi=1,320 ft overtopping,flooding, habitat or organism overftow pathways,potential impacts.
channel,pipe, depth,type of sensitive area,volume destruction, scouring, bank sloughing,
Pond;Size:diameter sedimentation, incision,other erosion
Surface area
A Natural Discharge Sheet flow across southeast property +0' None Observed None Anticipated
Point corner
A-B Southeasterly Sheet Sheet flow into roadside Ditch i10' None Observed None Anticipated
Flow
B-C Southerly Channel Trapezoidal Channel:2'Deep,3'wide ±25' None Observed None Anticipated Standing Water 2"Deep
Flow
C-D Southerly Pipe Flow 12"LCPP to a ditch ±55' None Observed None Anticipated Standing Water 2"Deep
D-E Southerly Channel Trapezoidal Channel:2'Deep,3'wide t100' None Observed None Anticipated Standing Water 3"Deep
Flow
E-F Southerly Pipe Flow 12"LCPE Pipe to a ditch t130' None Observed None Anticipated Standing Water 6"Deep At South End
of Pi e
F-G Southerly Channel Trapezoidal Channel: 2'Deep,3'wide ±155' None Observed None Anticipated Standing Water 6"Deep Throughout
Flow Channel
G-H Southerly Pipe Flow 12"RCP to a ditch ±190' None Observed None Anticipated Standing Water 6"Deep
H-I Southerly Channel Trapezoidal Channel:2'Deep,3'wide t310' None Observed None Anticipated Standing Water 3"Deep
Flow
I-J Easterly Pipe Flow 12"CMP to a Tee t340' None Observed None Anticipated Trickle Flow
J-K Southerly Pipe Flow 15"LCPE Pipe to a Type 2 CB t370' None Observed None Anticipated Trickle Flow
C�)2012 D. R.STRONG Consulting Engineers Inc. Page 20
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
K-L Easterly Pipe Flow 15"DIP to a Type 2 CB ±440' None Observed None Anticipated No Flow
L-M Easterly Pipe Flow 15"DIP to a Type 1 CB ±650' None Observed None Anticipated No Flow
M-N Easterly Pipe Flow 15"DIP to a Type 1 CB t800' None Observed None Anticipated No Flow
N-0 Easterly Pipe Flow 15"DIP to a Type 1 CB ±950' None Observed None Anticipated No Flow
O-P Easterly Pipe Flow 15"DIP to a Type 2 CB ±990' None Observed None Anticipated No Flow
P-Q Southerly Pipe Flow 24"DIP to a Roadside Ditch ±1110' None Observed None Anticipated No Flow
Q-R Southerly Channel Trapezoidal Channel:2'Deep,4'wide ±1560' None Observed None Anticipated No Flow
Flow
02012 D. R.STRONG Consulting Engineers Inc. Page 21
Levei One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
� _
_
TDA WEST
Basin: Cedar River Subbasin Name: Lower Cedar River Subbasin Number: N/A
Symbol Drainage Drainage Component Slope Distance Existing Potential Observations of field inspector
Component Type, Description From site Problems Problems resource reviewer, or resident
Name, and Size Dischar e
Type: sheet flow, Constrictions, under capacity, ponding, tributary area, likelihood of problem,
See map swale, Stream, drainage basin,vegetation,cover, % 1/4 mi=1,320 ft overtopping,flooding, habitat or organism overflow pathways, potential impacts.
channel,pipe, depth,type of sensitive area,volume destruction, scouring, bank sloughing,
Pond;Size:diameter sedimentation, incision,other erosion
Surface area
A Natural Discharge Sheet fiow across southwest property ±0' None Observed None Anticipated
Point corner
A-B Southwesterly Sheet Sheet flow into a Type 2 CB 115' None Observed None Anticipated
Flow
B-C Southerly Pipe Flow 12"PVC to a Type 1 CB ±105' None Observed None Anticipated Trickle Flow
C-D Southerly Pipe Flow 12"PVC to a Type 1 CB ±330' None Observed None Anticipated Trickle Flow
D-E Southerly Pipe Flow 12"PVC to a Type 2 CB ±345' None Observed None Anticipated Trickle Flow
E-F Southerly Pipe Flow 12"PVC to a Type 2 CB ±360' None Observed None Anticipated Trickle Flow
F-G Southerly Pipe Flow 12"PVC to a Type 2 CB t435' None Observed None Anticipated Trickle Flow
G-H Southerly Pipe Flow 12"PVC to a Type 2 CB i480' None Observed None Anticipated No Flow
H-I Southerly Pipe Flow 12"PVC to a Type 2 CB t555' None Observed None Anticipated No Flow
I-J Southerly Pipe Flow 12"PVC to a Type 2 CB ±595' None Observed None Anticipated No Flow
J-K Southerly Pipe Flow 12"PVC to a Type 1 CB t610' None Observed None Anticipated No Flow
K-L Southerly Pipe Flow 12"PVC to a Type 1 CB t750' None Observed None Anticipated No Flow
L-M Southerly Pipe Flow 12"PVC to a Type 1 CB ±g50' None Obsenred None Anticipated No Flow
02012 D. R. STRONG Consulting Engineers Inc. Page 22
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
_
M-N Southerly Pipe Flow 12"PVC to a Type 1 CB ±925' None Observed None Anticipated No Flow
N-0 Southerly Pipe Flow 12"PVC to a Type 1 CB ±1025' None Observed None Anticipated No Fiow
O-P Southerly Pipe Flow 12"PVC to a Type 1 CB ±1185' None Observed None Anticipated No Flow
P-Q Southerly Pipe Flow 12"PVC to a Type 1 CB ±1215' None Observed None Anticipated No Flow
Q-R Southerly Pipe Flow 12"PVC to a Type 1 CB ±1350' None Observed None Anticipated No Flow
c�2012 D. R. STRONG Consulting Engineers Inc. Page 23
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
TASK 5 MITIGATION OF EXISTING OR POTENTIAL PROBLEMS
A review of the King County Water and Land Resources Division — Drainage Services
Section Documented Drainage Complaints within one mile of the downstream flow
paths revealed no complaints within the last ten years.
The project should not create any problems as specified in Section 1.2.2.1 of the
Manual and therefore is not required to provide Drainage Problem Impact Mitigation
subject to the requirements of Section 1.2.2.2.
Project runoff from both TDA's will be combined, collected and released per the
Manual's requirements to accommodate Level 3 Flood Problem Flow Control and Basic
Water Quality requirements. During construction, standard sediment and erosion
control methods will be utilized. This will include the use of a stabilized construction
entrance, perimeter silt fencing, and other necessary measures to minimize soil erosion
during construction.
R:1201210112040131DocumentslReportslPreliminarylLevel 1 DS 12040.docx
02012 D. R. STRONG Consulting Engineers Inc. Page 24
Level One Downstream Analysis Saddlebrook Preliminary Plat City of Renton
SECTION IV
FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND DESIGN
The aforementioned granted Adjustment allows for the two existing drainage basins to
be combined into one drainage basin. Thus, the following calculations will be for the
entire Site as one drainage basin.
EXISTING SITE HYDROLOGY (PARTA)
KCRTS was used to model the peak runoff from the Site: Per Table 3.2.2.b of the
Manual the soil type is modeled as "Till" for the Alderwood gravelly sandy loam SCS
classification as shown in Figure 4. Soils. The entire Site is modeled as "Forest."
Results of the KCRTS analysis are included in this section.
Modeling input
Land cover Entire
Site
Till forest(ac) 4.601
Till Grass (ac) 0.000
Wetland (ac) 0.000
Impervious (ac) 0.000
Scale Factor: 1.00
Time Step: Hourly
Data Type: Reduced
Project location: Seatac
Total Area: 4.601
Table 1 Pre-Developed KCRTS Modeling Input
Modeling results
Entire Site
rlow Frequency Analysis
Time Series File:predev.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
0.290 2 2/09/O1 18:00 0.371 1 100.00 0. 990
0. 079 7 1/06/02 3:00 0.290 2 25.00 0. 960
0.215 4 2/28/03 3:00 0.223 3 10.00 0. 900
0.007 8 3/24/04 20:00 0.215 4 5.00 0.800
0. 128 6 1/05/05 8:00 0.188 5 3.00 0. 667
0.223 3 1/18/06 21:00 0.128 6 2.00 0.500
0. 188 5 11/24/06 4:00 0.079 7 1.30 0.231
0.371 1 1/09/08 9:00 0.007 8 1.10 0.091
Compated Peaks 0.344 50. 00 0. 980
O 2012 D. R.STRONG Consulting Engineers Inc. 13 Saddlebrook
Technical Information Report Renton,Washington
FIGURE 5. PREDEVELOPMENT AREA MAP
,'I
i . .
O 2012 D. R.STRONG Consulting Engineers Inc. 14 Saddlebrook
Technical Information Report Renton,Washington
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A REA BREA KD 0 WN L EGEND
�
� � � PROJECT BOUNDARY
TOTAL EXlST1NG SITE AREA: 189,797 S.F. (4.36 ACRES)
�
TOTAL PROJECT AREA: 200,420 S.F. (4.60 ACRES) � TILL FOREST N O RT H
TOTAL PROJECT DEVELOPMENT AREA: 200,420 S.F. (4.60 AC)
MODELED AS T/LL FOREST GRAPHIC SCALE ORAF7F0 BY• cw�
OESlCNED BY.• A/AJ
� 3� 60 �2� PRO,1fCT ENGIN£ER: 1UJ
� DATE: OB,27.Z0f2
PRC1lECT NO.: 11040
1 INCH =60 FT.
R:\2012\0\1204D\3\Drawings\Plats\PP\Report Fig�res\01-3FIG512040.cw� 11/13/2072 1G:18:09 P.4I PST F1GUA£.• Jr
COPYRIGHT �Q 2012, D.R. STR04G CCNSUL�7N� cK�NEERS INC.
DEVELOPED SITE HYDROLOGY tPART B) I
Soil type
The soil types are unchanged from pre-developed conditions.
Land covers
KCRTS was used to model the developed peak runoff from the Site. The portions of
the Site within the proposed clearing limits tributary to the proposed detention pond
were modeled as "Till Grass" and Impervious as appropriate. Results of the KCRTS
analysis are included in this section.
Modeling input
Land cover Entire
Site
Till forest(ac) O.ODd
Till Grass (ac) 1.956
Wetland (ac) 0.000
Impervious (ac) 2.452
Scale Factor: 1.00
Time Step: Hourly
Data Type: Reduced
Project location: Seatac
Total Area: 4.408
Table 2 Developed KCRTS Modeling Input
Detailed Impervious Area Breakdown:
TOTAL LOT AREA= 136673 S.F. 45%IMPERVIOUS=61503 S.F. 55% PERVIOUS=75170 S.F.
TOTAL R.O.W.AREA=35191 S.F. 100%IMPERVIOUS=35191 S.F. 0% PERVIOUS
' TRACT A AREA= 20130 S.F. 50% IMPERVIOUS= 10065 S.F. 50%PERVIOUS= 10065 S.F.
O 2012 D. R.STRONG Consulting Engineers Inc. 15 Saddlebrook
Technical Information Report Renton,Washington
Modeling Results
Entire Site
Flow Freqnency Analys-_s
Time Series File:rdin.ts�"
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flo�r Frequency P.naiysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) ?eriod
0.769 6 2/09/O1 2:00 1.57 1 100.00 0.990
0. 613 8 1/05/02 16:00 0. 940 2 25. 00 0. 960
0. 928 3 2/27/03 7:00 0. 928 3 10. 00 0. 900
0. 647 7 8/26/04 2:00 0.815 4 5.00 0.80C
0.783 5 10/28/04 16:00 0.783 5 3.00 0. 667
, 0.815 4 1/18/06 16:00 0.769 6 2.00 0.500
0. 940 2 10/26/06 0: 00 0.647 7 1.30 0.231
1.57 1 1/09/08 6: 00 0.613 S 1.10 0.091
Computed Peaks 1.36 �0.00 0. 980
O 2012 D.R. STRONG Consulting Engineers Inc. 16 Saddlebrook
Technical Information Report Renton,Washington
BYPASS AREA HYDROLOGY
Modeling input
Land cover Entire
Site I
Till forest(ac) 0.000 ',
Till Grass (ac) 0.103 ,
Wetland (ac) 0.000 '
Impervious (ac) 0.090
Scale Factor: 1.00
Time Step: Hourly
Data Type: Reduced
Project location: Seatac
Total Area: 0.193
Table 3 Bypass KCRTS Modeling Input
Modeling results
Bypass
Flo�a Frequency Analysis
Time Series File:bypass.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flc�a Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS} Period
0.031 5 2/09/O1 2:00 0.064 1 100.00 0.990
0.024 8 1/05/02 16:00 0.037 2 25.00 0.960
0.037 2 2/27/03 7:00 0.036 3 10.00 0.900
0.025 7 8/26/04 2:00 0.033 4 5.00 0.800
0.030 6 10/28/04 16:00 0.031 5 3.00 0.667
0.033 4 1/18/06 16:00 0.030 6 2.00 0.500
0.036 3 10/26/06 0:00 0.025 7 1.30 0.231
0.064 1 1/09/08 6:00 0.024 8 1.10 0.091 '
Computed Peaks 0.055 50.00 0. 980
The flow control facility is designed to compensate for uncontrolled bypass. The 100-
year discharge from the bypass areas is 0.064 cfs, which is less than the 0.4 cfs
threshold. There should be no adverse downstream impacts to the downstream
drainage system created by the runoff from the bypass. '
There is a bypass area associated with each TDA. For purposes of detention
calculations, both bypass areas were used as the approved drainage adjustment calls
for a combination of the TDA's.
The onsite bypass areas satisfy all the requirements set forth in the Manual, Section 1.2
with the exception of TDA East as it pertains to convergence with the downstream path
of the facility within a quarter mile. This is further detailed in the following section.
O 2012 D. R.STRONG Consulting Engineers Inc. 17 Saddlebrook
Technical Information Report Renton,Washington
TDA East Bypass Discussion
Modeling input
Land cover Entire
Site
Till forest (ac) 0.000
Till Grass (ac) 0.022
Wetland (ac) 0.000
Impervious (ac) 0.039
Scale Factor: 1.00
Time Step: Hourly
Data Type: Reduced
Project location: Seatac
Total Area: 0.061 ,
Table 4 TDA East Bypass KCRTS Modeling Input
Modeling results
TDA East Bypass
Flow Frequency Analysis
Tir.me Series File:bypass.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
0.011 6 2/09/O1 2:00 0.023 1 100.00 0. 990
0.009 8 1/05/02 16:00 0.015 2 25.00 0. 960
0.013 3 12/08/02 18:00 0.013 3 10.00 0. 900
0.010 7 8/26/04 2:00 0.012 4 5.00 0.800
0.012 4 10/28/04 16:00 0.012 5 3.00 0.667
0.012 5 1/18/06 16:00 0.011 6 2.00 0.500
0.015 2 10/26/06 0:00 0.010 7 1.30 0.231
0.023 1 1/09/08 6:00 0.009 8 1.10 0.091
Computed Peaks 0.020 50.00 0. 980
The bypass area for TDA East does not converge with the downstream path of the
facility. However, because the facility is discharging to TDA West, the bypass area
must be analyzed as a separate TDA.
As a separate TDA, the bypass area qualifies for the exemption from providing formal
flow control facilities. (Exceptions 2, Section 1.2.3.B, 0.1 cfs difference) Furthermore,
the area in question is located fully within right-of-way . Therefore, flow control BMP
implementation is not required for this area. (KCSWDM, Section 5.2.2.2)
O 2012 D.R.STRONG Consulting Engineers Inc. 18 Saddlebrook
Technical Information Report Renton,Washington
FIGURE 6. POST DEVELOPMENT AREA MAP
O 2012 D.R.STRONG Consulting Engineers Inc. 19 Saddlebrook
Technical information Report Renton,Washington
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AREA BREAKD 0 WN L�GEND p
TOTAL EXISTING SITE AREA: 189,797 S.F. (4.36 ACRES) � � � pROJECT BOUNDARY Q
�
TOTAL PROJECT AREA: 200,420 S.F. (4.60 ACRES)
LOT AREA (COLLECTED,Z, 136,673 S.F. (3.138 AC)
� lMPER l/lOUS: 61,503 S.F. (l.412 AC) (45q)
TlLL GRASS: 75,170 S F. (1.726 AC)
� ROW AREA (COLLECTED� 35,191 S F. (0.808 AC)
lMPER l/lOUS: 35,191 S.F. (0.808 AC)
TILL GRASS: 0 N O RT H
� TRACT A AREA (COLLECTED): 20,130 S F. (0.462 AC)
IMPERUlOUS: 10,065 S.F. 0.231 AC DRAFTED BY.• CWA
�. � GRAPHIC SCALE
TILL GRASS: 10,065 S.F. (0.231 AC) DE57GNED BY.- �r�r
Q 3� 6� �2� pR0„�CT ENGINE£R: NAJ
� � DATE: Q�27.?0f1
BYPASS• 8,426 (0.193 AC) 1 INCH - 60 FT. PRo,.�cT No.: rsao
lMPERUlOUS: 3,936 (0.090 AC) -
TILL GRASS: 4,490 �0.103 AC� R:�2oiz�o�izoao�3��rawines\Plots\PP\Repo-t Fiyures\01-3FIG612046.dwg 1/28/2C13 2:07:57 FIA PST F7GURE• 6
CCP'rBl�-iT QQ 2612, C.�4. ST�,�,fd� CO'�LJL-i�.G EP�61P.=ERS IPdC.
PERFORMANCE STANDARDS (PART C)
The Project is required to meet the Level 3 Flow Control and Basic Water Quality
Treatment requirements. The Level 3 performance requires the developed condition
discharge rates to match the predeveloped rates ranging from 50% of the two-year
peak up to the 50-year peak. Also match developed peak discharge rates to
predeveloped peak discharge rates for the 2-, 10- and 100-year return periods.
The Basic Water Quality Treatment goal is to remove 80% of TSS for flows or volumes
up to and including the WQ design flow or volume.
Conveyance criteria for the Project require that all new pipes be designed to convey
and contain (at minimum) the 25-year peak flow.
FLOW CONTROL SYSTEM (PART D)
The Site will utilize a detention pond meeting the Level 3 Flow Control Criteria. The
King County Runoff Time Series (KCRTS) software was used to size the detention
facility. The detention pond design information is included in this section.
FLOW CONTROL BMP SELECTION
Subdivision projects are required to mitigate for impervious surFace equal to a minimum
of 10% of each lot area by use of Flow Control Best Management Practices (BMP's).
Projects are required to first analyze the feasibility of dispersal and infiltration before
, choosing another method. The Site will utilize basic dispersion with the use of spash
' blocks. Two splash blocks mitigating a total of 1,400 s.f. of impervious area, will be
installed with each residence. This shall mitigate for 11.93% to 14.89% of impervious
area for each lot, thus accommodating flow control BMP requirements.
O 2012 D. R.STRONG Consulting Engineers Inc. 20 Saddlebrook
Technical Information Report Renton,Washington
FLOW CONTROL SYSTEM
The Project will utilize one detention pond to meet Level Three Flow Control criteria for
the Site. The King County KCRTS software was used to size the detention facility.
TDA
Retention/Detention Facility
Type of Facility: Detention Pond
Side Slope: 3.00 H:1V
Pond Bottom Length: ��� ft
Pond Bottom Width: 15 ft
Pond Bottom Area: 483 : sq. ft
Top Area at 1 ft. FB: 13 . sq. ft
0.310 acres
Effective Storage Depth: 6.50 ft
Stage 0 Elevation: -�89.00 ft
Storage Volume: 5338 cu. �t
1.225 ac-ft
Riser Head: . 0 ft
Riser Diameter: 00 inches
Number of orifices: 3
Full Head Pipe
Orifice # Heignt Diameter Discharge Diameter
(ft) (�n) (CFS} (in)
1 , �' 00' ��1.03 0.073
2 V4.74 t,2.27 0.185 6. G
3 ��
("1�6.OQ 2:09 0.084 6. 0
Top Notc eir: Nor.e
Ou�flo�a R.atinq Cur�.e: i�Ior_e
Stage Elevation Storage Discharg? Percolation Surf Area
(ft) (ft) (cu. ft) (ac-ft) {cfs) (cfs) (sq. ft)
0.00 489.00 0. 0.000 0.000 0.00 4831.
0.01 489.01 48. 0.001 0.003 0.00 4839.
0.02 489.02 97. 0.002 0.004 0. 00 4848 .
0.03 489.03 145. 0.003 0.005 0. 00 4857.
0.04 489.04 194 . 0.004 0.006 0. 00 4866.
0.05 489.05 243. 0.006 0.007 0.00 4875.
0.06 489.06 291. 0.007 0.007 0.00 4884 .
0.07 489.07 340. 0.008 0.008 0.00 4893.
0.09 489.09 438. 0.010 0.008 0. 00 4911.
0.21 489.21 1034 . 0.024 0.013 0. 00 5018.
0.34 489.34 1694 . 0.039 0.017 0.00 5136.
0.47 489.47 2369. 0.054 0.020 0.00 5254.
0. 60 489.60 3060. 0.070 0.022 0.00 5374 .
0.72 489.72 3712. 0.085 0. 024 0.00 5486.
0.85 489.85 4433. 0.102 0.026 0.00 5609.
0.98 489.98 5170. 0.119 0.028 0.00 5732.
l.11 490.11 5923. 0.136 0. 030 0.00 5857 .
1.23 490.23 6633. 0.152 0. 032 0.00 5973.
1.36 490.36 7418. 0.170 0.033 0.00 6100.
O 2012 D. R.STRONG Consulting Engineers Inc. 21 Saddlebrook
Technical Information Report Renton,Washington
1.49 490.49 8219. 0.189 0.035 0.00 6229.
1. 62 490.62 9038. 0.207 0.036 0.00 6358.
1.74 490.74 9808. 0.225 0.038 0.00 6479.
1.87 490.87 10658. 0.245 0.039 0.00 6611.
2.00 491.00 11527. 0.265 0.040 0. 00 6744.
2. 12 491.12 12343. 0.283 0. 042 0.00 6868.
2.25 491.25 13245. 0.304 0. 043 0.00 7003.
2.38 491.38 14164. 0.325 0. 044 0.00 7140.
2.51 491.51 15101. 0.347 0.045 0.00 7278• I
2. 63 491.63 15982. 0.367 0.046 0.00 7406. I
2.76 491.76 16954 . 0.389 0.048 0.00 7546. !
2.89 491.89 17944 . 0.412 0.049 0.00 7688. �
3.02 492.02 18953. 0.435 0.050 0.00 7831.
3.14 492.14 19901. 0.457 0.051 0.00 7963.
3.27 492.27 20945. 0.481 0.052 0.00 8108.
3.40 492.40 22009. 0.505 0.053 0.00 8255.
3.53 492.53 23092. 0.530 0.054 0.00 8402.
3. 65 492. 65 24108. 0.553 0.055 0.00 8539.
3.78 492.78 25228. 0.579 0.056 0.00 8689.
3. 91 492. 91 26367. 0.605 0.057 0.00 8840.
4 .04 493.04 27526. 0.632 0.058 0.00 8992.
4 . 16 493.16 28614. 0.657 0.058 0.00 9134.
4 .29 493.29 29811. 0.684 0.059 0.00 9288.
4 .42 493.42 31029. 0.712 0.060 0.00 9444 .
4 .55 493.55 32267. 0.741 0.061 0.00 9601.
4 . 67 493. 67 33428. 0.767 0.062 0.00 9747.
4.74 493.74 34113. 0.783 0.062 0.00 9833.
4.76 493.76 34310. 0.788 0.064 0.00 9857.
4.79 493.79 34606. 0.794 0.068 0.00 9894.
4.81 493.81 34804. 0.799 0.075 0.00 9919.
4.83 493.83 35003. 0.804 0.084 0.00 9943.
4.86 493.86 35302. 0.810 0.095 0.00 9980.
4.88 493.88 35501. 0.815 0. 109 0.00 10005.
4 . 91 493.91 35802. 0.822 0.120 0.00 10042.
4 . 93 493.93 36003. 0.827 0. 124 0.00 10067.
4 . 95 493.95 36205. 0.831 0.128 0.00 10092.
5.08 494.08 37527. 0.862 0.146 0.00 10254.
5.21 494.21 38871. 0.892 0.161 0.00 10417.
5.33 494.33 40130. 0.921 0. 174 0.00 10568.
5. 46 494.46 41515. 0.953 0. 185 0.00 10734.
5. 59 494.59 42921. 0.985 0. 196 0.00 10901.
5.72 494.72 44349. 1.018 0.206 0.00 11069.
�. 84 494.84 45686. 1.049 0.216 0.00 11225.
5. 97 494. 97 47157. 1.083 0.225 0.00 11395.
b. 00 495.00 47499. 1.090 0.227 0.00 11434.
6.02 495.02 47728 . 1.096 0.229 0.00 11461.
6.04 495.04 47958. 1. 101 0.234 0.00 11487.
6.07 495.07 48303. 1. 109 0.241 0.00 11527. '
6.09 495.09 48534 . 1.114 0.250 0.00 11553.
6.11 495.11 48765. 1.119 0.261 0.00 11580.
6.13 495.13 48997. 1.125 0.274 0.00 11606.
6.15 495.15 49229. 1.130 0.283 0.00 11633.
6.17 495.17 49462. 1.135 0.287 0.00 11659. '
6.30 495.30 50989. 1.171 0.311 0. 00 11833.
�J 2012 D. R.STRONG Consulting Engineers Inc. 22 Saddlebrook
Technical Information Report Renton,Washington
6. 43 495.43 52539. 1.206 0.331 0.00 12CC
b. 50 495.50 53382. 1.225 0.342 0.00 1210;
6. 60 495.60 54599. 1.253 0.817 0.00 1223 .
0.70 495.70 55830. 1.282 1. 670 0.00 1237-- .
6. 80 495.80 57074 . 1.310 2.780 0.00 1251_ .
6. 90 495.90 58332. 1.339 4.090 0.00 1264'"�.
7 .00 496.00 59604 . 1.368 5.570 0. 00 12787 .
7 . 10 496.10 60889. 1.398 7.010 0. 00 1292�.5.
7 .20 496.20 62189. 1.428 7.540 0. 00 1306�5.
7 .30 496.30 63503. 1.458 8.050 0. 00 13207 .
7 .40 496.40 64830. 1.488 8.520 0. 00 133<�� .
7 .50 496.50 66172. 1.519 8.960 0. 00 1349=, .
7 . 60 496.60 67529. 1.550 9.390 0.00 13633 .
7 .70 496.70 68899. 1.582 9.800 0.00 13777 .
7.80 496.80 70284. 1.613 10.180 0.00 13921 .
7. 90 496. 90 71683. 1. 646 10.560 0.00 14066.
8.00 497.00 73097. 1. 678 10.920 0.00 14212 .
8.10 497.10 74526. 1.711 11.270 0.00 1435� .
8 .20 497.20 75969. 1.744 11.610 0.00 14505. I
8.30 497.30 77427. 1.777 11. 940 0.00 14653. �
8.40 497.40 78899. 1.811 12.260 0.00 14802. �''
8.50 497.50 80387. 1.845 12.580 0.00 1�951. '
Hyd Inflow Outflow Peak Storage
Stage Elev (Cu-Ft) (Ac-Ft)
1 1.57 0.34 6.50 495.50 53383. 1.226
2 0.77 0.27 6.12 495.12 48858. 1.122
3 0. 93 0.20 5. 69 494. 69 44050. 1.011
� 0.94 0.19 5.50 494.50 41929. 0.963
5 0.82 0. 11 4.88 493.88 35479. 0.814
6 0.51 0.06 4.46 493.46 31450. 0.722
7 0. 61 0.06 3.92 492. 92 26498. 0.608
8 0. 65 0.05 2.80 491.80 17247. 0.396
Hyd R/D Facility Tributary Reservoir POC Outflow
Outflow Inflow Inflow Target Calc
1 0.34 0.06 ******x* 0.37 0.36
2 0.27 0.03 ****x*** ******* 0.28
3 0.20 0.04 ******** ******* 0.21
4 0.19 0.04 ******** ******* 0.20
5 0.11 0.03 ******** ******* 0. 11
6 0.06 0.02 ******** ******* 0.07
7 0.06 0.02 ***x**** ******* 0.07
8 0.05 0.02 *******X **x*�*X O. G7
Route Time Series through Facility
Inflow Time Series File:rdin.tst
Outflow Time Series File:rdout
POC Time Series File:dsout
Inflow/Outflow Analysis
Peak Inflow Discharge: 1.57 CFS at 6:00 on Jan 9 in Year 8
Pea� Outflow Discnarge: 0.344 CFS at 12:00 on Jan 9 in Year 8
�2012 D. R. STRONG Consulting Engineers Inc. 23 Saddlebrook
Technical Information Report Renton,Washington
Pea� Reservoir Stage: 6.50 Fi.
Peak Reservoir Elev: 495.50 Ft
Peak Reservoir Storage: 53383. C :
. 1. �� - - ,-r�
Add Time Series:bypass.ts-
Peak Summed Discnarge: 0. ;:,? CL'� at "-2: ;;0 c�= Jan 9 in �iear �
Point of Compliance File:dsout.�sT
Flow Frequency Analysis
Time Series File:rdout.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----F1ow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) (ft) Period
0.266 2 2/09/O1 20:00 0.344 6.50 1 100.00 0. 990
0.057 7 1/07/02 4:00 0.266 6.12 2 25.00 0. 960
0.204 3 3/06/03 22:00 0.204 5. 69 3 10.00 0. 900
0.048 8 8/26/04 7:00 0.188 5.50 4 5.00 0.800
0.060 6 1/08/05 5:00 0.107 4.88 5 3.00 0. 667
0.107 5 1/19/06 3:00 0.060 4.46 6 2.00 0.500
0.188 4 11/24/06 8:00 0.057 3. 92 7 1.30 0.231
0.344 1 1/09/08 12:00 0.048 2.80 8 1.10 0.091
Computed Peaks 0.318 6.35 50.00 0. 980
Flow Frequency Analysis
Time Series File:dsout.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
0.278 2 2/09/Ol 20:00 0.357 1 100.00 0. 990
0.072 7 1/05/02 16:00 0.278 2 25.00 0. 960
0.213 3 3/06/03 20:00 0.213 3 10.00 0.900
0.068 8 8/26/04 2:00 0.198 4 5.00 0.800
0.072 6 1/05/05 8:00 0.113 5 3.00 0.667
0.113 5 1/19/06 3:00 0.072 6 2.00 0.500
0.198 4 11/24/06 7:00 0.072 7 1.30 0.231
0.357 1 1/09/08 12:00 0.068 8 1.10 0.09"_
Computed Peaks 0.331 50.G0 0. 9�u
F1ow Duration from Time Series File:rdout.ts=
C�atoff Count Frequency CDF Exceedence Probab�---_,
CFS ° ° ° -
0 0 0
0.004 32796 53.483 53.483 46.517 0.465E+C _
0.011 6148 10.026 63.509 36.491 0.365E+i:_�
0.019 4821 7.862 71.371 28.629 0.286E+i;:=i
0.026 5268 8.591 79.962 20.038 0.200E+C��
0.034 4349 7.092 87.055 12.945 0.129E+C'2
0.041 3152 5.140 92.195 7.805 0.780E-C-
0.049 1871 3.051 95.246 4.754 0.475E-C"�
0.056 1556 2.538 97.784 2.216 0.222E-C1
0.064 1042 1.699 99.483 0.517 0.517E-�
0.071 54 O.C88 99.571 0.429 0.429E-'
O 2012 D.R.STRONG Consulting Engineers Inc. 24 Saddlebrook
Technical Information RepoR Renton,Washington ',
0.078 29 0.047 99.618 0.382 0.382E-02
0.086 17 0.028 99.646 0.354 0.354E-02
0.093 17 0.028 99.674 0.326 0.326E-02
0. 101 11 0.018 99.692 0.308 0.308E-02
0. 108 15 0.024 99.716 0.284 0.284E-02
0.116 9 0.015 99.731 0.269 0.269E-02
0.123 7 0.011 99.742 0.258 0.258E-02
0.131 23 0.038 99.780 0.220 0.220E-02
0. 138 14 0.023 99.803 0.197 0.197E-02
0. 146 14 0.023 99.826 0.174 0. 174E-02
0. 153 9 0.015 99.840 0.160 0. 160E-02
0. 161 8 0.013 99.853 0.147 0.147E-02
0.168 13 0.021 99.874 0.126 0.126E-02
0.176 10 0.016 99.891 0.109 0.109E-02
0. 183 11 0.018 99.909 0.091 0.913E-03
0. 191 11 0.018 99.927 0.073 0.734E-03
0. 198 10 0.016 99. 943 0.057 0.571E-03
0.205 14 0.023 99. 966 0.034 0.342E-03
0.213 5 0.008 99.974 0.026 0.261E-03
0.220 4 0.007 99.980 0.020 0.196E-03
0.228 5 0.008 99.989 0.011 0. 114E-03
0.235 2 0.003 99.992 0.008 0.815E-04
0.243 1 0.002 99.993 0.007 0. 652E-04
0.250 1 0.002 99. 995 0.005 0.489E-04
0.258 1 0.002 99.997 0.003 0. 326E-04
0.265 1 0.002 99.998 0.002 0. 163E-04
Flow Duration from Time Series File:dsout.tsf
Cutoff Count Frequency CDF Exceedence Probability
CFS ° ° ° -
o � o
0.004 32785 53.465 53.465 46.535 0.465E+00
0.012 6183 10.083 63.549 36.451 0.365E+00
0.020 4885 7.966 71.515 28.485 0.285E+00
0.027 5255 8.570 80.085 19.915 0. 199E+00
0.035 4253 6.936 87.021 12. 979 0. 130E+i"
0.043 3171 5.171 92.192 7.808 0.781E-C :
0.051 1952 3.183 95.375 4. 625 0.462E-C"
0.058 1473 2.402 97.777 2.223 0.222E-Gi
0.066 943 1.538 99.315 0.685 0. 685E-02 I
0.074 123 0.201 99.516 0. 484 0.484E-02
0.082 53 0.086 99.602 0.398 0.398E-02
0.090 25 0.041 99.643 0.357 0.357E-02
0.097 17 0.028 99.671 0.329 0.329E-02
0.105 14 0.023 99.693 0.307 0.307E-02
0. 113 13 0.021 99.715 0.285 0.285E-02
0.121 8 0.013 99.728 0.272 0.272E-02
0.129 13 0.021 99.749 0.251 0.251E-02
0. 136 18 0.029 99.778 0.222 0.222E-02
0. 144 16 0.026 99.804 0. 196 0.196E-02
0.152 14 0.023 99.827 0. 173 0.173E-02
0.160 7 0.011 99.839 0.161 0.161E-02
0.168 9 0.015 99.853 0.147 0.147E-02
0.175 13 0.021 99.874 0.126 0.126E-02
0. 183 10 0.016 99.891 0.109 0.109E-02
O 2012 D.R.STRONG Consulting Engineers Inc. 25 Saddlebrook
Technical Information Report Renton,Washington
0.191 11 0.018 99. 909 0.091 0.913E-03
0.199 12 0.020 99.928 0.072 0.718E-03
0.206 9 0.015 99.943 0.057 0.571E-03
0.214 14 0.023 99.966 0.034 0.342E-03
0.222 6 0.010 99.976 0.024 0.245E-03
0.230 3 0.005 99.980 0.020 0.196E-03
0.238 4 0.007 99.987 0.013 0.130E-03 ,
0.245 2 0.003 99.990 0.010 0.978E-04
0.253 2 0.003 99.993 0.007 0.652E-04
0.261 1 0.002 99.995 0.005 0.489E-04
0.269 1 0.002 99.997 0.003 0.326E-04
0.277 1 0.002 99.998 0.002 0.163E-04
Duration Comparison Anaylsis
Base File: predev.tsf
New File: dsout.tsf
Cutoff Units: Discharge in CFS
-----Fraction of Time----- ---------Check of Tolerance-------
Cutoff Base New oChange Probability Base New oChange
0.064 � 0. 95E-02 0.88E-02 -8.0 � 0.95E-02 0.064 0.063 -0.5
0.081 � 0. 63E-02 0.40E-02 -36.3 � 0.63E-02 0.081 0.067 -16. 9
0.098 I 0.50E-02 0.33E-02 -34.2 � 0.50E-02 0.098 0.073 -25.7
0.116 I 0.37E-02 0.28E-02 -25.1 � 0.37E-02 0.116 0.086 -25. 4
0.133 I 0.29E-02 0.23E-02 -18.3 � 0.29E-02 0.133 0.113 -15. 1 I
0.151 � 0.22E-02 0.17E-02 -21.3 � 0.22E-02 0.151 0.136 -9.7
0.168 I 0.15E-02 0.15E-02 -l. l � 0.15E-02 0.168 0.168 -0.3 � � / �
0.185 I O.10E-02 O.10E-02 3.2 � O.10E-02 0.185 0.188 1.2 '� I �
0.203 I 0. 62E-03 0.65E-03 5.3 � 0.62E-03 0.203 0.204 0. 7 ��
0.220 � 0.34E-03 0.28E-03 -19.0 � 0.34E-03 0.220 0.214 -2. 7
0.238 I 0.21E-03 0.13E-03 -38.5 � 0.21E-03 0.238 0.229 -3.7
0.255 I 0.16E-03 0.65E-04 -60.0 � 0.16E-03 0.255 0.234 -8. 1
0.272 � 0.11E-03 0.16E-04 -85.7 I 0.11E-03 0.272 0.240 -11.8
0.290 � 0.16E-04 O.00E+00 -100.0 I 0.16E-04 0.290 0.277 -4. 3
Maximum positive excursion = 0.005 cfs ( 2. 6%) G, /,c
�V�o � Li�
occurring at 0.190 cfs on the Base Data:predev.tsf
and at 0.195 cfs on the New Data:dsout.tsf
Maximum negative excursion = 0.031 cfs (-27.3%)
occurring at 0.114 cfs on the Base Data:predev.tsf
and at 0.083 cfs on the New Data:dsout.tsf
O 2012 D. R. STRONG Consulting Engineers Inc. 26 Saddlebrook
Technical Information Report Renton,Washington
Peaks Plot
Retum Perio�
2 5 10 20 50 100
<� rd:,ut.pks in Sea-Tz�
• dsout.pks
� predevpks
R �
3
000 �__
o �
° S
10-�
Y . �
in ' o 0
u' o
U
a�
rn
`m
U
N
�
'O Z
q
'0 3
1 2 5 10 20 30 40 50 60 70 80 90 45 98 99
Cumulative Probability
Duration Curve
�
0
rdcuLdur o
dsout dur •
� taroetdur �
N
0
. �
N
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ODO �
O
N
O
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rn I
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10-5 10� 10-3 10�Z 1p-� tp°
ProGability Exce�ence
O 2012 D. R.STRONG Consulting Engineers Inc. 27 Saddlebrook
Technical Information Report Renton,Washington
FLOW CONTROL PRIMARY OVERFLOW
Using standard orifice equation to determine stand pipe diameter in control structure
Ref. KCSWDM '09 Figure 5.3.4.H
Qioo = 100-Year Peak Storm calculated using KCRTS 15-Minute Time Steps
Q�oo = 3.88 cfs
HM�= Maximum available head in feet measured from crest of weir
HM,�= 0.5 ft.
D = Riser Diameter
D= {Q�oo/(3.782 * HM,,,z.$))°.s
D = 1.20 ft. (min. diameter) round up to nearest standard pipe diameter
use D = 18 in. or 1.5 ft.
Calculate actual height above the weir expected during the 100-year peak storm
H = Actual head above weir achieved with Q�oo
H = (Q�oo/(9.739 * D))^0.67
H = 0.41 ft.
JAILHOUSE SECONDARY OVERFLOW
Using standard weir equation to determine length of window opening in control structure
_ Ref. KCSWDM '09 Figure 5.3.4.E
D= Control structure diameter
D= 60 in.
Q�oo= 100-Year Peak Storm calculated using KCRTS 15-Minute Time Steps
Q�oo= 3.88 cfs
Hr,,,p,X= Head above weir achieved with Q�oo
H�,X= 0.41 ft.
P= Height of overflow above outlet invert elevation
P= 6.50 ft.
c= Constant
c= 3.27+0.4*HMAx/P
- C= 3.30 ft.
L= Arc length of the jailhouse window as necessary but not to exceed 50%of '
the control structure's internal circumference
L= �Qioo K�*HrnAx�.s>�+0.2*Hnn.vc
L= 4.57 ft. (min. length)
C= Control Structure Circumference
C= 16 ft.
Calculate corrected L due to vertical bars in window.
�', Lad�= adjusted arc length of the jail-house window
Lad�= L+0.083*(L/0.33)
Lad�= 5.72 ft.
O 2012 D. R.STRONG Consulting Engineers Inc. 28 Saddlebrook
Technical Information Report Renton,Washington
BIRDCAGE EMERGENCY OVERFLOW SPILLWAY
Using sharp crested weir equation to determine stand pipe diameter in control structure
Ref. KCSWDM '09 Figure 5.3.4.E
Q�oo= 100-Year Peak Storm calculated using KCRTS 15-Minute Time Steps
Qioo= 3.88 cfs
P= Height of primary overflow above outlet invert elevation I
P= 6.91 ft. '
D= Control structure diameter
D= 60 in. '
L= Control structure circumference
L= 15.71 ft. '
C= 3.27+0.4H/P (ft)
use...
Q�oo= 3.27+0.4H/P(L-0.2H)H^1.5
H= Emergency overflow water surface elevation
H= 0.18 ft.
WATER QUALITY TREATMENT (PART E)
The Project is located in the Basic Water Quality (WQ) Treatment area. The Project
will utilize a BayFilter vault meeting Basic Water Quality treatment criteria. See Figure
7 for details.
� I r k
O 2012 D. R.STRONG Consulting Engmeers Inc. 29 Sadd eb o0
Technical Information Report Renton,Washington
i I
FIGURE 7. DETENTION FACILITY DET i
AILS AND BAYFILTER SIZING
I
O 2012 D. R.STRONG Consulting Engineers Inc. 30 Saddlebrook
' '- Technical Information Report Renton,Washington
SE 1/4 SE OF SECT/ON 32, TOWNSH/P 23N, RANGE 5F, W.M.
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SWARf FfcT�Fd.7RAAON AREA 7HE FLL7ER . , } � �'�, . �'..
LOCA710N RENT0.4, WA CAR7RlGCES ARE HOU.�D 1N A CONCRE7E S7RUCNRE '�, ' ��. '�, I
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A-NNNN A
BayFilter Sizing
Details
�
ADS Representative: Kell Kokesh
Date: 1/29/2013
Site Information
Pro'ect Name Saddlebrook
Cit Seattle �
State WA
, Draina e Area 4.408 acres
' Im ervious Area 2.452 acres
Pervious Area 1.956 acres
%Im ervious 56%
Upstream Detention System
Peak release rate from detention 1 cfs
Treatment release rate from detention 0.073 cfs
S stem Confi uration Offline
Detention retreatment credit 60%
WA DOE Approval
General Use Desi nation Yes
A enc re uired%removal 80%
Filter System
Filtration Brand Ba Filter
Cartrid e Hei ht 28 in
Cartrid e Filter Area 43 sf
Maximum Cartrid e Flow Rate 0.7 gpm/sf
S ecific Flow Rate 30 gpm
Determine Critical Sizing Value
Number of Cartrid es Usin Flow Rate 2
SUMMARY
Treatment Flow Rate 0.o73 cfs
Cartrid e Flow Rate 30 gpm
Number of Cartrid es 2
SECTION V
CONVEYANCE SYSTEM ANALYSIS AND DESIGN
Per Core Requirement #4 of the KCSWDM, the con�eyance system must be analyzed
and designed for existing tributary and developed onsite runoff from the proposed
project. Pipe systems shall be designed to convey the 100-year design storm. The
Rational Method was used to calculate the Q-Ratio for each pipe node.
A conveyance system consisting primarily of pipes and catch basins has been designed
for the Project. Onsite runoff will be collected by the multiple catch basins. Pipes are
typically twelve- and eighteen-inch diameter LCPE material. The pipes will have a
minimum slope of 1.00%.
The pond primary overflow riser is designed to convey the 100-year peak storm (design
storm), based on the KCRTS 15-minute time series for developed, undetained
conditions on site. This is calculated at 3.88 cfs. The results of the 15-minute KCRTS
time series, overflow riser analysis, and KCBW Calculations are included in this
Section.
DEVELOPED 15-MINUTE TIME SERIES
Modeling input
Land cover Entire
Site
Till forest(ac) 0.000
Till Grass (ac) 1.956
, Wetland (ac) 0.000
Impervious (ac) 2.452
Scale Factor: 1.00
Time Step: 15-Min
Data Type: Reduced
Project location: Seatac
Total Area: 4.408
Tabfe 4 Developed 15-Min KCRTS Modeling Input
O 2012 D.R. STRONG Consulting Engineers Inc. 31 Saddlebrook
i Technical Information Report Renton,Washington
Modeling results
Developed 15-Min
Flow Frequency Analysis
Time Series File:l5-min-sea.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis------
Flc;a Rate Rank Time of Peak - - Peaks - - Rank Return Pro�
(CFS) (CFS) Period
1.17 6 8/27/O1 18:00 3.88 1 100.00 0.9°C
0.857 8 1/05/02 15:00 2.64 2 25.00 0.96i:
2. 64 2 12/08/02 17:15 1.65 3 10.00 0. 90i
0. 941 7 8/23/04 14:30 1.61 4 5.00 0.8C
1. 61 4 11/17/04 5:00 1.44 5 3.00 0.6E
1. 44 5 10/27/05 10:45 1.17 6 2.00 0.50C
1. 65 3 10/25/06 22:45 0.941 7 1.30 0.23=.
3. 88 1 1/09/08 6:30 0.857 8 1.10 0.09-
CO:"��Ltc� pEGr... �. q� G.�. �� �. �.^.����
O 2012 D. R.STRONG Consulting Engineers Inc. 32 Saddlebrook
Technical Information Report Renton,Washington
BACKWATER ANALYSIS
Storm Water Runoff Variables:
A= Total of Subasin and Tributary Areas
C= Runoff Coefficient(the anticipated proportion of rainfall volume that runs off the area)see 2009 KCSWM Table 3.2.1A
CC= Composite Runoff Coefficient
CC= S(Cn*An)/ATotal
Tc= Time of Concentration(Typically 6.3 minutes which is the minimum value used in calculations)
R= design return frequency
iR= Unit peak rainfall intensity factor
iR= (aR)(Tc)^(-bR)
aR,bR= coefficients from'09 KCSWM Table 3.2.1.B used to adjust the equation for the design storm
IR= Peak rainfall intensity factor for a storm of return frequency'R'
IR= PR*iR
PR= total precipitation(inches)for the 24-hour storm event for the given frequency. See Issopluvial Maps in 2009 KCSWM Figures 3.2.1.A-D
QR= peak flow(cfs)for a storm of return frequency'R'
QR= CC'iR'A
The Q-Ratio describes the ratio of the tributary flow to the main upstream flow.
R=° -year storm
aR= 2.61
bR= 0.63
PR= inches
Conveyance System Variables:
d= pipe diameter
n= Manning's Number
1= length of pipe
O 2012 D. R. STRONG Consulting Engineers Inc. 33 Saddlebrook
Technical Information Report Renton,Washington
Pipe Structures Subasins& A A C CC Tc iR IR oR SQR Q- d Material n I Slope invert invert over- Q V Bend CB
Tributaries subasin Ratio in out flow Full Full Dia
elev. Flow Flow
FROM CB To CB sf Ac Ac Min. cfs cfs in ft % ft ft ft cis fps
CB#4 TO INLET 1
4 4 3 4 589 0.01 0.90 6.3 0.82 3.27 0.04 0.04 0.00 12 N-12 0.012 36 1.46 498.50 497.98 501.50 4.68 5.95 0 2
RUN 103-3 39482 0.91 0.63
3 3 2 3 36336 0.83 0.61
3 3 2 3 75818 1.74 0.62 6.3 0.82 3.27 3.54 3.58 88.91 12 N-12 0.012 222 1.00 497.98 495.76 501.22 3.87 4.93 0.2 2
RUN 102-2 21239 0.49 0.58
2 2 1 2 30748 0.71 O.b7
2 2 1 2 51987 1.19 0.58 6.3 0.82 3.27 2.25 5.83 0.63 18 N-12 0.012 299 1.00 495.26 492.27 505.93 11.41 6.46 0.2 4
RUN 101-1 1006 0.02 0.90
RUN 6-1 36509 0.84 0.60
1 1 INLET 1 1 5477 0.13 0.90
1 1 INLET 1 1 42992 0.99 0.65 6.3 0.82 3.27 2.09 7.92 0.36 18 N-12 0.012 65 5.05 492.27 489 499.73 25.65 14.51 124.59 4
CB#6 TO CB#1
6 6 5 6 435 0.01 0.90 6.3 0.82 3.27 0.03 0.03 0.00 12 N-12 0.012 34 0.99 494.76 494.42 498.24 3.85 4.90 0 2
5 5 1 5 36074 0.83 0.60 6.3 0.82 3.27 1.62 1.65 55.04 12 N-12 0.012 25 6.73 494.42 492.77 499.42 10.04 12.78 54.1 2
36509 0.84 0.60
CB#101 TO CB#1
101 101 1 101 1006 0.02 0.90 6.3 0.82 3.27 0.07 0.07 0.00 12 N-12 0.012 21 0.98 492.98 492.77 497.86 3.83 4.88 0 2
CB#102 TO CB#2
102 102 2 102 21239 0.49 0.58 6.3 0.82 3.27 0.93 0.93 0.00 12 N-12 0.012 24 21.24 500.93 495.76 505.93 17.84 22.71 0 2
CB#103 TO CB#3
103 103 3 103 3�J482 0.91 0.63 6.3 0.82 3.27 1.88 1.88 0.00 12 N-12 0.012 24 0.99 498.22 497.98 501.22 3.84 4.89 0 2
O 2012 D. R.STRONG Consulting Engineers Inc. 34 Saddlebrook
Technical Information Report Renton,Washington
BACKWATER ANALYSIS MAP
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O 2012 D. R.STRONG Consulting Engineers Inc. 35 Saddlebrook
Technical Information Report Renton,Washington
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COPYRIGHT �Q 2012, D.R. STRONG CONSULTING ENGINE_RS INC. SHEEF. � OF �
BACKWATER ANALYSIS RESULTS
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:CB#4 TO INLET l .bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:495.12 feet
Discharge Range:0.788 to 7.92 Step of 0.788 [cfsj
Overflow Elevation:501.5 feet
Weir:NCNE
Upstream Velocity:0. feet/sec
PIPE N0. 1: 64 LF - 18"CP @ 5.05% OUTLET: 489.00 INLET: 492.27 INTYP: 5 j
JUNC N0. l: OVERFLOW-EL: 499.73 3END: 90 DEG DIA/WIDTH: 4.0 Q-RATIO: 0.36 I
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
x*�******************************************+******�***********************�**
' 0.79 2.87 495.14 * 0.012 0.34 0.19 6.12 6.12 2.86 2.87 0.41
1.58 2.88 495.15 * 0.012 0.48 0.26 6.12 6.12 2.86 2.88 0.62
2.36 2.93 495.20 * 0.012 0.59 0.31 6.12 6.12 2.88 2.93 0.79
3.15 2.99 495.26 * 0.012 0. 68 0.36 6.12 6.12 2.90 2.99 0. 94
3.94 3.07 495.34 * 0.012 0.76 0.40 6.12 6.12 2.93 3.07 1.09
4.73 3.16 495.43 * 0.012 0.84 0.44 6.12 6.12 2.96 3.16 1.24
5.52 3.28 495.55 * 0.012 0.91 0.48 6.12 6.12 3.00 3.28 1.39
6.30 3.41 495.68 * 0.012 0.98 0.51 6.12 6.12 3.05 3.41 1.54
7.09 3.56 495.83 * 0.012 1.04 0.54 6.12 6.12 3.10 3.56 1.70
7.88 3.72 495.99 * 0.012 1.09 0.58 6.12 6.12 3.16 3.72 1.85
8.67 3.90 496.17 * 0.012 1.15 0. 61 6.12 6.12 3.23 3.90 2.04
PIPE N0. 2: 299 LF - 18"CP @ 1.00°s OUTLET: 492.27 INLET: 495.26 INTYP: 5
JUNC NO. 2: OVERFLOW-EL: 505.93 BEND: 0 DEG DIA/WIDTH: 4.0 Q-RATIO: 0.63
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
***********��*****�*******�************************�************************�**
0.58 0.42 495.68 * 0.012 0.29 0.24 2.87 2.87 0.31 0.42 0.37
1.16 0.54 495.80 * 0.012 0.41 0.33 2.88 2.88 0.41 ***** 0.54
1.74 0.66 495.92 * 0.012 0.50 0.40 2.93 2.93 0.50 ***** 0.66
2.32 0.77 496.03 * 0.012 0.58 0.46 2.99 2.99 0.58 ***** 0.77
2.90 0.87 496.13 * 0.012 0.65 0.52 3.07 3.07 0.65 ***** 0.87
3.48 1.05 496.31 * 0.012 0.72 0.57 3.16 3.16 0.73 1.05 0.95
4.06 1.12 496.38 * 0.012 0.78 0.62 3.28 3.28 0.84 1.12 1.03
4.64 1.20 496.46 * 0.012 0.83 0.67 3.41 3.41 0.98 1.20 1.10
5.22 1.31 496.57 * 0.012 0.89 0.72 3.56 3.56 1.17 1.31 1.17
5.80 1.54 496.80 * 0.012 0.94 0.76 3.72 3.72 1.47 1.54 1.24
6.38 1.94 497.20 * 0.012 0.98 0.81 3.90 3.90 1.86 1.94 1.30
PIPE NO. 3: 221 LF - 12"CP @ 1.00$ OUTLET: 495.76 INLET: 497.98 INTYP: 5
JUNC N0. 3: OVERFLOW-EL: 501.22 BEND: 0 DEG DIA/WIDTH: 2.0 Q-RATI0:88.91
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI I
****x*********************************�*************************************+**
0.36 0.33 498.31 * 0.012 0.25 0.21 0.00 0.21 0.25 ***** 0.33 '
0.71 0.48 498.46 * 0.012 0.36 0.30 0.09 0.30 0.36 ***** 0.48 '
1.07 0.61 498.59 * 0.012 0.44 0.36 0.16 0.36 0.44 ***** 0.61 '
1.43 0.73 498.71 * 0.012 0.51 0.43 0.27 0.43 0.51 ***** 0.73
1.78 0.85 498.83 * 0.012 0.57 0.48 0.37 0.48 0.57 ***** 0.85
2.14 0.96 498.94 * 0.012 0.63 0.54 0.55 0.55 0.63 ***** 0.96
2.49 1.07 499.05 * 0.012 0.68 0.59 0.62 0.62 0.68 ***** 1.07
2.85 1.19 499.17 * 0.012 0.73 0.64 0.70 0.70 0.73 ***** 1.19
3.21 1.33 499.31 * 0.012 0.77 0.70 0.81 0.81 0.77 ***** 1.33
3.56 1.48 499.46 * 0.012 0.81 0.76 1.04 1.04 0.81 ***** 1.48
3.92 2.09 500.07 * 0.012 0.85 0.84 1.44 1.44 1.51 2.09 1.60
O 2012 D.R.STRONG Consulting Engineers Inc. 36 Saddlebrook
Technical Information Report Renton,Washington
PIPE VO. 4: 35 LF - 12"CP � 1.46o OUTLET: 497.98 INLE_: 498.50 INTYP: �
Q{CFS) HW(FT} HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
*x*****+******************�************+*************************************>_
0.00 0.04 498.54 * 0.012 0.03 0.03 0.33 0.33 0.03 0.04 O.G�
0.01 0.06 998.56 * 0.012 0.04 0.04 0.48 0.48 0.05 0.06 0.�4
0.01 0.10 498.60 * 0.012 0.05 0.04 0.61 0.61 . 0.10 0.10 0.05
0.02 0.22 498.72 * 0.012 0.06 0.05 0.73 0.73 0.22 0.22 0.05
0.02 0.33 498.83 * 0.012 0.06 0.05 0.85 0.85 0.33 0.33 O.C?
0.02 0.44 498.94 * 0.012 0.07 0.06 0.96 0.96 0.44 0.44 O.C8
0.03 0.56 499.06 * 0.012 0.07 0.06 1.07 1.07 0.56 0.56 0.08
0.03 0.67 499.17 * 0.012 0.08 0.06 1.19 1.19 0.67 0.67 O.G9
0.04 0.81 499.31 * 0.012 0.08 0.07 1.33 1.33 0.81 0.81 0.?0
0.04 0.97 499.47 * 0.012 0.09 0.07 1.48 1.48 0.97 0.97 0.`_0
0.04 1.58 500.08 * 0.012 0.09 0.07 2.09 2.0� 1.58 1.58 0.11
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:CB#6 TO CB#l .bwp
Ssrcharge condition at intermediate junctions '
�ailwater Elevation:496. feet
Discharge Range:0.162 to 1.65 Step of O.lo2 [c=s]
Overflow Elevation:498.24 feet
Weir:NONE
Upstream Velocity:0. feet/sec
PIPE NO. l: 24 LF - 12"CP @ 6.73°s OUTLET: 492.77 INLET: 494.42 INTYP: 5
JUNC NO. 1: OVERFLOW-EL: 499.42 BEND: 54 DEG DIA/WIDTH: 2.0 Q-RATI0:55.04
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
�*x****************+**********************************************************�
0.16 1.59 496.01 * 0.012 0.17 0.09 3.23 3.23 1.59 1.59 0.19
0.32 1.59 496.01 * 0.012 0.24 0.13 3.23 3.23 1.58 1.59 0.29
0.49 1.59 496.01 * 0.012 0.29 0.15 3.23 3.23 1.58 1.59 0.36
0.65 1.60 496_02 * 0.012 0.34 0.18 3.23 3.23 1.59 1.60 0.43
0.81 1.62 496.04 * 0.012 0.38 0.20 3.23 3.23 1.59 1.62 0.49
0.97 1.63 496.05 * 0.012 0.42 0.22 3.23 3.23 1.60 1.63 0.55
1.13 1.65 496.07 * 0.012 0.45 0.23 3.23 3.23 1.60 1.65 0.61
1.30 1.67 496.09 * 0.012 0.49 0.25 3.23 3.23 1.61 1.67 0.66
1.46 1.70 496.12 * 0.012 0.52 0.26 3.23 3.23 1.61 1.70 0.71
1.02 1.72 496.14 * 0.012 0.55 0.28 3.23 3.23 1.62 1.72 0.77
1.78 1.75 496.17 * 0.012 0.57 0.29 3.23 3.23 1.63 1.75 0.82
?IPE i10. 2: 34 LF - 12"CP @ 0.990 OUTLET: 494.42 INLET: 494.76 INTYP: 5
Q(CrS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
t�****�**************�*�*****�******************+******************************
0.00 1.26 496.02 * 0.012 0.03 0.03 1.59 1.59 1.26 1.26 0.03
0.01 1.25 496.01 * 0.012 0.04 0.03 1.59 1.59 1.25 1.25 0.04
0.01 1.25 496.01 * 0.012 0.04 0.04 1.59 1.59 1.25 1.25 0.05
0.01 1.26 496.02 * 0.012 0.05 0.05 1.60 1.60 1.26 1.26 0.05
0.01 1.28 496.04 * 0.012 0.05 0.05 1.62 1.62 1.28 1.28 0.06
0.02 1.29 496.05 * 0.012 0.06 0.05 1.63 1.63 1.29 1.29 0.07
0.02 1.31 496.07 * 0.012 0.06 0.06 1.65 1.65 1.31 1.31 0.07
0.02 1.33 496.09 * 0.012 0.07 0.06 1.67 1.67 1.33 1.33 0.08
0.03 1.36 496.12 * 0.012 0.07 0.06 1.70 1.70 1.36 1.36 0.08
0.03 1.38 490.19 * 0.012 0.07 0.07 1.72 1.72 1.38 1.38 0.09
0.03 1.41 �90.17 * 0.012 O.C8 �.0/ 1.75 1.7� 1.41 1.41 C.C°
O 2012 D.R.STRONG Consulting Engineers Inc. 37 Saddlebrook
Technical Information Report Renton,Washington
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:CB#101 TO CB#l .bwp
Surcharge condition at in�ermediate junctions
Tailwater Elevation:496. feet
Discharge Range:0.07 to 0.07 Step of 0.07 [cfs]
Overflow Elevation:497.86 feet
Weir:NONE
Upstream Velocity:0. feet/sec
PIPE N0. 1: 21 LF - 12"CP @ 0.98a OUTLET: 492.77 INLET: 492.98 INTYP: 5
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
*****�*************��*+*x**********************+**�***********�*************�**
0.07 3.03 496.01 * 0.012 0.11 0.10 3.23 3.23 3.03 3.03 0.14
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:CB#102 TO CB#2 .bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:496.81 feet
Discharge Range:0.93 to 0.93 Step of 0.93 [cfs]
Overflow Elevation:505.93 feet
Weir:NONE
Upstream Velocity:0. feet/sec
PIPE N0. 1: 24 LF - 12"CP @ 21.24o OUiLET: 495.76 INLET: 500.93 INTYP: 5
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
*���**********************�******�***�*+�***�*********************�*****�******
0.93 0.46 501.39 * 0.012 0.41 0.16 1.05 1.05 0.41 ***** 0.46
BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:CB#103 TO CB#3.bwp
Surcharge condition at i�termediate junctions
Tailwater Elevation:499.46 feet
Discharge Range:1.88 to 1.88 Step of 1.88 [cfs]
Overflow Elevation:501.22 feet
Weir:NONE
Upstream Velocity:0. feet/sec
PIPE N0. 1: 24 LF - 12"CP @ 0.99a OUTLET: 497.98 INLET: 498.22 INTYP: 5
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
*x**x�*****�****�**************�**********�**�*********************************
1.88 1.43 499.65 * 0.012 0.59 0.50 1.48 1.48 1.30 1.43 0.88
,II
I � 212DR.
O 0 . STRONG Consultmg Engineers Inc. 38 Saddlebrook
Technical Information Report Renton,Washington
SECTION VI '
SPECIAL REPORTS AND STUDIES !
The following report and studies have been provided with this submittal.
1. Traffic Impact Analysis —TraffEx, Inc., August 10, 2012 �'�,
2. Critical Areas Study — Sewall Wetland Consulting, Inc., August 20, 2012 �
3. Geotechnical Engineering Study— Earth Solutions NW, LLC., August 21, 2012
4. Arborist Report— Greenforest, Inc., August 27, 2012 '
�2012 D. R.STRONG Consulting Engineers Inc. 39 Saddlebrook
Technical Information Report Renton,Washington
SECTION VII
OTHER PERMITS, VARIANCES AND ADJUSTMENTS
Approved Drainage Adjustment 2012-03 (Attached)
Approved ADS BayFilter Adjustment 2012-04 (Attached)
;
�._�
,-_
� ;
�
O 2012 D. R.STRONG Consulting Engineers Inc. 40 Saddlebrook
Technical Information Report Renton,Washington
PUBL[C WORiCS DEPARTMEflIS cI�y�f
e C� r��rJO � .�'. ,,
. �1li E M O fi A N D U [Vi .
, DATE: August 16, 2012
TO: . � Arneta Henninger, Plan Reviewer .
FROM: ����on Straka, Surface Water Utility Supervisor,x7248
STAFF CONTACT: Hebe Bernardo, Surface Water Utility Engineer,x7264
SUBlECT: Sa�dlebrook Plat Adjustment 2012-03
The City of Renton Surface Water Utility has completed review of the adjustment ,
request for the Saddlebrook P[at in accordance with City adopted 2009 King County
Surface Water Design Manual (KCSWDM) anci City Amendments to the 2d09 KCSWDM.
Our review of the information leads us to understand that the appficant's engineering is
� requesting an adjustment from the 2009 King County Surface Water Design Manual to �
core requirement#1 (section 1.2.1), Qischarge at the Naturaf Location. Our review of v�1
the information provided by the applicant engineer on August 13, 2012, provides the ]-_
followingfindings: �
�
�
1. The proposed project has n�t completed the process preliminary plat approval �
or SEPA review_ �
� 2. The site is located in two existing parce{s (3564500260 and 3664500261) with a
total area of 4.36 acers. Parcels are situated atop a ridge and discharges
runoff into two subbasins. Tributary Drainage Area (TDA)�West is �
approximately 1.78 acres and discharges ta 156th Avenue SE while TDA East is
comprised of the remaining 2,58 acres and discharges to 158th Avenue SE.
The discharge elevation of TDA West is approximately six feet(ower than that of
TDA East. These two flowpaths converge at a point approximately 3,000 feet
downstream of TDA West and 4,900 feef downstream of TDA East at the
corner of 156th Avenue SE and SE 144th Street (convergence pointj.
3. The proposal is to collect much of the runoff from the project site (4.36 acres) '
and direct it to a single combined detention and water quality facility located in !
the west portion of the site. The allowed release would then discharge through 'i
an existing conveyance system into the right-of-way of 156th Avenue SE where i� �i
continues to go south and converges with TDA East in SE 1�4tn Stree�. '�i
II
!an Illian '
Page 2 of 4
August 16,2012
4. No downstream analysis has been completed and submitted to the City for
review. However, a preliminaryfield recognizance ofthe downstream drainage
system was completed bythe applicant and applicant's engineer. Finclings were
discussed in the adjustment [etter. Preliminary analysis demonstrated that the
downstream path from TDA West is mostly comprised of a constructed
conveyance system from the�site to the convergence point. This conveyan.ce
system is made up of grass and rock-lined ditches as wefl as cu(verts, pipes,
and catch basins.
5. King County drainage complaints in the area were reviewed and the basin
draining to the conveyance system was determined using King County
iMAP. This resource review revealed an overall basin size of approximately
73.5 acres and no relevant drainage complaints in the last 15 years
downsfream of the Site.
6. Ta analyze the impact of the discharge rate, the King County Runoff Time
Series Software was used to examine .the overall site in a forested condition, �
TDA West's existing condition, and the 73.5 acre basin in a forested condition as
well as a full build-out condition (undetained, �based on KCSWDM Table
3.2.2.0 for 4.0 DU/GA, 42% impervious). TDA 1Nest (in its existing condition)
generates approximately 0.29 cfs of runQff for the 100-year return interval.
TJ�e total site, when analyzed for the forested condition, will generate
approximately 0.35 cfs of runoff for the 100-year return interval. The existing
conveyance system downstream of the proposed pfat would receive a net
increase in runofFof Q.06 cfs,which is less than 0.1 cfs. The total drainage
basin currently generates 5.93 cfs and 23.59 cfs, for forested and build-out
conditions assuming no flow control, respective[y. �
Based on these understandings, findings, and per section 1.2.1 of the 2009 Surface
Water Design Manual as amended bythe City,the adjustment to allow the diversion of
runoff to a single combined stormwater flow control and water quality treatment facility
draining to SE 156th Avenue is approved with the following conditions:
1. A level one downstream analysis in accordance with se�ion 1.2.1 of the 2009
KCSWDM as amended by the City shall be submitted to the City for review.
Based on this analysis,the City may require the compfetion of a down5tream
anafysis and/or improverrzents to the downstream system.
H:\File Sys\SVJP-Surace�b'ater Projzcts\SVJP-Z7-5urfzce L"✓ater Projects(CIP)\27-3?29 Renton Stormevater �
Manual\ADIUSTMENTS\201Z\2012-3 Saddl�bro�k.doc\H3ah
Jan Illian
Page 3 of 4
. August 16,2012
2. The proposed combined cletention and water quality treatment facility to be
constructed on the northwest corner of the site shall be designed as a level 3
flow control for the entire site in using the two basins as the existing (forested)
site conditions. The stormwater facility shall be designed in accordance with
� section 1.23 ofthe 2009 KCSWDM. �
3. Surface water discharge from the west basin is required to follow its existing
drainage course.
4. Water quality treatment in accordance with�section 1.2.8 of the 2009 KCSWDM
shall be provided for al)targeted surfaces prior to discharging from the site. The
water quality facility shall be sized based on the entire proposed subdivision
draining to the facility including any required frontage improvemenfs.
5. The release rate from the detention facility will be based on all of the tributary
area being directed to the facility.
6. The volume of the stormwater detention facility shall be based on all flows .
directed to the facility at full deve{opment under current zoning. The detention
volume shall 6e sized using Level 3 Flood Prablem Flow Control Standards in the
2009 KCSWDM. The pre-developed condition runoff rates for the sizing of the
facility shall be based on the entire site using forested as pre-developed site
conditions. The TIR shall include all required documentation detai{ed in chapter
Z of the 2009 KCSWDM for the sizing of the facility.
7. Additional storm drainage requirements identified bythe Cityof Renton as part
of the SEPA review process or preliminary plat approval may apply to this
project. Please note that the approval of this adjustment does not relieve the
- applicant from other conditions that may be stipulated in future city, state, or _
federaf permits/requirements. �
tVo�es to applicant:
1. All lots within the Saddlebrook Plat are required to provide�low control BMPs in
accordance with figure C.1.3.A of the 2009 KCSWDM. Flow control BMP credits
in accordance with section 1.2.3 ofthe 2005 KCSWDM may be used to reduce
the size of the required flow control facility. The feasibility to implement full .
dispersion BMPs and full infiltration BMPs shafl be verified first. If
implementation of full dispersion BMPs and ful) infiltration BMPS are not
feasible alternatives,then any of the BMPs listed in figure C.1.3.A shall be
provided. The selected flow control BMP to be implemented on each lot shall be
shown on the co.nstruction plans. Drainage calculations for the sizing of the .
proposed BMPs to be constructed on each lot shall be included in the TIR.
H:\�ile Sys\SWP-Surface Water Projects\SWP-27-Surface Water Projects{CIP)\27-3129 Renton Stormwater
Mznual\ADJUS7MENTS\2012\2012-3 Saddlebro�k.doc\HBah
1an Illian
Page 4 of 4
August 16,2012
Construction of the proposed flow control BMPs may be difFered for
construction on the lof at time of bui(ding permit.
If you have any questions about this adjusfinent, please contact Hebe Bernardo or me. �
Attachments
cc_ Lys Hornsby,P.E.,Utility Systems Diredor
' Kayren K"rttrick,Development Engineering Supervisor
Vanessa Dolbee,Planner
File
H:\File Sys\SWP-Surface Water Projects\SWP-27-Surface���ater Projects(CIP)\27-3129 Ren`on Stormtivater
Manuaf\ADJUSTMENTS\2012\2012-3 Saddl�br�ok.doc\HBah
PUBLIC WORKS DEPARTMENT � �!�{�O� �}.,
�
M E � M O R A IV D U M -
DATE: October 31, 2012
TO: . Arneta Henninger, Plan Reviewer
FROM: ��1 Ron Straka,Surface Water Utility Supervisor, x7248
STAFF CONTACT: Hebe C. Bernardo, Surface Water Utility Engineer,x7248
SUBJECT: Saddlebrook Plat—ADS BayFilterT'�Adjustment 2012-U4
The City of Renton Surface Water Utility has completed review of the adjustment request from
� DR Strong Consultant Engineer for the 5addlebrook Plat in accordance with City adopted 2009
King County Surface Water Design Manual (KCSWDM) and City Amendments to the 2009
KCSWDM. Our review of the information leads us to understand that the applicant's
engineering is requesting an adjustment from the 2009 King County Surface Water Design
Manual.to core requirement#8}, Water Quality. Our review of the information provided by the
appficant engineer on October 16, 2012, prbvides the f�llowing findings:
1. The proposed project has not completed the process preliminery plat approval or SEPA
review. .
2. The site is located in two existing parcels(3664500260 and 3664500261) with a total
�rea oi4.3a acres. Parce(s ar� sii��ated aiop a ricige a��d uischargzs runu� ini� �wo
� sub-basins. An adjustment to Core Requirement#1, Discharge at the Natural Location
was approved in December 11,2012 allowing the project to collect much of the runoff
irom ihe projeci site(4.36 acres) and �irect it to a single combined detent�on an� water
. quality facility located in the west�ortion of the site.
The adjustment r2quesi proposes io use ihe BayFilterT"' Sys�em for Basic Water Quality
treatme�t. The Washington State Cepartment of Ecofogy has approved the BayFilterT"' System
• for General Use Level Designation for Basic Water Quality treatment. �
Based on the information provided in the adjustment request;the BayFilterT'� Sysiem for 6asic .
Water Quality Treatment is approved with the following conditions:
� 1. The u�aiei-quali�cy design flow shall be as follows,whichever is applicable:
a. Downstream of flow control facility:The full 2-year pre-developed a Ilo�vable
rate release rate from the i low control facility.
� Ms.Henninger
Page 2 of 3
October 31,20Z2
2. The Storm Filter system shall be sized as described in the BayFilterT"'Technica!ond
� . Design Monual, and#he designer shall select the result yielding the larger number of
cartridges. . �
3. Pre-settling shall be provided per Section 6.5.1 of the 2009 KCSWDM, General
� Requirements for Media Filtration Facilities.
4. BayFilrer'"'systems shall be installed in such a mannerthat the flows exceeding the
dzsign flow rat2s are bypassed around th� Ba�lter Water Quality treatment facility. An
external bypass to handle flow exceeding the facility design shall be provided.
5. The following maximum flow rates per cartridge system is limited to the following:
a. BayFilter Cartridge{BFC)Cartridge maximum flow rate of OJ gpm/sf. ,,
i. 30 gpm (0.067 cfs) per cartridge (43 sf filter area). I
ii. Z6 inches in diameter and approximately 28.75 inches tall.
6. Media combinations for the BayFilterTM'cartridges are limited to Sifica Sand, Perlite,
- Zeolite, and Activated Alumina. All filters are limited to the 19"vertical component to
the spiral filter layers.
7. Vaults used for the BayFilter""System shall conform to the"Materials"and "Structural
Stability" requirements specified in Section 5.3.3 of the 2009 KCWDM for detention
vaults.
8. The BayFilterTM'system must be�installed in an area that is accessible to maintenance
equipment. The maintenance of a BayFiltefTM'system requires a vacuum truck as well as
the removal and replacement of the filter cartridges. i he manhole covers,and/or
access hatches of the BayFilter�M System must be placed in locations that can be easily
reach�4 by s:.�ch a veh:c!e.
9. Access Requirements: �
a. Access consistent with City confined entry policy must be provided by either �
removable panels or other City approved accesses to alfow for removaf and
repl2�ement ef the L�;�Filter cartric�ges. Arrrc�vec► �ccess details for the Storm
Fi!ter s��stem may be��sed?s exam�le znd �re ava�lable in Reference Section 7C
of the 2D09 KCSWDM.
b. Removable panels, if used, shall be at�rade, have stainless steel lifting�yes, and
weigh no more than 5 t�ns per p�ne!. � �
c. Access io t�e in;fo�anu ou�,et cells must a�so be pr��i�e�.
C. �2C�4��C ZCC�SS IS f��'L':Cp�::��":A(1`:�:11` IIAIaG:�I EY('�P/MIS�: leeL.
e. Structures and access covers shaii be designed ror NS20 tranic ioading.
f. Removable panel access for vault shall not be located within the street
pav�ment section. _
� 1�J. I:�s;�l!����n of� RayFilterT"'system shal(i�Ho�v i�e manu�ac�urer's recomnendecf
nrocedures.
H:\Fiie Sys\SV✓?-Su��dce�Jater P�cjects\SW P-27-Sumc2��Jater Projects{CfF)\27-3129 2enton 5tormwaier
�=^anuci\A�)'JSTMEPJTS�?Oi2�i�Q12-4 c�r��h���U pl�r_h��,f;Ir=r.rip��Hgah
Ms.Henninger '
� Page 3 of 3
October 31,2012 �
. 11. The Bay FilterT"'system shall be inspected every six(6) months during the 2-year
maintenance defect bond period following completion of construction and plat '
recording..The owner is responsibie for the maintenance of the Bay Filter'TM system �
during the 2-year defect bod period. The City will maintain the facility after the two
year maintenance and defect bond period expires.
� 12. When BayFilter exhibits flows below design levels,the system should be inspected and '
maintained as soon as practical. Replacing a BayFilter cartridge should be considered at
ar above the level of the 4"collector pipes to the manifold. Maintenance procedures
can be found in the BayFilter System Technical and Design Manual. The maintenance
process comprises the removal.and replacement of each BayFilter cartridge and the
cleaning of the vault or manhole with a vacuum truck.
13. This is a conceptual approval for using the BayFilter for Basic Water Quality Treatment.
Further analysis and design calculations shall be included in the TIR for final approval.
14. The approval of this adjustment to use the Bay�ilter System for the Saddlebrook Plat
does not authorize the use of the BayFilter System on future projects without prior
approval from the City of Renton.
15. The BayFilter system shall be installed in accordance with the approved drawings and
shall not be located within City right-of-way or easements.
Please note that the approval of this adjustment does not relieve the applicant from other city,
state, or�ederal requirements. li you have any questions about this adjustment, please contact
Hebe C. Bernardo or me.
Attachments -
cc: Lys Hornsby,P.E.,Utili'ry Sysiems Director
. Kayren Kittrick,Developrnent Engineering Supervisor
Richzrd Marsfizl,SurFace W=ter and+?l�ater Maintenance Manager
Vanessa Dolbee,Planner
� Filz
N:\Fi;e Sys\5`.VP-Su�i�c2 Wa'ef Prcjects\SUJP-27-Surtace 1'Ja.er Projects jCiPj\27-3129 R=nton Stcrmv.at2r '
fv7arual\ADJUSTMENTS\2012\?012-4 Sattle6rc��Plat-tay�i'.ter.d�c\H3zh
SECTION VIII I
ESC PLAN ANALYSIS AND DESIGN (PART A)
The Erosion and Sedimentation Control Design will meet the nine minimum
requirements: ;
1. Clearing Limits - Areas to remain undisturbed shall be delineated with a high �I�
visibility plastic fence prior to any site clearing or grading. I
2. Cover Measures - Site disturbed areas shall be covered with mulch and '
seeded, as appropriate, for temporary or permanent measures. '
3. Perimeter Protection - Perimeter protection shall consist of a silt fence down ,
slope of any disturbed areas or stockpiles.
4. Traffic Area Stabilization - A stabilized construction entrance will be located at
the point of ingress/egress.
5. Sediment Retention — The proposed detention pond will be used as a sediment
pond.
6. Surface Water Control - Surface water control will be provided by interceptor
swales. ;
7. Dewatering Control — Not Applicable to this Site. I
8. Dust Control - Dust control shall be provided by spraying exposed soils with
water until wet. This is required when exposed soils are dry to the point that
wind transport is possible which would impact roadways, drainage ways,
surface waters, or neighboring residences.
9. Flow Control — Flow control will be provided by the detention pond.
SWPPS PLAN DESIGN (PART B)
Construction activities that could contribute pollutants to surFace and storm water
include the following, with applicable BMP's listed for each item:
1. Storage and use of chemicals: Utilize source control, and soil erosion and
sedimentation control practices, such as using only recommended amounts of
chemical materials applied in the proper manner; neutralizing concrete wash '�
water, and disposing of excess concrete material only in areas prepared for
concrete placement, or return to batch plant; disposing of wash-up waters from
water-based paints in sanitary sewer; disposing of wastes from oil-based paints,
solvents, thinners, and mineral spirits only through a licensed waste
management firm, or treatment, storage, and disposal (TSD) facility.
2. Material delivery and storage: Locate temporary storage areas away from
vehicular traffic, near the construction entrance, and away from storm drains.
Material Safety Data Sheets (MSDS) should be supplied for all materials stored,
and chemicals kept in their original labeled containers. Maintenance, fueling,
and repair of heavy equipment and vehicles shall be conducted using spill
O 2012 D. R.STRONG Consulting Engineers Inc. 41 Saddlebroo:�
Technical Information Report Ren,on. b�lashington
prevention and control measures. Contaminated surfaces shall be cleaned
immediately following any spill incident. Provide cover, containment, and
protection from vandalism for all chemicals, liquid products, petroleum products,
and other potentially hazardous materials.
3. Building demolition: Protect stormwater drainage system from sediment-laden
runoff and loose particles. To the extent possible, use dikes, berms, or other
methods to protect overland discharge paths from runoff. Street gutter,
sidewalks, driveways, and other paved surfaces in the immediate area of
demolition must be swept daily to collect and properly dispose of loose debris
and garbage. Spray the minimum amount of water to help control windblown
fine particles such as concrete, dust, and paint chips. Avoid excessive spraying
so that runoff from the site does not occur, yet dust control is achieved. Oils
must never be used for dust control. �
4. Sawcutting: Slurry and cuttings shall be vacuumed during the activity to prevent '
migration offsite and must not remain on permanent concrete or asphalt paving �
overnight. Collected slurry and cuttings shall be disposed of in a manner that �'
does not violate ground water or surface water quality standards.
The complete CSWPPP can be found in Appendix D of this report. The site plans can
be found in the engineering plan set. ,
C 2012 D.R.STRONG Consulting Engineers Inc. 42 Saddlebrook
Technical Information Report Renton,Washington
SECTION IX
BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT
1. Bond Quantity Worksheet— attached in Appendix B
2. Facility Summary— attached.
3. Declaration of Covenant—will be provided prior to final engineering approval.
O 2012 D. R.STRONG Consulting Engineers Inc. 43 Saddlebrook
Technical Information Report Renton,Washington
STORMWATER FACILITY SUMMARY SHEET
Development Saddlebrook Date November 14, 2012
Location 13426 156t" Avenue SE, Renton, Washinqton
ENGINEER DEVELOPER
Name Maher A. Joudi, P.E. Name
Firm D. R. STRONG Consulting Firm: PNW Holdings LLC
En ineers, Inc.
Address 10604 NE 38 Place, #232 Address 9675 SE 36 Street, # 105
Kirkland, WA 98033 Mercer Island, WA 98040
Phone 425 827-3063 Phone (206) 588-1147
Developed Site: 4.60 acres
Number of lots Fourteen
Number of detention facilities on site: Number of infiltration facilities on site:
1 pond ponds
vaults vaults
tanks tanks
Flow control provided in regional facility (give
location)
No flow control required Exemption number
Downstream Draina e Basins
Immediate Major Basin
Basin Lower Cedar River Cedar River
Number & type of water quality facilities on site:
biofiltration swale (regular/wet/or continuous inflow?)
sand filter (basic or large?) sand filter, linear (basic or
large?) 1 BayFilter
1 detention pond sand filter vault (basic or large?)
combined detention/wetvault stormwater wetland
compost filter wetpond (basic or large?)
, filter strip wetvault
28 flow dispersion pre-settling pond
farm management plan flow-splitter catchbasin
O 2012 D.R.STRONG Consulting Engineers Inc. 44 Saddlebrook
Technical Information Report Renton,Washington
landscape management plan
oil/water separator (baffle or coalescing plate?)
catch basin inserts:
Manufacturer
pre-settling structure:
Manufacturer
DESIGN INFORMATION INDIVIDUAL BASIN
East
Water Quality design flow
Water Quality treated volume
Drainage basin(s) 2
Onsite area (inlcudes frontage) 4.60 ac.
Offsite area 0
Type of Storage Facility Pond
Live Storage Volume (required) 53,382
Predev Runoff Rate 2-year 0.128
10-year 0.223
100-year 0.371
Developed Runoff Rate 2-year 0.769
(Including Bypass Rate) 10-year 0.928
100-year 1.570
Type of Restrictor Frop-Tee
Size of orifice/restriction No. 1 1.03
No. 2 2.27
No. 3 2.09
No. 4 N/A
�2012 D. R.STRONG Consulting Engineers Inc. 45 Saddlebrook
Technical Information Report Renton,Washington
SECTION X
OPERATIONS AND MAINTENANCE MANUAL
See Appendix C for excerpts from the 2009 King County Surface Water Design Manual
with regard to Operations and Maintenance.
�I
O 2012 D.R.STRONG Consulting Engineers Inc. 46 Saddlebrook
Technical Information Report Renton,Washington
APPENDICES
O 2012 D. R. STRONG Consulting Engineers Inc. 47 Saddlebrook
Technical Information Report Renton,Washington
APPENDIX "A" LEGAL DESCRIPTION
LOTS 1 AND 2, KING COUNTY SHORT PLAT NO. 976093, RECORDED UNDER
RECORDING NO. 7612010798, IN KING COUNTY, WASHINGTON.
O 2012 D. R.STRONG Consulting Engineers Inc. 48 Saddlebrook
Technical Information Report Renton,Washington
APPENDIX "B" BOND QUANTITY WORKSHEET
� ,
,
({
�� I ; .
; � �
�_� :j
O 2012 D.R.STRONG Consulting Engineers Inc. 49 Saddlebrook
Technical Information Report Renton,Washington
Site Improvement Bond Quantity Worksheet Webdate: 12/02/2008
� 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: Saddlebrook Date: 14-Nov-12
Location: Renton Project No.: LUA 12-007
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 Quantity Worksheet12040.x1sx Report Date: 11/15/2012
Site Improvement Bond Quantity Worksheet Webdate: 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 18 1 1215
Crushed surfacin 1 1/4" minus ESC-3 WSDOT 9-03.9(3) $ 85.45 CY
Ditching ESC-4 $ 8.08 CY 150 1 1212
Excavation-bulk ESC-5 $ 1.50 CY
Fence, silt ESC-6 SWDM 5.4.3.1 $ 1.38 LF 882 1 1217
Fence,Temporary(NGPE) ESC-7 $ 1.38 LF 2177 1 3004
Hydroseeding ESC-8 SWDM 5.4.2.4 $ 0.59 SY 18750 1 11063
Jute Mesh ESC-9 SWDM 5.4.2.2 $ 1.45 SY
Mulch, b hand, straw, 3"deep ESC-10 SWDM 5.4.2.1 $ 2.01 SY
Mulch, by machine, straw, 2"deep ESC-11 SWDM 5.4.2.1 $ 0.53 SY
Piping,temporary, CPP, 6" ESC-12 $ 10.70 LF
Piping, temporary, CPP, 8" ESC-13 $ 16.10 LF
Piping, temporary, CPP, 12" ESC-14 $ 20.70 LF 295 1 6107
Plastic covering,6mm thick, sandba ed ESC-15 SWDM 5.4.2.3 $ 2.30 SY
Rip Rap, machine placed; slopes ESC-16 WSDOT 9-13.1(2) $ 39.08 CY
Rock Construction Entrance, 50'x15'x1' ESC-17 SWDM 5.4.4.1 $ 1,464.34 Each
Rock Construction Entrance, 100'x15'x1' ESC-18 SWDM 5.4.4.1 $ 2,928.68 Each 1 1 2929
Sediment pond riser assembly ESC-19 SWDM 5.4.5.2 $ 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
Soddin , 1"deep, level round ESC-23 SWDM 5.4.2.5 $ 6.03 SY
Soddin , 1"dee , sloped round ESC-24 SWDM 5.4.2.5 $ 7.45 SY
TESC Supervisor ESC-25 $ 74.75 HR 120 1 8970
Water truck, dust control ESC-26 SWDM 5.4.7 $ 97.75 HR 80 1 7820
WRITE-IN-ITEMS **** (see paqe 9)
Each
ESC SUBTOTAL: $ 43,536.28
30%CONTINGENCY&MOBILIZATION: $ 13,060.88
ESC TOTAL: $ 56,597.16
COLUMN: A
Page 2 of 9 �
Unit prices updated: 02/12/02 �,
Version: 11/26/2008 '
Bond Quantity Worksheet12040.x1sx Report Date: 11/15/2012 '
,�
Site Improvement Bond Quantity Worksheet Webdate 1 210 2/2 0 0a
Existing Future Public Private Quantity Completed
Right-of-Way Right of Way Improvements (Bond Reduction)*
8�Drainage Facilities Quant. I
Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Complete Cost
GENERALITEMS No.
Backfill&Compaction-embankment GI-1 $ 5.62 CY 280 1,573.60 1575 8,851.50 3770 21,187.40
Backfill&Com action-trench GI-2 $ 8.53 CY 175 1,492.75 600 5,118.00
Clear/Remove Brush,b hand GI-3 $ 0.36 SY
Clearin /Grubbin /Tree Removal GI-4 $ 8,876.16 Acre 0.2 1,775.23 1.3 11,539.01 3.1 27,516.10
Excavation-bulk GI-5 $ 1.50 CY 880 1,320.00 2500 3,750.00 5000 7,500.00
Excavation-Trench GI-6 $ 4.06 CY 175 710.50 600 2,436.00
Fencin ,cedar,6'hi h GI-7 $ 18.55 LF
Fencin ,chain link,vin I coated, 6'high GI-8 $ 13.44 LF 425 5,712.00
Fencin ,chain link,gate,vinyl coated, 2 GI-9 $ 1,271.81 Each 1 1,271.81
Fencin ,s lit rail,3'hi h GI-10 $ 12.12 LF
Fill&compact-common barrow GI-11 $ 22.57 CY
Fill&compact-gravel base GI-12 $ 25.48 CY
Fiit&com act-screened topsoil GI-13 $ 37.85 CY
Gabion, 12"dee ,stone filled mesh GI-14 $ 54.31 SY �
Gabion, 18"deep,stone filled mesh GI-15 $ 74.85 SY
Gabion,36"dee ,stone fiiled mesh GI-16 $ 132.48 SY
Gradin ,fine,b hand GI-17 $ 2.02 SY
Gradin ,fine,with rader GI-18 $ 0.95 SY
Monuments,3'long GI-19 $ 135.13 Each 2 270.26
Sensitive Areas Si n GI-20 $ 2.88 Each
Soddin , 1"deep,sloped round GI-21 $ 7.46 SY
Surve in ,line& rade GI-22 $ 788.26 Da 5 3,941.30
Surveying,lot location/lines GI-23 $ 1,556.64 Acre 4 6,226.56
Traffic control crew 2 flag ers) 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,retainin ,concrete GI-28 $ 44.16 SF
Wall,rockery GI-29 $ 9.49 SF 30 284.70
Page 3 of 9 SUBTOTAI 10,549.54 38,963.02 66,371.36
Unit prices updated: 02/12/02
"KCC 27A authorizes only one bond reduction. V2fSi0n: 11/26/08
Bond Quantity Worksheet12040.x1sx Report Date: 11/15/2012
- _ I
Site Improvement Bond Quantity Worksheet Webdate: 12/02/2008
Existing Future Public Private Bond Reduction`
Right-of-way Right of Way Improvements
8 Draina e Facilities Quant.
Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Complete Cost
ROADIMPROVEMENT No.
AC Grinding,4'wide machine< 1000s RI-1 $ 28.00 SY 90 2,520.00 �,
AC Grinding,4'wide machine 1000-200 RI-2 $ 15.00 SY
AC Grindin ,4'wide machine>2000sy RI-3 $ 7.00 SY
AC Removal/Disposal/Re air RI-4 $ 67.50 SY 195 13,162.50
Barricade,t e 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 590 7,375.00 1185 14,812.50
Curb and Gutter,demolition and dis osa RI-9 $ 18.00 LF 175 3,150.00
Curb,extruded asphalt RI-10 $ 5.50 LF
Curb,e�ruded concrete RI-11 $ 7.00 LF
Sawcut,asphalt,3"depth RI-12 $ 1.85 LF 805 1,489.25
Sawcut,concrete,per 1"depth RI-13 $ 1.69 LF
Sealant,as halt RI-14 $ 1.25 LF 805 1,006.25 I
Shoulder,AC, see AC road unit rice) RI-15 $ - SY
Shoulder, ravel,4"thick RI-16 $ 15.00 SY
Sidewalk,4"thick RI-17 $ 35.00 SY 360 12,600.00 750 26,250.00
Sidewalk,4"thick,demolition and dis os RI-18 $ 29.50 SY
Sidewalk,5"thick RI-19 $ 38.50 SY
Sidewalk,5"thick,demolition and dis os RI-20 $ 37.50 SY
Si n,handica RI-21 $ 85.28 Each
Stri ing,per stali RI-22 $ 5.82 Each
Striping,thermoplastic,(for crosswalk) RI-23 $ 2.38 SF
Striping,4"reflectorized line RI-24 $ 0.25 LF
Page 4 of 9 SUBTOTAL 41,303.00 41,062.50
Unit prices updated: 02/12/02
'KCC 27A authorizes only one bond reduction. Versi0tl: 11/26/08
Bond Quantity Worksheet12040.x1sx Report Date: 11/15/2012
Site Improvement Bond Quantity Worksheet Webdate 12/02/2008
Existing Future Public Private Bond Reduction'
Right-of-way Right of Way Improvements
&Drainage Facilities Quant.
Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Complete Cost
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 S 3.60 SY
AC Overla , 1.5"AC RS-2 $ 11.25 SY
AC Overla ,2"AC RS-3 $ 15.00 SY 90 1,350.00
AC Road,2",4"rock,First 2500 SY RS-4 $ 21.00 SY 430 9,030.00 1605 33,705.00
AC Road,2",4"rock,Qt .over 2500SY RS-5 $ 19.00 SY
AC Road,3",4"rock,First 2500 SY RS-6 $ 23.30 SY
AC Road,3",4"rock,Qt .over 2500 SY RS-7 $ 21.00 SY
AC Road,5",First 2500 SY RS-8 $ 27.60 SY
AC Road,5",Qt .Over 2500 SY RS-9 $ 25.00 SY
AC Road,6",First 2500 SY RS-1 $ 33.10 SY
AC Road,6",Qt .Over 2500 SY RS-11 $ 30.00 SY
Asphalt Treated Base,4"thick RS-1 $ 20.00 SY 430 8,600.00 1605 32,100.00
Gravei Road,4"rock,First 2500 SY RS-1 $ 15.00 SY
Gravel Road,4"rock,Qt .over 2500 SY RS-1 $ 8.50 SY
PCC Road,5",no base,over 2500 SY RS-1 $ 27.00 SY
PCC Road, 6",no base,over 2500 SY RS-1 $ 25.50 SY
Thickened Edge RS-1 $ 8.60 LF
Page 5 of 9 SUBTOTAL 18,980.00 65,805.00
Unit prices updated: 02/12/02
'KCC 27A authorizes oniy one bond reduction. Version: 11/26/08
Bond Quantity Worksheet12040.x1sx Report Date: 11/15/2012
_
Site Improvement Bond Quantity Worksheet Webdate: 12/02/2008
Existing Future Public Private Bond Reduction`
Right-of-way Right of Way Improvements
&Draina e Facilities Quant.
Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Complete Cost
DRAINAGE (CPP=Corrugated Plastic Pipe,N12 Of Equivalent) For Culvert prices, Average of 4'cover was assumed.Assume perforated PVC is same rice as solid pipe.
Access Road, R/D D-1 $ 21.00 SY 100 2,100.00
Bollards-fixed D-2 $ 240.74 Each
Bollards-removable D-3 $ 452.34 Each
" CBs include frame and lid
CB T e I D-4 $ 1,257.64 Each 7 8,803.48 6 7,545.84
CB T e IL D-5 $ 1,433.59 Each
CB T pe II,48"diameter D-6 $ 2,033.57 Each 3 6,100.71
for additional depth over 4' D-7 $ 436.52 FT 15 6,547.80
CB T e 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 1 2,351.52
for additional depth over 4' D-11 $ 536.54 FT 4 2,146.16
CB T pe II,72"diameter D-12 $ 3,212.64 Each
for additional de th over 4' D-13 $ 692.21 FT
Through-curb Inlet Framework(Add) D-14 $ 366.09 Each 1 366.09 2 732.18
Cleanout, PVC,4" D-15 $ 130.55 Each
Cleanout, PVC,6" D-16 $ 174.90 Each 14 2,448.60
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 9,169.57 27,524.21 2,448.60
Unit prices updated: 02/12/02
'KCC 27A authorizes only one bond reduction. VerSion: 11/26/08
� Bond Quantity Worksheet12040.x1sx Report Date: 11/15/2012
Site Improvement Bond Quantity Worksheet Webdate 12/02/2008
Existing Future Public Private Bond Reduction'
Right-of-way Right of Way Improvements �,
DRAINAGE CONTINUED &Drainage Facilities Quant.
No. Unit Price Unit Quant. Cost C�uant. Cost Quant. Cost Com lete 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 675 7222.5
Culvert,CPP,8" D-42 $ 16.10 LF
Culvert,CPP, 12" D-43 $ 20.70 LF 345 7141.5 520 10764
Culvert,CPP, 15" D-44 $ 23.00 LF
Culvert,CPP, 18" D-45 $ 27.60 LF 400 11040 I
Culvert,CPP,24" D-46 $ 36.80 LF
Culvert,CPP,30" D-47 $ 48.30 LF
Culvert,CPP,36" D-48 $ 55.20 LF
Ditchin D-49 $ 8.08 CY
Flow Dispersal Trench (1,436 base+) D-50 $ 25.99 LF
French Drain (3'de th D-51 $ 22.60 LF
Geotextile,laid in trench,polyprop lene D-52 $ 2.40 SY
Infiltration ond testin D-53 $ 74.75 HR
Mid-tank Access Riser,48"dia, 6'deep D-54 $ 1,605.40 Each
Pond Overflow S illwa D-55 $ 14.01 SY
Restrictor/Oil Separator, 12" D-56 $ 1,045.19 Each
Restrictor/Oil Se arator, 15" D-57 $ 1,095.56 Each
Restrictor/Oil Se arator, 18" D-58 $ 1,146.16 Each 1 1146.16
Riprap,placed D-59 $ 39.08 CY 7 273.56
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 2 537.78
Trash Rack,21" D-64 $ 306.84 Each
Page 7 of 9 SUBTOTAL 7141.5 23761.5 7222.5
Unit prices updated: 02/12/02
"KCC 27A authorizes only one bond reduction. Version: 11/26/08
Bond Quantity Worksheet12040.x1sx Report Date: 11/15/2012
Site Improvement Bond Quantity Worksheet Webdate 12/02/2008
Existing Future Public Private Bond Reduction'
Right-of-way Right of Way Improvements
&Drainage Facilities Quant.
Unit Price Unit Quant. Price Quant. Cost Quant. Cost Complete Cost
PARKING LOT SURFACING
N o.
2"AC,2"top course rock&4"borrow PL-1 $ 21.00 SY
2"AC, 1.5" to 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 Utili ole relocation costs musi be accom anied by Franchise Utility's Cost Statement
Utilit Pole s Relocation UP-1 $ 10,000.00
Street Li ht Poles w/Luminaires UP-2 $ 3,000.00 [ach 4 12000 5 15,000.00
WRITE-IN-ITEMS
Such as detention/water ualit vaults. No.
Ba ilter Vault WI-1 $12,000.00 Each 1 12,000.00
WI-2 Each
WI-3 Each
WI-4 LF
WI-5 FT
WI-6
WI-7
WI-8
WI-9
wi-�o
SUBTOTAL 12,000.00 27,000.00
SUBTOTAL(SUM ALL PAGES): 99,143.61 224,116.23 76,042.46
30%CONTINGENCY 8�MOBILIZATION: 29,743.08 67,234.87 22,812.74
GRANDTOTAL: 128,886.70 291,351.10 98,855.19
COLUMN: B C D E �
Page 8 of 9
Unit prices updated: 02/12/02
"KCC 27A authorizes only one bond reduction. VerSiOn: 11/26/08
Bond Quantity Worksheet12040.x1sx Report Date: 11/15/2012
Site Improvement Bond Quantity Worksheet Webdate: 12/02/2008
Original bond computations prepared by:
Name: Maher A. Joudi Date: 15-Nov-12
PE Registration Number: 45232 Tel.#: (425) 827-3063
Firm Name: DR STRONG Consulting Engineers, Inc.
address: 10604 NE 38th Place, Suite 232 Kirkland, WA 98033 Project No: LUA 12-007
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) $ 56,597.2 TEMPORARY OCCUPANCY"*•
Existing Right-of-Way Improvements (B) $ 128,886.7
Future Public Right of Way&Drainage Facilities (C) $ 291,351.1
Private Improvements (D) $ 98,855.2
Calculated Quantity Completed (E) $ -
Total Right-of Way and/or Site Restoration Bond"/"* (A+B) $ 185,483.9
(First$7,500 of bond'shall be cash.)
Performance Bond`Amount (A+B+C+D) = TOTAL (T) $ 575,690.1 T x 0.30 $ 172,707.0 OR
Minimum bon "amount is .
Reduced PerFormance Bond'"Total'`*'` (T-E) $ 575,690.1
Use larger o x3 0 or( -
(B+�)X
Maintenance/Defect Bond*Total 0.25= $ 105,059.4
NAME OF PERSON PREPARING BOND`REDUCTION: Date:
*NOTE: The word"bond"as used in this document means a financial guarantee acceptable to King County.
'*NOTE: KCC 27A authorizes right of way and site restoration bonds to be combined when both are required.
The restoration requirement shall include the total cost for all TESC as a minimum,not a maximum. In addition,corrective work, both on-and off-site needs to be included.
Quantities shall reflect worse case scenarios not just minimum requirements. For example, if a salmonid stream may be damaged, some estimated costs for restoration
needs to be reflected in this amount. The 30%contingency and mobilization costs are computed in this quantity.
"**NOTE: Per KCC 27A,total bond amounts remaining after reduction shall not be less than 30°/o of the original amount(T)or as revised by major design changes.
REQUIRED BOND"AMOUNTS ARE SUBJECT TO REVIEW AND MODIFICATION BY DDES
Page 9 of 9 Unit prices updated: 02/12/02
Check out the DDES Web site at www.kinpcountv.qov/permits Version: 11/26/08
Bond Quantity Worksheet12040.x1sx Report Date: 11/15/2012
APPENDIX "C" OPERATIONS AND MAINTENACE MANUAL
,
ji
O 2012 D. R.STRONG Consulting Engineers Inc. 50 Saddlebrook '
iTechnical Information Report Renton,Washington 'I
APPENDIX A MAINTENAl`TCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,Ai�ID WQ FACILITIES
NO. 1 -DETENTION PONDS
Maintenance Defect or Problem Conditions When Maintenance Is Needed Results Expected When
Component Maintenance Is Performed
Site Trash and debris Any trash and debris which exceed 1 cubic foot Trash and debris cleared from site.
per 1,000 square feet(this is about equal to the
amount of trash it would take to fill up one
standard size office garbage can). In general,
there should be no visual evidence of dumping.
Noxious weeds Any noxious or nuisance vegetation which may Noxious and nuisance vegetation
constitute a hazard to County personnel or the removed according to appiicable
public. regulations. No danger of noxious
vegetation where County personnel
or the public might normally be.
Contaminants and Any evidence of contaminants or pollution such Materials remo�ed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented"rf
appropriate. No contaminants
present other than a surFace oil film.
Grass/groundcover Grass or groundcover exceeds 18 inches in Grass or groundcover mowed to a
height. height no greater than 6 inches.
Top or Side Siopes Rodent holes Any evidence of rodent holes if facility is acting Rodents removed or destroyed and
of Dam,Berm or � as a dam or berm,or any evidence of water dam or berm repaired.
Embankment piping through dam or berm via rodent holes.
Tree growth Tree growth threatens integrity of slopes,does Trees do not hinder facility
not allow maintenance access,or interFeres with performance or maintenance
maintenance activity. If trees are not a threat or activities.
not interfering with access or maintenance,they
do not need to be removed.
Erosion Eroded damage over 2 inches deep where cause Slopes stabilized using appropriate
of damage is still present or where there is erosion control measures. If erosion
potential for continued erosion. Any erosion is occurring on compacted slope,a
observed on a compacted slope. licensed civil engineer should be
consulted to resolve source of
erosion.
Settlement Any part of a dam,berm or embankment that has Top or side slope restored to design
settled 4 inches lower than the design elevation. dimensions. If settlement is
significant,a licensed civil engineer
should be consulted to determine
the cause of the settlement.
Storage Area Sediment Accumulated sediment that exceeds 10%of the Sediment cleaned out to designed
accumulation designed pond depth. pond shape and depth; pond
reseeded if necessary to control
erosion.
Liner damaged Liner is visible or pond does not hold water as Liner repaired or replaced.
(If Applicable) designed.
Inlet/Outlet Pipe. Sediment Sediment filling 20%or more of the pipe. Inlet/outlet pipes clear of sediment.
accumulation
Trash and debris Trash and debris accumulated in inleUoutlet No trash or debris in pipes.
pipes(includes floatables and non-floatables).
Damaged Cracks wider than%rinch at the joint of the No cracks more than'/.-inch wide at
inleUoutlet pipes or any evidence of soil entering the joint of the inletloutiet pipe.
at the joints of the inleUouilet pipes.
Emergency Tree growth Tree growth impedes flow or threatens stability of Trees removed.
Overflow/Spillway spillway.
Rock missing Only one layer of rock exists above native soil in Spiliway restored to design I
area five square feet or larger or any exposure of standards.
native soil on the spiliway.
1/9/2009 2009 Surface Water Design Manual—Appendix A
A-2
APPENDIX A b�AIIvTENANCE REQUIIZEMENTS FOR FLOW CONTROL,CONVEYA��ICE,AND WQ FACILITIES
NO.4-CONTROL STRUCTURE/FLOW RESTRICTOR
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Pertormed
Structure Trash and debris Trash or debris of more than%:cubic foot which No Trash or debris blocking or
is located immediately in front of the structure potentially blocking entrance to
opening or is blocking capacity of the structure by structure.
more than 10%.
Trash or debris in the structure that exceeds'/, No trash or debris in the structure.
the depth from the bottom of basin to invert the
lowest pipe into or out of the basin.
Deposits of garbage exceeding 1 cubic foot in No condition present which would
volume. attract or support the breeding of
insects or rodents.
Sediment Sediment exceeds 60%of the depth from the Sump of structure contains no
bottom of the structure to the invert of the lowest sediment.
pipe into or out of the structure or the bottom of
the FROP-T section or is within 6 inches of the
invert of the lowest pipe into or out of the
structure or the bottom of the FROP-T section.
Damage to frame Corner of frame extends more than'/+inch past Frame is even with curb.
and/or top slab curb face into the street(If applicable).
Top slab has holes larger than 2 square inches or Top slab is free of holes and cracks.
cracks wider than%inch.
Frame not sitting flush on top slab,i.e., Frame is sitting flush on top slab.
separation of more than'/,inch of the frame from
the top slab.
Cracks in walis or Cracks wider than%inch and longer than 3 feet, Structure is sealed and structurally
bottom any evidence of soil particles entering structure sound.
through cracks,or maintenance person judges
that structure is unsound.
Cracks wider than'/:inch and longer than 1 foot No cracks more than'/4 inch wide at
at the joint of any inieUoutlet pipe or any evidence the joint of inlet/outlet pipe.
of soil particles entering structure through cracks.
Settlement/ Strucfure has settled more than 1 inch or has Basin replaced or repaired to design
misalignment rotated more than 2 inches out of alignment. standards.
Damaged pipe joints Cracks wider than'/rinch at the joint of the No cracks more than'/.-inch wide at
inlet/outlet pipes or any evidence of soil entering the joint of inleUoutlet pipes.
the structure at the joint of the inletloutlet pipes.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Ladder rungs missing Ladder is unsafe due to missing rungs, Ladder meets design standards and
or unsafe misalignment, rust,cracks,or sharp edges. allows maintenance person safe
access.
FROP-T Section Damage T section is not securely attached to structure T section securely attached to wall
wall and outlet pipe structure should support at and outlet pipe.
least 1,000 Ibs of up or down pressure.
Structure is not in upright position(allow up to Structure in correct position.
10%from plumb).
Connections to outlet pipe are not watertight or Connections to outlet pipe are water
show signs of deteriorated grout. tight;structure repaired or replaced
and works as designed.
, Any holes—other than designed holes—in the Structure has no holes other than
structure. designed holes.
Cleanout Gate Damaged or missing Cleanout gate is missing. Replace cleanout gate.
2009 Surface Water Design Manual–Appendix A 1/9/2009
A-7
APPENDIX A MAINTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 4-CONTROL STRUCTURElFLOW RESTRICTOR
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Cleanout gate is not watertight. Gate is watertight and works as
designed.
Gate cannot be moved up and down by one Gate moves up and down easily and
maintenance person. is watertight.
Chain/rod leading to gate is missing or damaged. Chain is in place and works as
designed.
Orifice Plate Damaged or missing Control device is not working properly due to Plate is in place and works as
missing,out of place,or bent orifice plate. designed.
Obstructions Any trash,debris,sediment,or vegetation Plate is free of all obstructions and
blocking the plate. works as designed.
Overfiow Pipe Obstructions Any trash or debris blocking(or having the Pipe is free of all obstructions and
potential of blocking)the overflow pipe. works as designed.
Deformed or damaged Lip of overflow pipe is bent or deformed. Overflow pipe does not allow
lip overflow at an elevation lower than
' design
InIeUOutlet Pipe Sediment Sediment filling 20%or more of the pipe. InleUoutlet pipes clear of sediment.
accumulation
Trash and debris Trash and debris accumulated in inleUoutlet No trash or debris in pipes.
pipes(includes floatables and non-floatables).
. Damaged Cracks wider than%:-inch at the joint of the No cracks more than'/<-inch wide at
inleVoutlet pipes or any evidence of soil entering the joint of the inlet/outlet pipe.
at the joints of the inleUoutlet pipes.
Metal Grates llnsafe grate opening Grate with opening wider than'/e inch. Grate opening meets design
(If Applicable) standards.
Trash and debris Trash and debris that is blocking more than 20% Grate free of trash and debris.
of grate surface. footnote to guidelines for disposal
Damaged or missing Grate missing or broken member(s)of the grate. Grate is in place and meets design
standards.
Manhole CoverlLid Covedlid not in place Covedlid is missing or only partially in place. Cover/lid protects opening to
Any open structure requires urgent structure.
maintenance.
Locking mechanism Mechanism cannot be opened by one Mechanism opens with proper tools.
Not Working maintenance person with proper tools.Bolts
cannot be seated. Self-locking covedlid does not
work.
Cover/lid difficult to One maintenance person cannot remove Cover/lid can be removed and '
Remove coverAid after applying 80 Ibs.of lift. reinstalled by one maintenance !
person. I
1/9/2009 2009 Surface��'ater Design nlanual—Appendix A
A-8
I
APPE�iDIX A MAI�ITENANCE REQUIREMENTS FOR FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 5-CATCH BASINS AND MANHOLES
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Structure Sediment Sediment exceeds 60%of the depth from the Sump of catch basin contains no
bottom of the catch basin to the invert of the sediment.
lowest pipe into or out of the catch basin or is
within 6 inches of the invert of the lowest pipe
into or out of the catch basin.
Trash and debris Trash or debris of more than Y:cubic foot which No Trash or debris blocking or
is located immediately in front of the catch basin potentially blocking entrance to
opening or is blocking capacity of the catch basin catch basin.
by more than 10%.
Trash or debris in the catch basin that exceeds No trash or debris in the catch basin.
'/3 the depth from the bottom of basin to invert the
lowest pipe into or out of the basin.
Dead animals or vegetation that could generate No dead animals or vegetation
odors that could cause complaints or dangerous present within catch basin.
gases(e.g.,methane).
Deposits of garbage exceeding 1 cubic foot in No condition present which would
volume. attract or support the breeding of
insects or rodents.
Damage to frame Corner of frame extends more than'/<inch past Frame is even with curb.
and/or top slab curb face into the street(If applicable).
Top slab has holes larger than 2 square inches or Top slab is free of holes and cracks.
cracks wider than%<inch.
Frame not sitting flush on top slab,i.e., Frame is sitting flush on top slab.
separation of more than'/.inch of the frame from
the top slab.
Cracks in walls or Cracks wider than%=inch and longer than 3 feet, Catch basin is sealed and
bottom any evidence of soil particles entering catch structurally sound.
basin through cracks,or maintenance person
judges that catch basin is unsound.
Cracks wider than%:inch and longer than 1 foot No cracks more than'/.inch wide at
at the joint of any inleUoutlet pipe or any evidence the joint of inleUoutlet pipe.
of soil paiticles entering catch basin through
cracks.
Settlement/ Catch basin has settled more than 1 inch or has Basin replaced or repaired to design
misalignment rotated more than 2 inches out of alignment. standards.
Damaged pipe joints Cracks wider than%rinch at the joint of the No cracks more than'/.-inch wide at
inleUoutlet pipes or any evidence of soil entering the joint of inlet/outlet pipes.
the catch basin at the joint of the inieUoutlet
pipes.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Inlet/Outlet Pipe Sediment Sediment filling 20%or more of the pipe. InleUoutlet pipes clear of sediment.
accumulation
Trash and debris Trash and debris accumulated in inleUoutlet No trash or debris in pipes.
pipes(includes floatables and non-floatables).
Damaged Cracks wider than%:-inch at the joint of the No cracks more than'/.-inch wide at
inleUoutlet pipes or any evidence of soil entering the joint of the inleUoutlet pipe.
at the joints of the inleUoutlet pipes.
2009 Surface Water Design Manual—Appendix A 1/9/2009
A-9
APPENDIX A MAINTENAI�TCE REQUIItEMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 5-CATCH BASINS AND MANHOLES
Maintenance Defect or Problem Condition When Maintenance is Needed Resulfs Expected When
Component Maintenance is PerFormed
Metal Grates Unsafe grate opening Grate with opening wider than'/8 inch. Grate opening meets design
(Catch Basins) standards.
Trash and debris Trash and debris that is blocking more than 20% Grate free of trash and debris.
of grate surFace. footnote to guidelines for disposal
Damaged or missing Grate missing or broken member(s)of the grate. Grate is in place and meets design
Any open structure requires urgent standards.
maintenance.
Manhole Cover/Lid Cover/lid not in place Cover/lid is missing or only partially in place. Co�er/lid protects opening to
Any open structure requires urgent structure.
maintenance. �
Locking mechanism Mechanism cannot be opened by one Mechanism opens with proper tools.
Not Working maintenance person with proper tools.Bolts
cannot be seated. Self-locking cover/lid does not
work.
Covedlid difficult to One maintenance person cannot remove Cover/lid can be removed and
Remove coverAid after applying 80 Ibs.of lift. reinstalled by one maintenance
person.
li9%2009 2009 Surface Water Design Manual—Appendix A
A-10
APPENDIX A MAINTENANCE REQUIltEMENTS FOR FLOW C0�ITROL,CONVEYANCE,AND 4VQ FACILITIES
NO. 6-CONVEYANCE PIPES AND DITCHES
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Pipes Sediment&debris Accumulated sediment or debris that exceeds Water flows freely through pipes.
accumulation 20%of the diameter of the pipe.
Vegetation/roots Vegetation/roots that reduce free movement of Water flows freely through pipes.
water through pipes.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Damage to protective Protective coating is damaged;rust or corrosion Pipe repaired or replaced.
coating or corrosion is weakening the structural integrity of any part of
pipe.
Damaged Any dent that decreases the cross section area of Pipe repaired or replaced. ;
pipe by more than 20%or is determined to have ;
weakened structural integrity of the pipe.
Ditches Trash and debris Trash and debris exceeds 1 cubic foot per 1,000 Trash and debris cleared from
square feet of ditch and slopes. ditches. ;
Sediment Accumulated sediment that exceeds 20%of the Ditch cleaned/flushed of all sediment
accumulation design depth. and debris so that it matches design.
Noxious weeds Any noxious or nuisance vegetation which may Noxious and nuisance vegetation
constitute a hazard to Counry personnel or the removed according to applicable
public. regulations. No danger of noxious
vegetation where County personnel
or the public might normally be.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Vegetation Vegetation that reduces free movement of water Water flows freely through ditches.
through ditches.
Erosion damage to Any erosion observed on a ditch slope. Slopes are not eroding.
slopes
Rock lining out of One layer or less of rock exists above native soil Replace rocks to design standards.
place or missing(If area 5 square feet or more,any exposed native
Applicable) soil.
2009 Surface�Vater Design�fanual—Appendi?c A Ii912009
A-11
APPENDIX A �INTENANCE REQUIREMENTS FLOW CONTROL,CONVEYANCE,AND WQ FACILITIES
NO. 7- DEBRIS BARRIERS (E.G., TRASH RACKS)
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed.
Site Trash and debris Trash or debris plugging more than 20%of the Barrier clear to receive capacity flow.
area of the barrier.
Sediment Sediment accumulation of greater than 20%of Barrier clear to receive capacity flow.
accumulation the area of the barrier
Structure Cracked broken or Structure which bars attached to is damaged- Structure barrier attached to is
loose pipe is loose or cracked or concrete structure is sound.
cracked,broken of loose.
Bars Bar spacing Bar spacing exceeds 6 inches. Bars have at most 6 inche spacing.
Damaged or missing Bars are bent out of shape more than 3 inches. Bars in place with no bends more
bars than'/.inch.
Bars are missing or entire barrier missing. Bars in place according to design.
Bars are loose and rust is causing 50% Repair or repiace barrier to design
deterioration to any part of barrier. standards.
,II ,
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i ��
1/9/2009 2009 Surface Vv ater Design:�1anua1—Appendix A
I � A-12
APPENDIX A MAINTEN�'�10E REQUIREMENTS FLOW CONTROL,CONVEYA.�ICE,AND WQ FACILITIES I
NO. 9-FENCING
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Site Erosion or holes Erosion or holes more than 4 inches high and 12- No access under the fence.
under fence 18 inches wide permitting access through an
opening under a fence.
Wood Posts,Boards Missing or damaged Missing or broken boards,post out of plumb by No gaps on fence due to missing or
and Cross Members parts more than 6 inches or cross members broken broken boards,post plumb to within
1'/=inches,cross members sound.
Weakened by rotting Any part showing structural deterioration due to All parts of fence are structurally
or insects rotting or insect damage sound.
Damaged or failed Concrete or metal attachments deteriorated or Post foundation capable of
post foundation unable to support posts. supporting posts even in strong
wind.
Metal Posts,Rails Damaged parts Post out of plumb more than 6 inches. Post plumb to within 1%:inches.
and Fabric
Top rails bent more than 6 inches. Top rail free of bends greater than
1 inch.
Any part of fence(including post,top rails,and Fence is aligned and meets design
fabric)more than 1 foot out of design alignment. standards.
Missing or loose tension wire. Tension wire in place and holding
fabric.
Deteriorated paint or Part or parts that have a rusting or scaling Structurally adequate posts or parts
protective coating condition that has affected structural adequacy. with a uniform protective coating.
Openings in fabric Openings in fabric are such that an 8-inch Fabric mesh openings within 50%of
diameter ball could fit through. grid size.
1/9/2009 2009 Surface Water Design Manual–Appendix A
A-14
I�—
APPENDIX A MAINTENANCE REQUIRER4ENTS FOR FLOW CONTROL,CONVEYANCE,AND��Q FACILITIES
NO. 10-GATES/BOLLARDS/ACCESS BARRIERS
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Chain Link Fencing Damaged or missing Missing gate. Gates in place.
Gate members
Broken or missing hinges such that gate cannot Hinges intact and lubed.Gate is
be easily opened and closed by a maintenance working freely.
person.
Gate is out of plumb more than 6 inches and Gate is aligned and vertical.
more than 1 foot out of design alignment.
Missing stretcher bar,stretcher bands,and ties. Stretcher bar,bands,and ties in
place.
Locking mechanism Locking device missing, no-functioning or does Locking mechanism prevents
does not lock gate not link to ali parts. opening of gate.
Openings in fabric Openings in fabric are such that an 8-inch Fabric mesh openings within 50%of
diameter ball could fit through. grid size.
Bar Gate Damaged or missing Cross bar does not swing open or closed, is Cross bar swings fully open and
' cross bar missing or is bent to where it does not prevent closed and prevents vehicle access.
' vehicle access.
Locking mechanism Locking device missing, no-functioning or does Locking mechanism prevents
does not lock gate not link to all parts. opening of gate.
Support post Support post does not hold cross bar up. Cross bar held up preventing vehicle
damaged access into facility.
Bollards Damaged or missing Bollard broken,missing,does not fit into support No access for motorized vehicles to
hole or hinge broken or missing. get into facility.
Does not lock Locking assembly or lock missing or cannot be No access for motorized vehicles to
attached to lock boliard in place. get into facility.
Boulders Dislodged Boulders not located to prevent motorized vehicle No access for motorized vehicles to
access. get into facility.
Circumvented Motorized vehicles going around or between No access for motorized vehicles to
boulders. get into facility.
2009 Surface Water Design Manual—Appendix A 1/9/2009
�� , A-15
�
APPENDIX A MAINTENANCE REQUIREMENTS FLO�'V CONTROL,CONVEYANCE,AI�]D WQ FACILITIES
NO. 11 -GROUNDS (LANDSCAPING) I,
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When I�
Component Maintenance is PerFormed ',
Site Trash or litter Any trash and debris which exceed 1 cubic foot Trash and debris cleared from site. �'
per 1,000 square feet(this is about equal to the
amount of trash it would take to fill up one
standard size office garbage can). In general,
there should be no visual evidence of dumping.
Noxious weeds Any noxious or nuisance vegetation which may Noxious and nuisance vegetation
constitute a hazard to County personnel or the removed according to applicable
public. regulations. No danger of noxious '
vegetation where County personnel
or the public might normally be.
Contaminants and Any evidence of contaminants or pollution such Materials remo�ed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemenfed if
appropriate. No contaminants
present other than a surface oil film.
Grass/groundcover Grass or groundcover exceeds 18 inches in Grass or groundcover mowed to a
height. height no greater than 6 inches.
Trees and Shrubs Hazard Any tree or limb of a tree identified as having a No hazard trees in facility.
potential to fall and cause property damage or
threaten human life. A hazard tree identified by
a qualified arborist must be removed as soon
as possibie.
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 fhe total of total foliage with split or broken
foliage of the tree or shrub. limbs.
Trees or shrubs that have been blown down or No blown down vegetation or
knocked over. knocked over vegetation. Trees or
shrubs free of injury.
Trees or shrubs which are not adequately Tree or shrub in place and
supported or are leaning over,causing exposure adequately supported;dead or
of the roots. diseased trees removed.
1/9/2009 2009 Surface Water Design Manual—Appendix A
' A-16 '
APPEr�IX A hSA1;�ITEN��ICE REQliIREMENTS FOR FLOW CONTROL,CONVEYA��ICE,��ID WQ FACILITIES
N0. 12-ACCESS ROADS
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Site Trash and debris Trash and debris exceeds 1 cubic foot per 1,000 Roadway drivable by maintenance
square feet(i.e.,trash and debris would fill up vehicles.
one standards size garbage can).
Debris which could damage vehicle tires or Roadway drivable by maintenance
prohibit use of road. vehicles.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Blocked roadway Any obstruction which reduces clearance above Roadway overhead clear to 14 feet
road surface to less than 14 feet. high.
Any obstruction restricting the access to a 10-to At least 12-foot of width on access
12 foot width for a distance of more than 12 feet road.
or any point restricting access to less than a 10
foot width.
Road Surface Erosion,settlement, Any surface defect which hinders or prevents Road drivable by maintenance
potholes,soft spots, maintenance access. vehicles.
ruts
Vegetation on road Trees or other vegetation prevent access to Maintenance vehicles can access
surface facility by maintenance vehicles. facility.
Shoulders and Erosion Erosion within 1 foot of the roadway more than 8 Shoulder free of erosion and
Ditches inches wide and 6 inches deep. matching the surrounding road.
Weeds and brush Weeds and brush exceed 18 inches in height or Weeds and brush cut to 2 inches in
, hinder maintenance access. height or cleared in such a way as to
allow maintenance access.
Modular Grid Contaminants and Any evidence of contaminants or pollution such Materials remo�ed and disposed of
Pavement pollution as oil,gasoline,concrete slurries or paint. according to applicable regulations.
Source control BMPs implemented if
appropriate. No contaminants
present other than a surface oil film.
Damaged or missing Access surface compacted because of broken on Access road surface restored so
missing modular block. road infiltrates.
2009 Surface Water Design Manual—Appendix A 1/9/2009
A-17
APPENDIX A MANI'ENANCE REQUIREMENTS FLO��V CONTROL,CONVEYPu�ICE,AND WQ FACILITIES
NO. 20-SAND FILTER VAULT
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Site Trash and debris Trash and debris accumulated on facility site. Trash and debris removed from
facility site.
Noxious weeds Any noxious or nuisance vegetation which may Noxious and nuisance vegetation
constitute a hazard to County personnel or the removed according to applicable
public. regulations. No danger of noxious
vegetation where County personnel
or the public might normally be.
Contaminants and Any evidence of contaminants or pollution such Materials removed and disposed of
pollution as oii,gasoline,concrete slurries or paint. according to applicable regulations.
Source controi BMPs implemented if
appropriate. No contarninants
present other than a surface oil film.
Grass/groundcover Grass or groundcover exceeds 18 iriches in Grass or groundcover mowed to a
height. height no greater than 6 inches.
Pre-Treatment Sediment Sediment accumulation exceeds the depth of the Sediment storage contains no
Chamber accumulation sedimenf zone plus 6 inches. sediment.
Sand Filter Media Sediment Sediment depth exceeds%-inch on sand filter Sand fiiter freely drains at normal
accumulation media. rate.
Trash and debris Trash and debris accumulated in vault(floatables No trash or debris in vault.
and non-floatables).
Plugging Drawdown of water through the sand filter media, Sand filter media drawdown rate is
takes longer than 24 hours,andlor flow through normal.
the overflow pipes occurs frequently. A sieve
analysis of>4%-100 or>2°/a-200 requires
replacing sand filter media.
Short circuiting Seepage or flow occurs along the vault walls and Sand filter media section re-laid and
corners. Sand eroding near inflow area. compacted along perimeter of vault
Cleanout wyes are not watertight. to form a semi-seal. Erosion
protection added to dissipate force
of incoming flow and curtail erosion.
Vault Structure Damaged to walls, Cracks wider than'/=-inch,any evidence of soil Vault replaced or repaired to provide
frame,bottom and/or entering the structure through cracks or qualified compiete sealing of the structure.
top slab. inspection personnel determines that the vault is
not structurally sound.
Ventilation Ventilation area blocked or plugged. No reduction of ventilation area
exists.
Underdrains and SedimenUdebris Underdrains or clean-outs partialiy plugged,filled Underdrains and clean-outs free of
Cleanouts with sediment and/or debris or not watertight. sediment and debris and sealed.
Inlet/Outlet Pipe Sediment Sediment filling 20%or more of the pipe. InleUoutlet pipes clear of sediment. ��
accumulation
Trash and debris Trash and debris accumulated in inleUoutlet No trash or debris in pipes. !
pipes(includes floatables and non-floatables).
Damaged Cracks wider than'/:-inch at the joint of the No cracks more than'/<-inch wide at
inleUoutiet pipes or any evidence of soil entering the joint of the inleUoutlet pipe.
at the joints of the inlet/outlet pipes. �
1/9/2009 2009 Surface Water Design 14anual—Appendix A
A-28
APPENDIX A MAINTENANCE REQUIREMENTS FOR FLOW CONTROL,CONVEYAi�10E,AND WQ FACILITI
NO. 20-SAND FILTER VAULT
Maintenance Defect or Problem Condition When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Access Manhole Cover/lid not in place Cover/lid is missing or only partially in place. Manhole access covered.
Any open manhole requires immediate
maintenance.
Locking mechanism Mechanism cannot be opened by one Mechanism opens with proper tools.
not working maintenance person with proper tools.Bolts
cannot be seated. Self-locking covedlid does not
work.
Cover/lid difficult to One maintenance person cannot remove Cover/lid can be removed and
remove cover/lid after applying 80 ibs of lift. reinstalled by one maintenance
person.
Ladder rungs unsafe Missing rungs,misalignment,rust,or cracks. Ladder meets design standards.
Allows maintenance person safe
access.
Large access Damaged or difficult Large access doors or plates cannot be Replace or repair access door so it
doorslplate to open openedlremoved using normal equipment. can opened as designed.
Gaps,doesn't cover Large access doors not flat and/or access Doors close flat and covers access
completely opening not completely covered. opening completely.
Lifting Rings missing, Lifting rings not capable of lifting weight of door Lifting rings sufficient to lift or
rusted or plate. remove door or piate.
2009 Surface�Vater Design A�1anua1—Appendix?. 1i9/2009
a-29
APPENDIX A MAIN'TENANCE REQUIl2Er�NTS FOR FLOW CONTROL,CONVEYAI�TCE,AND WQ FACILITIES
NO. 24-CATCH BASIN INSERT
Maintenance Defect or Problem Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Media lnsert Visible Oil �sible oil sheen passing through media Media inset replaced.
insert does not fit Flow gets into catch basin without going through All flow goes through media.
catch basin properly media.
Filter media plugged Filter media plugged. Flow through filter media is normal.
Oil absorbent media Media oil saturated. Oil absorbent media replaced.
saturated
Water saturated Catch basin insert is saturated with water,which insert replaced.
no longer has the capacity to absorb.
Service life exceeded Regular interval replacement due to typical Media replaced at manufacturer's
average Iffe of inedia inseR product,typically one recommended interval.
month.
Seasonal When storms occur and during the wet season. Remove,clean and replace or install
maintenance new insert after major storms,
monthly during the wet season or at
manufacturer's recommended
irterval.
2009 Surface Water Design Manual—Appendix A 1/9/2009
A-3�
I
1
APPENDIX "D" CSWPPP
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O 2012 D. R.STRONG Consulting Engineers Inc. 51 Saddlebrook
Technical Information Report Renton,Washington
STORMWATER POLLUTION PREVENTION PLAN
For
SADDLEBROOK
Prepared For
Northwest Regional Office
3190 160t" Avenue SE
Bellevue, WA 98008-5452
425-649-7000
Owner Developer OperatorlContractor
PNW Holdings, LLC PNW Holdings, LLC Maher A. Joudi, P.E.
9675 SE 36th Street Suite 105 9675 SE 36th Street Suite 105 10604 NE 38th Place, Suite 232
Mercer Island, Washington Mercer Island, Washington Kirkland, Washington 98033
98040 98040
Project Site Location
13426 156th Avenue SE, Renton, Washington
Certified Erosion and Sediment Control Lead
Justin Lagers
253.405.5587
SWPPP Prepared By
D.R. Strong Consulting Engineers, Inc.
10604 NE 38th Place, Suite 232
Kirkland, Washington 98033
Maher A. Joudi, P.E., Senior Project Engineer
SWPPP Preparation Date
November 14, 2012
Approximate Project Construction Dates
Start Date: April 2013
End Date: August 2013
� O 2012 D.R.STRONG Consulting Engineers Inc.
STORMWATER POLLUTION PREVENTION PLAN
TABLE OF CONTENTS I
1.0 INTRODUCTION .......................................................................................................1
2.0 SITE DESCRIPTION .................................................................................................3
2.1 Existing Conditions............................................................................................3
2.2 Proposed Construction Activities.......................................................................3
3.0 CONSTRUCTION STORMWATER BMPS................................................................6
3.1 The 12 BMP Elements.......................................................................................6 �'
3.1.1 Element#1 — Mark Clearing Limits.............................................................6
3.1.2 Element#2 — Establish Construction Access .............................................6
3.1.3 Element#3 — Control Flow Rates...............................................................7
3.1.4 Element#4 — Install Sediment Controls .....................................................7
3.1.5 Element#5 — Stabilize Soils.......................................................................8
3.1.6 Element#6 — Protect Slopes......................................................................9
3.1.7 Element#7 — Protect Drain Inlets.............................................................10
3.1.8 Element#8 — Stabilize Channels and Outlets ..........................................10 '
3.1.9 Element#9 — Control Pollutants...............................................................11
3.1.10 Element#10 — Control Dewatering...........................................................12
3.1.11 Element#11 — Maintain BMPs .................................................................12
3.1.12 Element#12 — Manage the Project ..........................................................12
3.2 Site Specific BMPs..........................................................................................14
3.3 Additional Advanced BMPs .............................................................................14
4.0 CONSTRUCTION PHASING AND BMP IMPLEMENTATION................................15
5.0 POLLUTION PREVENTION TEAM.........................................................................16
5.1 Roles and Responsibilities ..............................................................................16
5.2 Team Members ...............................................................................................16
6.0 SITE INSPECTIONS AND IVIONITORING...............................................................17
6.1 Site Inspection.................................................................................................17
6.1.1 Site Inspection Frequency........................................................................17
6.1.2 Site Inspection Documentation.................................................................17
6.2 Stormwater Quality Monitoring ........................................................................18
6.2.1 Turbidity Sampling .........................................................................................18
6.2.2 pH Sampling ..................................................................................................18
6.2.3 Temperature Monitoring ...........................................................................19
7.0 REPORTING AND RECORDKEEPING ..................................................................20
7.1 Recordkeeping ................................................................................................20
7.1.1 Site Log Book...........................................................................................20
7.1.2 Records Retention....................................................................................20
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7.1.3 Access to Plans and Records...................................................................20
7.1.4 Updating the SWPPP...............................................................................20
7.2 Reporting.........................................................................................................21
7.2.1 Discharge Monitoring Reports..................................................................21
7.2.2 Notification of Noncompliance..................................................................21
7.2.3 Permit Application and Changes ..............................................................21
Appendices
AppendixA— Site Plans ................................................................................................22 I
Appendix B — Construction BMPs..................................................................................23 '
Appendix C —Alternative BMPs.....................................................................................24
AppendixD — General Permit........................................................................................25
Appendix E — Site Inspection Forms (And Site Log) ......................................................26
Appendix F — Engineering Calculations.........................................................................33
Appendix A Site Plans
• Vicinity map (with all discharge points)
• Site plan with TESC measures
Appendix B Construction BMPs
• Possibly reference in BMPs, but likely it will be a consolidated list so that
the applicant can photocopy from the list from the SWMM.
Appendix C Alternative Construction BMP list
• List of BMPs not selected, but can be referenced if needed in each of the
12 elements
Appendix D General Permit
Appendix E Site Log and Inspection Forms
Appendix F Engineering Calculations
• Flows, ponds, etc...
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-�
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` 1 .0 INTRODUCTION
This Stormwater Pollution Prevention Plan (SWPPP) has been prepared as part of the
NPDES stormwater permit requirements for the Saddlebrook residential project located
in Renton, Washington. The site is located at 13426 156th Avenue SE, Renton,
Washington. The proposed development consists of the construction of 14 single-family
dwelling units, roadway improvements, stormwater detention facility, and landscaping
on 4.36 acres.
Construction activities will include, grading, roadway construction, utility installation and
home construction. The purpose of this SWPPP is to describe the proposed
construction activities and all temporary and permanent erosion and sediment control
(TESC) measures, pollution prevention measures, inspection/monitoring activities, and
recordkeeping that will be implemented during the proposed construction project. The
objectives of the SWPPP are to:
1. Implement Best Management Practices (BMPs) to prevent erosion and
sedimentation, and to identify, reduce, eliminate or prevent stormwater
contamination and water pollution from construction activity.
2. Prevent violations of surface water quality, ground water quality, or sediment
management standards.
3. Prevent, during the construction phase, adverse water quality impacts
including impacts on beneficial uses of the receiving water by controlling peak
flow rates and volumes of stormwater runoff at the Permittee's outfalls and
downstream of the outfalls.
This SWPPP was prepared using the Ecology SWPPP Template downloaded from the
Ecology website on July 2, 2005. This SWPPP was prepared based on the
requirements set forth in the Construction Stormwater General Permit, Stormwater
Management Manual for Western Washington (SWMMWW 2005) and in the
Stormwater Management Manual for Eastern Washington (SWMMEW 2004). The
report is divided into seven main sections with several appendices that include
stormwater related reference materials. The topics presented in the each of the main
sections are:
• Section 1 — INTRODUCTION. This section provides a summary
description of the project, and the organization of the SWPPP document.
• Section 2 — SITE DESCRIPTION. This section provides a detailed
description of the existing site conditions, proposed construction activities,
and calculated stormwater flow rates for existing conditions and post—
canstruction conditions.
• Section 3 — CONSTRUCTION BMPs. This section provides a detailed
description of the BMPs to be implemented based on the 12 required
elements of the SWPPP (SWMMEW 2004).
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• Section 4 — CONSTRUCTION PHASING AND BMP IMPLEMENTATION.
This section provides a description of the timing of the BMP
implementation in relation to the project schedule.
• Section 5 — POLLUTION PREVENTION TEAM. This section identifies the
appropriate contact names (emergency and non-emergency), monitoring
personnel, and the onsite temporary erosion and sedimentation control
inspector
• Section 6 — INSPECTION AND MONITORING. This section provides a
description of the inspection and monitoring requirements such as the
parameters of concern to be monitored, sample locations, sample
frequencies, and sampling methods for all stormwater discharge locations
from the site.
• Section 7 — RECORDKEEPING. This section describes the requirements
for documentation of the BMP implementation, site inspections, monitoring
results, and changes to the implementation of certain BMPs due to site
factors experienced during construction.
Supporting documentation and standard forms are provided in the following
Appendices:
Appendix A— Site plans
Appendix B — Construction BMPs
Appendix C —Alternative Construction BMP list
Appendix D — General Permit
Appendix E — Site Log and Inspection Forms
Appendix F — Engineering Calculations
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Stormwater Pollution Prevention Plan Saddlebrook No�ember 14, 2012
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2.0 SITE DESCRIPTION
2.1 Existing Conditions
Total existing Site area is approximately 189,797 s.f. (4.36 ac). Total proposed Project
area is 200,420 s.f. (4.60 ac) which includes 10,623 s.f. (0.24 ac) for the right-of-way
frontage improvements on 156t" and 158th. The Parcels are currently developed with
two single-family residences, out buildings and a gravel driveway. The remainder of the
Site is lawn, landscaping, scattered trees and horse pasture. '
The 4.36 acre parcel is situated atop a ridge and discharges runoff into two subbasins.
TDA West is approximately 1.78 acres and discharges to 156th Avenue SE while TDA
East is comprised of the remaining 2.58 acres and discharges to 158t" Avenue SE. The
discharge elevation of TDA West is approximately six feet lower than that of TDA East.
These two flowpaths converge at a point approximately 3,000 feet downstream of TDA
West and 4,900 feet downstream of TDA East at the corner of 156th Avenue SE and SE
144th Street.
For the purpose of hydrologic calculations, the entire Site is modeled as till forest.
2.2 Proposed Construction Activities
The applicant has gained approval to subdivide 4.36 acres into 14 single-family
residential lots (Project), with lot sizes ranging from approximately 9,400 to 11,734 s.f.
All existing improvements will be demolished or removed during plat construction. The
proposed impervious surface area will include a new subdivision road right-of-way with
26 feet of pavement, vertical curb, gutter, 8-foot planter and a 5-foot sidewalk (53-foot
right of way) as well as offsite half-street improvements along 156t" Avenue SE and
158th Aveneu SE. The proposed right-of-way improvements total approximately 39,130
s.f. The 14 single-family residences and their driveways combined will create
approximately 61,230 s.f. of impervious area (reduced from maximum allowable, see
next paragraph for details). Post-developed impervious areas including rights-of-way,
sidewalks, roofs, dri�eways and site frontage improvements total approximately 110,642
s.f. (includes Bypass area). The remainder of the Project will be modeled as till grass
with the total being approximately 89,733 s.f.
Per the 2009 King County Surface Water Design Manual (Manual), Appendix C, each
lot within a new subdivision is required to mitigate for impervious surface area equal to
10% of the lot area. Per Figure C.1.3.A, Flow Control BMP Flowchart, the Project will
utilize Basic Dispersion with the use of splash blocks. Two splash blocks mitigating a
total of 1,400 s.f. of impervious area, will be installed with each residence. This shall
mitigate for 11.93% to 14.89% of impervious area for each lot, thus accommodating flow
control BMP requirements. Additionally, use of Basic Dispersion allows for a 50% flow
control BMP sizing credit which was used in detention facility calculations. See table
below for lot area, percent impervious mitigated per lot, impervious area used for
detention calculations, and actual allowable impervious area per lot.
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Stor�r��,�;at�r Pc!'��u'�n Pre�����ention Plan
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1 10690 1400 13.10 4811 5511
2 9400 1400 14.89 423Q '-,-' '
3 9400 1400 14.89 4230 -
4 9400 1400 14.89 4230
, 5 9440 1400 14.89 4230
� 6 9400 1400 14.89 4230
7 9400 1400 14.89 4230
8 11734 1400 11.93 5280 �_ _
9 9445 1440 14.82 4250
10 9437 1400 14.84 4247 _ .,
11 9429 1400 14.85 4243 �_+-1�
12 9421 1400 14.86 4239 ���C:
13 9413 1400 14.87 4236 �+'�.
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Two drainage adjustments have been granted to this subdivision (Saddlebrook Plat
Adjustment 2012-03 and Saddlebrook Plat — ADS BayFilter Adjustment 2012-04).
Saddlebrook Plat Adjustment 2012-03 allows the two existing TDAs onsite to combine
runoff into one single drainage facilty. As a condition of this adjustment, the Project
drainage facility is required to adhere to Level 3 Flow Control Criteria. The Project is
required to provide Basic Water Quality treatment and Level 3 Flow Control, per the
2009 KCSWDM (Manual). All surface water runoff from impervious surFaces will be
collected and conveyed to a storm detention pond located in Tract "A. From there, the
water runoff will be conveyed through a BayFilter vault before entering the existing
conveyance system within 156th Avenue SE. The BayFilter adjustment allows the use
of a BayFilter for this project to meet water quality treatment standards.
The following summarizes details regarding site areas:
• Total site developable area: 4.60 acres
• Percent impervious area before construction: 5.6 %
• Percent impervious area after construction: 55.3 %
• Disturbed area during construction: 4.61 acres
• Disturbed area that is characterized as impervious
(i.e., access roads, staging, parking): 0.95 acres
TDA
• 2-year stormwater runoff peak flow prior to construction (existing): 0.128 cfs
• 10-year stormwater runoff peak flow prior to construction (existing): 0.223 cfs
• 2-year stormwater runoff peak ffow during construction: 0.769 cfs
• 10-year stormwater runoff peak flow during construction: 0.928 cfs
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• 2-year stormwater runoff peak flow after construction: 0.076 cfs ,
• 10-year stormwater runoff peak flow after construction: 0.213 cfs
All stormwater flow calculations are provided in Appendix F.
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3.0 CONSTRUCTION STORMWATER BMPS
- 3.1 The 12 BMP Elements
� 3.1.1 Element#1 — Mark Clearing Limits
To protect adjacent properties and to reduce the area of soil exposed to construction,
the limits of construction will be clearly marked before land-disturbing activities begin.
Trees that are to be preserved, as well as all sensitive areas and their buffers, shall be
clearly delineated, both in the field and on the plans. In general, natural vegetation and
; native topsoil shall be retained in an undisturbed state to the maximum extent ossible.
p
! The BMPs relevant to marking the clearing limits that will be applied for this project
include:
• High Visibility Plastic or Metal Fence (BMP C103)
The plastic fence will be placed around the perimeter of the developable area of the
Site. BMP will be implemented at the start of construction.
Alternate BMPs for marking clearing limits are included in Appendix C as a quick
reference tool for the onsite inspector in the event the BMP(s) listed above are deemed
ineffective or inappropriate during construction to satisfy the requirements set forth in
the General NPDES Permit (Appendix D). To avoid potential erosion and sediment
control issues that may cause a violation(s) of the NPDES Construction Stormwater
permit (as provided in Appendix D), the Certified Erosion and Sediment Control Lead
will promptly initiate the implementation of one or more of the alternative BMPs listed in
, Appendix C after the first sign that existing BMPs are ineffective or failing.
�
3.1.2 Element#2 — Establish Construction Access
Construction access or activities occurring on unpaved areas shall be minimized, yet
where necessary, access points shall be stabilized to minimize the tracking of sediment
onto public roads, and wheel washing, street sweeping, and street cleaning shall be
employed to prevent sediment from entering state waters. All wash wastewater shall be
controlled on site. The specific BMPs related to establishing construction access that
will be used on this project include:
'� • Stabilized Construction Entrance (BMP C105)
• Construction Road/Parking Area Stabilization (BMP C107)
A Stabilized Construction Entrance will be placed at the intersection of, the proposed
road, "Road A" and 156t" Avenue SE. This BMP will be implemented at the start of
construction.
Construction Road and Parking Area Stabilization will occur along the road into the site
and in staging areas where parking of equipment will occur. This will occur as the
project goes along.
Alternate construction access BMPs are included in Appendix C as a quick reference
tool for the onsite inspector in the event the BMP(s) listed above are deemed ineffective
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or inappropriate during construction to satisfy the requirements set forth in the General
NPDES Permit (Appendix D). To avoid potential erosion and sediment control issues
that may cause a violation(s) of the NPDES Construction Stormwater permit (as
provided in Appendix D), the Certified Erosion and Sediment Control Lead will promptly
initiate the implementation of one or more of the alternative BMPs listed in Appendix C
after the first sign that existing BMPs are ineffective or failing.
3.1.3 Element#3 — Control Flow Rates
In order to protect the properties and waterways downstream of the project site,
stormwater discharges from the site will be controlled. The specific BMPs for flow
control that shall be used on this project include:
• Detention Pond
A detention pond will be installed in Tract A. The pond will be constructed and used as
a sedimentation device during construction.
Alternate flow control BMPs are included in Appendix C as a quick reference tool for the
onsite inspector in the event the BMP(s) listed above are deemed ineffective or
inappropriate during construction to satisfy the requirements set forth in the General
NPDES Permit (Appendix D). To avoid potential erosion and sediment control issues
that may cause a violation(s) of the NPDES Construction Stormwater permit (as
provided in Appendix D), the Certified Erosion and Sediment Control Lead will promptly
initiate the implementation of one or more of the alternative BMPs listed in Appendix C
after the first sign that existing BMPs are ineffective or failing.
The project site is located west of the Cascade Mountain Crest. As such, the project
must comply with Minimum Requirement 7 (Ecology 2005).
In general, discharge rates of stormwater from the site will be controlled where
increases in impervious area or soil compaction during construction could lead to
downstream erosion, or where necessary to meet local agency stormwater discharge
requirements (e.g. discharge to combined sewer systems).
3.1.4 Element#4— Install Sediment Controls
All stormwater runoff from disturbed areas shall pass through an appropriate sediment
removal BMP before leaving the construction site or prior to being discharged to an
infiltration facility. The specific BMPs to be used for controlling sediment on this project
include:
• Silt Fence (BMP C233)
• Storm Drain Inlet Protection (BMP C220)
• Interceptor Swale (BMP C200)
• Detention Pond
Silt fence will be installed around the perimeter of the Site in areas where runoff could
sheet-flow offsite. This BMP will be installed at the start of construction.
Storm Drain Inlet Protection will be installed on all newly constructed catch basins
throughout the site as well as the existing catch basins in 156th Avenue SE. The
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existing catch basin protection will be installed at the start of construction, and
protection for the newly constructed catch basins will occur as they are installed.
The interceptor swales will be installed during site grading.
The detention pond will be installed and used for sedimentation at the commencement
of construction.
Alternate sediment control BMPs are included in Appendix C as a quick reference tool
for the onsite inspector in the event the BMP(s) listed above are deemed ineffective or
inappropriate during construction to satisfy the requirements set forth in the General
NPDES Permit (Appendix D). To avoid potential erosion and sediment control issues
that may cause a violation(s) of the NPDES Construction Stormwater permit (as
provided in Appendix D), the Certified Erosion and Sediment Control Lead will promptly
initiate the implementation of one or more of the alternative BMPs listed in Appendix C
after the first sign that existing BMPs are ineffective or failing.
In addition, sediment will be removed from paved areas in and adjacent to construction
work areas manually or using mechanical sweepers, as needed, to minimize tracking of
sediments on vehicle tires away from the site and to minimize washoff of sediments
from adjacent streets in runoff.
Whenever possible, sediment laden water shall be discharged into onsite, relatively
level, vegetated areas (BMP C240 paragraph 5, page 4-102).
In some cases, sediment discharge in concentrated runoff can be controlled using
permanent stormwater BMPs (e.g., infiltration swales, ponds, trenches). Sediment
loads can limit the effectiveness of some permanent stormwater BMPs, such as those
used for infiltration or biofiltration; however, those BMPs designed to remove solids by
settling (wet ponds or detention ponds) can be used during the construction phase.
When permanent stormwater BMPs will be used to control sediment discharge during
construction, the structure will be protected from excessive sedimentation with adequate
erosion and sediment control BMPs. Any accumulated sediment shall be removed after
construction is complete and the permanent stormwater BMP will be restabilized with
vegetation per applicable design requirements once the remainder of the site has been
stabilized.
The following BMPs will be implemented as end-of-pipe sediment controls as required
to meet permitted turbidity limits in the site discharge(s). Prior to the implementation of
these technologies, sediment sources and erosion control and soil stabilization BMP
efforts will be maximized to reduce the need for end-of-pipe sedimentation controls.
• Construction Stormwater Filtration (BMP C251)
• Construction Stormwater Chemical Treatment (BMP C 250) (implemented
only with prior written approval from Ecology).
3.1.5 Element#5 — Stabilize Soils
Exposed and unworked soils shall be stabilized with the application of effective BMPs to
prevent erosion throughout the life of the project. The specific BMPs for soil
stabilization that shall be used on this project include:
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• Temporary and Permanent Seeding (BMP C120)
• Plastic Covering (BMP C123)
• Dust Control (BMP C140)
Permanent Seeding will occur as grading is completed. All stabilized sections will be
seeded and vegetated.
Plastic Covering will occur throughout the site as deemed necessary by the contractor
and CESCL.
Dust Control will occur throughout the site as deemed necessary by the contractor and
CESCL.
Alternate soil stabilization BMPs are included in Appendix C as a quick reference tool
for the onsite inspector in the event the BMP(s) listed above are deemed ineffective or
inappropriate during construction to satisfy the requirements set forth in the General
NPDES Permit (Appendix D). To avoid potential erosion and sediment control issues
that may cause a violation(s) of the NPDES Construction Stormwater permit (as
provided in Appendix D), the Certified Erosion and Sediment Control Lead will promptly
initiate the implementation of one or more of the alternative BMPs listed in Appendix C
after the first sign that existing BMPs are ineffective or failing.
The project site is located west of the Cascade Mountain Crest. As such, no soils shall
remain exposed and unworked for more than 7 days during the dry season (May 1 to
September 30) and 2 days during the wet season (October 1 to April 30). Regardless of
the time of year, all soils shall be stabilized at the end of the shift before a holiday or
weekend if needed based on weather forecasts.
In general, cut and fill slopes will be stabilized as soon as possible and soil stockpiles
will be temporarily covered with plastic sheeting. All stockpiled soils shall be stabilized
from erosion, protected with sediment trapping measures, and where possible, be
located away from storm drain inlets, waterways, and drainage channels.
3.1.6 Element#6 — Protect Slopes
All cut and fill slopes will be designed, constructed, and protected in a manner than
minimizes erosion. The following specific BMPs will be used to protect slopes for this
project:
• Temporary and Permanent Seeding (BMP C120)
• Check Dams (BMP C207) I
Permanent Seeding will occur throughout the site as slopes are stabilized. ��
Checks Dams will be installed every 50' as shown on the plan.
Alternate slope protection BMPs are included in Appendix C as a quick reference tool
for the onsite inspector in the event the BMP(s) listed above are deemed ineffective or
inappropriate during construction to satisfy the requirements set forth in the General
NPDES Permit (Appendix D). To avoid potential erosion and sediment control issues
that may cause a violation(s) of the NPDES Construction Stormwater permit (as
provided in Appendix D), the Certified Erosion and Sediment Control Lead will promptly
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initiate the implementation of one or more of the alternative BMPs listed in Appendix C
after the first sign that existing BMPs are ineffective or failing.
3.1.7 Element#7 — Protect Drain Inlets
All storm drain inlets and culverts made operable during construction shall be protected
to prevent unfiltered or untreated water from entering the drainage conveyance system.
However, the first priority is to keep all access roads clean of sediment and keep street
wash water separate from entering storm drains until treatment can be provided. Storm
Drain Inlet Protection (BMP C220) will be implemented for all drainage inlets and
culverts that could potentially be impacted by sediment-laden runoff on and near the
project site. The following inlet protection measures will be applied on this project:
Drop Inlet Protection
• Catch Basin Filters
There are three existing catch basins which will require a filter. The outlet catch basin in
Tract A will require a catch basin filter to be installed while the outfall system is being
constructed for the detention pond.
If the BMP options listed above are deemed ineffective or inappropriate during
construction to satisfy the requirements set forth in the General NPDES Permit
(Appendix D), or if no BMPs are listed above but deemed necessary during
construction, the Certified Erosion and Sediment Control Lead shall implement one or
more of the alternative BMP inlet protection options listed in Appendix C.
3.1.8 Element#8 — Stabilize Channels and Outlets
_ Where site runoff is to be conveyed in channels, or discharged to a stream or some
', other natural drainage point, efforts will be taken to prevent downstream erosion. The
specific BMPs for channel and outlet stabilization that shall be used on this project
include:
• No BMPs implemented
_ The project will not discharge to any outlets or channels; therefore no BMP's are I
required. i�
Alternate channel and outlet stabilization BMPs are included in Appendix C as a quick
reference tool for the onsite inspector in the event the BMP(s) listed above are deemed
ineffective or inappropriate during construction to satisfy the requirements set forth in
the General NPDES Permit (Appendix D). To avoid potential erosion and sediment
control issues that may cause a violation(s) of the NPDES Construction Stormwater
permit (as provided in Appendix D), the Certified Erosion and Sediment Control Lead
will promptly initiate the implementation of one or more of the alternative BMPs listed in
Appendix C after the first sign that existing BMPs are ineffective or failing.
The project site is located west of the Cascade Mountain Crest. As such, all temporary
on-site conveyance channels shall be designed, constructed, and stabilized to prevent
erosion from the expected peak 10 minute velocity of flow from a Type 1A, 10-year, 24-
hour recurrence interval storm for the developed condition. Alternatively, the 10-year, 1-
hour peak flow rate indicated by an approved continuous runoff simulation model,
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5i01f11'uValcf I�OiIUiIOII f fCVcIlIlOII f
increased by a factor of 1.6, shall be used. Stabilization, including armoring mater: . II
adequate to prevent erosion of outlets, adjacent streambanks, slopes, and downstrear��
reaches shall be provided at the outlets of all conveyance systems.
3.1.9 Element#9 — Control Pollutants
All pollutants, including waste materials and demolition debris, that occur onsite shall be �
handled and disposed of in a manner that does not cause contamination of stormwater. �I
Good housekeeping and preventative measures will be taken to ensure that the site will
be kept clean, well-organized, and free of debris. If required, BMPs to be implemented
to control specific sources of pollutants are discussed below.
Vehicles, construction equipment, and/or petroleum product storage/dispensing:
• All vehicles, equipment, and petroleum product storage/dispensing areas
will be inspected regularly to detect any leaks or spills, and to identify
maintenance needs to prevent leaks or spills.
• On-site fueling tanks and petroleum product storage containers shall
include secondary containment.
• Spill prevention measures, such as drip pans, will be used when
conducting maintenance and repair of vehicles or equipment.
• In order to perform emergency repairs on site, temporary plastic will be
placed beneath and, if raining, over the vehicle.
• Contaminated surfaces shall be cleaned immediately following any
discharge or spill incident.
Demolition:
• Dust released from demolished sidewalks, buildings, or structures will be
controlled using Dust Control measures (BMP C140).
• Storm drain inlets vulnerable to stormwater discharge carrying dust, soil,
or debris will be protected using Storm Drain Inlet Protection (BMP C220
as described above for Element 7).
• Process water and slurry resulting from sawcutting and surfacing
operations will be prevented from entering the waters of the State by
implementing Sawcutting and SurFacing Pollution Prevention measures
(BMP C152).
Concrete and grout:
• Process water and slurry resulting from concrete work will be prevented
from entering the waters of the State by implementing Concrete Handling
measures (BMP C151).
Sanitary wastewater:
• Portable sanitation facilities will be firmly secured, regularly maintained,
and emptied when necessary.
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Solid Waste:
�
Othei :
• Other BMPs will be administered as necessary fio address any additional
pollutant sources on site.
The facility does not require a Spill Prevention, Control, and Countermeasure (SPCC)
Plan under the Federal regulations of the Clean Water Act (CWA).
3.1.10 Element#10 — Control Dewatering
There will be no dewatering as part of this construction project.
3.1.11 Element#11 — Maintain BMPs
All temporary and permanent erosion and sediment control BMPs shall be maintained
and repaired as needed to assure continued perFormance of their intended function.
Maintenance and repair shall be conducted in accordance with each particular BMPs
specifications (attached). Visual monitoring of the BMPs will be conducted at least once
every calendar week and within 24 hours of any stormwater or non-stormwater
discharge from the site. If the site becomes inactive, and is temporarily stabilized, the
inspection frequency will be reduced to once every month.
All temporary erosion and sediment control BMPs shall be removed within 30 days after
the final site stabilization is achieved or after the temporary BMPs are no longer
needed. Trapped sediment shall be removed or stabilized on site. Disturbed soil
resulting from removal of BMPs or vegetation shall be permanently stabilized.
3.1.12 Element#12 — Manage the Project
Erosion and sediment control BMPs for this project have been designed based on the
following principles:
• Design the project to fit the existing topography, soils, and drainage
patterns.
• Emphasize erosion control rather than sediment control.
• Minimize the extent and duration of the area exposed.
• Keep runoff velocities low.
• Retain sediment on site.
• Thoroughly monitor site and maintain all ESC measures.
• Schedule major earthwork during the dry season.
In addition, project management will incorporate the key components listed below:
(West Response) As this project site is located west of the Cascade Mountain Crest, the
project will be managed according to the following key project components:
Phasing of Construction
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Stormwater Pollution Prevention Plan
• The construction project is being phased to the extent practicable in order
to prevent soil erosion, and, to the maximum extent possible, the transport
of sediment from the site during construction.
• Revegetation of exposed areas and maintenance of that vegetation shall
, be an integral part of the clearing activities during each phase of
construction, per the Scheduling BMP (C 162).
Seasonal Work Limitations
• From October 1 through April 30, clearing, grading, and other soil
disturbing activities shall only be permitted if shown to the satisfaction of
the local permitting authority that silt-laden runoff will be prevented from
leaving the site through a combination of the following:
o Site conditions including existing vegetative coverage, slope, soil type,
and proximity to receiving waters; and
o Limitations on activities and the extent of disturbed areas; and
o Proposed erosion and sediment control measures.
• Based on the information provided and/or local weather conditions, the
local permitting authority may expand or restrict the seasonal limitation on
site disturbance.
• The following activities are exempt from the seasonal clearing and grading
limitations:
o Routine maintenance and necessary repair of erosion and sediment
control BMPs;
o Routine maintenance of public facilities or existing utility structures that
do not expose the soil or result in the removal of the vegetative cover
to soil; and
o Activities where there is 100 percent infiltration of surFace water runoff
within the site in approved and installed erosion and sediment control
facilities.
, Coordination with Utilities and Other Jurisdictions
• Care has been taken to coordinate with utilities, other construction
projects, and the local jurisdiction in preparing this SWPPP and
scheduling the construction work.
Inspection and Monitoring
• All BMPs shall be inspected, maintained, and repaired as needed to
assure continued performance of their intended function. Site inspections
shall be conducted by a person who is knowledgeable in the principles
and practices of erosion and sediment control. This person has the
necessary skills to:
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
Stormwater Pollution Prevention Plan
o Assess the site conditions and construction activities that could impact
the quality of stormwater, and
o Assess the effectiveness of erosion and sediment control measures
used to control the quality of stormwater discharges. !
• A Certified Erosion and Sediment Control Lead shall be on-site or on-call
at all times.
• Whenever inspection and/or monitoring reveals that the BMPs identified in
this SWPPP are inadequate, due to the actual discharge of or potential to
discharge a significant amount of any pollutant, appropriate BMPs or
design changes shall be implemented as soon as possible.
Maintaining an Updated Construction SWPPP
• This SWPPP shall be retained on-site or within reasonable access to the
site.
• The SWPPP shall be modified whenever there is a change in the design,
construction, operation, or maintenance at the construction site that has,
or could have, a significant effect on the discharge of pollutants to waters
of the state.
• The SWPPP shall be modified if, during inspections or investigations
conducted by the owner/operator, or the applicable local or state
regulatory authority, it is determined that the SWPPP is ineffective in
eliminating or significantly minimizing pollutants in stormwater discharges
from the site. The SWPPP shall be modified as necessary to include
additional or modified BMPs designed to correct problems identified.
Revisions to the SWPPP shall be completed within seven (7) days
following the inspection.
If the BMP(s) listed above are deemed ineffective or inappropriate during construction to
satisfy the requirements set forth in the General NPDES Permit (Appendix D). To avoid
potential erosion and sediment control issues that may cause a violation(s) of the
NPDES Construction Stormwater permit (as provided in Appendix D), the Certified
Erosion and Sediment Control Lead will promptly initiate the implementation of one or
more of the alternative BMPs listed in Appendix C after the first sign that existing BMPs
are ineffective or failing.
3.2 Site Specific BMPs
Site specific BMPs are shown on the TESC Plan Sheets and Details in Appendix A.
These site specific plan sheets will be updated annually.
3.3 Additional Advanced BMPs
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
Stormwater Pollution Prevention Plan
4.0 CONSTRUCTION PHASING AND BMP IIVIPLEMENTATION
The BMP implementation schedule will be driven by the construction schedule. The
following pro�ides a sequential list of the proposed construction schedule milestones
and the corresponding BMP implementation schedule. The list contains key milestones
such as wet season construction.
The BMP implementation schedule listed below is keyed to proposed phases of the
construction project, and reflects differences in BMP installations and inspections that
relate to wet season construction. The project site is located west of the Cascade
Mountain Crest. As such, the dry season is considered to be from May 1 to September
30 and the wet season is considered to be from October 1 to April 30.
• Estimate of Construction start date: 4/2/2013
• Estimate of Construction finish date: 8/1/2013
• Mobilize equipment on site: 4/2/2013
• Mobilize and store all ESC and soil stabilization products: 4/3/2013 - 4/6/2013
• Install ESC measures: 4/3/2013 - 4/10/2013
• Install stabilized construction entrance: 4/3/2013
• Begin clearing and grubbing: 4/11/2013 —4/18/2013
• Demolish existing buildings: 4/11/2013 —4/18/2013
• Begin Site Grading: 4/20/2013
• Begin implementing soil stabilization and
sediment control BMPs throughout the site: 4/19/2013
• End Site Grading: 5/18/2013
• Begin Utility Construction: 5/21/2013
• End Utility Construction: 6/25/2013
• Begin Paving and Sidewalk Installation: 7/2/2013
• Permanent erosion control measures (hydroseeding): 7/24/2013
• End Paving and Sidewalk Installation: 7/23/2013
• Final landscaping and planting begins: 7/24/2013
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Stormwater Pollution Prevention Plan Saddlebrook November 14.2012
Stormwater Pollution Prevention Plan
5.0 POLLUTION PREVENTION TEAM '
5.1 Roles and Responsibilities I
The pollution prevention team consists of personnel responsible for implementation of
the SWPPP, including the following:
• Certified Erosion and Sediment Control Lead (CESCL) — primary
contractor contact, responsible for site inspections (BMPs, visual
monitoring, sampling, etc.); to be called upon in case of failure of any ESC
measures.
• Resident Engineer — For projects with engineered structures only
(sediment ponds/traps, sand filters, etc.): site representative for the owner
that is the project's supervising engineer responsible for inspections and
issuing instructions and drawings to the contractor's site supervisor or
representative
• Emergency Ecology Contact — individual to be contacted at Ecology in
case of emergency
• Emergency Owner Contact — individual that is the site owner or
representative of the site owner to be contacted in the case of an
emergency.
• Non-Emergency Ecology Contact — individual that is the site owner or
representative of the site owner than can be contacted if required.
• Monitoring Personnel — personnel responsible for conducting water quality
monitoring; for most sites this person is also the Certified Erosion and
Sediment Control Lead.
5.2 Team Members
Names and contact information for those identified as members of the pollution
prevention team are provided in the following table.
Title Name(s) Phone Number
Certified Erosion and Sediment Control Justin Lagers 253.405.5587
Lead(CESCL)
Resident Engineer MaherA.Joudi 425.827.3063
Emergency Ecology Contact NW Regional O�ce 425.649.7000
Emergency Owner Contact Justin Lagers 253.405.5587
Non-Emergency Ecology Contact Ken Waldo 425.649.7279
Monitoring Personnel TBD
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Stormurater Pollution Prevention Plan Saddlebrook November 14,2012
Stormwater Pollution Prevention Plan
6.0 SITE INSPECTIONS AND MONITORING
Monitoring includes visual inspection, monitoring for water quality parameters of
concern, and documentation of the inspection and monitoring findings in a site log book.
A site log book will be maintained for all on-site construction activities and will include:
• A record of the implementation of the SWPPP and other permit
requirements;
• Site inspections; and,
• Stormwater quality monitoring.
For convenience, the inspection form and water quality monitoring forms included in this
SWPPP include the required information for the site log book. This SWPPP may
function as the site log book if desired, or the forms may be separated and included in a
separate site log book. However, if separated, the site log book but must be maintained
on-site or within reasonable access to the site and be made available upon request to
Ecology or the local jurisdiction.
6.1 Site Inspection
All BMPs will be inspected, maintained, and repaired as needed to assure continued
performance of their intended function. The inspector will be a Certified Erosion and
Sediment Control Lead (CESCL) per BMP C160. The name and contact information for
the CESCL is provided in Section 5 of this SWPPP.
Site inspection will occur in all areas disturbed by construction activities and at all
stormwater discharge points. Stormwater will be examined for the presence of
suspended sediment, turbidity, discoloration, and oily sheen. The site inspector will
evaluate and document the effectiveness of the installed BMPs and determine if it is
necessary to repair or replace any of the BMPs to improve the quality of stormwater
discharges. All maintenance and repairs will be documented in the site log book or
forms provided in this document. All new BMPs or design changes will be documented
in the SWPPP as soon as possible.
6.1.1 Site Inspection Frequency
Site inspections will be conducted at least once a week and within 24 hours following
any discharge from the site. For sites with temporary stabilization measures, the site
inspection frequency can be reduced to once every month.
6.1.2 Site Inspection Documentation
The site inspector will record each site inspection using the site log inspection forms
provided in Appendix E. The site inspection log forms may be separated from this
SWPPP document, but will be maintained on-site or within reasonable access to the site
and be made available upon request to Ecology or the local jurisdiction.
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
Stormwater Pollution Prevention Plan
6.2 Stormwater Quality Monitoring
The Site will discharge into an existing storm drainage system. 13efore pro�ec��
discharge leaves the Site, it enters a detention pond which outlets into a BayFilter vault
before entering the existing conveyance system located within 156t" Avenue SE. This
will be sufficient in accommodating water quality requirements. Testing at the outlet will
still occur as necessary.
6.2.1 Turbidity Sampling ,
Sampling and monitoring will be conducted during the entire construction phase of the �
project. Samples will be collected daily at the downstream catch basin for both the
pond and vault. If there is no flow in this catch basin, the attempt to sample will be !
recorded in the site log book and reported to Ecology in the monthly Discharge '
Monitoring Report (DMR) as "No Discharge". Samples will be analyzed for turbidity
using the EPA 180.1 analytical method.
The key benchmark turbidity value is 25 nephelometric turbidity units (NTU) for the
downstream receiving water body. If the 25 NTU benchmark is exceeded in any sample
collected from the tested catch basins, the following steps will be conducted:
1. Ensure all BMPs specified in this SWPPP are installed and functioning as
intended.
2. Assess whether additional BMPs should be implemented, and document
modified BMPs in the SWPPP as necessary.
3. Sample discharge daily until the discharge is 25 NTU or lower.
If the turbidity exceeds 250 NTU at any time, the following steps will be conducted:
1. Notify Ecology by phone within 24 hours of analysis (see Section 5.0 of this
SWPPP for contact information).
2. Continue sampling daily until the discharge is 25 NTU or lower Initiate
additional treatment BMPs such as off-site treatment, infiltration, filtration and
chemical treatment within 24 hours, and implement those additional treatment
BMPs as soon as possible, but within a minimum of 7 days.
3. Describe inspection results and remedial actions taken in the site log book
and in monthly discharge monitoring reports as described in Section 7.0 of
this SWPPP.
6.2.2 pH Sampling
Sampling and monitoring for pH will occur during the phase of construction when
concrete pouring will be conducted until fully cured (3 weeks from last pour) and
discharges are documented to be below pH 8.5. Samples will be collected weekly at
the sedimentation pond prior to discharge to surface water. Samples will be analyzed
for pH using a calibrated pH meter and recorded in the site log book.
The key benchmark pH value for stormwater is a maximum of 8.5. If a pH greater than
8.5 is measured in the sedimentation trap/pond(s) that has the potential to discharge to
surface water, the following steps will be conducted:
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
Stormwater Pollution Prevention Plan I
1. Prevent (detain) all discharges from leaving the site and entering surFace
waters or storm drains if the pH is greater than 8.5
2. Implement CO2 sparging or dry ice treatment in accordance with Ecology
BMP C252.
Describe inspection results and remedial actions that are taken in the site log book and
in monthly discharge monitoring reports as described in Section 7.0 of this SWPPP.
6.2.3 Temperature Monitoring
No temperature monitoring is required for this construction site.
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. 1
Stormwater Pollution Prevention Plan
7.0 REPORTING AND RECORDKEEPING
7.1 Recordkeeping
7.1.1 Site Log Book
A site log book will be maintained for all on-site construction activities and will include:
• A record of the implementation of the SWPPP and other permit
requirements;
• Site inspections; and,
• Stormwater quality monitoring.
For convenience, the inspection form and water quality monitoring forms included in this
SWPPP include the required information for the site log book.
7.1.2 Records Retention
Records of all monitoring information (site log book, inspection reports/checklists, etc.),
this Stormwater Pollution Prevention Plan, and any other documentation of compliance
with permit requirements will be retained during the life of the construction project and
for a minimum of three years following the termination of permit coverage in accordance
with permit condition SS.C.
7.1.3 Access to Plans and Records
The SWPPP, General Permit, Notice of Authorization letter, and Site Log Book will be
retained on site or within reasonable access to the site and will be made immediately
available upon request to Ecology or the local jurisdiction. A copy of this SWPPP will be
provided to Ecology within 14 days of receipt of a written request for the SWPPP from
Ecology. Any other information requested by Ecology will be submitted within a
reasonable time. A copy of the SWPPP or access to the SWPPP will be pro�ided to the
public when requested in writing in accordance with permit condition SS.G.
7.1.4 Updating the SWPPP
In accordance with Conditions S3, S4.B, and S9.B.3 of the General Permit, this SWPPP
will be modified if the SWPPP is ineffective in eliminating or significantly minimizing
pollutants in stormwater discharges from the site or there has been a change in design, '
construction, operation, or maintenance at the site that has a significant effect on the '�,
discharge, or potential for discharge, of pollutants to the waters of the State. The �,
SWPPP will be modified within seven days of determination based on inspection(s) that
additional or modified BMPs are necessary to correct problems identified, and an
updated timeline for BMP implementation will be prepared.
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Stormwater Pollution Prevention Plan Saddlebrook November 14, 2012
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Stormwater Pollution Prevention Plan I
7.2 Reporting I
7.2.1 Discharge Monitoring Reports
Water quality sampling results will be submitted to Ecology monthly on Discharge
Monitoring Report (DMR) forms in accordance with permit condition S5.B. If there was
no discharge during a given monitoring period, the form will be submitted with the words
"no discharge" entered in place of the monitoring results. If a benchmark was
exceeded, a brief summary of inspection results and remedial actions taken will be ��
included. If sampling could not be perFormed during a monitoring period, a DMR will be ',
submitted with an explanation of why sampling could not be perFormed.
7.2.2 Notification of Noncompliance
If any of the terms and conditions of the permit are not met, and it causes a threat to
human health or the environment, the following steps will be taken in accordance with
permit section SS.F:
1. Ecology will be immediately notified of the failure to comply.
2. Immediate action will be taken to control the noncompliance issue and to
correct the problem. If applicable, sampling and analysis of any
noncompliance will be repeated immediately and the results submitted to
Ecology within five (5) days of becoming aware of the violation.
3. A detailed written report describing the noncompliance will be submitted to
Ecology within five (5) days, unless requested earlier by Ecology.
Any time turbidity sampling indicates turbidity is 250 nephelometric turbidity units (NTU)
or greater or water transparency is 6 centimeters or less, the Ecology regional office will
be notified by phone within 24 hours of analysis as required by permit condition SS.A
(see Section 5.0 of this SWPPP for contact information).
In accordance with permit condition S4.F.6.b, the Ecology regional office will be notified
if chemical treatment other than CO2 sparging is planned for adjustment of high pH
water (see Section 5.0 of this SWPPP for contact information).
7.2.3 Permit Application and Changes
In accordance with permit condition S2.A, a complete application form will be submitted
to Ecology and the appropriate local jurisdiction (if applicable) to be covered by the
General Permit.
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012 II
Stormwater Pollution Prevention Plan
APPENDIX A - SITE PLANS
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
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APPENDIX B - CONSTRUCTION BMPS
High Visibility Plastic or Metal Fence (BMP C103)
Stabilized Construction Entrance (BMP C105)
Construction Road/Parking Area Stabilization (BMP C107)
Temporary and Permanent Seeding (BMP C120)
Plastic Covering (BMP C123)
Dust Control (BMP C140)
Materials on Hand (BMP C150)
Interceptor Swale (BMP C200)
Check Dams (BMP C207)
Storm Drain Inlet Protection (BMP C220)
Silt Fence (BMP C233)
Detention Pond
1
�2012 D. R. STRONG Consulting Engineers Inc. Page 23 of 44
Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
Stormwater Pollution Prevention Plan
APPENDIX C - ALTERNATIVE BMPS
The following includes a list of possible alternative BMPs for each of the 12 elements
not described in the main SWPPP text. This list can be referenced in the event a BMP
for a specific element is not functioning as designed and an alternative BMP needs to
be implemented.
None Proposed
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Stormwater Pollution Pre�ention Plan Saddlebrook November 14,2012
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APPENDIX D - GENERAL PERMIT I'
� !
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
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i
APPENDIX E - SITE INSPECTION FORMS (AND SITE LOG)
The results of each inspection shall be summarized in an inspection report or checklist �
that is entered into or attached to the site log book. It is suggested that the inspection
report or checklist be included in this appendix to keep monitoring and inspection I
information in one document, but this is optional. However, it is mandatory that this
SWPPP and the site inspection forms be kept onsite at all times during construction,
and that inspections be performed and documented as outlined below.
At a minimum, each inspection report or checklist shall include:
a. Inspection date/times
b. Weather information: general conditions during inspection, approximate
amount of precipitation since the last inspection, and approximate amount
of precipitation within the last 24 hours.
c. A summary or list of all BMPs that have been implemented, including
observations of all erosion/sediment control structures or practices.
d. The following shall be noted:
i. locations of BMPs inspected,
ii. locations of BMPs that need maintenance,
iii. the reason maintenance is needed,
Miv. locations of BMPs that failed to operate as designed or intended, and
v. locations where additional or different BMPs are needed, and the
reason(s) why
e. A description of stormwater discharged from the site. The presence of
suspended sediment, turbid water, discoloration, and/or oil sheen shall be
noted, as applicable.
f. A description of any water quality monitoring performed during inspection,
and the results of that monitoring.
g. General comments and notes, including a brief description of any BMP
repairs, maintenance or installations made as a result of the inspection.
h. A statement that, in the judgment of the person conducting the site ;
inspection, the site is either in compliance or out of compliance with the I
terms and conditions of the SWPPP and the NPDES permit. If the site
inspection indicates that the site is out of compliance, the inspection report
shall include a summary of the remedial actions required to bring the site
back into compliance, as well as a schedule of implementation.
i. Name, title, and signature of person conducting the site inspection; and
the following statement: "I certify under penalty of law that this report is
true, accurate, and complete, to the best of my knowledge and belief'.
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I
When the site inspection indicates that the site is not in compliance with any terms and
conditions of the NPDES permit, the Permittee shall take immediate action(s) to: stop,
contain, and clean up the unauthorized discharges, or otherwise stop the
noncompliance; correct the problem(s); implement appropriate Best Management
Practices (BMPs), and/or conduct maintenance of existing BMPs; and achieve
compliance with all applicable standards and permit conditions. In addition, if the
noncompliance causes a threat to human health or the environment, the Permittee shall
comply with the Noncompliance Notification requirements in Special Condition S5.F of
the permit.
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2o12
SITE INSPECTION FORM
General Information
Project Name:
Inspector Name: Titie:
CESCL# :
Date: Time:
Inspection Type: ❑ After a rain event
❑ Weekly
❑ Turbidity/transparency benchmark exceedance
❑ Other
Weather
Precipitation Since last inspection In last 24 hours
Description of General Site Conditions:
Inspection of BMPs
Element 1: Mark Clearing Limits
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
�
BMP:
Inspected Functioning
Location Y N Y N NIP ProblemlCorrective Action
Element 2: Establish Construction Access
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
Element 3: Contro!Flow Rares
BMP:
Location Inspected Functioning Problem/Corrective Action
Y N Y N NIP
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Stormavater Pollution Prevention Plan Saddlebrook November 14,2012
BMP:
Location Inspected Functioning ProblemlCorrective Action
Y N Y N NIP
Element 4: lnstall Sediment Controls
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
�
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
Element 5: Stabilize Soils
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP ProblemlCorrective Action
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
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BMP:
Location Inspected Functioning Problem/Corrective Action
Y N Y N NIP
BMP:
Inspected Functioning '
Location Y N Y N NIP Problem/Corrective Action
Element 6: Protect Slopes
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
Element 7: Profect Drain Inlets
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
�
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
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Element 8: Stabilize Channels and Outlets
BMP:
Inspected Functioning
Location Y N Y N NIP ProblemJCorrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
Element 9: Control Pollutants
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP: I
Location Inspected Functioning Problem/Corrective Action
Y N Y N NIP
Element 10: Contro!Dewatering
BMP:
Location Inspected Functioning Problem/Corrective Action
Y N Y N NIP
BMP:
Location Inspected Functioning Problem/Corrective Action
Y N Y N NIP
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
Stormwater Discharges From the Site �
Observed? Problem/Corrective Action
Y �N
Location
Turbidity
Discoloration
Sheen
Location
Turbidity
Discoloration
Sheen
Water Quality Monitoring
Was any water quality monitoring conducted? ❑ Yes ❑ No
If water quality monitoring was conducted, record results here:
If water quality monitoring indicated turbidity 250 NTU or greater; or transparency 6 cm or less,
was Ecology notified by phone within 24 hrs?
❑ Yes ❑ No
If Ecology was notified, indicate the date, time, contact name and phone number below:
Date:
Time:
Contact Name:
Phone#:
General Comments and Notes
Include BMP repairs, maintenance, or installations made as a result of the inspection.
Were Photos Taken? ❑ Yes ❑ No
If photos taken, describe photos below:
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
APPENDIX F - ENGINEERING CALCULATIONS
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
EXISTING SITE HYDROLOGY
For the purpose of these calculations the predeveloped site conditions were modeled as
"till forest".
Modeling input '
Land cover Entire
Site
Till forest(ac) 4.601
Till Grass (ac) 0.000
Wetland (ac) 0.000
Impervious (ac) 0.000
Scale Factor: 1.00
Time Step: Hourly
Data Type: Reduced
Project location: Seatac
Total Area: 4.601
Table 1 Pre-Developed KCRTS Modeling Input
Modeling results
Entire Site
� Flow Frequer.cy Analysis
Time Series File:predev.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
0.290 2 2/09/Ol 18:00 0.371 1 100.00 0.990
0.079 7 1/06/02 3:00 0.290 2 25.00 0.960
0.215 4 2/28/03 3:00 0.223 3 10.00 0. 900
0.007 8 3/24/04 20:00 0.215 4 5.00 0.800
0.128 6 1/05/05 8:00 0.188 5 3.00 0.667
0.223 3 1/18/06 21:00 0.128 6 2. 00 0.500
0.188 5 11/24/06 4:00 0.079 7 1.30 0.231
0.371 1 1/09/08 9:00 0.007 8 1.10 0.091
Computed Peaks 0.344 50.00 0.980
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Stormwater Pollution Prevention Plan Saddlebrook November 14, 2012 �
DEVELOPED SITE HYDROLOGY
Soil type
The soil types are unchanged from pre-developed conditions.
Land covers
KCRTS was used to model the developed peak runoff from the Site. The portions of the
Site within the proposed clearing limits tributary to the proposed detention pond were
modeled as "Till Grass" and Impervious as appropriate. Results of the KCRTS analysis
are included in this section.
Modeling input
Land cover Entire
Site �
Till forest(ac) 0.000
Till Grass (ac) 1.956
Wetland (ac) 0.000
Impervious (ac) 2.452
Scale Factor: 1.00
Time Step: Hourly
Data Type: Reduced
Project location: Seatac
Total Area: 4.408
Table 2 Developed KCRTS Modeling Input
Modeling Results
Entire Site
F1ow Frequency Analysis
Time Series File:rdin.tsf
aroject Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flos� Rate Rank Time of Peak - - Peaks - - Rank Return Prob
;CrS) (CFS) Period
0.769 6 2/09/O1 2:00 1.57 1 100.00 0.990
0. 613 S 1/05/02 16:00 0.940 2 25.00 0.960
0. 928 3 2/27/03 7:00 0. 928 3 10.00 0.900
C . 647 7 8/26/04 2:00 0.815 4 5.00 0.800
C.783 5 10/28/04 16:00 0.783 5 3.00 0.667
C.815 4 1/18/06 16:00 0.769 6 2.00 0.500
0. 940 2 10/26/06 0:00 0. 647 7 1.30 0.231
1.57 1 1/09/08 6:00 0. 613 8 1.10 0.091
Ccmp�:ted Feaks 1.36 50.00 0. 980
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
BYPASS AREA HYDROLOGY
Modeling Input
Land cover Entire
Site
Till forest(ac) 0.000
Till Grass (ac) 0.103
Wetland (ac) 0.000
Impervious (ac) 0.090
Scale Factor: 1.00
Time Step: Hourly
Data Type: Reduced
Project location: Seatac '�,
Total Area: 0.193 '
Table 3 Bypass KCRTS Modeling Input
Modeling Results
Bypass
Flow Frequency Analysis
Tirte Series File:bypass.tsf
Prcject Location:Sea-Tac
---Annual Peak Flow Rates--- -----F1ow Frequency Analysis-------
�=ow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.031 5 2/09/O1 2:00 0.064 1 100.00 0.990
0.024 8 1/05/02 16:00 0.037 2 25.00 0. 960
0.037 2 2/27/03 7:00 0.036 3 10.00 0. 900
0.025 7 8/26/04 2:00 0.033 4 5.00 0.800
0. 030 6 10/28/04 16:00 0.031 5 3.00 0.667
0. 033 4 1/18/06 16:00 0.030 6 2.00 0.500
0. 036 3 10/26/06 0:00 0.025 7 1.30 0.231
0.064 1 1/09/08 6:00 0.024 8 1.10 0.091
Co_�.�uted Peaks 0.055 50.00 0.980
The on-site bypass areas satisfy all the requirements set forth in the Manual, Section
1.2. Runoff from the bypass areas and the flow control facilities converge within a
quarter-mile. The flow control facility is designed to compensate for uncontrolled
bypass. The 100-year discharge from the bypass areas is 0.064 cfs, which is less than
the 0.4 cfs threshold. There should be no adverse downstream impacts to the
downstream drainage system created by the runoff from the bypass.
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Stormwater Pollution Pre�ention Plan Saddlebrook November 14,2012
FLOW CONTROL SYSTEM
The Project will utilize a detention pond meeting the Level Three Flow Control criteria.
This King County KCRTS software was used to size the detention facilities.
Flow Control Facility Design Output
Retention/D2tention Facility
Type of Facility: Detention Fcnd
Side 51ope: 3.00 H: 1C'
Pond Bottom Length: 98.29 ft
Pond Bottom Width: 49.15 ft
Pond Bottom Area: 4831. sq. ft
Top Area at 1 ft. FB: 13490. sq. ft
0.310 Gc�es
Effective Storage Depth: 6.50 ft
Stage 0 Elevation: 489.00 ft
Storage Volume: 53382. cu. �^t
1.225 ac-=t
Riser Head: 6.50 ft
Riser Diameter: 18.00 inches
Number of orifices: 3
Full Head Pic=
Orifice � Height Diameter Discharge Diameter
(ft) (in) (CFS) (inj
1 0.00 1.03 0.073
2 4.74 2.27 0.185 6.0
3 6.00 2.09 0.084 6.0
� Top Notch Weir: None
Outflow Rating Curve: None
Stage Elevation Storage Discharge Percolation Surf Area
(ft) (ft) (cu. ft) (ac-ft) (cfs) (c=s) (sq. ft)
0.00 489.00 0. 0.000 0.000 0.00 4831.
0.01 489.01 48. 0.001 0.003 0.00 4839.
0.02 489.02 97. 0.002 0.004 0.00 4848.
0.03 489.03 145. 0.003 0.005 0. 00 4857.
0.04 489.04 194. 0.004 0.006 0.00 4866.
0.05 489.05 243. 0.006 0.007 0.00 4875.
0.06 489.06 291. 0.007 0.007 0.00 4884.
0. 07 489.07 340. 0.008 0.008 0.00 4893.
0.09 489.09 438. 0.010 0.008 0.00 4911.
0.21 489.21 1034. 0.024 0.013 0.00 5018.
0.34 489.34 1694. 0.039 0.017 0.00 5136.
0.47 489.47 2369. 0.054 0.020 0.00 5254.
0.60 489.60 3060. 0.070 0.022 0.00 5374.
0.72 489.72 3712. 0.085 0.024 0.00 5486.
0.85 489.85 4433. 0.102 0.026 0.00 5609.
0.98 489.98 5170. 0.119 0.028 0.00 5732.
1.11 490.11 5923. 0.136 0.030 0.00 5857.
1.23 490.23 6633. 0.152 0.032 0.00 5973.
1.36 490.36 7418. 0.170 0.033 0.00 6100.
1.49 490.49 8219. 0.189 0.035 0.00 6229.
1.62 490.62 9038. 0.207 0.036 0.00 6358.
1.74 490.74 9808. 0.225 0.038 0.00 6479.
1.87 490.87 10658. 0.245 0.039 0.00 6611.
2.00 491.00 11527. 0.265 0.040 0.00 6744.
2. 12 491.12 12393. 0.2�3 O.Q^-_2 0.00 5R6g,
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
2.25 491.25 13245. 0.304 0.043 0.00 7003.
2.38 491.38 14164. 0.325 0.044 0.00 7140.
2.51 991.51 15101. 0.347 0.045 0.00 7278.
2.63 491.63 15982. 0.367 0.046 0.00 7406.
2.76 491.76 16954. 0.389 0.048 0.00 7546.
2.89 491.89 17944. 0.412 0.049 0.00 7688.
3.02 492.02 18953. 0.435 0.050 0.00 7831.
3.14 492.14 19901. 0.457 0.051 0.00 7963. i
3.27 492.27 20945. 0.481 0.052 0.00 8108. '
3.40 492.40 22009. 0.505 0.053 0.00 8255.
3.53 492.53 23092. 0.530 0.054 0.00 8402.
3.65 492.55 24108. 0.553 0.055 0.00 8539.
3.78 492.78 25228. 0.579 0.056 0.00 8689.
3.91 492.91 26367. 0.605 0.057 0.00 8840.
4.04 493.04 27526. 0.632 0.058 0.00 8992.
4.16 493.16 28614. 0.657 0.058 0.00 9134.
�.29 493.29 29811. 0.684 0.059 0.00 9288.
4.42 493.42 31029. 0.712 0.060 0.00 9494.
4.55 493.55 32267. 0.741 0.061 0.00 9601.
4. 67 493.67 33428. 0.767 0.062 0.00 9747.
4.74 493.74 34113. 0.783 0.062 0.00 9833.
4.76 493.76 34310. 0.788 0.064 0.00 9857.
4.79 493.79 39606. 0.794 0.068 0.00 9894.
9.81 493.81 34804. 0.799 0.075 0.00 9919.
4. �3 493.83 35003. 0.804 0.084 0.00 9943.
4.86 493.86 35302. 0.810 0.095 0.00 9980.
4.88 493.88 35501. 0.815 0.109 0.00 10005.
4.91 493.91 35802. 0.822 0.120 0.00 10092.
-^_.93 493.93 36003. 0.827 0.124 0.00 10067.
�.95 493.95 36205. 0.831 0.128 0.00 10092.
�.C8 494.08 37527. 0.862 0.146 0.00 10254.
5.21 494.21 38671. 0.892 0.161 0.00 10417.
�.33 494.33 40130. 0.921 0.174 0.00 10568.
5.46 494.46 41515. 0.953 0.185 0.00 10734.
5.59 494.59 42921. 0.985 0.196 0.00 10901.
5.72 494.72 44349. 1.018 0.206 0.00 11069.
5.�4 494.84 45686. 1.049 0.216 0.00 11225.
5. 97 494.97 47157. 1.083 0.225 0.00 11395.
0'.00 495.00 47499. 1.090 0.227 0.00 11434.
0.02 495.02 97728. 1.096 0.229 0.00 11461.
6.04 495.04 97958. 1.101 0.234 0.00 11487.
�.07 495.07 48303. 1.109 0.241 0.00 11527 .
6.G9 495.09 48534. 1.114 0.250 0.00 11553.
6. 11 495.11 48765. 1.119 0.261 0.00 11580.
6. 13 495.13 48997. 1.125 0.274 0.00 11606.
6. 15 495.15 49229. 1.130 0.283 0.00 11633.
F. 17 495.17 49462. 1.135 0.287 0.00 11659.
E.30 495.30 50989. 1.171 0.311 0.00 11833.
6.43 495.43 52539. 1.206 0.331 0.00 12007.
6.50 495.50 53382. 1.225 0.342 0.00 12102.
6.60 995.60 59599. 1.253 0.817 0.00 12237.
6.70 995.70 55830. 1.282 1.670 0.00 12374.
6.80 495.80 57074. 1.310 2.780 0.00 12511.
6.90 495.90 58332. 1.339 4.090 0.00 12649.
7.00 496.00 59604. 1.368 5.570 0.00 12787.
7.10 496.10 60889. 1.398 7.010 0.00 12926.
7.20 496.20 62189. 1.428 7.540 0.00 13066.
7.30 496.30 63503. 1.458 8.050 0.00 13207.
7.40 496.40 64830. 1.488 8.520 0.00 13348.
7.50 496.50 66172. 1.519 8.960 0.00 1349D.
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
7.60 496.60 67529. 1.550 9.390 0.00 13633.
7.70 496.70 68899. 1.582 9.800 0.00 13777.
7.80 496.80 70284. 1.613 10.180 0.00 13921.
7.90 496.90 71683. 1.646 10.560 0.00 14066.
8.00 497.00 73097. 1.678 10.920 0.00 14212.
8.10 497.10 74526. 1.711 11.270 0.00 14358. �,
8.20 497.20 75969. 1.744 11.610 0.00 14505. �i
8.30 497.30 77427. 1.777 11.940 0.00 14653. I
8.40 497.40 78899. 1.811 12.260 0.00 14802.
8.50 497.50 80387. 1.845 12.580 0.00 14951. I
Hyd Inflow Outflow Peak Storage I�I
Stage Elev (Cu-Ft) (Ac-Ft) �
1 1.57 0.34 6.50 495.50 53383. 1.226
2 0.77 0.27 6.12 495.12 48858. 1.122
3 0.93 0.20 5.69 494.69 44050. 1.011
4 0.94 0.19 5.50 494.50 41929. 0. 963
5 0.82 0.11 4.88 493.88 35479. 0.814
6 0.51 0.06 9.46 493.46 31450. 0.722
7 0.61 0.06 3.92 492.92 26498. 0. 608
8 0.65 0.05 2.80 491.80 17247. 0.396
Hyd R/D Facility Tributary Reservoir POC Outflow
Outflow Inflow Inflow Target Calc
_ 0.34 0.06 ******** 0.37 0.36
2 0.27 0.03 ******** ******* 0.28
3 0.20 0.04 ******** ******* 0.21
� 0. 19 0.04 ******** ******* 0.20
5 0.11 0.03 ******** ******* 0.11
6 0.06 0.02 ******** ******* 0.07 '�
7 0.06 0.02 ******** ******* 0.07
8 0. 05 0.02 *x****** x**x*** G.07
----------------------------------
R.oute Tir„e Series thrcagh �aci�i�y
�nflow Time Series File:rdin.tsf
Outflow Time Series File:rdout
POC Time Series File:dsout
In=1c��r/Outflow Analysis
Feak Inflow Discharge: 1.57 CFS at 6:00 on Jan 9 in Year 8 '
Fe�k Outflow Discharge: 0.344 CFS at 12:00 on Jan 9 in Year 8
Feak Reservoir Stage: 6.50 Ft
Peak Reservoir Elev: 495.50 Ft
Pea'.� Reservoir Storage: 53383. Cu-Ft
. 1.226 Ac-rt
Add Time Series:bypass.tsf
Peak Summed Discharge: 0.3�7 CFS at 12:G0 on Jan 9 in Year 8 �
Foint of Compliance File:dsout.tsf
F1ow Frequency Analysis
Time Series File:rdout.rsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Ara��ysis-------
�1ow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
{CFS) (CFS) (ft) Period
0.266 2 2/09/Ol 20:00 0.344 6.50 1 100.00 0.990
0.057 7 1/07/02 4:00 0.266 6.12 2 25.00 0.960
0.20^ 3 3/05/03 22:00 0.20� 5. 69 3 1�.00 0. 90�
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Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
0.048 8 8/26/04 7:00 0.188 5.50 4 5.00 0.800
0.060 6 1/08/05 5:00 0.107 4.88 5 3.00 0.667
0.107 5 1/19/06 3:00 0.060 4.46 6 2.00 0.500
0.188 4 11/24/06 8:00 0.057 3.92 7 1.30 0.231
0.344 1 1/09/08 12:00 0.048 2.80 8 1.10 0.091
Computed Peaks 0.318 6.35 50.00 0.980
Flow Frequency Analysis
Time Series File:dsout.tsf
Project Location:Sea-Tac
---Annual Peak F1ow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.278 2 2/09/O1 20:00 0.357 1 100.00 0.990
0.072 7 1/05/02 16:00 0.278 2 25.00 0.960
0.213 3 3/06/03 20:00 0.213 3 10.00 0.900
0.068 8 8/26/04 2:00 0.198 4 5.00 0.800
0.072 6 1/05/05 8:00 0.113 5 3.00 0.667
0.113 5 1/19/06 3:00 0.072 6 2.00 0.500
0.198 4 11/24/06 7:00 0.072 7 1.30 0.231
0.357 1 1/09/08 12:00 0.068 8 1.10 0.091
Computed Peaks 0.331 50.00 0.980
Flow Duration from Time Series File:rdout.tsf
Cutoff Count Frequency CDF Exceedence Probab-lity
CFS � s %
0.004 32796 53.483 53.483 46.517 0.465E+00
0.011 6148 10.026 63.509 36.491 0.365E+00
0.019 4821 7.862 71.371 28.629 0.286E+00
0.026 5268 8.591 79.962 20.038 0.200E+00
0.034 4349 7.092 87.05� 12.945 0.129E+00
0.041 3152 5.140 92.195 7.805 0.780E-01
0.049 1871 3.051 95.246 4.754 0.475E-01
0.056 1556 2.538 97.784 2.216 0.222E-01
0.064 1042 1.099 99.483 0.517 0.517E-02
0.071 54 0.088 99.571 0.429 0.429E-02
0.078 29 0.047 99.618 0.382 0.382E-02
0.086 17 0.028 9°.646 0.354 0.354E-02
- 0.093 17 0.028 99.674 0.326 0.326E-02
0.101 11 0.018 99.692 0.308 0.308E-02
0.108 15 0.024 99.716 0.284 0.284E-02
0.116 9 0.015 99.731 0.269 0.269E-02
0.123 7 0.011 99.742 0.258 0.258E-02
0.131 23 0.038 99.780 0.220 0.220E-02
I 0.138 14 0.023 99.803 0.197 0.197E-02
0.146 14 0.023 99.826 0.174 0.174E-02
0.153 9 0.015 99.840 0.160 0.160E-02
, 0.161 8 0.013 99.853 0.147 0.147E-02
0.168 13 0.021 99.874 0.126 0.126E-02
0.176 10 0.016 99.891 0.109 0.109E-02
0.183 11 0.018 99.909 0.091 0.913E-G3
0.191 11 0.018 99.927 0.073 0.734E-03
0.198 10 0.016 99.943 0.057 0.571E-03
0.205 14 0.023 99.966 0.034 0.342E-03
0.213 5 0.008 99.974 0.026 0.261E-03
0.220 4 0.007 99.980 0.020 0.196E-03
0.228 5 0.008 99.989 0.011 0.114E-03
0.235 2 0.003 99.992 0.008 0.815E-04
0.243 1 0.002 99.993 0.007 0.652E-04
0.250 1 0.002 99.995 0.005 0.489E-04
O 2012 D. R.STRONG Consufting Engineers Inc. Page 40 of 44
Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
0.258 1 0.002 99.997 0.003 0.326E-C=
0.265 1 0.002 99.998 0.002 0.163E-C�
Flow Duration from Time Series File:dsout.tsf
Cutoff Count Frequency CDF Exceedence Probabilit��
CFS o $ $
0.004 32785 53.465 53.465 46.535 0.465E+C0
0.012 6183 10.083 63.599 36.451 0.365E+C0
0.020 4885 7.966 71.515 28.485 0.285E+00
0.027 5255 8.570 80.085 19.915 0.199E+Q0
0.035 4253 6.936 87.021 12.979 0.130E+00
0_093 3171 5_171 92.192 7.808 0.781E-0_
0.051 1952 3.183 95.375 4.625 0.462E-Oi
0.058 1473 2.402 97.777 2.223 0.222E-01
0.066 943 1.538 99.315 0.685 0.685E-02
0.074 123 0.201 99.516 0.484 0.484E-02
0.082 53 0.086 99.602 0.398 0.398E-02
0.090 25 0.041 99.693 0.357 0.357E-02
0.097 17 0.028 99.671 0.329 0.329E-02
0.105 14 0.023 99.693 0.307 0.307E-C2
0.113 13 0.021 99.715 0.285 0.285E-C2
0.121 8 0.013 99.728 0.272 0.272E-C2
0.129 13 0.021 99.749 0.251 0.251E-02
0.136 18 0.029 99.778 0.222 0.222E-C2
0.144 16 0.026 99.804 0.196 0.196E-C2
0.152 14 0.023 99.827 0.173 0.173E-C2
0.160 7 0.011 99.839 0.161 0.161E-C2
0.168 9 0.015 99.853 0.147 0.147E-C2
0.175 13 0.021 99.874 0.126 0.126E-C2
� 0.183 10 0.016 99.891 0.109 0.109E-02
0.191 11 0.018 99.909 0.091 0.913E-03
0.199 12 0.020 99.928 0.072 0.718E-03
0.206 9 0.015 99.943 0.057 0.571E-03
0.214 14 0.023 99.966 0.034 0.392E-03
0.222 6 0.010 99.976 0.024 0.245E-03
0.230 3 0.005 99.980 0.020 0.196E-03
0.238 4 0.007 99.987 0.013 0.130E-03
0.245 2 0.003 99.990 0.010 0.978E-04
0.253 2 0.003 99.993 0.007 0.652E-04
0.261 1 0.002 99.995 0.005 0.489E-04
0.269 1 0.002 99.997 0.003 0.32'0E-��
0.277 1 0.002 :?. �?8 �.0�2 �."�03E-�4
Duration Comparison Anayls'_s
Base File: predev.tsr"
New File: dsout.ts�
Cutoff Units: Discharge in CFS
-----Fraction of Time----- ---------�heck of Tolerance-------
Cutoff Base New $Change Probability Base New $Chance
0.064 � 0.95E-02 0.88E-02 -8.0 I 0.95E-02 0.064 0.063 -0.5
0.081 I 0.63E-02 0.40E-02 -36.3 I 0.63E-02 0.081 0.067 -16.9
0.098 � 0.50E-02 0.33E-02 -34.2 I 0.50E-02 0.098 0.073 -25.7
0.116 I 0.37E-02 0.28E-02 -25.1 I 0.37E-02 0.116 0.086 -25.4
0.133 I 0.29E-02 0.23E-02 -18.3 I 0.29E-02 0.133 0.113 -15.1
0.151 I 0.22E-02 0.17E-02 -21.3 I 0.22E-02 0.151 0.136 -9.7
0.168 I 0.15E-02 0.15E-02 -1.1 I 0.15E-02 0.168 0.168 -C.3
0.185 I O.10E-02 O.10E-02 3.2 I O.10E-02 0.185 0.188 1.-
0.203 I 0.62E-03 0.65E-03 5.3 � 0.62E-03 0.203 0.204 O.l
0.220 I 0.34E-03 0.28E-03 -19.0 I 0.34E-03 0.220 0.214 -2.�
C.238 � 0.21E-p3 0.13�-03 -39.� I 0.2-�-G3 0.233 0.229 -3.;
O 2012 D. R.STRONG Consulting Engineers Inc. Page 41 of 44
Stormwater Pollution Prevention Plan Saddlebrook November 14, 2012
0.255 � 0.16E-03 0.65E-04 -60.0 I 0.163-03 0.255 0.234 -8 .1
0.272 � 0.11E-03 0.16E-04 -85.7 I 0.11�-03 0.272 0.240 -11.8
0.290 I 0.16E-04 O.00E+00 -100.0 I 0.16�-04 0.290 0.2?7 -�.3
Maximum positive excursion = 0.005 cfs ( 2.6'=)
occurring at 0.190 cfs on the Base Data:predev.tsf
and at 0.195 cfs on the New Data:dsout.tsf
Maximum negative excursion = 0.031 cfs (-27.30)
occurring at 0.114 cfs on the Base Data:predev.tsf
', and at 0.083 cfs on the New Data:dsout.tsf
O 2012 D. R.STRONG Consulting Engineers Inc. Page 42 of 44
Stormwater Pollution Prevention Plan Saddlebrook November 14, 2012
Peaks Plot
Return Period
2 5 10 20 50 100
o rdoul.pks in�ea-Tac
♦ dsout.pks
3 prcd2v.pk;
R
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1 2 5 10 20 30 40 50 60 70 80 90 95 98 99
Cumulative Probabiliry
Duration Curve
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m a� target.dur �
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ProGabilfty Exceedence
O 2012 D. R. STRONG Consulting Engineers Inc. Page 43 of 44
St�rmwater Pollution Prevention Plan Saddlebrook November 14,2012
Water Quality Treatment
The Project is located in the Basic Water Quality (WQ) Treatment area.
The Project will utilize a BayFilter vault meeting Basic Water Quality Treatment criteria.
The design information is as attached.
O 2012 D. R.STRONG Consulting Engineers Inc. Page 44 of 44
Stormwater Pollution Prevention Plan Saddlebrook November 14,2012
�e 5.
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� �'�'�'�'W� C' �+.ersea,&.ccm NO. REVISION 6Y 6ATE APrR """"�"Oi''�
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� � 13�17
A-NNNNAA
January 30, 2013
Project No. 12040
Arneta Henninger
Plan Reviewer, Development Services Division
Renton City Hall
1055 South Grady Way, 6'h Floor
Renton, Washington 98057
Re: Saddlebrook Plat, LUA 12-077, 14 Lots
Dear Mrs. Henninger:
This letter is provided as response to your letter, entitled "Saddlebrook Plat", dated January 10,
2013. Each item has been carefully reviewed and considered and the following is a summary
of how each item was addressed.
Horizontal and Vertical Control: Aqproved with condition
• Need to label the Benchmark listed (2103 & 1909) in the plan view.
The Benchmark 2103 and 1909 have been labeled and called out in the plan view.
TESC: A rov �
Road: Not Approved
• Street names: 156'h Ave SE will remain 156th Ave SE (note Not Vesta; any earlier
reference to this street being called Vesta is an error). 158th Ave SE will now be Yakima
Ave NE north the internal street which is NE ist St and Yakima Ave SE south of NE 15t
St. These are the correct street names. Plans need to show the location of street name
signs; include City of Renton standard detail in the plan set.
All references to Vesta have been removed from the plan set. Road `A' has been
changed to NE 1St St and Yakima Ave NE and SE have been called out
appropriately on the plan set. The locations of the street name signs have been
called out on sheet C3. The City of Renton standard detail for ground mounted
street name signs has been added to sheet C9.
• See typical road section on 156th Ave SE under 6" crushed rock find the first use of
word "Base" and edit to read "Top".
The first use of the word "Base" has been changed to "Top", under the typical
road section for 156th Ave SE.
• See typical road section on Yakima Ave under 6" crushed rock find the first use of word
"Base" and edit to read "Top".
The first use of the word "Base" has been changed to "Top", under
the typical road section for Yakima Ave.
Arneta Henninger
January 30, 2013
Page2of6
• Insert the word "Vertical" next to the cail out for "Curb and gutter" so as to leave no
doubt.
All references to curb and gutter now state "Vertical Curb and Gutter".
• Regarding the way the typical roadbed sections are drafted, it appears that the proposal
is to construct the entire road width with the way the callouts and leaders are drafted-
staff does not think that was the developer's intent. Review how it is drafted and revise
accordingly.
The typical roadbed sections have been revised to show the portions that are to
be constructed.
• Sheet C9 show bearing on all centerline right-of-way.
The Road and Storm Drainage Plan (Sheet C10 now) now labels bearing on all
centerline right-of-way.
• Show stationing on all centerlines. Include station equations & source (that is what is
the source of the stationing of 32+08).
The stationing on all centerlines has been shown on all pertinent sheets. The
stationing has been revised to start at monument locations. Therefore, the
station equations have been updated.
� • Show road way geometry.
; , The road way geometry (Curb Return) has been provided on the Horizontal
. Control Plan (Sheet C3).
• Use a break line and show at least one cross street & bearing.
A break line has been added to show the intersection of Yakima Ave SE and SE
136th St. The bearing has also been given for SE 136th St.
• Call out location and station to install monuments.
The location and station to install monuments have been called out on Sheet C10.
It has been noted that the monuments are to be installed per City of Renton
Standard Plan H031.
• Call out location of street name signs.
The locations of the street name signs have been called out on Sheet C3.
• Call out location and station of barrier free curb cuts.
The location and station for all barrier free curb cuts have been called out on
Sheet C3.
• Show Sta. "Begin Paving" Call out taper ratio.
"Begin Sawcut" and "End Sawcut" have been revised to "Begin Paving" and
"End Paving". The taper ratio, length and calculation have been called out where
applicable.
Arneta Henninger
January 30, 2013
Page 3 of 6
• Label adjacent PID.
All adjacent Parcels have been labeled on Sheets C2, C10, and SS1.
� See storm pipe in 156th Ave SE see CB 6-review and determine if CB 6 could not drain
directly to P101.
CB 6 is needed for drainage and cannot be eliminated.
• CB 7 should be a curb inlet; review and revise accordingly.
CB 7 has been called out as a curb inlet in both the plan and profile views.
• Tract A-label on Sheet C9 next to the pond that Landscaping to be installed by others
outside of the fenced area. Also, that Landscaping shall be maintained by the HOA.
A note has been added to the plan sheet which clarifies the landscaping around
the fenced area of the pond.
• Tract A in addition to the gate shown there also need to be an access gate to the
overflow structure on the south or southerly end of the pond.
A gate has been added near the overflow structure for access to this structure.
• The landscape plan needs to be revised around said gate.
The landscape plan has been revised around the added gate.
• The plans need to provide additional design for the storm at both north end and south of
156�h Ave SE and Yakima Ave NE and Yakima Ave SE. You might need a trash rack
and some sort of energy dissipater. Include some downstream contours.
,:
A debris barrier, per City of Renton Standard Plan 223.00, and riprap pad have
been added to the south end of Yakima Ave SE.
� Review the sidewalk transition at �he same locations mentioned above. Design
sidewalk to end with a concrete ramp to match existing grade. You may need to install
end of sidewalk signs.
A note has been added to each sidewalk ramp which states, "End of Sidewalk
Ramp with Truncated Domes (12:1 Max. Slope)." All ramps have been graded to
match existing grade with sufficient slope.
• Add City of Renton standard detail STD Plan 202 Catch Basin Installation.
This standard detail was already included within the plan set. It is located on
Sheet C14.
• Add this note to (all) plan views. Note: All Trench Restoration shall be per the current
City of Renton Trench Restoration and Street Overlay Detail. Below that note add this-
Per Section 7 Requirement for Patching, Overlay, Overlay widths, 1. Trenches (Road
Crossings) d. If the outside of the trenching is within three feet (3') of any adjacent lane
line, the entire adjacent traveled lane affected will be repaved.
This note has been added to Sheets C10 and SS1.
Arneta Henninger
January 30, 2013
Page 4 of 6
• Install "No Parking This Side" signs on NE 1S' St on the side where the fire hydrants are
located.
No parking signs have been added to the north side of NE 1S' St. This has been
called out on Sheet C10.
Storm Drainage Plans & Report: Not Approved
• !Are there any landscaping requirements applicable to this project? Will there be any
landscaping proposed in Tract A? If yes, then Tract A will be owned and maintained by
� the HOA. An easement over and across the Tract allowing the City access to inspect
� and maintain the pond and all stormwater facilities in the Tract will be recorded.
Tract "A" will be owned by the HOA and pond landscaping outside of the fenced
area shall be maintained b the HOA. A note has been rovided on Sheet C10
Y P �
stating the Tract shall have an easement over and across to allow for City access.
• Were there any flow control BMP credits taken for the use of splashblocks on the lots?
-� There was 700 s.f. of BMP credit taken for �each lot due to the use of
� splashblocks. (50% of actual area routed to splashblocks)
• Per section 1.2.4 a spill control structure is required for all projects that will result in
more than 5,000 s.f. of new pollution generating impervious surface.
� The restrictor within the control structure for the detention facility acts as a spill
control structure.
• The pre-developed area used for the sizing of the facility is bigger than the developed.
Please explain, address and clarify.
,�� The developed area has a bypass portion. Once this is included the developed
( area it will be equivalent to th� pre-developed.
• Include in the TIR sizing of the bayfilter by the manufacturer.
� The sizing for the bayfilter by the manufacturer has been included in the TIR.
• Some of the roadway improvements along 158'h Ave SE will be routed to the detention
facility. Section 1.2.3.E requires that runoff discharged from the bypassed targeted
surfaces and the flow control facility must be within a quarter mile. This is not the case
on this project and therefore, mitigation for these areas is required.
� A subsection called "TDA East Bypass Discussion", under Section IV of the
report, has been added to the TIR clarifying exemptions for this area.
• On the drainage plan please:
a. Show direction of flow.
�low direction arrows for the storm drainage have been added to the Sheet C10.
b. Show and label all easements.
'� All easements have been shown and labeled on Sheet C10.
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Arneta Henninger
January 30, 2013
Page 5 of 6
c. Will P9 conflict with the water hydrant?
�There are no hydrants in this location, only street lights.
d. Outfall protection for discharge into roadside ditch.
� A debris barrier, per City of Renton Standard Plan 223.00, and riprap pad have
� been added to the outlet into the roadside ditch.
Sanitary Sewer: Not Approved
• Label the existing sewer main in Yakima with size and drawing number (8" #S-3148);
include a station equation.
The existing sewer main in Yakima has been labeled with its size and drawing
number. The existing sewer manholes have been stationed according to
Saddlebrook's stationing along Yakima Ave.
• Label the existing sewer main in 156`h with size and drawing number (8" #S-3338);
include a station equation.
The existing sewer main in 156th has been labeled with its size and drawing
number. There is no station equation provided because there is no connection
into the existing main within 156th Ave SE.
• Add note that sewer stubs need to be 6 inches in diameter minimum.
The call out for the sewer stubs has been revised to read, "Proposed 6" Side
Sewer Stub @ 2.00% Min. (Typ.)."
• Add City of Renton standard detail STD Plan 400.4 Typical Utility Cover Adjustment for
pavement or Overlay for the sewer.
City of Renton STD. Plan 400.4 has been added to Sheet SS3.
Water: Not Approved
• Please submit the water drawings as soon as possible to avoid any unnecessary delay.
I will coordinate the plan review with the City of Renton Fire Marshal. I know that this is
WD 90 however show the location of all existing Fire hydrants within 300 feet of the
project.
A copy of the water plans has been included with this package. Existing fire
hydrants have been called out on Sheets C10 and SS1.
• Direct the landscaper that there shall be a minimum of 3 foot clear radius at all fire
hydrants.
The landscaper has been directed to keep landscaping a minimum of 3 foot clear
radius of all fire hydrants. Also, a note has been added to Sheet C10 stating this.
Street Lightinq: Not Approved
� All street lighting comments have been addressed by TraffEx.
�
. , -
Arneta Henninger
, January 30, 2013
Page 6 of 6
General
• Delete shading it does not microfilm.
Ail shading has been deleted from the plans.
If you have any questions or concerns regarding any of the items submitted, please do not
hesitate to contact me.
Sincerely yours,
D. R. STRONG Consulting Engineers Inc.
Maher A. Joudi, P.E.
Senior Project Engineer, Vice President
MAJ/ylp
Enclosures: 3 — Revised Plans (Civil, Landscape, and Illumination)
2 — Revised TI R
R:�2012101120401CorrespondencelLetterslout1L130125_HE NNI NGER.doc